further dissemination unlimited approved for public release;...rpp river protection project rtr...

Approved for Public Release; Further Dissemination Unlimited

Approved for Public Release; Further Dissemination Unlimited

By Janis Aardal at 3:29 pm, Jun 15, 2017

DOE/RL-2017-02, Rev. 0

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EXECUTIVE SUMMARY

The Hanford Site Air Operating Permit (AOP) Standard Terms and General Conditions (STGC)

Section 5.10, Annual Compliance Certification, requires submittal of an annual compliance

certification report by July 31 of each year. The regulatory agencies will use this information to

verify the U.S. Department of Energy’s compliance with the AOP.

This annual compliance certification report contains information for the reporting period of

January 1, 2016 through December 31, 2016.

The report contains emission unit-specific terms and conditions listed in AOP Attachments 1, 2,

and 3 along with a corresponding compliance status of continuous, intermittent, or not

applicable, and the method by which compliance was demonstrated.

The required information is compiled from affected Hanford Site Contractors. For this reporting

period, the affected contractors are Bechtel National, Inc.; CH2M HILL Plateau Remediation

Company; Johnson Controls, Inc.; Mission Support Alliance, LLC; Pacific Northwest National

Laboratory; and Washington River Protection Solutions, LLC.

The permittee (U.S. Department of Energy, Hanford Operations) must submit a report that is

certified by a responsible official consistent with Washington Administrative Code

(WAC) 173-401-520, “Certification.” A responsible official for a federal agency, defined under

WAC 173-401-200(29)(c), is:

“Either a principal executive officer or ranking elected official. For the purposes

of this part, a principal executive officer of a federal agency includes the chief

executive officer having responsibility for the overall operations of a principal

geographic unit of the agency (e.g., a regional administrator of EPA).”

Thus, the responsible official is represented by the managers of both the U.S. Department of

Energy, Richland Operations Office and the U.S. Department of Energy, Office of River

Protection and a joint certification is required for this submittal.

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CONTENTS

1.0 INTRODUCTION .............................................................................................................. 1 1.1 ATTACHMENT 1 REQUIREMENTS .................................................................. 2 1.2 ATTACHMENT 2 REQUIREMENTS .................................................................. 2 1.3 ATTACHMENT 3 REQUIREMENTS .................................................................. 2

2.0 REFERENCES ................................................................................................................... 3

APPENDICES

A AIR OPERATING PERMIT ATTACHMENT 1 REQUIREMENTS ............................ A-i

B AIR OPERATING PERMIT ATTACHMENT 2 REQUIREMENTS ............................ B-i

C AIR OPERATING PERMIT ATTACHMENT 3 REQUIREMENTS ............................ C-i

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ACRONYMS

ABCASH Automated Bar Coding of All Samples at Hanford

ALARA As Low As Reasonably Achievable

ALARACT As Low As Reasonably Achievable Control Technology

AMS articulating mast system

ANSI American National Standards Institute

AOP Air Operating Permit

APQ annual possession quantity

ASIL acceptable source impact level

ASME American Society of Mechanical Engineers

BACT best available control technology

BCAA Benton Clean Air Agency

BTU British thermal unit

CAM continuous air monitor

CAS Chemical Abstracts Service

CDM compliance determination method

CEM continuous emission monitor

CFR Code of Federal Regulations

CH contact handled

CHAMPS Computerized History and Maintenance Planning Software

CHPRC CH2M HILL Plateau Remediation Company

Ci curie

cm centimeters

CO carbon monoxide

COLIWASA composite liquid waste sampler

CSB Canister Storage Building

CU combustion unit

CWC Central Waste Complex

CY calendar year

DCSS dry cask storage system

DE dose equivalent

DMS Data Management System

DOE U.S. Department of Energy

DOE/RL U.S. Department of Energy, Richland Operations Office

DOH/WDOH State of Washington, Department of Health

dpm disintegrations per minute

DST double-shell tank

DVS Drum Venting System

DWP Dangerous Waste Portion (of the Resource Conservation and Recovery

Act Permit)

Ecology State of Washington, Department of Ecology

EDE effective dose equivalent

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EPA U.S. Environmental Protection Agency

EPR Electronic Prep & Risk

ERDF Environmental Restoration Disposal Facility

ESPC Energy Savings Performance Contract

ETF 200 Areas Effluent Treatment Facility

FFTF Fast Flux Test Facility

FMP Facility Modification Plans

FSF Fuel Storage Facility

FVT Filtered Vacuum Truck

GED Gaseous Emission Database

HAMMER Volpentest HAMMER Federal Training Center

HCA High Contamination Area

HDI How Do I?

HEGA high-efficiency gas absorber

HEME high-efficiency mist eliminator

HEPA high-efficiency particulate air

HIHTL hose-in-hose transfer line

HLW high-level waste

HP horsepower

HPT health physics technician

HSGS head space gas sampling

IDF Integrated Disposal Facility

IDS Interim Decay Storage

IH industrial hygiene

ISA interim storage area

JCI Johnson Controls, Inc.

JCS Job Control System

LAW low-activity waste

LERF Liquid Effluent Retention Facility

LLBG low-level burial grounds

LLMW low-level mixed waste

LLW low-level waste

MACT maximum achievable control technology

MARS Mobile Arm Retrieval System

MASF Maintenance and Storage Facility

MCO multi-canister overpack

MEI maximally exposed individual

MHF Material Handling Facility

MLLW mixed low-level waste

mrem millirem

MSA Mission Support Alliance, LLC

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NDA nondestructive assay

NDE nondestructive examination

NESHAP National Emission Standards for Hazardous Air Pollutants

NIOSH National Institute for Occupational Safety and Health

NLOP North Loadout Pit

NMHC non-methane hydrocarbons

NOC notice of construction

NOX nitrogen oxides

NRF Neutron Radiography Facility

NSR new source review

O2 oxygen

ORSS Off-Riser Sample Collection System

OSHA Occupational Safety and Health Administration

PAH polyaromatic hydrocarbon

PCB polychlorinated biphenyl

PCM periodic confirmatory measurement

PID photoionization detector

PM particulate matter

PNNL Pacific Northwest National Laboratory

PORTEX portable exhauster

ppm parts per million

PTE potential-to-emit

PTRAEU portable/temporary radioactive air emission unit

PUREX Plutonium Uranium Extraction (Plant)

QA quality assurance

R&D research and development

RCRA Resource Conservation and Recovery Act of 1976

REDOX Reduction Oxidation (Plant)

RH remote handled

RHL radioactivity handling limit

RPP River Protection Project

RTR real-time radiography

RWM restricted waste management

RWP Radiological Work Permit

S&M Surveillance and Maintenance

SAP sampling and analysis plan

SCA Soil Contamination Area

SNF spent nuclear fuel

SO2 sulfur dioxide

SOx sulfur oxides

SQER Small Quantity Emission Rate

SSP superheated steam process

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SST single-shell tank

STGC Standard Terms and General Conditions

SWITS Solid Waste Information Tracking System

TAP toxic air pollutant

T-BACT best available control technology for toxics

TEDE total effective dose equivalent

TEDF Treated Effluent Disposal Facility

TRIGA Test Reactor and Isotope Production General Atomics

TRU transuranic

TSCA Toxic Substances Control Act of 1976

TWINS Tank Waste Information Network System

ULSF ultra-low sulfur fuel

URMA Underground Radioactive Materials Area

VE visible emissions

VOA volatile organic analysis

VOC volatile organic compound

WAC Washington Administrative Code

WESF Waste Encapsulation and Storage Facility

WIPP Waste Isolation Pilot Plant

WRAP Waste Receiving and Processing Facility

WRPS Washington River Protection Solutions, LLC

WSCF Waste Sampling and Characterization Facility

WTP Waste Treatment and Immobilization Plant

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DOE/RL-2017-02, Rev. 0

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HANFORD SITE AIR OPERATING PERMIT

ANNUAL COMPLIANCE CERTIFICATION REPORT FOR THE PERIOD

JANUARY 1, 2016 THROUGH DECEMBER 31, 2016

1.0 INTRODUCTION

The Hanford Site Air Operating Permit (AOP), Number 00-05-006, Renewal 2, became effective

on April 1, 2013. AOP Standard Terms and General Conditions (STGC) Section 5.10, “Annual

Compliance Certification,” requires submittal of an annual compliance certification report by

July 31 of each year. This report is required to be certified by a Responsible Official

(Washington Administrative Code [WAC] 173-401-200(29)) for truth, accuracy, and

completeness (WAC 173-401-520, “Certification”).

This annual compliance certification report contains information from January 1, 2016 through

December 31, 2016.

NOTE: Some requirements included in AOP Renewal 2, Revision B that was effective August 1,

2016 had already become obsolete or were modified prior to or after that date. These

requirements were approved by either the State of Washington, Department of Ecology

(Ecology) or the State of Washington Department of Health (DOH) via normal, approved air

permitting processes but were not physically removed from or incorporated into AOP Renewal 2,

Revision B. During calendar year (CY) 2016, emission units were being operated pursuant to

the permitted activities that were in effect at the time.

Copies of the annual compliance certification report are transmitted to Ecology, DOH, the

Benton Clean Air Agency (BCAA), and the U.S. Environmental Protection Agency (EPA),

Region 10.

For the applicable reporting period, AOP STGC Section 5.10, “Annual Compliance

Certification,” requires the following content for the annual compliance certification report:

1. Each emission unit-specific term or condition listed in Attachments 1, 2, and 3, pursuant to

the source’s or emission unit’s operational portion of the calendar year.

2. The compliance status.

3. Whether compliance was continuous, intermittent, or not applicable.

4. Method(s) used to determine compliance status of the source over the reporting period

consistent with WAC 173-401-615(3)(a).

5. Such other facts as Ecology, DOH, or BCAA might require to determine compliance status

of the source.

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In addition, identification by the owner or operator of any material information beyond required

monitoring that potentially affects the compliance status of an emission unit will be identified in

this report, consistent with WAC 173-401-630(5)(c)(v).

No certification is required for insignificant emission units:

1.1 ATTACHMENT 1 REQUIREMENTS

AOP Attachment 1 contains terms and conditions issued by Ecology. Appendix A of this report

provides emission unit-specific terms and conditions, compliance status during the reporting

period, and the basis used to determine the compliance status.


AOP Attachment 2 contains terms and conditions issued by DOH. Emission unit-specific terms

and conditions are contained in Enclosure 1 of Attachment 2. Appendix B of this report provides

emission unit-specific terms and conditions, the compliance status during the reporting period,

and the basis used to determine compliance status.


AOP Attachment 3 contains conditions issued by BCAA which apply on a sitewide basis. These

two conditions are for asbestos and open burning. Appendix C of this report lists the conditions,

the compliance status during the reporting period, and the basis used to determine compliance

status.

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2.0 REFERENCES

40 CFR 51, “Requirements for Preparation, Adoption, and Submittal of Implementation Plans,”

Title 40, Code of Federal Regulations, Part 51, as amended.

40 CFR 60, “Standards of Performance for New Stationary Sources,” Title 40, Code of Federal

Regulations, Part 60, as amended.

40 CFR 61, “National Emission Standard for Hazardous Air Pollutants,” Subpart M, “National

Emission Standards for Asbestos,” Title 40, Code of Federal Regulations, Part 61, as

amended.

40 CFR 63, “National Emission Standards for Hazardous Air Pollutants for Source Categories,”

Title 40, Code of Federal Regulations, Part 63, as amended.

40 CFR 80, “Regulation of Fuels and Fuel Additives,” Title 40, Code of Federal Regulations,

Part 80, as amended.

40 CFR 86, “Control of Emissions from New and In-Use Highway Vehicles and Engines,” Title

40, Code of Federal Regulations, Part 86, as amended.

40 CFR 89, “Control of Emissions from New and In-Use Nonroad Compression-Ignition

Engines,” Title 40, Code of Federal Regulations, Part 89, as amended.

Benton Clean Air Agency, Regulation 1.

DOE/RL-2016-05, 2016, Hanford Site Air Operating Permit Semiannual Report for the Period

January 1, 2016 through June 30, 2016, U.S. Department of Energy, Richland Operations

Office, Richland, Washington.

DOE/RL-2016-10, 2016, Radionuclide Air Emissions Report for the Hanford Site, Calendar

Year 2015, U.S. Department of Energy, Richland Operations Office, Richland,

Washington.

DOE/RL-2017-01, 2017, Hanford Site Air Operating Permit Semiannual Report for the Period

July 1, 2016 through December 31, 2016, U.S. Department of Energy, Richland Operations

Office, Richland, Washington.

WAC 173-400, “General Regulations for Air Pollution Sources,” Washington Administrative

Code, Olympia, Washington.

WAC 173-401, “Operating Permit Regulation,” Washington Administrative Code, Olympia,

Washington.

WAC 173-425, “Outdoor Burning,” Washington Administrative Code, Olympia, Washington

WAC 173-460, “Controls for New Sources of Toxic Air Pollutants,” Washington Administrative

Code, Olympia, Washington.

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WAC 173-491, “Emission Standards and Controls for Sources Emitting Gasoline Vapors,”

Washington Administrative Code, Olympia, Washington.

WAC 246-247, “Radiation Protection – Air Emissions,” Washington Administrative Code,

Olympia, Washington.

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APPENDIX A

AIR OPERATING PERMIT

ATTACHMENT 1 REQUIREMENTS

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CONTENTS

Emission Units are in order of AOP Page Number in Renewal 2, Revision B.

General Standards ........................................................................................................................... 1

Energy Savings Performance Contract Boilers ............................................................................... 3

234-5Z, Boiler 1, 2 and 3 (>5mmBTU/hr-Fuel Oil) ....................................................................... 9

242-A, Boiler 1, 2 and 3 (>5 mmBTU/hr – Fuel Oil) ................................................................... 12

318 Boiler (<5 mmBTU/hr–Natural Gas) ..................................................................................... 15

323 Boiler (<5 mmBTU/hr–Natural Gas) ..................................................................................... 16

3709A Boiler (<5 mmBTU/hr–Natural Gas) ................................................................................ 18

324 Boiler 1 and Boiler 2 (>5 mmBTU/hr–Natural Gas) ............................................................. 19

325 Boiler 1 and Boiler 2 (>5 mmBTU/hr–Natural Gas) ............................................................. 22

331 Boiler 1 and Boiler 2 (<5 mmBTU/hr–Natural Gas) ............................................................. 24

Portable Boiler (<5 mmBTU/hr–Dual Fuel) ................................................................................. 27

E-225BC 001 ................................................................................................................................ 31

E-225BG 001 ................................................................................................................................ 32

E-4250-001, G-3 ........................................................................................................................... 33

E-WSCF 001 ................................................................................................................................. 34

J-CWC 001.................................................................................................................................... 35

Concrete Batch Plant..................................................................................................................... 36

E-282ED 001 ................................................................................................................................ 38

E-282WD 001 ............................................................................................................................... 39

E-3709A-001................................................................................................................................. 40

E-331-001 ..................................................................................................................................... 42

E-325-001 ..................................................................................................................................... 43

P-2025E ETF ................................................................................................................................ 45

P-2706T 001.................................................................................................................................. 47

P-296A042-001 ............................................................................................................................. 48

P-296W004 001 ............................................................................................................................ 50

P-WTP-001 ................................................................................................................................... 53

Integrated Disposal Facility .......................................................................................................... 61

Ventilation Systems for 241-AN and 241-AW Tank Farms ........................................................ 64

200 Area Single Shell Tank Categorical Waste Retrieval ............................................................ 68

E-85 Fuel Station .......................................................................................................................... 72

600 Area Diffuse/Fugitive – HAMMER ...................................................................................... 73

181B/182B Emergency Diesel Engines ........................................................................................ 75

WTP Construction Heaters & Dehumidifiers ............................................................................... 75

E-339A-001................................................................................................................................... 77

241-AP, 241-SY, and 241-AY/AZ Ventilation (AOP Cert. Rep. Compilation) .......................... 78

Lagoon Treatment System ............................................................................................................ 78

211ED/212ED Diesel Generator................................................................................................... 79

Single-Shell Tank Direct Fired Water Heaters ............................................................................. 79

Hanford Site Asbestos Landfill ..................................................................................................... 79

G-6290 (600 Area Gasoline Distribution) .................................................................................... 81

6120 Tent (200 East) ..................................................................................................................... 82

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100K Water Treatment Plant ........................................................................................................ 83

385 Building.................................................................................................................................. 84

219H Tent and MO-414 (200E) .................................................................................................... 85

North of MO-414 (200E) 1 of 2 .................................................................................................... 86

North of MO-414 (200E) 2 of 2 .................................................................................................... 87

WTP MHF South-40 Laydown Critical Equipment Storage ........................................................ 88

2720EA ......................................................................................................................................... 89

Rattle Snake Barricade .................................................................................................................. 89

222-SE........................................................................................................................................... 90

242-A ............................................................................................................................................ 90

234-5Z ........................................................................................................................................... 91

400 Area ........................................................................................................................................ 92

600 Area Fire Station (Building (609A) ....................................................................................... 93

2721E ............................................................................................................................................ 94

Yakima Barricade ......................................................................................................................... 95

282-B............................................................................................................................................. 96

282-BA .......................................................................................................................................... 97

225BC ........................................................................................................................................... 98

TEDF Pump Station 2 (225E) ....................................................................................................... 99

WTP MHF South-40 Laydown Entry Gate (Light Tower) ........................................................ 100

WTP MHF North-10 Laydown Area (Light Tower) 1 of 2 ........................................................ 101

WTP MHF North-10 Laydown Area (Light Tower) 2 of 2 ........................................................ 102

WTP MHF South-40 Laydown Yard East X-Ray Tent .............................................................. 103

WTP Construction Site Pretreatment Tower Crane .................................................................... 104

WTP Construction Site High-Level Waste Tower Crane ........................................................... 106

WTP Construction Site Building T-14 ....................................................................................... 107

Light Towers Waste Transfer Corridor East ............................................................................... 108

Light Towers Waste Transfer Corridor West ............................................................................. 109

Light Towers C Farm Trailer Area ............................................................................................. 110

Light Towers C Farm .................................................................................................................. 111

AY/AZ Farm DMI-LT Light Tower ........................................................................................... 112

C and AN Farm Compressors ..................................................................................................... 113

Light Towers AN Farm ............................................................................................................... 114

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General Standards

Page in AOP Page in AOP Renewal 2, Revision A: 1-01

Page in AOP Page in AOP Renewal 2, Revision B: 1-08

Requirement Compliance

Status

Compliance Determination

Method

Condition: 20% Opacity.

Prohibits visible emissions exceeding 20% opacity for more

than 3 minutes in any 1 hour of an air contaminant from any

emissions unit or within a reasonable distance of the emission

unit except for scheduled soot blowing/grate cleaning or due to

documented water.

Periodic Monitoring: Visible emission surveys (2.1)

Test Method: EPA Method 9 of 40 CFR 60, Appendix A.

Test Frequency: Not applicable.

Required Records: As specified in Section 2.1.

Calculation Model: Not applicable.

Intermittent

CDM: Records review and

field observations as required

by Air Operating Permit

(AOP) Attachment 1, Section

2.1.

Comment: Review of

facility records indicated that

visible emission surveys

were not performed for

single-shell tank (SST)

Retrieval Direct Fired Water

Heaters in calendar year

(CY) 2016.

Condition: Fallout.

Prohibits emissions of particulate matter from any source to be

deposited beyond the facility boundaries in sufficient quantity

to interfere unreasonably with the use and enjoyment of the

property upon which the material was deposited.

Periodic Monitoring: Recordkeeping of complaint

investigation. (2.2)

Test Method: Not specified.




Continuous

CDM: No requests for

complaint investigations

were received from State of

Washington Department of

Ecology (Ecology) during

CY 2016 for issues related to

this standard (as required by

AOP Attachment 1, Section

2.2).

Condition: Fugitive emissions.

The Permittee shall take reasonable precautions to prevent the

release of air contaminants from any emissions unit engaging in

materials handling, construction, demolition, or any other

operation that is a source of fugitive emissions.

Periodic Monitoring: Pre-job planning to determine

reasonable control measures. (2.3)





Continuous CDM: Records review and

procedural adherence.

Condition: Odor.

Requires any facility causing an odor that unreasonably

interferes with another person's use and enjoyment of their

property to use recognized good practices and procedures to

reduce odors to a reasonable minimum.


investigations. (2.2)





Continuous



were received from Ecology

during CY 2016 for issues

related to this standard (as

required by AOP Attachment

1, Section 2.2).

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Status


Method

Condition: Emissions detrimental to persons or property.

Prohibits emissions of any air contaminant from any source that

is detrimental to the health, safety, or welfare of any person, or

causes damage to property or business







Continuous







1, Section 2.2)

Condition: 1,000 ppm SO2 @7% O2 on a dry basis.

Prohibits emission of a gas containing sulfur dioxide from any

emissions unit in excess of 1,000 ppm of a dry basis, corrected

to 7% oxygen for combustion sources, and based on the

average of any period of 60 consecutive minutes.

Periodic Monitoring: For fossil-fuel combustion units:

Recordkeeping of the certification that Ultra Low Sulfur Fuel

was used. (2.7)

Test Method: EPA Method 6 or 6C of 40 CFR 60, Appendix

A.




Continuous

CDM: Reviewed fuel

records to verify ultra-low

sulfur fuel [ULSF] (<0.0015

wt. %) was purchased and

consumed.

Condition: Concealment and masking.

Prohibits the installation or use of any device or use of any

means that conceals or masks an emission of an air contaminant

that would otherwise violate any provision of WAC 173-400.







Continuous







1, Section 2.2)

Condition: Fugitive dust.

Requires reasonable precautions be taken to prevent fugitive

dust from becoming airborne and to minimize dust generation.


reasonable control measures. (2.3)





Continuous CDM: Records review and

procedural adherence.

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Energy Savings Performance Contract Boilers

Energy Savings Performance Contract (ESPC) Boilers consist of the following boilers: 242-A, Boiler 1 | 234-5Z,

Boiler 1 | 234-5Z, Boiler 2 | 234-5Z Boiler 3 | 242-A, Boiler 2 | 242-A, Boiler 3 | 318, Boiler 1 | 323, Boiler 1 |

3709A, Boiler 1 | Portable Boiler 1 | 324, Boiler 1 | 324, Boiler 2 | 325, Boiler 1 | 325, Boiler 2 | 331, Boiler 1 | 331,

Boiler 2 |

Page in AOP Renewal 2, Revision A: 1-012 Permit: AOP 1.3 NG (Less than 5mmBTU/hr

Issue Date: 04-01-13 Effective Date: 04-01-13 Obsolete Date: 07-31-16 Date In AOP: 04-01-13

NOC: AOP Table 1.3 Natural Gas Steam Generator (Less than 5mmBTU/hr)


Status


Method

Condition: WAC 173-400-040(1)

20% Opacity:




unit except for scheduled soot blowing/grate cleaning or due

to documented water.

Periodic Monitoring: Visible emission surveys, Section 2.1,

Tier 2

Test Method: EPA Method 9 of 40 CFR 60, Appendix A

Test Frequency: At least once per quarter.



Continuous

CDM: Visual observations

and inspections are made

during daily rounds. Visible

emissions are considered an

unusual or abnormal

condition signaling

operational difficulties.

Conditions of this type are

recorded on round sheets

and in the operations log.

Corrective measures are

immediately implemented

whenever possible or

entered into the Johnson

Control, Inc. (JCI)

Maintenance Management

Program. In addition,

presence or absence of

visible emissions are noted

on monthly inspection

checklists. Checklists are

maintained and available for

review on request.

Comment: No unusual

conditions were noted

during the period of

compliance January 1, 2016

through December 31, 2016.

Permit: AOP 1.3 NG (5mmBTU/hr and Greater)


NOC: AOP Table 1.3 Natural Gas Steam Generators (5mmBTU/hr and Greater)


Status


Method

Condition: WAC 173-400-040(1) [Table 1.2 General

Standard]

20% Opacity.


Continuous

CDM: Visual observations

and inspections are made

during daily rounds. Visible

emissions are considered an

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Status


Method



unit except for scheduled soot blowing/grate cleaning or due to

documented water.

Periodic Monitoring: Visible Emission surveys, Section 2.1,

Tier 2


Test Frequency: At least once per quarter.

Required Records: As specified in Section 2.1


unusual or abnormal

condition signaling

operational difficulties.

Conditions of this type are

recorded on round sheets

and in the operations log.

Corrective measures are

immediately implemented

whenever possible or

entered into the JCI

Maintenance Management

Program. In addition,

presence or absence of

visible emissions are noted

on monthly inspection

checklists. Checklists are

maintained and available for

review on request.

Comment: No unusual

conditions were noted

during the period of

compliance January 1, 2016

through December 31, 2016.

Condition: 97NM-138

NOx shall not exceed 0.037 lb/mmBTU and 30 ppm @ 3% O2.

Periodic Monitoring: Recordkeeping. Section 2.5

See Section 2.6

Test Method: EPA Method 7E of 40 CFR 60, Appendix A




Continuous

CDM: Owner/operator

maintains required records

of monthly fuel use and

provides an annual report

and certification that this

represents all fuel

combusted during the year.

Logs of boiler tune-ups and

significant boiler

maintenance activities are

kept, indicating good

combustion practices and

maximum achievable

control technology (MACT)

standards are maintained.

Condition: 97NM-138

CO shall not exceed 0.225 lb/mmBTU and 300 ppm @ 3% O2.


See Section 2.6





Continuous

CDM: Owner/operator





represents all fuel



significant boiler




MACT standards are

maintained.

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Status


Method

Condition: 97NM-138

Particulate matter (PM10) shall not exceed 0.012 lb/mmBTU.


See Section 2.6





Continuous

CDM: Owner/operator





represents all fuel



significant boiler




MACT standards are

maintained.

Condition: 97NM-138

VOC shall not exceed 0.013 lb/mmBTU and 30 ppm @ 3% O2.


See Section 2.6

Test Method: EPA Method 25 or

25A of 40 CFR 60, Appendix A




Continuous

CDM: Owner/operator





represents all fuel



significant boiler




MACT standards are

maintained.

Condition: 97NM-138

S02 shall not exceed 0.0006 lb/mmBTU.


See Section 2.6

Test Method: EPA Method 6 or

6C of 40 CFR 60, App. A.




Continuous

CDM: Owner/operator





represents all fuel



significant boiler




MACT standards are

maintained.

Permit: AOP 1.3 FO (5mmBTU/hr and Greater)


NOC: AOP Table 1.3 Fuel Oil Steam Generators (5mmBTU/hr and Greater)

DOE/RL-2017-02, Rev. 0

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Status Compliance Determination Method

Condition: WAC 173-400-040(1) [Table 1.2 General

Standard]

20% Opacity.

Prohibits visible emissions exceeding 20% opacity for

more than 3 minutes in any 1 hour of an air contaminant

from any emissions unit or within a reasonable distance

of the emission unit except for scheduled soot

blowing/grate cleaning or due to documented water.

Periodic Monitoring: Visible emission surveys, See

Section 2.1

Test Method: EPA Method 9 of 40 CFR 60,

Appendix A.




Continuous

CDM: Visual observations and

inspections are made during daily

rounds. Visible emissions are

considered an unusual or abnormal

condition signaling operational

difficulties. Conditions of this type

are recorded on round sheets and in

the operations log. Corrective

measures are immediately

implemented whenever possible or

entered into the JCI Maintenance

Management Program. In addition,

presence or absence of visible

emissions are noted on monthly

inspection checklists. Checklists are

maintained and available for review

on request.

Comment: No unusual conditions

were noted during the period of

compliance January 1, 2016 through

December 31, 2016.

Condition: 97NM-138

0.05% sulfur distillate fuel oil will be used in the 200

Areas; natural gas will be used in the 300 Area. 200 HP

Portable boiler uses 0.0015% sulfur distillate fuel oil.






Continuous

CDM: Owner/operator maintains

required records of monthly fuel use

and provides an annual report and

certification that this represents all

fuel combusted during the year. Logs

of boiler tune-ups and significant

boiler maintenance activities are kept,

indicating good combustion practices

and MACT standards are maintained.

Condition: 97NM-138

NOx shall not exceed 0.150 lb/mmBTU and 115 ppm @

3% O2.


See Section 2.6

Test Method: EPA Method 7E of 40 CFR 60, App. A.




Continuous










Condition: 97NM-138

SO2 shall not exceed 0.051 lb/mmBTU.

Periodic Monitoring: Recordkeeping. Section 2.5 See

Section 2.6

Test Method: EPA Method 6 or 6C of 40 CFR 60,

App. A




Continuous










Condition: 97NM-138

CO shall not exceed 0.071 lb/mmBTU and 90 ppm @

3% O2.

Continuous




DOE/RL-2017-02, Rev. 0

A-7




See Section 2.6

Test Method: EPA Method 10 of 40 CFR 60, App. A










Condition: 97NM-138

Particulate matter (PM10) shall not exceed 0.011

lb/mmBTU.


See Section 2.6

Test Method: EPA Method 5 of 40 CFR 60, App. A




Continuous










Condition: 97NM-138

VOC shall not exceed 0.013 lb/mmBTU and 30 ppm @

3% O2.


See Section 2.6

Test Method: EPA Method 25 or 25A of 40 CFR 60,

App. A




Continuous










Permit: AOP 1.3 Small Industrial Units


NOC: AOP Table 1.3 Small Industrial-Commercial-Institutional Steam Generating Units



Condition: 40 CFR 60 Subpart Dc; WAC 173-400-115

0.5 weight percent sulfur fuel (NOC 97NM-138

condition listed below)

Periodic Monitoring: Fuel supplier certifications and

monthly records reported annually. Recordkeeping.

Section 2.5





Continuous










Permit: AOP 1.3 Good Combustion Practices


NOC: Good Combustion Practices for All Boilers

DOE/RL-2017-02, Rev. 0

A-8



Condition: Operation and maintenance manuals will be

obtained from the manufacturer(s) and made available

for review by Ecology on request.

Periodic Monitoring: None.



Required Records: Not specified.


Continuous CDM: Operation and Maintenance

manuals are available for review.

Condition: DAILY

1. Visually check combustion.

2. Record available operating data.

Periodic Monitoring: Not specified.





Continuous


inspections are conducted daily.

Operating data are recorded and daily

round sheet records are maintained.

In addition, abnormal conditions are

discussed and corrective measures

immediately are implemented

whenever possible or entered into the

JCI Maintenance Management

Program.

Condition: MONTHLY

1. Inspect burner.

2. Inspect boiler exteriors.

3. Check combustion controls.

4. Check for leaks.

5. Check for unusual noise, vibrations, etc.






Continuous


inspections are made monthly.

Abnormal conditions (leaks,

excessive noise, vibrations) are

recorded on monthly inspection

checklists and records are maintained.

Corrective measures immediately are



Management Program.

Condition: SEMI-ANNUALLY

1. Visually inspect air supply system, and clean and

repair if necessary.

2. Clean and check fuel supply system (visually inspect

and replace filters if necessary).






Continuous


inspections are conducted monthly.

Abnormal conditions are discussed

and recorded and checklists are

maintained. Corrective measures




Program.

Condition: ANNUALLY

1. Conduct boiler tuneups on large boilers

(>5mmBTU/hr heat input) by manufacturer trained

technicians or other qualified personnel. Section 2.5

Recordkeeping.

2. Clean fireside surfaces and breaching for power

boilers.

3. Inspect refractory for power boilers.

Periodic Monitoring: Not Specified.



Continuous

CDM: Boiler tune-ups are performed

annually or more frequently if

needed. Tapes recording the tune-up

and boiler performance are

maintained as records. Fireside

surfaces and breaching are cleaned

just prior to the annual inspection.

Annual internal inspection is

conducted by a third-party certified

inspector. The inspector completes a

report certifying conditions were

satisfactory. Any unsatisfactory

DOE/RL-2017-02, Rev. 0

A-9





conditions immediately are corrected,

otherwise certification for operation

will not be granted. The inspection

report is maintained as record of the

inspection.

Condition: EVERY TWO YEARS

1. Conduct boiler tuneups on smaller boilers

2. Inspect refractory for low pressure boilers.

3. Clean fireside surfaces and breaching for low

pressure boilers.

Periodic Monitoring: Not Specified.





Continuous


annually or more frequently if

needed. Tapes recording the tune-up

and boiler performance are

maintained as records. Fireside

surfaces and breaching are cleaned

just prior to the biennial inspection.

The internal inspection is conducted

every 2 years by a third-party

certified inspector. The inspector

completes a report certifying

conditions were satisfactory. Any

unsatisfactory conditions

immediately are corrected or

certification for operation will not be

granted. The inspection report is

maintained as record of inspection.

Comment: No unsatisfactory

conditions were noted for the last

biennial inspection.

234-5Z, Boiler 1, 2 and 3 (>5mmBTU/hr-Fuel Oil)

Page in AOP Renewal 2, Revision B: 1-013 Permit: 234-5Z, Boiler 1, 2 and 3 (>5mmBTU/hr-Fuel Oil)

Issue Date: 08-01-16 Effective Date: 08-01-16 Date In AOP: 08-01-16

NOC: 234-5Z, Boiler 1, 2 and 3 (>5mmBTU/hr-Fuel Oil)



Condition: 20% opacity: Prohibits visible emissions

exceeding 20% opacity for more than 3 minutes in any 1

hour of an air contaminant from any emissions unit or

within a reasonable distance of the emission unit except

for scheduled soot blowing/grate cleaning or due to

documented water.

Periodic Monitoring: Section 2.1.

Test Method: EPA Method 9 of 40 CFR 60, Appendix

A.

Test Frequency: Quarterly.

Required Records: As specified in Section 2.1, Tier 1


Continuous
















DOE/RL-2017-02, Rev. 0

A-10




on request.




December 31, 2016.

Condition: Use of fuel per 97NM-138

Periodic Monitoring: Compliance will be demonstrated

by use of fuel containing no greater than 0.05 weight

percent sulfur (500 parts per million by weight).

Test Method: Not applicable.


Required Records: Vendor certification for diesel fuel

sulfur content for all purchases.


Continuous










Condition: NOx shall not exceed 0.150 lb/mm BTU

and 115 ppm @ 3% O2


Test Method: EPA Method 7E of 40 CFR 60,

Appendix A.

Test Frequency: Monthly

Required Records: Monthly records of fuel use on

each boiler (See Section 2.5).


Continuous










Condition: SO2 shall not exceed 0.051 lb/mm BTU


Frequency: Monthly


Appendix A.





Continuous










Condition: CO shall not exceed 0.071 lb/mm BTU and

90 ppm @ 3% O2

Periodic Monitoring: Section 2.6

Frequency: Monthly

Test Method: EPA Method 10of 40 CFR 60, Appendix

A.





Continuous










Condition: Particulate matter (PM10) shall not exceed

0.011 lb/mm BTU.


Frequency: Monthly


A



Continuous








DOE/RL-2017-02, Rev. 0

A-11







Condition: VOC shall not exceed 0.013 lb/mm BTU

and 30 ppm @ 3% O2


Frequency: Monthly


Appendix A.





Continuous










Condition: A. Inspect burner.

B. Inspect boiler exteriors.

C. Check combustion controls.

D. Check for leaks.

E. Check for unusual noise, vibrations, etc.

Periodic Monitoring: Not applicable.

Frequency: Monthly



Required Records: Records of inspections.


Continuous








whenever possible or entered into

JCI's Maintenance Management

Program.

Condition: Visual check of combustion.

Periodic Monitoring: Not applicable

Frequency: Daily



Required Records: Record available operating data.


Continuous










Program.

Condition: A. Inspect air supply system and clean and


B. Clean and check fuel supply system, replace filters if

necessary.


Frequency: Semi-annually.



Required Records: Records of inspections and work

performed.


Continuous









Program.

Condition: A. Conduct boiler tune-up by manufacturer

trained technician or other qualified personnel.

B. Clean fireside surfaces and breaching.

C. Inspect refractory.


Frequency: Annually.


Continuous


annually or more frequently if needed.

Tapes recording the tune-up and

boiler performance are maintained as

records. Fireside surfaces and

breaching are cleaned just prior to the

annual inspection. Annual internal

DOE/RL-2017-02, Rev. 0

A-12




Required Records: See Section 2.5.


inspection is conducted by a third-

party certified inspector. The

inspector completes a report certifying


unsatisfactory conditions immediately

are corrected, otherwise certification

for operation will not be granted. The

inspection report is maintained as

record of the inspection.

242-A, Boiler 1, 2 and 3 (>5 mmBTU/hr – Fuel Oil)

Page in AOP Renewal 2, Revision B: 1-017

Permit: 242-A, Boiler 1, 2 and 3 (>5 mmBTU/hr-Fuel Oil)


NOC: 242-A, Boiler 1, 2 and 3 (>5 mmBTU/hr-Fuel Oil)








documented water.



A

Test Frequency: Quarterly

Required Records: As specified in Section 2.1, Tier 1


Continuous

















on request.




December 31, 2016.

Condition: Use of fuel per 97NM-138









Continuous










DOE/RL-2017-02, Rev. 0

A-13




and 115 ppm @ 3% O2.


Frequency: Monthly.


Appendix A.





Continuous










Condition: SO2 shall not exceed 0.051 lb/mm BTU.


Frequency: Monthly.


Appendix A.





Continuous











90 ppm @ 3% O2.


Frequency: Monthly


A.





Continuous











0.011 lb/mm BTU.


Frequency: Monthly


A.





Continuous











and 30 ppm @ 3% O2.


Frequency: Monthly


Appendix A.





Continuous











B. Inspect boiler exteriors. Continuous



DOE/RL-2017-02, Rev. 0

A-14




D. Check for leaks.



Frequency: Monthly












Program.



Frequency: Daily





Continuous










Program.




necessary.


Frequency: Semi-annually




performed.


Continuous









Program.



B. Clean fireside surfaces and breaching.

C. Inspect refractory.


Frequency: Annually





Continuous

















DOE/RL-2017-02, Rev. 0

A-15

318 Boiler (<5 mmBTU/hr–Natural Gas)


Permit: 318 Boiler (<5 mmBTU/hr – Natural Gas


NOC: 318 Boiler (<5 mmBTU/hr – Natural Gas)








documented water.



A.


Required Records: As specified in Section 2.1, Tier 2.


Continuous

















on request.




December 31, 2016.



Frequency: Daily.





Continuous










Program.




necessary.






performed.


Continuous









Program.




Continuous




DOE/RL-2017-02, Rev. 0

A-16



D. Check for leaks.



Frequency: Monthly.

Test Method: Not Applicable.









Program.



B. Inspect refractory.

C. Clean fireside surfaces and breaching.


Frequency: Every two years.





Continuous







inspection. Internal inspection is

conducted every 2 years by a third-









323 Boiler (<5 mmBTU/hr–Natural Gas)


Permit: 323 Boiler (<5 mmBTU/hr-Natural Gas)


NOC: 323 Boiler (<5 mmBTU/hr-Natural Gas








documented water.



A.




Continuous

CDM: This discharge point was

demolished prior to this certification

reporting year.

DOE/RL-2017-02, Rev. 0

A-17






D. Check for leaks.



Frequency: Monthly.





Continuous



reporting year.



Frequency: Daily.





Continuous



reporting year.




necessary.






performed.


Continuous



reporting year.











Continuous



reporting year.

DOE/RL-2017-02, Rev. 0

A-18

3709A Boiler (<5 mmBTU/hr–Natural Gas)

Page in AOP Renewal 2, Revision B: 1-025 Permit: 3709A Boiler (<5 mmBTU/hr-Natural Gas)

Issue Date: 08-01-16 Effective Date:08-01-16 Date In AOP: 08-01-16

NOC: 3709A Boiler (<5 mmBTU/hr-Natural Gas)








documented water.



A.




Continuous

















on request.




December 31, 2016.




D. Check for leaks.



Frequency: Monthly.



Required Records: Record of inspections.


Continuous









Program.



Frequency: Daily.





Continuous










Program.




Continuous




DOE/RL-2017-02, Rev. 0

A-19



necessary.






performed.







Program.









Required Records: See Section 2.5


Continuous







inspection. Internal inspection is

conducted by a third-party certified

inspector every 2 years. The inspector

completes a report certifying







324 Boiler 1 and Boiler 2 (>5 mmBTU/hr–Natural Gas)


Permit: 324 Boiler 1and 2 (>5 mmBTU/hr-Natural Gas)


NOC: 324 Boiler 1 and 2 (>5 mmBTU/hr-Natural Gas)








documented water.



A.




Continuous

















on request.

DOE/RL-2017-02, Rev. 0

A-20






December 31, 2016.



Frequency: Monthly


Appendix A.





Continuous











and 30 ppm @ 3% O2.


Frequency: Monthly


Appendix A.





Continuous











300 ppm @ 3% O2.


Frequency: Monthly


A.





Continuous











0.012 lb/mm BTU.


Frequency: Monthly


A.





Continuous











and 30 ppm @ 3% O2


Frequency: Monthly


Appendix A.



Continuous








DOE/RL-2017-02, Rev. 0

A-21









Frequency: Daily.





Continuous










Program.




D. Check for leaks.



Frequency: Monthly





Continuous










Program.




necessary.






performed.


Continuous










Program.






Frequency: Annually





Continuous



Tapes recording the tune-up and boiler

performance are maintained as









are corrected otherwise certification




DOE/RL-2017-02, Rev. 0

A-22

325 Boiler 1 and Boiler 2 (>5 mmBTU/hr–Natural Gas)


Permit: 325 Boiler 1 and 2 (>5 mmBTU/hr-Natural Gas)


NOC: 325 Boiler 1 and 2 (>5 mmBTU/hr-Natural Gas)








documented water.



A.




Continuous






difficulties. Conditions of this type are

recorded on round sheets and in the

operations log. Corrective measures

are immediately implemented



Program. In addition, presence or

absence of visible emissions are noted

on monthly inspection checklists.

Checklists are maintained and available

for review on request.

Comment: No unusual conditions were

noted during the period of compliance

January 1, 2016 through December 31,

2016.



Frequency: Monthly


Appendix A.





Continuous




certification that this represents all fuel

combusted during the year. Logs of

boiler tune-ups and significant boiler

maintenance activities are kept,




and 30 ppm @ 3% O2.


Frequency: Monthly


Appendix A.

Test Frequency: Not spplicable.




Continuous











300 ppm @ 3% O2.


Frequency: Monthly


A.

Continuous







DOE/RL-2017-02, Rev. 0

A-23











0.012 lb/mm BTU.


Frequency: Monthly


A.





Continuous











and 30 ppm @ 3% O2.


Frequency: Monthly


Appendix A.





Continuous












Frequency: Daily.





Continuous




round sheet records are maintained. In

addition, abnormal conditions are





Program.




D. Check for leaks.



Frequency: Monthly





Continuous










Program.




necessary.



Continuous



Abnormal conditions are discussed and

recorded and checklists are maintained.



DOE/RL-2017-02, Rev. 0

A-24






performed.



Management Program.






Frequency: Annually





Continuous




performance are maintained as records.

Fireside surfaces and breaching are

cleaned just prior to the annual

inspection. Annual internal inspection

is conducted by a third-party certified




conditions immediately are corrected




inspection.

331 Boiler 1 and Boiler 2 (<5 mmBTU/hr–Natural Gas)

Page in AOP Renewal 2, Revision B: 1-035 Permit: 331 Boiler 1 and 2 (<5 mmBTU/hr-Natural Gas)


NOC: 331 Boiler 1 and 2 (<5 mmBTU/hr-Natural Gas)








documented water.



A.




Continuous




















2016.

DOE/RL-2017-02, Rev. 0

A-25



Condition: S O2 shall not exceed 0.0006 lb/mm BTU.


Frequency: Monthly.


Appendix A.





Continuous











and 30 ppm @ 3% O2.


Frequency: Monthly


Appendix A.





Continuous











300 ppm @ 3% O2.


Frequency: Monthly


A.





Continuous











0.012 lb/mm BTU.


Frequency: Monthly


A.





Continuous











and 30 ppm @ 3% O2.


Frequency: Monthly


Appendix A.





Continuous











Periodic Monitoring: Not applicable. Continuous



DOE/RL-2017-02, Rev. 0

A-26



Frequency: Daily.












Program.




D. Check for leaks.



Frequency: Monthly





Continuous










Program.




necessary.






performed.


Continuous








Management Program.






Frequency: Annually





Continuous












conditions immediately are corrected,




inspection.

DOE/RL-2017-02, Rev. 0

A-27

Portable Boiler (<5 mmBTU/hr–Dual Fuel)

Page in AOP Renewal 2, Revision B: 1-039 Permit: Portable Boiler (<5 mmBTU/hr-Dual Fuel)


NOC: Portable Boiler (<5 mmBTU/hr-Dual Fuel)



Natural Gas

Condition: SO2 shall not exceed 0.0006 lb/mm BTU –

fired using natural gas


Frequency: Monthly


Appendix A.





Continuous











and 30 ppm @ 3% O2 – fired using natural gas


Frequency: Monthly


Appendix A.





Continuous











300 ppm @ 3% O2 – fired using natural gas.


Frequency: Monthly


A.





Continuous











0.012 lb/mm BTU – fired using natural gas.


Frequency: Monthly


A.





Continuous










DOE/RL-2017-02, Rev. 0

A-28




and 30 ppm @ 3% O2 – fired using natural gas.


Frequency: Monthly


Appendix A.





Continuous










Distillate Fuel Oil

Condition: Use of fuel per 97NM-138 – fired using

distillate fuel-oil.









Continuous











and 115 ppm @ 3% O2 – fired using distillate fuel-oil.


Frequency: Monthly


Appendix A.





Continuous










Condition: SO2 shall not exceed 0.051 lb/mm BTU –

fired using distillate fuel-oil.


Frequency: Monthly

Test Method: EPA Method 6 or 6C10 of 40 CFR 60,

Appendix A.





Continuous











90 ppm @ 3% O2 – fired using distillate fuel-oil.


Frequency: Monthly

Test Method: EPA Method 10, 40 CFR 60, Appendix

Continuous






DOE/RL-2017-02, Rev. 0

A-29



A.










0.011 lb/mm BTU – fired using distillate fuel-oil.


Frequency: Monthly


A.





Continuous











and 30 ppm @ 3% O2 – fired using distillate fuel-oil.


Frequency: Monthly


Appendix A.





Continuous










Conditions Applicable Regardless of Fuel Used






documented water.



A.




Continuous




















2016.



Frequency: Daily.



Continuous






DOE/RL-2017-02, Rev. 0

A-30









Program.

Condition: A. Inspect burner

B. Inspect boiler exteriors

C. Check combustion controls

D. Check for leaks



Frequency: Monthly





Continuous










Program.




necessary.






performed.


Continuous








Management Program.






Frequency: Annually





Continuous












conditions immediately are corrected




inspection.

DOE/RL-2017-02, Rev. 0

A-31

E-225BC 001

Page in AOP Renewal 2, Revision A: 1-019

Permit: AOP 1.4 ICE (500HP and Greater)


NOC: AOP Table 1.4 Internal Combustion Engines (500HP and Greater)


Permit: E-225BC 001


NOC: E-225BC 001



Condition: 20% Opacity: Prohibits visible emissions

exceeding 20% opacity for more than 3 minutes in any

1 hour of an air contaminant from any emissions unit or



documented water.

Periodic Monitoring: Section 2.1, Tier 1.


Appendix A




Continuous

CDM: Reviewed maintenance records.

Comment: At the facility this is a

diesel engine powering an emergency

generator, known as 225B-DG-1. See

JCS PM/S 2C00013 and technical

procedure WESF-PRO-MN-51822.

Condition: 1,000 ppm SO2 @ 7% O2 on a dry basis.

Prohibits emission of a gas containing sulfur dioxide

from any emissions unit in excess of 1,000 ppm of a

dry basis, corrected to 7% oxygen for combustion

sources, and based on the average of any period of 60

consecutive minutes.

Periodic Monitoring: Section 2.7, Tier 1

Frequency: Not applicable.


App. A.


Required Records: 1. Amount and type of fuel burned.

2. Vendor documentation or fuel analysis once per year.


Continuous CDM: Reviewed fuel specification.

DOE/RL-2017-02, Rev. 0

A-32

E-225BG 001






Permit: E-225BG 001


NOC: E-225BG 001








documented water.

Periodic Monitoring: Method: Section 2.1, Tier 1.


Appendix A




Continuous

CDM: Confirmed visible emissions

checks all four quarters of 2016.

Comment: See JCS PM/S 2C30306

and technical procedure WESF-PRO-

MN-52634.



from any emissions unit in excess of 1,000 ppm of a

dry basis, corrected to 7% oxygen for combustion

sources, and based on the average of any period of 60




Appendix A






DOE/RL-2017-02, Rev. 0

A-33

E-4250-001, G-3






Permit: E-4250 001, G-3225BC 001


NOC: E-4250 001, G-3225BC 001








documented water.



Appendix A




Continuous

CDM: Emergency turbine generator

did not run during the CY.

Comment: Engine removed from

service 2006. Change Not Requiring

Permit Revision Notification

documentation submitted via DOE

Letter 15-ESQ-0101, dated August 24,

2015.



from any emissions unit in excess of 1,000 ppm of a dry

basis, corrected to 7% oxygen for combustion sources,

and based on the average of any period of 60




Appendix A




Calculation Model: Not applicable

Continuous

CDM: Emergency turbine generator

did not run during the CY.

Comment: Engine removed from

service 2006. Change Not Requiring

Permit Revision Notification

documentation submitted via DOE

Letter 15-ESQ-0101, dated August 24,

2015.

DOE/RL-2017-02, Rev. 0

A-34

E-WSCF 001






Permit: E-WSCF 001


NOC: E-WSCF 001








documented water.



Appendix A




Continuous

CDM: The emission unit did not

operate during the reporting period.

The unit was removed from service in

September 2014.


1,000 ppm S O2 @ 7% O2 on a dry basis.


from any emissions unit in excess of 1,000 ppm of a dry






Appendix A





Continuous

CDM: The emission unit did not


The unit was removed from service in

September 2014.

DOE/RL-2017-02, Rev. 0

A-35

J-CWC 001

Page in AOP Renewal 2, Revision A: 1-027 Page in AOP Renewal 2, Revision B: 1-049

Permit: DE00NWP-002, Revision 1

Issue Date: 06-29-06 Effective Date: 06-29-06 Date In AOP: 01-01-07 NOC: Central Waste Complex, Rev. 1



Condition: Visible emissions shall not exceed limits

specified in WAC 173-400-040(2).


survey/observation.

Frequency: Not applicable (assessment of cause of

visible emissions). Test Method: EPA Method 9 of 40 CFR 60, Appendix

A or Tier 3 Visible Emissions Survey of this AOP.

Test Frequency: Routine observation.

Required Records: Log book.


Continuous

CDM: Central Waste Complex

(CWC) performs routine surveillance

along with record keeping and

reporting of surveillance results.

Although not noted during the

reporting period, items reported would

include visible emissions.

Condition: VOC emissions shall not exceed 3.5 tons

per year.

Periodic Monitoring: Emission estimation (Condition

3.0 of this NOC).

Test Method: Material assessment, inventory, and

calculation as identified in the NOC Approval

Condition 3.0.

Test Frequency: Annually.

Required Records: Results of analyses.


Continuous

CDM: Confirmed by annual criteria &

toxic air pollutants (TAP) air

emissions reporting process.

Condition: All TAPs, as submitted in the Permittee's

Notice of Construction Application, shall be below

their respective ASIL.

Periodic Monitoring: Emission estimation (Condition

3.0 of this NOC)

Test Method: Material assessment, inventory, and

calculation as identified in the NOC Approval

Condition 3.0.




Continuous CDM: Confirmed by annual criteria &

TAPs air emissions reporting process.

Permit: AOP 1.6 Non-CUs <20 Pct Opacity & Fugitive


NOC: AOP Table 1.6 - Non Combustion Units (CU) with <20% Opacity Requirements



Condition: 1000 ppm S O2 @ 7% O2 on a dry basis:

Prohibits emission of a gas containing sulfur dioxide Continuous

CDM: Ecology has determined, based

on process knowledge, that these

DOE/RL-2017-02, Rev. 0

A-36



from any emissions unit in excess of 1000 ppm of a dry




Periodic Monitoring: Section 2.7, Tier 2, unless an

alternative SO2 emission limit is identified in Table 1.6.


Appendix A.




emission units do not emit significant

levels of SO2. The processes have not

been modified to increase SO2

emissions and no SO2 monitoring is

required.

Concrete Batch Plant


Permit: DE01NWP-003, Rev. 09-24-02


NOC: Revision to Concrete Batch Plant NOC



Condition: Total Emission Limits

A. Particulate Matter - Particulates from the bag-house

exhaust shall not exceed 0.01grains per dry standard

cubic foot, with no visible emissions. Engineering

calculations or vendor information that the bag-house,

when properly operated and maintained, will control

emissions to less than 0.01 grains per dry standard

cubic foot will be available at the facility. Periodic

measurements shall consist of visible emission

inspections per EPA Reference Method 22, Title 40

Part 60, Appendix A, July 1, 2000.

B. Fugitive Dust - Visible emissions from the sand and

aggregate transfer points, truck loading station, the

piles, or any other source shall not be allowed beyond

100 yards.

Periodic Monitoring: A. Recordkeeping

Test Method: B. EPA Method 22, Title 40 Part 60,

Appendix A, July 1, 2000.


Required Records: A. Calculations, vendor

information, baghouse maintenance logs, surveillance

checklists.

B. Visible emission survey results.


Continuous CDM: Records review and field

observations.

Condition: Fugitive Dust

All unpaved areas at the CBP and quarry will be

controlled by watering or chemical stabilization, or


observations.

DOE/RL-2017-02, Rev. 0

A-37



both. Means of chemical stabilization include the

application of petroleum resins (EPA 1998). A water

spray additive, (such as, "soil cement") will also be

considered for application on unpaved roads. Soil

cement has been previously used on the Hanford Site

with effective results.

Vehicle speed limit signs will be posted to control

speeds. Paved roads between the quarry and CBP will

be kept clear of heavy accumulations of dust and

debris. Front-end loaders will be used to pick up any

significant spill of sand or aggregate material on the

pave roads between the quarry and CBP. The sand and

aggregate stockpiles will be kept sprinkled with water

to prevent the movement of materials that may migrate

because of wind erosion. Transfer points at conveyors,

crushers, and screens will also be sprayed with water.

Periodic Monitoring: Recordkeeping



Required Records: Surveillance checklists.


Condition: Emission Control Monitors

Emission equipment control monitors shall include but

not be limited to the following:

A. Bag-house - None required if there are no visible

emissions per section 1.A. of the APPROVAL

CONDITIONS, and maintenance records indicate

proper maintenance practices and schedules.




Required Records: Surveillance checklists and bag

house maintenance logs.



observations.

Condition: General Conditions

A. Visible Emissions: No visible emissions shall be

allowed beyond 100 yards of source. During periods of

high winds, an assessment shall be made to suspend

operations or initiate a more comprehensive plant

watering scheme.

Periodic Monitoring: Visible Emission Surveys.



Required Records: Results of visible emission

surveys.



observations.

Permit: DE01NWP-003, Rev. 03-12-03


NOC: Revision to Concrete Batch Plant NOC to add Diesel Fuel Oil Boiler

DOE/RL-2017-02, Rev. 0

A-38



Condition: Diesel Fuel Oil Boiler

1. A 4.4 MMBtu diesel fuel oil boiler will be operated

2. The diesel fuel sulfur content will be less than or

equal to 0.05% S, by weight.

3. Operation of the boiler is limited to 2000 hours per

year.

4. Good combustion engineering practices shall be

followed, including adherence to the boiler

manufacturer's specification for operation,

maintenance, and combustion control.

5. Specific combustion feed gas ratios, including the

fuel-air ratio, monitoring, startup and shutdown

procedures shall be followed to maximize combustion

efficiency and minimize discharge of pollutants into

the atmosphere.




Required Records: 1. Manufacturer's specifications

for operation, maintenance, and combustion control.

2. Records of operating hours.

3. Records of fuel specification (sulfur content).

4. Records of good combustion engineering practices

and operating procedures.


Continuous

CDM: Records review. A diesel

boiler did not operate during reporting

period.

E-282ED 001



Permit: NWP-96-1 – A


NOC: Diesel Powered Emergency Fire Pump Generator



Condition: Engine E shall operate no more than 350

hours per year.

Periodic Monitoring: Recordkeeping.



Required Records: Maintain records showing all

hours of operation.


Continuous CDM: Recordkeeping.

Condition: Engine E shall burn only No. 2 fuel oil with

sulfur content no more than 0.05 weight percent.

Periodic Monitoring: Recordkeeping for compliance

with condition.



Continuous

CDM: Vendor documentation shows

fuel oil delivered contained no more

than 0.05 weight percent sulfur.

DOE/RL-2017-02, Rev. 0

A-39



Required Records: Vendor documentation of fuel

purchase from retail outlet (i.e., for use in the motor

vehicles, see 40 CFR 80), or fuel analysis once per year

showing <=0.05wt% sulfur.


Condition: NOx 75.5 pounds per hour NOx.

Periodic Monitoring: Recordkeeping & average fuel

consumption rate determination shall be performed at

least once per 12 months.

Test Method: EPA Method 7A of 40 CFR 60, App. A.


Required Records: 1. Monthly fuel burned (this

calculation is based on fuel added to supply tank).

2. Hours of operation logged.

Calculation Model: 2B.

Continuous

CDM: Recordkeeping and calculation

shows average fuel consumption is

below manufacturer's specification.

Condition: Opacity 10 %.

Periodic Monitoring: See Section 2.1, Tier 1.

Frequency: At least once per quarter, if operates.

Test Method: EPA Method 9 of 40 CFR 60, App. A.


Required Records: Results of visible emissions survey

or records of visual determination of the opacity.


Continuous CDM: EPA Method 9 opacity surveys

were conducted and recorded.

E-282WD 001


Permit: NWP-96-1 – B


NOC: Diesel Powered Emergency Fire Pump Generator



Condition: Engine W shall operate no more than 350

hours per year.




Required Records: Maintain records showing all

hours of operation.



Condition: Engine W shall burn only No. 2 fuel oil

with sulfur content no more than 0.05 weight percent.

Periodic Monitoring: Recordkeeping for compliance

with condition.



Continuous


fuel oil delivered contained no more

than 0.05% weight percent sulfur.

DOE/RL-2017-02, Rev. 0

A-40



Required Records: Vendor documentation of fuel

purchase from retail outlet (i.e. for use in motor

vehicles, see 40 CFR 80), or fuel analysis once per year

showing <=0.05 wt% sulfur.


Condition: NOx 42 pounds per hour.

Periodic Monitoring: Recordkeeping & average fuel

consumption rate determination shall be performed at

least once per 12 months.

Test Method: EPA Method 7A of 40 CFR 60, App. A.


Required Records: 1. Monthly fuel burned (this

calculation is based on fuel added to supply tank).

2. Hours of operation logged.

Calculation Model: 2B.

Continuous

CDM: Recordkeeping and

calculation shows average fuel

consumption is below manufacturer's

specification.

Condition: 10 % Opacity.

Periodic Monitoring: See Section 2.1, Tier 1

Frequency: At least once per quarter, if operates

Test Method: EPA Method 9 of 40 CFR 60, App. A.


Required Records: Results of visible emissions survey

or records of visual determination of the opacity.


Continuous CDM: EPA Method 9 Opacity

surveys were conducted and recorded.

E-3709A-001

Page in AOP Renewal 2, Revision A: 1-031 Page in AOP Renewal 2, Revision B: 1-057 Permit: DE02NWP-001


NOC: Emergency Diesel Generators




A. The activities described in the Notice of

Construction application will be permitted without

additional control technologies required, provided that

the total emissions from all activities will not result in

exceedance of WAC 173-460 ASILs.

B. A new Notice of Construction will be required, if

total emissions of toxic air pollutants exceed the Small

Quantity Emission Rates, unless dispersion modeling

demonstrates that emissions would continue to result in

concentrations less than the ASILs. Results of any such

dispersion modeling demonstrations/calculations will

be maintained on file and made available upon

inspection.

C. A new NOC also is required if total emissions of

Continuous

CDM: No changes in fuel usage or

significant operating hours occurred

in 2016 warranting additional

demonstration acceptable source

impact levels (ASIL) were not

exceeded.

DOE/RL-2017-02, Rev. 0

A-41



criteria pollutants would exceed the WAC 173-400-110

thresholds.

Periodic Monitoring: Analyze each proposed change

to determine if emissions would exceed an ASIL or

NSR threshold.





Condition: Monitoring and Recordkeeping

Specific records shall be kept on-site by the Permittee

and made available for inspection by Ecology upon

request. The records shall be organized in a readily

accessible manner and cover a minimum of the most

recent sixty (60) month period. The records to be kept

shall include the following:

A. Maintain records of the hours of operation.




Required Records: 1. Hours of operation

2. Fuel consumption.


Continuous

CDM: Hours of operation and fuel

consumption recorded monthly.

Records of operation and fuel

consumption are on file.

Condition: Emissions Control

SOx emissions will be controlled through use of #2

Diesel Fuel with sulfur content <0.5%.



Test Frequency: Per fuel shipment.

Required Records: Vendor documentation or fuel

analysis showing sulfur content <0.5%.


Continuous


#2 diesel fuel delivered contained less


Permit: AOP 1.6 CUs

Issue Date: 04-01-13 Effective Date:04-01-13 Obsolete Date: 07-31-16 Date In AOP: 04-01-13

NOC: AOP Table 1.6 - CUs








documented water.

Periodic Monitoring: Section 2.1, unless an alternative

visible emissions, opacity, or particulate matter

emission limit is identified in Table 1.6.


Continuous CDM: Tier 1 Visible Emissions

Surveys conducted and recorded.

DOE/RL-2017-02, Rev. 0

A-42



Appendix A.

Test Frequency: Not Applicable.



E-331-001



Permit: DE02NWP-001


















inspection.



thresholds.



NSR threshold.





Continuous

CDM: Reviewed PM results to verify

generators only ran during required

maintenance periods as permitted.

The number of hours operated were

below permit limits and total

emissions did not result in an


Hours operated during CY 2016 were

within permit limits.












Continuous

CDM: Fuel consumption and hours

of operation are recorded monthly.

Records are maintained for a period

of 5 years and are available upon

request.

DOE/RL-2017-02, Rev. 0

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Continuous

CDM: Reviewed fuel records and

purchase order records to verify only

ULS fuel (<0.0015 wt. %) was

purchased and consumed by

generators.

Permit: AOP 1.6CUs










documented water.





Appendix A.




Continuous

CDM: Reviewed Visible Emissions

Survey records for 2016 to verify

visible emissions did not exceed 20%

opacity. Visible emissions surveys

were performed as directed in AOP

Renewal 2, Attachment 1, Section

2.1, Tier 2.

E-325-001



Permit: DE02NWP-001








Continuous

CDM: Reviewed PM results to verify

generators only ran during required

maintenance periods as permitted.

DOE/RL-2017-02, Rev. 0

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inspection.



thresholds.



NSR threshold.





The number of hours operated were

below permit limits and total

emissions did not result in an


Hours operated during CY 2016 were

within permit limits.















Continuous

CDM: Fuel consumption and hours

of operation are recorded monthly.

Records are maintained for a period

of 5 years and are available upon

request.










Continuous

CDM: Reviewed fuel records and

purchase order records to verify only

ULS fuel (<0.0015 wt. %) was

purchased and consumed by

generators.

Permit: AOP 1.6 CUs



DOE/RL-2017-02, Rev. 0

A-45








documented water.





A.




Continuous

CDM: Reviewed Visible Emissions

Survey records for 2015 to verify

visible emissions did not exceed 20%

opacity. Visible emissions surveys

were performed as directed in AOP

Renewal 2, Attachment 1, Section

2.1, Tier 2.

P-2025E ETF




NOC: Effluent Treatment Facility



Condition: Visible emissions from the ETF stack

(Figure 1 of Order DE07NWP-003, Rev. 1) shall not

exceed five percent (5%).

Periodic Monitoring: Section 1, Tier 3.



Required Records: As required in AOP Attachment 2

for maintaining abatement control technology.


Continuous

CDM: Field interviews and work

documents.

Comment: No reported visible

emissions during reporting period.

Abatement equipment (i.e., HEPA

filters) intact and operational.

Condition: Volatile Organic Compound (VOC)

emissions from the ETF (Figure 1 of Order DE07NWP-

003) shall not exceed 0.55 gram per cubic meter (g/m3)

at standard conditions or 0.50 gram per minute (g/min).

Periodic Monitoring: Initial compliance verified by

EPA Method 18 of 40 CFR 60, Appendix A in 1996

(NOC-93-3).


Appendix A.

Test Frequency: Not applicable (initial test condition

for construction).

Required Records: Testing Results of 1996 EPA

Method.


Continuous CDM: Field interviews and work

documents.

DOE/RL-2017-02, Rev. 0

A-46




emissions from ETF operations shall not exceed 4,000

lb/yr. [WAC 173-400-110(5)(b)]

Periodic Monitoring: Material emission estimates.

Test Method: Calculations and record-keeping.

Test Frequency: Annual.

Required Records: Records of data and calculations

for the VOC emissions from ETF operations.



documents.

Condition: Particulate matter emissions shall not

exceed 1,500 lb/yr.

Periodic Monitoring: HEPA filtration of ETF stack

gases.

Test Method: See Required Records.


Required Records: Maintenance and operating records

of all filtration systems.



documents.

Condition: All TAPs in the NOC application and

identified in Table 1 of DE07NWP-003 Amendment 2

(9/27/2007) and Revision 1 (8/10/2010), shall not

exceed ASILs. [WAC 173-400-460-070]

Periodic Monitoring: Waste analysis records (see

Required Records).



Required Records: (1) Laboratory or waste analysis

results for TAPs identified in Table 1 of DE07NWP-

003 Amendment 2 (9/27/2007) and Revision 1

(8/10/2010), and (2) waste stream influent volumetric

records.



documents.

Condition: All newly identified TAPs shall not exceed

ASILs (with assessment of ASIL compliance). [WAC

173-460-070]

Periodic Monitoring: Assessment of ASIL compliance

(see Required Records).



Required Records: (1) Report laboratory or waste

analysis result of newly identified TAPs within 90 days

of completion of analysis, and (2) waste stream influent

volumetric records.


Continuous

CDM: Field interviews and work

documents.

Comment: No new TAPs identified.

DOE/RL-2017-02, Rev. 0

A-47

Permit: AOP 1.6 Non-CUs Less 20 Pct Opacity & No Fugitive


NOC: AOP Table 1.6 - Non CUs with <20% Opacity and No Fugitive Requirements



Condition: 1000 ppm SO2 @ 7% O2 on a dry basis.









App. A.




Continuous

CDM: Ecology has determined that

this emission unit does not emit

significant levels of SO2. The process

has not yet been modified to increase

SO2 emissions.

P-2706T 001


Permit: DE01NWP-002 Revision 1

Issue Date: 06-29-06 Effective Date: 06-29-06 Date In AOP: 01-01-07 NOC: T Plant Complex, Toxic Air Emissions



Condition: Visible Emissions

A. Visible emissions from any T-Plant Complex stack

will not exceed limits specified in WAC 173-400-

040(2).

Periodic Monitoring: Section 2, Tier 3.


A.

Test Frequency: Not applicable (when visible

emissions are observed).

Required Records: Maintenance records.


Continuous

CDM: HEPA filter ventilation used;

no visible emissions were observed

during the reporting period.

Condition: Emission Limits

A. VOC emissions will not exceed 3.5 tons per year.

B. All TAPs, as submitted in the Permittee's Notice of

Construction Application, will be below their respective

ASIL.

Periodic Monitoring: Analyze each proposed changed

to determine if emissions would exceed Emission

limits.

Test Method: Section 3.0 of the Approval Order

DE01NWP-002 Revision 1

Test Frequency: Section 3.0 of the Approval Order

Continuous

CDM: Confirmed by annual criteria

and TAPs air emissions reporting

process.

DOE/RL-2017-02, Rev. 0

A-48

DE01NWP-002 Revision 1





NOC: AOP Table 1.6 - Non-CUs with Less the 20 Percent Opacity Requirements and No Fugitive Requirements












Appendix A.




Continuous

CDM: Ecology determined this

emission unit does not emit


has not been modified to increase SO2

emissions.

P-296A042-001



Permit: NOC 94-07, Revision 3


NOC: AY and AZ Tank Farms Ventilation Upgrades, Amendment 1



Condition: Visible emissions at the stack shall not

exceed 5%. Should visible emissions be observed, the

excess emissions shall be discontinued by removing the

emission unit from service and Health notified

immediately.

Periodic Monitoring: Tier 3 requirements (Section

2.1, Visible Emission Surveys).

Test Method: Maintain abatement control technology

(AOP Attachment 2).


Required Records: Operation logs or records

Calculation Model: Not specified.

Continuous

CDM: Field interviews.

Comment: Abatement equipment

intact and operational, and no visible

emissions were reported during

reporting period.

Condition: The primary tank ventilation exhauster

system for the 241-AY and 241-AZ double-shell tank

farms shall not exceed daily average flow rates of 1,000

Continuous

CDM: Field interviews, work control

process, operations logs, and

Washington River Protection

DOE/RL-2017-02, Rev. 0

A-49



ft3/min (standard temperature and pressure).

Periodic Monitoring: Flow calculations based on

stack gas flow and temperature measurement.

Test Method: Flow calculations.

Test Frequency: Semi-annually.

Required Records: Calibrations and calculations of

exhauster system stack gas flow and temperature

measurement devices.

Calculation Model: None specified.

Solutions, LLC (WRPS) work

documents.

Condition: All toxic air pollutants (TAPs) shall be

below their respective ASIL or Screening Level of

Table 1 of the most updated NOC approval order.

Periodic Monitoring: T-BACT compliance (HEME,

HEPA, exhauster flow rate, etc.).

Test Method: T-BACT compliance.


Required Records: All monitoring and operations

records required for T-BACT compliance.

Calculation Model: Method 7B (Statement of Basis

3.1.7) or other approved methods.

Intermittent

CDM: Field interviews and industrial

hygiene (IH) monitoring and

database. Operated in accordance

with best available control technology

for toxics (T-BACT), WRPS

notification procedure, and

notification logbook.

Comment: During a review of

sampling information, it was

determined that dimethyl mercury

emissions were greater than the limits

in approval Order DE11NWP-001.

The limits had been based on

modeled values. Reported per WRPS

operating procedures.

Condition: Emissions of VOCs shall not exceed 0.175

lb/hr from the primary tank ventilation exhauster

system.

Periodic Monitoring: Calculations based on VOC

concentration readings and stack flow rate.

Test Method: Field instruments, which may include

Draeger Tubes.


Required Records: Supporting data and calculations.

Calculation Model: Method 4 (Statement of Basis


Continuous CDM: IH monitoring and database,

and WRPS work documents.

Permit: NOC 94-07, Amendment A


NOC: AY and AZ Tank Farms Ventilation Upgrades



Condition: Emissions of ammonia shall not exceed 2.5

lbs/hr from the primary tank ventilation exhauster

system.

Periodic Monitoring: Calculations based on ammonia

concentration readings and stack flow rates.

Test Method: Field instruments, which may include

Draeger Tubes.


Continuous CDM: IH monitoring and database


DOE/RL-2017-02, Rev. 0

A-50

Required Records: Supporting data and calculations.

Calculation Model: Method 5 (Statement of Basis
















Appendix A.




Continuous





emissions.

P-296W004 001


Permit: DE03NWP-002


NOC: Nonrad NOC for TAPs Emissions at the Waste Receiving and Processing Facility (WRAP) Facility



Condition: Total Emission Limits:

The processing and repackaging activities described in

the Notice of Construction application will be permitted

without requiring additional emission controls,

provided that the emissions form the stack, venting the

100 and 300 Series Waste Process Lines, the 200 and

400 Restricted Waste process Lines, the process area,

and the storage areas are maintained below the level

described in and meeting T-BACT (according to

WRAP Module 1 Best Available Control Technology

Assessment, WHC-SD-W026-TI-005, January 1993,

Westinghouse Hanford Company, Richland,

Washington).




Required Records: Documentation implementing T-

Continuous

CDM: Evaluation of emissions

potential from stored inventory using

criteria from WHC-SD-W026-TI-

005, Section 3.4, confirms total

emissions are below license limit,

compliance therewith.

DOE/RL-2017-02, Rev. 0

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BACT.


Condition: Total Emission Limits:

For toxic compounds not included in the T-BACT

analysis, the emission limits shall be the Small Quantity

Emission Rate (SQER). A modification submittal of a

Notice of Construction (NOC) application will be

required if the SQER limit would be exceeded for

compounds not addressed under the T-BACT

assessment. The calculation/measurement methods

described in section 4 of the NOC Approval Order

DE03NWP-002, or other method as approved by

Ecology, may be used to document compliance with the

SQER limit.

Periodic Monitoring: PID or other device capable of

detecting TAPs measurements.


Test Frequency: Once every 2 years.

Required Records: 1. IH Test Plan.

2. Results of measurements.


Continuous

CDM: Evaluation of emissions

potential from stored inventory

confirms toxic compounds not

included in T-BACT analysis were

below SQER limits.

Condition: An internal annual assessment of the

facility container tracking system, such as SWITS of

the data management system (DMS), shall be

conducted by the facility to document/ verify de

minimus emissions from the source. This assessment

will be maintained on file, made available for Ecology

inspector requests, and compiled into emission

estimates that will be reported annually beginning as

part of the Calendar Year 2003 nonradioactive

inventory of airborne emissions.

Periodic Monitoring: Recordkeeping; Comparison to

threshold.



Required Records: 1. Throughput records, SWITs

query evaluation if > 1,000 drums.

2. Nonradioactive air emissions inventory report

required by WAC 173-400-105.


Continuous

CDM: Fewer than 1,000 drums were

processed through WRAP during the

CY. Also, the emissions potential

from stored inventory was evaluated.

Condition: Emission Controls Monitors:

Source data from an Organic Vapor Analyzer using a

Photoionization detector (PID) with at least an 11.7eV

lamp, or other device capable of detecting TAPs, was

conducted by the facility in providing verification of de

minimus ( i.e., parts per million levels) fugitive

emissions in the drum storage and NDE/NDA areas.

The results of source test information, conducted on or

at the source(s) locations in lieu of downstream at the

stack, have been provided to the permit writer under

separate cover. This information had been determined

Continuous

CDM: Reasonable inquiry of

knowledgeable personnel confirmed

that IH monitoring has been

performed during the last 2 years.

DOE/RL-2017-02, Rev. 0

A-52



to satisfy the previous approval order condition for this

source in performing one-time monitoring to

demonstrate TAP emissions are below the estimates

provided in the NOC application and T-BACT analysis

for the drum storage and DNE/NDA areas. As such, no

additional sampling or monitoring will be required

under this approval order.

The facility will continue to perform at least once every

two years, and make available upon request or

inspection, results from any Industrial Hygiene program

measurements to further demonstrate compliance with

limits contained herein. The test plan for conducting

these measurements shall also be maintained on file and

made available upon request and/or inspection by

Ecology.

Periodic Monitoring: IH Program measurements as

specified in NOC, including alternative methods.


Test Frequency: Once every two years.

Required Records: Test plan.

Measurement results.


Permit: AOP 1.6 Non-CUs


NOC: AOP 1.6 Non-CUs with No Fugitive Emission or Dust Requirements








documented water.





Appendix A.




Continuous

CDM: WRAP maintains abatement

control technology (stack HEPA

filtration) as required in AOP

Attachment 2.








Continuous

CDM: Ecology determined this

emission unit does not emit

significant levels of SO2. Process has

not been modified to increase SO2

emissions.

DOE/RL-2017-02, Rev. 0

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Appendix A




P-WTP-001




NOC: Waste Treatment and Immobilization Plant (WTP)



Condition: 9.8 Construction Phase Fugitive Dust

Control Plan(s), prepared using EPA and Ecology

guidelines, shall be developed and implemented. The

plan(s) shall address fugitive dust control at the WTP

construction site adjacent to the Hanford 200 Area and

the Material Handling Facility established upon property

leased from the Port of Benton. A copy of this plan(s)

shall be maintained on-site at all times in a place known

to facility employees that are responsible for complying

with the requirements contained therein and shall be

retrievable by those employees at all times when

activities regulated by the documents are occurring.

These documents shall be made available to Ecology

upon request

Periodic Monitoring: Not applicable. The owner or

operator shall take reasonable precautions (such as pre-

job planning) to prevent fugitive dust from becoming

airborne.

Test Method: Construction Phase Fugitive Dust Control

Plan

Test Frequency: During construction or routine/ad hoc

dust suppression

Required Records: Fugitive Dust Control Plan and

records or actions taken to minimize fugitive dust.


Continuous CDM: Records Review.

Condition: 2.1 Opacity from each exhaust stack from

process facilities (Pretreatment, HLW and LAW) shall

not exceed 5%, other facility stacks shall not exceed 10

percent, over a 6 minute average as measured by EPA

Reference Method 9 of 40 CFR 60, Appendix A, or an

equivalent method approved in advance by Ecology. A

certified opacity reader shall read and record the opacity

Not

Applicable

CDM: Facilities were under

construction during the reporting

period; therefore, this condition did

not apply.

DOE/RL-2017-02, Rev. 0

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concurrent with any source testing.

Periodic Monitoring: For Pretreatment, HLW and

LAW, See Section 2.1, Tier 3.

Test Method: EPA Reference Method 9 of 40 CFR 60,

Appendix A.

Test Frequency: Initial test.

Required Records: Test Records.


Condition: 2.1 Opacity from each exhaust stack from

process facilities (Pretreatment, HLW and LAW) shall

not exceed 5%, other facility stacks shall not exceed 10

percent, over a 6 minute average as measured by EPA

Reference Method 9 of 40 CFR 60, Appendix A, or an

equivalent method approved in advance by Ecology. A

certified opacity reader shall read and record the opacity

concurrent with any source testing.

Periodic Monitoring: For Boilers, generators and fire

pumps, See Section 2.1, Tier 1.


Appendix A.

Test Frequency: At least once per calendar quarter.



Continuous CDM: Test Records.

Condition: Condition: 2.1 Opacity from each exhaust

stack from process facilities (Pretreatment, HLW and

LAW) shall not exceed 5%, other facility stacks shall

not exceed 10 percent, over a 6 minute average as

measured by EPA Reference Method 9 of 40 CFR 60,

Appendix A, or an equivalent method approved in

advance by Ecology. A certified opacity reader shall

read and record the opacity concurrent with any source

testing.

Periodic Monitoring: For other facility stacks, See

Section 2.1, Tier 3.


Appendix A.

Test Frequency: Initial test.



Not

Applicable

CDM: 'Other' Facilities were under



not apply.

Condition: 2.2; PSD-02-01, Cond. 2. All boilers,

generators and the diesel fire pump shall be fired on

Ultra-Low Sulfur Fuel (ULSF). ULSF means natural

gas, propane, or fuel oil with a sulfur content of

0.0015% or less. Compliance shall be monitored by

maintaining and submitting reports of fuel purchases.

Periodic Monitoring: Recordkeeping and Semiannual

report.



Required Records: Records of monthly fuel purchases

Continuous CDM: Monthly fuel purchase records

and certification of fuel sulfur content.

DOE/RL-2017-02, Rev. 0

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and use and an annual certification, from the fuel

distributor, stating the sulfur content of the fuel that was

supplied. (PSD-02-01 Cond 17.3)


Condition: 2.3; PSD-02-01, Cond. 8. The operation of

the six steam generating boilers shall not exceed an

annual aggregated fuel consumption limit of 13,400,000

gallons per year summed daily for the previous 365

days.

Periodic Monitoring: Recordkeeping and Semiannual

report of consumption over 12 months.


Test Frequency: Daily

Required Records: Maintain fuel purchase records

(PSD-02-01 Cond 17.3)


Not

Applicable

CDM: Boiler facilities were under



not apply

Condition: 2.4; PSD-02-01, Cond. 11, Cond 13. The

emergency generator shall not operate for more than 164

hours per year on a 12 month rolling summation

calculated once per month. Compliance shall be

monitored by installing and operating non-resettable

totalizers on each generator.



Test Frequency: Monthly.

Required Records: Records showing all hours of

operation.


Not

Applicable

CDM: Generator construction was not

complete during the reporting period;

therefore, this condition did not apply.

Condition: 2.4; PSD-02-01, Cond 13. The emergency

turbine generators shall not operate for more than 164

hours per year on a 12 month rolling summation

calculated once per month. Compliance shall be

monitored by installing and operating non-resettable

totalizers on each generator.



Test Frequency: Monthly.

Required Records: Records showing all hours of

operation.


Not

Applicable

CDM: Turbine generator construction

was not complete during the reporting


not apply.

Condition: 2.5; PSD-02-01, Cond 15. Each of the diesel

fire pumps shall not operate for more than 230 hours per

year on a 12 month rolling summation calculated once

per month. Compliance shall be monitored by installing

and operating a non-resettable totalizer on the fire pump.




Required Records: Monthly



DOE/RL-2017-02, Rev. 0

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Condition: 3.2 A new NOC will be required, if total

emissions of toxic air pollutants exceed the values

specified in the tables in Attachment 1 of the Notice of

Construction Application. These values shall be

confirmed by emission calculations, for indicator

constituents, derived from waste characterization data

obtained through implementation of the Ecology

approved Regulatory Data Objectives Supporting Tank

Waste Remediation System Privatization Project

(PNNL-12040). The mass feed rates for the indicator

constituents will be verified to be less than or equal to

the mass feed rates used in the Integrated Emissions

Baseline Report for the Hanford Tank Waste Treatment

and Immobilization Plant (24590-WTP-RPT-PO-03-

008, Rev. 0). Results of any such calculations will be

maintained on file and made available upon

inspection/request.



Test Frequency: At least once per calendar year.

Required Records: 1. Calculations of TAPs emissions

derived from waste feed characterization.

2. Calculations of ammonia emissions from LAW and

HLW.


Not

Applicable




not apply.

Condition: 2.3 A new NOC also is required if total

emissions of any criteria pollutants, derived from

calculations/monitoring, would exceed the estimates

listed under the Emissions section of this order.


Test Method: Not Specified.

Test Frequency: At least once per calendar year.

Required Records: Calculations of criteria pollutants.


Not

Applicable




not apply.

Condition: 4.1; PSD-02-01, Conditions 3.2, 4.2, 5.2,

6.2, and 7.2. Within 180-days of achieving the

optimized feed rate of simulant at which the facilities

will be operated, the permittee shall demonstrate initial

compliance through a performance demonstration

conducted per an Ecology approved Performance

Demonstration Plan. The permittee shall utilize the

Performance Demonstration Plan requirements

identified in the Dangerous Waste Portion of the

Resource Conservation and Recovery Act Permit for the

Treatment, Storage, and Disposal of Dangerous Waste

Hanford Tank Waste Treatment and Immobilization

Plant (DWP), condition III.10.H.5.f (LAW) and

III.10.J.5.f (HLW). Ecology shall be notified at least 30

days prior to the test and invited to participate in the test

activities at least one week prior to testing.




Not

Applicable




not apply.

DOE/RL-2017-02, Rev. 0

A-57



Required Records: 1. Notification Documentation.

2. Performance Demonstration Plan.


Condition: 4.2 Testing per the initial compliance testing

identified in 3.1 shall be conducted in accordance with

the frequency identified in the DWP, condition

III.10.I.1.h (LAW) and II.10.K.1.h (HLW).

Periodic Monitoring: Recordkeeping, measurements,

and emission calculations.

Test Method: As stated in DWP conditions III.10.I.1.h

(LAW) and III.10.K.1.h (HLW).

Test Frequency: At startup and at least once every 5

years thereafter.

Required Records: Test records.


Not

Applicable




not apply.

Condition: 4.5; PSD-02-01 Conditions 3-7, 9-10, 12,

14. Within 180 days of initial startup, boiler, emergency

generator, and process facility source testing shall be

conducted according to the following methods, unless an

alternate method has been proposed in writing by the

permittee and approved by Ecology in writing in

advance of the testing.

Tested Pollutant Reference Method (40 CFR §60

Appendix A unless otherwise

defined), as of 7/1/2000

Carbon Monoxide Method 10

Nitrogen Oxide Method 7E

Volatile Organic

Compounds Method 18

Sulfur Dioxide Method 6C

Visible Emissions Method 9

Particulate Matter

40 CFR 60 Appendix A Method

5; 40 CFR 51 Appendix M

Method 201 or 201A for the

front half analysis and 40 CFR

51 Appendix M Method 202 for

the back half



Test Method: As stated in condition.

Test Frequency: Initial startup and every 5 years

thereafter.



Not

Applicable

CDM: Boiler and generator

construction was not completed during

the reporting period; therefore, this

condition did not apply.

Condition: 4.6 During the boiler source testing, a

direct-reading measurement device for carbon monoxide

with a minimum measurement accuracy of five percent

or less shall take readings according to methods

proposed by the permittee and approved by Ecology in

Not

Applicable

CDM: Boiler construction was not

completed during the reporting period;

therefore, this condition did not apply.

DOE/RL-2017-02, Rev. 0

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writing in advance of the testing. The direct-reading

instrument shall be calibrated for future use, using the

results of the source testing.



Test Method: Portable emissions analyzer calibrated

during most recent source test.

Test Frequency: Initial startup.

Required Records: Logs of boiler tune-ups and

significant boiler maintenance activities will be

maintained.


Condition: 5.0 Emissions from boilers and generators

shall be monitored for CO, and Oxygen by means of a

portable emissions analyzer (direct-reading

measurement device) at initial startup and after routinely

scheduled maintenance activities and burner/control

adjustments such as fuel/air metering ratio control and

oxygen trim control.



Test Method: Portable emissions analyzer calibrated

during most recent source test.

Test Frequency: Initial startup and after routinely

scheduled maintenance activities and burner/control

adjustments such as fuel/air metering ratio control and

oxygen trim control.

Required Records: Logs of boiler tune-ups and

significant boiler maintenance activities will be

maintained.


Not

Applicable

CDM: Boiler and generator

construction was not completed during

the reporting period; therefore, this

condition did not apply.

Permit: PSD-02-01, Amend 3


NOC: PSD-02-01, Amendment 3



Condition: Condition 2; Ultra-low sulfur fuel <=

0.0015% by wt. for Steam Generating Boilers, Diesel

Fire Pumps, and Backup Emergency Generators


Test Method: Recordkeeping.

Test Frequency: Semiannually.

Required Records: Fuel Purchase records and a written

statement in each semiannual report of the type of fuel

used.


Continuous CDM: Fuel Purchase Records.

Condition: Condition 3; PM10 <= 0.02 g/dscf, 24- hour

average or 0.456 lb/hr, 24-hour average for the

Pretreatment Plant.

Not

Applicable CDM: Facilities were under


DOE/RL-2017-02, Rev. 0

A-59




Test Method: 40 CFR 60 Appendix A, Method 5, 40

CFR 51 Appendix M Method 201 or 201A for the front

half analysis and 40 CFR 51 Appendix M Method 202

for the back half.

Test Frequency: 5 years.

Required Records: Calculations based on testing

results and hours of operation.



not apply.

Condition: Condition 5; PM10 <= 0.36 lb/hr at 21% O2,

24-hr average for the LAW Vitrification Plant.





for the back half.

Test Frequency: 5 Years.




Not

Applicable




not apply.

Condition: Condition 4; NOx <= 477 ppm dry per

volume at 21% O2, 24 hr average or 200.1 lb/day

averaged over 30 consecutive days for the LAW

Vitrification Plant.


Test Method: 40 CFR 60 Appendix A, Method 7E

Test Frequency: Continuous; using a Continuous

Emission Monitor (CEM) for NOx and a flow meter.

Required Records: Testing results CEM for NOx and

flow meter, and CEM performance evaluation.


Not

Applicable




not apply.

Condition: Condition 7; PM10 <= 0.135 lb/hr at 21%

O2, when averaged over 24 consecutive hours for the

HLW Vitrification Plant.





for the back half.

Test Frequency: 5 years




Not

Applicable




not apply.

Condition: Condition 6; NOx 352 ppmdv at 21% O2,

over a 24 hr. average 24 hr average or 23.3 lb/day

averaged over 30 consecutive days for the HLW

Vitrification Plant.


Test Method: 40 CFR 60 Appendix A, Method 7E;

CEM.

Not

Applicable




not apply.

DOE/RL-2017-02, Rev. 0

A-60



Test Frequency: CEM Continuous

Required Records: Testing results, CEM for NOx and

flow meter, and CEM performance evaluation.


Condition: Condition 8; Maximum aggregated fuel

consumption for steam boilers 1, 2, 3, 4, 5, and 6 shall

not exceed 13,400,000 gallons per year.


Test Method: Verification of fuel purchases.

Test Frequency: Semiannual

Required Records: Fuel purchase records and a written

statement in each semiannual report of the total fuel

consumption over the previous 12 months.


Not

Applicable




not apply.

Condition: Condition 10; PM or PM10; <= 0.02

lb/MMBtu or 1.0 lb/hr averaged over 24 consecutive

hours for all steam boilers.





for the back half.


Required Records: Testing results and hours of

operation.


Not

Applicable




not apply.

Condition: Condition 9; NOx <= 0.09 lb/MMBtu at 3%

02 or 4.52 lb/hr averaged over 24 consecutive hours for

Steam Boilers.


Test Method: Method 7E of 40 CFR 60 Appendix A.

Test Frequency: 5 Years




Not

Applicable




not apply.

Condition: Conditions 11 and 13; Each Type 1

emergency generator and turbine generators shall not

exceed 164 hours per year when averaged over 12

consecutive months, calculated once per month.


Test Method: Installing and operating a non-resettable

totalizer on each generator.

Test Frequency: Semiannual.

Required Records: Hours of operation reported in the

semiannual report for the previous 6 months and the

summation of hours operated over the previous 12

months.


Not

Applicable




not apply.

Condition: Condition 12; NOx from the Type I

generator <= 391.1 lb/day (each), when averaged over

24 consecutive hours.

Not

Applicable CDM: Facilities were under


DOE/RL-2017-02, Rev. 0

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not apply.

Condition: PSD-02-01, Condition 14; Emissions of

NOx from the emergency turbine generators shall not

exceed 69.8 pounds per day (each), when averaged over

24 consecutive hours and 164 hours per year averaged

over 12 consecutive months.



Test Frequency: 5 years




Not

Applicable




not apply.

Condition: Condition 15; Hours of operation for each

pump shall not exceed 230 hours per year averaged over

12 consecutive months.


Test Method: Installing and operating a non-resettable

totalizer on each generator.

Test Frequency: Semiannually.

Required Records: Written statement in each

semiannual report of hours of operation.



Integrated Disposal Facility



Permit: DE05NWP-004


NOC: Operation of the Integrated Disposal Facility (IDF)



Condition: EMISSION LIMITS FOR WASTE

COVERING OPERATIONS

During waste covering operations, aggregate will be

used to cover the waste package at the IDF. Dust

control for covering the waste package will consist of

watering and/or chemical wetting agents. Waste

covering operations will be curtailed during high winds

in accordance with abnormal operating procedures for

high winds. Prior to long periods of inactivity, an

assessment shall be made to implement more

comprehensive dust control methods, such as chemical

stabilization, on disturbed areas. A reassessment will be

Not

Applicable

CDM: Waste has not been introduced

to the IDF. The facility is operating

under caretaker status.

DOE/RL-2017-02, Rev. 0

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made once per week.




Required Records: Daily activity reports, logs, pre-job

reviews, management assessments, surveillances or

similar documents.


Condition: EMISSION LIMITS FOR TRAVEL ON

UNPAVED ROADS

Surface treatment for dust control will consist of

watering and/or chemical stabilization. Minimize

vehicle use on unpaved road. Perform regular

maintenance of road surface. Reduce vehicle speed

limit on unpaved roads.






similar documents.


Continuous


Comment: This is an inactive facility

with access controls. Water was

applied, when needed, to unpaved

roads and disturbed soil for dust

control during the reporting period.

Vehicle traffic on unpaved roads is

kept to a minimum and speed limits

are reduced. Conditions were

assessed weekly. Main access gate is

closed and locked.

Condition: EMISSION LIMITS FOR AGGREGATE

COVER COMPACTING

A water truck will be provided, and operated as needed

to spray water for compaction. Waste covering

operations will be curtailed during high winds in

accordance with abnormal operating procedures for

high winds. Prior to long periods of inactivity an

assessment shall be made to implement more

comprehensive dust control methods, such as chemical

stabilization, on disturbed areas. A reassessment will be

made once per week.






similar documents.


Not

Applicable



under caretaker status.

Condition: EMISSION LIMITS FOR AGGREGATE

STORAGE PILE

Watering will be utilized to minimize wind erosion

during storage pile operation. Storage pile work will be

curtailed during high winds in accordance with

abnormal operating procedures for high winds. Prior to

long periods of inactivity an assessment shall be made

to implement more comprehensive dust control

methods, such as chemical stabilization, on disturbed

areas. A reassessment will be made once per week.

Minimize vehicle traffic. Minimize areas of

Continuous



under caretaker status. The storage

pile has not been disturbed and is

periodically assessed to verify that

additional dust control measures are

not needed.

Comment: Water was applied, when

needed, to prevent fugitive dust from

becoming airborne, to minimize dust

DOE/RL-2017-02, Rev. 0

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disturbance.






similar documents.


generation, and to minimize wind

erosion during the reporting period.

Condition: FUGITIVE EMISSIONS

The permittee shall take reasonable precautions to

prevent the release of air contaminants from any

emissions unit engaging in materials handling,

construction, demolition, or any other operation that is

a source of fugitive emissions.


reasonable control measures.



Required Records: None listed.


Continuous


Comment: Water was applied, when

needed, to prevent fugitive dust from




Condition: FUGITIVE DUST

Requires reasonable precautions be taken to prevent

fugitive dust from becoming airborne and to minimize

dust generation.


reasonable control measures.



Required Records: None listed.


Continuous


Comment: Water was applied as

required to prevent fugitive dust from














documented water.





Appendix A.


Continuous



under care taker status.

DOE/RL-2017-02, Rev. 0

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Appendix A




Continuous



significant levels of SO2. The

process has not been modified to

increase S O2 emissions.

Comment: Waste has not been

introduced to the IDF. The facility is

operating under care taker status.

Ventilation Systems for 241-AN and 241-AW Tank Farms

The following emission units are summarized here: P-296A044-001 | P-296A045-001 | P-296A046-001 |

P-296A047-001.


Page in AOP Renewal 2, Revision B: 1-084Permit: DE05NWP-001 R1


NOC: Non-Radioactive Air Emissions NOC for Operation of New Ventilation Systems in AN and AW Tank Farms




Visible emissions from each stack shall not exceed five

(5) percent.

Periodic Monitoring: Compliance and monitoring

shall be met by Tier 3 Visible Emissions Survey

requirements of the Hanford AOP, Section 2.1. Should

visible emissions be observed which are not solely

attributable to water condensation, compliance shall be

met by performing an opacity determination utilizing

40 CFR 60, Appendix A, Method 9, providing that such

determination shall not place the visible emission

observer in hazard greater than that identified for the

general worker.

Test Method: 40 CFR 60, Appendix A, Method 9, as

applicable.

Test Frequency: None specified (as needed for

monitoring and compliance).

Required Records: Visible emission surveys records

in which a visible emission was observed, which are

not solely attributable to water condensation; and

Method 9 results if conducted.


Continuous




emissions were reported during CY

2016.

DOE/RL-2017-02, Rev. 0

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Condition: EMISSION LIMITS

Primary tank ventilation exhauster systems shall not

exceed 4,000 ft3/min (at standard temperature and

pressure).

Periodic Monitoring: Compliance and monitoring of

this condition shall be demonstrated by stack gas flow

and temperature measurement.




Required Records: (1) Records of exhauster system

stack flow rates and temperature records.

(2) Records of calibration of stack gas flow rate and

temperature measurement devices.


Continuous

CDM: Field interviews, work control

process, operations logs, and WRPS

work documents.

Condition: REPORTING

Visible emission surveys conducted and a report of the

maintenance conducted to maintain the subject exhaust

system's T-BACT operations shall be submitted to

Ecology within 30 days of completion of the survey

with an assessment of the cause of visible emissions.

Periodic Monitoring: Compliance of this condition is

met by submitting to Ecology within thirty (30) days of

completion of the survey with an assessment of the

cause of visible emissions.



Required Records: Visible emission surveys

conducted and a report of the maintenance.


Continuous




emissions reported during CY 2016.


Identification of any TAP not previously identified

within the Notice of Construction Application or

Supplement emissions estimates shall be submitted to

Ecology within ninety (90) days of completion of

laboratory analyses which verify emissions of that toxic

air pollutant from the project.


met by submitting to Ecology within ninety (90) days

of completion of laboratory analyses which verify

emissions of that toxic air pollutant from the project.



Required Records: Laboratory analysis.


Continuous

CDM: Tank Waste Information

Network System (TWINS), IH

monitoring and sample analysis

database. WRPS notification

procedure and notification logbook.

DOE/RL-2017-02, Rev. 0

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Results of emission assessments conducted shall be

submitted to Ecology within 90 days of completion of

the assessment.


met by submitting to Ecology within ninety (90) days

of completion of such assessment.



Required Records: Emission assessment results.


Continuous CDM: Field interviews.

Permit: DE05NWP-001, Amend A


NOC: Non-Radioactive Air Emissions NOC for Operation of New Ventilation Systems in AN and AW Tank Farms,

Amendment 1




Emissions of ammonia shall not exceed 2.9 pounds per

hour (3.63E-01 gram/second) from the primary tank

ventilation exhauster system. The term 'either exhauster

system' shall mean each individual primary tank

ventilation exhauster system within the 241-AN and

241-AW Tank Farms, where an exhauster system may

be operated in single-train or dual-train modes.

Periodic Monitoring: Conduct of ammonia

concentration readings and apply these concentration

readings with contemporaneous stack flow rate and

temperatures to determine instantaneous mass release

rate of ammonia.

Test Method: Ammonia sampling and analysis will be

in accord with approved alternative sampling

procedures including the use of Draeger tubes to

measure stack gas concentration of ammonia providing

such devices are spanned to appropriately measure the

stack gas ammonia concentration. Stack flow rate and

temperature will be applied with the ammonia stack gas

concentration to report ammonia emission in terms of

grams per second.

Test Frequency: In order to assess baseline emission

concentrations from each exhauster system, emission

levels of ammonia will be assessed between 12 and 24

hours after initiation of exhauster operation (single train

or duel train). Ammonia stack concentrations shall be

sampled a minimum of three times.

Baseline Assessments

Baseline assessments shall be conducted within ninety

(90) days of commencement of operations. Should dual

exhauster train operation not be required by the

Continuous

CDM: IH monitoring and sample

analysis plans and database, and

WRPS work documents.

DOE/RL-2017-02, Rev. 0

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Permittee during this ninety (90) day period, assessment

of dual train operation emissions shall be conducted on

the first occasion of dual train operation which is

anticipated to exceed 24 hours duration.

Bi-Annual Emission Assessment

In order to maintain reasonable assurance of continued

compliance with emission limitations from these

exhauster systems, bi-annual assessment of ammonia

stack emissions will be conducted beginning the second

calendar year following completion of single train

exhauster operation assessment under Section 3.1 of

NOC approval order DE05NWP-001. A minimum of

three samples shall be used to assess these emissions.

Required Records: Results of emission assessments,

baseline and bi-annual emission monitoring results,

supporting data and calculations to demonstrate

compliance with ammonia limits.



All TAPs, as shown in Table 2 of Approval Order

DE05NWP-001, Rev 1 and Amd A, shall be below their

respective ASIL or Screening Level of Table 1 of

Approval Order DE05NWP-001 Rev 1.

Periodic Monitoring: Compliance and monitoring shall

be met by operating the exhauster systems only when in

accord with T-BACT emission controls for the project.

T-BACT for this project has been determined to be

operation of the primary tank ventilation exhauster

systems not exceeding 4,000 cubic feet per minute with

moisture de-entrainment, pre-heater, and HEPA

filtration in service in the treatment train.




Required Records: Documentation and record-keeping

of T-BACT compliance of emission control found for

this project (operation of the primary tank ventilation

exhauster system not exceeding 4,000 ft3/min with

moisture de-entrainment, pre-heater, and HEPA

filtration in service in the treatment train).


Continuous

CDM: Field interviews, Site Wide

Industrial Hygiene Database

(SWIHD), operation logs and WRPS

work documents.

Comment: Operated in accordance

with T-BACT. WRPS notification

procedure and notification logbook.









Continuous




DOE/RL-2017-02, Rev. 0

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Appendix A.





increase SO2 emissions.

200 Area Single Shell Tank Categorical Waste Retrieval

The following emission units are summarized here: P-296P043-001 | P-296P044-001 | P-296P045-001 | P 296P047-

001 | P-296P048-001 | P-296P107-001.



Permit: DE05NWP-002 R2


NOC: Approval of Criteria and Toxics Air Emissions NOC Application for Operations of Waste Retrieval Systems

in SST Farms as supplemented with C Farm Exhauster Operation




Visible emissions from each tank ventilation exhauster

stack or aggregated exhauster stack shall not exceed

five percent.


shall be met by Tier 3 Visible Emissions Survey

requirements of the Hanford AOP, Section 2.1. Should

visible emissions be observed which are not solely

attributable to water condensation, compliance shall be

met by performing an opacity determination utilizing

40 CFR 60, Appendix A, Method 9, providing that such

determination shall not place the visible emission

observer in hazard greater than that identified for the

general worker.

Test Method: 40 CFR 60, Appendix A, Method 9, as

applicable.

Test Frequency: None Specified (as needed for

monitoring and compliance)

Required Records: Visible emission surveys records

in which a visible emission was observed, which are

not solely attributable to water condensation; and

Method 9 results if conducted.


Continuous

CDM: Field interviews and

operations logs.




2016.

DOE/RL-2017-02, Rev. 0

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Tank ventilation exhauster systems for the 241-C SST

farm 100 series tanks (241-C-101 through 241-C-112)

shall not exceed cumulative flow rates of 7,000 ft3/min

(at standard temperature and pressure) for three

exhausters individually limited to 1,000 ft3/min, 3,000

ft3/min, and 3,000 ft3/min, respectively (at standard

temperature and pressure).












Continuous

CDM: Field interviews, Work

Management System, operations logs,



SST ventilation exhauster systems for the retrieval of

wastes other than those of the 241-C tank farm 100

series tanks shall not exceed 1,000 ft3/min (at standard

temperature and pressure).












Continuous


Comment: No activities were

conducted requiring the use of this

condition during the reporting period.


All TAPs, as submitted in the permittee's NOC

Applications, shall be below their respective ASIL or

Screening Level of Table 1 in Approval Order

DE05NWP-002, Rev. 2.


with this condition shall be met by:

(1) Operating the exhauster systems only when in

accord with T-BACT emission controls found for this

project (operation of the tank ventilation exhauster

systems with moisture de-entrainment, pre-heater, and

HEPA filtration in service in the treatment train).

(2) Development and implementation of a sampling and

analysis plan (SAP) for each tank retrieval. For each

retrieval, the SAP shall address the emission of a

minimum of the three TAPs with the higher potential

ambient concentration relative to their ASILs of WAC

Continuous

CDM: Field interviews and IH

monitoring and sample analysis plans

and database. Operated in accordance

with T-BACT.

DOE/RL-2017-02, Rev. 0

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173-460-150 and WAC-173- 460-160 or relative to

their Screening Level of Table 1 of the Approval Order

DE05NWP-002, Rev 2. The TAPs addressed in the

SAP shall be identified from Table 2 of the Approval

Order DE05NWP-002, Rev 2, and based upon best

engineering judgment and most current tank content

data. Analytical methods for the analysis shall be the

United States EPA, OSHA, or NIOSH approved, or by

approved equivalent method.




Required Records: (1) All monitoring and operations

records required to operate and maintain the emission

control equipment which implements T-BACT as

required in Periodic Monitoring above.

(2) SAPs developed for compliance demonstration as

described in Periodic Monitoring above.

(3) Laboratory analysis result summaries of any

samples undertaken after the effective date of the

Approval Order DE05NWP-002, Rev 2, from SST tank

farm tank headspaces or SST ventilation system

exhaust which are examined for organic species or

other TAPs.



Visible emission surveys, conducted pursuant to

Compliance Demonstration requirement 1.3.2, per

NOC approval DE05NPW-002, and a report of the

maintenance conducted to maintain the subject exhaust

system's T-BACT operations.

Periodic Monitoring: The reporting condition shall be

submitted to Ecology within thirty (30) days of

completion of the survey with an assessment of the

cause of visible emissions.



Required Records: Visible emission surveys

conducted and a report of the maintenance.


Continuous





2016.



within the Notice of Construction Application or

Supplement emissions estimates as defined in Table 2,

per NOC approval DE05NWP-002R1, shall be

submitted to Ecology within ninety (90) days of

completion of laboratory analyses which verify



submitted to Ecology within ninety (90) days of

completion of laboratory analyses which verify


Continuous

CDM: TWINS, IH monitoring and

sample analysis database.

Comment: New TAPs were

identified 2016 for 296-P-47.

Nitrosodiethylamine and

Nitrosopyrrolidine. Environmental

Operational Notification TOC-ENV-

NOT-2016-4245.

DOE/RL-2017-02, Rev. 0

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Required Records: Laboratory analysis.



An annual schedule (Federal fiscal year basis) of

anticipated operations and installations of exhauster

systems.


submitted by November first of each year.



Required Records: Annual schedule.


Continuous

CDM: Field interviews, WRPS work

documents and WRPS notification

procedure.

Condition: OPERATIONAL NOTICE

Notification shall be made at least ten (10) days prior to

initial operation of any exhauster system covered by the

ORDER DE05NWP-002 when installed to ventilate a

tank not previously actively ventilated under this

ORDER.




Required Records: Not applicable.


Continuous

CDM: Field interviews, WRPS work

documents and WRPS notification

procedure.

Comment: POR 126 and POR 127

operational notification, TOC-ENV-

NOT-2016-4271 R0 and R1, were

submitted in CY 2016.

Permit: AOP 1.6 Non-CUs <20 Pct Opacity & Fugitive


NOC: AOP Table 1.6 - Non-CUs with Less than 20 Percent Opacity and Fugitive Requirements



Condition: 1000 ppm SO2 @ 7% O2 on a dry basis:









Appendix A.




Continuous





increase SO2 emissions.

DOE/RL-2017-02, Rev. 0

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E-85 Fuel Station



Permit: DE06NWP-001


NOC: E-85 Alternative Fuel




A. Emission of Volatile Organic Compounds shall not

exceed 40 tons per year.

B. All TAPs, as submitted in the Permittee's NOC

Application, shall be below their respective ASIL.

Periodic Monitoring: Record fuel storage tank loading

of the E-85 fuel and verify NOC Condition 1.6

requirements for each load received.

Test Method: Compliance of the approval condition

shall be demonstrated by installation of BACT and T-

BACT emission controls including (1) submerged or

bottom fill pipe such that the pipe inlet is fully

submerged when the fluid level in the tank is six inches

(15.2 cm) or greater, and (2) fitting to vapor balance

gasoline vapors with the delivery transport tank.

Test Frequency: Not applicable (maintenance records).

Required Records: Retention of fuel storage tank

loading records detailed in NOC (DE06NWP-001)

Approval Condition 1.6.













documented water.





Appendix A.





DOE/RL-2017-02, Rev. 0

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Appendix A




Continuous





emissions.

600 Area Diffuse/Fugitive – HAMMER

Page in AOP Renewal 2, Revision A: 1-068 Page in AOP Renewal 2, Revision B: 1-095 Permit: DE07NWP-001


NOC: HAMMER Training Facility



Condition: Visible emissions from training operations

shall not exceed twenty (20) percent opacity.

[WAC 173-400-040(2)]


Test Method: Section 2.1, Tier 2 and/or EPA Method

9 of 40 CFR 60, Appendix A.

Test Frequency: Once per year, if visible emissions

are observed (see Periodic Monitoring).

Required Records: Records of Tier 2 visible emission

event surveys including EPA Method 9 results.


Continuous CDM: The emission unit did not


Condition: Fugitive emissions from training operations

shall be minimized. [WAC 173-400-040(4)(a)]

Periodic Monitoring: Use of operating procedures: (1)

keep containers closed when not in use, and (2) ensure

proper handling and storage to minimize unintentional

losses.



Required Records: Records of (1) fugitive release

control procedure training, and (2) events which detail

non-compliance with fugitive release control

procedures or unintentional releases and response to

such events.




DOE/RL-2017-02, Rev. 0

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Condition: Particulate matter emissions from training

materials shall not exceed 1,500 pounds per year

(lb/yr). [WAC 173-400-1 10(5)(b)]

Periodic Monitoring: Material record-keeping.



Required Records: Material balance records which

detail materials receipt and disposal, with a summary

assessment of losses calculated each calendar quarter.





emissions from training materials shall not exceed

4,000 lb/yr.

[WAC 173-400-1 10(5)(b)]

Periodic Monitoring: Material record-keeping.




detail materials receipt and disposal, with a summary

assessment of losses calculated each calendar quarter.




Permit: DE07NWP-001, Amendment 1


NOC: HAMMER Training Facility



Condition: Emissions of all TAPs, as identified in

Table 1 of NOC Order DE07NWP-001 (4/19/2007) and

Amendment 1 (7/31/2007), or newly identified, shall be

below their respective SQERs. [WAC 173-460-150]

Periodic Monitoring: Materials record-keeping.




detail materials receipt and disposal with a summary

assessment of losses, calculated each calendar quarter.

Emission of any TAP exceeding SQERs detailed in

Table 1 of Order DE07NWP-001 shall be reported to

Ecology in accord with WAC 173-400-107.


within Order DE07NWP-001, shall be submitted to

Ecology within 90 days of initiation of use in training

with an estimate of annual emissions.




DOE/RL-2017-02, Rev. 0

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NOC: AOP Table 1.6 - Non CUs with <20% Opacity and No Fugitive Requirements












App. A.






181B/182B Emergency Diesel Engines

181B/182B Emergency Diesel Engines consist of the following emission units: E-181B-001 | E-182B-001 |

E-182B-002


No active NOC approvals in the AOP for this certification period.

WTP Construction Heaters & Dehumidifiers


Permit: DE07NWP-004


NOC: WTP Construction Site Heaters and Dehumidifiers




1. Total Suspended Particulates emission shall not

exceed 1.25 tons per year. [WAC 173-400-110(5)(b)].

2. PM-10 particulate emission shall not exceed 0.75

tons per year [WAC 173-400-110(5)(b)].

Periodic Monitoring: Compliance shall be monitored

by:

(1) Emission of visible emissions of no more than five

percent opacity during normal operation of diesel-fired

Continuous CDM: No visible emissions were

observed during the reporting period.

DOE/RL-2017-02, Rev. 0

A-76



heaters.

(2) Diesel-fired heaters exceeding five percent opacity

shall be removed from operation until maintenance of

the unit results in visible emissions in compliance (no

more than 5%).

(3) Compliance with visible emissions survey

requirements of Approval Condition 3.0 of the

Approval Order DE07NWP-004. Visible emissions

(VE) from diesel-fired heaters in normal operation (not

start-up or shutdown) will be monitored through a VE

survey described herein. A minimum representation of

20 percent of active diesel-fired heaters under this

ORDER shall be subject to VE survey. If VEs from one

of these emission units are observed for more than 10

consecutive minutes, an attempt to identify the cause(s)

of the VEs will be made and those results recorded. The

recorded entry also will identify any corrective actions

taken and the likely frequency of a future reoccurrence.

If the event is likely to be re-occurring, and cannot be

demonstrated to consist of water vapor, a determination

of opacity will be made using EPA Method 9 of 40

CFR 60, Appendix A. A VE survey shall be conducted

weekly for a period of three months. If weekly VE

surveys do not demonstrate emissions in excess of

Approval Condition 1.3.1, the VE survey frequency

will reduce to once every three months for a period of

six months. After nine months of no excess visible

emissions, visible emission surveys will be performed

for any diesel-fired heater subject to this ORDER only

when visible emissions are observed during normal

operation.

Test Method: VE Surveys and/or EPA Method 9 of 40

CFR 60, Appendix A (if needed).

Test Frequency: Not specified.

Required Records: (1) VE Surveys and/or EPA

Method 9 of 40 CFR 60, Appendix A, results.

(2) Maintenance records for any diesel-fired heater

removed from service.



Sulfur Oxides (SOx) emission shall not exceed 2.0 tons

per year [WAC 173-400-110(5)(b)].


by:

(1) Combustion of distillate fuel oil No. 2 with a sulfur

content no greater than 0.0015 wt percent (15 ppm) for

diesel heaters.

(2) Combustion of no greater than 933,100 gallons of

distillate fuel oil per year, based upon a daily rolling

summation.

Test Method: Record-keeping.

Test Frequency: Per daily rolling summation and/or

fuel shipment.

Continuous CDM: Fuel use records and

emissions calculations.

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Required Records: Fuel analysis data and

consumption rates, including supporting data and

calculations.



(1) Nitrogen Oxides (NOx) emission shall not exceed

16.2 tons per year [WAC 173-400-110(2)(a)].

(2) Total Volatile Organic Compounds emission shall

not exceed 2.0 tons per year [WAC 173-400-110(5)(b)].

(3) Carbon Monoxide emissions shall not exceed 5.0

tons per year [WAC 173-400-110(5)(b)].

(4) Toxic Air Pollutant (TAP) emissions as specified in

Table 1 of Approval Order DE07NWP-004 [WAC 173-

460-070].


by:

(1) Operation in compliance with BACT/T-BACT

(implementation of vendor-recommended combustion

and maintenance practices).

(2) Fuel Limitation: (a) combustion of no greater than

933,100 gallons of distillate fuel oil per year, based

upon a daily rolling summation, and (b) combustion of

no greater than 1,109,500 gallons of propane per year,

based upon a daily rolling summation.

Test Method: Record-keeping.

Test Frequency: Per daily rolling summation and/or

fuel shipment.

Required Records: Fuel analysis data and

consumption rates, including supporting data and

calculation.


Continuous CDM: Fuel use records and

emissions calculations.

E-339A-001




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241-AP, 241-SY, and 241-AY/AZ Ventilation

The following emission units are summarized here: P-296A048-001 | P-296A049-001 | P-296A050-001 |

P-296A051-001 | P-296S026-001 | P-296S027-001


















Appendix A.




Not

Applicable

CDM: Document review and field

interviews.

Comment: Not applicable for SY.

Emission unit not installed for 241-

SY ventilation. For 241-AP and 241-

AY/AZ, the requirements in the AOP

have been superseded by more recent

modifications (Revisions 2, 3, 4,

Modification A, and administrative

changes).

Lagoon Treatment System


Permit: DE12NWP-001


NOC: 200 West Evaporative Sewage Lagoon, Project L-691



Condition: All TAPs, as submitted in the Permittee's

Notice of Construction Application, shall be below their

respective ASIL.

Periodic Monitoring: Annual collection and analysis

of wastewater between the wastewater truck discharge

point and the truck unloading chamber.

Test Method: Surrogate wastewater sample analyzed

with an EPA approved method in 40CFR Part 136.




Continuous CDM: Sampling records.

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Appendix A.




Continuous

CDM: Per Section 2.7, Tier 2,

Ecology has determined, based on

process knowledge, that this emission

units does not emit significant levels

of SO2. The processes have not been

modified to increase SO2 emissions

and no SO2 monitoring is required.

211ED/212ED Diesel Generator



Single-Shell Tank Direct Fired Water Heaters




Hanford Site Asbestos Landfill


Permit: AOP 1.7 - Asbestos Landfill


NOC: AOP Table 1.7 Miscellaneous Emission Units - Asbestos Landfill


Permit: Hanford Site Asbestos Landfill


NOC: Hanford Site Asbestos Landfill

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Condition: 40 CFR 61.151(a)

1. Either discharge no visible emissions to the outside

air from an inactive waste disposal site subject to this

paragraph: or

2. Cover the asbestos-containing waste material with at

least 15 centimeters (6 inches) of compacted

nonasbestos-containing material, and grow and

maintain a cover of vegetation on the area adequate to

prevent exposure of the asbestos-containing waste

material. In desert areas where vegetation would be

difficult to maintain, at least 8 additional centimeters (3

inches) of well-graded, nonasbestos crushed rock may

be placed on top of the final cover instead of vegetation

and maintained to prevent emissions: or

3. Cover asbestos-containing waste with at least 60

centimeter of compacted nonasbestos-containing

material, and maintain to prevent exposure.




Required Records: Calculation Model: Not applicable.

Continuous

CDM: Recordkeeping and inquiry of

responsible personnel.

Comment: Waste was originally

covered with at least 60 centimeters

of soil. The landfill is periodically

visually inspected to verify cover

material integrity and to ensure cover

material is maintained to prevent

exposure.

Condition: 40 CFR 61.151(d)

Notify in writing at least 45 days prior to excavation. If

construction will begin on a date other than the one in

the original notice, notice of the new date must be

provided at least 10 working days in advance.

1. Notice shall contain starting and completion dates.

2. Notice shall contain reason for disturbing the waste.

3. Notice shall contain procedures to be used to control

emissions.

4. Notice shall contain a location for any temporary

storage site and the final disposal site.





Continuous

CDM: Inquiry of responsible

personnel.

Comment: Requirement was not

triggered.


Permittee is considered to be in compliance if no

complaints are forwarded or generated by Ecology.





Continuous

CDM: No requests for complaint

investigations were received from

Ecology during CY 2016 for issues

related to these standards (as required

by AOP Attachment 1, Section 2.2).




Periodic Monitoring: Monitor per Section 2.7, Tier 2.


Continuous





by AOP Attachment 1, Section 2.2).

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G-6290 (600 Area Gasoline Distribution)


Permit: AOP 1.7 - Gas Distribution


NOC: AOP Table 1.7 Miscellaneous Emission Units - Gas Distribution


Permit: 600 Area Gas Distribution


NOC: 600 Area Gas Distribution



Condition: WAC 173-491-040(4)(b)

All gasoline storage tanks shall be equipped with

submerged or bottom fill lines and fittings to vapor

balance gasoline vapors with the delivery transport

tank.






Continuous


knowledgeable personnel confirmed

no facility modifications.

Comment: Drop tubes part of

original installation.

Condition: WAC 173-491-040(4)(d)

The owner or operator shall not permit the loading of

gasoline into a storage tank equipped with vapor

balance fittings from a transport tank equipped with

vapor balance fittings unless the vapor balance system

is attached to the transport tank and operated

satisfactorily.






Continuous

CDM: Recordkeeping and contract

with fuel provider.

Comment: The vapor balance system

is attached to the transport tank and

operated properly when loading

gasoline into a storage tank with

vapor balance fittings.

Condition: WAC 173-491-040(6)(d)

(i) The owner or operator of a gasoline transport tank or

vapor collection system shall maintain records of all

certification tests and repairs for at least two years after

the test or repair is completed.

(ii) The records of certification tests required by this

section shall, as a minimum, contain:


DOE/RL-2017-02, Rev. 0

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(A) The transport tank identification number;

(B) The initial test pressure and the time of the reading;

(C) The final test pressure and the time of the reading;

(D) The initial test vacuum and the time of the reading;

(E) The final test vacuum and the time of the reading;

(F) At the top of each report page the company name,

date, and location of the tests on that page; and

(G) Name and title of the person conducting the test.

(iii) The owner or operator of a gasoline transport tank

shall annually certify that the transport tank passed the

required tests.

(iv) Copies of all records required under this section

shall immediately be made available to the department,

upon written request, at any reasonable time.

Periodic Monitoring: Annually













Continuous





by AOP Attachment 1 Section 2.2).


Ecology has determined, based on process knowledge,

that these emission units do not emit significant levels

of SO2.




Required Records: The Permittee shall annually

certify that the processes have not been modified to

increase SO2 emissions and no SO2 monitoring is

required.


Continuous

CDM: This emission unit is not a

significant source of SO2 emissions.

It has not been modified to increase

SO2.

6120 Tent (200 East)


Permit: NSPS Subpart IIII


NOC: Standards of Performance for Stationary Compression Ignition Internal Combustion Engines


Permit: 6120 Tent (200 East)


NOC: 6120 Tent (200 East)

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Condition: (1) Non-methane hydrocarbons (NMHC)

and nitrogen oxides (NOX) emission limit of 7.5

g/KW-hr

(2) Carbon monoxide (CO) emission limit of 6.6 g/KW-

hr.

(3) Particulate matter emission limit of 0.40 g/KW-hr

Compliance Requirement: Compliance will be

determined by operating and maintaining the engine in

accordance with the manufacturer's recommendations

or instructions.

Required Records: (1) Manufacturer's maintenance or

operation manual.

(2) Documentation of maintenance performed.


Continuous

CDM: Interviews with field

personnel and records review indicate

emission related components have

been maintained per manufacturer’s

recommendations.

Comment: Ecology determined this

unit to be in intermittent compliance

in inspection close-out letter 17-

NWP-010 because all operation and

maintenance manual-identified items

were either not performed or not

recorded. The emission-related

components of this unit were

operated and maintained in

accordance with the applicable

regulation, i.e., 40 CFR 60 Subpart

IIII

Condition: Use of fuel per 40 CFR 60.4207 (b)

Periodic Monitoring: Compliance will be

demonstrated by use of fuel containing no greater than

0.0015 weight percent sulfur (15 parts per million by

weight).






Continuous




100K Water Treatment Plant






Permit: 100K Water Treatment Plant


NOC: 100K Water Treatment Plant





g/KW-hr




Intermittent

CDM: Work package review and

interviews with field personnel.

Comment: This unit was determined

to be in intermittent compliance by

Ecology in inspection close-out letter

17-NWP-026 due to all operation and

DOE/RL-2017-02, Rev. 0

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or instructions.


operation manual.




not performed or recorded.





weight).







385 Building






Permit: 385 Building


NOC: 385 Building





g/KW-hr





or instructions.


operation manual.



Continuous

CDM: Maintenance Records.

Comment: The emission unit did not


DOE/RL-2017-02, Rev. 0

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weight).






Continuous

CDM: Vendor fuel certification.

Comment: The emission unit did not


219H Tent and MO-414 (200E)






Permit: 219H Tent and MO-414 (200 east)


NOC: 219H Tent and MO-414 (200 east)




and nitrogen oxides (NOX) emission limit of 7.5 g/KW-

hr


hr.





or instructions.


operation manual.



Continuous



emission-related components have


recommendations. Comment: Ecology determined this







components of this unit were

operated and maintained in



IIII.





weight).




Continuous




DOE/RL-2017-02, Rev. 0

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North of MO-414 (200E) 1 of 2






Permit: North of MO-414 (200 East) 1 of 2


NOC: North of MO-414 (200 East) 1 of 2





hr.


hr.

(3) Particulate matter emission limit of 0.30 g/KW-hr.




or instructions.


operation manual.



Continuous





recommendations.








components of this unit are operated

and maintained in accordance with

the applicable regulation, i.e., 40 CFR

60 Subpart IIII.





weight).






Continuous




DOE/RL-2017-02, Rev. 0

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North of MO-414 (200E) 2 of 2






Permit: North of MO-414 (200 East) 2 of 2


NOC: North of MO-414 (200 East) 2 of 2





hr.


hr.





or instructions.


operation manual.



Continuous





recommendations.










the applicable regulation, i.e., 40 CFR

60 Subpart IIII.





weight).






Continuous




DOE/RL-2017-02, Rev. 0

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WTP MHF South-40 Laydown Critical Equipment Storage






Permit: WTP MHF South-40 Lay Down Critical Equipment


NOC: WTP MHF South-40 Laydown Critical Equipment Storage





g/KW-hr


hr





or instructions.


operation manual



Continuous

CDM: Review of the 40 CFR 60,

Subpart IIII emissions standards

determined that Bechtel National,

Inc.’s (BNI) existing engine

maintenance program is consistent

with EPA’s standards in 40 CFR

60.4211(g) although the AOP

contains language that could be

interpreted differently than 40 CFR

60.4211(g) as it is currently written.

This conclusion is based on EPA’s

allowance that engine operators may

demonstrate compliance by keeping a

maintenance plan and records

documenting that the engine is

maintained and operated in a manner

consistent with good air pollution

control practices. BNI-WTP has

developed and implements an engine

maintenance program consistent with

good air pollution control practices.





weight).






Continuous CDM: Records review of fuel

invoices.

DOE/RL-2017-02, Rev. 0

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2720EA


Permit: NSPS Subpart JJJJ


NOC: Standards of Performance for Stationary Spark Ignition Internal Combustion Engines


Permit: 2720EA


NOC: 2720EA



Condition: (1) Hydrocarbons (HC) and nitrogen oxides

(NOx) emission limit of 13.4 g/kW-hr.

(2) Carbon monoxide (CO) emission limit of 519 g/kW-

hr.




or instructions


operation manual



Intermittent



that some elements of the

manufactures maintenance schedule

was not performed in 2016 due to

minimal run time. The engine ran a

total of 21 hours in 2016.

Rattle Snake Barricade


Permit: NSPS Subpart JJJJ


NOC: Standards of Performance for Stationary Spark Ignition Internal Combustion Engines


Permit: Rattle Snake Barricade


NOC: Rattle Snake Barricade



Condition: (1) Hydrocarbons (HC) and nitrogen oxides

(NOx) emission limit of 8 g/kW-hr.

(2) Carbon monoxide (CO) emission limit of 610 g/kW-

hr.




or instructions


operation manual

Intermittent






minimal run time. The engine ran

about 13 hours in 2016.

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222-SE



AOP conditions replaced by DE15NWP-001 that was effective September 1, 2015. DE15NWP-001 has not been

incorporated into the AOP.

242-A


Permit: National Emission Standards for Hazardous Air Pollutants (NESHAP) Subpart ZZZZ


NOC: National Emissions Standards for Hazardous Air Pollutants for Stationary Reciprocating Internal Combustion

Engines


Permit: 242-A


NOC: 242-A



Condition: (1) Operate and Maintain the engine in

accordance with Manufacturer's recommendations or

instructions.

(2) Change oil and filter every 500 hours of operation

or annually, whichever comes first.

(3) Inspect air cleaner every 1,000 hours of operation or

annually whichever comes first.

(4) Inspect all hoses and belts every 500 hours of

operation or annually, whichever comes first, and

replace as necessary.

Compliance Requirement: (1) Compliance will be



or instructions; or a written maintenance plan in a

manner consistent with good air pollution control

practice for minimizing emissions.

(2) Compliance will be demonstrated by installation

and operation of non-resettable hour meter.


operation manual.

(2) Hour meter readings



Intermittent

CDM: Field interviews and WRPS

work documents.

COMMENT: Ecology determined

this unit to be in intermittent

compliance in inspection close-out

letter 17-NWP-039 because all

operation and maintenance manual-

identified items were either not

performed or not recorded. The

emission related components of this

unit are operated and maintained in



ZZZZ.

DOE/RL-2017-02, Rev. 0

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234-5Z


Permit: NESHAP Subpart ZZZZ



Engines


Permit: 234-5Z


NOC: 234-5Z





instructions.

(2) Change oil and filter every 500 hours of operation










or instructions; or a written maintenance plan in a

manner consistent with good air pollution control

practice for minimizing emissions.

(2) Compliance will be demonstrated by installation

and operation of non-resettable hour meter.


operation manual.




Continuous

CDM: Quarterly Inspections

performed by Site Staff. Annual

Inspection and Maintenance

performed by Factory Certified

Representative. All inspections and

maintenance verified and recorded.

Permit: AOP Table 1.5 Engines


NOC: Table 1.2 General Standards for Maximum Emissions (SO2 requirements)







and based on the average of any period of 60 consecutive

minutes.


Test Method: Not specified. EPA Method 6 or 6C of 40

Continuous

CDM: Reviewed fuel records to

verify ULS fuel (<0.0015 wt. %) was

purchased and consumed.

DOE/RL-2017-02, Rev. 0

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CFR 60, Appendix A.




400 Area





Engines


Permit: 400 Area


NOC: 400 Area





instructions.

(2) Change oil and filter every 500 hours of operation or

annually, whichever comes first.








accordance with the manufacturer's recommendations or

instructions; or a written maintenance plan in a manner

consistent with good air pollution control practice for

minimizing emissions.

(2) Compliance will be demonstrated by installation and

operation of non-resettable hour meter.


operation manual.




Intermittent

CDM: Work package review and

interviews with Field personnel

Comment: This unit was determined

to be in intermittent compliance by

Ecology in inspection close-out letter

17-NWP-026 due to all operation and


not performed or recorded.




DOE/RL-2017-02, Rev. 0

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minutes.



CFR 60, Appendix A.




Continuous




600 Area Fire Station (Building (609A)





Engines


Permit: 600 Area Fire Station (Building 609A)


NOC: 600 Area Fire Station (Building 609A)





instructions.

















operation manual.




Intermittent


personnel and records review.

Comment: Oil and filter change not

performed during 2016. Engine only

operated 18.5 hours.

DOE/RL-2017-02, Rev. 0

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2721E





Engines


Permit: 2721E


NOC: 2721E





instructions.

















operation manual.




Intermittent






minimal run time. The engine ran a

total of 46 hours in 2016.

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Yakima Barricade





Engines


Permit: Yakima Barricade


NOC: Yakima Barricade





instructions.

















operation manual.




Intermittent






minimal run time. The engine ran

about13 hours in 2016.

DOE/RL-2017-02, Rev. 0

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282-B





Engines


Permit: 282-B


NOC: 282-B





instructions.

















operation manual.




Continuous

CDM: Review of preventive

maintenance records.

Comment: See JCS PM/S 2C-01982

and JCS Work Package 2C-16-02062.











minutes.



Continuous




DOE/RL-2017-02, Rev. 0

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CFR 60, Appendix A.




282-BA





Engines


Permit: 282-BA


NOC: 282-BA





instructions.

















operation manual.




Continuous

CDM: Interviews with Facility

personnel revealed that the deep well

pump system (powered by the diesel

engine) was removed from service in

2015. Ecology was notified of the

permanent shutdown of this emission

unit per DOE-RL letter to Ecology,

16-ESQ-0051, dated March 7, 2016.

DOE/RL-2017-02, Rev. 0

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minutes.



CFR 60, Appendix A.




Continuous




225BC





Engines


Permit: 225BC


NOC: 225BC





instructions.

















Continuous

CDM: Engine removed from

service in 2015 and physically

removed from the location on

2/2/2016.

Comment: Unit's last PM was in

June 2015, JCS 2C-15-02232 and

subsequently removed from service

in 2015. Email DOE/RL (Faust) to

Ecology (Gent) dated August 3,

2016, and DOE letter 17-ESQ-0063,

dated May 8, 2017, notified Ecology

of removal of 225BC engine.

DOE/RL-2017-02, Rev. 0

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operation manual.




TEDF Pump Station 2 (225E)





Engines


Permit: Treated Effluent Disposal Facility (TEDF) Pump Station 2 (225E)


NOC: TEDF Pump Station 2 (225E)





instructions.






operation or annually, whichever comes first, and replace

as necessary.










operation manual.




Intermittent


work documents.

Comment: A permit modification is

being pursued to allow usage of a

facility specific operations and

maintenance manual as allowed by

40 CFR 63 Subpart ZZZZ.

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WTP MHF South-40 Laydown Entry Gate (Light Tower)





Engines


Permit: WTP MHF South-40 Laydown Entry Gate (Light Tower)


NOC: WTP MHF South-40 Laydown Entry Gate (Light Tower)





instructions.

(2) Change oil and filter every 1,000 hours of operation or






as necessary.




instructions.




operation manual.




Continuous


Subpart ZZZZ emissions standards

determined that BNI’s existing

engine maintenance program is

consistent with EPA’s standards in

40 CFR 63.6625(e) although the

AOP contains language that could

be interpreted differently than 40

CFR 63.6625(e) as it is currently

written. This conclusion is based on

EPA’s allowance that engine

operators may either maintain

engines according to manufacturer’s

emission-related instructions or may

develop their own maintenance

program consistent with good air

pollution control practices. BNI-

WTP has developed and

implemented an engine maintenance

program consistent with good air

pollution control practices.







Prohibits emission of a gas containing sulfur dioxide from

any emissions unit in excess of 1000 ppm of a dry basis,

corrected to 7% oxygen for combustion sources, and

based on the average of any period of 60 consecutive

minutes.



CFR 60, Appendix A.



invoices.

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WTP MHF North-10 Laydown Area (Light Tower) 1 of 2


Permit: NESHAP Subpart ZZZZ (WTP)



Engines


Permit: WTP MHF N-10 Laydown Area (Light Tower) 1 of 2


NOC: WTP MHF North-10 Laydown Area (Light Tower) 1 of 2





instructions.







as necessary.




instructions.




operation manual.





DOE/RL-2017-02, Rev. 0

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minutes.



CFR 60, Appendix A.





invoices.

WTP MHF North-10 Laydown Area (Light Tower) 2 of 2





Engines


Permit: WTP MHF North-10 Laydown Area (Light Tower) 2 of 2


NOC: WTP MHF North-10 Laydown Area (Light Tower) 2 of 2





instructions.







as necessary.




instructions.




operation manual.



DOE/RL-2017-02, Rev. 0

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minutes.



CFR 60, Appendix A.





invoices.

WTP MHF South-40 Laydown Yard East X-Ray Tent





Engines


Permit: WTP MHF South-40 Laydown Yard East X-Ray Tent


NOC: WTP MHF South-40 Laydown Yard East X-Ray Tent





instructions.







as necessary.



DOE/RL-2017-02, Rev. 0

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instructions.




operation manual.














minutes.



CFR 60, Appendix A.





invoices.

WTP Construction Site Pretreatment Tower Crane





Engines


Permit: WTP Construction Site Pretreatment Tower Crane


NOC: WTP Construction Site Pretreatment Tower Crane





instructions.

Intermittent

CDM: 16-ECD-0044, Hanford Site

AOP 00-05-006 Deviation Report

of Discharge Points 1.4.61 and

DOE/RL-2017-02, Rev. 0

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as necessary.




instructions.




operation manual.




1.4.62 (September 22, 2016)

identified self-reported deviation

for the WTP Pretreatment Tower

Crane Stationary Engine.











minutes.



CFR 60, Appendix A.





invoices.

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WTP Construction Site High-Level Waste Tower Crane





Engines


Permit: WTP Construction Site High-Level Waste Tower Crane


NOC: WTP Construction Site High-Level Waste Tower Crane





instructions.







as necessary.




instructions.




operation manual.




Intermittent

CDM: 16-ECD-0044, Hanford Site

AOP 00-05-006 Deviation Report

of Discharge Points 1.4.61 and

1.4.62 (September 22, 2016)

identified self-reported deviation

for the WTP HLW Tower Crane

Stationary Engine.











minutes.



CFR 60, Appendix A.



invoices.

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WTP Construction Site Building T-14





Engines


Permit: WTP Construction Site Building T-14


NOC: WTP Construction Site Building T-14





instructions.

(2) Change oil and filter every 1,000 hours of operation










instructions.




operation manual.




Continuous


Subpart ZZZZ emissions standards

determined that BNI’s existing

engine maintenance program is

consistent with EPA’s standards in

40 CFR 63.6625(e) although the

AOP contains language that could

be interpreted differently than 40

CFR 63.6625(e) as it is currently

written. This conclusion is based

on EPA’s allowance that engine

operators may either maintain

engines according to

manufacturer’s emission-related

instructions or may develop their

own maintenance program


control practices. BNI-WTP has

developed and implemented an

engine maintenance program


control practices.




DOE/RL-2017-02, Rev. 0

A-108








minutes.



CFR 60, Appendix A.





invoices.

Light Towers Waste Transfer Corridor East




NOC: Light Towers Waste Transfer Corridor East



Condition: (1) Non-methane hydrocarbons (NMHC) and

nitrogen oxides (NOX) emission limit of 7.5 g/KW-hr.

(2) Carbon monoxide (CO) emission limit of 6.6 g/KW-hr.




accordance with the manufacturer’s recommendations or

instructions OR

(2) If the engine and control device is not installed,

configured, operated, or maintained according to the

manufacturer’s emission-related written instructions, or

the emission-related settings are changed in a way that is

not permitted by the manufacturer, then:

• Keep a maintenance plan and records of conducted

maintenance to demonstrate compliance and must, to the

extent practicable, maintain and operate the engines in a

manner consistent with good air pollution control practices

for minimizing emissions.

Required Records: (1) Manufacturer’s maintenance or

operation manual.


(3) Maintenance plan, as appropriate.


Intermittent

CDM: Review of surveillance

records and maintenance records.

Comment: Maintenance plan used

in lieu of manufacturer’s

instructions. Ecology determined











IIII.

Condition: Use of fuel per 40 CFR 60.4207 (b).



percent sulfur (15 parts per million by weight.)


Continuous

CDM: Reviewed fuel records.

Comment: Reviewed fuel records

to verify ULSF was purchased and

consumed

DOE/RL-2017-02, Rev. 0

A-109







Condition: Maintain no more than eight Waste Transfer

Corridor East engines.

Periodic Monitoring: Inventory of engines used to power

the Waste Transfer Corridor East light plants. At a

minimum; record the current and past engines in the

Corridor with the date the engine was located in the

Corridor and the date it was removed from the Corridor.



Required Records: Engine inventory.


Continuous CDM: Review of surveillance

records

Light Towers Waste Transfer Corridor West


Permit: Light Towers Waste Transfer Corridor West


NOC: Light Towers Waste Transfer Corridor West










instructions OR












operation manual.




Intermittent
















IIII.


Periodic Monitoring: Compliance will be demonstrated Continuous



DOE/RL-2017-02, Rev. 0

A-110









consumed.

Condition: Maintain no more than eight Waste Transfer

Corridor East engines.


the Waste Transfer Corridor East light plants. At a

minimum; record the current and past engines in the

Corridor with the date the engine was located in the

Corridor and the date it was removed from the Corridor.



Required Records: Engine inventory



records.

Light Towers C Farm Trailer Area


Permit: Light Towers C Farm Trailer Area


NOC: Light Towers C Farm Trailer Area










instructions OR












operation manual.




Intermittent
















IIII.

DOE/RL-2017-02, Rev. 0

A-111












Continuous




consumed

Condition: Maintain no more than eight C Farm Trailer

Area engines.


the C Farm Trailer Area light plants. At a minimum;

record the current and past engines in the trailer area with

the date the engine was located in the trailer area and the

date it was removed from the trailer area.






records

Light Towers C Farm


Permit: Light Towers C Farm


NOC: Light Towers C Farm










instructions OR












operation manual.

Intermittent
















IIII.

DOE/RL-2017-02, Rev. 0

A-112













Continuous




consumed

Condition: Maintain no more than eight C Farm engines.


the C Farm light plants. At a minimum; record the current

and past engines in the trailer area with the date the engine

was located in the C Farm and the date it was removed

from the C Farm.






records

AY/AZ Farm DMI-LT Light Tower


Permit: AY/AZ Farm DMI-LT Light Tower


NOC: AY/AZ Farm DMI-LT Light Tower










instructions OR












operation manual.

Intermittent


records and maintenance records,

maintenance plan. Comment:

Ecology determined this unit to be

in intermittent compliance in

inspection close-out letter 17-NWP-

039 because all operation and

maintenance manual-identified

items were either not performed or

not recorded. The emission related



the applicable regulation, i.e., 40

CFR 60 Subpart IIII.

DOE/RL-2017-02, Rev. 0

A-113













Continuous


verify ULSF was purchased and

consumed.

C and AN Farm Compressors

Page in AOP Renewal 2, Revision B: 1-165 Permit: C and AN Farm Compressors


NOC: C and AN Farm Compressors










instructions OR



manufacturer’s emission- related written instructions, or









operation manual.




Not

Applicable

CDM: N/A

Comment: No stationary engine

compressors present at C or AN

Tank Farms during reporting

period.








Not

Applicable

CDM: N/A




period.

DOE/RL-2017-02, Rev. 0

A-114



Condition: Maintain no more than two C and AN Farm

Compressor engines.


the C and AN Farm compressors. At a minimum; record

the current and past engines used for the compressors with

the date the engine was located in the C or AN Farm and

the date it was removed from the C or AN Farm.



Required Records: Engine inventory.


Not

Applicable

CDM: N/A




period.

Light Towers AN Farm


Permit: Light Towers AN Farm


NOC: Light Towers AN Farm










instructions OR














operation manual.




Intermittent
















IIII.

DOE/RL-2017-02, Rev. 0

A-115












Continuous

CDM: Reviewed fuel records



consumed

Condition: Maintain no more than eight AN Farm

engines.


the AN Farm light plants. At a minimum; record the

current and past engines in the trailer area with the date

the engine was located in the AN Farm and the date it was

removed from the AN Farm.






records.

DOE/RL-2017-02, Rev. 0

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DOE/RL-2017-02 Rev. 0

B-i

APPENDIX B



DOE/RL-2017-02 Rev. 0

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DOE/RL-2017-02 Rev. 0

B-iii

CONTENTS

Emission Units are listed in Order by Air Operating Permit (AOP) Page Number

Single Shell Breather Vents moved into Table 1 (see page B-351)

W-296P045-001 .............................................................................................................................. 1

P-296P022-001 ............................................................................................................................... 1

P-296SY-001................................................................................................................................... 2

W-296P043-001 .............................................................................................................................. 3

W-296P044-001 .............................................................................................................................. 3

S-296S025-001 ............................................................................................................................... 3

S-6266-001 ...................................................................................................................................... 4

S-6266-002 ...................................................................................................................................... 4

P-296A042-001 ............................................................................................................................... 4

P-204AR-001 .................................................................................................................................. 6

P-242A-002 ..................................................................................................................................... 6

P-242AL44-001 .............................................................................................................................. 9

P-242AL43-001 .............................................................................................................................. 9

P-242AL42-001 ............................................................................................................................ 10

P-296A028-001 ............................................................................................................................. 11

P-242S-001 ................................................................................................................................... 11

P-296A020-001 ............................................................................................................................. 12

EP-318-01-S .................................................................................................................................. 13

P-296W004 001 ............................................................................................................................ 13

P-296AP-001................................................................................................................................. 21

P-296A041-001 ............................................................................................................................. 22

P-296A043-001 ............................................................................................................................. 23

P-296A018-001 ............................................................................................................................. 24

P-296A019-001 ............................................................................................................................. 25

P-296AN-001 ................................................................................................................................ 25

P-296A030-001 ............................................................................................................................. 26

S-296S021-001 ............................................................................................................................. 27

P-2025E ETF ................................................................................................................................ 27

P-213W-001 .................................................................................................................................. 28

P-291T001-001 ............................................................................................................................. 29

P-296T007-001 ............................................................................................................................. 40

P-291S001-001 ............................................................................................................................. 42

P-296S016-001 ............................................................................................................................. 44

P-296B010-001 ............................................................................................................................. 44

EP-325-01-S 325 Building Radiological Processing Laboratory ................................................. 50

P-291A001-001 ............................................................................................................................. 51

P-296A010-001 ............................................................................................................................. 53

P-437MN&ST-001 ....................................................................................................................... 54

P-FFTFRESB-001......................................................................................................................... 55

P-FFTFHTTR-001 ........................................................................................................................ 55

P-FFTFCBEX-001 ........................................................................................................................ 55

Sodium Storage Facility ................................................................................................................ 56

DOE/RL-2017-02 Rev. 0

B-iv

P-437-002 ...................................................................................................................................... 56

P-296B001-001 ............................................................................................................................. 57

EP-331-01-V Life Sciences Laboratory I ..................................................................................... 61

P-296H212 001 ........................................................................................................................... 108

S-296S023-001 ........................................................................................................................... 109

J-CWC 001.................................................................................................................................. 110

300 Area Emissions .................................................................................................................... 118

Sitewide Type-1, 2, 3 .................................................................................................................. 119

Vented Containers ....................................................................................................................... 122

200 Area ISA .............................................................................................................................. 125

Sitewide HEPA Vacuums ........................................................................................................... 128

W-PORTEX 011 ......................................................................................................................... 133

P-Trench31 001 ........................................................................................................................... 133

P-Trench34 001 ........................................................................................................................... 135

Sitewide Guzzler ......................................................................................................................... 138

200 Area Diffuse/Fugitive .......................................................................................................... 143

W-296P047-001 .......................................................................................................................... 167

J Nonpoint Source ....................................................................................................................... 168


P-244CR-002 .............................................................................................................................. 169

P-296A044-001 ........................................................................................................................... 170

P-296A045-001 ........................................................................................................................... 173

P-244A-002 ................................................................................................................................. 176

P-244BX-002 .............................................................................................................................. 178

P-244S-002 ................................................................................................................................. 180

P-244TX-002 .............................................................................................................................. 182

W-296P048-001 .......................................................................................................................... 184

P-241AZ301-001 ........................................................................................................................ 184

200W DVS - Active .................................................................................................................... 187

200W DVS - Passive .................................................................................................................. 187

P-296A046-001 ........................................................................................................................... 188

P-296A047-001 ........................................................................................................................... 191

P-BULKVIT-001 ........................................................................................................................ 194

W-296P049-001 .......................................................................................................................... 194

W-296P050-001 .......................................................................................................................... 195

Tanker Loading of Contaminated Waste Water ......................................................................... 195

P-241UX302A-001 ..................................................................................................................... 199

P-241ER311-001......................................................................................................................... 210

P-244A-003 ................................................................................................................................. 210

P-244BX-003 .............................................................................................................................. 212

P-244S-003 ................................................................................................................................. 214

P-244TX-003 .............................................................................................................................. 216


P-241U301B-001 ........................................................................................................................ 223

P-241AZ154-001 ........................................................................................................................ 224

FFTF PTRAEUs ......................................................................................................................... 226

Drum Venting System 2.............................................................................................................. 226

S-MO444-001 ............................................................................................................................. 226

DOE/RL-2017-02 Rev. 0

B-v

P-6241V-001 ............................................................................................................................... 231

P-241A417-001 ........................................................................................................................... 231

P-6241A-001 ............................................................................................................................... 232

P-241EW151-001 ....................................................................................................................... 232

P-241S302-001 ........................................................................................................................... 233

W-TRUDECON-001 .................................................................................................................. 236

W-TRUDECON-002 .................................................................................................................. 236

P-241S102-002 ........................................................................................................................... 237

J-HAMMER-001 ........................................................................................................................ 237

Decon Trailer 200E (Int. Power Exhaust)................................................................................... 237

Decon Trailer 200W (Int. Power Exhaust) ................................................................................. 237

Decon Trailer 200E (Collection Tank Vent) .............................................................................. 237

Decon Trailer 200W (Collection Tank Vent) ............................................................................. 238

W-296P107-001 .......................................................................................................................... 238

P-242A-003 ................................................................................................................................. 239

W-PES-001 ................................................................................................................................. 243

Vapor Extraction System ............................................................................................................ 243

Next Generation Retrieval (Active) ............................................................................................ 243

P-296A048-001 ........................................................................................................................... 243

P-296A049-001 ........................................................................................................................... 247

318 Building................................................................................................................................ 250

W-MARS-001 ............................................................................................................................. 296

P-296S26-001 ............................................................................................................................. 296

P-296S27-001 ............................................................................................................................. 297

W-MARS-002 ............................................................................................................................. 297

EP-331-09-S ................................................................................................................................ 297

W-MARS-003 ............................................................................................................................. 343

W-MARS-004 ............................................................................................................................. 345

W-SXPWET-001 ........................................................................................................................ 347

W-AZ-301 Tanker-001 ............................................................................................................... 347

TABLES

Table 1. Compliance Demonstration for Requirements on Minor, Passively Ventilated

Vents on Single Shell Tanks ................................................................................. B-351

Table 2. Attachment 2 Emission Units That Did Not Operate During

this Certification Period .......................................................................................... B-353

Table 3. Attachment 2 NOC Approvals That Were Not Utilized During

this Certification Period .......................................................................................... B-355

DOE/RL-2017-02 Rev. 0

B-vi

This page was left intentionally blank.

DOE/RL-2017-02 Rev. 0

B-1

W-296P045-001 State of Washington, Department of Health (WDOH) Emission Unit ID: 50

Page in Air Operating Permit (AOP): EU0050-001


Status Compliance Determination

Method

For the time period of : (01-01-16 to 12-31-16)

Zone or Area :

Abatement Technology : Prefilter

Required Units : 1

Add'l Description:

Continuous


Washington River Protection

Solutions (WRPS) work

documents.

Zone or Area :

Abatement Technology : Heater

Required Units : 1

Add'l Description:

Continuous CDM: Field interviews and


Zone or Area :

Abatement Technology : HEPA

Required Units : 2

Add'l Description: 2 HEPAs in series



Zone or Area :

Abatement Technology : Fan

Required Units : 1

Add'l Description:



Zone or Area :

Abatement Technology : Demister

Required Units : 1

Add'l Description:



Required Sampling: Record sample.

Sampling Frequency: Continuous

Radionuclide Requiring Measurement: Cs-137, Sr-90



Federal and State Regulatory Requirement: 40 CFR

61.93(b)(4)(i) & WAC 246-247-075(2)

Permit Monitoring and Testing Procedure: 40 CFR 61,

Appendix B Method 114

Continuous




P-296P022-001 WDOH Emission Unit ID: 53

Page in AOP: EU0053-001


Status


Method

For the time period of: (01-01-16 to 12-31-16)

Zone or Area: Abatement Technology: HEPA



DOE/RL-2017-02 Rev. 0

B-2

Required Units: 2

Add'l Description: 2 in series

Zone or Area: Abatement Technology: Fan

Required Units: 1

Add'l Description:



Required Sampling: Record Sample

Sampling Frequency: 4 week sample/ year

Radionuclide Requiring Measurement: TOTAL ALPHA

TOTAL BETA

Continuous

CDM: Automated Bar Coding

of All Samples at Hanford

(ABCASH) program.


61.93(b)(4)(i) & WAC 246-247-075(3)


Appendix B, Method 114(3)




P-296SY-001 WDOH Emission Unit ID: 56




Method


Zone or Area: Abatement Technology: Deentrainer

Required Units: 1

Add'l Description:



Zone or Area: Abatement Technology: Heater

Required Units: Non-Operational

Add'l Description:



Zone or Area: Abatement Technology: Prefilter

Required Units: 1

Add'l Description:




Required Units: 2

Add'l Description: In series




Required Units: 1

Add'l Description:



DOE/RL-2017-02 Rev. 0

B-3


Sampling Frequency: 1 week sample / 4 times per year


TOTAL BETA

Continuous CDM: ABCASH program and



61.93(b)(4)(i) & WAC 246-247-075(3)






W-296P043-001 WDOH Emission Unit ID: 57


EMISSION UNIT DID NOT OPERATE DURING CY 2016 SEE TABLE 2


W-296P044-001 WDOH Emission Unit ID: 58 Page in AOP: EU0058-0016



S-296S025-001 WDOH Emission Unit ID: 59




Method


Zone or Area :

Abatement Technology : Deentrainer

Required Units : 1

Add'l Description:



Zone or Area :


Required Units : 1

Add'l Description: Heater runs intermittently due to

temperature Regulation



Zone or Area :


Required Units : 1

Add'l Description:



DOE/RL-2017-02 Rev. 0

B-4

Zone or Area :


Required Units : 2




Zone or Area :


Required Units : 1

Add'l Description: Emission unit operates intermittently






TOTAL BETA

Continuous CDM: ABCASH program.


61.93(b)(4)(i) & WAC 246-247-075(3)






S-6266-001 WDOH Emission Unit ID: 62


Emission unit was closed on September 18, 2014. Official closure acceptance by WDOH was provided on

March 5, 2015

S-6266-002 WDOH Emission Unit ID: 63


Emission unit was closed on September 18, 2014. Official closure acceptance by WDOH was provided on

March 5, 2015

P-296A042-001 WDOH Emission Unit ID: 93




Method


Zone or Area :

Abatement Technology : Condenser

Required Units : 1

Add'l Description: (In the common exhaust train) At common

header. Downtime to be reported by the tank Farm air

emissions notification procedure.



DOE/RL-2017-02 Rev. 0

B-5

Zone or Area :

Abatement Technology : Water Chiller

Required Units : 1

Add'l Description: (In the common exhaust train) Downtime

to be reported by the tank farm air emissions notification

procedure.

Intermittent



WRPS notification procedure

and notification logbook.

Comment: The exhauster

operated for a period of time

after the chiller shut down.

Reported per the WRPS

notification procedure.

Zone or Area :

Abatement Technology : HEME

Required Units : 1

Add'l Description: (In (In the common exhaust train)

Downtime to be reported by the tank Farm air emissions

notification procedure.

Continuous



Zone or Area :


Required Units : 1

Add'l Description: (In the common exhaust train) 2 parallel

flow paths with 1 operational. Downtime to be reported by the

tank Farm air emissions notification procedure.



Zone or Area :


Required Units : 2


flow paths. Downtime to be reported by the tank Farm air




Zone or Area :

Abatement Technology : Chiller Pump

Required Units : 1

Add'l Description: (In the common exhaust train) Downtime

to be reported by the tank farm air emissions notification

procedure.



Zone or Area :


Required Units : 1


flow paths. Downtime to be reported by the tank Farm air


Continuous







Radionuclide Requiring Measurement: Sr-90, Cs-137, and

Am-241



61.93(b)(4)(i) & WAC 246-247-075(2)






DOE/RL-2017-02 Rev. 0

B-6

P-204AR-001 WDOH Emission Unit ID: 96



P-242A-002 WDOH Emission Unit ID: 142



Status


Method


Zone or Area :


Required Units : 1

Add'l Description:



Zone or Area :


Required Units : 2




Zone or Area :


Required Units : 1

Add'l Description: Fan operates during 242-A processing.



Zone or Area :


Required Units : 1

Add'l Description:



Zone or Area :


Required Units : 1

Add'l Description:




Sampling Frequency: One week sample per quarter, and

continuous sampling during campaign.

Radionuclide Requiring Measurement: Campaign: TOTAL

ALPHA, TOTAL BETA, 137Cs, 90Sr, 239Pu, 238Pu, and

241Am. Non-Campaign: Total Alpha, Total Beta.

Continuous CDM: Review of ABCASH

database.


61.93(b)(4)(i) & WAC 246-247-075(3)

Permit Monitoring and Testing Procedure: During

campaigns: 40 CFR 60, Appendix A, Method 2: 40 CFR 61,

Appendix B, Method 114: During non-campaigns: 40 CFR 61,

Appendix B, Method 114(3).

Continuous



Permit: AIR 12-306 Issue Date: 03-06-12 Effective Date: 02-23-12

NOC: Operation of the 242-A Evaporator Emission Unit 296-A-22

WDOH NOC ID: 824 Date In AOP: 04-01-13 Page in AOP: EU0142-001

DOE/RL-2017-02 Rev. 0

B-7

The total abated emission limit for this Notice of Construction

is limited to 5.00E-07 mrem/year to the Maximally Exposed

Individual (WAC 246-247-040(5)). The total limit on the

Potential-To-Emit for this Notice of Construction is limited to

1.00E-03 mrem/year to the Maximally Exposed Individual

(WAC 246-247-030(21)).

Continuous

CDM: Reviewed applicable

radionuclide air emissions data

in ABCASH database, or other

source data/information for

2016 to verify total abated

emissions are below the NOC

limit.

This approval applies only to those activities described below.

No additional activities or variations on the approved activities

that constitute a "modification" to the emission unit, as defined

in WAC 246-247-030(16), may be conducted.

The 242-A Evaporator facility is used to reduce the volume of

waste solutions that do not self-boil, and thus reduce the

number of underground double-shell tanks required for waste

storage. The 242-A Evaporator employs a conventional forced-

circulation, vacuum evaporation system to concentrate

radioactive waste solutions. Principal process components of

the evaporator system are located in the 242-A Building. They

include the reboiler, vapor-liquid separator, recirculation pump

and pipe loop, slurry product pump, condensers, and vessel

ventilation system.

The evaporator system receives a mixed blend feed from the

feed tank. The feed consists of unprocessed and processed

waste and recycled liquid that are removed from storage tanks

after solids have settled. The feed is pumped into the

recirculation line and blended with the main product slurry

stream, which flows to the reboiler via the recirculation pump.

The mixture is heated in the reboiler. The vapor liquid separator

is maintained at a reduced pressure. Under this reduced

pressure, a fraction of the water in the heated slurry flashes to

steam and is drawn through two wire mesh deentrainer pads

into a vapor line that leads to the primary condenser. As

evaporation takes place in the separator vessel, the slurry

becomes concentrated. When the process solution has been

concentrated to the parameters specified by the campaigns

process memo, a fraction is withdrawn from the upper

recirculation line, upstream of the feed addition point, and is

either gravity drained or pumped by the slurry pump to

underground storage tanks.

Vapors removed from the vapor-liquid separator via the vapor

line are condensed and routed to the condensate collection tank.

The process condensate is discharged to the Liquid Effluent

Retention Facility (LERF). Steam condensate is continuously

monitored for excessive radiation, pH, and conductivity, and

then discharged from the building to the 200 Area Treated

Effluent Disposal Facility (TEDF). Upon detection of

radioactive contamination, the radiation monitor will

automatically divert the steam condensate stream to the feed

tank. Cooling water from the condensers, which is also

continuously monitored for excessive radiation, pH, and

conductivity, is also discharged to the 200 Area TEDF. This

used cooling water stream cannot be diverted, thus, if



DOE/RL-2017-02 Rev. 0

B-8

contamination is detected, an evaporator shutdown is required.

Non-condensable vapors from the evaporator are filtered and

discharged to the atmosphere via the vessel vent system. This

system consists of a deentrainment pad, prefilter, heater, high-

efficiency filter assembly, and vessel vent exhauster.

The Annual Possession Quantity is limited to the following

radionuclides (Curies/year):

Am-241 3.50E+04 C-14 1.80E+05

Cm-244 4.50E+02 Co-60 4.20E+04

Cs-134 5.20E+05 Cs-137 5.20E+07

Eu-154 1.70E+05 Eu-155 2.40E+05

I-129 9.10E+01 Nb-94 3.40E+03

Pu-238 4.50E+01 Pu-239/240 5.60E+03

Pu-241 5.20E+05 Ra-226 1.10E+03

Ru-106 1.80E+06 Se-79 2.70E+03

Sr-90 7.70E+06 Tc-99 7 .00E+04

Continuous

CDM: TWINS and WRPS

Process Engineering

documentation.

Permit: As Low As Reasonably Achievable Control Technology (ALARACT) 29.1 Issue Date: 03-06-12

Effective Date: 02-23-12

NOC: 242-A Evaporator Maintenance Facility Shutdowns

Date In AOP: 04-01-13

1. Description of Activity

Scope will include planned maintenance facility shutdowns at

242-A Evaporator where electrical power to both 296-A-21 and

296-A-22 stacks are de-energized for greater than 24 hours.

The process of planned maintenance outages and facility

upgrades that require de-energizing both the building stack

(296-A-21) and vessel vent (296-A-22) for facility upgrades or

maintenance will be performed. Building process areas will

have the interior doors sealed with tape to help minimize

diffuse and fugitive emissions to facility personnel and the

outside ambient atmosphere pursuant to meeting WAC 246-

247-130 to meet ALARACT compliance demonstration

requirements. If entry to process areas is required then

radiological controls will be in accordance with the latest

revision of HNF-5183, Tank Farms Radiological Control

Manual to minimize both time and provide controls for diffuse

and fugitive emissions. No facility operational (double shell

tank liquid minimization) activities will be performed during

the time that neither the 296-A-21 and 296-A-22 stacks are not

operating. Radiological containment practices and devices will

be employed as applicable per the Containment Selection

Guide



2. Controls

a. Work with removable contamination will be contained per

the Containment Selection Guide, Attachment A, from the

latest revision of TFC-ESHQ-RP_RWP-C-02, Radiological

Containment.

b. HPT coverage as specified in the Radiological Work Permit.

Continuous

CDM: Field interviews,

Radiological Survey Reports,


DOE/RL-2017-02 Rev. 0

B-9

3. Monitoring

a. Radiological monitoring shall be in accordance with the

latest revision of HNF-5183, Tank Farms Radiological Control

Manual.

Continuous




4. Records/Documentation

a. Radiological Work Permit

b. Radiological survey report(s)



P-242AL44-001 WDOH Emission Unit ID: 146



Status


Method


Zone or Area :

Abatement Technology : Charcoal Filter

Required Units : 1

Add'l Description:

Continuous


work documents.

Required Sampling: Near Field Environment Sampling

Sampling Frequency: Air - every 2 weeks

continuous/deposition - annually


TOTAL BETA

Continuous

CDM: ABCASH program,

field interviews, WRPS

notification procedure and

notification logbooks.

Comment: Monitoring system

met operating time

requirement.


61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous





No Active NOC approvals in the AOP for this certification period.




Status


Method


Zone or Area :

Abatement Technology : Charcoal filter

Required Units : 1

Add'l Description:


work documents.

DOE/RL-2017-02 Rev. 0

B-10



continuous/deposition annually


TOTAL BETA

Continuous






met operating time

requirement.


61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous









Status


Method


Zone or Area :

Abatement Technology : Charcoal filter

Required Units : 1

Add'l Description:


work documents.



continuous/deposition annually


TOTAL BETA

Continuous






met operating time

requirement.


61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous






DOE/RL-2017-02 Rev. 0

B-11




Status


Method


Zone or Area :


Required Units : 2

Add'l Description: 2 filter in series for each train, trains may

be operated independently or together



Zone or Area :


Required Units : 1

Add'l Description: 1 for each train, trains may be operated

independently or together



Zone or Area :


Required Units : 1

Add'l Description: 1 for each train



Zone or Area :


Required Units : 1

Add'l Description: 1 for each train






TOTAL BETA



61.93(b)(4)(i) & WAC 246-247-075(3)






P-242S-001 WDOH Emission Unit ID: 163



DOE/RL-2017-02 Rev. 0

B-12




Status


Method


Zone or Area :


Required Units : 4

Add'l Description: 2 HEPA's in series for each train, 2 trains



Zone or Area :


Required Units : 1

Add'l Description:



Zone or Area :

Abatement Technology : Radial Damper

Required Units : 1

Add'l Description: Set to allow only 2,000 CFM (1,000 CFM

per annulus)



Zone or Area :


Required Units : 2

Add'l Description: 1 per train, 2 trains






TOTAL BETA



61.93(b)(4)(i) & WAC 246-247-075[3]






NOC: 241-AZ Tank Farm Annulus Exhauster Operation







(WAC 246-247-030(21)).

Continuous



(or other source data/

information) to verify total

abated emissions are below the

NOC limit.







DOE/RL-2017-02 Rev. 0

B-13

Exhausting the annulus of the 241-AZ-101 and 241-AZ-102

double-shell tanks (DSTs). The inner shell is constructed from

heat-treated, stress-relieved steel. The outer shell is constructed

of non-stress-relieved steel. The two shells are separated by a

2.5 foot annulus and are contained inside a concrete shell. The

tanks have a usable waste volume of approximately 1,000,000

gallons each. The 296-A-20 stack exhauster ventilates the

annular space of both 241-AZ-101and 241-AZ-102. The 241-

AZ annulus exhaust fan draws outside air into a common inlet

filter assembly. The inlet filter assembly shall consist of two

filter stages, a pre-filter bank, and an inlet filter. The air will

pass through a distribution manifold and flow control valves

into the annular space of both the 241-AZ-101 and 241-AZ-102

tanks, via underground ductwork. The flow control butterfly

dampers can be adjusted to distribute air between the sides of

the annuli and the air slots below the primary tanks. Exhaust air

shall be drawn out of each annulus through underground

ducting to individual aboveground exhaust HEPA filter banks

(one for each tank), associated heaters, and isolation dampers.

To allow for balancing flow between annuli or to allow

isolation of an individual exhaust HEPA filter bank, dampers

shall be installed upstream of each exhaust HEPA filter bank.



Alpha-0 7.00E-05 | Beta-0 2.99E-02 |

Continuous CDM: TWINS

Flow rate through the HEPA filters shall not exceed the

manufactures rating of those HEPA filters. Continuous



EP-318-01-S WDOH Emission Unit ID: 175



P-296W004 001 WDOH Emission Unit ID: 193



Status


Method


Zone or Area : 1


Required Units : 2

Add'l Description: Redundant systems in parallel consisting

of two banks each

Continuous

CDM: Engineering Drawing

H-2-131891 - Sheet 1 -Current

revision.

DOE/RL-2017-02 Rev. 0

B-14

Zone or Area : 2


Required Units : 2

Add'l Description: Redundant systems in parallel consisting

of two banks each

Continuous


H-2-131891 - Sheet 1 -

Current revision.

Zone or Area :


Required Units : 1

Add'l Description: Prefilter for each HEPA housing

Continuous


H-2-131891 - Sheet 1 -

Current revision.

Zone or Area :


Required Units : 2

Add'l Description: 2 parallel paths (1-in use, 1 in backup)

Continuous


H-2-131891 - Sheet 1 -Current

revision.


Sampling Frequency: Continuous, Collect samples biweekly

at a minimum

Radionuclide Requiring Measurement: Each radionuclide

that could contribute greater than 10% of the potential TEDE

Continuous

CDM: Reviewed sampling

data (e.g., ABCASH) and

verified the required sampling

was performed.


61.93(b)(4)(i) & WAC 246-247-075(2)

Permit Monitoring and Testing Procedure: 40 CFR 60

Appendix A, Method 2; 40 CFR 61, Appendix B, Method 114;

61.93(b)(2)(ii) ANSI N13.1

Continuous

CDM: National Emission

Standards for Hazardous Air

Pollutants (NESHAP) Quality

Assurance Project Plan for

Radioactive Air Emissions,

CHPRC-00189, APPENDIX

E. Mission Support Alliance,

LLC (MSA) and Pacific

Northwest National

Laboratory (PNNL) near-

facility monitoring quality

assurance (QA) programs.

Maintenance procedure WRP-

99001 Stack Airflow Test.

Comment: WRP-99001

alternative procedure # is

WRAP-PRO-MN-52077

Permit: AIR 12-301 - A Issue Date: 03-06-12 Effective Date: 02-23-12

NOC: Waste Receiving and Processing Facility (WRAP)




Individual (WAC 246-247-040(5)).

Continuous

CDM: Confirmed annual

possession quantity (APQ) and

is below levels used in NOC

application calculations for

2016 to verify that abated


limit.

The mission of the WRAP includes examining, assaying,

characterizing, treating, verifying, and repackaging solid

radioactive waste material and mixed radioactive waste to

enable treatment, storage, or disposal. The WRAP manages

many categories of radioactive materials such as low-level

waste (LLW), transuranic (TRU) waste, TRU mixed waste,

Continuous


knowledgeable personnel

confirmed no operational or

facility modifications.

DOE/RL-2017-02 Rev. 0

B-15

and low-level mixed waste (LLMW) in contact-handled (CH)

containers where the external surface dose rate does not

exceed 200 mrem/hr. CH containers are defined as packages

having surface dose rates of less than 200 mrem/hr. Remote–

handled (RH) containers (i.e., containers where the external

surface dose rate is equal to or greater than 200 mrem/hr) also

are processed and stored at WRAP in accordance with the

approved safety analysis.

Building 2336-W at the WRAP consists of the following areas

• Shipping and receiving area

• Nondestructive examination/nondestructive assay

(NDE/NDA) area

• Process area

• Ancillary support areas, including the heating, ventilation,

and air conditioning (HVAC), electrical room, mechanical

room, and administration areas

See the following emission units for a detailed description of

additional controls/conditions and limits under this approval.

EU 193 296-W-4; Waste Receiving and Processing Facility

EU 486 200 Area Diffuse/Fugitive; Waste Receiving and

Processing Facility

Eu 1183 HSGS Analysis Facility

The PTE for this project as determined under

WAC 246-247-030(21)(a-e) [as specified in the application] is

1.02E+02 mrem/year. Approved are the associated potential

release rates (Curies/year) of:

DE-0 1.80E+04 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

DE-Ci is a method of normalizing the exposure risk of the

Various isotopes, where the DE-Ci are represented as Pu-239.

Continuous

CDM: Confirmed APQ and is

below levels used in notice of

construction (NOC)




limit.

PROCESS DESCRIPTION - General Overview of WRAP

Operations

This approval applies to those additional activities described

below. No additional activities or variations on the approved

activities that constitute a "modification" to the emission unit,

as defined in WAC 246-247-030(16), may be conducted.

Numerous activities within the WRAP complex, which

includes now includes the 2404-WA, 2404-WB, and 2404 WC

buildings, have been and will be conducted as routine

activities. TRU and mixed wastes are received and processed

at WRAP. The 2404-WA and 2404-WB buildings are used for

waste container storage activities. The 2404-WC buildings is

used for storage as well as for conducting some head space gas

sampling (HSGS) utilizing a darting process.

WRAP also has support buildings to perform NDE and NDA

of larger waste containers. These units include:

• MO-610 - MOBILE BOX ASSAY UNIT(SuperHENC)

MO-610 is a mobile box assay unit used to determine the

AEA-regulated material content of a waste container. The

mobile trailer is approximately 3.0 m (10 ft) by 12.2 m (40 ft)

and is used to assay containers smaller than 2 m3 in volume.

2406-W Facility - HIGH ENERGY REAL-TIME

RADIOGRAPHY (HERTR)

The HERTR unit is a mobile unit used to perform NDE of

containers smaller than 2 m3 (71 ft3). The HERTR unit

Continuous




facility modifications. Facility

procedures demonstrate that

activities at WRAP are as

described in the NOC.

DOE/RL-2017-02 Rev. 0

B-16

consists of two components: (1) a shielded vault where

containers are examined, and (2) an operator control area. The

vault is a shielded enclosure of modular concrete construction.

The operator control area is a mobile trailer that is located in

close proximity to the unit. The NDE is used to examine dense

waste items to indicate the physical appearance of the waste,

identify if liquids are present, and/or other identified suspect

nonconformance waste forms are present to support waste

characterization and processing, confirmation, treatment,

and/or certification.

THE FOLLOWING SECTIONS BRIEFLY DISCUSS THE

GENERAL OPERATIONAL ACTIVITIES CONDUCTED

AT WRAP:

PACKAGING AND REPACKAGING WASTE

Packaging and repackaging activities are performed for waste

generated at WRAP as well as for onsite and offsite

generators. The repackaging of waste supports waste

acceptance criteria for other TSD facilities. For example:

prohibited items from waste packages (i.e., waste items that do

not meet acceptance criteria) are removed and either staged for

later handling or repackaging using remote or manual

methods, and must have a void space of less than 10%. To

meet the less than 10% requirement, void filler can be added.

Packaging and repackaging activities can include the

following:

• Adding absorbent

• Aerosol can/drum puncturing

• Compositing/aggregating solids or liquids

• Over packing

• Pressure relief/release (e.g., aerosol cans, gas cylinders,

drums, or other similar containers)

• Removing prohibited items

• Segregation

• Size reduction [e.g., cutting (jaws, saws)], bending, folding,

crushing (e.g., drum crusher), shredding, compacting, or

similar methods that do not have a higher extent of disruption]

• Sorting

• Void filling

Some packaging of waste (e.g., personal protective equipment,

maintenance waste, types of innocuous waste), as a result of

surveillances/inspections and maintenance that does have a

potential to create minimal airborne contamination, can occur

within the 2336-W Building when the 296-W-4 exhaust stack

emission system is shutdown.

VERIFICATION ACTIVITIES

Verification support activities are provided for waste and other

materials that are generated on or off the Hanford Site.

Verification activities can consist of the following:

• Chemical field screening

• Chemical sampling

• NDE

• Physical observation

SAMPLING ACTIVITIES

Sampling of waste generated by operations or by other onsite

or offsite generators is performed. The purpose of sampling is

to confirm process knowledge, characterize waste, support

DOE/RL-2017-02 Rev. 0

B-17

verification, and determine applicable land disposal

requirements. Sampling can consist of the following:

• Container sampling (liquid, sludge, salt cake, composites).

• Disposition of sample returns (e.g., placement back into the

parent container or another approved container)

• Field screening [e.g., pH paper, oxidizer, volatile organic

analyses (VOAs), or similar screening parameters]

• Headspace gas analysis [typically in support of the WIPP

Project]

• Obtaining a sample for analysis (e.g., grab, composite, or

other similar sampling techniques)

• Shipping/transferring the samples to an approved laboratory

for analysis.

DECONTAMINATION ACTIVITIES

Decontamination activities have been performed since 1997.

Materials, equipment, and waste can be decontaminated (e.g.,

free release, reduce the radiological levels, or other similar

criteria) using a variety of methods. Decontamination at

WRAP can consist of the following:

• Abrasive tools

• Brushing

• Cutting (e.g., removal by sawing, or other similar methods)

• Electrical repairs

• Immersion

• Rust/paint removal

• Scraping

• Washing (e.g., chemicals/detergents)

In addition, WRAP also performs decontamination of WRAP

structures (e.g., building walls, glove boxes, or other similar

surfaces) by any of the above methods.

MAINTENANCE ACTIVITIES

Because of the age of WRAP, current mission, future mission,

support of the cleanup of the Hanford Site, as well as waste

and other materials from offsite generators, a variety of

preventative and/or repair maintenance activities are

performed at WRAP. Some maintenance activities involve the

shutdown of the 296-W-4 exhaust stack.

Maintenance activities can consist of the following:

• Calibrations

• Crane maintenance (bridge crane, jib crane, A frame hoist)

• Electronic systems functional checks and repairs [e.g.,

continuous air monitors (CAMs), personnel contamination

monitors (PCMs), or other similar equipment]

• Painting

• Rollup doors

• Scale systems

• Stack systems (e.g., fan lubes or other similar maintenance

activities)

• Transformers

Certain maintenance activities (e.g., wire rope inspections,

lubrication, functional tests, calibrations, or similar innocuous

activities) that do have a potential to generate minimal

airborne contamination can occur within the 2336-W Building

when the 296-W-4 exhaust stack emission system is

shutdown.

WASTE TREATMENT ACTIVITIES

DOE/RL-2017-02 Rev. 0

B-18

WRAP is a treatment facility permitted by the Washington

State Department of Ecology (Ecology). Treatment activities

can consist of the following:

• Amalgamation

• Deactivation

• Solidification or absorption of free liquids

• Microencapsulation

• Macroencapsulation

• Neutralization of corrosives

• Volume Reduction of waste (e.g., compaction)

STORAGE ACTIVITIES

WRAP is permitted for waste storage by Ecology. WRAP also

stores other materials (e.g., chemicals, equipment, or similar

materials) to support operations. Storage can consist of the

following:

• Container storage (e.g., boxes, drums, ten-drum over packs

(TDOP), transuranic package transporter containers, standard

waste boxes, or similar containers)

• Equipment storage

• NucFil replacement

NucFil replacement will be done by reinstalling a filter. This

activity will consist of sealing an unvented glove bag over the

damaged filter, replacing the filter and removing the glove

bag. Negligible emissions are assumed for this activity such

that they are encompassed within the overall estimate of

emissions for storage activities.

EQUIPMENT, MATERIALS, AND WASTE MOVEMENT

ACTIVITIES

The movement of materials, equipment, waste, chemicals, or

similar items involves the receipt and/or

packaging/repackaging, transferring/shipping, and the

movement and/or relocation within the WRAP TSD unit

boundary. The movement of these items is necessary to

support operations, maintenance, or similar activities.

Movement activities (e.g., using a forklift, crane, truck, dolly,

personnel, or similar equipment) can consist of, but are not

limited to, the following:

• Placing and storing chemical products in flammable cabinets,

over packing or other approved storage locations

• Receiving waste (e.g., liquid, solid, semi solid) for storage

and/or treatment

• Waste container transfers (among outdoor storage pads,

within buildings, glove boxes, or other approved locations)

HOUSEKEEPING ACTIVITIES

Housekeeping activities involve maintaining WRAP in a clean

and orderly condition. Housekeeping activities include the

following:

• Dusting

• Mopping (e.g., squeegees or other similar techniques)

• Picking up debris

• Removal of trash.

• Sweeping (e.g., brooms)

• Vacuuming

• Wiping (e.g., sponges, towels, or other similar methods)

SURVEILLANCE ACTIVITIES

Surveillance activities involve walking down and inspecting

DOE/RL-2017-02 Rev. 0

B-19

various areas, systems, and components. Surveillances

typically consist of daily, weekly, and monthly inspections of

waste containers, buildings, or similar locations. Surveillances

are subject to change (adding, deleting and/or modifying) as

operations, maintenance, engineering, and radiological control

dictates. The following are examples of surveillances currently

performed at WRAP:

• Cold weather surveillances (typically done between October

1 and March 31)

• Container storage areas (buildings, pads, conex boxes, or

other similar locations)

• General condition of building structures

• Inspection/testing of equipment (e.g., 296-W-4 exhaust

system sampling and components, differential pressure

gauges, or similar equipment)

• Inspection/testing of HEPA-filtered vacuums

• Radiological surveys

• Safety equipment (e.g., decontamination showers, eye wash

stations, first aid kits, fire extinguishers, fire suppression

systems, communication equipment, spill kits, emergency

lighting, Scott Air Pak or other similar units, personnel

contamination monitors, masks)

• Treatment and storage locations and ancillary equipment

Surveillances, inspections, and maintenance activities that

have the potential to create minimal airborne contamination

can occur within the 2336-W Building when the 296-W-4

exhaust stack emission system is shutdown.

PROCESS DESCRIPTION - Nondestructive

Examination/Nondestructive Assay Systems





The NDE/NDA area is used to examine and to certify LLW,

MLLW, TRU, and TRU mixed waste container contents

without opening the containers.

The primary function of NDE is to examine the physical

contents of containers entering and leaving the WRAP to

determine whether there are any noncompliant items or

unacceptable conditions in the containers. This examination of

the containers is accomplished by the use of the real-time

radiography (RTR) systems. The RTR systems consists of an

x-ray imaging systems used to identify noncompliant items,

such as free or containerized liquids, compressed gas

containers including aerosol cans, and other suspected

dangerous waste/materials. Data from the x-ray examinations

are entered into the data management system for each

container.

The primary function of NDA is to determine the activity

levels of radio nuclides in the radioactive material entering

and leaving the WRAP. This information is used to categorize

the radioactive material, provide inventory control

information, determine appropriate handling of individual

containers, and to determine if the material meets applicable

transportation and disposal criteria. The NDA equipment

Continuous








DOE/RL-2017-02 Rev. 0

B-20

includes passive-active neutron assay systems and/or gamma

energy analysis systems. Data from the analysis of each

container are entered into the data management system.

PROCESS DESCRIPTION - Process Area





The process area consists of four glove box lines: a TRU

waste process glove box, a TRU waste restricted waste

management (RWM) glove box, a LLW process glove box,

and a LLW RWM glove box. In the process glove boxes,

drums are opened, the contents sorted and sampled, if

necessary, noncompliant items are removed and transferred to

the RWM glove boxes, and the remaining compliant waste

repackaged into new drums.

The airborne radiological contaminants produced at the

WRAP are expected to be primarily generated in these glove

boxes. Incoming drums generally are opened in glove boxes.

However, it might be necessary to loosen a lid or replace a

damaged lid outside of a glove box. For example, an 85-gal

drum lid is removed by placing the drum in an air exhauster

canister, which vents to the process area through a high-

efficiency particulate air (HEPA)-like filter. No credit is taken

for this HEPA-like filter so far as estimating the abated

emissions. Emissions from the process area will exhaust

through the 296-W-4 stack emission system.

TRANSURANIC WASTE PROCESS LINE

The TRU waste process glove box line consists of stainless

steel modular glove boxes that are bolted together in a linear

configuration. Glove box ventilation is of the once through

type. Air is drawn from the process room, through a

nontestable high efficiency process filter, and into the glove

box. The air is exhausted from the glove box through another

nontestable high efficiency process filter to the combined

glove box exhaust system.

Process operations are performed inside of the glove boxes by

using the gloves and/or remote controlled manipulators.

Drums are loaded into the glove box through an airlock and

sealed type entry systems. Noncompliant items are labeled and

transferred to the TRU RWM glove box using a reusable

transfer system. Compliant waste is repackaged into new

containers.

TRANSURANIC WASTE RESTRICTED MANAGEMENT

LINE

The TRU waste RWM glove box line is constructed of

stainless steel. Glove box ventilation is of the once through


nontestable high efficiency process filter, and into the glove


nontestable high-efficiency process filter to the combined

glove box exhaust system. Noncompliant waste is received

from the TRU waste process line in a reusable transfer

container.

The treatment and repackaging operations that occur in the

Continuous








DOE/RL-2017-02 Rev. 0

B-21

TRU waste RWM glove box could include other treated LLW

packages being loaded into new drums and routed to the LLW

process glove box for compaction or loaded out of the RWM

glove box for storage, disposal, or additional treatment.

LOW LEVEL WASTE PROCESS LINE

The LLW/TRU process glove box line consists of stainless

steel modular glove boxes that are bolted together in a linear

configuration. Glove box ventilation is of the once through


nontestab1e high efficiency process filter, and into the glove


nontestable high efficiency process filter to the combined

glove box exhaust system.

Drums enter the glove box through an airlock entry system.

Noncompliant items are bar code labeled and transferred to the

LLW RWM or TRU/RWM glove box using a reusable

transfer system. Compliant waste is compacted and

repackaged into new drums.

PROCESS DESCRIPTION - Shipping and Receiving





Containers are delivered to and transferred from the shipping

and receiving area by truck or forklift. In the shipping and

receiving area, incoming boxes and drums are unloaded,

visually inspected, labeled, and radiologically surveyed. The

resulting information pertaining to each container is entered

into the data management system. Following visual inspection,

containers are transferred to the lag storage area. From the lag

storage area, incoming drums are transferred to a weigh

station and on to the NDE/NDA area for further

characterization. If there are any noncompliant items or

unacceptable conditions discovered in the NDE process, the

containers are transferred to the process area for repackaging.

Once characterized, verified, and/or certified, the certified

TRU waste is loaded into transuranic package transporter

(TRUPACT-2 or equivalent) shipping casks for shipment to

the Waste Isolation Pilot Plant (WIPP) in New Mexico or

other approved facility.

Continuous








P-296AP-001 WDOH Emission Unit ID: 204



Status


Method


Zone or Area :

Abatement Technology : Deentrainer Continuous



DOE/RL-2017-02 Rev. 0

B-22

Required Units : 1

Add'l Description: 2 parallel flow paths

Zone or Area :


Required Units : 1




Zone or Area :


Required Units : 1




Zone or Area :


Required Units : 2

Add'l Description: 2 parallel flow paths with 2 HEPAs in

series



Zone or Area :


Required Units : 1

Add'l Description: 2 parallel flow paths, 1 in operation at a

time






TOTAL BETA



61.93(b)(4)(i) & WAC 246-247-075(3)





Permit: AIR 12-310 Issue Date: 03-06-12 Effective Date: 02-23-12 Obsolete Date: 02-25-16

NOC: Installation and Operation of Waste Retrieval System in Tanks 241-AP-102 and 241-AP-104


NOC NOT UTILIZED DURING CY 2016 SEE TABLE 3




Status


Method


Zone or Area :


Required Units : 1

Add'l Description: 2 parallel flow paths with 1 heater



DOE/RL-2017-02 Rev. 0

B-23

Zone or Area :


Required Units : 2


series



Zone or Area :


Required Units : 1

Add'l Description: 2 parallel flow paths, minimum of 1 in

operation at a time; annulus exhauster






TOTAL BETA



61.93(b)(4)(i) & WAC 246-247-075(3)









Status


Method


Zone or Area :


Required Units : 1




Zone or Area :


Required Units : 1


Continuous



Zone or Area :


Required Units : 1




Zone or Area :

Abatement Technology : Isolation Damper

Required Units : 1

Add'l Description: Allows for operation of one flow path at a

time




Sampling Frequency: 1 week sample / 4 times per year Continuous CDM: ABCASH program.

DOE/RL-2017-02 Rev. 0

B-24


TOTAL BETA


61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous







Status


Method


Zone or Area :


Required Units : 2


series

Continuous





Zone or Area :


Required Units : 1




Zone or Area :


Required Units : 1


Continuous






TOTAL BETA



61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous




DOE/RL-2017-02 Rev. 0

B-25




Status


Method



Required Units: 2


Continuous



Comment: This emission unit

did not operate since April

2016.


Required Units: 1

Add'l Description: Annulus Exhauster

Continuous





2016.


Required Units: 1

Add'l Description:

Continuous





2016.




TOTAL BETA

Continuous

CDM: ABCASH program.



2016.


61.93(b)(4)(i) & WAC 246-247-075[3]



Continuous





2016.


P-296AN-001 WDOH Emission Unit ID: 227


Emission unit closure was reported on October 15, 2014. Official closure acceptance by WDOH was provided on

January 15, 2015

DOE/RL-2017-02 Rev. 0

B-26




Status


Method


Zone or Area :


Required Units : 1

Add'l Description: 2 parallel flow paths with 1 de-entrainer in

each train



Zone or Area :


Required Units : 1

Add'l Description: 2 parallel flow paths with 1 heater in each

train



Zone or Area :


Required Units : 1

Add'l Description: 2 parallel flow paths with 1 fan in each

train



Zone or Area :


Required Units : 2


series in each train.






TOTAL BETA


Federal and State Regulatory Requirement: 40 CFR 61.93

(b)(4)(i)& WAC 246-247-075(3)



Continuous




DOE/RL-2017-02 Rev. 0

B-27




Status


Method


Zone or Area :


Required Units : 3

Add'l Description: In series for both the primary and backup

exhaust systems (222-S Lab Hot Cells)



Zone or Area :


Required Units : 1

Add'l Description: For both primary and backup exhaust

systems (222-S Lab Complex)



Zone or Area :


Required Units : 3

Add'l Description: Primary exhaust operated in parallel,

serves both hot cell addition & main lab.



Zone or Area :


Required Units : 1

Add'l Description: Backup exhaust operates independently or

in parallel with primary exhaust





Radionuclide Requiring Measurement: Sr-90, Cs-137 and

Pu-239

Continuous


field interviews, and WRPS

work documents.


(b)(4)(i) & WAC 246-247-075(2)






P-2025E ETF WDOH Emission Unit ID: 301



Status


Method


Zone or Area : Vessel Off-Gas System

Abatement Technology : HEPA Continuous



DOE/RL-2017-02 Rev. 0

B-28

Required Units : 3

Add'l Description: 1 heater and 2 filters in series, with 2

parallel fans (minimum of 1 in operation). VOG discharges

into Building Ventilation

Zone or Area : Vessel Off-Gas System


Required Units : 1

Add'l Description:



Zone or Area : Building Ventilation System


Required Units : 2

Add'l Description: 3 parallel flowpaths each with 1 filter and

1 fan; minimum 2 in operation



Zone or Area : Building Ventilation System


Required Units : 2

Add'l Description: Serves both areas



Required Sampling: Monitoring stations N498, N499, N972,

and N999



TOTAL BETA

Continuous


ABCASH data.

Comment: 296-E-1 met the

sampling frequency

requirement of 4 week

sample/yr. The ambient air

monitors that are listed met the

continuous

monitoring/sampling

requirements specified in the

Diffuse & Fugitive license.


(b)(4)(i)& WAC 246-247-075(3)



Continuous

CDM: Contractor NESHAP

Quality Assurance Plan for

Radioactive Emissions.


P-213W-001 WDOH Emission Unit ID: 308



DOE/RL-2017-02 Rev. 0

B-29

P-291T001-001 WDOH Emission Unit ID: 314



Status


Method


Zone or Area :


Required Units : 1

Add'l Description:

Continuous

CDM: Heating & Ventilation

Air Flow & Control Diagram

(HVAC), Engineering

Drawing H-2-91269, Sheet 2.

Comment: Engineering

drawings verify the presence

of prefilter

Zone or Area :


Required Units : 2


Continuous



(HVAC), Engineering




of two HEPA filters, in series.

Zone or Area :


Required Units : 2

Add'l Description: 2 in parallel (with one as a backup)

Continuous



(HVAC), Engineering




of two fans, in parallel with

one as backup.


Sampling Frequency: Particulates shall be continuously

sampled and analyzed every two weeks for gross alpha and

gross beta/gamma, composited quarterly, and analyzed

isotopically.

Radionuclide Requiring Measurement: All radionuclides

that contribute greater than 10 percent of the potential-to-emit

TEDE to the MEI, greater than 0.1 mrem/yr potential-to-emit

TEDE to the MEI, and greater than 25 percent of the TEDE to

the MEI after controls.

Continuous




was performed.


(b)(4)(i) & WAC 246-247-075(2)


Appendix B, Method 114 NDA as detailed in conditions

below.

Continuous

CDM: NESHAP Quality


Radioactive Air Emissions

(CHPRC-00189, Appendix E).


NOC: Consolidated T Plant Operations


DOE/RL-2017-02 Rev. 0

B-30




Continuous

CDM: Confirmed Dose

Equivalent (DE) Curie (Ci) for

year reported in T Plant Curie

Inventory Logbook, HNF-N-

42, was <15,000 DE-Ci/year

basis for this NOC limit in the

application.





This consolidated T-Plant license supersedes all radioactive air

licenses for 291-T-1.

a. This approval subsumes those activities approved in three

previous license approvals, retains/revises the specific

conditions and limitations of those approvals, and replaces

them as the radioactive air license for T-Plant:

i. AIR 03-1208 (NOC ID # 445, "Storage in T-Plant Complex

of Sludge from K-Basins")

ii. AIR 01-1010 (NOC ID # 499, "T-Plant Complex Fuel

Removal Project")

iii. AIR 02-704 (NOC ID # 500, "Entering and Characterizing

of the 224-T Facility Process Cells")

b. With additional conditions and limitations provided herein,

this approval also extends to new activities discussed in the

NOC application "Radioactive Air Emissions Notice of

Construction for Consolidated T Plant Operations", DOE/RL-

2004-50, Rev.0, September, 2004, described briefly:

i. Receipt, Storage, Treatment, and Loads out of Contact-

Handled and Remote-Handled Transuranic (TRU) and

Transuranic Mixed Waste (M-91 Initiative)

ii. Treatment (in addition to storage) of K-Basin Sludge from

the North Load out Pit (NLOP)

iii. Such activities considered routine at T Plant as are

described in succeeding conditions.

Activities a)i through a)iii may emit radioactive air through

291-T-1. Additionally, activity a)iii may emit to the 200 Area

Diffuse & Fugitive emission unit and to Portable Temporary

Radioactive Air Emission Units.

Continuous

CDM: Facility procedures

demonstrate that activities at

T-Plant are as described in the

NOC.

Comment: 224-T was

removed from the license on

2/16/2017 (AIR 17-206).

The PTE for this project ad determined under WAC 246-247-

030(21)(a-e)[as specified in the application] is 1.20E+02

mrem/year. Approved are the associated potential release rates

(Curies/year) of:

Am-241 1.38E+00 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

isotopic distribution based on destructive analysis of pre-filter

four

Cs-137 1.46E+01 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Continuous

CDM: Confirmed DE-Ci for


Inventory Logbook, HNF-N-

42, was <15,000 DE-Ci/year

basis for this NOC limit in the

application.

DOE/RL-2017-02 Rev. 0

B-31

Pu-239/240 1.38E+01 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Sr-90 1.94E+01 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

The radioactive isotopes identified for this emission unit are

(no quantities specified):

Am-241 Cs-137 Pu-239/240 Sr-90

The potential release rates described in this Condition were

used to determine control technologies and monitoring

requirements for this approval. DOE must notify the

Department of a "modification" to the emission unit, as

defined in WAC 246-247-030(16). DOE must notify the

Department of any changes to a NESHAP major emission unit

when a specific isotope is newly identified as contributing

greater than 10% of the potential TEDE to the MEI, or greater

than 25% of the TEDE to the MEI after controls. (WAC 246-

247-110(9)) DOE must notify the Department of any changes

to potential release rates as required by state or federal

regulations including changes that would constitute a

significant modification to the Air Operating Permit under

WAC 173-401-725( 4). Notice will be provided according to

the particular regulation under which notification is required.

If the applicable regulation(s) does not address manner and

type of notification, DOE will provide the Department with

advance written notice by letter or electronic mail but not

solely by copies of documents.

All activities involving radioactive materials shall be

conducted in accordance with radiation control procedures

approved per applicable QA program.

(WAC 246-247-040(5))

Continuous

CDM: NESHAP Quality



(CHPRC-00189, Appendix).

CH2M HILL Plateau

Remediation Company

(CHPRC) Radiological

Control Manual (CHPRC-

00073).

Calibrate all differential pressure gauges associated with

291-T-1 HEPA filters annually. (WAC 246-247-040(5)) Continuous

CDM: WMP-18006,

Pressure/Vacuum Gauge,

Differential Pressure/Vacuum

Gauge Calibration; work

package 2T-16-02564

Completed on 7/27/2016.

Receipt, Storage, Treatment, and Load out of Contact-handled

and Remote-handled transuranic (TRU) and transuranic mixed

(TRUM) (M-91 Initiative):

A. M91 project activities shall be conducted in T-Plant within

the head end, the railroad tunnel, and/or the T-Plant Canyon.

M-91 waste shall be received at the head end or at the railroad

tunnel. M91 waste is remote or contact handled transuranic,

Continuous

CDM: No M-91 activities

were conducted during the

reporting period. Procedures

will be written prior to

resuming M-91 activities.

DOE/RL-2017-02 Rev. 0

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transuranic mixed, mixed, or mixed low level waste.

B. M-91 waste containers shall be opened and their contents

treated in the head end of T-Plant only under containment,

containment being defined here as either vented and HEPA-

filtered glove box/bag, sealed glove box/bag, ventilated and

HEPA-filtered containment tent or ventilated and HEPA-

filtered solid-structure temporary containment, or PTRAEU.

Where active ventilation is provided, that ventilation shall

discharge into the T-Plant canyon so that radioactive air

emissions originating in this process are further controlled by

the 291-T-1 ventilation system controls. Procedures (approved

in accord with applicable QA program) to ensure the initial

integrity of the containment and to ensure the continued

integrity of the containment structures shall be followed, shall

include periodic radiological surveys, and shall be kept

available for WDOH review. The head end will be posted

based on radiological conditions in accordance with radiation

control procedures approved per applicable QA program.

C. M-91 waste containers shall be opened and their contents

treated in the railroad tunnel and/or canyon of T-Plant, in

accord with radiological control procedures (approved in

accord with applicable QA program).

D. Lower risk M-91 containers may be received at the head

end of T-Plant, and higher risk M-91 containers shall be

received at the railroad tunnel. Risk criteria, including

radiological risk considerations, governing receipt location

shall be developed and documented.

E. Surface contamination and dose rate limits on M-91 waste

containers received at T-Plant shall be governed by approved

solid waste acceptance procedures. Deviations from approved

solid waste acceptance procedures are allowed under a

controlled waiver process. Stand-alone solid waste acceptance

documents specifying surface contamination and dose rate

limits shall be developed and approved for any M-91

containers received under the waiver process. These

procedures shall be kept readily available for WDOH review.

Documentation shall be sufficient to allow ready identification

of the criteria under which each waste container is accepted,

and shall note definite compliance with the applicable criteria

on receipt.

F. Applicable surface contamination/dose rate criteria shall be

documented for each container of M-91 waste repackaged at

T-Plant for transshipment. Documentation of applicable

criteria and compliance thereto shall be maintained for M-91

waste containers shipped from T-Plant.

G. Receipt, Storage, Treatment, and Load out of Contact-


Transuranic Mixed Waste (M-91Initiative) includes the

following activities:

G1) Receiving.

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G2) Sorting.

G3) Storing.

G4) Size Reduction.

G5) Repackaging.

G6) Containerizing.

G7) Load out.

G8) Treatment. (WAC 246-247-040(5)).

Routine T-Plant Activities:

A1) Packaging and Repackaging Waste - Packaging and

repackaging activities are performed for waste generated at T-

Plant as well as for onsite and offsite generators. Packaging

and repackaging activities are:

A1a) Sorting.

A1b) Segregation.

A1c) Removing prohibited items.

A1d) Compositing/aggregating solids or liquids.

A1e) Adding absorbent.

A1f) Size reduction [e.g., cutting (jaws, saws, torches)],

bending, folding, crushing (e.g., drum crusher), shredding,

compacting, or similar methods that do not have a higher

extent of disruption].

A1g) Void filling.

A1h) Pressure relief/release (e.g., aerosol cans, gas cylinders,

drums, or other similar containers).

A1i) Aerosol can/drum puncturing.

A2) Verification Activities - Verification support activities are

provided for waste and other materials that are generated on or

off the Hanford Site. Verification activities are:

A2a) Physical observation.

A2b) Nondestructive examination (NDE).

A2c) Nondestructive assay (NDA).

A2d) Chemical field screening.

A2e) Radiological surveys.

A2f) Radiological samples.

A2g) Headspace gas analysis.

A2h) Chemical sampling.

A3) Sampling Activities - Sampling of waste generated by

operations or by other onsite or offsite generators is

performed. The purpose of sampling is to confirm process

knowledge, characterize waste, support verification, and

determine land disposal requirements as applicable. Sampling

activities are:

A3a) Field screening [e.g., pH paper, oxidizer, volatile organic

analyses (VOAs), polychlorinated biphenyls (PCBs), or

similar screening parameters].

A3b) Obtaining a sample for analysis [e.g., grab, composite,

composite liquid waste sampler (COLIWASA), or other

similar sampling techniques].

A3c) Shipping/transferring the samples to an approved

laboratory for analysis.

A3d) Disposition of sample returns (e.g., placement back into

the parent container or another approved container/tank).

A3e) Headspace gas analysis [typically in support of the

Waste Isolation Pilot Plant (WIPP) Project].

Continuous



T-Plant are as described in the

NOC.

DOE/RL-2017-02 Rev. 0

B-34

A3f) Tank sampling (liquid, sludge, salt cake, composites).

A4) Decontamination/Refurbishment Activities - Materials,

equipment, and waste can be decontaminated (e.g., free

release, reduce the radiological levels, or other similar criteria)

using a variety of methods. T-Plant also performs

decontamination of T- Plant structural components (e.g., 221-

T Building walls, cells, or other similar surfaces).

Decontamination activities at T-Plant are:

A4a) Water (fog, high or low-pressure spraying).

A4b) Steam.

A4c) Ice blasting.

A4d) Vacuum blasting.

A4e) Brushing.

A4f) Abrasive tools.

A4g) Scraping.

A4h) Washing (e.g., chemicals/detergents).

A4i) Immersion.

A4j) Electro-polishing.

A4k) Cutting (e.g., removal by sawing, torch cutting more

highly radioactive components or other similar methods).

A4l) Rust/paint removal.

A5) Maintenance Activities - A variety of preventative and/or

repair maintenance activities are performed at T-Plant. Some

maintenance activities involve the temporary shut down of the

291-T-1 exhaust stack. Maintenance activities are:

A5a) Painting.

A5b) Crane maintenance.

A5c) Electronic systems functional checks and repairs

[CAMs, personnel contamination monitors (PCMs)].

A5d) Calibrations.

And may be performed on:

A5e) Rollup doors.

A5f) Heat pumps.

A5g) Exhaust fans.

A5h) Transformers.

A5i) Scale systems.

A5j) Wire rope.

A5k) Stack systems fan lubes.

A5l) Forklifts.

A6) Waste Treatment Activities - T-Plant is a treatment

facility permitted by the Washington State Department of

Ecology (Ecology). Treatment activities are:

A6a) Macroencapsulation.

A6b) Absorption.

A6c) Neutralization.

A6d) Immobilization.

A6e) Encapsulation.

A6f) Stabilization (solidification, cementation, grouting).

A6g) Compaction.

A6h) Amalgamation.

A6i) Segregation.

A6j) Shredding.

A6k) Venting.

A6l) Size Reduction.

A7) Recycling Activities - Materials are recycled whenever

possible. Recycled materials are collected in accumulation

DOE/RL-2017-02 Rev. 0

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containers in approved locations and transferred to the

Recycling Center. Only nonradioactive materials are sent to

the Recycling Center. Some radioactive materials (ferrous and

nonferrous metals) can be recycled. Recycled materials are:

ferrous and non-ferrous metal, light bulbs, aerosol cans, oils,

and batteries.

A8) Storage Activities - T-Plant is permitted for waste storage

by Ecology. Plant also stores other materials (chemicals, or

equipment, or similar materials) to support operations.

Radioactive wastes may be stored uncontainerized or in:

A8a) Containers (boxes, drums, tanker trucks/railcars, or large

diameter containers).

A8b) Tanks.

A8c) Sumps and pipes.

A9) Equipment, Materials, and Waste Movement Activities -


similar items involves the receipt and/or transferring/shipping,

and movement and/or relocation within the T-Plant TSD unit

boundary. Movement activities (using a forklift, crane, truck,

dolly, personnel) are:

A9a) Receiving waste (liquid, solid, semi-solid) for storage

and/or treatment.

A9b) Movement of waste (liquid, solid, semi-solid) and

equipment in or out of process cells, canyon deck craneway,

or tunnel in the 221-T Building.

A9c) Movement of liquids, sludges, or other waste from

containers and/or tanks via transfer lines.

A9d) Waste container transfers (among outdoor storage pads,

within buildings, process cells, canyon deck, or other

approved locations). A9e) Placing and storing chemical

products in flammable cabinets or other approved storage

locations.

A9f) Transloading from the 221-T tunnel to canyon deck

and/or process cells.

A10) Housekeeping Activities - Housekeeping activities

involve maintaining T-Plant in a clean and orderly condition.

Housekeeping activities are:

A10a) Sweeping (brooms).

A10b) Mopping (squeegees or mops).

A10c) Vacuuming.

A10d) Dusting.

A10e) Wiping (sponges, towels).

A10f) Picking up debris.

A10g) Removal of trash.

A11) Surveillance Activities - Surveillance activities involve

walking down and inspecting various areas, systems, and

components. Surveillances typically consist of daily, weekly,

and monthly inspections of waste containers, tanks, buildings,

or similar locations. Surveillances are subject to change

(adding, deleting and/or modifying) as operations,

maintenance, engineering, and radiological control dictates.

Surveillances, inspections, and maintenance activities that do

not have the potential to create airborne contamination can

occur within the 221-T Building when the 291-T-1 exhaust

stack emission system is shutdown. The following

surveillances are performed at T-Plant:

DOE/RL-2017-02 Rev. 0

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A11a) Container storage areas treatment and storage tanks and

ancillary equipment.

A11b) General condition of building structures.

A11c) Safety Cold weather surveillances (typically, between

October 1 and March 31).

A11d) Inspection of equipment.

A11e) Inspection of HEPA filtered vacuums.

A11f) Radiological surveys.

A12) Contamination Within the Canyon - The operational

activities described inherently involve the spread of

contamination within the canyon. The canyon is designed to

provide containment for these operational activities. Job

specific contamination controls are used (spreading paper to

facilitate easy decontamination, fogging, fixing contamination,

covering, performing operations remotely or other similar

methods that cover, seal, or remove smearable contamination).

(WAC 246-247-040(5))

The abated and unabated emissions for this license have been

estimated using particulate 241-Am, 239/240-Pu, 137-Cs, and

90-Sr, based on the isotopic distribution measured in

destructive analysis of a T-Plant pre-filter, a Dose Equivalent-

Curie limit of 15,000 DE-Ci, and also include a small

contribution from gaseous radionuclides that may be

encountered. The amounts of radioactive gases included are:

(3-H, 25 Ci), (85-Kr, 3000 Ci), (129-I, 0.05 Ci), (219-Rn, 0.2

Ci), (220-Rn, 30 Ci), (222-Rn, 2 Ci). Radionuclides that may

be encountered as particulates are: 242-Cm, 243-Am, 244-Cm,

60-Co, 134-Cs, 154-Eu, 40-K, 94-Nb, 237-Np, 238-Pu, 241-

Pu, 242-Pu, 244-Pu, 226-Ra, 106-Ru, 125-Sb, 228-Th, 234-

Th, 232-U, 233-U, 234-U, 235-U, 236-U, 238-U. Other

particulate radionuclides are permitted, the total to remain

within the DE-Ci limit of 15,000 DE-Ci and the abated

emission limit of the license. Gaseous radionuclides are

permitted, the sum of doses from radioactive gases to remain

less than 6% of the total abated emission limit for this license.

This condition does not apply to naturally occurring Radon.

Not

Applicable

CDM: Ecology and WDOH

have determined that licensee

need not certify compliance

with conditions that convey a

right, are a historical summary

or fact, that pertain to action to

be complete in the future or

that pertain to actions required

of the agency. Verified

unabated PTE from DECi

logbook, HNF-N-42 Inventory

Control Program, WMP 340,

Section 1.8.

The alternative flow measurement method proposed for the

291-T-1 stack by USDOE letter 03-RCA-0210, dated April 9,

2003, is approved for use (WAC 246-247-075(3)).

Not

Applicable






or fact, that pertain to action to

be complete in the future or


of the agency.

The annual inspection and maintenance of the HEPAs must

include visual inspection of the filter housing. Documentation

of these activities must be made available to DOH upon

request. (WAC 246-247-040(5))

Continuous

CDM: In-Place Testing of

HEPA Filter Systems, 2T-

99042. Work package 2T-16-

00958. Completed on

6/16/2016.

The emission unit monitoring system shall have the following

activities performed: Continuous

CDM: Stack Monitor Record

Sampler Components Swap,

DOE/RL-2017-02 Rev. 0

B-37

A1) By December 31, 2005 and annually thereafter:

A1a) A visual check of nozzle position and orientation as well

as measurements of nozzle openings;

A1b) Checks to ensure the tightness of all fittings and

connections as well as a leak test of the entire sampling

system.

A1c) Visual inspections for corrosion, physical damage, or

dust loading of the probe, sample lines, and monitoring system

equipment.

A2) Annually, from December 31, 2003:

A2a) A functional/calibration check of monitoring system

instrumentation shall be performed.

A2b) USDOE shall provide to WDOH for review copies of

the procedures used to perform the above activities.

(WAC 246-247-060(5)).

Functional Check, and

Calibration, 2T18599. Work

package 2T-16-03318.

Completed on 9/20/2016.

The PTE at T-Plant shall be tracked in DE curies. A running

total of DE curies present at the beginning of the calendar year

plus DE curies introduced into T-Plant during that year shall

be maintained and kept available for WDOH review. This

record shall be made current at no greater than weekly

intervals. That the total does not exceed license limits shall be

routinely verified, and documentation of that verification shall

be maintained. (WAC 246-247-040(5))

(WAC 246-247-060(5))

Continuous

CDM: Inventory Control

Program, WMP 340, Section

1.8. T Plant Curie Inventory,

HNF-N-42 Logbook.

The Quality Assurance Standards for the sampling of

emissions and subsequent analysis must remain in compliance

with HNF-0528 NESHAPS Quality Assurance Project Plan

for Radioactive Airborne (all of sections 2.0, 3.0, 5.0).

(WAC 246-247-060(5))

Continuous

CDM: MSA has staff and

procedures in place to collect

and analyze samples in

compliance with applicable

QA requirements.

T-Plant must continue to demonstrate that the adequacy of

their system design and operation is equivalent to the intent of

ASME/ANSI N 510. Both stages of HEPA filtration must be

individually aerosol tested in place, a minimum of annually (at

a minimum control efficiency of 99.95 percent). (WAC 246-

247-040(5))

Continuous

CDM: In-Place Testing of

HEPA Filter Systems,

2T99042. Work package 2T-

16-00958. Completed on

6/16/2016.

Receipt and Storage of K-Basins Sludge:

A. Receipt, Treatment, Storage and Load out of north load out

pit (NLOP) Sludge:

A1) Sludge treatment consists of mixing the sludge with grout

via the following major process steps:

A1a) Transferring sludge from Large Diameter Container into

the grout system.

A1b) Sampling to ensure grouted containers meet waste

isolation project plant (WIPP) acceptance requirements.

A1c) Transferring aliquots into WIPP certified 55 gallon

drums.

A1d) Grouting to meet WIPP waste acceptance criteria.

A2) Prior to treatment, NLOP sludge shall be stored in T-Plant

process cells 3L, 10L, 13L, 15L, 8R, 9L, 14R, and/or 16R.

A3) Containerized and grouted sludge shall be stored for not

longer than 23 years from the date of issue of this license

within the T-Plant complex.

A4) Containerized and grouted sludge shall be stored within

Continuous

CDM: DOE/WIPP-02-3122,

"Waste Acceptance Criteria for

the Waste Isolation Pilot

Plant." No K-Basins’ sludge

was received or treated at

T-Plant during the reporting

period. Waste Profile Sheet,

TPLT-220-0001; RL letter 06-

ESD-0156, dated September

15, 2006 to WDOH

documenting that the PWR

Fuel Removal Project was

completed on September 18,

2004; HNF-EP-0063,

"Hanford Site Solid Waste

Acceptance Criteria;"

Radiological Work Permits,

RWP T-240, RWP T-246,

DOE/RL-2017-02 Rev. 0

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the TSD unit boundary, and disposed according to assay of

individual containers.

A5) The potential-to-emit of NLOP sludge received at T-Plant

shall not exceed 0.9 mrem/year, corresponding to 120 DE Ci.

B. Receipt and Storage of K-Basins Sludge:

B1) Preparation of cells to receive sludge containers, which

shall be limited to the following activities:

B1a) Intrusive cell operations to relocate items within cells

and to transfer items between cells.

B1b) Removal of cell contents, which shall be limited to the

following operations.

B1b1) Remote crane operations using lifting bails and

clamshells.

B1b2) Pumping of liquids.

B1b3) Vacuum suction.

B1b4) Storage, repackaging, and treatment of containerized

and uncontainerized radioactive waste.

B1b5) Waste characterization, verification, repackaging, size

reduction, segregation, immobilization, and consolidation.

B1b6) Preparation of waste shipments in accordance with

acceptance criteria for other facilities.

B1b7) Treatment and storage of liquid mixed waste.

B1c) Storage of contaminated process equipment and debris in

the 221-T Canyon Building cells and deck shall be limited to:

B1c1) Tanks, pulsers, precipitators, centrifuges, and

jumpers/connectors.

B1c2) Decontamination equipment, immersion tanks,

sprayers, and blasters.

B1c3) Equipment racks, pumps, mixers, and motors.

B1c4) Original equipment (prior to decontamination mission).

B1c5) Condensers, chillers, filter assemblies, and columns.

B1c6) Open and closed boxes, drums, and containers, filled

with debris.

B1c7) Tools, concrete blocks, and loose debris.

B1d) Refurbishing, recycling, and maintenance of

contaminated equipment shall be limited to the items of

equipment listed above. B1e) Decontamination of equipment

and materials, which shall be limited to the following

operations:

B1e1) Hand, spray, and abrasive methods.

B1e2) Steam cleaning.

B1e3) High pressure hot water.

B1e4) High pressure cold water

B1e5) Ice blasting.

B1e6) Abrasive tools.

B2) The chemical and physical processes associated with the

sludge storage shall consist of the following:

B2b) Radioactive waste shall be managed in accordance with

written facility and Hanford Site waste management

procedures and acceptance criteria. Criteria for moving

containers from the canyon into the tunnel include the

requirements that smearable contamination on the outside of

the container must be less than 400 dpm/100 cm2 alpha and

less than 20,000 dpm/100 cm2 beta/gamma for low risk

RWP T-248, RWP T-250,

RWP T-252.

DOE/RL-2017-02 Rev. 0

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evolutions. For medium risk evolutions the criteria for moving

containers from the canyon into the tunnel shall include the

requirements that smearable contamination on the outside of

the container must be less than 2,000 dpm/100 cm2 alpha and

less than 100,000 dpm/100 cm2 beta/gamma.

B2c) New liner systems shall be installed in the pool if storage

under water is required and in four to twelve of the process

cells. Existing water conditioning systems (coolers, filtration

system, ion exchange columns, and piping) shall be used,

modified, replaced or removed if storage under water is

required.

B2d) Spent nuclear fuel (SNF) sludge retrieved from the 105-

KE and 105-KW Basins shall be managed as two separate

waste streams. Sludge containers configured for dry storage

shall be used for less reactive floor and pit sludge components,

including windblown sand and rocks, spalled concrete from

the basin walls, iron and aluminum corrosion products, ion

exchange resin beads, uranium oxides, and uranium fuel

particles. More reactive sludge collected in the knockout pots

and settler tank during SNF retrieval and processing at K-

Basins shall be stored in a container configured for storage

under water or for dry storage if allowed by criticality and

thermal analyses.

B2e) Physical upgrades to the 221-T Canyon, as determined in

final design, shall include installation of new cell containment,

liner bracing systems, sump pumps, leak detectors, and

instrumentation and controls in the 221-T Canyon.

B2g) Canyon radiation detectors, alarms, and cameras will be

upgraded to provide surveillance.

B2h) Sludge containers shall be designed to ensure a safe

storage configuration, based on final design results determined

in criticality and heat rejection requirements analysis. Final

design shall analyze maximum sludge loading and container

sizing to minimize the number of transfers and number of

containers.

B2i) Contents of filled sludge containers shall consist of a

layer of sludge below a layer of water and a layer of air to

provide a void space in each container. Sludge containers shall

be capable of maintaining sludge in a wet state during

transport and storage. B2j) Sludge containers shall be received

and placed into interim storage in the 221-T Canyon,

configured for dry cell storage or storage under water. All

sludge container handling and placement within the 221-T

Building shall be performed remotely via crane operations.

B2k) The containers shall be transported from K- Basins to the

221-T Building via tractor and trailer. Each transfer shall

consist of one transport cask which shall be inspected upon

receipt according to approved receipt methods.

B2l) Sludge container unloading operations shall be done

remotely using the canyon crane system. T-Plant Complex

personnel shall vent and purge the transport cask with non-

radioactive inert gas within the controlled airspace. The

purge/venting system shall include a radiation detection

method to verify that the storage container does not leak

during transport and shall purge all hydrogen from the

transport cask.

DOE/RL-2017-02 Rev. 0

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B2m) As a sludge container is moved from the tunnel into the

canyon, operations personnel shall verify remotely the

identification number and record the container number, via

existing camera systems. After the container is removed from

the cask, an empty container will be placed in the cask and the

lid shall be replaced. The transport system shall be surveyed

for possible contamination on exiting the Radiological Area

and will return to K- Basins.

B2n) After the sludge containers are placed in the 221-T

Canyon interim dry storage location, surveillance shall be

performed to ensure that safety, regulatory, and safeguards

and security requirements are met. Water levels within the dry

storage containers shall be monitored (weight differential),

and water additions shall be made remotely.

B2o) After sludge containers are placed in the interim

underwater pool storage location, surveillance shall be

performed to ensure that safety, regulatory, and safeguards

and security requirements are met. Pool storage conditions

(water quality, water temperature, water level, and ion

exchange column status) shall be monitored, and water shall

be added as needed to the pool to maintain the necessary water

depth.

(WAC 246-247-040(5))

P-296T007-001 WDOH Emission Unit ID: 315



Status


Method


Zone or Area :


Required Units : 1

Add'l Description: To operate per Conditions and Limitations

of the license.

Intermittent



(HVAC), Engineering

Drawings H-2-83095 Sheet 1,

H-2-83100 Sheet 1, H-2-

826566 Sheet 1 show removal

of Demister unit.

Comment: The DOH issued

new air permit on October 10,

2014 (AIR 14-1001) for 2706T

that provided for removal the

demister as abatement

technology. This is reflected

in AOP Renewal 2, Revision

B.

DOE/RL-2017-02 Rev. 0

B-41

Zone or Area :


Required Units : 1


of the license.

Intermittent



(HVAC), Engineering


H-2-83100 Sheet 1, H-2-

826566 Sheet 1 show removal

of heater

Comment: The DOH issued

new air permit on October 10,

2014 (AIR 14-1001)for 2706T

that provided for removal the

demister as abatement

technology. This is reflected

in AOP Renewal 2, Revision

B.

Zone or Area :


Required Units : 1

Add'l Description:

Continuous



(HVAC), Engineering


H-2-83100 Sheet 1, H-2-

826566 Sheet 1.



of prefilter.

Zone or Area :


Required Units : 1

Add'l Description:

Continuous



(HVAC), Engineering


H-2-83100 Sheet 1, H-2-

826566 Sheet 1.



of a HEPA filter.

Zone or Area :


Required Units : 1


of the license.

Continuous



(HVAC), Engineering


H-2-83100 Sheet 1, H-2-

826566 Sheet 1.



of fan.


Sampling Frequency: See special conditions.


TOTAL BETA

Continuous




was performed.


61.93(c)(4)(e) & WAC 246-247-075(3)



Continuous

CDM: CHPRC NESHAP QA

program (CHPRC-00189).

DOE/RL-2017-02 Rev. 0

B-42

No active NOC approvals in the AOP for this emission unit.

P-291S001-001 WDOH Emission Unit ID: 332



Status


Method


Zone or Area :

Abatement Technology : Sandfilter

Required Units : 1

Add'l Description:

Continuous CDM: Verify with technical

authority.

Zone or Area :


Required Units : 2

Add'l Description: In parallel, only 1 operates at a time

Continuous CDM: Verify with technical

authority.


Sampling Frequency: 4 week sample/year


TOTAL BETA

Continuous CDM: ABCASH data review.


61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous

CDM: CHPRC-00189,

NESHAP Quality Assurance

Project "j" Plan for

Radioactive Air Emissions.

Permit: ALARACT 28.1 Issue Date: 03-06-12 Effective Date: 02-23-12

NOC: Shutdown of Stack System(s) (Maintenance and Incidental)

WDOH NOC ID: Date In AOP: 04-01-13


The listed facilities are currently under Surveillance and

Maintenance (S&M) status, meaning active processing has

ceased with radioactive feed materials no longer brought in.

Surveillances and maintenance activities are performed in

these facilities including, but not limited to minor activities

such as exterior and interior inspections; checking for door

security, for any unauthorized building intrusions, and for

structural integrity; water intrusion cleanup; waste

handling/removal; maintaining radiological airborne control

zones; animal or insect intrusion abatement; maintaining

operating systems and building integrity, eliminating utilities

when possible; identifying and reducing hazards; and

housekeeping. The primary ventilation systems and associated

record sampling systems operate at each facility as described

in the Hanford Site Air Operating Permit.

Not

Applicable






or fact, that pertain to actions

to be completed in the future,

or that pertain to actions

required of the agency.

DOE/RL-2017-02 Rev. 0

B-43

At certain times to support these various S&M activities, or

related to maintenance or replacement-inkind, any one of these

primary ventilation systems may be shut down for a period up

to or exceeding two days (48 consecutive hours) duration.

The three ventilation systems which may be shut down are:

332 REDOX, 402 B-Plant, 369 PUREX.

2. Controls

It was agreed that an As Low As Reasonably Achievable

Control Technology (ALARACT) demonstration is

appropriate to address control and monitoring of potential

radioactive air emissions during these extended periods of

shutdown exceeding two days.

During periods of pre-planned shutdown of less than two days

duration, no additional monitoring or controls are required

under the ALARACT. During shutdown periods exceeding

two days, the following controls will be implemented:

Inform the Washington Department of Health (WDOH) by

telecom or email at the start of each use of this ALARACT

action or as soon as it is realized that the systems will be

shutdown for more than two days.

To provide assurance that containment of airborne

contamination is maintained during the subject periods of

shutdown, Contractor Radiological Control Technicians

(RCTs) will perform daily (during normal work days I.e., not

weekends or holidays) radiological swipe surveys on a

representative few normally accessible outer facility doors. If

an increase in removable (smearable) contamination is

detected at any of these locations during the period of

shutdown, notify the WDOH and describe containment

measures to be taken.

During the subject periods of shutdown, to avoid situations

which might encourage increased diffuse or fugitive

emissions, no activities will be conducted inside the facility

except those approved for unfiltered containment in

accordance with established Radiological Control criteria.

If the fans are not restarted within the scheduled time

discussed with WDOH, WDOH will be contacted, and

continued monitoring and/or airborne controls will be

discussed.

Continuous CDM: Records review.

3. Monitoring





shutdown.

Not

Applicable










DOE/RL-2017-02 Rev. 0

B-44




Status


Method



Required Units: 1

Add'l Description:




Required Units: 1

Add'l Description:






TOTAL BETA



61.93(b)(4)(i) & WAC 246-247-075(3)






P-296B010-001 WDOH Emission Unit ID: 340



Status


Method


Zone or Area : K-1 Filter Bldg.


Required Units : 2


Continuous

CDM: As Built Drawings (H-

2-66531 latest revision.)

Comment: During periods

when K-1 system was shut

down during change over of

K3 exhaust system to K3N

(i.e., 7/8/2016 to 9/1/2016)

emission controls were

provided by use of portable

exhausters to the Hot Cells in

the canyon per AIR 16-309.




2-66531 latest revision).

DOE/RL-2017-02 Rev. 0

B-45

Required Units : 2



when K-1 system was shut



(i.e., 7/8/2016 to 9/1/2016)







Required Units : 1

Add'l Description: 2 in parallel, operated, one fan at a time

and one in backup mode

Continuous


2-66531 latest revision).


when K1 system was shut



(i.e., 7/8/2016 to 9/1/2016)





Zone or Area : K-3 Filter Pit


Required Units : 1

Add'l Description:

Continuous

CDM: CDM: As Built

Drawings (H-2-99443 latest

revision).

Comment: The K3N

ventilation skid began

operating on 9/2/2016. From

7/8/2016 to 9/1/2016, portable


the canyon were used for

emission controls of the K3

ventilated air space per AIR

16-309. Prior to 7/8/2016,

emission control for the K3

ventilated air space was

provided by the K3 exhaust

system. As Built Drawings

(H-2-836753 latest revision).



Required Units : 1

Add'l Description:

Continuous


2-99443 latest revision)

Comment: The K3N



7/8/2016 to 9/1/2016, portable





16-309. Prior to 7/8/2016,






DOE/RL-2017-02 Rev. 0

B-46


Abatement Technology : Impingement Vanes

Required Units : 1

Add'l Description:

Continuous

CDM: As Build Drawings (H-


Comment: The K3N



7/8/2016 to 9/1/2016, portable





16-309. Prior to 7/8/2016,




system.



Required Units : 2

Add'l Description: 2 parallel flow paths, in-series

Continuous



Comment: The K3N



7/8/2016 to 9/1/2016, portable





16-309. Prior to 7/8/2016,








Required Units : 1

Add'l Description: 2 parallel paths (1 in-use, 1 backup)

Continuous



Comment: The K3N



7/8/2016 to 9/1/2016, portable





16-309. Prior to 7/8/2016,






DOE/RL-2017-02 Rev. 0

B-47





Continuous

CDM: Applicable ABCASH

data were reviewed to verify

continuous sampling.

Comment: Prior to 7/8/2016,

the 296-B-10 stack sampling

system was in operation used

to sample the combined

exhaust of the K1 and K3

ventilation systems. From

7/8/2016 to 9/1/2016, the K1

and K3 exhaust systems were

shut down for the K3 to K3N

ventilation changeover.

During this time the 296-B-10

stack sampling system was not

in operation but portable


the canyon used as emission

controls for the K3 ventilated

air space were sampled per

AIR 16-309. During the

ventilation outage, which time

the door the WESF pool cell

was left open, the K1


monitored as fugitive

emissions by ambient air

monitoring stations.


61.93(b)(4)(i) & WAC 246-247-075(2)


Appendix A, Method 2; 40 CFR 61, Appendix B, Method 114;

61.93(b)(2)(ii) ANSI N13.1

Continuous

CDM: NESHAP Quality



(CHPRC-00189, Attachment

E-6).

Comment: Prior to 7/8/2016

the 296-B-10 stack sampling

system was in operation used

to sample the combined

exhaust of the K1 and K3

ventilation systems. From

7/8/2016 to 9/1/2016 the K1

and K3 exhaust systems were

shut down for the K3 to K3N

ventilation changeover.

During this time, the 296-B-10

stack sampling system was not

in operation but portable


the canyon used as emission

controls for the K3 ventilated

air space were sampled per

AIR 16-309. During the

ventilation outage, which time

the door the WESF pool cell

was left open, the K1

DOE/RL-2017-02 Rev. 0

B-48


monitored as fugitive

emissions by ambient air


Permit: AIR 06-1014 (2012) Issue Date: 12-10-12 Effective Date: 10-05-06 Obsolete Date: 02-22-16

NOC: WESF Liquid Low Level Radioactive Liquid Removal from Tank 100





Continuous

CDM: Reviewed ABCASH

data to confirm low

concentration of radionuclides

in emissions compared with

prior years confirming off site

dose limit was not exceeded.





Modification and continuous operations of the Waste

Encapsulation and Storage Facility (WESF) liquid low level

radioactive (LLLW) stream piping. The tank TK-100 serves as

a catch tank for liquid low level radioactive waste streams

originating from WESG, condensate from the K-1 and K-3

filter pits, and the 296-B-10 stack. TK-100 is ventilated

through the WESF K-3 ventilation system and out of the 296-

B-10 Stack.

The contents of TK-100 are emptied by pumping the LLLW to

a tanker truck at the Truck Load-Out Port. In the event that

additional storage capacity is needed, a new portable

aboveground storage tank (nominal capacity of 4,000 gallons)

will be installed at the Truck Load-Out Port and vented to TK-

100 during filling operations. After filling the portable

aboveground storage tank, the tank will be disconnected from

the Truck Load-Out Port, a HEPA or NucFil filter shall be

installed, and then the tank will be moved outside for storage

until arrangements are made to dispose of the excess LLLW.

During normal operations the LLLW streams to TK-100 are

less than 0.001 curie/liter of Sr-90 and Cs-137. In the event

that the TK-100 contents are greater than or equal to 0.001

curie/liter of Sr-90 and Cs-137 during routine operations, a

WESF Ion Exchange Module will be installed at the Truck

Load-Out Port and the contents of TK-100 will be recirculated

through the WESF Ion Exchange Module until the

concentration is less than 0.001 curie/liter of Sr-90 and Cs-

137. The WESF Ion Exchange Module will be vented to TK-

100 during recirculation. Storage of the WESF Ion Exchange

Module will normally be outdoors and will vent to atmosphere

through a HEPA or NucFil filter. Use of the WESF Ion

Exchange Module will continue up to a maximum loading of

Continuous

CDM: Review of facility

operations and Project W130

work documents.

DOE/RL-2017-02 Rev. 0

B-49

20,000 curies of Sr-90 or 25,000 curies of Cs-137.

In addition, certain piping modifications will be made to the

current WESF LLLW system. They are as follows:

A. TK-50 Vault

- Remove existing Tank 50 Vault Piping.

- Remove remaining equipment (e.g., Tank 50, Heat

Exchanger, Pumps) if possible, and all other equipment and

debris in the vault.

- Install new pipe.

B. Valve Pit 225B-VP-05

- Remove 3-way valve.

- Blank off line to B Plant.

- Install new pipe elbows.

The PTE for this project as determined under WAC 246-247-

030(21)(a-e)[as specified in the application] is 3.51E-02


(Curies/year) of :

Release rates are not listed; emission release rates are

controlled by special conditions.










247-110(9)). DOE must notify the Department of any changes



significant modification to the AIR Operating Permit under

WAC 173-401-725(4). Notice will be provided according to

the particular regulation under which notification is required. If

the applicable regulation(s) does not address manner and type

of notification, DOE will provide the Department with advance

written notice by letter or electronic mail but not solely by

copies of documents.

Continuous

CDM: Review of facility

operations and Project W130

work documents.

DOE/RL-2017-02 Rev. 0

B-50

EP-325-01-S 325 Building Radiological Processing Laboratory WDOH Emission Unit ID: 361



Status


Method


Zone or Area :


Required Units : 2

Add'l Description: 2 in series

Continuous

CDM: Reviewed 2016 HEPA

Filter PM results (55490,

55500, 55510, 55440A, and

[55481, 55482, 55483,

55484]). Confirmed with the

System Engineer.

Zone or Area :


Required Units : 1

Add'l Description: Variable flow (4 in parallel, up to 3

operational) Variable flow 4 in parallel (1 minimum

operational). The system has the capability to going down to 1

fan during set back operations.

Continuous

CDM: Reviewed the 2016

Exhaust Fan PM results (PM-

41120C, 41130C, 41140C,

41150C). Confirmed with the

System Engineer.

Required Sampling: Record Sample; tritium by silica gel

Sampling Frequency: Particulates are continuously sampled

and collected every two-weeks for gross alpha and gross beta

analysis, and composited on a semi-annual basis and analyzed

isotopically. Tritium samples are collected on a monthly basis

for analysis.



Continuous

CDM: A review of

radionuclide sample collection

data confirmed that all

required samples were

collected during the reporting

period, including the start and

end dates of sample periods.

Radionuclides contributing

greater than 10% of the TEDE

are evaluated during the annual

NESHAPS inventory

assessment. These particulate

isotopes are then analyzed

isotopically on semi-annual

composites. Semi-annual

composite data was included

as part of the emission data

review. Tritium was verified

to be collected and analyzed

monthly.

Comment: Verified that gross

a and gross ß samples were

collected bi-weekly and that

isotopic analyses were

conducted semi-annually by

composite analysis. Appendix

D reports were reviewed for all

others. Tritium is collected

monthly.


61.93(b)(4)(i) & WAC 246-247-075(2) Continuous

CDM: A NESHAPs inventory

of radioactive materials is

conducted for PNNL facilities

DOE/RL-2017-02 Rev. 0

B-51


Appendix B, Method 114

on an annual basis in

accordance with PNNL-10855

Rev. 5, “Assessment of

Unabated Facility Emission

Potentials for Evaluating

Airborne Radionuclide

Monitoring Requirements at

PNNL-2010." The “Pacific

Northwest National

Laboratory Effluent

Management Quality

Assurance Plan” (EM-QA-01)

specifies QA requirements.

The “Airborne Radionuclide

Emission Sample Analysis

Statement of Work,” Rev. 9

(March 2013), specifies

radionuclide analysis methods.

The "Memorandum of

Agreement Pacific Northwest

National Laboratory EW&T-

F&O-RMI,” Rev. 3, specifies

methods for determining stack

velocity, volumetric exhaust

rate, and cyclonic flow

determinations.





Status


Method


Zone or Area :

Abatement Technology : Fiberglass Filter

Required Units : 1

Add'l Description: (Deep Bed Fiberglass filter)

Continuous



(HVAC), Drawing H-2-58546-

001, Rev. 3 and H-2-58540-

001, Rev. 2.

Zone or Area :


Required Units : 2


Continuous



(HVAC) Drawing H-2-75975-

001, Rev. 2 and H-2-75976-

001, Rev. 3.

Zone or Area :


Required Units : 2

Add'l Description: In parallel, one operating, one back-up

Continuous

CDM: I&E Flow Diagram H-

2-825908; Heating &

Ventilation Air Flow &

Control Diagram (HVAC), H-

2-75975 and H-2-75976

DOE/RL-2017-02 Rev. 0

B-52



Radionuclide Requiring Measurement: 239/240Pu, 241Am

Intermittent

CDM: CDM: ABCASH.

ALARCT 28.1 from 3/08/2016

to 07/25/2016.


61.93(b)(4)(i) & WAC 246-247-075(2)


Appendix A, Method 2; 40 CFR 61, Appendix B, Method 114

61.93(b)(2)(ii) ANSI N13.1

Continuous

CDM: CHPRC-00189,

CHPRC Environmental

Quality Assurance Program

Plan (EQAPP)- Appendix E -

NESHAP; Radionuclides

QAPjP.


























Not

Applicable










2. Controls













Intermittent

CDM: Records review.

Comment: On 05/11/2016, the

PUREX Facility had missed an

ALARACT 28.1 survey.

DOE/RL-2017-02 Rev. 0

B-53




















discussed.

3. Monitoring





shutdown.

Not

Applicable













Permit: AIR 06-1026 (2012) Issue Date: 10-05-06 Effective Date: 02-23-12 Obsolete Date: 04-26-16 NOC: Reactivation of PUREX Storage Tunnel Number 2



DOE/RL-2017-02 Rev. 0

B-54

P-437MN&ST-001 WDOH Emission Unit ID: 385



Status


Method


Zone or Area :


Required Units : 2

Add'l Description: In parallel, serves all MN&ST,

intermittent use

Continuous CDM: Verified by discussion

with the cognizant engineer.

Zone or Area : Decon 1 & 2 Activities


Required Units : 1

Add'l Description: 2 parallel flow paths, minimum of one

HEPA operational

Not

Applicable

CDM: HEPA filters were

removed as abatement

technology in revised license

AIR 15-1103 which was

approved on 11/10/15.

Zone or Area : Liquid Radioactive Waste Loadout Facility

Ventilation


Required Units : 1

Add'l Description:

Not

Applicable

CDM: Prefilter was removed

as abatement technology in

revised license AIR 15-1103

which was approved on

11/10/15.

Zone or Area : Liquid Radioactive Waste Loadout Facility

Ventilation


Required Units : 1

Add'l Description:

Not

Applicable






Zone or Area : Radiological Waste Tank Room Ventilation


Required Units : 1

Add'l Description:

Not

Applicable





11/10/15.

Zone or Area : Radiological Waste Tank Room Ventilation


Required Units : 1

Add'l Description:

Not

Applicable






Zone or Area : Waste Tank 1 & 2 Vents


Required Units : 1

Add'l Description: 1 stage with 2 parallel flowpaths

Not

Applicable






Zone or Area : Contaminated Equipment Repair Area


Required Units : 1

Add'l Description:

Not

Applicable





11/10/15.

DOE/RL-2017-02 Rev. 0

B-55

Zone or Area : Contaminated Equipment Repair Area


Required Units : 1

Add'l Description: 2 in parallel

Not

Applicable







Sampling Frequency: 4 week sample/year


TOTAL BETA

Continuous

CDM: ABCASH Review

Comment: Samples sent to the

laboratory for the required

analysis.


(b)(4)(i) & WAC 246-247-075(3)



Continuous

CDM: Review of the MSA

contract with GEL Laboratory,

"Offsite Analytical Services

for MSA Stack Samples -

Effluent Monitoring Program."


P-FFTFRESB-001 WDOH Emission Unit ID: 395

Page in AOP: EU0395-001 EMISSION UNIT DID NOT OPERATE DURING CY 2016 SEE TABLE 2

P-FFTFHTTR-001 WDOH Emission Unit ID: 396


P-FFTFCBEX-001 WDOH Emission Unit ID: 397



Status


Method


Zone or Area : Bldg 405 Process Operations


Required Units : 2

Add'l Description: In parallel (intermittent use)

Continuous CDM: Verified with the

system's technical authority.

Zone or Area : Access Control Area Process


Required Units : 1

Add'l Description: Intermittent use

Continuous CDM: Verified with the

system's technical authority.

Required Sampling: Radionuclide emissions will be

estimated annually using WAC 246-247-030(21)(a) Continuous

CDM: Calculations are

performed by MSA and

DOE/RL-2017-02 Rev. 0

B-56


Status


Method

calculation in lieu of monitoring.

Sampling Frequency: Annual (calculation)


TOTAL BETA Tritium

reported in the annual

Radionuclide Air Emissions

Report for the Hanford Site.


61.93(b)(4)(i) & WAC 246-247-075(3)

Permit Monitoring and Testing Procedure: Engineering

calculations based on WAC 246-247-030(21)(a)

Continuous

CDM: Calculations are

performed by MSA and

reported in the annual


Report for the Hanford Site.


Sodium Storage Facility WDOH Emission Unit ID: 398



Permit: AIR 12-321 Issue Date: 03-06-12 Effective Date: 02-23-12 NOC: Construction and Operation of Sodium Storage Facility



P-437-002 WDOH Emission Unit ID: 399



Status


Method


No active Abatement Controls in the AOP for this certification period.




TOTAL BETA

Continuous

CDM: ABCASH review.

Comment: Samples sent to the

laboratory for the required

analysis.


(b)(4)(i) & WAC 246-247-075(3)



Continuous

CDM: Review of the MSA

contract with GEL Laboratory,

"Offsite Analytical Services

for MSA Stack Samples -

Effluent Monitoring Program."


DOE/RL-2017-02 Rev. 0

B-57

P-296B001-001 WDOH Emission Unit ID: 402



Status


Method


Zone or Area :


Required Units : 2

Add'l Description: Two trains, one bank in each train

Continuous



(HVAC), H-2-828927

Engineering Drawing and

Field Walkdowns.



of prefilter

Zone or Area :


Required Units : 4

Add'l Description: Two trains, 2 banks in each train

Continuous



(HVAC), H-2-828927


Field Walkdowns.



of two trains of two banks of

HEPA filters

Zone or Area :


Required Units : 2

Add'l Description: Only one fan operates at a time.

Continuous



(HVAC), H-2-828927


Field Walkdowns.



of two fans.



Radionuclide Requiring Measurement: 137Cs, 90Sr

Continuous

CDM: ABCASH

Comment: Initiated

ALARACT 28.1 on 08/31/16

due to high dP on the

Prefilters.


61.93(b)(4)(i) & WAC 246-247-075(2)



Continuous

CDM: NESHAP Quality




Comment: Initiated

ALARACT 28.1 on 08/31/16


Prefilters.

DOE/RL-2017-02 Rev. 0

B-58

Permit: AIR 06-1010 (2012) Issue Date: 03-06-12 Effective Date: 02-23-12

NOC: B Plant Modification of the Ventilation System (Emission Point: 296-B-1)





Continuous



for CY 2016 to verify total


NOC limit

Comment: Initiated

ALARACT 28.1 on 08/31/16


Prefilters.





Operate the installed ventilation systems and conduct S&M

activities.

Continuous

CDM: Reviewed work

management (Job Control

System [JCS]) records .

Comment: Initiated

ALARACT 28.1 on 08/31/16


Prefilters.


030(21)(a-e) [as specified in the application] is 7.87E+01


(Curies/year) of:

Am-241 2.56E-01 Liquid/Particulate Solid

WAC 246-247-030(21)(b)

Cs-137 8.40E+02 Liquid/Particulate Solid

WAC 246-247-030(21)(b)

Pu-238 3.60E-02 Liquid/Particulate Solid

WAC 246-247-030(21)(b)

Pu-239/240 3.84E+00 Liquid/Particulate Solid

WAC 246-247-030(21)(b)

Sb-125 Liquid/Particulate Solid

WAC 246-247-030(21)(b)

Contributes less than 0.1 mrem/yr to the MEI, and represents

less than 10% of the unabated PTE and represents less than

25% of the abated dose.

Y-90 Liquid/Particulate Solid

WAC 246-247-030(21)(b)






Am-241 Cs-137 Pu-238 Pu-239/240

Continuous

CDM: The APQ Values listed

in the NOC application have

not changed.

Comment: Development of

PTE values is historical and

approved by WDOH.

DOE/RL-2017-02 Rev. 0

B-59

Sb-125 Sr-90 Y-90




















The new HEPA filters must be fully compatible with ANSI

509/510 standards. Continuous

CDM: Field interview

Comment: See work package

SW-13-07687/W for filter

replacement. Initiated

ALARACT 28.1 on 08/31/16


Prefilters.
























Not

Applicable










DOE/RL-2017-02 Rev. 0

B-60



2. Controls
































discussed.

Continuous CDM: Field Interviews and

records review.

3. Monitoring





shutdown.

Not

Applicable










DOE/RL-2017-02 Rev. 0

B-61

EP-331-01-V Life Sciences Laboratory I WDOH Emission Unit ID : 412

Page in AOP : EU0412-001


Status


Method


Zone or Area :


Required Units : 1

Add'l Description: Labs and hoods and glove boxes.

Continuous

CDM: Reviewed 2016 HEPA

Filter PM Results (PM-55020)

and confirmed with Building

Engineer.

Zone or Area :


Required Units : 1

Add'l Description: 1 of 3 fans operating

Continuous

CDM: Reviewed 2016

Exhaust Fan PM Results

(42160, 42170, and 42180) and

confirmed with Building

Engineer.




that could contribute greater than 10 percent of the potential-

to-emit TEDE

Continuous

CDM: A review of

radionuclide sample collection

data confirmed that all


collected during the reporting

period, including the start and

end dates of sample periods.

Radionuclides contributing

greater than 10% for the

potential-to-emit (PTE) are

evaluated during the annual

NESHAPS inventory

assessment. These isotopes

are then analyzed isotopically

on semi-annual composites.

Semi-annual composite data

was included as part of the

emission data review.

Comment: Verified that gross

a and gross ß samples were

collected bi-weekly and that

isotopic analysis were

conducted semi-annually by

composite analysis. Appendix

D reports were reviewed for all

others.


61.93(b)(4)(i) & WAC 246-247-075(2)



Continuous

CDM: A NESHAP inventory










DOE/RL-2017-02 Rev. 0

B-62

PNNL-2010.” The “Pacific

Northwest National Laboratory

Effluent Management Quality

Assurance Plan” (EM-QA-01),

specifies QA requirements.

The “Airborne Radionuclide

Emission Sample Analysis

Statement of Work” Rev. 9

(March 2013) specifies

radionuclide analysis methods.


NOC: Life Sciences Laboratory - 1 (331 Building), Revision 2





Continuous

CDM: The radionuclide air

emissions data for the calendar

year (CY) 2016 was reviewed

to verify the abated emissions

from the 331 Building were

below the NOC limits.



that constitute a "modification" to the emission unit, as

defined in WAC 246-247- 030(16), may be conducted.

The mission of the 331 Building is to conduct fundamental

science and to develop environmental technology. Research

activities conducted in the 331 Building support the Hanford

Site environmental mission and other key DOE missions of

national and international importance. Research activities

performed within the 331 Building include the use of

radioactive materials. Laboratory processes are conducted

"continuously" (i.e., year-round, during normal business,

swing-shift, night-shift, and weekend hours). The 331

Building provides research capabilities to study the

interactions of chemicals and radionuclides with plants,

animals, and microorganisms and the fate of chemicals and

radionuclides in the environment. The building also has

research capabilities for conducting studies on the uptake and

transformation effects of radioactive material and chemicals in

soils, plants, animals, and microorganisms.

The inventory of radioactive material in the building can

include gram quantities of fissionable materials and up to curie

quantities of other radionuclides. The laboratory activities

conducted in the 331 Building include:

-Experimental studies with molecular and cellular processes.

-Studies to determine precise cross-species and low-dose

extrapolation of health risks and to understand disease

mechanisms.

-Basic and applied research concerning microorganisms

Continuous

CDM: Under the PNNL HDI

system, each new research

project is required to be

reviewed via the Electronic

Prep & Risk (EPR) assessment

process (Procedure EPRP-

ECR-01 Rev 9.01.

Environmental Compliance

Representative Administrative

Procedure for Reviewing

Electronic Prep & Risk

Forms). The reviews are

recorded in the EPR database.

Projects with potential air

emissions are reviewed by

Effluent Management (EM)

under the HDI Airborne

Emission Work Control.

DOE/RL-2017-02 Rev. 0

B-63

and/or their processes in various environments.

-Subsurface microbiology including the physiology and

ecology of subsurface microorganisms, degradation of organic

contaminants and bioremediation, enzymatic reductions of

metals, and biogeochemical cycling of nutrients.

-Studies investigating macromolecular structure and dynamics

and consequences of observables on molecular function.

-Development of instrumentation and analytical methods.

-Development of comprehensive environmental monitoring

programs.

-Development of advanced scientific and technological

solutions for long-term stewardship of waste sites.

-Waste management activities including satellite accumulation

areas and <90 day storage areas.

-Characterizing and monitoring aquatic and terrestrial

ecosystems including the development and monitoring of new

technologies and methods.

-Studies of impacts of water use practices on fisheries and

wildlife and the response of the ecosystems to engineered

structures and natural and man-induced stresses.

-Activities involving nuclear process engineering,

radiomaterials characterization, and radiochemical separations

and processing.

-Studies of the health effects of chemical and radiation

exposure on animals (rodents) and in cells grown in culture.

-Examining the uptake and transformation effects of

radionuclides in soils, plants, animals and microorganisms.

-Studies with radioactive tracer materials in biological and

non-biologic systems.

-Research to promote the understanding of the chemical,

biological, and biogeochemical processes that govern the

mobility, transportation, and degradation of a range of

inorganic, radionuclide, and organic contaminants in soils,

sediments, and ground water systems.

-Measurements of exposures to physical, radiological, and

chemical agents.

-Developing technology for the separation, purification,

production, and delivery of radioisotopes (e.g., for medical

purposes, and standards development).

-Research and laboratory activities that may include processes

where the temperature may be equal to or exceed 100°C.

-Research activities involving mixed activation products

(MAP) and mixed fission products (MFP).

-Laboratory setup projects involving fume hood

removals/upgrades and ductwork tie-in.

-Microscopic and spectroscopic characterization of the mass

transfer of radioactive material in soils and sediments under

the influence of biogeochemical reactions.

-Investigate the sorption and desorption processes of

radioactive material in soils and sediments.

-Develop models to predict the geochemical retardation of

radioactive material in sediments.

-Activities involving corrosion and stress-corrosion cracking

studies of irradiated specimens of metals and other materials.

-Studies investigating structural properties, such as tensile and

compression strengths, of irradiated materials.

DOE/RL-2017-02 Rev. 0

B-64

-Activities involving corrosion and stress-corrosion studies of

autoclaved materials.




(Curies/year) of:

Ac-225 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)












Ag-108 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)




Ag-108 m | Liquid/Particulate Solid | WAC 246-247-

030(21)(a)




Ag-109 m | Liquid/Particulate Solid - WAC 246-247-

030(21)(a)








Ag-110 m | Liquid/Particulate Solid | WAC 246-247-

030(21)(a)








Continuous






Rev. 5, "Assessment of





PNNL-2010." Reviewed the

2016 NESHAPs radionuclide

inventory assessment results to

verify compliance.

DOE/RL-2017-02 Rev. 0

B-70




25% of the abated dose. Cs-137 unit dose factor used as a

worst case assumption.

Cd-111 m | Liquid/Particulate Solid | WAC 246-247-

030(21)(a)









030(21)(a)









030(21)(a)









030(21)(a)




Ce-139 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)





Contributes less than 0.1 mrem/yr to the Mel, and represents




DOE/RL-2017-02 Rev. 0

B-81



Kr-81 | Gas | WAC 246-247-030(21)(a)




Kr-81 m | Gas | WAC 246-247-030(21)(a)




Kr-83 m | Gas | WAC 246-247-030(21)(a)




Kr-85 | Gas | WAC 246-247-030(21)(a)




Kr-85 m | Gas | WAC 246-247-030(21)(a)




Kr-87 | Gas | WAC 246-247-030(21)(a)




Kr-88 | Gas | WAC 246-247-030(21)(a)




Kr-89 | Gas | WAC 246-247-030(21)(a)




Kr-90 | Gas | WAC 246-247-030(21)(a)




La-137 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)







DOE/RL-2017-02 Rev. 0

B-87
















Pd-103 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)












Pm-143 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)


















DOE/RL-2017-02 Rev. 0

B-88









Pm-148 m | Liquid/Particulate Solid | WAC 246-247-

030(21)(a)












Po-208 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)
























DOE/RL-2017-02 Rev. 0

B-95



























Sn-113 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)




Sn-117 m | Liquid/Particulate Solid | WAC 246-247-

030(21)(a)





030(21)(a)









DOE/RL-2017-02 Rev. 0

B-98
























Te-121 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)




Te-121 m | Liquid/Particulate Solid | WAC 246-247-

030(21)(a)









030(21)(a)





030(21)(a)




DOE/RL-2017-02 Rev. 0

B-99






030(21)(a)









030(21)(a)









030(21)(a)













030(21)(a)








Th-227 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)

DOE/RL-2017-02 Rev. 0

B-100
































Ti-44 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)














DOE/RL-2017-02 Rev. 0

B-102


























V-48 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)








W-181 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)












DOE/RL-2017-02 Rev. 0

B-103





Xe-122 | Gas | WAC 246-247-030(21)(a)




Xe-123 | Gas | WAC 246-247-030(21)(a)




Xe-125 | Gas | WAC 246-247-030(21)(a)




Xe-127 | Gas | WAC 246-247-030(21)(a)




Xe-127 m | Gas | WAC 246-247-030(21)(a)




Xe-129 m | Gas | WAC 246-247-030(21)(a)




Xe-131 m | Gas | WAC 246-247-030(21)(a)




Xe-133 | Gas | WAC 246-247-030(21)(a)




Xe-133 m | Gas | WAC 246-247-030(21)(a)




Xe-135 | Gas | WAC 246-247-030(21)(a)




DOE/RL-2017-02 Rev. 0

B-106


















Ac-225 Ac-227 Ac-228 Ag-108 m Ag-108

Ag-109 m Ag-110 m Ag-110 Ag-111 Al-26

Al-28 Am-241 Am-242 m Am-242 Am-243

Am-245 Am-246 Ar-37 Ar-39 Ar-41

Ar-42 As-74 As-76 As-77 At-217

Au-195 Au-198 Au-198 m Ba-131 Ba-133

Ba-133 m Ba-137 m Ba-139 Ba-140 Ba-141

Ba-142 Ba-143 Be-10 Be-7 Bi-207

Bi-208 Bi-210 m Bi-210 Bi-211 Bi-212

Bi-213 Bi-214 Bk-249 Bk-250 Br-82

Br-82 m Br-83 Br-84 Br-84 m Br-85

C-11 C-14 C-15 Ca-41 Ca-45

Ca-47 Cd-107 Cd-109 Cd-111 m Cd-113 m

Cd-113 Cd-115 m Cd-115 Cd-117 Cd-117 m

Ce-139 Ce-141 Ce-142 Ce-143 Ce-144

Cf-249 Cf-250 Cf-251 Cf-252 Cl-36

Cm-241 Cm-242 Cm-243 Cm-244 Cm-245

Cm-246 Cm-247 Cm-248 Co-56 Co-57

Co-58 Co-60 Co-60 m Cr-49 Cr-51

Cr-55 Cs-131 Cs-132 Cs-134 Cs-134 m

Cs-135 Cs-136 Cs-137 Cs-138 Cs-139

Cs-140 Cs-141 Cu-64 Cu-66 Dy-165

Dy-169 Er-169 Er-171 Es-254 Eu-150

Eu-152 Eu-152 m Eu-154 Eu-155 Eu-156

Eu-157 F-18 Fe-55 Fe-59 Fr-221

Fr-223 Ga-67 Ga-68 Ga-70 Ga-72

Gd-148 Gd-149 Gd-151 Gd-152 Gd-153

Ge-68 Ge-71 Ge-71 m Ge-75 Ge-77

Ge-77 m H-3 Hf-175 Hf-178 Hf-178 m

Hf-181 Hf-182 Hg-203 Ho-163 Ho-166

Ho-166 m I-122 I-123 I-125 I-126

I-128 I-129 I-130 I-130 m I-131

I-131 I-132 I-132 m I-133 I-133 m

I-134 I-134 m I-135 In-106 In-111

In-113 m In-114 m In-114 In-115 In-115 m

DOE/RL-2017-02 Rev. 0

B-107

In-116 In-116 m In-117 In-117 m Ir-192

K-40 K-42 Kr-81 Kr-81 m Kr-83 m

Kr-85 Kr-85 m Kr-87 Kr-88 Kr-89

Kr-90 La-137 La-138 La-140 La-141

La-142 La-144 Lu-177 Mg-27 Mg-28

Mn-52 Mn-54 Mn-56 Mo-103 Mo-104

Mo-105 Mo-93 Mo-99 N-13 Na-22

Na-24 Na-24 m Nb-100 Nb-101 Nb-103

Nb-91 Nb-91 m Nb-92 Nb-93 m Nb-94

Nb-95 Nb-95 m Nb-97 Nb-97 m Nb-98

Nd-144 Nd-147 Ni-56 Ni-59 Ni-63

Ni-65 Np-235 Np-236 Np-237 Np-238

Np-239 Np-240 Np-240 m O-15 O-19

Os-191 P-32 P-33 Pa-231 Pa-233

Pa-234 Pa-234 m Pb-209 Pb-210 Pb-211

Pb-212 Pb-214 Pd-103 Pd-107 Pd-109

Pm-143 Pm-144 Pm-145 Pm-146 Pm-147

Pm-148 m Pm-148 Pm-149 Pm-151 Po-208

Po-209 Po-210 Po-211 Po-212 Po-213

Po-214 Po-215 Po-216 Po-218 Pr-143

Pr-144 Pr-144 m Pu-234 Pu-236 Pu-237

Pu-238 Pu-239 Pu-240 Pu-241 Pu-242

Pu-243 Pu-244 Pu-246 Ra-223 Ra-224

Ra-225 Ra-226 Ra-228 Rb-81 Rb-83

Rb-84 Rb-86 Rb-87 Rb-88 Rb-89

Rb-90 Rb-90 m Re-186 Re-187 Re-188

Rh-102 Rh-102 Rh-103 Rh-103 m Rh-104

Rh-105 Rh-105 m Rh-106 Rn-219 Rn-220

Rn-222 Rn-224 Ru-103 Ru-105 Ru-106

Ru-97 S-35 Sb-122 Sb-124 Sb-125

Sb-126 Sb-126 m Sb-127 Sb-129 Sc-46

Sc-47 Se-75 Se-79 Se-79 m Si-31

Sm-145 Sm-146 Sm-147 Sm-148 Sm-151

Sm-153 Sm-157 Sn-113 Sn-117 m Sn-119 m

Sn-121 m Sn-121 Sn-123 Sn-125 Sn-126

Sr-85 Sr-87 m Sr-89 Sr-90 Sr-91

Sr-92 Ta-179 Ta-180 Ta-182 Ta-182 m

Ta-183 Tb-157 Tb-158 Tb-160 Tb-161

Tc-101 Tc-103 Tc-106 Tc-95 m Tc-97

Tc-97 m Tc-98 Tc-99 Tc-99 m Te-121 m

Te-121 Te-123 Te-123 m Te-125 m Te-127 m

Te-127 Te-129 m Te-129 Te-131 Te-131 m

Te-132 Te-133 Te-133 m Te-134 Th-227

Th-228 Th-229 Th-230 Th-231 Th-232

Th-233 Th-234 Ti-44 Ti-45 Ti-51

Tl-201 Tl-204 Tl-206 Tl-207 Tl-208

Tl-209 Tm-168 Tm-170 Tm-171 U-232

U-233 U-234 U-235 U-236 U-237

U-238 U-239 U-240 V-48 V-49

W-181 W-185 W-187 W-188 Xe-122

Xe-123 Xe-125 Xe-127 Xe-127 m Xe-129 m

Xe-131 m Xe-133 Xe-133 m Xe-135 Xe-135 m

Xe-137 Xe-138 Xe-139 Y-88 Y-90

Y-90 m Y-91 Y-91 m Y-92 Y-93

Yb-164 Yb-169 Yb-175 Yb-177 Zn-65

Zn-69 Zn-69 m Zr-100 Zr-88 Zr-89

DOE/RL-2017-02 Rev. 0

B-108

Zr-93 Zr-95 Zr-97 Zr-98 Zr-99









than 25% of the TEDE to the MEI after controls. WAC 246-

247-110(9). DOE must notify the Department of any changes










Total design flow through each HEPA filter bank shall not

exceed the maximum rated flow rate for the individual HEPA

filters multiplied by the number of filters. This does not limit

the design flow rate of the stack, just that of the filters.

Continuous

CDM: Confirmed that the

number of filters times the

filter rating is greater than the

actual exhaust.

To account for all radioisotopes that may be affected by a

process in which the temperature may be equal to or exceed

100 degrees Celsius, a release factor of one is applied to a

gaseous form of Am-241 and Cs-137.

Not

Applicable

CDM: This is a statement of

fact, as there is no action to be

taken by the permittee. This

condition conveys information

stated as a footnote to emission

estimates.

P-296H212 001 WDOH Emission Unit ID: 435



Status


Method


Zone or Area :


Required Units : 2

Add'l Description: double stage, operates in parallel, one

HEPA at a time and one in backup mode

Continuous CDM: As Built Drawings (H-

2-129588) and walk down.

Zone or Area :


Required Units : 2

Add'l Description: operates in parallel, one fan at a time and

one in backup mode

Continuous CDM: As Built Drawings (H-

2-129588) and walk down.

DOE/RL-2017-02 Rev. 0

B-109

Required Sampling: The record filter is replaced monthly

and analyzed quarterly (either destructive or non-destructive

technique) using a gamma spectrometer calibrated to Cs-137.



that could contribute greater than 10% of the potential-to-emit

TEDE.


data.


61.93(b)(4)(i) & WAC 246-247-075(2)



Continuous

CDM: NESHAP Quality

Assurance Plan for

Radioactive Emissions

(CHPRC-00189, Appendix E,

Attachment E-7).





Status


Method


Zone or Area :


Required Units : 1

Add'l Description:



Zone or Area :


Required Units : 2




Zone or Area :


Required Units : 1

Add'l Description:



Required Sampling: NDA

Sampling Frequency: 1 every 2 years


TOTAL BETA

Continuous

CDM: NDA and field

interviews.

Comment: NDA performed in

2015.


61.93(b)(4)(i) & WAC 246-247-075(3)






DOE/RL-2017-02 Rev. 0

B-110

J-CWC 001 WDOH Emission Unit ID: 439



Status


Method



Required Sampling: Environment Sampling; Ambient air

monitors N-449, N-457, N-964, and N-433.

Sampling Frequency: Near field ambient monitoring

program as specified in the Conditions and Limitations.

Continuous


procedures in place to operate

and collect samples and review

ABCASH data to verify


collected from the near-facility


Radionuclides that contribute

greater than 10% of the PTE

TEDE are reported in the CY

2016 Hanford Site


Report.


61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous CDM: MSA near-facility

monitoring QA programs.


NOC: Central Waste Complex (CWC) Operations


I) The total abated emission limit for this Notice of

Construction is limited to l.57E-05 mrem/year to the

Maximally Exposed Individual (WAC 246-247-040(5)).

Continuous

CDM: Verified APQ is less

than 4.69E+06 DE-Ci/yr and

unabated PTE is less than

9.38E-03 DE-Ci/yr per the

NOCA Table 1. Unabated and

Abated CWC Container

Fugitive Emissions, Current

License.




in WAC 246-247-030(16), may be conducted

The mission of the CWC is the storage of mixed and/or

radioactive waste that is generated on or off the Hanford Site.

There could be up to 88,500 emission units (i.e., containers)

within CWC. CWC manages many categories of radioactive

materials such as low-level waste (LLW), transuranic (TRU)

waste, TRU mixed waste and low-level mixed waste (LLMW)

in contact-handled (CH) containers.

Continuous

CDM: There were no

additional activities or

variations on the approved

activities that would constitute

a "modification" to the

emissions unit, as defined in

WAC 246-247-030(16) during

the reporting period. Facility


activities at CWC are as


DOE/RL-2017-02 Rev. 0

B-111

TRU waste is waste that contains at least 100nCi of alpha

emitting transuranic constituents with half-lives greater than 20

years. LLW is not TRU waste. TRU waste and LLW are not

spent nuclear fuel, high level waste or byproduct material. CH

containers are packages are defined having surface dose rates

less than 200 mrem/hr while remote handled (RH) containers

are packages with dose rates of greater than 200 mrem/hr. RH

containers may be stored at the CWC in accordance with the


The LLW typically contains rags, paper, rubber gloves,

disposal supplies, tools, industrial waste (e.g., failed

equipment), and solidified waste that are contaminated with

radioactive material. TRU and TRU-mixed waste typically

contains rags, paper, rubber gloves, disposable supplies, tools,

industrial waste (e.g., failed equipment), solidified process

byproducts, and laboratory wastes that are contaminated with

TRU material. Both TRU and LLW may contain non-

radioactive constituents that could be managed as RCRA

and/or TSCA waste.

The TRU waste accepted by CWC may contain varying

concentration of TRU radionuclides and limited amounts of

non-TRU radionuclides. With some exceptions all based on

safety analysis, the TRU content of waste containers is

generally limited to fifty three (53) Pu 239/Pu-240 dose

equivalent curies (DE-Ci), where the DE-Ci is derived by

multiplying the isotopic composition (i.e., weight fractions of

the various TRU isotopes) by the specific activities of each

isotope, and then converting that number with correction

factors taken from the Hanford Site Solid Waste Acceptance

Criteria. The DE-Ci unit is designed to control inhalation dose

impacts independent of radionuclide type. The radionuclides

Pu-239 and Pu-240 are considered equivalent and are

combined for calculation purposes and are used to track the

unabated emissions. The TRU waste containers are generally

equipped with a pressure relief vent device such as the

NucFil® filter. This filter allows the release of gases that may

be produced as a result of radiolysis inside the container, while

preventing release of particulate matter.

The waste storage areas and facilities at CWC include the

following:

-Shipping and Receiving Area

-Outdoor Waste Storage Areas

-Flammable & Alkali Metal Waste Storage Modules

-Mixed and/or Radioactive Waste Storage Buildings

-RO/RO containers

As needed, the operational activity at CWC includes

overpacking waste containers found to be in unsatisfactory

condition. Additionally, there may be future instances where

potential radiological contamination associated with the outer

DOE/RL-2017-02 Rev. 0

B-112

surfaces of containers and soils needs to be managed. As

discussed in AIR 13-602, Central Waste Complex (CWC) Box

231ZDR-11 As Low As Reasonably Achievable. Control

Technology (ALARACT) Approval, a general purpose burial

box dripped contaminated water to the soil. Following

discovery, the contaminated water was contained in collection

containers that are emptied periodically. The ALARACT

described actions to be taken to place the container in a

configuration that would allow installation of a cover, move

the container, and provide for the management of contaminated

soil and materials disturbed during the activity (as needed).

The ALARACT also identified associated radiological

controls, monitoring, and records/documentation. To address

potential radiological releases from a container, the cleanup of

containers, buildings, equipment, and/or contaminated soil

would be performed in a manner that is protective of workers

and the environment. To address potential future releases from

a CWC waste container, conditions 10 through 14 identify the

controls that would be implemented to remediate the

radiological release.


030(2l)(a-e) [as specified in the application] is 3.13E- 02


(Curies/year) of:

Am - 244 Liquid/Particulate Solid WAC 246-247-030(21)(e)




C - 14 Liquid/Particulate Solid WAC 246-247-030(21)(e)




Cm - 243 Liquid/Particulate Solid WAC 246-247-030(21)(e)




Cm - 244 Liquid/Particulate Solid WAC 246-247-030(21)(e)




Co - 60 Liquid/Particulate Solid WAC 246-247-030(21)(e)




Cs - 137 Liquid/Particulate Solid WAC 246-247-030(21)(e)




DE - 0 Liquid/Particulate Solid WAC 246-247-030(21)(e)

Continuous

CDM: Verified APQ is less

than 4.69E+06 DE-Ci/yr and

unabated PTE is less than

9.38E-03 DE-Ci/yr per the

NOCA Table 1. Unabated and

Abated CWC Container

Fugitive Emissions, Current

License.

DOE/RL-2017-02 Rev. 0

B-113

Alpha release rate is assumed to be Pu239/249. Other

radionuclides may be encountered and are approves so long as

they are conservatively represented by the total alpha

constituents.

Eu - 154 Liquid/Particulate Solid WAC 246-247-030(21)(e)




Eu - 155 Liquid/Particulate Solid WAC 246-247-030(21)(e)




Ni - 59 Liquid/Particulate Solid WAC 246-247-030(21)(e)




Ni - 63 Liquid/Particulate Solid WAC 246-247-030(21)(e)




Pu - 238 Liquid/Particulate Solid WAC 246-247-030(21)(e)




Pu - 241 Liquid/Particulate Solid WAC 246-247-030(21)(e)




Pu -242 Liquid/Particulate Solid WAC 246-247-030(21)(e)




Se -79 Liquid/Particulate Solid WAC 246-247-030(21)(e)




Sm - 151 Liquid/Particulate Solid WAC 246-247-030(21)(e)




Sn - 126 Liquid/Particulate Solid WAC 246-247-030(21)(e)




Sr - 90 Liquid/Particulate Solid WAC 246-247-030(21)(e)

DOE/RL-2017-02 Rev. 0

B-114




Tc - 994 Liquid/Particulate Solid WAC 246-247-030(21)(e)




U - 233 Liquid/Particulate Solid WAC 246-247-030(21)(e)




















Zr - 93 Liquid/Particulate Solid WAC 246-247-030(21)(e)






Am-241 C-14 Cm-243 Cm-244 Co-60

Cs-137 Pu-238 Eu-154 Pu-239 Eu-155

Pu-240 Ni-59 Pu-241 Ni-63 Pu-242

Se-79 U-233 U-234 U-235 U-238

U-236 Sm-151 Sn-126 Sr-90 Tc-99

Zr-93




Department of a "modification" to the emission unit, as defined

in WAC 246-247-030(16). DOE must notify the Department of

any changes to a NESHAP major emission unit when a specific

isotope is newly identified as contributing greater than 10% of

DOE/RL-2017-02 Rev. 0

B-115

the potential TEDE to the MEI, or greater than 25% of the

TEDE to the MEI after controls. (WAC 246-247-110(9)) DOE

must notify the Department of any changes to potential release

rates as required by state or federal regulations including

changes that would constitute a significant modification to the

Air Operating Permit under WAC 173-401-725(4). Notice will

be provided according to the particular regulation under which

notification is required. If the applicable regulation(s) does not

address manner and type of notification, DOE will provide the

Department with advance written notice by letter or electronic

mail but not solely by copies of documents.

WDOH NOTIFICATION- Contamination Levels

WDOH will be notified when the following contamination

levels are found:

-Direct contamination on soil, container, or adjacent surfaces is

detected greater than 500,000 dpm/100 cm^2 alpha and/or 1

rad/hr/100 cm^2 beta gamma are encountered.

-Removable/transferrable contamination levels above 2,000

dpm/100 cm^2 alpha or 100,000 dpm/100cm^2 beta gamma

are encountered. (WAC 246-247-040((5))

Continuous

CDM: No direct contamination

on soil, container, or adjacent

surfaces greater than 500,000

disintegrations per minute

(dpm)/100 cm^2 alpha and/or 1

rad/hr/100 cm^2 beta gamma

was detected.

WDOH NOTIFICATION & IMPLEMENTATION OF

CONTROLS-Contamination Levels

Removable/transferrable contamination will be maintained less

than a maximum level of 2,200,000 dpm/100 cm^2 alpha

and/or less than 4 rad/hr/100 cm^2 beta gamma. Direct

contamination levels will be maintained less than a maximum

of 20,000dpm/100 dpm^2 alpha, and or 1,000,000

dpm/100cm^2 beta gamma. Exceeding these contamination

limits requires work to stop and WDOH notification. The

following appropriate controls must then be implemented prior

to resuming work:

-Contamination will be secured or contained prior to

continuing work. -Appropriate controls such as water,

fixatives, covers, containment tents, or windscreens shall be

applied.

-Soil shall be wetted prior to removal if not already damp.

-If soil is to be removed such as during excavation activities, it

would be fixed or covered until excavated or otherwise

dispositioned.

-General work place air monitoring shall be performed during

removal activities.

-Removed soil or vegetation not already in containers will be

covered with plastic, fixative applied at the end of each shift,

and/or the material will be covered as necessary to prevent

airborne dust particles.

Continuous



CWC are as described in the

NOC. Additional

environmental controls are

placed in work packages and

RWPs on a case-by-case basis.

ABATEMENT-Drum Vents TRU drum and box waste

containers shall be equipped with passive vents, either vent

clips, NucFil® filters, or similar devices. Vent clips will be

replaced with NucFil® filters or similar devices as containers

are prepared for shipment either to the Waste Isolation Pilot

Plant (WIPP) or transferred to other locations onsite. (WAC

246-247- 040(5))

Continuous




NOC. HNF-EP-006 Hanford

Site Solid Waste Acceptance

Criteria provides a list of the

approved vents for CWC.

DOE/RL-2017-02 Rev. 0

B-116

Comment: No containers were

sent to WIPP in CY 2016.

ABATEMENT-NucFil® Filters or Similar Device A NucFil

filter or similar device may be constructed with a variety of

filter media (e.g. a porous carbon/carbon composite or sintered

316 SS metal) housed in stainless steel. At a minimum, the

NucFil filter or similar device shall restrict the release of

99.95% of particles with a mean 0.3 microns in size. (WAC

246-24 7-040(5)) (WAC 246-247-040(5))

Continuous




NOC. HNF-EP-006 Hanford

Site Solid Waste Acceptance

Criteria provides a list of the

approved vents for CWC.

ABATEMENT-PermaCon A PermaCon modular containment

unit may be placed in select, existing CWC buildings for the

purpose of sampling the head space gas within solid waste

storage containers. Such buildings would have roof mounted

exhausters, rated at a minimum of 16,000 cubic feet per

minute. (WAC 246-247-040(5))

Continuous CDM: PermaCon's were not

used at CWC in CY 2016.

ABATEMENT-Roll-on/Roll-off (RO/RO) Containers RO/RO

containers are commercially-available, open-top dumpsters.

They may be used for storage/disposal of LLW generated on

the Hanford Site from routine maintenance and surveillance

activities (e.g., rags, paper, rubber gloves, disposal supplies,

tools, industrial waste potentially contaminated with

radioactive material). For routine activities, the waste is placed

in plastic on location, and the plastic is secured (e.g., taped

close). - The bagged waste shall be transported to the CWC

and stored in a RO/RO.

-A maximum of four (4) RO/RO containers may be generated

per year for waste streams associated with routine maintenance

and surveillance activities.

-The containers could be located anywhere within the CWC

fenced area.

-The filled containers shall be transported to ERDF for

disposal.

The RO/RO containers may also be used in support of the

management of contaminated soil and materials disturbed

during the cleanup of containers, buildings, equipment, and/or

contaminated soil (i.e. non-routine activities). The RO/RO

container is located adjacent to the waste generation site and

non-routine activity waste is loaded directly into the container.

-Prior to the use of RO/RO containers for non-routine cleanup

activities, WDOH shall be notified of the anticipated waste

volumes, radiologic contamination levels and any radiological

controls required beyond those specified in the license.

-There is no maximum limit on the number of RO/RO

containers that can be used for waste streams associated with

non-routine activities.

-The containers could be located anywhere within the CWC

fenced area.

-The filled containers shall be transported to ERDF for

disposal. (WAC 246-247-040(5))

Continuous




NOC. No more than 4 RO/RO

containers were generated for

waste streams associated with

routine maintenance and

surveillance activities.

ABATEMENT-Additional Controls for Spill or Release In the

event that a spill or release of contamination associated with a

waste container is discovered, additional controls will be

implemented -During work activities, continuous radiological

Continuous




NOC.

DOE/RL-2017-02 Rev. 0

B-117

control technician (RCT) coverage will be provided. -Alpha

and beta-gamma contamination surveys will be performed

prior to and during cleanup activities that have the potential to

disturb radioactive contamination such as soil disturbance and

box covering. (WAC 246-247- 040(5))

ABATEMENT- Wind Speeds-Stop Work In any

Contamination Area (CA), High Contamination Area (HCA) or

Airborne Radioactivity Area (ARA), cleanup activities

involving dispersible contaminated material shall stop if

average wind speeds exceed 10 miles per hour (mph) for

elevated work or 20 mph for ground level work, as measured at

the site. (WAC 246-247-040(5))

Continuous




NOC. Additional



RWP's on a case-by-case basis.

ABATEMENT- Misters-fixatives -Hand-held and/or over-head

atomized misting will be performed during work activities

where a potential exists to generate airborne radioactivity.

-Atomized misters and fixative sprayers shall be function-

checked at the work site prior to commencing work activities.

(WAC 246-247-040(5))

Continuous




NOC. Additional


placed in work packages on a

case-by-case basis.

BATEMENT-Related Approvals If a truck-mounted vacuum

(i.e., GuzzlerTM) Portable/Temporary Radioactive Air

Emission Units (PTRAEU), or HEPA filtered vacuum

radioactive air emission unit is used, controls as described in

the Hanford Site Radioactive Air Emissions License #FF-01,

for the Sitewide GuzzlerTM NOC (Emission Unit ID: 476), the

PTRAEU NOC (Emission Unit ID: 447), and the Hanford

Sitewide W PORTEX 007 [HEPA vacuums] NOC (Emission

Unit ID: 455), respectively, would be followed. (WAC 246-

247-040(5))

Continuous

CDM: truck-mounted vacuum

(i.e., GuzzlerTM)

Portable/Temporary

Radioactive Air Emission Units

(PTRAEU), or HEPA filtered

vacuum radioactive air

emission unit were not used at

CWC in CY 2016.

ABATEMENT-Soil Removal -During and after removal of

radiologically-contaminated soil, soil surface radiological

contamination levels shall be verified.

-If contamination is present >500,000 dpm/100cm^2 beta-

gamma or> 10,000 dpm/l 00cm^2 alpha:

--- Additional soil shall be removed and containerized for

disposal

--- Soil shall be containerized, fixed or covered if it is to be left

for greater than 48 hours (WAC 246-247-040(5))

Continuous




NOC. Additional



RWP's on a case-by-case basis.

INVENTORY TRACKING-Container Inventory Container

inventory tracked (logged) in the SWITS database and

available for audits. (WAC 246-247-040(5)

Continuous

CDM: Container inventory is

tracked in SWITS and available

for audits.

TRACKING-Activity Log The facility must maintain a log in

an approved format (SWITS database) for this activity or

emission unit. (WAC 246-247-040(5))

Continuous CDM: The facility maintains a

log in the SWITS database.

HOUSEKEEPING Decontamination and/or replacement of

leaking containers shall be performed as needed. Frequent

smears throughout the CWC will be used to ensure that the

emission control equipment is working properly.

• Smears that exceed 20 dpm/100 cm^2 for alpha and 1,000

dpm/100 cm^2 for beta/gamma contamination will be

investigated to determine the cause of the contamination and

appropriate corrective actions shall be implemented. (WAC

246-247-040(5))

Continuous




NOC.

DOE/RL-2017-02 Rev. 0

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MONITORING-Periodic Confirmatory Sampling Periodic

confirmatory sampling is required. It must consist of: sampling

quarterly using a portable sampler for a two-week interval

inside the CWC building (excluding outdoor pads) containing

vented containers with the highest cumulative inventory of DE

curies during the quarter sampled. (Samples will be handled

following the applicable sections of 40 CFR 61, Appendix B,

Method 114.) (WAC 246-247-040(5))

Continuous

CDM: Periodic confirmatory

sampling was done inside the

CWC buildings containing

vented containers with the

highest cumulative inventory of

DE-Ci during each quarter of

CY 2016.

MONITORING-Ambient Air Monitoring Network The 200

Area near-facility ambient air monitoring network shall be

used for continuous monitoring. Ambient air monitors N-449,

N-457, N-964, and N-433 are maintained as monitors for CWC

diffuse/fugitive emissions. These monitors shall provide

indication of potential elevated airborne radioactivity using the

same frequency and protocol of the Hanford Site Near-Facility

Environmental Monitoring Program. (WAC 246-247-040(5))

Continuous


procedures in place to operate

and collect samples and review

ABCASH data to verify


collected from the near-facility


300 Area Emissions WDOH Emission Unit ID: 443



Status


Method


Zone or Area: Abatement Technology: Administrative Controls

Required Units: Add'l Description: Abatement controls as required in the

following Conditions and Limitations.

Continuous CDM: Controls as required by

the NOC were followed.

Required Sampling: Per the sitewide ambient monitoring

program samples will be collected from the existing near-

facility monitoring stations.

Sampling Frequency: Per the sitewide ambient monitoring

program.



TEDE.

Continuous

CDM: ABCASH data were

reviewed to verify required

samples were collected from

the near-facility monitoring

stations.




2016 Hanford Site


Report.

Federal and State Regulatory Requirement: WAC 246-

247-075(3)


Appendix B, Method 114 (3)




NOC: 300 Area Excavation Activities



DOE/RL-2017-02 Rev. 0

B-119

Sitewide Type-1, 2, 3 WDOH Emission Unit ID: 447



Status


Method



Required Units: 1

Add'l Description: Type-1


records review.


Required Units: 1

Add'l Description: Type-2 and Type-3

Continuous


records review.

Comment: No Type-2 or

Type-3 PTRAEUs were

operated during the reporting

period.

Zone or Area: Abatement Technology: Charcoal Filter

Required Units: 1

Add'l Description: Type-2 and Type-3

Continuous


records review.

Comment: No Type-2 or

Type-3 PTRAEUs were

operated during the reporting

period.

Required Sampling: One of the following methods may be

chosen for actual emissions reporting: nondestructive assay,

record sampler, or continuous air monitoring, whichever is

more appropriate.

Sampling Frequency: Annual, unless specified by the NOC.

Radionuclide Requiring Measurement: GROSS

ALPHA/BETA

Continuous


ABCASH program, and

portable/temporary radioactive

air emission unit (PTRAEU)

operating logs.


61.93(b)(4)(i) & WAC 246-247-075(3)




records review.


NOC: Portable/Temporary Radionuclide Airborne Emissions Units (PTRAEU)





Continuous




information) for CY 2016 to

verify total abated emissions

are below the NOC limit.






records review.

DOE/RL-2017-02 Rev. 0

B-120

Type I PTRAEUs are portable ventilation-filter units. Type II

PTRAEUs are mobile sample preparation units. Type III

PTRAEUs are mobile screening and analysis units. Each type

of PTRAEU is described in the following paragraphs.

Most of the PTRAEUs are portable ventilation-filter units

(Type I) with a capacity from approximately 50 to 2,000+

cubic feet per minute exhaust flow rate. The portable

ventilation filter units control radionuclide emissions by

providing filtered ventilation on sites where work activities

potentially could disturb areas with radioactive contamination.

Type I units that are vacuums are listed to be used as

ventilation units. If the vacuum is used in any other

manner/process, the WDOH must approve its use under

separate application before the activity commences.

Mobile sample preparation units (Type II) decrease the chance

of unintentional cross-contamination of samples and enhance

personnel radiological safety. The sample preparation units

enable technicians to remove material from core barrels,

homogenize the material, and fill prescribed sample containers

for onsite and offsite analysis. In enclosed, self-contained

sample preparation units, radiological exposure and

interference from environmental conditions (i.e., wind,

precipitation, and exhaust fumes) are minimized.

Mobile sample screening and analysis units (Type III) provide

preliminary screening of samples to determine potential

problem areas at a site. The units also screen samples to

I\identify those samples requiring further in-depth analysis.

Screening samples decreases the number of samples

transported for analysis. The fast turnaround time can provide

results for a field situation requiring expeditious response.

The source of radionuclides handled by the mobile sample

preparation facilities and mobile screening and analysis

facilities is contaminated soils and/or liquids extracted from

cribs, ditches, ponds, burial sites, and other such areas with

surficial soil contamination. An additional source of

radionuclides is preparation of radioactive standards to be used

for instrument calibration.


030(21a-e) [as specified in the application] is 8.90E-02


(Curies/year) of:









records review.

DOE/RL-2017-02 Rev. 0

B-121















Department of Health reserves the right to request an

nondestructive analysis (NDA) after each exhaust job

assignment (WAC 246-247-075(3)). The monitoring includes:

emission estimates to include the methodology, all monitoring

measurement results taken during the operation, copy of all

logs submitted to the department on June 30th. One of the

following methods may be chosen for actual emissions

reporting, nondestructive assay, record sampler, or continuous

air monitoring, whichever is more appropriate.


records review.

Ductwork, seams, and potential release locations on the

portable exhauster are to be monitored on a routine basis for

potential radionuclide releases according to the NOC. These

routine checks should be kept as retrievable records.


records review.

The required possession quantity is RHL's calculated for a

daily use because many of the activities are of short duration.

In calculating the RHL's 0.1 mrem per year criteria will be

used as a beginning point and the source term, which can be

handled each day, is back calculate.

Not

Applicable










Permit: AIR 12-312 - B Issue Date: 03-06-12 Effective Date: 02-23-12





NOC: Roof Replacement Activities Involving Radioactive Contamination at Facilities on the Central Plateau



DOE/RL-2017-02 Rev. 0

B-122


NOC: Categorical Tank Farm Facility Entry and Surveillance



Permit: AIR 12-320 – A Issue Date: 03-06-12 Effective Date: 02-23-12

NOC: Tank Farm Restoration and Safe Storage

WDOH NOC ID: 841 Date In AOP: 04-01-13 Page in AOP: EU-0447-010


Vented Containers WDOH Emission Unit ID: 448



Status


Method



Required Sampling: Environment Sampling

Sampling Frequency: Air-every 2 weeks

continuous/deposition - annually


TOTAL BETA

Continuous





stations.


61.93(b)(4)(i) & WAC 246-247-075(3)






NOC: Sitewide Vented Container Storage





Continuous











Containers are used to store mixed and/or radioactive waste

generated on and off the Hanford Site. Venting devices are


work documents.

DOE/RL-2017-02 Rev. 0

B-123

installed when there is the potential for non-radioactive gases

(I.e., hydrogen) to be generated as a result of radiolysis.




(Curies/year) of:






















Continuous CDM: Annual compliance

evaluation.

Containers other than drums are also approved if they meet the

conditions of this NOC. Continuous


work documents.

Establishes a categorical As Low As Reasonably Achievable

Control Technology (ALARACT) demonstration for existing

Hanford Site vented containers.

Not

Applicable










Establishes a categorical Best Available Radionuclide Control

Technology (BARCT) demonstration for all future Hanford

Site vented containers ( i.e., up to 6667 vented container units

(UVC) based on a total abated emissions offering less than

3.4E-05 mrem/year to the MEI). (WAC 246-247-040 (5))

Not

Applicable










DOE/RL-2017-02 Rev. 0

B-124

NucFil(TM) filter or an equivalent filter shall be BARCT and

ALARACT. Vent clips are accepted as ALARACT for

existing systems to date, however, when conditions require

repackaging vent clips shall be replaced by NucFil(TM) or

equivalent filters.


work documents.

Pu239/240 equivalent curies (PE-Ci) represents the

radionuclide of concern as discussed in the Hanford Site Solid

Waste Acceptance Criteria, WHC-EP-0063.

Not

Applicable










The vented container Latitude and Longitude coordinates (46

degrees 22' 13.8", 119 degrees 16' 12.3") refer to the location

resulting in the highest impact to the MEI.

Not

Applicable










These containers are used for storing mixed and or radioactive

waste generated on or off Hanford Site.

Not

Applicable










WDOH accepts vent clips as ALARACT since they are no

longer installed.

Not

Applicable










DOE/RL-2017-02 Rev. 0

B-125

200 Area ISA WDOH Emission Unit ID: 454



Status


Method



Required Sampling: Smear Survey

Sampling Frequency: Annual Continuous

CDM: Review Radiological

Survey Reports within the

several PMs that perform the

annual inspections.


247-075(3) Continuous

CDM:WAC 246-247-075(3)

allows WDOH to approve

other methods of monitoring.

Radiological field swipe/smear

survey is the defined method

per the NOC.


NOC: Construction and Operation of the 200 Area Interim Storage Area (ISA)





Continuous


source data/information for

CY 2016 to verify total abated


limit.





The construction and operation of the 200 Area ISA. The 200

Area ISA will be constructed and operated for the interim

storage of non-defense production reactor SNF in dry cask

storage systems (DCSSs). [Note: Dry cask storage system is a

generic term referring to the various storage systems

employed for SNF storage at the 200 Area ISA and does not

refer to a specific storage system.]

Dry Cask Storage System Interim Storage

Once the DCSSs are prepared for interim storage the systems

can be transferred to the 200 Area ISA for interim storage. Up

to sixty Interim Storage Casks (ISCs) storing FFTF SNF, 7

NAC-1 casks storing LWR SNF, and 12 NRF TRIGA casks

and 2 DOT-6M containers storing TRIGA SNF will be

required for storage at the 200 Area ISA. Each of the dry cask

storage systems will be transported via road to the 200 Area

ISA and unloaded using a mobile crane. Each DCSS will be

Continuous

CDM: Review of description

provided in the permit

application and review of

Daily Ops Report and/or

project field execution

schedules verified no new

activities were performed.

DOE/RL-2017-02 Rev. 0

B-126

placed at a specific location within the 200 Area ISA.

Dry Cask Storage System Equipment

Different DCSSs are utilized for the different SNF types to be

stored at the 200 Area ISA to accommodate the particular

characteristics of the SNF. The FFTF SNF DCSS, the NRF

TRIGA SNF DCSS, and the LWR SNF DCSS.

200 Area ISA Design and Construction

The 200 Area ISA consists of concrete pads, perimeter fencing

and lighting, access for transporters and mobile cranes, and

conduit for potential future electrical service and

instrumentation. This construction will not involve

contaminated items. The 200 Area ISA will be situated within

the current CSB construction site. This site is currently not a

radiological area nor does it contain an underground

radioactive material area. No contaminated excavation will be

involved.


030(21a-e) [as specified in the application] is1.92E-03


(Curies/year) of:


WAC 246-247-030(21)(a)


WAC 246-247-030(21)(a)

Am-242 m 1.12E-06 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Ba-137m 1.18E-03 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

C-14 5.75E-03 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Ce-144 1.92E-04 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Cm-242 1.21E-06 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Co-60 1.07E+03 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Cs-134 1.56E-04 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Cs-137 1.25E-03 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Eu-154 3.30E-05 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Eu-155 1.21E-04 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Fe-55 1.01E-03 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

H-3 3.62E+00 Gas

Continuous

CDM: Review of description

provided in the permit

application and review of

Daily Ops Report and/or

project field execution

schedules verified no new

activities were performed.

DOE/RL-2017-02 Rev. 0

B-127

WAC 246-247-030(21)(a)

I-129 3.07E-04 Gas

WAC 246-247-030(21)(a)

Kr-85 3.07E+01 Gas

WAC 246-247-030(21)(a)

Mn-54 9.55E-04 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Ni-63 9.18E-05 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Np-237 1.15E-09 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Pm-147 9.64E-04 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Pr-144 4.15E+05 Liquid/Particulate Solid

WAC 246-247-030(21)(a)


WAC 246-247-030(21)(a)


WAC 246-247-030(21)(a)


WAC 246-247-030(21)(a)


WAC 246-247-030(21)(a)

Rh-106 5.51E-04 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Ru-106 5.51E-04 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Sb-125 1.21E-04 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Sm-151 5.15E-05 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Sr-90 4.55E-04 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Tc-99 1.83E-07 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Te-125 m 2.95E-05 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

U-235 9.70E-12 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

U-238 1.01E-09 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Y-90 4.55E-04 Liquid/Particulate Solid

WAC 246-247-030(21)(a)


(no quantity specified):

Am-241 Am-242 Am-242 m Ba-137 m C-14

Ce-144 Cm-242 Co-60 Cs-134 Cs-137

Eu-154 Eu-155 Fe-55 H-3 I-129

Kr-85 Mn-54 Ni-63 Np-237 Pm-147

DOE/RL-2017-02 Rev. 0

B-128

Pr-144 Pu-238 Pu-239 Pu-240 Pu-241

Rh-106 Ru-106 Sb-125 Sm-151 Sr-90

Tc-99 Te-125 m U-235 U-238 Y-90




















Any detectable contamination above 2200 dpm/100 cm ^2

Beta-Gamma or 220 dpm/100 cm^2 Alpha as a result of the

ISA specific monitoring shall be reported to the department.

Continuous

CDM: Contamination levels

observed with radiological

field swipe/smear surveys did

not require reporting.

Periodic confirmatory monitoring shall consist of annual

smears or swipes of the outer surfaces of the containers using

hand held survey instruments capable of detecting

contamination above 2200 dpm/100 cm ^2 Beta-Gamma or

220 dpm/100 cm^2 Alpha.

Continuous



field swipe/smear surveys of

rad/operating data.

The emission limit for this emission unit is no smearable

contamination above 2200 dpm/100 cm ^2 Beta-Gamma or

220 dpm/100 cm^2 Alpha using standard portable instruments

used, and survey methods followed at Hanford (WAC 246-

247-040(5)).

Continuous



field swipe/smear surveys did

not require reporting.

Sitewide HEPA Vacuums WDOH Emission Unit ID: 455



Status


Method



Required Sampling: None Not

Applicable

CDM: No requirement

specified.

DOE/RL-2017-02 Rev. 0

B-129


61.93(b)(4)(i) & WAC 246-247-075(3) Continuous CDM: Field interviews.


NOC: HEPA Filtered Vacuum Radioactive Air Emission Units (HVU)





Continuous











The use of specified HVUs located and operated on the

Hanford Site, and represents establishment of unregistered,

portable and temporary, insignificant emission units.

For the purposes of estimating (modeling) offsite exposures

for this application, all applicable HVU emissions at an

individual facility (e.g., B Plant Complex, C Tank Farm, SX

Tank Farm, T Plant Complex, 100-K East Basin, 100-K West

Basin, 324 Building, 340 Complex, etc.) or activity (e.g.,

D&D of a building) will be considered as a single emission

point for that facility.

HVUs are portable cleaners with exhaust flow rates ranging

from 50 to 300 cubic feet per minute. The units control

radionuclide emissions by providing filtered vacuuming for

surfaces that radioactively are contaminated.

HVUs fall into two categories of use, those used for the

reduction of smearable contamination and those used to

reduce fixed contamination. For smearable contamination, the

use of HVUs is limited to reduction of contamination on hard

surfaces (e.g., concrete, permanently installed metal

equipment such as risers, ventilation system components,

piping, etc.). Soil matrices are excluded from this NOC.

Smearable contamination on these hard surfaces will not

exceed limits established in DOE/RL-96-109. These limits, if

exceeded, require the affected are to be posted as a high

contamination area. The limits are 2,000 disintegrations per

minute per 100 square centimeters (dpm/100 cm2) alpha

contamination and 100,000 dpm/100 cm2 beta/gamma

contamination.

An exception to these limits is restricted to spot surface

contamination areas found during outdoor radiological field

surveys, and to clean up localized, radiologically contaminated

material (e.g., dust, dirt, bird droppings, animal feces, insects,


work documents.

DOE/RL-2017-02 Rev. 0

B-130

spider webs, tumbleweed fragments, etc.). These types of

materials could have beta/gamma contamination levels

exceeding 1 million dpm/100 cm2, but are very localized (i.e.,

a few square meters, rather than hundreds of square meters)

and could occur in contamination areas, buffer zones, and

clean zones. This exception does not apply to areas normally

posted as high contamination areas.

The second category of use is for reduction of fixed

contamination, involving the removal and/or penetration of

contaminated surfaces. This category of use includes using

HVUs and associated shrouded tools for sanding, stripping,

spalling, drilling, and cutting operations. Limits in areas of

fixed contamination to ensure compliance will be established

before these tools are used.


030(21)(a-e) [as specified in the application] is 4.97E-02


(Curies/year) of:

Alpha-0 | 3.09E-03 | Liquid/Particulate Solid |

WAC 246-247-030(21)(a)

Alpha release rate for 100 Areas, emission calculations will

assume Pu-239/240


WAC 246-247-030(21)(a)

Alpha release rate for 300 Area, emission calculation will

assume Pu-239/240.


WAC 246-247-030(21)(a)

Alpha release rate for 400 East Area, emission calculation will

assume Pu-239/240


WAC 246-247-030(21)(a)

Alpha release rate for 200 East Area, emission calculation will

assume Pu-239/240


WAC 246-247-030(21)(a)

Alpha release rate for 200 West Area, emission calculation

will assume Pu-239/240

B/G-0 | 3.88E-01 | Liquid/Particulate Solid |

WAC 246-247-030(21)(a)

B/G release rate for 200 West Area, emission calculations will

assume Sr-90.


WAC 246-247-030(21)(a)

B/G release rate for 300 Area, emission calculations will

assume Sr-90.


work documents.

DOE/RL-2017-02 Rev. 0

B-131


WAC 246-247-030(21)(a)

B/G release rate for 400 Area, emission calculations will

assume Sr-90.


WAC 246-247-030(21)(a)

B/G release rate for 100 Areas, emission calculations will

assume Sr-90.


WAC 246-247-030(21)(a)

B/G release rate for 200 East Area, emission calculations will

assume Sr-90.



Pu-239/240 | Sr-90









than 25% of the TEDE to the MEI after controls. WAC 246-

247-110(9). DOE must notify the Department of any changes










All HEPA vacuum logs shall be submitted to the department

on a quarterly basis (beginning with the first quarter of 2002).

This submittal shall be to the department 30 days after the end

of each quarter.


work documents.

Monitoring requirements are as follows: In the event that the

exhauster is used on different emission units, the Department

of Health reserves the right to request a nondestructive

analysis/assay (NDA) after each exhaust job assignment

(WAC 246-247-075(3)). The monitoring includes: emission

estimates to include the methodology, all monitoring

measurement results taken during the operation, copy of all

logs kept on site and the summary submitted to the department

on June 30th.

Log sheets will include the following information:


work documents.

DOE/RL-2017-02 Rev. 0

B-132

Results of smears on the exhaust ports;

Maximum contamination level encountered or analysis results,

area cleaned,

and air emission source constituents if other than plutonium

239 and strontium 90 potential radionuclide releases.

The approved process is as follows: The HVU's fall into two

categories. The first category is the use if the HVU's for the

reduction of smearable contamination and the other is to

reduce fixed contamination. Soil matrices are excluded from

this NOC.

Not

Applicable










The required controls are described as follows: The HVU's

must be field tested annually requiring an aerosol

test/efficiency test or equivalent pass/fail criteria of 95.95%

using an aerosol defined in ASME N510 or approved

equivalent. In addition, the HVU's filtration systems are to be

tested whenever the configuration is modified and/or the

filtration system is opened. A smear of the exhaust port shall

be conducted before and after each use of HVU's. If the

exhaust port smear is positive, the unit shall be tagged and

removed from service.


work documents.

This NOC shall be revised no later than September 1, 2002.

Revision 2 was received in September, 2002. The NOC

application was determined to be incomplete, a new NOC

application shall be submitted.

Not

Applicable











NOC: Operation of the Transuranic Waste Retrieval Project



Permit: AIR 12-317 – B Issue Date: 03-06-12 Effective Date: 02-23-12




DOE/RL-2017-02 Rev. 0

B-133

W-PORTEX 011 WDOH Emission Unit ID: 461




P-Trench31 001 WDOH Emission Unit ID: 472



Status


Method



Required Sampling: Smear sample of overflow pipe.

Sampling Frequency: Before and after emptying the tank.

When the tank is not empty, take a monthly smear (after

commencement of bulk waste disposal).

Continuous

CDM: Facility operating and

radiological control

procedures.



CDM: NESHAP Quality



(CHPRC-00189, Appendix E)

specifies the hardware and

methods used to sample and

the analytical methods used in

the laboratory.

Permit: AIR 12-315 – A Issue Date: 03-06-12 Effective Date: 02-23-12 Obsolete Date: 09-12-16

NOC: Trench 31 and 34: Leachate Collection and Storage Tank (LLBG Mixed Waste Disposal)





Continuous

CDM: MREM/year calculated

via spreadsheet using trench

volume transfer data for

reporting period to confirm

levels used in NOC application

PTE calculations are

bounding.





Trenches 31 and 34 shall be used for the disposal of low-level

waste, low-level mixed waste, and radioactive waste

containing Toxic Substances Control Act regulated

Continuous

CDM: There were no






WAC 246-247-030(16) during


DOE/RL-2017-02 Rev. 0

B-134

polychlorinated biphenyls resulting from current operations

across the Hanford Site, cleanup activities across the Hanford

Site and from other offsite facilities. Each trench shall provide

disposal capacity for approximately 22,000 m3 (28,000 yd3)

of waste. Waste to be disposed of in the trenches can consist

of contaminated soil and debris (bulk waste), sealed

containers, vented containers, and any other type of waste

meeting Low Level Burial Grounds (LLBG) waste acceptance

criteria.

The leachate collection systems for Trenches 31 and 34 share

a common design. That design encompasses primary and

secondary leachate collection systems. The primary and

secondary leachate collection systems are comprised of

alternating layers of soils, geomembrane liners, collection

pipes, collection sumps, sump pumps, and a single collection

tank for each trench. Liquid accumulates under the disposed

material in the bottom of each trench in the primary liner of

each trench (not exposed directly to atmosphere). When

approximately one foot of precipitation of liquid is

accumulated in the collection sumps, the pumps are activated

to transfer the liquid to the tanks.

The leachate collection tanks at Trench 31 and34 are both

above ground. Each tank has a capacity of approximately

10,000 gallons. Both tanks are cylindrical and approximately 8

feet (2.5 meters) in diameter and 24 feet (7.2 meters) long.

Both tanks are passively vented via a liquid overflow pipe.

For disposal, the liquid will be transferred from the tanks to a

tanker truck. Based on past operational experience, it is

anticipated that up to approximately 415,000 gallons, per tank,

per year could be transferred to the tanker trucks. More than

one truck may be used at the same time. The tanker truck(s)

shall be fitted with a three-quarter inch vent that will be

opened during filling and emptying operations.


activities at LLBG are as

described in the NOC. NOC

application not revised during

CY 2016.




(Curies/year) of:

Pu-239/240 | 9.74E-05 | Liquid/Particulate Solid |

WAC 246-247-030(21)(e)

U-0 | 7.00E-04 | Liquid/Particulate Solid |

WAC 246-247-030(21)(e)

Isotopes of U-233/234/235/238.



Am-241 C-14 Co-60 Cs-137 Eu-152

Eu-154 Eu-155 Na-22 Pu-238 Pu-239/240

Ra-226 Sr-90 Tc-99 Th-230 Th-232

U-0

Continuous






PTE calculations are

bounding.

DOE/RL-2017-02 Rev. 0

B-135




Department of a “modification” to the emission unit, as
















The radioactive isotopes identified for this emission unit

represent all of the significant radionuclides historically

present for the leachate collection tank 31, including some that

are not significant. Any radionuclide on the chart of nuclides

could be present or received at leachate collection tank 31 in

the future.

Not

Applicable










Upon commencement of placing non-containerized

radioactively contaminated waste in Trench 31 and/or Trench

34, a periodic confirmatory measurement (PCM) activity shall

be implemented. This PCM activity shall consist of smearing

the orifice(s) of the liquid overflow pipe(s) before and after

emptying the tank(s). During those months when the tank(s)

is/are not emptied, a smear shall be taken monthly. After the

accumulation of one year's worth of smear data.

Not

Applicable










P-Trench34 001 WDOH Emission Unit ID: 473



Status


Method



Required Sampling: Smear sample of overflow pipe.

Sampling Frequency: Before and after emptying the tank.

When the tank is not empty, take a monthly smear (after

commencement of bulk waste disposal).

Continuous

CDM: Facility operating and

radiological control

procedures.

DOE/RL-2017-02 Rev. 0

B-136



CDM: NESHAP Quality



(CHPRC-00189, Appendix E)

specifies the hardware and

methods used to sample and

the analytical methods used in

the laboratory.


NOC: Trench 31 and 34: Leachate Collection and Storage Tank (LLBG Mixed Waste Disposal)





Continuous






PTE calcs are bounding.





Trenches 31 and 34 shall be used for the disposal of low-level

waste, low-level mixed waste, and radioactive waste

containing Toxic Substances Control Act regulated

polychlorinated biphenyls resulting from current operations

across the Hanford Site, cleanup activities across the Hanford

Site and from other offsite facilities. Each trench shall provide

disposal capacity for approximately 22,000 m3 (28,000 yd3)

of waste. Waste to be disposed of in the trenches can consist

of contaminated soil and debris (bulk waste), sealed

containers, vented containers, and any other type of waste

meeting Low Level Burial Grounds (LLBG) waste acceptance

criteria.

The leachate collection systems for Trenches 31 and 34 share

a common design. That design encompasses primary and

secondary leachate collection systems. The primary and

secondary leachate collection systems are comprised of

alternating layers of soils, geomembrane liners, collection

pipes, collection sumps, sump pumps, and a single collection

tank for each trench. Liquid accumulates under the disposed

material in the bottom of each trench in the primary liner of

each trench (not exposed directly to atmosphere). When

approximately one foot of precipitation of liquid is

accumulated in the collection sumps, the pumps are activated

to transfer the liquid to the tanks.

The leachate collection tanks at Trench 31 and34 are both

above ground. Each tank has a capacity of approximately

10,000 gallons. Both tanks are cylindrical and approximately 8

feet (2.5 meters) in diameter and 24 feet (7.2 meters) long.

Continuous

CDM: There were no






WAC 246-247-030(16) during



activities at LLBG are as

described in the NOC. NOC

application not revised during

CY 2016.

DOE/RL-2017-02 Rev. 0

B-137

Both tanks are passively vented via a liquid overflow pipe.

For disposal, the liquid will be transferred from the tanks to a

tanker truck. Based on past operational experience, it is

anticipated that up to approximately 415,000 gallons, per tank,

per year could be transferred to the tanker trucks. More than

one truck may be used at the same time. The tanker truck(s)

shall be fitted with a three-quarter inch vent that will be

opened during filling and emptying operations.




(Curies/year) of:

Pu-239/240 | 9.74E-05 | Liquid/Particulate Solid |

WAC 246-247-030(21)(e)

U-0 | 7.00E-04 | Liquid/Particulate Solid | WAC 246-247-

030(21)(e)

Isotopes of U-233/234/235/238.



Am-241 C-14 Co-60 Cs-137 Eu-152

Eu-154 Eu-155 Na-22 Pu-238 Pu-239/240

Ra-226 Sr-90 Tc-99 Th-230 Th-232

U-0




















Continuous






PTE calculations are bounding

DOE/RL-2017-02 Rev. 0

B-138

Upon commencement of placing non-containerized

radioactively contaminated waste in Trench 31 and/or Trench

34, a periodic confirmatory measurement (PCM) activity shall

be implemented. This PCM activity shall consist of smearing

the orifice(s) of the liquid overflow pipe(s) before and after

emptying the tank(s). During those months when the tank(s)

is/are not emptied, a smear shall be taken monthly. After the

accumulation of one year's worth of smear data.

Not

Applicable










The radioactive isotopes identified for this emission unit

represent all of the significant radionuclides historically

present for the leachate collection tank 34, including some that

are not significant. Any radionuclide on the chart of nuclides

could be present or received at leachate collection tank 34 in

the future.

Not

Applicable










Sitewide Guzzler WDOH Emission Unit ID: 476



Status


Method


Zone or Area: Abatement Technology: Collection Tank and Plate Separator

Required Units: 1

Add'l Description:

Continuous


responsible personnel. Control

equipment has not been

modified.

Zone or Area: Abatement Technology: Cyclone Separator

Required Units: 2

Add'l Description:

Continuous




modified.

Zone or Area: Abatement Technology: Micro-strainer Device

Required Units: 1

Add'l Description:

Continuous




modified.


Required Units: 3

Add'l Description: Three in-place tested HEPA filters in

parallel.

Continuous




modified.

DOE/RL-2017-02 Rev. 0

B-139


Status


Method

Zone or Area: Abatement Technology: Baghouse

Required Units: 2

Add'l Description: Baghouse system with a total of 68 bags

(i.e., 34 bags per baghouse).

Continuous




modified.

Required Sampling: Radiation surveys and to include but not

limited to NDA testing of the HEPA filters and screening the

HEPA filtration system using gamma spectroscopy.

Sampling Frequency: When the HEPA filters are replaced

and annually screening the HEPA filtration system.



TEDE to the MEI, greater than 0.1 mrem/yr potential-to-emit

TEDE to the MEI, and greater than 25% of the TEDE to the

MEI, after controls.

Continuous

CDM: Radiological Survey

Records and NDA results for

Guzzler HEPA filters.


61.93(b)(4)(i) & WAC 246-247-075(3)

Permit Monitoring and Testing Procedure: 40 CFR 61;


Continuous




Comment: NDA was

performed on filters using

gamma spectroscopy. NDA

results showed that any

radionuclides observed were

equivalent to levels detected in

background spectra.


NOC: Operation of the Guzzler in Tank Farm Facilities



Permit: AIR 12-317 – C Issue Date: 03-06-12 Effective Date: 02-23-12









NOC: Categorical Tank Farm Facility Waste Retrieval and Closure: Phase 1 -

Site Preparation and System Installation



DOE/RL-2017-02 Rev. 0

B-140


Status


Method


NOC: Use of the Guzzler Vacuum Excavation System for Radiologically Limited Activities on the Hanford

Site WDOH NOC ID: 860 Date In AOP: 04-01-13 Page in AOP: EU0476-023




Continuous

CDM: NDA results for

Guzzler HEPA filters and

Radiological Survey Records.




defined in WAC 246-247-030(16), may be conducted.

The utilization of the Guzzler(TM) Vacuum Excavation

System (Guzzler(TM)) for potholing to support utility

locations, soil removal/general excavations, and radiologically

limited activities involving roof or pit cleaning (note,

radiologically limited activities means work locations where

soil radiological contamination levels are not expected to

exceed 50,000 dpm/probe size beta-gamma and/or 140

dpm/probe size alpha). For purposes of this license, "soil" will

be defined as sand, dirt, gravel, gravel and tar mixtures and

rock, or any combination of these items. Note, beta-gamma

probe size is ~16.7 com^2 and alpha probe size is ~50 cm^2.

Note, the terms, "Guzzler(TM)," and "Filtered Vacuum Truck

(FVT)," may be used interchangeable.

In most cases, for excavations, the excavated soil will be used

for backfilling of the excavated areas. The backfilling

activities will be completed manually, using shovels, or using

backhoes, loaders, or packers. For cleaning activities and

some excavations, the soil will either be containerized for

disposal or transported to an appropriate disposal facility (e.g.,

LLBGs, ERDF, etc.) within the FVT collection tank for

noncontainerized disposal. In some cases, soil may be

unloaded from the FVT and packaged at the disposal facility

for containerized disposal.

Only radiologically contaminated or potentially contaminated

soil will be removed or excavated using the regulated FVT

system. All soil removed from the system will be handled as

potentially contaminated, unless otherwise surveyed or

analyzed.

The regulated FVT will not be used for the decontamination of

valve pits within the tank farms. The regulated FVT is also

excluded from areas containing radiological contamination

above 50,000 dpm/probe size beta-gamma and/or 140

dpm/probe size alpha.

Soil can be slowly dumped from the collection tank by

controlling the raising and lowering speed of the tank.

Continuous

CDM: Guzzler Work Activity

Instruction and Desk

Instruction, Guzzler Usage

Information Request form,

training, and/or observations

by Guzzler Coordinator.

DOE/RL-2017-02 Rev. 0

B-141


Status


Method

Soil from contaminated areas enters the unit through a hose.

An air lance attachment may be used to aid in the loosening of

soil.

The various cleaning and excavation activities will be

completed using the FVT along with shovels, picks and/or the

air lance attachment to loosen the soil, and backfilling

activities will be completed using backhoes, loaders,

compactors with plates, and picks and shovels, as appropriate.

In some cases, however, an area may be physically

inaccessible for the regulated FVT. In those instances, the

cleaning or excavation, as well as any backfilling activities

will be completed using backhoes, loaders, compactors with

plates, and/or picks and shovels, as appropriate.

Areas of the vacuum truck where condensate may accumulate

such as the HEPA filter housing, silencer, and micro-strainer

will be drained on an as needed basis to remove condensate

buildup. The drained water will be containerized and properly

dispositioned. If radiological contamination is present, the

liquid may be solidified with absorbent materials, and the

resulting matrix may be packaged and disposed of at a

radioactive landfill (e.g., LLBG, ERDF, etc.). Alternatively,

the liquids may be transferred to an approved container or

tanker truck (see Emission Unit ID 888) for transport to the

Effluent Treatment Facility (Emission Unit ID 301) or other

facility licensed to receive radioactively contaminated liquids.




(Curies/year) of:

Alpha-0 | 1.79E-03 | Gas | WAC 246-247-030(21)(a)

200 Area *gaseous physical state assumed for purposes of

conservatism relative to assigned release fraction. AM-241

used as conservative alpha emitter.

Alpha-0 | 1.30E-04 | Gas | WAC 246-247-030(21)(a)


conservatism relative to assigned release fraction. U-234 used

as conservative alpha emitter.

Alpha-0 | 7.26E-04 | Gas | WAC 246-247-030(21)(a)


conservatism relative to assigned release fraction. Pu-239 used

as conservative alpha emitter.

Alpha-0 | 1.79E-03 | Gas | WAC 246-247-030(21)(a)


conservatism relative to assigned release fraction. Am-241

used as conservative alpha emitter.

Continuous


Records and NDA results.

Reasonable inquiry of

knowledgeable personnel.

DOE/RL-2017-02 Rev. 0

B-142


Status


Method

B/G-0 | 4.48E-02 | Gas | WAC 246-247-030(21)(a)


conservatism relative to assigned release fraction. Sr-90 used

as conservative beta emitter.

B/G-0 | 4.48E-02 | Gas | WAC 246-247-030(21)(a)




B/G-0 | 1.46E-02 | Gas | WAC 246-247-030(21)(a)




B/G-0 | 4.48E-02 | Gas | WAC 246-247-030(21)(a)



as conservative B/G emitter.



Am-241 Co-60 Cs-134 Cs-137 Eu-152

Eu-154 Eu-155 Pu-238 Pu-239 Pu-240

Pu-241 Ru-106 Sb-125 Sn-113 Sr-90

Th-232 U-234 U-235 U-238




















All soil excavation activities operating under this NOC must

cease operations when sustained wind conditions reach or

exceed 20 miles per hour.

Continuous

CDM: Recordkeeping.

Operator and RCT training to

NOC Conditions/Limitations.

Inquiry of Guzzler

Coordinator.

DOE/RL-2017-02 Rev. 0

B-143


Status


Method

The facility must maintain a log in an approved format for this

activity or emission unit (WAC 246-247-080(7)). Continuous

CDM: Department approved

Regulated Guzzler Emission

Log is maintained by the

Guzzler Coordinator.

The following are the allowable radionuclides: Co-60, Sr-90,

Cs-137, Cs-134, Th-232. U-234, U-235, U-238, Eu-152, Eu-

154, Eu-155, Ru-106, Sn-113, Sb-125, Am-241, Pu-238, Pu-

239, Pu-240, and Pu-241. If any other radionuclides are

suspected or verified through soil analysis the department

must be notified.

Continuous

CDM: No other radionuclides

were suspected. No other

radionuclides were detected, as

verified by NDA, above

background spectra of Guzzler

HEPA filters.

The following are the annual emission limits for the NOC:

100 AREA:

For FVT Cleaning/Excavation: 2.88E-3 mrem Sr-90, 3.4E-2

mrem Am-241 For Backfilling: 2.88E-6 mrem Sr-90, 3.45E-5

mrem Am-241

200 AREA:


mrem Am-241 For Backfilling: 1.96E-6 mrem Sr-90, 2.34E-5

mrem Am-241

300 AREA:


mrem U-234 For Backfilling: 3.9E-5 mrem Sr-90, 8.3E-6

mrem U-234

400 AREA:


mrem Pu-239 For Backfilling: 8.5E-7 mrem Sr-90, 8.34E-6

mrem Pu-239.

Continuous

CDM: NDA results for

Guzzler HEPA filters and

Radiological Survey Records.

Comment: No radionuclides

were detected above

background spectra.

U.S. DOE shall monitor this project or emission unit as

follows: In addition to the surveys described in this NOC

periodic confirmatory measurements are required. This may

include but is not limited to NDA testing of the HEPA filters

when the HEPA filters are replaced and annually screening the

HEPA filtration system using gamma spectroscopy (WAC

246-247-075(8).

Continuous




200 Area Diffuse/Fugitive WDOH Emission Unit ID: 486



Status


Method



DOE/RL-2017-02 Rev. 0

B-144


Status


Method



facility monitoring stations.


program



to-emit TEDE

Continuous





stations.




2016 Hanford Site


Report.


247-075[2]










NOC: 241-SY Tank Farm Ventilation System Upgrades Installation and Pre Operational Permit for 241-

SY/AP/AY/AZ Tank Farm Exhauster Upgrade




NOC: Waste Receiving and Processing Facility


The total abated emission limit for this Notice of

Construction is limited to 5.42E-02 mrem/year to the


Continuous


below levels used in NOC




limit.

The mission of the WRAP includes examining, assaying,

characterizing, treating, verifying, and repackaging solid

radioactive waste material and mixed radioactive waste to

enable treatment, storage, or disposal. The WRAP manages

many categories of radioactive materials such as low-level

waste (LLW), transuranic (TRU) waste, TRU mixed waste,

and low-level mixed waste (LLMW) in contact-handled (CH)

containers where the external surface dose rate does not

exceed 200 mrem/hr. CH containers are defined as packages

Continuous



confirmed no "modifications"

to the emission unit as defined

in WAC 246-247-030(16).

Facility procedures demonstrate

that activities at WRAP are as


DOE/RL-2017-02 Rev. 0

B-145


Status


Method

having surface dose rates of less than 200 mrem/hr. Remote–

handled (RH) containers (i.e., containers where the external

surface dose rate is equal to or greater than 200 mrem/hr) also

are processed and stored at WRAP in accordance with the


Building 2336-W at the WRAP consists of the following

areas

• Shipping and receiving area

• Nondestructive examination/nondestructive assay

(NDE/NDA) area

• Process area

• Ancillary support areas, including the heating, ventilation,

and air conditioning (HVAC), electrical room, mechanical

room, and administration areas

See the following emission units for a detailed description of

additional controls/conditions and limits under this approval.

EU 193 296-W-4; Waste Receiving and Processing Facility

EU 486 200 Area Diffuse/Fugitive; Waste Receiving and

Processing Facility

Eu 1183 HSGS Analysis Facility



mrem/year. Approved are the associated potential release

rates (Curies/year) of:

DE-0 2.73E+05 Liquid/Particulate Solid WAC 246-247-

030(21)(a)

DE-Ci is a method of normalizing the exposure risk of the

Various isotopes, where the DE-Ci are represented as Pu-239.

Continuous


below levels used in NOC




limit.

PROCESS DESCRIPTION - General Overview of WRAP

Operations





Numerous activities within the WRAP complex, which

includes now includes the 2404-WA, 2404-WB, and 2404

WC buildings, have been and will be conducted as routine

activities. TRU and mixed wastes are received and processed

at WRAP. The 2404-WA and 2404-WB buildings are used

for waste container storage activities. The 2404-WC buildings

is used for storage as well as for conducting some head space

gas sampling (HSGS) utilizing a darting process.

WRAP also has support buildings to perform NDE and NDA

of larger waste containers. These units include:

• MO-610 - MOBILE BOX ASSAY UNIT(SuperHENC)

MO-610 is a mobile box assay unit used to determine the

AEA-regulated material content of a waste container. The

mobile trailer is approximately 3.0 m (10 ft) by 12.2 m (40 ft)

and is used to assay containers smaller than 2 m3 in volume.

2406-W Facility - HIGH ENERGY REAL-TIME

RADIOGRAPHY (HERTR)

The HERTR unit is a mobile unit used to perform NDE of

Continuous








DOE/RL-2017-02 Rev. 0

B-146


Status


Method

containers smaller than 2 m3 (71 ft3). The HERTR unit

consists of two components: (1) a shielded vault where

containers are examined, and (2) an operator control area. The

vault is a shielded enclosure of modular concrete

construction. The operator control area is a mobile trailer that

is located in close proximity to the unit. The NDE is used to

examine dense waste items to indicate the physical

appearance of the waste, identify if liquids are present, and/or

other identified suspect nonconformance waste forms are

present to support waste characterization and processing,

confirmation, treatment, and/or certification.

THE FOLLOWING SECTIONS BRIEFLY DISCUSS THE

GENERAL OPERATIONAL ACTIVITIES CONDUCTED

AT WRAP:

PACKAGING AND REPACKAGING WASTE

Packaging and repackaging activities are performed for waste

generated at WRAP as well as for onsite and offsite

generators. The repackaging of waste supports waste

acceptance criteria for other TSD facilities. For example:

prohibited items from waste packages (i.e., waste items that

do not meet acceptance criteria) are removed and either

staged for later handling or repackaging using remote or

manual methods, and must have a void space of less than

10%. To meet the less than 10% requirement, void filler can

be added. Packaging and repackaging activities can include

the following:

• Adding absorbent

• Aerosol can/drum puncturing

• Compositing/aggregating solids or liquids

• Over packing

• Pressure relief/release (e.g., aerosol cans, gas cylinders,

drums, or other similar containers)

• Removing prohibited items

• Segregation

• Size reduction [e.g., cutting (jaws, saws)], bending, folding,

crushing (e.g., drum crusher), shredding, compacting, or

similar methods that do not have a higher extent of

disruption]

• Sorting

• Void filling

Some packaging of waste (e.g., personal protective

equipment, maintenance waste, types of innocuous waste), as

a result of surveillances/inspections and maintenance that

does have a potential to create minimal airborne

contamination, can occur within the 2336-W Building when

the 296-W-4 exhaust stack emission system is shutdown.

VERIFICATION ACTIVITIES

Verification support activities are provided for waste and

other materials that are generated on or off the Hanford Site.

Verification activities can consist of the following:

• Chemical field screening

• Chemical sampling

• NDE

DOE/RL-2017-02 Rev. 0

B-147


Status


Method

• Physical observation

SAMPLING ACTIVITIES

Sampling of waste generated by operations or by other onsite

or offsite generators is performed. The purpose of sampling is

to confirm process knowledge, characterize waste, support

verification, and determine applicable land disposal

requirements. Sampling can consist of the following:

• Container sampling (liquid, sludge, salt cake, composites).

• Disposition of sample returns (e.g., placement back into the

parent container or another approved container)

• Field screening [e.g., pH paper, oxidizer, volatile organic

analyses (VOAs), or similar screening parameters]

• Headspace gas analysis [typically in support of the WIPP

Project]

• Obtaining a sample for analysis (e.g., grab, composite, or

other similar sampling techniques)

• Shipping/transferring the samples to an approved laboratory

for analysis.

DECONTAMINATION ACTIVITIES

Decontamination activities have been performed since 1997.

Materials, equipment, and waste can be decontaminated (e.g.,

free release, reduce the radiological levels, or other similar

criteria) using a variety of methods. Decontamination at

WRAP can consist of the following:

• Abrasive tools

• Brushing

• Cutting (e.g., removal by sawing, or other similar methods)

• Electrical repairs

• Immersion

• Rust/paint removal

• Scraping

• Washing (e.g., chemicals/detergents)

In addition, WRAP also performs decontamination of WRAP

structures (e.g., building walls, glove boxes, or other similar

surfaces) by any of the above methods.

MAINTENANCE ACTIVITIES

Because of the age of WRAP, current mission, future

mission, support of the cleanup of the Hanford Site, as well as

waste and other materials from offsite generators, a variety of

preventative and/or repair maintenance activities are

performed at WRAP. Some maintenance activities involve

the shutdown of the 296-W-4 exhaust stack.

Maintenance activities can consist of the following:

• Calibrations

• Crane maintenance (bridge crane, jib crane, A frame hoist)

• Electronic systems functional checks and repairs [e.g.,

continuous air monitors (CAMs), personnel contamination

monitors (PCMs), or other similar equipment]

• Painting

• Rollup doors

• Scale systems

• Stack systems (e.g., fan lubes or other similar maintenance

activities)

DOE/RL-2017-02 Rev. 0

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Method

• Transformers

Certain maintenance activities (e.g., wire rope inspections,

lubrication, functional tests, calibrations, or similar innocuous

activities) that do have a potential to generate minimal

airborne contamination can occur within the 2336-W

Building when the 296-W-4 exhaust stack emission system is

shutdown.

WASTE TREATMENT ACTIVITIES

WRAP is a treatment facility permitted by the Washington

State Department of Ecology (Ecology). Treatment activities

can consist of the following:

• Amalgamation

• Deactivation

• Solidification or absorption of free liquids

• Microencapsulation

• Macroencapsulation

• Neutralization of corrosives

• Volume Reduction of waste (e.g., compaction)

STORAGE ACTIVITIES

WRAP is permitted for waste storage by Ecology. WRAP

also stores other materials (e.g., chemicals, equipment, or

similar materials) to support operations. Storage can consist

of the following:

• Container storage (e.g., boxes, drums, ten-drum over packs






activity will consist of sealing an unvented glove bag over the

damaged filter, replacing the filter and removing the glove

bag. Negligible emissions are assumed for this activity such

that they are encompassed within the overall estimate of

emissions for storage activities.

EQUIPMENT, MATERIALS, AND WASTE MOVEMENT

ACTIVITIES










• Placing and storing chemical products in flammable

cabinets, over packing or other approved storage locations


and/or treatment


within buildings, glove boxes, or other approved locations)

HOUSEKEEPING ACTIVITIES

Housekeeping activities involve maintaining WRAP in a

DOE/RL-2017-02 Rev. 0

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Status


Method

clean and orderly condition. Housekeeping activities include

the following:

• Dusting





• Vacuuming


SURVEILLANCE ACTIVITIES




waste containers, buildings, or similar locations.

Surveillances are subject to change (adding, deleting and/or

modifying) as operations, maintenance, engineering, and

radiological control dictates. The following are examples of

surveillances currently performed at WRAP:


1 and March 31)



















PROCESS DESCRIPTION - Nondestructive

Examination/Nondestructive Assay Systems





The NDE/NDA area is used to examine and to certify LLW,

MLLW, TRU, and TRU mixed waste container contents

without opening the containers.

The primary function of NDE is to examine the physical

contents of containers entering and leaving the WRAP to

determine whether there are any noncompliant items or

unacceptable conditions in the containers. This examination

of the containers is accomplished by the use of the real-time

radiography (RTR) systems. The RTR systems consists of an

Continuous








DOE/RL-2017-02 Rev. 0

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Status


Method

x-ray imaging systems used to identify noncompliant items,

such as free or containerized liquids, compressed gas

containers including aerosol cans, and other suspected

dangerous waste/materials. Data from the x-ray examinations

are entered into the data management system for each

container.

The primary function of NDA is to determine the activity

levels of radionuclides in the radioactive material entering

and leaving the WRAP. This information is used to categorize

the radioactive material, provide inventory control

information, determine appropriate handling of individual

containers, and to determine if the material meets applicable

transportation and disposal criteria. The NDA equipment

includes passive-active neutron assay systems and/or gamma

energy analysis systems. Data from the analysis of each

container are entered into the data management system.

PROCESS DESCRIPTION - Storage Activities





WRAP is permitted for waste storage by Ecology. WRAP

also stores other materials (e.g., chemicals, equipment, or

similar materials) to support operations. Storage can consist

of the following:

• Container storage (e.g., boxes, drums, ten-drum overpacks






activity will consist of sealing an unvented glovebag over the

damaged filter, replacing the filter and removing the

glovebag. Negligible emissions are assumed for this activity

such that they are encompassed within the overall estimate of

emissions for storage activities

Continuous








PROCESS DESCRIPTION - Housekeeping Activities





Housekeeping activities involve maintaining WRAP in a

clean and orderly condition. Housekeeping activities include

the following:

• Dusting





• Vacuuming


Continuous








DOE/RL-2017-02 Rev. 0

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Method

PROCESS DESCRIPTION - Surveillance Activities








waste containers, buildings, or similar locations.

Surveillances are subject to change (adding, deleting and/or

modifying) as operations, maintenance, engineering, and

radiological control dictates. The following are examples of

surveillances currently performed at WRAP:


1 and March 31)



















Continuous








PROCESS DESCRIPTION - Shipping and Receiving





Containers are delivered to and transferred from the shipping

and receiving area by truck or forklift. In the shipping and

receiving area, incoming boxes and drums are unloaded,

visually inspected, labeled, and radiologically surveyed. The

resulting information pertaining to each container is entered

into the data management system. Following visual

inspection, containers are transferred to the lag storage area.

From the lag storage area, incoming drums are transferred to

a weigh station and on to the NDE/NDA area for further

characterization. If there are any noncompliant items or

unacceptable conditions discovered in the NDE process, the

containers are transferred to the process area for repackaging.

Once characterized, verified, and/or certified, the certified

TRU waste is loaded into transuranic package transporter

(TRUPACT-2 or equivalent) shipping casks for shipment to

Continuous








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Method

the Waste Isolation Pilot Plant (WIPP) in New Mexico or

other approved facility.

PROCESS DESCRIPTION - Equipment, Materials and

Waste Movement Activities.














• Placing and storing chemical products in flammable

cabinets, overpacking or other approved storage locations


and/or treatment


within buildings, gloveboxes, or other approved locations

Continuous









NOC: 241-AP Tank Farm Ventilation System Upgrades Installation and Pre Operational Permit for 241-

SY/AP/AY/AZ Tank Farm Exhauster Upgrade



Permit: AIR 12-307 – D Issue Date: 03-06-12 Effective Date: 02-23-12 Obsolete Date: 07-29-15

NOC: Categorical Tank Farm Facility Waste Retrieval and Closure: Phase II Waste Retrieval Operations









Continuous



Inventory Logbook, HNF-N-42,

was <15,000 DE-Ci/year basis

for this NOC limit in the

application.

This approval applies only to those activities described

below. No additional activities or variations on the approved Continuous


demonstrate that activities at T

DOE/RL-2017-02 Rev. 0

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Method



This consolidated T-Plant license supersedes all radioactive

air licenses for 291-T-1.

a. This approval subsumes those activities approved in three

previous license approvals, retains/revises the specific

conditions and limitations of those approvals, and replaces

them as the radioactive air license for T-Plant:

i. AIR 03-1208 (NOC ID # 445, "Storage in T-Plant Complex

of Sludge from K-Basins")

ii. AIR 01-1010 (NOC ID # 499, "T-Plant Complex Fuel

Removal Project")

iii. AIR 02-704 (NOC ID # 500, "Entering and Characterizing

of the 224-T Facility Process Cells")

b. With additional conditions and limitations provided herein,

this approval also extends to new activities discussed in the

NOC application "Radioactive Air Emissions Notice of

Construction for Consolidated T Plant Operations", DOE/RL-

2004-50, Rev.0, September, 2004, described briefly:

i. Receipt, Storage, Treatment, and Loads out of Contact-


Transuranic Mixed Waste (M-91 Initiative)

ii. Treatment (in addition to storage) of K-Basin Sludge from

the North Load out Pit (NLOP)

iii. Such activities considered routine at T Plant as are

described in succeeding conditions.

Activities a)i through a)iii may emit radioactive air through

291-T-1. Additionally, activity a)iii may emit to the 200 Area

Diffuse & Fugitive emission unit and to Portable Temporary

Radioactive Air Emission Units.

Plant are as described in the

NOC.

Comment: 224-T was removed

from the license on 2/16/2017

(AIR 17-206).


030(21a-e) [as specified in the application] is 1.20E+02



Alpha-0 1.78E-04 Beta-0 5.49E-05






Department of any changes to a NESHAP major emission

unit when a specific isotope is newly identified as

contributing greater than 10% of the potential TEDE to the

MEI, or greater than 25% of the TEDE to the MEI after

controls. (WAC 246-247-110(9)). DOE must notify the

Department of any changes to potential release rates as

required by state or federal regulations including changes that

would constitute a significant modification to the AIR

Operating Permit under WAC 173-401-725(4). Notice will be

Continuous



Inventory Logbook, HNF-N-42,

was <15,000 DE-Ci/year basis

for this NOC limit in the

application.

DOE/RL-2017-02 Rev. 0

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Method

provided according to the particular regulation under which

notification is required. If the applicable regulation(s) does

not address manner and type of notification, DOE will

provide the Department with advance written notice by letter

or electronic mail but not solely by copies of documents.

A. Entry/Characterization of 224-T Process Cells:

A1) (Deleted)

A2) All work covered by this NOC must be completed by

December 31, 2005.

A3) (Deleted)

A4) (Deleted)

A5) HPT coverage shall be provided during all cell entries

and excavation activities.

A6) (Deleted)

A7) When a HEPA Filtered Vacuum Radioactive Air

Emission Unit (HEPA VAC) is used, the condition, controls,

monitoring requirements and limitations of the latest

approved revision of the HEPA VAC Notice of Construction

shall be required.

A8) (Deleted)

A9) Approved activities for the Entry/Characterization of

224-T Process Cells are:

A9a) Approval extends to entry of the 224-T Facility to

determine the condition and contents of the facility's cells,

tanks, and vessels, as described below: A containment tent

shall be erected outside each access door. The containment

tent shall consist of two or more chambers, where the inner

chamber shall surround the cell door and the outer chamber

shall function as an airlock. Alpha and beta continuous air

monitors (CAM) shall monitor each chamber and shall run

continuously whenever the cell door is open. The inner

chamber shall be fitted with a Type I portable temporary

radioactive air emissions unit (PTRAEU) exhauster to

provide air flow and contamination control in the containment

tent. The exhauster shall be run intermittently to control

radiological conditions, at the direction of the field work

supervisor in collaboration with the health physics technician

(HPT). The containment tent shall be isolated from the cell

(door closed or otherwise blocked) before operating the

exhauster. The Type I PTRAEU shall be used in accordance

with the conditions, controls, monitoring requirements and

limitations of the latest approved revision of the PTRAEU

NOC (DOE/RL-96-75)

A9b) The following characterization activities are allowed in

the cells and/or containment tent:

A9b1) Establishing radiological conditions/map (i.e., dose

rates, smearable and fixed contamination, and airborne

concentrations).

A9b2) Nondestructive data analyses (NDA) measurements of

equipment.

A9b3) Collection of liquid and solid samples from open

vessels, trenches, or sumps.

A9b4) Collection of ultrasonic data on vessels and piping.

Continuous

CDM: No entries or

characterizations occurred in

the 224-T Process Cells for this

reporting period, therefore this

requirement was not triggered.

Comment: 224-T was removed

from the license on 2/16/2017

(AIR 17-206).

DOE/RL-2017-02 Rev. 0

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Method

A9b5) Taking photographs.

A9b6) Performing visual inspections.

A9b7) Removing flanges to collect samples from inside

equipment or piping.

A9b8) Cutting or drilling into piping to collect samples with

appropriate equipment such as a reciprocating saw, a circular

saw, a hacksaw, a tri-tool, or an abrasive wheel.

Aa9b9) Minor decontamination activities such a wiping

down, applying fixatives or sealants, etc., performed in the

cell or in the containment tent.

A9b10) Decontamination to reduce dose rates or remove

contamination for personnel safety, to remove

characterization equipment brought in, or to remove

incidental loose equipment or waste found in the cell.

A9b11) Size reduction and packaging and containerizing

incidental, loose equipment or waste found in the cell for

removal and /or disposal.

A9b12) Removal of infiltrated water from the pit and the

submerged tanks in C-Cell by pumping into tanker trucks for

subsequent disposal.

A9b13) Characterization of the removed water prior to

disposal.

A9b14) Investigation of the source of water infiltrated into C-

Cell.

A9b15) Sealing and grouting of leaks causing water

infiltration.

A9b16) A small amount of excavation is allowed to take

place around the cell access doors to support installation of

the containment tents. Manual digging methods with shovels,

picks and rakes shall be used. Up to two cubic meters of

contaminated may be disturbed.

A9b17) Within the containment tent, the weather barrier

cover over the cell access door shall be removed. The

integrity and functionality of the cell door shall be determined

and as a result the door may be removed and replaced with

another door. Any other physical barrier that limits access to

the cell also shall be removed.

A9b18) (Deleted) (WAC 246-247-040(5)

Actions to assure quality of periodic confirmatory

measurement shall be as follows:

(1) Implementation of quality checks supporting the periodic

confirmatory measurements. These checks shall assure that

the emissions measurements are sufficient to verify low

emissions.

(2) (Deleted)

(3) An annual calibration will be performed on the existing

sample flow meter or an annual function check will be

performed if the flow meter is replaced by either a rotameter

or a magnahelic gauge.

(4) The effluent samples will be collected on standard (very

high efficiency particulate air) sample filters.

(5) The laboratory sample analysis will meet the requirements

of Appendix B, Method 114(3); and

Continuous

CDM: NESHAP Quality




DOE/RL-2017-02 Rev. 0

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Method

(6) The following items shall be documented in a NESHAP

Quality Assurance Project Plan or other documents.

(i) The sample collection and analysis procedures used.

(ii) The quality control program for evaluation and tracking

the quality of the periodic confirmatory measurement data

against preset criteria. The quality control program should

include, where applicable, a system of replicates, spiked

samples, split samples, blanks and control charts. The number

and frequency of such quality control checks shall be

identified: and

(iii) The sample tracking system to provide positive

identification of samples and data through all phases of the

sample collection, analysis, and reporting system. Sample

handling and preservation procedures, to maintain the

integrity of the samples during collection, storage, and

analysis. (WAC 246-247- 040(5))(WAC 246-247-

075(3))(WAC 246-247-075(6))(WAC 246-247-075(13)).

After backfilling, the soil surface radiological contamination

levels shall be verified to be less than 5,000 dpm/100 cm^2

beta/gamma and less than 100 dpm/100 cm^2 alpha. If

contamination is present above these levels, the contaminated

soil shall be removed and containerized for disposal or

covered or fixed to provide containment of the contamination.

(WAC 246-247-040(5))

Continuous

CDM: Soil excavating

activities did not take place

during this reporting period,

therefore this backfilling

requirement was not triggered.

All activities involving radioactive materials shall be

conducted in accordance with radiation control procedures

approved in accord with applicable QA program. (WAC 246-

247-040(5))

Continuous

CDM: CHPRC Radiological

Control Manual (CHPRC-

00073).

Appropriate excavation controls such as water, fixatives,

covers, or windscreens shall be applied, if needed, as

determined by the contractor's Health Physics organization.

Spoil piles containing contaminated soil shall be segregated

from the clean soil. Containerizing soil for disposal may also

be performed. (WAC 246-247-040(5))(WAC 246-247-

060(5))

Continuous




therefore these excavation

control requirements were not

triggered.

If a Portable/Temporary Radioactive Air Emission Unit

(PTRAEU) is used, the conditions, controls, monitoring

requirements and limitations of the latest approved version of

the PTRAEU Notice of Construction shall be required. (WAC

246-247-060(5))(WAC 246-247-080(7))

Continuous

CDM: No activities requiring

the use of the PTRAEU NOC

occurred at the T Plant

Complex during the reporting

period, therefore this

requirement to follow the

PTRAEU NOC was not

triggered.

Comment: DO-021-030,

Operate Portable Exhauster.

Periodic confirmatory measurements (PCM) for the diffuse

and fugitive emissions shall be performed and shall consist of

the radiological surveys from the soil excavation activities.

Compliance shall be demonstrated by showing that actual

Continuous

CDM: Soil excavating or

PTRAEU activities did not take

place during this reporting

period, therefore these PCM

DOE/RL-2017-02 Rev. 0

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Method

emissions are inherently less than the estimated emissions,

which are based and calculated from the same contamination

levels.

If a PTRAEU of HEPA filtered vacuum radioactive air

emission unit is used, PCM for emissions from those units

shall be performed as required by the respective NOCs.

(WAC 246-247-040(5))(WAC 246-247-080(7))

requirements were not

triggered.

The dose to the maximally exposed member of the public

from unabated diffuse and fugitive emissions associated with

excavation activities under this NOC shall not exceed 3.05E-

03 mrem/year. For the purposes of dose estimation, gross beta

air concentrations shall be conservatively assumed to consist

entirely of Sr-90. Also for the purposes of dose estimation,

gross alpha air concentrations associated with excavation

under this NOC shall be conservatively assumed to consist

entirely of Am-241. (WAC 246-247-040(5))

Continuous




therefore this dose limit was not

exceeded.

Total volume of contaminated soil disturbed in excavation for

installation of containment tents shall not exceed two cubic

meters. (WAC 246-247-040(5))

Continuous




therefore the total volume limit

was not exceeded.

Permit: AIR 12-317 - D Issue Date: 03-06-12 Effective Date: 02-23-12




Permit: AIR 12-318 – B Issue Date: 03-06-12 Effective Date: 02-23-12 Obsolete Date: 10-01-15

NOC: Categorical Tank Farm Facility Entry and Surveillance



Permit: AIR 12-320 - C Issue Date: 03-06-12 Effective Date: 02-23-12 Obsolete Date: 10-01-15




DOE/RL-2017-02 Rev. 0

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NOC: Vapor Sampling of Miscellaneous Underground Units




NOC: 241-AN Tank Farm Installation and Operation of a New Ventilation System




NOC: 241-AW Tank Farm Installation and Operation of a New Ventilation System




NOC: Characterization and Stabilization Activities Involving Radioactive Contamination at Facilities on the

Central Plateau





Continuous



(or other source

data/information) for CY 2016

to verify total abated emissions

are below the NOC limit. See

below (Compliance Log

submitted by June 30).




as defined in (WAC 246-247-030(16)), may be conducted.

The approved activities are limited to:

The characterization and stabilization (as defined in other

conditions) of emission units within 200 West and 200 East

areas, and 212 N, 212 P, and 212 R. (WAC 246-247-040(5))

Continuous

CDM: Review of work

management and job control

system records. Reviewed

applicable radionuclide air

emissions data (or other source








Alpha-0 | 3.50E-03 | Liquid/Particulate Solid | WAC 246-247-

030(21)(a)

License PTE limit bounds 3.5 Ci/yr 241Am and release

Continuous

CDM: Estimated PTE for each

activity performed under this

NOC.

DOE/RL-2017-02 Rev. 0

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Status


Method

fraction of 0.001. Any radionuclide on the chart of the

nuclides could be encountered during characterization and

stabilization operations. The radionuclides specifically listed

in the NOC application were chosen to conservatively

represent all radionuclide emissions that may occur in

particulate form. A small contribution from the gaseous

radionuclides may be encountered. Although any radionuclide

could be present, for conservatism all beta/gamma is assumed

to be Cs-137 and all alpha is assumed to be Am-241 for dose

calculation estimates. Other radionuclides may be

encountered and are approved so long as they are

conservatively represented by the total alpha and total beta-

gamma constituents.

B/G-0 | 1.40E-02 | Liquid/Particulate Solid | WAC 246-247-

030(21)(a)

License PTE limit bounds 14.0 Ci/yr 137Cs and release

fraction of 0.001. Any radionuclide on the chart of the

nuclides could be encountered during characterization and

stabilization operations. The radionuclides specifically listed

in the NOC application were chosen to conservatively

represent all radionuclide emissions that may occur in

particulate form. A small contribution from the gaseous

radionuclides may be encountered. Although any radionuclide

could be present, for conservatism all beta/gamma is assumed

to be Cs-137 and all alpha is assumed to be Am-241 for dose

calculation estimates. Other radionuclides may be

encountered and are approved so long as they are

conservatively represented by the total alpha and total beta-

gamma constituents.










controls. (WAC 246-247-110(9)) DOE must notify the



would constitute a significant modification to the Air

Operating Permit under WAC 173-401-725(4). Notice will be






The basis for selection of radioactive air controls/abatements

for each emission unit shall be documented in sufficient detail

to demonstrate compliance. DOH may audit the controls and

Not

Applicable




DOE/RL-2017-02 Rev. 0

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Status


Method

determination of containment risk under this NOC, and

independently judge the adequacy of controls, assigned risk

and risk components for any activity. (WAC 246-247-040(5))

and WAC 246-247-080 (1, 8, 10))



or fact, that pertain to actions to

be completed in the future, or


of the agency.

Soil Excavation Associated with

Characterization/Stabilization: Soil may be excavated to

support characterization/stabilization of central plateau

emission units. An initial survey shall be performed of the

area to be excavated. Surveys shall be performed throughout

the excavation to assure that environmental protection is

maintained. Once the excavation begins, water or other

fixative of equal or better effectiveness shall be used, as

necessary, to prevent the spread of dust. To the extent

practicable using hand held instrument field survey

techniques, the clean soil shall be separated from the soil

identified as contaminated. The contaminated soil shall have a

fixative applied or shall be covered by plastic at the end of the

shift, and as necessary, to stabilize the contaminated soil.

Radiological Controls for Soil Excavation:

A. Health Physics coverage shall be provided as specified in

the radiological work permit. DOH does not approve work

permits. DOH may independently judge the adequacy of the

Health Physics coverage. Licensee shall maintain records of

Health Physics coverage and survey results.

B. Beta-gamma surveys of the ground surface are required

prior to excavation in Contamination Areas (CA's), High

Contamination Areas (HCA's), Soil Contamination Areas

(SCA's), and Underground Radioactive Material Areas

(URMA's). If in an area of known or suspected alpha

contamination, or if beta/gamma contamination is detected,

alpha surveys shall be performed as well.

C. Suppressants such as water, fixatives, covers, or

windscreens shall be used as necessary, including at the end

of each shift or when sustained or predicted winds are >20

mph.

D. Excavation of radioactive material shall not commence if

sustained winds are predicted to exceed 20 mph during the

work shift.

E. Excavation of radioactive material shall cease if sustained

winds exceed 20 mph. A local wind-speed measurement

device may be utilized in lieu of Hanford Meteorological

Station readings, provided the reading is taken in an

unobstructed location that is representative of the work area.

Use of a local device and the measured wind-speed readings

taken from it must be documented, and the documentation

retained.

F. If the contamination for the general area is greater than

2000 dpm/100 sq.cm. alpha or greater than 100,000 dpm/100

cm.sq. beta-gamma, place in a safe and stable condition and

Continuous

CDM: No excavation activities

were conducted under this NOC

during the reporting period.

DOE/RL-2017-02 Rev. 0

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Status


Method

stop work, notify DOH, and implement the controls listed

below. Once notifications have been made and the following

controls implemented, excavation may continue:

a. Soil shall be wetted prior to excavation if not already damp.

b. General area workplace air monitoring shall be performed

during excavation activities.

c. Excavation and contaminated soil piles shall be covered

with plastic, or fixative shall be applied, at the end of each

shift or as necessary to prevent the spread of airborne

contamination.

G. Contaminated soil containing >100,000 dpm/100 sq.cm.

beta-gamma or >2000 dpm/100 sq.cm. alpha shall be

containerized or covered with clean fill if it is to be left for

greater than 48 hours.

H. If soil contamination exceeds 20 mrad/hour (open window

reading), work shall be stopped and placed in a safe and

stable condition, and adequacy of controls will be reassessed.

DOH shall be notified (e-mail notification is required). Work

may continue when approved by DOH (e-mail concurrence is

required).

I. If hot specks are detected during the radiological surveys,

the specks shall be removed and contained before the activity

is allowed to continue unless located in the bottom of the

trench after excavation has been completed. Specks found in

the bottom of the completed trench may be covered with

clean fill. A hot speck is defined as a very small amount (i.e.

less than or equal to 100 square centimeters) of

contamination.

Monitoring for Soil Excavation:

J. At a minimum, pre-job and post-job surveys shall be made.

K. Radiological monitoring shall be in accordance with

approved governing procedures. DOH may independently

judge the adequacy of the monitoring.

Records for Soil Excavation:

L. Work instructions (written).

M. Radiological work permit.

N. Radiological survey report(s).

(WAC 246-247-040(5))

DOH reserves the right to require additional monitoring on a

case-by-case basis 6) (WAC 246-247-040(5)).

Not

Applicable






or fact, that pertain to actions to

be completed in the future, or


of the agency.

DOE/RL-2017-02 Rev. 0

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Method

Monitoring: In addition to the monitoring required on page

one of this license, total alpha, total beta/gamma shall be

monitored periodically, the period to be consistent with the

duration of the activity. The bases for the monitoring method

and the period shall be documented. Monitoring records shall

explicitly demonstrate compliance to the limit on TEDE to

the MEI set down in this license. Monitoring may include air

monitoring, or CAM records.

For soil excavation, compliance may be demonstrated via

calculation based on a release fraction of 0.001, appropriate

Hanford dose conversion factors, soil survey records,

excavated volume, and estimated Ci content per unit soil

volume. Unless excavation is conducted in accord with the

DOH approved

Truck (Guzzler) license, credit for abatement or limited

disturbance shall not be taken without prior written approval

by DOH.

The near-field monitoring system is not sufficient in itself to

demonstrate compliance to the emission limits of the license

(WAC 246-247-040 (1, 5, 6)).

Continuous


record review to verify

additional monitoring was

implemented.

The characterization and stabilization activities licensed are

limited to emission units managed by DOE/RL within the 200

West and 200 East areas, and 212 N, 212 P, and 212 R. DOH

shall be informed, and written DOH concurrence obtained,

prior to initiation of stabilization activities at 212 N, 212 P, or

212 R (WAC 246-247-040(5)).

Continuous

CDM: Review of work

management and job control

system records. Reviewed

applicable radionuclide air

emissions data (or other source




The characterization and stabilization activities licensed are

limited to emission units listed in a compliance log

maintained by a DOE central coordinator. The compliance

log shall initially categorize each emission unit as low or high

PTE on the basis of best available information. Low PTE is

defined as 1.0 E-3 mrem/year or less, and high PTE is defined

as greater than 1.0 E-3 mrem/year.

Stabilization activities shall not be initiated for high PTE

emission units without written DOH approval. Stabilization

of emission units having PTE greater than 0.1 mrem/year

shall require the submittal of a separate notice of construction

application.

Disturbance factors shall not be used in the determination of

PTE except as by permission of DOH on a case-by-case basis.

The WAC 246-247-030(21)(a) release fractions shall be

assumed, except as may be approved otherwise on a case-by-

case basis.

In the case of emission units in which the work activity may

Continuous

CDM: Compliance Log

submitted by June 30 each year

and updated as needed through

the year; estimates of PTE for

each activity; WDOH

notification/approval

documentation.

DOE/RL-2017-02 Rev. 0

B-163


Status


Method

be effectively isolated from a significant fraction of the

source material comprising the PTE, DOH will, on a case-by-

case basis, consider a suitably defined and calculated PTE

less than that for the whole emission unit. "Effectively

isolated" may but does not necessarily imply physical

barriers. E-mail approval of such cases is required prior to

use.

Emission units may be added to the compliance log, provided

DOH is given the new compliance log entry in writing (e-

mail is sufficient). (WAC 246-247-040(5))

The compliance log shall list estimated or measured actual

calendar year emissions for each emission unit on which

stabilization activities have commenced. Additionally, the

compliance log shall provide a total project actual emission

for the calendar year (WAC 246-247-040(5)).

Continuous

CDM: Compliance Log



the year.

An initial copy of the compliance log shall be formally

transmitted to DOH by June 30 or prior to initiating any

activities under the license, whichever comes first. This initial

transmittal shall provide all log information available by the

time of submittal, and shall also include a projected list of

emission units to be addressed under the license during the

next 12 months. Following the date of the first transmittal,

and by June 30 of each year, a copy of the previous calendar

year compliance log shall be formally transmitted to DOH,

along with a projected list of emission units to be addressed

under the license during the next 12 months. The log shall be

available for DOH inspection (WAC 246-247-040(5)).

Continuous

CDM: Compliance Log



the year.

Characterization means entry and

radiological/industrial/chemical characterization activities,

not to include activities defined as stabilization below. The

license allows characterization of low and high PTE emission

units. Characterization is expected to improve the accuracy

with which the PTE is estimated for a particular emission

unit. Characterization data shall be documented to confirm

the initial categorization:

a. Characterization data may require the upgrading of a

particular emission unit from low to high PTE. DOH shall

then be informed, and written DOH concurrence to proceed to

stabilization shall be required (email is adequate).

b. Characterization data may allow the downgrading of a

particular emission unit from high to low PTE. DOH shall

then be informed (e-mail). The basis for the downgrading

shall be provided to DOH as part of this information.

c. Characterization activities shall be conducted in accord

with the ALARA principle. (WAC 246-247-040(5))

Continuous

CDM: Compliance Log and

work management and job

control system records.

Stabilization means the size reduction, packaging/removal or

fixing of whatever contamination or radioactive material may

be removed or fixed without altering the existing emission

unit structure or environmental containment function.

Continuous

CDM: Compliance Log and

work management and job

control system records.

DOE/RL-2017-02 Rev. 0

B-164


Status


Method

Stabilization is not to proceed without first obtaining

characterization data as above.

a. Stabilization activities shall be conducted in accord with

the ALARA principle.

b. Monitoring and documentation sufficient to demonstrate

compliance shall be maintained.

c. Disposition and transportation of removed material shall be

in accord with applicable regulations.

(WAC 246-247-040(5))


NOC: Operation of the Integrated Disposal Facility (IDF)




NOC: Cleaning Radiologically Contaminated Vehicles



Permit: AIR 12-329 - B Issue Date: 03-06-12 Effective Date: 02-23-12 Obsolete Date: 07-23-15

NOC: Removal of Liquid from Catch Tank 241-ER-311




NOC: Decontamination Trailer at the Transuranic Waste Retrieval Project




NOC: Tank Farms - Phase 1-Waste Retrieval and Closure




NOC: 244-CR Vault Isolation and Interim Stabilization



DOE/RL-2017-02 Rev. 0

B-165


Status


Method


NOC: Tank Waste Remediation System Vadose Zone Characterization




NOC: Tank Farm Decontamination Trailer East




NOC: Tank Farm Decontamination Trailer West




Maximally Exposed Individual (WAC 246-247-040(5)). The

total limit on the Potential-To-Emit for this Notice of



Continuous

Records review and field

interviews including log entries,

ABCASH, and event reports.





a. Upon identification of the need of additional

decontamination activities in the 200 area, individuals would

be escorted to the nearest decontamination trailer.

b. As appropriate, contaminated clothing, coverings, and/or

articles will be removed and packaged for laboratory analysis

and/or disposition, in accordance with As Low As

Reasonably Achievable Control Technology (ALARACT) 4

and 12, Tank Farm ALARACT Demonstration for Packaging

and Transportation of Waste and Tank Farm ALARACT

Demonstration for Packaging and Transportation of

Equipment and Vehicles, RPP HNF-4327.

c. Personnel decontamination processes might include various

methods or a combination of cleaning agents and /or

chemicals. For example: soap and water, pre-moistened

towelettes, removal of hair, abrasive soaps for toughened skin

surfaces (e.g., hands and feet), and chelating agents.

d. Spent decontamination solutions will be transferred from

the holding tanks and/or bladder and containerized (e.g.,

packaged in absorbents in drums or placed in drums or

Continuous




DOE/RL-2017-02 Rev. 0

B-166


Status


Method

carboys) and transported to existing facilities on the Hanford

Site for disposal.

e. Periodic maintenance inspection of the decontamination

trailers will be performed without the use of containment or

portable exhausters.



Pu-239 1.40E-01

Alpha rates are based on PU-239+D. While the potential

release rates for all emissions are conservatively represented

by Pu-239+D (Alpha) and Sr-90+D (Beta/gamma),

essentially any radionuclide may be present.

Sr-90 1.40E-01

Beta/Gamma release rates are based on Sr-90+D. While the

potential release rates for all emissions are conservatively

represented by Pu-239+D (Alpha) and Sr-90+D

(Beta/gamma), essentially any radionuclide may be present.

Continuous




The proposed periodic confirmatory monitoring (PCM) for

the diffuse and fugitive emissions shall consist of the

radiological surveys during and at the completion of

personnel decontamination operations (e.g., smears and direct

readings on the interior of the decontamination trailers). The

methods of PCM are not a direct measurement of effluent

emissions. The methods are intended to demonstrate

compliance by showing that the levels on the interior of the

trailers, during a personnel decontamination operation, are

controlled; and the levels on the interior of the trailers after a

decontamination operation shall keep the trailers from being

posted a radiological buffer area (RBA) for contamination

control and/or a contamination area (CA). This shall make the

actual emissions below the estimated emissions, which shall

be based and calculated from the same contamination levels.

Continuous




When Portable Temporary Radioactive Air Emission Units

are used they shall follow all the requirements of the latest

revision of the Radioactive Air Emissions Notice of

Construction for Portable Temporary Radioactive Air

Emission Units (DOE/RL-96-75).

Continuous

CDM: PTREAU was not used

during this reporting period. Comment: No activities were

conducted requiring the use of

this NOC during the reporting

period.

When Tank Farm Decontamination Trailer West is activated

under this approval, and ventilation is not used, a log shall be

maintained to document emissions. The log shall contain

records of important operations parameters including the date,

location, and duration of the release, measured or calculated

radionuclide concentrations, the type of emissions (liquid,

gaseous, solid), and the type of emission control and

monitoring equipment. The emissions may be calculated from

the best estimate of radiological material from surveys

Continuous




DOE/RL-2017-02 Rev. 0

B-167


Status


Method

performed during personnel decontamination operations

(WAC 246-247-040(5) and WAC 246-247-060(5)).

Permit: AIR 12-1001 - A Issue Date: 09-27-12 Effective Date: 09-27-12 Obsolete Date: 10-01-15

NOC: E-525 Double-Shell Tank (DST) Transfer System Modifications Project




NOC: Sidewall Coring of Single Shell Tanks




NOC: Diffuse and Fugitive Operations at LERF and ETF




NOC: Removal and Disposal of the Obsolete 242A Evaporator Building K-1 Exhauster






Status


Method


Zone or Area :


Required Units : 1

Add'l Description:



Zone or Area :


Required Units : 1

Add'l Description:



Zone or Area :


Required Units : 1

Add'l Description:



DOE/RL-2017-02 Rev. 0

B-168

Zone or Area :


Required Units : 2

Add'l Description: 2 HEPA filters in series



Zone or Area :


Required Units : 1

Add'l Description:








61.93(b)(4)(i) & WAC 246-247-075(2)





Permit: AIR 12-332 - C Issue Date: 03-06-12 Effective Date: 02-23-12




J Nonpoint Source WDOH Emission Unit ID: 504



Status


Method





facility monitoring stations


program



to-emit TEDE

Not

applicable

Comment: Emission unit was

closed on September 18, 2014.

Official closure acceptance by

WDOH was provided on

March 5, 2015.


247-075(3)



Not

applicable

Comment: Emission unit was

closed on September 18, 2014.

Official closure acceptance by

WDOH was provided on

March 5, 2015.

DOE/RL-2017-02 Rev. 0

B-169





Status


Method


Zone or Area:

Abatement Technology:

Required Units: Add'l Description: Abatement controls as required in the

following Conditions and Limitations.

Continuous

CDM: There are no active

NOC approvals for 100-K

Area associated with the 100

Diffuse and Fugitive emission

unit in the AOP for this

certification period.





program


that could contribute greater than 10 percent of the potential

TEDE

Continuous








247-075(3)



Continuous








P-244CR-002 WDOH Emission Unit ID: 713



Status


Method



Required Units: 1

Add'l Description: Passive Breather Filter



DOE/RL-2017-02 Rev. 0

B-170

Required Sampling: Smear survey on the inside surface of

the ducting and downstream of the HEPA filter or on the

outside of the screen covering the outlet of the vent

Sampling Frequency: 1 per year

Radionuclide Requiring Measurement: Levels below

10,000 dpm/ 100 cm2 beta/gamma and 200 dpm/100 cm2 alpha

will verify low emission.

Continuous CDM: Radiological Survey

Reports.


60.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,

Appendix B Method 114 does

not apply, as clarified in

Attachment 2 Section 4.0,

because this EU does not use

sample extraction as its PCM.

Permit: AIR 12-332 – D Issue Date: 03-06-12 Effective Date: 02-23-12







Status


Method


Zone or Area :


Required Units : 1

Add'l Description: Operational at all times, when the

exhauster is in use.



Zone or Area :


Required Units : 1





Zone or Area :


Required Units : 1

Add'l Description:



Zone or Area :


Required Units : 2

Add'l Description: In series.



Zone or Area :


Required Units : 1

Add'l Description:



DOE/RL-2017-02 Rev. 0

B-171

Required Sampling: Record sample


Radionuclide Requiring Measurement: Sr-90, Cs-137, Am-

241, Y-90, Cs-134, Pa-231, Pu-238, Pu-239, Pu-240, Pu-241

Continuous


Field interviews and WRPS

work documents.


61.93(b)(4)(i) & WAC 246-247-075(2)



Continuous



Permit: AIR 11-1004 - A Issue Date: 10-18-11 Effective Date: 10-10-11 Obsolete Date: 01-01-17

NOC: Operation of New Ventilation Systems in AN and AW Tank Farms



is limited to 2.60E+00 mrem/year to the Maximally Exposed



3.30E+02 mrem/year to the Maximally Exposed Individual

(WAC 246-247-030(21)).

Continuous



(ABCASH), or other source

data/ information for CY 2016







The 296-A-44 and 296-A-45 shall ventilate the 241-AN Double

Shell Tank (DST) Farm which consists of seven individual

DSTs. The 296-A-46 and 296-A-47 shall ventilate the 241-AW

Double Shell Tank (DST) Farm which consists of six

individual DSTs. The DSTs are fabricated as two concentric

tanks surrounded by a concrete shell. The inner tank containing

the waste is 75 feet in diameter and 46.8 feet high at the crown.

Each tank stores 1.14E6 gallons. The DSTs are used for

storage, treatment, retrieval, and disposal of the waste

contained in the tanks, as well as transfers to the Waste

Treatment Plant.

The 296-A-44, 296-A-45, 296-A-46 and 296-A-47 ventilation

systems serve to remove heat, and serve as containment

systems for radioactive particulates present in the tank

headspace, they ventilate/remove flammable gases and vapors

that evolve from the liquid surface in the DSTs. The ventilation

systems do this by drawing air into the tank vapor space. After

the air leaves the vapor space the air is conditioned by the

ventilation system. It removes entrained moisture, the relative

humidity is reduced, and particulates are filtered out. Before

discharge of this air to the atmosphere from the stack, the air is

monitored and sampled for radionuclide particulates.

Occasionally, the exhausters may be shut down for testing and

sampling purposes to evaluate waste conditions, meteorological

effects, and/or ventilation configuration on individual DST

Ventilation rates.





Intermittent

CDM: TWINS, WRPS



Comment: Review of TWINS

DOE/RL-2017-02 Rev. 0

B-172

Ac-227 1.30E+02 Am-241 1.03E+05

Am-243 1.37E+01 Ba-137 m 1.75E+07

C-14 5.07E+02 Cd-113 m 7.50E+03

Cm-242 7.57E+01 Cm-243 8.35E+00

Cm-244 2.36E+02 Co-60 4.46E+03

Cs-134 1.81E+04 Cs-137 1.85E+07

Eu-152 1.06E+03 Eu-154 4.63E+04

Eu-155 4.56E+04 H-3 2.71E+03

I-129 9.18E+00 Nb-93 m 1.82E+03

Ni-59 7.70E+02 Ni-63 7.26E+04

Np-237 6.20E+01 Pa-231 2.70E+02

Pu-238 3.04E+03 Pu-239 2.92E+04

Pu-240 5.25E+03 Pu-241 6.40E+04

Pu-242 4.05E-01 Ra-226 2.38E+02

Ra-228 3.87E+01 Ru-106 1.02E+03

Sb-125 2.06E+04 Se-79 5.70E+01

Sm-151 1.53E+06 Sn-126 2.40E+02

Sr-90 2.30E+07 Tc-99 6.89E+03

Th-229 2.49E+01 Th-232 6.16E+00

U-232 2.79E+01 U-233 4.48E+02

U-234 6.76E+01 U-235 2.58E+00

U-236 2.87E+00 U-238 5.61E+01

Y-90 2.30E+07 Zr-93 1.86E+03

for CY 2016 has shown U-233

exceeded the APQ, reported per

WRPS notification procedure.

The radiological license was

revised to remove the APQ for

U-233 (AIR 17-103) on

January 1, 2017.

Each HEPA filter shall be in-place tested annually in

accordance with the requirements of ASME AG-1. HEPA

filters shall have a minimum efficiency of 99.95%.



The Annual Possession Quantity shall be tracked on a WDOH

approved log. Continuous CDM: TWINS

The ductwork between the de-entrainer and heater, along with

the filter housings shall be insulated. Continuous



The exhauster shall be operational during all waste transfer,

waste disturbing, or particulate generating activities. Continuous



Prior to operation of the ventilation system a leak test of the

entire train including the ductwork from the exit of the tank to

the entrance to the stack shall be performed meeting the

requirements called out in ASME AG-1.

Continuous



Comment: Leak test was

performed during acceptance

testing in 2008.

The effluent monitoring and sampling system shall meet the

requirements of ANSI N13.1-1999. A written technical basis

document required by Section 4 of ANSI N13.1-1999 shall be

provided to WDOH for review and approval.

Continuous



Comment: RPP-ENV-46801

submitted to WDOH in 2010.

Tank waste will be maintained at a ph of 8 or greater to ensure

that the radionuclide C-14 is not emitted as a gas. This

condition will be met by maintaining tank sampling and tank

analysis documents in accordance with the "Waste Chemistry

Continuous

CDM: Review TWINS or other

source data/information to

verify pH value of supernate in

AN Farm is greater than 8.

DOE/RL-2017-02 Rev. 0

B-173

Limits" outlined in the document "Operating Specifications for

the Double-Shell Storage Tanks, OSD-T-151-000007".

When the tracer gas tests and data collection are conducted on

the AN and AW tank farms the tracer gas to be used during the

tests is helium.

Continuous



Comment: Tracer gas test did

not occur in CY 2016.


the AN and AW tank farms the tracer gas helium will be

injected into the double shell tanks at a rate not to exceed 10

cubic feet per minute.

Continuous






the AN and AW tank farms the passive filtered vents will be in

the open position. If a tracer gas test requires the passive

filtered vents to be closed notification to the Washington State

Department of Health will be made indicating when the vents

will be closed and for how long.

Continuous






the AN and AW tank farms no waste disturbing activities will

occur.

Continuous








Status


Method


Zone or Area: Abatement Technology: Deentrainer

Required Units: 1






Required Units: 1





Zone or Area: Abatement Technology: Prefilter

Required Units: 1

Add'l Description:




Required Units: 2




DOE/RL-2017-02 Rev. 0

B-174


Required Units: 1

Add'l Description:



Required Sampling: Record sample collected biweekly.

Sampling Frequency: Continuous.

Radionuclide Requiring Measurement: Sr-90,Cs-137, Am-

241, C-14, Y-90, Cs-134, Eu-154, Ac-227, Pa-231, U-233, Pu-

238, Pu-240, Pu-241, Cm-244.

Continuous


Field interviews and WRPS

work documents.


60.93(b)(4)(i) & WAC 246-247-075(2)













(WAC 246-247-030(21)).

Continuous




data/information for CY 2016







The 296-A-44 and 296-A-45 shall ventilate the 241-AN

Double Shell Tank (DST) Farm which consists of seven

individual DSTs. The 296-A-46 and 296-A-47 shall ventilate

the 241-AW Double Shell Tank (DST) Farm which consists of

six individual DSTs. The DSTs are fabricated as two

concentric tanks surrounded by a concrete shell. The inner

tank containing the waste is 75 feet in diameter and 46.8 feet

high at the crown. Each tank stores 1.14E6 gallons. The DSTs

are used for storage, treatment, retrieval, and disposal of the

waste contained in the tanks, as well as transfers to the Waste

Treatment Plant.





that evolve from the liquid surface in the DSTs. The

ventilation systems do this by drawing air into the tank vapor

space. After the air leaves the vapor space the air is

conditioned by the ventilation system. It removes entrained

moisture, the relative humidity is reduced, and particulates are

filtered out. Before discharge of this air to the atmosphere

from the stack, the air is monitored and sampled for



DOE/RL-2017-02 Rev. 0

B-175

radionuclide particulates.


sampling purposes to evaluate waste conditions,

meteorological effects, and/or ventilation configuration on

individual DST Ventilation rates.



Ac-227 1.30E+02 Am-241 1.03E+05

Am-243 1.37E+01 Ba-137 m 1.75E+07

C-14 5.07E+02 Cd-113 m 7.50E+03

Cm-242 7.57E+01 Cm-243 8.35E+00

Cm-244 2.36E+02 Co-60 4.46E+03

Cs-134 1.81E+04 Cs-137 1.85E+07

Eu-152 1.06E+03 Eu-154 4.63E+04

Eu-155 4.56E+04 H-3 2.71E+03

I-129 9.18E+00 Nb-93 m 1.82E+03

Ni-59 7.70E+02 Ni-63 7.26E+04

Np-237 6.20E+01 Pa-231 2.70E+02

Pu-238 3.04E+03 Pu-239 2.92E+04

Pu-240 5.25E+03 Pu-241 6.40E+04

Pu-242 4.05E-01 Ra-226 2.38E+02

Ra-228 3.87E+01 Ru-106 1.02E+03

Sb-125 2.06E+04 Se-79 5.70E+01

Sm-151 1.53E+06 Sn-126 2.40E+02

Sr-90 2.30E+07 Tc-99 6.89E+03

Th-229 2.49E+01 Th-232 6.16E+00

U-232 2.79E+01 U-233 4.48E+02

U-234 6.76E+01 U-235 2.58E+00

U-236 2.87E+00 U-238 5.61E+01

Y-90 2.30E+07 Zr-93 1.86E+03

Intermittent

CDM: TWINS, WRPS



Comment: Review of TWINS

for CY 2016 showed U-233

exceeded the APQ. This was

reported per WRPS

notification procedure. The

radiological license was

revised to remove the APQ for

U-233 (AIR 17-104) on

January 5, 2017. Effective

date is January 1, 2017.




















Continuous





testing in 2008.

DOE/RL-2017-02 Rev. 0

B-176





Continuous









Limits" outlined in the document "Operating Specifications

for the Double-Shell Storage Tanks, OSD-T-151-000007".

Continuous

CDM: Review TWINS or

other source data/information

to verify pH value of supernate

in AN Farm is greater than 8.


the AN and AW tank farms the tracer gas to be used during

the tests is helium.

Continuous









Continuous






the AN and AW tank farms the passive filtered vents will be

in the open position. If a tracer gas test requires the passive




Continuous







occur.

Continuous








Status


Method


Zone or Area :


Required Units : 1






outside of the screen covering the outlet of the vent.

Additional Requirement

Radial breather filters shall be replaced every 365 days.

Sampling Frequency: Every 365 days



Reports.

DOE/RL-2017-02 Rev. 0

B-177

10,000 dpm/100 cm2 beta/gamma and 200 dpm/100 cm2 alpha

will verify low emissions.


61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,







NOC: Operation of 244-A Primary HEPA Breather Filter







(WAC 246-247-030(21)).

Continuous



(or other source

data/information) to verify total


NOC limit.





The 244-A DCRT is located west of the 241-AN tank farm in

the 200 east area. The DCRT catch tank is a steel vessel with a

volume capacity of 19,000 gallons. The catch tank and the

concrete pit containing the tank define the annulus space.

The tank has been fitted with ventilation breather filters which

serve as static vents for instrument air injected for operating of

liquid measuring devices called weight-factor dip tubes. The

breather filters also allow flammable gases and other vapors to

escape.

There is currently less than 10,000 gallons of waste stored in

the tank. Current operational activities in this tank include

level monitoring for leaks and intrusion by a variety of

methods including dip tubes, manual tapes, zip cords, and

ENRAFs; sampling tank contents, pumping tank contents,

adding flush water used pursuant to ALARACT practices.

The breather filter system will, at a minimum, consist of an

isolation valve (normally open during operation), filter

housing, and HEPA filter. The isolation valve will isolate the

HEPA filter from the tank to facilitate testing of the





Ac-227


DOE/RL-2017-02 Rev. 0

B-178

Alpha-0 1.17E+01

All Alpha radioactivity was attributed to Am-241 Identified as

contributing GREATER than 10% of the potential TEDE to

the MEI

Am-241 Am-243 Ba-137 m

Beta-0 5.31E+03

All Beta radioactivity was attributed to Sr-90 Identified as


the MEI

C-14 Cd-113 m Cm-242 Cm-243 Cm-244

Co-60 Cs-134 Cs-137 Eu-152 Eu-154

Eu-155

Gamma-0 2.84E+03

All Gamma radioactivity was attributed to Cs-137 Identified as


the MEI

H-3 I-129 Nb-93 m Ni-59 Ni-63

Np-237 Pa-231 Pu-238 Pu-239 Pu-240

Pu-241 Pu-242 Ra-226 Ra-228 Ru-106

Sb-125 Se-79 Sm-151 Sn-126 Sr-90

Tc-99 Th-229 Th-232 U-232 U-233

U-234 U-235 U-236 U-238 Y-90 m

Zr-93

ALTERNATE APPROVAL-Annual Replacement

Radial breather filters shall be replaced every 365 days. (WAC

246-247-040(5) and WAC 246-247-075(4)).



P-244BX-002 WDOH Emission Unit ID: 740



Status


Method


Zone or Area :


Required Units : 1












Reports.

DOE/RL-2017-02 Rev. 0

B-179

10,000 dpm/ cm2 beta/gamma and 200 dpm/100 cm2 alpha



60.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,







NOC: Operation of 244-BX Primary HEPA Breather Filter







(WAC 246-247-030(21)).

Continuous











The 244-BX DCRT is located east of the 241-BX Tank Farm

in the 200 east area. This DCRT is a steel vessel with a volume

capacity of 31,000 gallons. The catch tank and the concrete pit

containing the tank define the annulus space.

The tank and annulus have been fitted with ventilation breather

filters which serve as static vents for instrument air injected for

operating of liquid measuring devices called weight-factor dip

tubes. The breather filters also allow flammable gases and

other vapors to escape.










HEPA filter from the tank to facilitate testing of the filter.





Ac-227


DOE/RL-2017-02 Rev. 0

B-180

Alpha-0 2.37E+01



the MEI

Am-241 Am-243 Ba-137 m

Beta-0 1.07E+04



the MEI

C-14 Cd-113 m Cm-242 Cm-243 Cm-244

Co-60 Cs-134 Cs-137 Eu-152 Eu-154

Eu-155

Gamma-0 5.74E+03



the MEI

H-3 I-129 Nb-93 m Ni-59 Ni-63

Np-237 Pa-231 Pu-238 Pu-239 Pu-240

Pu-241 Pu-242 Ra-226 Ra-228 Ru-106

Sb-125 Se-79 Sm-151 Sn-126 Sr-90

Tc-99 Th-229 Th-232 U-232 U-233

U-234 U-235 U-236 U-238 Y-90 m

Zr-93



246-247-040(5) and WAC 246-247-075(4)).

Continuous

CDM: Field interviews, WRPS

work documents and

Radiological Survey Reports.




Status


Method


Zone or Area :


Required Units : 1











Reports.

DOE/RL-2017-02 Rev. 0

B-181

Radionuclide Requiring Measurement: Levels below 10,000

dpm/ cm2 beta/gamma and 200 dpm/100 cm2 alpha will verify

low emission.


60.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,







NOC: Operation of 244-S Primary HEPA Breather Filter







(WAC 246-247-030(21)).

Continuous



(or other source








The 244-S DCRT is located south of the 241-SY Tank Farms

in the 200 west area. This DCRT is a steel vessel with a


concrete pit containing the tank define the annulus space. The

tank and annulus have been fitted with ventilation breather






the tank. Current operational activities in this tank include level

monitoring for leaks and intrusion by a variety of methods

including dip tubes, manual tapes, zip cords, and ENRAFs;

sampling tank contents, pumping tank contents, adding flush

water used pursuant to ALARACT practices.









Ac-227

Alpha-0 1.17E+01



DOE/RL-2017-02 Rev. 0

B-182

contributing GREATER than 10% of the potential TEDE to the

MEI

Am-241 Am-243 Ba-137 m

Beta-0 5.31E+03



MEI

C-14 Cd-113 m Cm-242 Cm-243 Cm-244 Co-60

Cs-134 Cs-137 Eu-152 Eu-154 Eu-155

Gamma-0 2.84E+03



MEI

H-3 I-129 Nb-93 m Ni-59 Ni-63

Np-237 Pa-231 Pu-238 Pu-239 Pu-240

Pu-241 Pu-242 Ra-226 Ra-228 Ru-106

Sb-125 Se-79 Sm-151 Sn-126 Sr-90

Tc-99 Th-229 Th-232 U-232 U-233

U-234 U-235 U-236 U-238 Y-90 m

Zr-93



246-247-040(5) and WAC 246-247-075(4)).



P-244TX-002 WDOH Emission Unit ID: 744



Status


Method


Zone or Area :


Required Units : 1











10,000 dpm/ cm2 beta/gamma and 200 dpm/100 cm2 alpha



Reports.

DOE/RL-2017-02 Rev. 0

B-183


Status


Method


60.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,







NOC: Operation of 244-TX Primary HEPA Breather Filter







(WAC 246-247-030(21)).

Continuous










in WAC 246-247-030(16), maybe conducted.

The 244-TX DCRT is located north of the 241-TX Tank Farm

in the 200 west area. This DCRT is a steel vessel with a






















Ac-227

Alpha-0 2.37E+01



DOE/RL-2017-02 Rev. 0

B-184


Status


Method


the MEI

Am-241 Am-243 Ba-137 m

Beta-0 1.07E+04



the MEI

C-14 Cd-113 m Cm-242 Cm-243 Cm-244

Co-60 Cs-134 Cs-137 Eu-152 Eu-154

Eu-155

Gamma-0 5.74E+03



the MEI

H-3 I-129 Nb-93 m Ni-59 Ni-63

Np-237 Pa-231 Pu-238 Pu-239 Pu-240

Pu-241 Pu-242 Ra-226 Ra-228 Ru-106

Sb-125 Se-79 Sm-151 Sn-126 Sr-90

Tc-99 Th-229 Th-232 U-232 U-233

U-234 U-235 U-236 U-238 Y-90 m

Zr-93



246-247-040(5) and WAC 246-247-075(4)).





P-241AZ301-001 WDOH Emission Unit ID: 751



Status


Method


Zone or Area :





DOE/RL-2017-02 Rev. 0

B-185

Required Units : 1









10,000 dpm/100 cm2 alpha will verify low emissions.


Reports.


61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,







NOC: E-525 Double-Shell Tank (DST) Transfer System Modifications Project







(WAC 246-247-030(21)).

Continuous






NOC limit.




in WAC 246-247-030(16)), may be conducted.

241-AZ-151 CATCH TANK BYPASS

The modification description for the 241-AZ-151 catch tank

bypass modification includes the installation of a new RCRA-

compliant condensate distribution system for condensate

generated from the existing 241-AZ-702 ventilation system.

This will involve tapping into existing ventilation headers.

This work will be done according to ALARACT 16

requirements. This new system will consist of a 1200 gallon

capacity catch tank (241-AZ-301), secondary containment,

piping, pumps, and controls. The system is designed to collect

condensate at rate of 0.29 gallons per minute (154,424 gallons

per year). The tank will be emptied every 2 to 3 days. At that

time, the condensate will be pumped back to one of the 241-

AY or 241-AZ tanks at a rate of 4 to 5 gallons per minute.

Condensate accumulation is currently estimated at between

6000 to 8000 gallons per month- 72,000 to 96,000 gallons per

year.



DOE/RL-2017-02 Rev. 0

B-186

The new 241-AZ-301 tank and system will be located outside

the northeast corner of building 241-AZ-702. Most of the

secondary containment structure will be located below grade

(except for the cover that will be located above grade) to

provide operator access and remote valve operation. A HEPA

filter will also be installed above grade. This filter will be

connected to 241-AZ-301 tank and will be used as the vent for

the 241-AZ-301 tank.

The lower level of the fabricated tank system will contain the

receiver tank for the condensate coming from the AZ-PC-SP-1

seal pot via line AZ-503. Other components housed in the

lower level will include the sump, sump suction line, tank

suction piping, tank return piping, tank vent lines, instrument

access risers, leak detection, and freeze protection, as required.

The upper level of the fabricated tank system will contain the

distribution pumps, valves, instrumentation, and controls.

Operator access will be provided as required (e.g., access

ladder, door in system cover, mid-level grating to support

operator). Distribution valves will be located to provide the

ability to use remote valve actuators. Freeze protection for the

piping, pumps, and valves will be used as required.

The AZ-PC-SP-1 seal pot is located in the 241-AZ-702

building and this seal pot serves as a collection point for

condensate originating from the 241-AZ-702 ventilation

system. The 241-AZ-702 ventilation system provides primary

tank ventilation for the 241-AY and 241-AZ DSTs. The

existing 241-AZ-151 catch tank would be isolated in a separate

effort to support other commitments.

Currently there are two drain paths into the 241-AZ-151 catch

tank that will remain active after June 30, 2005. Those two

drain paths are the condensate from the 241-AZ-702 facility

and the 241-AZ-801A floor drain. The 241-AZ-702

condensate drain line will be rerouted to the 241-AY tanks and

also to the 241-AZ tanks. In addition, the 241-AZ-801A floor

drain will be isolated. In addition to the installation of a drain

line to AZ-102, a new jumper will be installed in the 241-AZ-

02A pit. This work will be accomplished under ALARACT

4.1,6.1,14.1 and 15.1.

204-AR TRANSFER LINE MODIFICATION

The 204-AR Waste Unloading Facility will continue to be in

operation after June 30, 2005. Waste transfer line LIQW-702

will be modified to extend the transfer line encasement through

the pit wall. This pipe is buried approximately three and a half

feet below grade, so the excavated area will be approximately

10' x 10' x 6'. A portion of the slab under an old laundry

facility and a section of the asphalt surface adjacent to the

doorstep of the facility will require demolition for access.

The new encasement section will be open-ended, upstream of

DOE/RL-2017-02 Rev. 0

B-187

the exterior wall seal plate. The obsolete air purge connection

to the existing encasement pipe will be removed.



Ac-227 4.70E-03 Am-241 7.76E+02

Am-243 4.29E-02 Ba-137 m 1.41E+06

C-14 5.77E+00 Cd-113 m 1.76E+02

Cm-242 7.44E+00 Cm-243 1.93E-01

Cm-244 2.63E+00 Co-60 1.07E+02

Cs-134 3.32E+00 Cs-137 1.49E+06

Eu-152 8.21E+00 Eu-154 6.09E+02

Eu-155 7.03E+02 H-3 8.16E+02

I-129 1.12E+00 Nb-93 m 2.04E+01

Ni-59 1.82E+00 Ni-63 1.73E+02

Np-237 9.02E-01 Pa-231 1.19E-02

Pu-238 6.19E+00 Pu-239 1.07E+02

Pu-240 2.26E+01 Pu-241 3.89E+02

Pu-242 2.37E-03 Ra-226 4.36E-04

Ra-228 1.98E-01 Ru-106 1.49E-04

Sb-125 8.20E+01 Se-79 2.06E+01

Sm-151 3.25E+04 Sn-126 6.86E+00

Sr-90 1.68E+05 Tc-99 1.34E+03

Th-229 7.22E-03 Th-232 3.26E-02

U-232 4.66E-01 U-233 1.91E-00

U-234 2.57E-01 U-235 5.90E-02

U-236 1.05E-01 U-238 1.13E+00

Y-90 1.67E+05 Zr-93 2.16E+01


200W DVS - Active WDOH Emission Unit ID : 755



Permit: AIR 11-1006 - C Issue Date: 10-28-11 Effective Date: 10-19-11 Obsolete Date: 12-19-16




200W DVS - Passive WDOH Emission Unit ID : 756

Page in AOP : EU0756-001 EMISSION UNIT DID NOT OPERATE DURING CY 2016 SEE TABLE 2

Permit: AIR 11-1006 – D Issue Date: 10-28-11 Effective Date: 10-19-11




DOE/RL-2017-02 Rev. 0

B-188




Status


Method


Zone or Area :


Required Units : 1





Zone or Area :


Required Units : 1





Zone or Area :


Required Units : 1

Add'l Description:



Zone or Area :


Required Units : 2




Zone or Area :


Required Units : 1

Add'l Description:






241, Y-90, Cs-134, Pa-231, Pu-238, Pu-239, Pu-240, Pu-241



61.93(b)(4)(i) & WAC 246-247-0075(2)



Continuous











(WAC 246-247-030(21)).

Continuous







DOE/RL-2017-02 Rev. 0

B-189















Treatment Plant.





















Ac-227 1.29E+02 Am-241 9.67E+04

Am-243 1.34E+01 Ba-137 m 1.61E+07

C-14 4.38E+02 Cd-113 m 7.25E+03

Cm-242 6.99E+01 Cm-243 7.92E+00

Cm-244 2.25E+02 Co-60 4.13E+03

Cs-134 1.08E+04 Cs-137 1.70E+07

Eu-152 1.01E+03 Eu-154 4.26E+04

Eu-155 4.42E+04 H-3 2.47E+03

I-129 8.13E+00 Nb-93 m 1.77E+03

Ni-59 7.44E+02 Ni-63 7.02E+04

Np-237 5.18E+01 Pa-231 2.70E+02

Pu-238 2.59E+03 Pu-239 2.71E+04

Pu-240 4.86E+03 Pu-241 6.00E+04

Pu-242 3.77E-01 Ra-226 2.38E+02


DOE/RL-2017-02 Rev. 0

B-190

Ra-228 3.65E+01 Ru-106 1.02E+03

Sb-125 2.04E+04 Se-79 5.38E+01

Sm-151 1.48E+06 Sn-126 2.21E+02

Sr-90 2.08E+07 Tc-99 6.09E+03

Th-229 2.49E+01 Th-232 6.08E+00

U-232 2.73E+01 U-233 4.46E+02

U-234 6.14E+01 U-235 2.34E+00

U-236 2.73E+00 U-238 5.06E+01

Y-90 2.08E+07 Zr-93 1.80E+03










Continuous





testing in 2008.











Continuous















Continuous

CDM: Reviewed TWINS or



in AW farm is greater than 8.




Continuous









Continuous









Continuous





DOE/RL-2017-02 Rev. 0

B-191





occur.

Continuous








Status


Method


Zone or Area :


Required Units : 1





Zone or Area :


Required Units : 1





Zone or Area :


Required Units : 1

Add'l Description:



Zone or Area :


Required Units : 2




Zone or Area :


Required Units : 1

Add'l Description:






241, Y-90, Cs-134, Pa-231, Pu-238, Pu-239, Pu-240, Pu-241



61.93(b)(4)(i) & WAC 246-247-0075(2)



Continuous



DOE/RL-2017-02 Rev. 0

B-192

Permit: AIR 11-1004 - D Issue Date: 10-18-11 Effective Date: 10-10-11








(WAC 246-247-030(21)).

Continuous





















Treatment Plant.





















Ac-227 1.29E+02 Am-241 9.67E+04

Am-243 1.34E+01 Ba-137 m 1.61E+07

C-14 4.38E+02 Cd-113 m 7.25E+03

Cm-242 6.99E+01 Cm-243 7.92E+00


DOE/RL-2017-02 Rev. 0

B-193

Cm-244 2.25E+02 Co-60 4.13E+03

Cs-134 1.08E+04 Cs-137 1.70E+07

Eu-152 1.01E+03 Eu-154 4.26E+04

Eu-155 4.42E+04 H-3 2.47E+03

I-129 8.13E+00 Nb-93 m 1.77E+03

Ni-59 7.44E+02 Ni-63 7.02E+04

Np-237 5.18E+01 Pa-231 2.70E+02

Pu-238 2.59E+03 Pu-239 2.71E+04

Pu-240 4.86E+03 Pu-241 6.00E+04

Pu-242 3.77E-01 Ra-226 2.38E+02

Ra-228 3.65E+01 Ru-106 1.02E+03

Sb-125 2.04E+04 Se-79 5.38E+01

Sm-151 1.48E+06 Sn-126 2.21E+02

Sr-90 2.08E+07 Tc-99 6.09E+03

Th-229 2.49E+01 Th-232 6.08E+00

U-232 2.73E+01 U-233 4.46E+02

U-234 6.14E+01 U-235 2.34E+00

U-236 2.73E+00 U-238 5.06E+01

Y-90 2.08E+07 Zr-93 1.80E+03










Continuous





testing in 2008.











Continuous





The emission unit shall meet the quality assurance

requirements of 40 CFR 61 Subpart H, as effective on October

9, 2002.

Continuous

CDM: TFC-PLN-71, Quality

Assurance Program Plan for

Tank Farm Contractor

Radioactive Air Emissions.





DOE/RL-2017-02 Rev. 0

B-194







Continuous

CDM: Review TWINS or



in AW farm is greater than 8.




Continuous









Continuous











Continuous







occur.

Continuous





P-BULKVIT-001 WDOH Emission Unit ID: 878








DOE/RL-2017-02 Rev. 0

B-195





Tanker Loading of Contaminated Waste Water WDOH Emission Unit ID: 888



Status


Method



Required Sampling: As listed in the following Conditions and

Limitations.

Sampling Frequency: As listed in the following Conditions

and Limitations.

Radionuclide Requiring Measurement: Total alpha, total

beta

Not

Applicable











61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous


work documents.

Comment: This requirement

was met by complying with the

license/permit. Emissions from

unit were less than criteria

specified in 40 CFR

61.93(b)(4)(i).


NOC: Tanker Truck Loading of Radioactively Contaminated Waste Water





Continuous

CDM: Field interviews, 200

Areas Effluent Treatment

Facility (ETF) personnel, and

work documents.

Comment: ETF personnel

evaluate WRPS condensate

data to verify emission limit

won’t be exceeded.

DOE/RL-2017-02 Rev. 0

B-196




in (WAC 246-247-030(16)), may be conducted. The approved

activities are limited to transfer of radioactive waste water

(e.g., purgewater, pool cell water, decontamination solutions)

from various locations on the Hanford site by mobile tanker

trucks. The tanker trucks will be used to transport this

wastewater to the Liquid Effluent Retention Facility (LERF),

the 200 Areas Effluent Treatment Facility (ETF), and/or to a

Double-Shell Tank (DST) located in one of the 200 Area tank

farms. The proposed action includes isolated instances where

small quantities of wastewater might be transferred to 55

gallon drums or smaller containers, and transported to LERF,

the ETF, and/or to a DST. The license is a categorical license

under WAC 246-247-060(8). In the text of the license

conditions, it should be understood that the term "tanker" or

"tanker/drum" or variants of these terms includes smaller

containers, so that the license shall apply to loading of tankers,

drums, or smaller containers.

The physical and chemical processes associated with tanker

truck loading activities are:

Isotopic analysis of wastewater.

Tanker truck or truck deployment.

Hookup of transfer equipment for transfer of wastewater into

tanker, drums, or smaller container.

Wastewater transfer to the tanker truck, drums, or smaller

containers via pumping or vacuum transfer.

Associated surveys, spill prevention, other radcon activities.

Decontamination of tanker/drums/smaller containers.

Decontamination or packaging of transfer equipment for

transport.

Decontamination or packaging of spillage and resulting

contamination.

Unloading of the tanker trucks, drums, or smaller containers is

not licensed under this approval.

Continuous

CDM: Field interviews, ETF

personnel, and work

documents.


030(21)(a-e)[as specified in the application] is 6.00E-02


(Curies/year) of:

Alpha-0 | 3.60E-07 | Liquid/Particulate Solid | WAC 246-247-

030(21)(a)

Any radionuclide on the chart of the nuclides could be

encountered during tanker loading operations. The

radionuclides specifically listed in the NOC application were

chosen to conservatively represent all radionuclide emissions

that may occur in particulate form. A small contribution from

the gaseous radionuclides may be encountered. Although any

radionuclide could be present, for conservatism all

beta/gamma is assumed to be Cs-137 and all alpha is assumed

to be Am-241 for dose calculation estimates. Other

radionuclides may be encountered and are approved so long as

Continuous


personnel, and work

documents.

DOE/RL-2017-02 Rev. 0

B-197

they are conservatively represented by the total alpha and total

beta-gamma constituents.

Beta-0 | 1.10E-02 | Liquid/Particulate Solid | WAC 246-247-

030(21)(a)

Any radionuclide on the chart of the nuclides could be

encountered during tanker loading operations. The

radionuclides specifically listed in the NOC application were

chosen to conservatively represent all radionuclide emissions

that may occur in particulate form. A small contribution from

the gaseous radionuclides may be encountered. Although any

radionuclide could be present, for conservatism all

beta/gamma is assumed to be Cs-137 and all alpha is assumed

to be Am-241 for dose calculation estimates. Other

radionuclides may be encountered and are approved so long as

they are conservatively represented by the total alpha and total

beta-gamma constituents.














WAC 173-401-725( 4). Notice will be provided according to

the particular regulation under which notification is required. If

the applicable regulation(s) does not address manner and type




At all times, activities shall conform to procedures for prior

characterization and handling of radioactive liquid approved in

accord with applicable QA program. Prior to commencing

liquid transfer into tanker/drum/smaller container:

a) Waste liquid shall be characterized, and acceptability at the

LERF, ETF and DST shall be verified.

b) All transfer line hookups shall be inspected to verify leak-

tight connections.

c) Spill prevention measures shall be verified to be in place.

d) Volume of tanker/drum/smaller container contents shall be

verified and documented.

e) Seals separating tanker/drum/smaller container contents

from environment shall be verified fully functional.

During the loading operation:

f) Surveys shall be performed according to radiation control

procedures approved via applicable QA program.

Continuous


personnel, and work

documents.

DOE/RL-2017-02 Rev. 0

B-198

g) Fill rates shall be controlled below 50 cfm.

On completion of the loading operation:

h) All tanker/drum fittings shall be disconnected and closed.

i) All liquid/gas release points on the tanker/drum shall be

closed and shall remain closed until commencement of

unloading operations at the LERF, ETF and/or DST.

j) Spill prevention measures shall remain in place until the

tanker/drum is closed.

k) The tanker/drum shall be surveyed and if necessary

decontaminated before release for transport.

l) Transfer equipment shall be surveyed and if necessary

decontaminated or packaged for transport subject to radcon

procedures approved in accord with applicable QA program.

m) Spillage shall be surveyed and if necessary decontaminated

or packaged or transport and disposal subject to radcon

procedures approved in accord with applicable QA program.

n) Volume of tanker/drum contents shall be verified and

documented.

The surface contamination release criteria for the vehicle,

tanker, drums, and transport equipment shall be documented

and approved in accord with an applicable QA program.

(WAC 246-247-040(5))

Log, Monitoring, and Demonstration of Compliance to

Licensed Emission Limit:

a) A single log shall be maintained, reflect each individual

loading operation, and be updated after each individual

tanker/drum/container is offloaded, so long as the emissions

associated with the transferred but un-logged quantity

(material residing in partially filled tankers) remain less than

10% of licensed limit, as estimated using the method described

in this condition.

b) The log shall record the sum to date of the calendar year's

emissions estimated using the method described in this

condition for activities herein licensed.

c) The log shall include monthly confirmation that licensed

annual emission limits have not been exceeded, that transfer

low rates remain below the limit specified in this license, and

identify the radiological work package under which each

loading is accomplished.

d) The estimated emissions for each loading operation shall be

determined using one of the following methods:

Method 1: From the characterization of the liquid being

loaded, gross alpha and gross beta/gamma activities shall be

determined. The emission shall be determined using the

volume of liquid transferred, and assumed release fraction of

0.001, location-specific dose conversion factors from the latest

revision of HNF-3602, assuming gross alpha is 241-AM and

Continuous


personnel, and work

documents.

DOE/RL-2017-02 Rev. 0

B-199

gross beta/gamma is 137-Cs.

Method 2: Form the characterization of the liquid being

loaded, a complete isotopic distribution of radionuclides shall

be determined. The emission shall be determined using the

volume of liquid transferred and assumed release fraction of

0.001, and location-specific dose conversion factor from the

latest revision of HNF-3602 for known isotopes.

(WAC 246-247-040(5) WAC 246-247-080(7), WAC 246-247-

075(3)).

P-241UX302A-001 WDOH Emission Unit ID: 894



Status


Method


Zone or Area :


Required Units : 1














Reports.


61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,







NOC: Operation of Breather Filter on 241-UX-302A






Continuous





DOE/RL-2017-02 Rev. 0

B-200


(WAC 246-247-030(21)).







The 241-UX-302A catch tank is a 17,600 gallon capacity catch

tank located near U Plant. The tank has a breather filter

installed whose purpose is to minimize any radioactive

particulates that may be emitted.

Currently, there is currently less than 1,000 gallons of waste

stored in the tank. Current operational activities in this tank

include level monitoring for leaks and intrusion by a variety of








Alpha-0 | 1.99E-11

Based on 241AM

Beta-0 | 1.32E-08

Based on 90Sr

Gamma-0 | 1.27E-08

Based on 137Cs



The breather filter must be replaced annually. The new filter

must be a Type 1 (radial flow filter) with a Type C filter pack,

as define by AG-1 Code on Nuclear Air and Gas Treatment

Section FK, Special HEPA Filters. The filter must have a

minimum removal efficiency of 99.97% and a rated flow of 40

cfm. (WAC 246-247-040(5) and WAC 246-247-075(4)).



218-E-12B WDOH Emission Unit ID: 909



Status


Method



Required Sampling: Per sitewide ambient monitoring



Continuous CDM: ABCASH review.

DOE/RL-2017-02 Rev. 0

B-201


61.93(c)(4)(i) & WAC 246-247-075(3)

Permit Monitoring and Testing Procedure: Hanford Site

Near-Facility Environmental Ambient Monitoring program

Continuous

CDM: MSA near-facility



NOC: Management of Radiological Contamination at Trench 94






data.

This approval l applies only to those activities described below.




The Management of Radiological contamination, including

cleanup activities, at Trench 94

Trench 94 is located within the 200 East Area Burial Ground,

218-E-12B. Trench 94 contains submarine and other reactor

compartments, as it provide s long term disposal of the U .S.

Navy defueled reactor compartments.

The design of the trench allows for a wide variety of naturally

transferred contamination to be potentially found within the

trench due to lack of physical barriers. Forms of naturally

transferred contamination include but are not limited to:

vegetation (rooted or windblown), animal feces, bird nests,

scent marks, burrows, and animals. Due to the potential for

conditions involving radioactive vegetation, contaminated soil,

mud, nests and feces, continued management of this area is

necessary.

Misting, spraying, or fogging will be used to minimize the

spread of contamination and potential for airborne particles.

Contaminated debris will be collected and packaged in

containers for disposal at the Environmental Restoration

Disposal Facility or another approved disposal facility.

Radiological contamination and dose rate monitoring is

conducted prior to transporting waste containers or packages.

All waste containers or packages will be prepared for transport

per established procedures. Specific controls will be in place

during cleanup. The following controls are consistent with the

2012 Personal Communication ("Re: Request for Approval:

Trench 94/SRC ALARACT Demonstration") and were

developed in accordance with the latest revision of the CH2M

HILL Plateau Remediation Company (CHPRC) Radiological

Control Manual, CHPRC Radiological Control procedures, as

provided with the application. ALARA principles shall be

utilized.

Specific controls will be in place during cleanup. The

following controls are consistent with the 2012 Personal

Continuous

CDM: Interview with field

personnel.

Comment: Reactor

compartment preventative

maintenance (painting)

occurred from May through

early June 2016.

DOE/RL-2017-02 Rev. 0

B-202

Communication ("Re: Request for Approval: Trench 94/SRC

ALARACT Demonstration") and were developed in

accordance with the latest revision of the CH2M HILL Plateau

Remediation Company (CHPRC) Radiological Control

Manual, CHPRC Radiological Control procedures, as provided

with the application. ALARA


030(2l)(a-e) [as specified in the application] is 2.21E- 05


(Curies/year) of:

Alpha -0 1.77E-08 Liquid/Particulate Solid

WAC 246-247-030(21)(e)

Alpha release rate is assumed to be Pu-239. Other

radionuclides may be encountered and are conservatively

represented by the total alpha and total beta-gamma

constituents.

Am -241 Liquid/Particulate Solid

WAC 246-247-030(21)(a)


less than

10% of the unabated PTE and represents less than 25% of the

abated dose.

B/G -0 1.17E-04 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Beta/Gamma release rate is assumed to be Sr-90. Other

radionuclides may be encountered and are conservatively

represented by the total alpha and total beta-gamma

constituents.

C -14 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




Ce -144 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




Cm -244 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




Co -60 Liquid/Particulate Solid

WAC 246-247-030(21)(a)





data.

DOE/RL-2017-02 Rev. 0

B-203

Cs -134 Liquid/Particulate Solid

WAC 246-247-030(21)(a)


less than10% of the unabated PTE and represents less than


Ce -137 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

Alpha release rate is assumed to be Pu239/249. Other

radionuclides may be encountered and are approves so long as

they are conservatively represented by the total alpha

constituents.

Eu -154 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




Eu -155 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




H -3 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




I -129 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




K -40 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




Mn -54 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




Na -22 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




Nb -94 Liquid/Particulate Solid

WAC 246-247-030(21)(a)

DOE/RL-2017-02 Rev. 0

B-204




Np -237 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




Pu -238 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




Pu -240 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




Pu -241 Liquid/Particulate Solid WAC 246-247-

030(21)(a)




Ra -226 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




Ru -106 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




Sb -125 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




Se -79 Liquid/Particulate Solid

WAC 246-247-030(21)(a)


less than10% of the unabated PTE and represents less than


Tc -99 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




DOE/RL-2017-02 Rev. 0

B-205

U -233 Liquid/Particulate Solid

WAC 246-247-030(21)(a)





WAC 246-247-030(21)(a)





WAC 246-247-030(21)(a)





WAC 246-247-030(21)(a)





WAC 246-247-030(21)(a)




Zn -65 Liquid/Particulate Solid

WAC 246-247-030(21)(a)




Zr -95 Liquid/Particulate Solid

WAC 246-247-030(21)(a)






Am – 241 C – 14 Ce – 144 Cm – 244 Co - 60

Cs – 134 Cs – 137 Eu – 154 Eu -155 H - 3

I – 129 K – 40 Mn – 54 Na-22 Nb - 94

Np-237 Pu -238 Pu -240 Pu -241 Ra -226

Ru -106 Sb – 125 Se - 79 Sr – 90 Tc-99

U – 233 U – 234 U – 235 U – 236 U- 238

Zn – 65 Zr-93





DOE/RL-2017-02 Rev. 0

B-206





TEDE to the MEI after controls. (WAC 246-247-110(9)) DOE










WDOH NOTIFICATIONS-Contamination Levels

WDOH will be notified when the following contamination

levels are found:

-Direct contamination readings are detected greater than

500,000 disintegrations per minute (dpm)/100 cm^2 alpha

and/or 1 rad/hr/100cm^2 beta-gamma are encountered.

-Removable/transferrable contamination levels above 2,000

dpm/100cm^2 alpha or above 100,000 dpm/ 100cm^2 beta-

gamma are encountered. For activities that also include

cleanup activities

(WAC 246-247-040(5)),(WAC 246-247-040(6))

Continuous CDM: Interview with field

personnel.

WDOH NOTIFICATION-Abatement of

Removable/Transferrable & Direct Contamination Levels-

Cleanup Exceeding the following contamination limits requires

WDOH notification and implementation of additional controls

before work may resume.

-Removable/transferrable contamination will be maintained

less than a maximum level of 2,200,000 dpm/ 100cm^2 alpha

and/or less than 4 rad/hr/100cm^2 beta-gamma.

-Direct contamination levels of 20,000dpm/100cm^2 alpha,

and or 1,000,000dpm/ 100cm^2 beta-gamma The following

additional controls, as described below, shall be implemented

before work resumes.

-Soil shall be wetted prior to removal if not already damp

-General work place air monitoring shall be performed during

removal activities

-Removed soil and vegetation containing

>500,000dpm/100cm^2 beta-gamma or > 10,000dpm/100cm^2

alpha will be containerized, or fixative applied, if it is to be left

for greater than 48 hours.

(WAC 246-247-040(5))


personnel.

WDOH NOTIFICATION -Submarine and Other Reactor

Compartments WDOH will be notified (under the

environmental notification protocol) if the following levels are

found in the area from the submarine and other reactor

compartments to an area 1,000 ft from the submarine and other

reactor compartments:


personnel.

DOE/RL-2017-02 Rev. 0

B-207

-Removable/transferrable contamination levels >2,000

disintegrations per minute per 100cm^2 alpha or > 100,000

disintegrations per minute per 100 cm^2 beta-gamma

-Direct contamination readings of >500,000 disintegrations per

minute per 100 cm^2 alpha and/or 1 rad per hour per 100 cm^2

beta-gamma

If detection is made within overlap with LERF Basin Area,

only one notification is required. If the detection is made in an

area not managed by Trench 94 or LERF, but within the 1,000

ft area, the party responsible for management of the area where

the detection occurred shall make the notification.

(WAC 246-247-040(5)),WAC 246-247-040(6)

ABATMENT DURING CLEANUP ACTIVITIES-Dispersable

Contaminated Material Monitoring

-Contamination monitoring, workplace air monitoring, and

dose rate monitoring will be conducted during cleanup

activities. Routine contamination surveys of contaminated

areas will occur.

-During work activities, continuous radiological control

technician coverage will be provided.

-Alpha and beta-gamma contamination surveys shall be

performed prior to and during activities that have the potential

to disturb radioactive contamination, such as removal of

nesting material or soil disturbance.

-Annual alpha and beta-gamma contamination surveys shall be

performed to confirm the dose rates within the boundaries of

each posted radiation area. Records of the annual surveys shall

be available for audits.

-In any Contamination Area (CA), High Contamination Area

(HCA) or Airborne Radioactivity Area (ARA), cleanup

activities involving dispersible contaminated material shall

stop if average wind speeds exceed 10 miles per hour (mph)

for elevated work or 20 mph for ground level work, as

measured at the work site.

-Suppressants such as water, fixatives, and covers shall be

used, as necessary, to control contamination spread. Handheld

and/or overhead atomized misting will be performed during

work activities where a potential exists to generate airborne

radioactivity.

-Atomized misters and fixative sprayers shall be function-

checked at the work site prior to commencing work activities.

(WAC 246-247-040(5))


personnel.

ABATEMENT TECHNOLOGY-Related Approvals

If a truck-mounted vacuum (i.e.,GuzzlerTM)

Portable/Temporary Radioactive Air Emission Units

(PTRAEU), or high-efficiency particulate air (HEPA) filtered

vacuum radioactive air emission unit is used, controls

described in the Hanford Site Radioactive Air Emissions

License #FF-01, for the Sitewide GuzzlerTM Notice of

Construction (NOC) (Emission Unit ID: 476), the PTRAEU

Continuous


personnel.


conducted that required the use

of the related licenses.

DOE/RL-2017-02 Rev. 0

B-208

NOC (Emission Unit ID: 447), and the Hanford Sitewide W-

PORTEX 007 [HEPA vacuums] NOC (Emission Unit ID:

455), respectively, would be followed. (WAC 246-247-

040(5))

EFFLUENT CONTINOUS MONITORING-Ambient Air

Monitoring Network

The 200 Area near-facility ambient air monitoring network

shall be used for continuous monitoring. The stations (N967,

N973, N498, N972) will also provide indication of potential

elevated airborne radioactivity using the frequency and

protocol of the Hanford Site Near-Facility Environmental

Monitoring Program.

(WAC 246-247-040(5))


personnel

EFFLUENT CONTINUOUS MONITORING- Chain of

Custody

Air sample data shall be analyzed by MSA and ABCASH data

shall available to WDOH. The chain of custody shall follow

standard protocol for the 200 Area near-facility ambient air

monitoring network. (WAC 246-247-040(5))


EFFLUENT MONITORING-Periodic Confirmatory

Measurements-Air Monitors

Periodic confirmatory measurements (PCMs) will be made to

verify the low emissions. The existing 200 Area network

system for near-field monitoring (DOE/RL-91-50,

Environmental Monitoring Plan United States Department of

Energy Richland Operations Office, as amended) will continue

to be used for the PCM mechanism to verify low emissions

during Trench 94 radiologically-contaminated material cleanup

activities. The 200 Area general fugitive/diffuse emission unit

is already approved in WDOH, 2012b for related continuous

monitoring). Specific ambient air monitors N-967, N-973, N-

498, and N-972 (as identified in WDOH, 2012a, are in close

proximity to Trench 94 and will provide indication of potential

elevated airborne radioactivity. (WAC 246-247- 040(5))


MONITORING REQUIREMENTS-Sampling Frequency-Soil

Deposition

Annual soil deposition sampling shall be performed in three

prominent downwind locations, as determined by the previous

year's wind rose data. (WAC 246-247-040(5))

Continuous

CDM: Verified sampling

occurred by interview with

field sampling personnel.

Comment: MSA sampling

subcontract

MONITORING-Diffuse and Fugitive-Soil Monitoring

Activities

Additional monitoring for diffuse and fugitive emissions will

consist of radiological surveys when soil excavation activities

are being performed. The survey methods for monitoring are

not a direct measurement of effluent emissions. The methods

are intended to demonstrate compliance by showing that by

being under the contamination levels for which work is

controlled, the actual emissions would be inherently below the

Continuous


personnel.


performed requiring soil

monitoring.

DOE/RL-2017-02 Rev. 0

B-209

estimated emissions, which are based on (calculated from) the

same contamination levels. (WAC 246-247-040(5))

CONTAMINATION CONTROL - Diffuse and Fugitive

Activities

The Diffuse/Fugitive Activities Unit at Trench 94 are limited

to the following:

-Soil excavation activities

-Fauna and flora transport activities

-Cleanup of bird nesting/droppings

-Work in preparation for reactor compartment placement

-Work during reactor compartment placement

During these activities radiological surveys shall be performed.

(WAC 246-247-040(5))


personnel.

CONTAMINATION CONTROL - Diffuse and Fugitive

Activities

The Diffuse/Fugitive Activities Unit at Trench 94 are limited

to the following:

-Soil excavation activities

-Fauna and flora transport activities

-Cleanup of bird nesting/droppings

-Work in preparation for reactor compartment placement

-Work during reactor compartment placement

During these activities radiological surveys shall be performed.

(WAC 246-247-040(5))


personnel.

CONTAMINATION CONTROL DOCUMENTATION-

Submarine and Other Reactor Compartments

A record of rad con reports that were performed during the

month (routine, pre-job and during-job surveys). Each instance

of anomalous data will be evaluated by a supervisor and

entered into a corrective action database for tracking and

trending purposes (as required) and shall be available for the

audit. (WAC 246-247-040(5))


personnel.

CONTAMINATION CONTROL -Soil Removal

After removal of radiologically contaminated soil, the soil

surface radiological contamination levels would be verified. If

contamination is present above identified levels, additional soil

may be removed and containerized for disposal or covered or

fixed to provide control of the contamination.

(WAC 246-247040(5))

Continuous


personnel.


performed requiring soil

monitoring.

DOE/RL-2017-02 Rev. 0

B-210

P-241ER311-001 WDOH Emission Unit ID: 910



Status


Method


Zone or Area :


Required Units : 1














Reports.


61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,










Status


Method


Zone or Area :


Required Units : 1










Reports.

DOE/RL-2017-02 Rev. 0

B-211






61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,







NOC: Operation of 244-A Annulus HEPA Breather Filter







(WAC 246-247-030(21)).

Continuous






NOC limit.





The 244-A DCRT is located west of the 241-AN tank farm in

the 200 east area. The DCRT catch tank is a steel vessel with


concrete pit containing the tank define the annulus space.





escape.















Ac-227


DOE/RL-2017-02 Rev. 0

B-212

Alpha-0 1.17E+01



the MEI

Am-241 Am-243 Ba-137 m

Beta-0 5.31E+03



the MEI

C-14 Cd-113 m Cm-242 Cm-243 Cm-244

Co-60 Cs-134 Cs-137 Eu-152 Eu-154

Eu-155

Gamma-0 2.84E+03



the MEI

H-3 I-129 Nb-93 m Ni-59 Ni-63

Np-237 Pa-231 Pu-238 Pu-239 Pu-240

Pu-241 Pu-242 Ra-226 Ra-228 Ru-106

Sb-125 Se-79 Sm-151 Sn-126 Sr-90

Tc-99 Th-229 Th-232 U-232 U-233

U-234 U-235 U-236 U-238 Y-90 m

Zr-93



246-247-040(5) and WAC 246-247-075(4)).



P-244BX-003 WDOH Emission Unit ID: 922



Status


Method


Zone or Area :


Required Units : 1












Reports.

DOE/RL-2017-02 Rev. 0

B-213




61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,







NOC: Operation of 244-BX Annulus HEPA Breather Filter







(WAC 246-247-030(21)).

Continuous











The 244-BX DCRT is located east of the 241-BX Tank Farm

in the 200 east area. The DCRT catch tank is a steel vessel

with a volume capacity of 31,000 gallons. The catch tank and

the concrete pit containing the tank define the annulus space.





escape.













DOE/RL-2017-02 Rev. 0

B-214



Ac-227

Alpha-0 2.37E+01



the MEI

Am-241 Am-243 Ba-137 m

Beta-0 1.07E+04



the MEI

C-14 Cd-113 m Cm-242 Cm-243 Cm-244

Co-60 Cs-134 Cs-137 Eu-152 Eu-154

Eu-155

Gamma-0 5.74E+03



the MEI

H-3 I-129 Nb-93 m Ni-59 Ni-63

Np-237 Pa-231 Pu-238 Pu-239 Pu-240

Pu-241 Pu-242 Ra-226 Ra-228 Ru-106

Sb-125 Se-79 Sm-151 Sn-126 Sr-90

Tc-99 Th-229 Th-232 U-232 U-233

U-234 U-235 U-236 U-238 Y-90 m

Zr-93




246-247-040(5) and WAC 246-247-075(4)).

Continuous


Reports. Field interviews and





Status


Method


Zone or Area :


Required Units : 1








Reports.

DOE/RL-2017-02 Rev. 0

B-215








61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,







NOC: Operation of 244-S Annulus HEPA Breather Filter







(WAC 246-247-030(21)).

Continuous











The 244-S DCRT is located south of the 241-SY Tank Farms

in the 200 west area. The DCRT catch tank is a steel vessel

with a volume capacity of 19,000 gallons. The catch tank and

the concrete pit containing the tank define the annulus space.

The tank and annulus have been fitted with ventilation breather


















radionuclides (Curies/year): Continuous CDM: TWINS

DOE/RL-2017-02 Rev. 0

B-216

Ac-227

Alpha-0 1.17E+01



the MEI

Am-241 Am-243 Ba-137 m

Beta-0 5.31E+03



the MEI

C-14 Cd-113 m Cm-242 Cm-243 Cm-244

Co-60 Cs-134 Cs-137 Eu-152 Eu-154

Eu-155

Gamma-0 2.84E+03



the MEI

H-3 I-129 Nb-93 m Ni-59 Ni-63

Np-237 Pa-231 Pu-238 Pu-239 Pu-240

Pu-241 Pu-242 Ra-226 Ra-228 Ru-106

Sb-125 Se-79 Sm-151 Sn-126 Sr-90

Tc-99 Th-229 Th-232 U-232 U-233

U-234 U-235 U-236 U-238 Y-90 m

Zr-93



246-247-040(5) and WAC 246-247-075(4)).



P-244TX-003 WDOH Emission Unit ID: 969



Status


Method


Zone or Area :


Required Units : 1












Reports.

DOE/RL-2017-02 Rev. 0

B-217




61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,







NOC: Operation of 244-TX Annulus HEPA Breather Filter







(WAC 246-247-030(21)).

Continuous




















HEPA filter from the tank to facilitate testing of the filter. The

244-TX DCRT is located north of the 241-TX Tank Farm in

the 200 west area. The DCRT catch tank is a steel vessel with

a volume capacity of 31,000 gallons. The catch tank and the











Ac-227

Alpha-0 2.37E+01


DOE/RL-2017-02 Rev. 0

B-218



the MEI

Am-241 Am-243 Ba-137 m

Beta-0 1.07E+04



the MEI

C-14 Cd-113 m Cm-242 Cm-243 Cm-244

Co-60 Cs-134 Cs-137 Eu-152 Eu-154

Eu-155

Gamma-0 5.74E+03



the MEI

H-3 I-129 Nb-93 m Ni-59 Ni-63

Np-237 Pa-231 Pu-238 Pu-239 Pu-240

Pu-241 Pu-242 Ra-226 Ra-228 Ru-106

Sb-125 Se-79 Sm-151 Sn-126 Sr-90

Tc-99 Th-229 Th-232 U-232 U-233

U-234 U-235 U-236 U-238 Y-90 m

Zr-93



246-247-040(5) and WAC 246-247-075(4)).






Status


Method







program



to-emit TEDE.

Continuous





stations.




2016 Hanford Site

DOE/RL-2017-02 Rev. 0

B-219


Status


Method


Report.


247-075(3)





Permit: AIR 12-314 – E Issue Date: 03-06-12 Effective Date: 02-23-12

NOC: Sodium Residual Reaction/Removal and other Deactivation Work

Activities at the Fast Flux Test Reactor





Continuous



(or other source








The activity will involve reaction of sodium residuals

associated with the Fast Flux Test Facility Project systems and

equipment. This activity could be conducted in place or at

designated cleaning locations. Typically, the sodium residuals

would be reacted with superheated steam. The primary

advantages of the superheated steam process (SSP) are that it

does not allow condensation to occur and component cleaning

can be performed in a shorter time period. Prior to steam

injection into the system to be cleaned the steam is heated to

~204 C (400 F). The equipment to be cleaned is heated to a

minimum of 100 C (212 F) and higher if possible. Most

systems will require multiple injection points. As the

superheated steam reacts with the metallic sodium, the

temperature increases. The temperature is controlled such that

the maximum reaction temperature is no greater than ~538 C

(1,000 F).

Because of the high initial temperature and the increase of the

temperature caused by the reaction, no condensation occurs.

The caustic formed is a liquid at the processing temperatures

and because it is denser than the liquid sodium, it settles to the

bottom of any pools leaving the sodium on top where it is

always exposed to the superheated steam. Due to the

continued exposure of the molten sodium to the superheated

steam, the reaction continues at a constant rate. Superheated

steam injection is continued until hydrogen is no longer being

generated. The system is then cooled and rinsed and the fluid

Continuous

CDM: FFTF-36419, Fast Flux

Test Facility (FFTF) Closure

Project Documented Safety

Analysis, inquiry of facility

personnel, and review of

facility records associated with

PRC-PRO-WKM-12115

"Work Management."

Comment: Only S&M

activities were performed

during CY 2016.

DOE/RL-2017-02 Rev. 0

B-220


Status


Method

is drained from the system.

PERFORM IN PLACE CLEANING OF VESSELS,

COMPONENTS, AND LARGE BORE PIPE

A PTRAEU would be used to clean, in place, large bore

sodium pipe [greater than or equal to ~20 centimeter (8 inch)

diameter], components and vessels in the primary and

secondary sodium cooling systems. The PTRAEU also would

be used to clean the Interim Decay Storage (IDS) and Fuel

Storage Facility (FSF) vessels [Note: Select components in the

primary sodium system, and large diameter piping and

components in the secondary sodium system may be removed

and cleaned in FSF or the Maintenance and Storage Facility

(MASF), as described below].

Typically, penetrations into the piping/vessels would be made

at appropriate locations using a low speed drill. Existing

sodium heating systems would be energized, and

piping/vessels heated to liquefy the existing sodium residuals.

A PTRAEU would be connected to the penetration points, and

used at various locations to inject the superheated steam into

plant systems.

The superheated steam would be injected. Hydrogen

generation would be monitored to follow the reaction. Sulfuric

acid would be added to the resultant process liquid (i.e.,

sodium hydroxide solution) to reduce the pH to <13. This

solution would be routed for offloading to tanker transport for

overland transfer to Liquid Effluent Treatment Facility

(LERF) and subsequent treatment at 200 Area Effluent

Treatment Facility (ETF). If needed or chosen for use during

these activities, the categorical NOC for sitewide use of tanker

loading for wastewater could be used.

REMOVE SMALL BORE PIPE AND COMPONENTS FOR

REACTION IN A CLEANING STATION

Small bore piping [<20 centimeter (8 inch) diameter], valves

and other components [e.g., core component pots from IDS,

fuel storage tubes from FSF, and dump heat exchangers

(DHX) tube bundles] may be removed and processed in a

proposed stationary cleaning station that would be located in

FSF. Mechanical means (e.g., portable saws, pipe cutters)

would be used to cut the pipe, valves, and components into

manageable size. All heat exchanger tube bundles, which

contain multiple parallel flow paths, would be dismantled to

ensure effective cleaning.

The proposed FSF stationary cleaning station would consist of

a chamber with removable rack for loading piping and

components. The piping would be loaded at an angle, allowing

the residual sodium to drain to a catch basin when heated

before the injection of inert gas and/or reaction medium. The

process in the cleaning station would be consistent with the in

DOE/RL-2017-02 Rev. 0

B-221


Status


Method

place process where the resultant waste sodium hydroxide

solution is collected, the pH reduced to <13, and transported

to the 200 Areas. The FSF is considered an appropriate

location due to availability of sufficient floor space, existing

overhead crane, available utilities, and proximity to proposed

operations. If needed or chosen for use during these activities,

the categorical NOC for sitewide use of tanker loading for

wastewater could be used.

Cleaned piping and components would be disposed of in a

Hanford Site solid waste management facility.

REMOVE LARGE COMPONENTS FOR CLEANING

The large diameter cleaning vessel (LDCV) located in the

existing MASF could be used for cleaning large components

following removal (e.g., primary sodium pumps, intermediate

heat exchanger (IHX) tube bundles, and instrument trees). The

LDCV could be retrofitted with a new super heated steam

supply and associated control system for use in cleaning the

aforementioned components. The IHX tube bundles, which

contain multiple parallel sodium flow paths, may be

dismantled to ensure effective cleaning. Small bore pipe and

components also could be cleaned in MASF, if necessary.

OTHER DEACTIVATION ACTIVITIES

Other related routine, continued deactivation activities that

could occur as part of the proposed action are:

remove/dispose of asbestos; remove/stabilize existing hazards

in conjunction with systems and equipment deactivation

associated with sodium residuals; remove/recycle/dispose

excess deactivated equipment and components; and remove

depleted uranium and/or lead shielding.




(Curies/year) of:

Alpha-0 9.00E-15 Liquid/Particulate Solid

WAC 246-247-030(21)(e)

Alpha release rate based on Pu-239.

B/G-0 1.50E-01 Liquid/Particulate Solid

WAC 246-247-030(21)(e)

Beta/Gamma release rate based on Cs-137.



Ba-137m Co-60 Cs-134 Cs-137 H-3

Mn-54 Na-22 Pu-239 Ru-106 Zn-65



Continuous

CDM: Verified the basis for

the PTE calculation in the

NOC application.

DOE/RL-2017-02 Rev. 0

B-222


Status


Method


















Operations shall be performed in accordance with the controls

specified in radiation work planning documents and/or

operating procedures and shall be available for inspection

upon request.

Continuous

CDM: FFTF-36419, FFTF

Closure Project Documented

Safety Analysis, inquiry of

facility personnel, and review

of facility records associated

with PRC-PRO-WKM-12115

"Work Management."

All activities shall be conducted under the auspices of

radiological or health physics control technicians or personnel.

Routine field surveys, including swipes/smears, shall be

conducted. Fixatives, covers, or other standard measures shall

be used, as necessary to contain contamination.

Continuous







"Work Management."

Appropriate spill prevention procedures shall be in place to

minimize the release of radioactive liquid waste to the

environment, and to provide immediate cleanup of any liquid

spills.

Continuous







"Work Management."

The total amount of sodium reacted from all emission units

shall not exceed 4,000 gallons per year with no more than

2,000 gallons challenging a single emission unit.

Continuous







"Work Management."

Other radioisotopes may be present due to activation products,

fission products, decay products, and tracer gases. These other

isotopes are approved for this emission unit and will not

contribute significantly to the calculated potential-to-emit.

Not

Applicable





DOE/RL-2017-02 Rev. 0

B-223


Status


Method






P-241U301B-001 WDOH Emission Unit ID: 1129



Status


Method


Zone or Area :


Required Units : 1














Reports.


61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,







NOC: Operation of Breather Filter on 241-U-301B







(WAC 246-247-030(21)).

Continuous







DOE/RL-2017-02 Rev. 0

B-224





The 241-U-301B catch tank is a 36,000 gallon capacity catch

tank located in U Farm. The tank has a breather filter installed

whose purpose is to minimize any radioactive particulates that

may be emitted.











Am-241 1.11E-09 Pu-239/240 1.39E-09

Sr-90 3.33E-09 U-234 3.28E-10

U-235 1.28E-10 Zn-65 7.77E-08








cfm. (WAC 246-247-040(5) and WAC 246-247-075(4)).



P-241AZ154-001 WDOH Emission Unit ID: 1130



Status


Method


Zone or Area :


Required Units : 1














Reports.

DOE/RL-2017-02 Rev. 0

B-225


61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,







NOC: Operation of Breather Filter on 241-AZ-154







(WAC 246-247-030(21)).

Continuous

CDM: Reviewed radionuclide

air emissions data (or other

source data/ information)to






in (WAC 246-247-030(16), may be conducted.

The 241-AZ-154 catch tank is an 867 gallon capacity catch

tank located in AZ Farm. The tank has a breather filter



There is currently less than 100 gallons of waste stored in the

tank. Current operational activities in this tank include level

monitoring for leaks and intrusion by a variety of methods

including dip tubes, manual tapes, zip cords, and ENRAFs;

sampling tank contents, pumping tank contents, adding flush

water used pursuant to ALARACT practices.





Alpha-0 | 1.99E-11

Based on 241Am

Beta-0 | 1.32E-08

Based on 90Sr

Gamma-0 | 1.27E-08

Based on 137Cs








cfm. (WAC 246-247-040(5) and WAC 246-247-075(4)).



DOE/RL-2017-02 Rev. 0

B-226

FFTF PTRAEUs WDOH Emission Unit ID: 1176



Permit: AIR 12-314 - F Issue Date: 03-06-12 Effective Date: 02-23-12 NOC: Sodium Residual Reaction/Removal and other Deactivation Work Activities at the Fast Flux Test

Reactor WDOH NOC ID: 833 Date In AOP: 04-01-13 Page in AOP: EU1176-001


Drum Venting System 2 WDOH Emission Unit ID: 1181



Permit: AIR 11-1006 - E Issue Date: 10-28-11 Effective Date: 10-19-11 NOC: Operation of the Transuranic Waste Retrieval Project



S-MO444-001 WDOH Emission Unit ID: 1183


Permit: AIR 12-301 - C Issue Date: 03-06-12 Effective Date: 02-23-12 NOC: Waste Receiving and Processing Facility



J-361 Building WDOH Emission Unit ID: 1185


Requirement Compliance Status Compliance

Determination Method




determined using 40 CFR 61 Appendix D calculations in lieu

of monitoring.

Sampling Frequency: None

Radionuclide Requiring Measurement: Radioxenon and

radon

Continuous

CDM: Radioactive

gases released are

tracked by the

Radioactive Gas

Inventory/Database.

Radionuclide emissions

DOE/RL-2017-02 Rev. 0

B-227

were evaluated during

the annual NESHAPS

inventory assessment.


247-075[3]

Permit Monitoring and Testing Procedure: None

Continuous

CDM: Radionuclide

emissions during 2016

for the J-361 air permit

were estimated by

calculations performed

in accordance with 40

CFR 61, Appendix D,

and documented in the

2016 NESHAPs

assessment results. This

report was reviewed and

it was verified that the

calculated emissions for

J-361 were well below

the authorized PTE.


NOC: Operation of the 361 Building in Testing Equipment Operability Utilizing Radioxenon and Radon


1) The total abated emission limit for this Notice of



Continuous

CDM: The radionuclide

air emissions data for the

CY 2016 were reviewed

to verify the emissions

from the 361 Building

were below the NOC

limits.

2) The 361 Building is pre-cast concrete portable equipment

shelter that is pennanently located in the southwest comer of

the 300 Area on the Hanford Site. Sampling equipment (i.e.,

Swedish Automatic Unit for Noble gas and Acquisition and

analysis [SAUNA] samples atmospheric gases, some of which

may be radioactive. Periodically radioactive gases/materials

will be used to confinn operability of the instrument. The

SAUNA is a collection and analysis system. Gases/materials

are consumed by the system, analyzed, transferred to an

archive storage bottle, and then finally released by evacuating

the archive b0ttle in to the room air space. Other radioactive

gases/materials may also be utilized by the project.

Continuous

CDM: Under the PNNL

HDI system each new

research project is

required to be reviewed

via the EPR assessment

process (Procedure

EPRP-ECR-01 Rev 9.01,

Environmental

Compliance

Representative

Administrative




recorded in the EPR

database. Projects with

potential air emissions

are reviewed by Effluent

Management (EM)


Emissions Work

Control.

DOE/RL-2017-02 Rev. 0

B-228

3) The PTE for this project as detennined under WAC 246-

247-030(2 l)(a-e) [as specified in the application] is 9.00E- 04



Alpha - 0 Gas WAC 246-247-030(21)(a)


less than 10°/o of the unabated PTE and represe-nts less than

25°/o of the abated dose.

Beta - 0 Gas WAC 246-247-030(21)(a)


less than 10°/o of the unabated PTE and represents less than

25°/o of the abated dose.



Ac-225 Ac-227 Ac-228 Ag-108m Ag-108

Ag-109m Ag-110m Ag-110 Ag-111 Al-26

Al-28 Am-241 Am-242m Am-242 Am-243

Am-245 Am-246 Ar-37 Ar-39 Ar-41

Ar-42 As-74 As-76 As-77 At-217

Au-195 Au-198 Au-198 Ba-131 Ba-133

Ba-133m Ba-137m Ba-139 Ba-140 Ba-141

Ba-142 Ba-143 Be-10 Be-7 Bi-207

Bi-208 Bi-210m Bi-210 Bi-211 Bi-212

Bi-213 Bi-214 Bk-247 Bk-249 Bk-250

Br-82 Br-82m Br-83 Br-84 Br-84m

Br-85 C-11 C-14 C-15 Ca-41

Ca-45 Ca-47 Cd-107 Cd-109 Cd-111m

Cd-113m Cd-113 Cd-115m Cd-115 Cd-117

Cd-117m Ce-139 Ce-141 Ce-142 Ce-143

Ce-144 Cf-249 Cf-250 Cf-251 Cf-252

Cl-36 Cm-241 Cm-242 Cm-243 Cm-244

Cm-245 Cm-246 Cm-247 Cm-248 Cm-250

Co-56 Co-57 Co-58 Co-60 Co-60m

Cr-49 Cr-51 Cr-55 Cs-131 Cs-132

Cs-134 Cs-134m Cs-135 Cs-136 Cs-137

Cs-138 Cs-139 Cs-140 Cs-141 Cu-64

Cu-66 Dy-159 Dy-165 Dy-169 Er-169

Er-171 Es-254 Eu-150 Eu-152 Eu-152m

Eu-154 Eu-155 Eu-156 Eu-157 F-18

Fe-55 Fe-59 Fr-221 Fr-223 Ga-67

Ga-68 Ga-70 Ga-72 Gd-148 Gd-149

Gd-151 Gd-152 Gd-153 Ge-68 Ge-71

Ge-71m Ge-75 Ge-77 Ge-77m H-3

Hf-175 Hf-178m Hf-179m Hf-181 Hf-182

Hg-203 Ho-163 Ho-166 Ho-166m I-122

I-123 I-125 I-126 I-128 I-129

I-130 I-130m I-131 I-132 I-132m

I-133 I-133m I-134 I-134m I-135

In-106 In-111 In-113m In-114m In-114

In-115 In-115m In-116 In-116m In-117

In-117m Ir-192 K-40 K-42 Kr-81

Kr-81m Kr-83m Kr-85 Kr-85m Kr-87

Continuous

CDM: A NESHAPs

inventory of radioactive

materials is conducted

for PNNL facilities on

an annual basis in

accordance with PNNL-

10855 Rev. 5,

"Assessment of

Unabated Facility

Emission Potentials for

Evaluating Airborne

Radionuclide Monitoring

Requirements at PNNL-

2010". Conducted a

review of the 2016

NESHAPs radionuclide

inventory assessment

results to verify

compliance.

DOE/RL-2017-02 Rev. 0

B-229

Kr-88 Kr-89 Kr-90 La-137 La-138

La-140 La-141 La-142 La-144 Lu-177

Lu-177m Mg-27 Mg-28 Mn-52 Mn-54

Mn-56 Mo-103 Mo-104 Mo-105 Mo-93

Mo-99 N-13 Na-22 Na-24 Na-24m

Nb-100 Nb-101 Nb-103 Nb-91 Nb-91m

Nb-92 Nb-93m Nb-94 Nb-95 Nb-95m

Nb-97 Nb-97m Nb-98 Nd-144 Nd-147

Ni-56 Ni-59 Ni-63 Ni-65 Np-235

Np-236 Np-237 Np-238 Np-239 Np-240

Np-240m O-15 O-19 Os-191 P-32

P-33 Pa-231 Pa-233 Pa-234 Pa-234m

Pb-209 Pb-210 Pb-211 Pb-212 Pb-214

Pd-103 Pd-107 Pd-109 Pm-143 Pm-144

Pm-145 Pm-146 Pm-147 Pm-148m Pm-148

Pm-149 Pm-151 Po-208 Po-209 Po-210

Po-211 Po-212 Po-213 Po-214 Po-215

Po-216 Po-218 Pr-143 Pr-144 Pr-144m

Pu-234 Pu-236 Pu-237 Pu-238 Pu-239

Pu-240 Pu-241 Pu-242 Pu-243 Pu-244

Pu-246 Ra-223 Ra-224 Ra-225 Ra-226

Ra-228 Rb-81 Rb-83 Rb-84 Rb-86

Rb-87 Rb-88 Rb-89 Rb-90 Rb-90m

Re-186 Re-187 Re-188 Rh-101 Rh-102

Rh-102m Rh-103m Rh-104 Rh-105 Rh-105m

Rh-106 Rn-219 Rn-220 Rn-222 Rn-224

Ru-103 Ru-105 Ru-106 Ru-97 S-35

Sb-122 Sb-124 Sb-125 Sb-126 Sb-126m

Sb-127 Sb-129 Sc-44 Sc-46 Sc-47

Se-75 Se-79 Se-79m Si-31 Si-32

Sm-145 Sm-146 Sm-147 Sm-148 Sm-151

Sm-153 Sm-157 Sn-113 Sn-117m Sn-119m

Sn-121m Sn-121 Sn-123 Sn-125 Sn-126

Sr-85 Sr-87m Sr-89 Sr-90 Sr-91

Sr-92 Ta-179 Ta-180 Ta-182 Ta-182m

Ta-183 Tb-157 Tb-158 Tb-160 Tb-161

Tc-101 Tc-103 Tc-106 Tc-95m Tc-95

Tc-97 Tc-97m Tc-98 Tc-99 Tc-99m

Te-121m Te-121 Te-123 Te-123m Te-125m

Te-127m Te-127 Te-129m Te-129 Te-131

Te-131m Te-132 Te-133 Te-133m Te-134

Th-227 Th-228 Th-229 Th-230 Th-231

Th-232 Th-233 Th-234 Ti-44 Ti-45

Ti-51 Tl-201 Tl-204 Tl-206 Tl-207

Tl-208 Tl-209 Tm-168 Tm-170 Tm-171

U-232 U-233 U-234 U-235 U-236

U-237 U-238 U-239 U-240 V-48

V-49 W-181 W-185 W-187 W-188

Xe-122 Xe-123 Xe-125 Xe-127 Xe-127m

Xe-129m Xe-131m Xe-133 Xe-133m Xe-135

Xe-135m Xe-137 Xe-138 Xe-139 Y-88

Y-90 Y-90m Y-91 Y-91m Y-92

Y-93 Yb-164 Yb-169 Yb-175 Yb-177

Zn-65 Zn-69 Zn-69m Zr-100 Zr-88

Zr-89 Zr-93 Zr-95 Zr-97 Zr-98

Zr-99

DOE/RL-2017-02 Rev. 0

B-230













would constitute a significant modification to the Air

Operating Pennit under WAC 173-401-725(4). Notice will be






4) Monitoring - The gross alpha and gross beta release rates

will be confirmed via 40 CFR 61, Appendix D calculations in

lieu of monitoring. WAC 246-247-040( 5), -060( 5)

Continuous

CDM: A NESHAPs

Inventory of radioactive

materials is conducted

for PNNL facilities on

an annual basis in

accordance with PNNL-

10855 Rev. 5,

"Assessment of

Unabated Facility

Emission Potentials for

Evaluating Airborne

Radionuclide Monitoring

Requirements at PNNL-

2010". Reviewed the

2016 NESHAPs

radionuclide inventory

assessment results to

verify compliance.

5) RADIONUCLIDES -Activities at the 361 Building will be

assessed to ensure that no radionculides are handled that are

not listed in this license. If any activity at the 361 Building

results in a new radionuclide being handled at the building, a

written notification will be made to the Washington State

Department of Health (email is acceptable). [WAC 246-247-

060(5).

Continuous

CDM: The radionuclide

air emissions data for the

CY 2016 were reviewed

to verify the no

radionuclides were

handled in the 361

Building that were not

listed in the license.

DOE/RL-2017-02 Rev. 0

B-231

P-6241V-001 WDOH Emission Unit ID: 1228




Method




Applicable CDM: No requirement specified.


P-241A417-001 WDOH Emission Unit ID : 1229



Status


Method


Zone or Area :


Required Units : 1














Reports.


61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,







DOE/RL-2017-02 Rev. 0

B-232




Status


Method




Applicable

CDM: No requirement

specified.


P-241EW151-001 WDOH Emission Unit ID : 1231



Status


Method


Zone or Area :


Required Units : 1
















61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,







DOE/RL-2017-02 Rev. 0

B-233




Status


Method


Zone or Area :


Required Units :







Additional Requirements

Radial breather filter shall be replaced every 365 days. Annual

NDA of the filter shall be conducted for reporting purposes.

Sampling Frequency: Once per month.





Reports.


61.93(b)(4)(i) & WAC 246-247-075(3)



Continuous



Comment: 40 CFR 61,







NOC: Operation of Breather Filter on 240-S-302







(WAC 246-247-030(21)).

Continuous











The 240-S-302 catch tank is a 17,670 gallon capacity catch

tank located near S Plant. The tank has a breather filter






DOE/RL-2017-02 Rev. 0

B-234


Status


Method







radionuclide (Curies/year):

Am-241




Ce-144




Cm-243




Co-60




Cs-134




Cs-137




Eu-152




Eu-154




Eu-155





DOE/RL-2017-02 Rev. 0

B-235


Status


Method

Nb-94




Pu-239/240 | 3.05E+00

Identified as contributing greater than 10% of the potential

TEDE to the MEI, or greater than 25% of the TEDE to the

MEI after controls.

Ra-226




RuRh-106




Sb-125




Sr-89/90 | 1.58E+03

Identified as contributing greater than 10% of the potential

TEDE to the MEI, or greater than 25% of the TEDE to the

MEI after controls.







cfm. (WAC 246-247-040(5) and WAC 246-247-075(4)).



ALTERNATE APPROVAL-Release Fraction

Alternate approval is given to use a release fraction of 7.53 E-

9 based on back calculations using in situ measurements of the

control equipment efficiencies. (WAC 246-247-030 (21)(b)).

This approval cannot be used as a basis for other emission unit

alternative approvals.



CONDITIONAL ALTERNATIVE APPROVAL-NDA

Testing of Filters

Under passive ventilation pumping of waste contents for 240-

S-302 shall require a post job Non Destructive Analysis

(NDA) of the filter to validate previous NDA results, with

results reported to WDOH. (WAC 246-247-040(5) and WAC

246-247-075(4)).

Continuous



Comment: No activities

occurred during the reporting

period to require an NDA.

DOE/RL-2017-02 Rev. 0

B-236

W-TRUDECON-001 WDOH Emission Unit ID : 1243



Status


Method




program






to-emit TEDE

Continuous





stations.




2016 Hanford Site


Report.


247-075[2]



Continuous CDM:Near facility monitoring

QA programs.





W-TRUDECON-002 WDOH Emission Unit ID: 1244



Status


Method



Required Sampling: NONE Continuous CDM: No requirement

identified.





DOE/RL-2017-02 Rev. 0

B-237

P-241S102-002 WDOH Emission Unit ID : 1249



J-HAMMER-001 WDOH Emission Unit ID: 1250



Permit: AIR 09-903 (2012) Issue Date: 09-15-09 Effective Date: 02-23-12 NOC: Use of Radioactive Materials at the Volpentest HAMMER/Hanford Training and Education Center



Decon Trailer 200E (Int. Power Exhaust) WDOH Emission Unit ID: 1289



Permit: AIR 12-335 – B Issue Date: 03-06-12 Effective Date: 02-23-12 Obsolete Date: 01/25/16 NOC: Tank Farm Decontamination Trailer East



Decon Trailer 200W (Int. Power Exhaust) WDOH Emission Unit ID: 1290



Permit: AIR 12-336 – B Issue Date: 03-06-12 Effective Date: 02-23-12 Obsolete Date: 01/25/16 NOC: Tank Farm Decontamination Trailer West



Decon Trailer 200E (Collection Tank Vent) WDOH Emission Unit ID: 1291



Permit: AIR 12-335 – C Issue Date: 03-06-12 Effective Date: 02-23-12 Obsolete Date: 01/25/16 NOC: Tank Farm Decontamination Trailer East




DOE/RL-2017-02 Rev. 0

B-238

Decon Trailer 200W (Collection Tank Vent) WDOH Emission Unit ID: 1292



Permit: AIR 12-336 - C Issue Date: 03-06-12 Effective Date: 02-23-12 Obsolete Date: 01/25/16 NOC: Tank Farm Decontamination Trailer West






Status


Method


Zone or Area :


Required Units : 1

Add'l Description: Operational at all times when exhauster is

in use.



Zone or Area :


Required Units : 1

Add'l Description: Operational at all times when exhauster is

in use.



Zone or Area :


Required Units : 1

Add'l Description:



Zone or Area :

Abatement Technology : HEPA Filter

Required Units : 2




Zone or Area :


Required Units : 1

Add'l Description:








61.93(b)(4)(i) & WAC 246-247-075(2)






DOE/RL-2017-02 Rev. 0

B-239

P-242A-003 WDOH Emission Unit ID : 1294



Status


Method


Zone or Area : K-1 Exhaust System


Required Units : 3

Add'l Description: 3 parallel flow paths, 1 bank (3 x 3 array)

per flow path, 2 in operation, 1 in standby





Required Units : 3

Add'l Description: 3 parallel flow paths, 1 bank (3 x 3 array)

per flow path, 2 in operation, 1 in standby





Required Units : 2

Add'l Description: 1 in operation, 1 in standby





The exhaust air from the stack is monitored by a record sampler

through shrouded probe extraction nozzle on sample probe

located in the stack. The filter paper is analyzed and the results

of the analysis document emissions.



TOTAL BETA



61.93(b)(4)(i) & WAC 246-247-075(3)


Appendix B Method 114(3)




NOC: 242-A Evaporator Maintenance Facility Shutdowns

WDOH NOC ID: Date In AOP: 04-01-13 Page in AOP: EU1294-001


Scope will include planned maintenance facility shutdowns at

242-A Evaporator where electrical power to both 296-A-21 and

296-A-22 stacks are de-energized for greater than 24 hours.

The process of planned maintenance outages and facility

upgrades that require de-energizing both the building stack

(296-A-21) and vessel vent (296-A-22) for facility upgrades or

maintenance will be performed. Building process areas will

have the interior doors sealed with tape to help minimize

diffuse and fugitive emissions to facility personnel and the



DOE/RL-2017-02 Rev. 0

B-240

outside ambient atmosphere pursuant to meeting WAC 246-

247-130 to meet ALARACT compliance demonstration

requirements. If entry to process areas is required then

radiological controls will be in accordance with the latest


Manual to minimize both time and provide controls for diffuse

and fugitive emissions. No facility operational (double shell

tank liquid minimization) activities will be performed during

the time that neither the 296-A-21 and 296-A-22 stacks are not

operating. Radiological containment practices and devices will

be employed as applicable per the Containment Selection

Guide

2. Controls

a. Work with removable contamination will be contained per

the Containment Selection Guide, Attachment A, from the latest

revision of TFC-ESHQ-RP_RWP-C-02, Radiological

Containment.

b. HPT coverage as specified in the Radiological Work Permit.

Continuous




3. Monitoring

a. Radiological monitoring shall be in accordance with the latest


Manual.

Continuous




4. Records/Documentation

a. Radiological Work Permit

b. Radiological survey report(s)

Continuous





NOC: 242-A Evaporator Building Exhauster K-1 Upgrade







(WAC 246-247-030(21)).

Continuous



(or other source







in (WAC 246-247-030(16)), may be conducted.

The 242-A Evaporator Building Ventilation Systems are

designed for air flow from uncontaminated to progressively

more contaminated zones. The contaminated (hot) zones are

maintained at a negative pressure, while the non-contaminated

(cold) zones are maintained at a positive pressure. This is

considered a secondary confinement for liquids and airborne

particulates released to the building. Maintaining the proper

pressure in each zone will ensure that any leakage between the

zones will always flow from a cold to a hot zone minimizing

the spread of contamination.



DOE/RL-2017-02 Rev. 0

B-241

The K-1 Ventilation system exhausts the following rooms in the

Hot Zone:

- Evaporator Room

- Pump Room

- Condenser Room

- Ion Exchange Enclosure

- Load-Out and Hot Equipment Storage Room

- Loading Room

Air is exhausted from the condenser, ion exchange, evaporator,

and pump rooms through separate underground ducts into a

common header to the three exhaust filter trains.

Exhaust air from this common header passes through the two

exhaust trains having a pre-filter section and two stages of

HEPA filters in series, with a third filter train being redundant

as backup, before it is exhausted through stack 296-A-21A.

Air flow moves from areas of lesser contamination to areas of

greater contamination, while maintaining a negative air

pressure. This system has two fans, each with a 100 percent

system flow capability, with one in operation and the other fan

as back-up. Failure to maintain a specified flow will cause the

shutdown of the primary fan and initiate the startup of the

backup exhaust fan. The ventilation system will have an

approximate flow rate of 18,000 cfm (max 19,500 cfm). Each

filter train will have a 50 percent system flow rate, or

approximately 9,000 cfm.

Negative pressure in the hot zones is maintained by the

operation of the vortex damper mounted on the suction of

electric exhaust fan. The backup fan has a similar vortex

damper. Both dampers are adjusted automatically to maintain a

preset negative pressure in the Evaporator room when their

respective fan is operating.

The exhaust air from the stack will be monitored by a record

sampler and a beta continuous air monitor (CAM). The stack

radiation detector monitors the exhaust air discharged out of

Stack 296-A-21A and initiates an automatic shutdown of both

exhaust fans if beta radioactive emissions exceed the set point.

A sample of the exhaust air is withdrawn from the stack

through a shrouded probe and is sent to a record sampler where

radioactive particulates are collected on a filter paper. The filter

paper is analyzed and the results of the analysis document

emissions from the 291-A-21A Stack.

Any other replacement, replacement-in-kind, or upgrades of

parts and/or equipment not here specified, shall require review,

and/or review and approval (WAC 246-247-030(16), WAC

246-247-030(19)).



Ac-227 Alpha-0 4.20E-03 based on Am-241 Am-241

Am-243 Ba-137m Beta-0 1.80E-02 based on Sr-90

C-14 Cd-113m Cm-242 Cm-243 Cm-244


DOE/RL-2017-02 Rev. 0

B-242

Co-60 Cs-134 Cs-137 Eu-152 Eu-154

Eu-155 H-3 I-129 Nb-93m Ni-59

Ni-63 Np-237 Pa-231 Pu-238 Pu-239

Pu-240 Pu-241 Pu-242 Ra-226 Ra-228

Ru-106 Sb-125 Se-79 Sm-151 Sn-126

Sr-90 Tc-99 Th-229 Th-232 U-232

U-233 U-234 U-235 U-236 U-238

Y-90 Zr-93

The Technical Basis Document required by ANSI N13. 1-1999

(Clause 4) is required for review prior to startup operations of

the stack.

Continuous



Comment: Technical basis

document was submitted on

10/19/11 and approved on

10/20/11.

Ensure the HEPA manufactures temperature, humidity, and air

flow ratings are not exceeded (i.e., to ensure HEPA filter media

is not ruptured nor performance compromised).



To verify the alternate potential-to-emit calculation method,

annually provide the back-calculation using the measured

emission rates and in situ measurements of the control

equipment efficiencies (WAC 246-247-030(21)). A re-

evaluation of the need for this requirement may be requested

after 5 years of operation.



Periodic confirmatory monitoring (PCM) shall be required to

verify low emissions monitoring during construction,

deactivation, and operation activities. The PCM, as described in

ALARACT 5, will be used to verify low emissions during

manual soil excavation.

If a regulated Filtered Vacuum Truck (FVT) is used, the PCM

will be performed as required by either NOC_ID 774

"Operation of the Guzzler ™ in Tank Farm Facilities" or NOC

_ID 658 "Use of the Guzzler™ (Filter Vacuum Truck) Vacuum

Excavation System for Radiologically Limited Activities on the

Hanford Site," or one of the latest WDOH approval of these

two licenses. A FVT log will be used to track these emissions.

Monitoring during equipment installation and deactivation

activities will be in accordance with the following ALARACT

Demonstrations and the WRPS Radiological Control Manual:

- ALARACT 4 - Tank Farm ALARACT Demonstration for

Packaging and Transportation of Waste


Size Reduction of Waste Equipment for Disposal Contaminated

Ventilation Systems Components


Work on Potentially Contaminated Ventilation System

Components

- HNF-5183 - Tank Farms Radiological Control Manual.

Continuous


work documents, and

Radiological Survey Reports.

A report of closure for 296-A-21 is required when this emission

unit is permanently deactivated and isolated, so the department

can perform a closure inspection prior to the system's disposal.

Continuous



Comment: WDOH closure for

296-A-21 submitted 6/5/12 and

approved 6/20/13.

DOE/RL-2017-02 Rev. 0

B-243

The facility shall notify the department of any unplanned

shutdown of exhaust fans (e.g., triggered by a high exhaust

stack beta radiation level).

Continuous


work documents, WRPS



Comment: Unplanned

exhauster shutdowns during

CY 2016 and were reported per

the WRPS Notification

procedure.

W-PES-001 WDOH Emission Unit ID: 1322



Permit: AIR 11-1006 - F Issue Date: 10-28-11 Effective Date: 10-19-11 Obsolete Date: 12-19-16




Vapor Extraction System WDOH Emission Unit ID : 1326


Permit: AIR 11-1006 - G Issue Date: 10-28-11 Effective Date: 10-19-11 Obsolete Date: 12-19-16




Next Generation Retrieval (Active) WDOH Emission Unit ID : 1327


Permit: AIR 11-1006 – H Issue Date: 10-28-11 Effective Date: 10-19-11 Obsolete Date: 12-19-16







Status


Method


Zone or Area :

Abatement Technology : Deenttrainer Continuous



DOE/RL-2017-02 Rev. 0

B-244

Required Units : 1

Add'l Description: Operational at all times, when the exhauster

is in use.

Zone or Area :


Required Units : 1


is in use.



Zone or Area :


Required Units : 1

Add'l Description: Bank of prefilter NOTE: 1 bank of

prefilters not required for abatement control.



Zone or Area :


Required Units : 2

Add'l Description: 2 HEPA's in series per bank; 2 banks; 1

HEPA per bank required operational.



Zone or Area :


Required Units : 1

Add'l Description:






Continuous

CDM: ABCASH program, field

interviews, and WRPS

documents.


61.93(b)(4)(i) & WAC 246-247-075(2)



Continuous




NOC: 241-AP Tank Farm Ventilation System Upgrade Operational Permit for 241-SY/AP/AY/AZ Tank Farm

Exhauster Upgrade







(WAC 246-247-030(21)).

Continuous

CDM: Reviewed radionuclide

air emissions data (ABCASH),

or other source data/information



NOC limit.





The upgraded ventilation systems will support future tank farm

operation activities and waste feed delivery to Hanford's Waste

Treatment and Immobilization Plant (WTP).

The ventilation exhausters are being upgraded with increased



DOE/RL-2017-02 Rev. 0

B-245

flow rates to accommodate the increased heat from the mixer

pumps, which will be added to mix the waste in the waste tanks

prior to transfers and feed delivery to the WTP. The upgraded

ventilation systems include replacing the existing exhauster

trains with two new identical parallel exhauster trains. The

ventilation systems will be installed on new concrete pads.

Each exhauster train for the 241-AP ventilation system upgrade

is capable of up to 3,000 Standard Cubic Feet per Minute

(scfm) flow rate. Operation of the upgraded ventilation systems

will support the storage, treatment, retrieval, sampling, mixing,

and transfer of the waste in the tanks. Removal of the obsolete

exhausters and exhaust filter trains will be performed under

separate department approval. Monitoring of the obsolete

exhausters shall be in accordance the As Low As Reasonably

Achievable (ALARA) principles.

The emissions to the ambient air resulting from the proposed

actions covered by this NOC application, in conjunction with

other operations on the Hanford Site, shall not exceed the

National Emission Standard of 10 millirem (mrem) per year (40

CFR 61, Subpart H).

The new ventilation system shall consist of a de-entrainer

system for removal of moisture from vented air, a heater for

lowering the relative humidity of the vented air, one bank of

pre-filters, two banks of HEPA filters in series, and an exhaust

fan. Either subsystem de-entrainer may be used with either

HEPA filter subsystem via a ventilation duct cross-tie.



Ac-227 3.33E+00 Am-241 9.17E+04

Am-243 4.39E+01 Ba-137 m 1.44E+07

C-14 1.12E+02 Cd-113 m 1.32E+03

Cm-242 8.25E+01 Cm-243 8.38E+00

Cm-244 1.86E+02 Co-60 1.95E+03

Cs-134 6.82E+02 Cs-137 1.52E+07

Eu-152 6.02E+02 Eu-154 3.28E+04

Eu-155 1.90E+04 H-3 6.34E+02

I-129 8.39E+00 Nb-93 m 8.69E+02

Ni-59 5.06E+02 Ni-63 4.46E+04

Np-237 4.79E+01 Pa-231 1.70E+00

Pu-238 1.02E+03 Pu-239 1.44E+04

Pu-240 3.33E+03 Pu-241 3.69E+04

Pu-242 2.87E-01 Ra-226 3.34E-03

Ra-228 5.91E+00 Ru-106 1.14E+01

Sb-125 3.63E+03 Se-79 4.63E+01

Sm-151 1.83E+06 Sn-126 1.65E+02

Sr-90 2.33E+07 Tc-99 7.24E+03

Th-229 1.30E+00 Th-232 5.91E+00

U-232 6.24E+00 U-233 5.24E+02

U-234 6 50E+01 U-235 2.49E+00

U-236 3.07E+00 U-238 5.38E+01

Y-90 2.33E+07 Zr-93 1.06E+03

Continuous CDM: TWINS, WRPS work

documents.

CONTROL TECHNOLOGY- Annual HEPA Filter test

Each HEPA filter shall be in-place tested annually in Continuous



DOE/RL-2017-02 Rev. 0

B-246


filters shall have a minimum efficiency of 99.95%. (WAC 246-

247-060(5) and WAC 246-247-080(7)).

WDOH APPROVED LOG


approved log. (WAC 246-247-060(5) and WAC 246-247-

080(7)).


CONTROL TECHNOLOGY- Ductwork insulation


the filter housings shall be insulated. (WAC 246-247-040(5)

and WAC 246-247-060(5)).



CONTROL TECHNOLOGY- Exhauster operation

The exhauster shall be operational during waste transfers, waste

disturbing, or vapor space particulate generating activities. In

the event there is an unplanned shutdown of the exhauster,

waste transfer lines may be flushed. (WAC 246-247-040(5) and

WAC 246-247-060(5)).



CONTAMINATION CONTROL- ph control





Limits" outlined in the latest version of document "Operating

Specifications for the Double-Shell Storage Tanks, OSD-T-

151-00007". (WAC 246-247-060(5) and WAC 246-247-

080(7)).

Continuous

CDM: Review of TWINS or

other source data/information to


AP Farm is greater than 8.

CONTAMINATION CONTROL- tracer gas studies


the AP tank farms the tracer gas to be used during the tests is

helium. (WAC 246-247-060(5) and WAC 246-247-080(7)).

Continuous





CONTAMINATION CONTROL- Tracer gas injection rate


the AP tank farms the tracer gas helium will be injected into the

double shell tanks at a rate not to exceed 10 cubic feet per

minute. (WAC 246-247-060(5) and WAC 246-247-080(7)).

Continuous





CONTAMINATION CONTROL- WDOH Notification,Tracer

gas vent valves


the AP tank farms the passive filtered vents will be in the open

position. If a tracer gas test requires the passive filtered vents to

be closed notification to the Washington State Department of

Health will be made indicating when the vents will be closed

and for how long. (WAC 246-247-060(5) and WAC 246-247-

080(7)).

Continuous





CONTAMINATION CONTROL- Operations during tracer gas

studies


the AP tank farms no waste disturbing activities will occur.

(WAC 246-247-060(5) and WAC 246-247-080(7)).

Continuous





DOE/RL-2017-02 Rev. 0

B-247




Status


Method


Zone or Area :

Abatement Technology : Dennttrainer

Required Units : 1


is in use.



Zone or Area :


Required Units : 1


is in use.



Zone or Area :


Required Units : 1

Add'l Description: Bank of prefilter NOTE: 1 bank of

prefilters not required for abatement control.



Zone or Area :


Required Units : 2

Add'l Description: 2 HEPA's in series per bank; 2 banks; 1

HEPA per bank required operational.



Zone or Area :


Required Units : 1

Add'l Description:






Continuous

CDM: ABCASH program, field

interviews, and WRPS

documents.


61.93(b)(4)(i) & WAC 246-247-075(2)



Continuous



Permit: AIR 11-916 - B Issue Date: 09-30-11 Effective Date: 09-26-11 NOC: 241-AP Tank Farm Ventilation System Upgrade Operational Permit for 241-SY/AP/AY/AZ Tank Farm

Exhauster Upgrade WDOH NOC ID: 818 Date In AOP: 04-01-13 Page in AOP: EU1329-001

The total abated emission limit for this Notice of Construction is

limited to 2.62E-01 mrem/year to the Maximally Exposed




(WAC 246-247-030(21)).

Continuous




data/information for CY 2016 to

verify total abated emissions are

below the NOC limit.

DOE/RL-2017-02 Rev. 0

B-248



activities that constitute a "modification" to the emission unit, as


The upgraded ventilation systems will support future tank farm

operation activities and waste feed delivery to Hanford's Waste

Treatment and Immobilization Plant (WTP).

The ventilation exhausters are being upgraded with increased

flow rates to accommodate the increased heat from the mixer

pumps, which will be added to mix the waste in the waste tanks

prior to transfers and feed delivery to the WTP. The upgraded

ventilation systems include replacing the existing exhauster

trains with two new identical parallel exhauster trains. The

ventilation systems will be installed on new concrete pads. Each

exhauster train for the 241-AP ventilation system upgrade is

capable of up to 3,000 Standard Cubic Feet per Minute (scfm)

flow rate. Operation of the upgraded ventilation systems will

support the storage, treatment, retrieval, sampling, mixing, and

transfer of the waste in the tanks. Removal of the obsolete

exhausters and exhaust filter trains will be performed under

separate department approval. Monitoring of the obsolete

exhausters shall be in accordance the As Low As Reasonably

Achievable (ALARA) principles.

The emissions to the ambient air resulting from the proposed

actions covered by this NOC application, in conjunction with

other operations on the Hanford Site, shall not exceed the

National Emission Standard of 10 millirem (mrem) per year (40

CFR 61, Subpart H).

The new ventilation system shall consist of a de-entrainer

system for removal of moisture from vented air, a heater for

lowering the relative humidity of the vented air, one bank of

pre-filters, two banks of HEPA filters in series, and an exhaust

fan. Either subsystem de-entrainer may be used with either

HEPA filter subsystem via a ventilation duct cross-tie.





Ac-227 3.33E+00 Am-241 9.17E+04

Am-243 4.39E+01 Ba-137 m 1.44E+07

C-14 1.12E+02 Cd-113 m 1.32E+03

Cm-242 8.25E+01 Cm-243 8.38E+00

Cm-244 1.86E+02 Co-60 1.95E+03

Cs-134 6.82E+02 Cs-137 1.52E+07

Eu-152 6.02E+02 Eu-154 3.28E+04

Eu-155 1.90E+04 H-3 6.34E+02

I-129 8.39E+00 Nb-93 m 8.69E+02

Ni-59 5.06E+02 Ni-63 4.46E+04

Np-237 4.79E+01 Pa-231 1.70E+00

Pu-238 1.02E+03 Pu-239 1.44E+04

Pu-240 3.33E+03 Pu-241 3.69E+04

Pu-242 2.87E-01 Ra-226 3.34E-03

Ra-228 5.91E+00 Ru-106 1.14E+01

Sb-125 3.63E+03 Se-79 4.63E+01

Continuous CDM: TWINS, WRPS work

documents.

DOE/RL-2017-02 Rev. 0

B-249

Sm-151 1.83E+06 Sn-126 1.65E+02

Sr-90 2.33E+07 Tc-99 7.24E+03

Th-229 1.30E+00 Th-232 5.91E+00

U-232 6.24E+00 U-233 5.24E+02

U-234 6.50E+01 U-235 2.49E+00

U-236 3.07E+00 U-238 5.38E+01

Y-90 2.33E+07 Zr-93 1.06E+03

CONTROL TECHNOLOGY- Annual HEPA Filter test


accordance with the requirements of ASME AG-1. HEPA filters

shall have a minimum efficiency of 99.95%. (WAC 246-247-

060(5) and WAC 246-247-080(7)).



WDOH APPROVED LOG


approved log. (WAC 246-247-060(5) and WAC 246-247-

080(7)).


CONTROL TECHNOLOGY- Ductwork insulation


the filter housings shall be insulated. (WAC 246-247-040(5) and

WAC 246-247-060(5)).



CONTROL TECHNOLOGY- Exhauster operation

The exhauster shall be operational during waste transfers, waste

disturbing, or vapor space particulate generating activities. In

the event there is an unplanned shutdown of the exhauster,

waste transfer lines may be flushed. (WAC 246-247-040(5) and

WAC 246-247-060(5)).



CONTAMINATION CONTROL- ph control


that the radionuclide C-14 is not emitted as a gas. This condition

will be met by maintaining tank sampling and tank analysis

documents in accordance with the "Waste Chemistry Limits"

outlined in the latest version of document "Operating

Specifications for the Double-Shell Storage Tanks, OSD-T-151-

00007". (WAC 246-247-060(5) and WAC 246-247-080(7)).

Continuous

CDM: Review of TWINS or

other source data/information to


AP Farm is greater than 8.

CONTAMINATION CONTROL- tracer gas studies


the AP tank farms the tracer gas to be used during the tests is

helium. (WAC 246-247-060(5) and WAC 246-247-080(7)).

Continuous





CONTAMINATION CONTROL- Tracer gas injection rate


the AP tank farms the tracer gas helium will be injected into the

double shell tanks at a rate not to exceed 10 cubic feet per

minute. (WAC 246-247-060(5) and WAC 246-247-080(7)).

Continuous





CONTAMINATION CONTROL- WDOH Notification,Tracer

gas vent valves


the AP tank farms the passive filtered vents will be in the open

position. If a tracer gas test requires the passive filtered vents to

be closed notification to the Washington State Department of

Health will be made indicating when the vents will be closed

and for how long. (WAC 246-247-060(5) and WAC 246-247-

080(7)).

Continuous





DOE/RL-2017-02 Rev. 0

B-250

CONTAMINATION CONTROL- Operations during tracer gas

studies


the AP tank farms no waste disturbing activities will occur.

(WAC 246-247-060(5) and WAC 246-247-080(7)).

Continuous





318 Building WDOH Emission Unit ID : 1333



Status


Method




determined using 40 CFR 61 Appendix D calculations in lieu of

monitoring.


Emission results shall be reported in the Hanford Site Air

Operating Permit Annual Compliance Certification Report

Sampling Frequency: Tracking system

Radionuclide Requiring Measurement: As listed in condition

3 of this emission unit.

Continuous











PNNL-2010." Conducted a

review of the 2016 NESHAPs


assessment results to verify

compliance.

Federal and State Regulatory Requirement: WAC 246-247-

075(3)

Permit Monitoring and Testing Procedure: Tracking System

Continuous

CDM: Radionuclide emissions

during 2015 for the J-318 air

permit were estimated by

calculations performed in

accordance with 40 CFR 61,

Appendix D, and documented

in the 2016 NESHAPs

assessment results. This report

was reviewed and it was

verified that the calculated

emissions for J-318 were well

below the maximum PTE

allowed of 4.25E-04

mrem/year.


NOC: J-318 Fugitive Emissions from the 318 Building (Radiological Calibrations Laboratory)


DOE/RL-2017-02 Rev. 0

B-251




Continuous

CDM: Reviewed the




NOC limit.

The 318 Building provided technical services in internal

dosimetry, external dosimetry, instrument calibration, repair,

and testing for protecting the health of workers and the public,

and providing liability protection for government and industrial

customers. Additionally, workplace measurements are applied

to research and development (R&D) activities to better

understand and determine occupational exposures. Work

activities are performed “continuously” (i.e. year-round,

normal-business, swing-shift, and night-shift hours).

In addition to the technical services, there is direct support for

environment, health, safety and security systems. Product line

R&D includes a strategic intent of assisting the government and

individual customers to comply with exposure limits by

providing accurate information about the level of exposure and

dose to the workers from chemical and radioactive agents. The

318 Building also supports national nuclear security activities;

it also stages and maintains equipment and performs team

training for radiological assistance, training, and response to

radiological incidents.

The laboratory activities conducted in the 318 Building include:

* Instrument testing with dispersible short-lived medical

isotopes.

* Laboratory setup projects.

*Provide technical services in dosimetry and instrumentation

(e.g. calibration, and ANSI N42 equipment testing).

* Research activities involving the use and creation of mixed

activation products (MAPs) and mixed fission products (MFPs)

* Research and laboratory activities that may include processes

where the temperatures may be equal to or exceed 100C.

* Research capabilities to support determining occupational and

environmental doses and exposures.

* Research capabilities to support the development of radiation

detection and measuring instruments.

* Support of national nuclear security and radiological

assistance activities (e.g. equipment and sample management,

and training).

Continuous


system, each new research


reviewed via the Electronic

Prep & Risk (EPR) assessment

process (Procedure EPRP-

ECR-01 Rev 9.01,











Emission Work Control.




(Curies/year) of:







Continuous











PNNL-2010.” A review was

conducted of the 2016

DOE/RL-2017-02 Rev. 0

B-252











Ag-108 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)




Ag-109 m | Liquid/Particulate Solid – WAC 246-247-

030(21)(a)
































verify compliance.

DOE/RL-2017-02 Rev. 0

B-255


Ba-137 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)








































Bi-210 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)




DOE/RL-2017-02 Rev. 0

B-256

































Br-82 m | Gas | WAC 246-247-030(21)(a)












DOE/RL-2017-02 Rev. 0

B-258














































DOE/RL-2017-02 Rev. 0

B-259
















Cl-36 | Gas | WAC 246-247-030(21)(a)






























DOE/RL-2017-02 Rev. 0

B-260



















Co-60 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)



























DOE/RL-2017-02 Rev. 0

B-261






Cs-134 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)
















Cs-137 | Gas | WAC 246-247-030(21)(a)
























DOE/RL-2017-02 Rev. 0

B-262





















Es-254 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)












Eu-152 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)












DOE/RL-2017-02 Rev. 0

B-263









F-18 | Gas | WAC 246-247-030(21)(a)





































DOE/RL-2017-02 Rev. 0

B-264












































H-3 | Gas | WAC 246-247-030(21)(a)


DOE/RL-2017-02 Rev. 0

B-266






I-125 | Gas | WAC 246-247-030(21)(a)




I-126 | Gas | WAC 246-247-030(21)(a)




I-128 | Gas | WAC 246-247-030(21)(a)




I-129 | Gas | WAC 246-247-030(21)(a)




I-130 | Gas | WAC 246-247-030(21)(a)




I-130 m | Gas | WAC 246-247-030(21)(a)








I-131 | Gas | WAC 246-247-030(21)(a)




I-132 | Gas | WAC 246-247-030(21)(a)




I-132 m | Gas | WAC 246-247-030(21)(a)




DOE/RL-2017-02 Rev. 0

B-269




Kr-85 m | Gas | WAC 246-247-030(21)(a)




Kr-87 | Gas | WAC 246-247-030(21)(a)




Kr-88 | Gas | WAC 246-247-030(21)(a)




Kr-89 | Gas | WAC 246-247-030(21)(a)




Kr-90 | Gas | WAC 246-247-030(21)(a)


























DOE/RL-2017-02 Rev. 0

B-270



Lu-177 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)











































DOE/RL-2017-02 Rev. 0

B-272













































DOE/RL-2017-02 Rev. 0

B-274




Os-191 | Liquid/Particulate Solid | WAC 246-247-030(21)(a)
























Pa-234 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)


















DOE/RL-2017-02 Rev. 0

B-275























Pd-111 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)
















case assumption.





case assumption.


DOE/RL-2017-02 Rev. 0

B-276








Pm-148 m | Liquid/Particulate Solid | WAC 246-247-

030(21)(a)





































DOE/RL-2017-02 Rev. 0

B-277
























Pr-144 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)








Condition 3 Continued:














Continuous











PNNL-2010." A review was




verify compliance.

DOE/RL-2017-02 Rev. 0

B-278














































DOE/RL-2017-02 Rev. 0

B-279







































Rb-90 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)







DOE/RL-2017-02 Rev. 0

B-280


















Rh-102 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)
























Rn-219 | Gas | WAC 246-247-030(21)(a)




DOE/RL-2017-02 Rev. 0

B-282





Sb-126 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)








Sb-128 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)

































DOE/RL-2017-02 Rev. 0

B-284







































Sr-87 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)







DOE/RL-2017-02 Rev. 0

B-285


























Ta-182 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)




















DOE/RL-2017-02 Rev. 0

B-286













































DOE/RL-2017-02 Rev. 0

B-287

Te-121 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)













































DOE/RL-2017-02 Rev. 0

B-288














































DOE/RL-2017-02 Rev. 0

B-289














































DOE/RL-2017-02 Rev. 0

B-290














































DOE/RL-2017-02 Rev. 0

B-291

















Xe-122 | Gas | WAC 246-247-030(21)(a)




Xe-123 | Gas | WAC 246-247-030(21)(a)




Xe-125 | Gas | WAC 246-247-030(21)(a)




Xe-127 | Gas | WAC 246-247-030(21)(a)




Xe-127 m | Gas | WAC 246-247-030(21)(a)




Xe-129 m | Gas | WAC 246-247-030(21)(a)




Xe-131 m | Gas | WAC 246-247-030(21)(a)




DOE/RL-2017-02 Rev. 0

B-292

Xe-133 | Gas | WAC 246-247-030(21)(a)




Xe-133 m | Gas | WAC 246-247-030(21)(a)




Xe-135 | Gas | WAC 246-247-030(21)(a)




Xe-135 m | Gas | WAC 246-247-030(21)(a)




Xe-137 | Gas | WAC 246-247-030(21)(a)




Xe-138 | Gas | WAC 246-247-030(21)(a)




Xe-139 | Gas | WAC 246-247-030(21)(a)












Y-90 m Liquid/Particulate Solid WAC 246-247-030(21)(a)








Y-91 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)

DOE/RL-2017-02 Rev. 0

B-293
























case assumption.













Zn-69 m | Liquid/Particulate Solid | WAC 246-247-030(21)(a)









DOE/RL-2017-02 Rev. 0

B-294




























The radioactive isotopes identified for this emission unit are (no

quantities specified):

Ac-225 Ac-227 Ac-228 Ag-108 m Ag-108

Ag-109 m Ag-110 m Ag-110 Ag-111 Ag-111 m

Ag-113 Al-26 Al-28 Am-241 Am-242 m

Am-242 Am-243 Am-245 Am-246 Ar-37

Ar-39 Ar-41 Ar-42 As-74 As-76

As-77 At-217 Au-195 Au-198 Au-198 m

Ba-131 Ba-133 Ba-133 m Ba-137 m Ba-139

Ba-140 Ba-141 Ba-142 Ba-143 Be-10

Be-7 Bi-207 Bi-208 Bi-210 m Bi-210

Bi-211 Bi-212 Bi-213 Bi-214 Bk-249

Bk-250 Br-82 Br-82 m Br-83 Br-84

Br-84 m Br-85 C-11 C-14 C-15

Ca-41 Ca-45 Ca-47 Cd-107 Cd-109

Cd-111 m Cd-113 m Cd-113 Cd-115 m Cd-115

Cd-117 Cd-117 m Ce-139 Ce-141 Ce-142

Ce-143 Ce-144 Cf-249 Cf-250 Cf-251

Cf-252 Cl-36 Cm-241 Cm-242 Cm-243

Cm-244 Cm-245 Cm-246 Cm-247 Cm-248

Co-56 Co-57 Co-58 Co-60 Co-60 m

Cr-49 Cr-51 Cr-55 Cs-131 Cs-132

DOE/RL-2017-02 Rev. 0

B-295

Cs-134 Cs-134 m Cs-135 Cs-136 Cs-137

Cs-138 Cs-139 Cs-140 Cs-141 Cu-64

Cu-66 Dy-165 Dy-169 Er-169 Er-171

Es-254 Eu-150 Eu-152 Eu-152 m Eu-154

Eu-155 Eu-156 Eu-157 F-18 Fe-55

Fe-59 Fr-221 Fr-223 Ga-67 Ga-68

Ga-70 Ga-72 Gd-148 Gd-149 Gd-151

Gd-152 Gd-153 Ge-68 Ge-71 Ge-71 m

Ge-75 Ge-77 Ge-77 m H-3 Hf-175

Hf-178 Hf-178 m Hf-181 Hf-182 Hg-203

Ho-163 Ho-166 Ho-166 m I-122 I-123

I-125 I-126 I-128 I-129 I-130

I-130 m I-131 I-132 I-132 m I-133

I-133 m I-134 I-134 m I-135 In-106

In-111 In-113 m In-114 m In-114 In-115

In-115 m In-116 In-116 m In-117 In-117 m

Ir-192 K-40 K-42 Kr-81 Kr-81 m

Kr-83 m Kr-85 Kr-85 m Kr-87 Kr-88

Kr-89 Kr-90 La-137 La-138 La-140

La-141 La-142 La-144 Lu-177 Mg-27

Mg-28 Mn-52 Mn-54 Mn-56 Mo-103

Mo-104 Mo-105 Mo-93 Mo-99 N-13

Na-22 Na-24 Na-24 m Nb-100 Nb-101

Nb-103 Nb-91 Nb-91 m Nb-92 Nb-93 m

Nb-94 Nb-95 Nb-95 m Nb-97 Nb-97 m

Nb-98 Nb-98 m Nd-144 Nd-147 Nd-149

Ni-56 Ni-59 Ni-63 Ni-65 Np-235

Np-236 Np-237 Np-238 Np-239 Np-240

Np-240 m O-15 O-19 Os-191 P-32

P-33 Pa-231 Pa-233 Pa-234 Pa-234 m

Pb-209 Pb-210 Pb-211 Pb-212 Pb-214

Pd-103 Pd-107 Pd-109 Pd-111 Pd-111 m

Pm-143 Pm-144 Pm-145 Pm-146 Pm-147

Pm-148 m Pm-148 Pm-149 Pm-151 Po-208

Po-209 Po-210 Po-211 Po-212 Po-213

Po-214 Po-215 Po-216 Po-218 Pr-143

Pr-144 Pr-144 m Pr-145 Pu-234 Pu-236

Pu-237 Pu-238 Pu-239 Pu-240 Pu-241

Pu-242 Pu-243 Pu-244 Pu-246 Ra-223

Ra-224 Ra-225 Ra-226 Ra-228 Rb-81

Rb-83 Rb-84 Rb-86 Rb-87 Rb-88

Rb-89 Rb-90 Rb-90 m Re-186 Re-187

Re-188 Rh-101 Rh-102 Rh-102 m Rh-103 m

Rh-104 Rh-105 Rh-105 m Rh-106 Rn-219

Rn-220 Rn-222 Rn-224 Ru-103 Ru-105

Ru-106 Ru-97 S-35 Sb-122 Sb-124

Sb-125 Sb-126 Sb-126 m Sb-127 Sb-128

Sb-128 m Sb-129 Sb-130 Sc-44 Sc-46

Sc-47 Se-75 Se-79 Se-79 m Si-31

Sm-145 Sm-146 Sm-147 Sm-148 Sm-151

Sm-153 Sm-157 Sn-113 Sn-117 m Sn-119 m

Sn-121 m Sn-121 Sn-123 Sn-125 Sn-126

Sn-127 Sn-128 Sr-85 Sr-87 m Sr-89

Sr-90 Sr-91 Sr-92 Ta-179 Ta-180

Ta-182 Ta-182 m Ta-183 Tb-157 Tb-158

Tb-160 Tb-161 Tc-101 Tc-103 Tc-106

DOE/RL-2017-02 Rev. 0

B-296

Tc-95 m Tc-97 Tc-97 m Tc-98 Tc-99

Tc-99 m Te-121 m Te-121 Te-123 Te-123 m

Te-125 m Te-127 m Te-127 Te-129 m Te-129

Te-131 Te-131 m Te-132 Te-133 Te-133 m

Te-134 Th-227 Th-228 Th-229 Th-230

Th-231 Th-232 Th-233 Th-234 Ti-44

Ti-45 Ti-51 Tl-201 Tl-204 Tl-206

Tl-207 Tl-208 Tl-209 Tm-168 Tm-170

Tm-171 U-232 U-233 U-234 U-235

U-236 U-237 U-238 U-239 U-240

V-48 V-49 W-181 W-185 W-187

W-188 Xe-122 Xe-123 Xe-125 Xe-127

Xe-127 m Xe-129 m Xe-131 m Xe-133 Xe-133 m

Xe-135 Xe-135 m Xe-137 Xe-138 Xe-139

Y-88 Y-90 Y-90 m Y-91 Y-91 m

Y-92 Y-93 Yb-164 Yb-169 Yb-175

Yb-177 Zn-65 Zn-69 Zn-69 m Zr-100

Zr-88 Zr-89 Zr-93 Zr-95 Zr-97

Zr-98 Zr-99









TEDE to the MEI after controls. WAC 246-247-110(9). DOE










W-MARS-001 WDOH Emission Unit ID : 1334


Emission unit closed as of 07/23/15 per AIR 15-801.




Permit: AIR 11-915 – A Issue Date: 09-30-11 Effective Date: 09-26-11 NOC: 241-SY Tank Farm Ventilation System Upgrade Operational Permit for 241-SY/AP/AY/AZ Tank Farm

DOE/RL-2017-02 Rev. 0

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Permit: AIR 11-915 – B Issue Date: 09-30-11 Effective Date: 09-26-11 NOC: 241-SY Tank Farm Ventilation System Upgrade Operational Permit for 241-SY/AP/AY/AZ Tank Farm





Emission unit closed as of 07/23/15 per AIR 15-801.

EP-331-09-S WDOH Emission Unit ID : 1370



Status


Method



Required Sampling: The radioactive material inventory will be

tracked throughout the year to ensure that the yearly emission

limit is not exceeded.

Sampling Frequency: Inventory

Radionuclide Requiring Measurement: As listed in condition

3 of this emission unit

Continuous











PNNL-2010". Conducted a

review of the 2016 NESHAP


assessment results to verify

compliance.

Federal and State Regulatory Requirement: WAC 246-247-

075(3)

Permit Monitoring and Testing Procedure: Determine using

40 CFR 61 Appendix D calcuations in lieu of monitoring

Continuous

CDM: Radionuclide emissions

during 2016 for the 331-09 air

permit were estimated by

calculations performed in

accordance with 40 CFR 61,

DOE/RL-2017-02 Rev. 0

B-298

Appendix D, and documented

in the 2016 NESHAPs

assessment results. This report

was reviewed and it was

verified that the calculated

emissions for 331-09 were

well below the maximum PTE

allowed of 9.93E-04

mrem/year.


NOC: The Operation of EP-331-09-S in the North Wing at the Life Sciences Laboratory (331 Building)


1) The total abated emission limit for this Notice of

Construction is limited to 9.93E-04 mrem/year to the Maximally

Exposed Individual (WAC 246-247-040(5)).

Continuous

CDM: Reviewed the



abated emissions are below

the NOC limit.

2) The mission of the 331 Building is to conduct fundamental

science and develop enviromnental technology. Research

activities conducted in the 331 Building support the Hanford

Site environmental mission and other key DOE missions of

national and international importance. Research activities

performed within the 331 Building include the use of

radioactive materials. Laboratory processes are conducted

"continuously" (i.e., year-round, during normal business, swing-

shift, night-shift, and weekend hours). The 331 Building

provides research capabilities to study the interactions of

chemicals and radionuclides with plants, animals, and

microorganisms and the fate of chemicals and radionuclides in

the environment. The building also has research capabilities for

Nuclear Magnetic Resonance (NMR) and actinide chemistry.

The research activities conducted in the 331 Building, emission

unit EP-331-09-S include:

• Actinide chemistry involving liquids and solids.

• Examining the uptake and transformation effects of

radionuclides in soils, plants, animals, and microorganisms.

• Experimental studies with molecular and cellular processes.

• Laboratory setup projects involving fume hood

removals/upgrades and ductwork tie-in. Measurements of

exposures to physical, radiological, and chemical agents.

• Non-dispersible radioactive material uses in research

programs.

• NuNMR spectroscopic experiments with radioactive and non-

radioactive materials. Processes in which temperatures may

exceed 100 degrees centigrade. • Research activities involving

various types of radioactive material, including mixed activation

products (MAPs), Mixed fission products (MFPs), and

naturally-occuring radioactive material, actinides, and a wide

range of standards and tracer radionuclides.

• Studies with radioactive materials in biological and non-

biological systems.

Continuous


system each new research


reviewed via the EPR

assessment process (Procedure

EPRP-ECR-01 Rev 9.01.











Emissions Work Control.

DOE/RL-2017-02 Rev. 0

B-299

3) The PTE for this project as determined under WAC 246-247-

030(2 l)(a-e) [as specified in the application] is 9.93E- 04


(Curies/year) of: Ac-225 Liquid/Particulate Solid WAC 246-

247-030(21 )(a)


less than 10% of the unabated PTE and represents less than 25%

of the abated dose.

Ac-227 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Ac-228 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Ag-108 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.



less than 10%o of the unabated PTE and represents less than


Al-26 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Al-28 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Am-241 Gas WAC 246-247-030(21 )(a)



of the abated dose.

Am-241 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.



Continuous











PNNL-2010". A review was




verify compliance.

DOE/RL-2017-02 Rev. 0

B-300


of the abated dose.

Am-242m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Ar-37 Gas WAC 246-247-030(21 )(a)



of the abated dose.

Ar-39 Gas WAC 246-247-030(21 )(a)



of the abated dose.

Ar-41 Gas WAC 246-247-030(21 )(a)



of the abated dose.

Ar-42 Gas WAC 246-247-030(21 )(a)



of the abated dose.

As-74 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

As-76 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

At-217 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



DOE/RL-2017-02 Rev. 0

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of the abated dose.

Au-195 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

Au-198m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Ba-131 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.

Ba-133m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Ba-137m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

DOE/RL-2017-02 Rev. 0

B-302




of the abated dose.




of the abated dose.

Be-10 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Be-7 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Bi-207 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

DOE/RL-2017-02 Rev. 0

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Bk-247 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

Br-82 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Br-82m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

Br-84m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.

C-11 Gas WAC 246-247-030(21 )(a)



of the abated dose.

C-14 Gas WAC 246-247-030(21 )(a)



of the abated dose.

C-15 Gas WAC 246-247-030(21 )(a)

DOE/RL-2017-02 Rev. 0

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of the abated dose.

Ca-41 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

Cd-107 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.

Cd-111m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.



DOE/RL-2017-02 Rev. 0

B-305


of the abated dose.




of the abated dose.

Ce-141 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Cf-249 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Cl-36 Gas WAC 246-247-030(21 )(a)



of the abated dose.

Cm-141 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



DOE/RL-2017-02 Rev. 0

B-306

of the abated dose.



less than 1Oo/o of the unabated PTE and represents less than





of the abated dose.








of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Co-56 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

DOE/RL-2017-02 Rev. 0

B-307




of the abated dose.

Co-60m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Cr-49 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

Cs-131 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.

Cs-134m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

DOE/RL-2017-02 Rev. 0

B-308




of the abated dose.

Cs-137 Gas WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Cu-64 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Cu-66 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Dy-159 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

Er-169 Liquid/Particulate Solid WAC 246-247-030(21 )(a)

DOE/RL-2017-02 Rev. 0

B-309



of the abated dose.

Er-171 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Es-254 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Eu-150 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

Eu-152m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

F-18 Liquid/Particulate Solid WAC 246-247-030(21 )(a)


DOE/RL-2017-02 Rev. 0

B-310


of the abated dose.

Fe-55 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Fe-59 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Fr-221 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Fr-223 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Ga-67 Liquid/Particulate Solid WAC 246-247-030(21 )(a)


less than 10 of the unabated PTE and represents less than 25%

of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Gd-148 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




Continuous















verify compliance.

DOE/RL-2017-02 Rev. 0

B-311





of the abated dose.




of the abated dose.

Ge-68 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.





Ge-71m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

Ge-77m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

H-3 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Hf-175 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Hf-178m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

DOE/RL-2017-02 Rev. 0

B-312

Hf-179m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.





Hg-203 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Ho-163 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Ho-166 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Ho-166m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

I-122 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

DOE/RL-2017-02 Rev. 0

B-313




of the abated dose.




of the abated dose.




of the abated dose.

I-130m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.


DOE/RL-2017-02 Rev. 0

B-314



of the abated dose.

In-106 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.

In-113m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.







DOE/RL-2017-02 Rev. 0

B-315


of the abated dose.

Ir-192 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

K-40 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

K-42 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Kr-81 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Kr-81m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.





Kr-85m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




Continuous















verify compliance.

DOE/RL-2017-02 Rev. 0

B-316

of the abated dose.




of the abated dose.

La-137 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Lu-177 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Lu-177m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Mg-28 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Mn-52 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

DOE/RL-2017-02 Rev. 0

B-317




of the abated dose.




of the abated dose.

Mo-103 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

N-13 Gas WAC 246-247-030(21 )(a)



of the abated dose.

Na-22 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Na-24 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Na-24m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

DOE/RL-2017-02 Rev. 0

B-318

Nb-100 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.



less than 10%of the unabated PTE and represents less than 25%

of the abated dose.




of the abated dose.

Nb-91m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.



DOE/RL-2017-02 Rev. 0

B-319


of the abated dose.

Nd-144 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Nd-147 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Ni-56 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Np-236 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




DOE/RL-2017-02 Rev. 0

B-320

of the abated dose.

Np-240m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

O-15 Gas WAC 246-247-030(21 )(a)



of the abated dose.

O-19 Gas WAC 246-247-030(21 )(a)



of the abated dose.

Os-191 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

P-32 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

P-33 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Pa-231 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

Pa-234m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Pb-209 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

DOE/RL-2017-02 Rev. 0

B-321




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Pd-103 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

Pm-143 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

DOE/RL-2017-02 Rev. 0

B-322




of the abated dose.




of the abated dose.

Pm-148m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

Po-208 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.


DOE/RL-2017-02 Rev. 0

B-323



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Pr-144 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Pr-144m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Pu-234 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.



DOE/RL-2017-02 Rev. 0

B-324






of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Ra-223 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Rb-81 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



DOE/RL-2017-02 Rev. 0

B-325

of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Rb-90m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Re-186 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

DOE/RL-2017-02 Rev. 0

B-326

Rh-102 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Rh-102m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Rn-220 Gas WAC 246-247-030(21 )(a)



of the abated dose.

Rn-222 Gas WAC 246-247-030(21 )(a)



of the abated dose.

Rn-224 Gas WAC 246-247-030(21 )(a)



of the abated dose.

Ru-103 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

DOE/RL-2017-02 Rev. 0

B-327




of the abated dose.




of the abated dose.




of the abated dose.

S-35 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Sb-122 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Sb-126m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

Sc-44 Liquid/Particulate Solid WAC 246-247-030(21 )(a)

DOE/RL-2017-02 Rev. 0

B-328



of the abated dose.




of the abated dose.




of the abated dose.

Se-75 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Se-79 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Se-79m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Si-31 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Si-32 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Sm-145 Liquid/Particulate Solid WAC 246-247-030(21 )(a)







of the abated dose.




of the abated dose.



DOE/RL-2017-02 Rev. 0

B-329


of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Sn-113 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Sn-117m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




DOE/RL-2017-02 Rev. 0

B-330

of the abated dose.

Sr-85 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Sr-87m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Ta-179 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

Ta-182m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.

Continuous











PNNL-2010." A review was




verify compliance.

DOE/RL-2017-02 Rev. 0

B-331

Tb-157 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.








of the abated dose.

Tc-101 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Tc-95m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

DOE/RL-2017-02 Rev. 0

B-332




of the abated dose.




of the abated dose.




of the abated dose.

Te-121 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Te-121m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.


DOE/RL-2017-02 Rev. 0

B-333



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Th-227 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.



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of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Ti-44 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

Tl-201 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




DOE/RL-2017-02 Rev. 0

B-335

of the abated dose.




of the abated dose.

Tm-168 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

U-232 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

DOE/RL-2017-02 Rev. 0

B-336




of the abated dose.




of the abated dose.

V-48 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

V-49 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

W-181 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Xe-122 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

DOE/RL-2017-02 Rev. 0

B-337




of the abated dose.

Xe-127m Liquid/Particulate Solid WAC 246-247-030(21 )(a)


less than 10o/o of the unabated PTE and represents less than





of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Y-88 Liquid/Particulate Solid WAC 246-247-030(21 )(a)

DOE/RL-2017-02 Rev. 0

B-338



of the abated dose.




of the abated dose.

Y-90m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.

Y-91m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.

Yb-164 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.

Zn-65 Liquid/Particulate Solid WAC 246-247-030(21 )(a)


DOE/RL-2017-02 Rev. 0

B-339


of the abated dose.

Zn-69 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Zn-69m Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.

Zr-100 Liquid/Particulate Solid WAC 246-247-030(21 )(a)



of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.




of the abated dose.



less than 10o/o of the unabated PTE and represents less than





of the abated dose.




of the abated dose.

DOE/RL-2017-02 Rev. 0

B-340

The radioactive isotopes identified for this emission unit are (no

quantities specified):

Ac-225 Ac-227 Ac-228 Ag-108m Ag-108

Ag-109m Ag-110m Ag-110 Ag-111 Al-26

Al-28 Am-241 Am-242m Am-242 Am-243

Am-245 Am-246 Ar-37 Ar-39 Ar-41

Ar-42 As-74 As-76 As-77 At-217

Au-195 Au-198 Au-198 Ba-131 Ba-133

Ba-133m Ba-137m Ba-139 Ba-140 Ba-141

Ba-142 Ba-143 Be-10 Be-7 Bi-207

Bi-208 Bi-210m Bi-210 Bi-211 Bi-212

Bi-213 Bi-214 Bk-247 Bk-249 Bk-250

Br-82 Br-82m Br-83 Br-84 Br-84m

Br-85 C-11 C-14 C-15 Ca-41

Ca-45 Ca-47 Cd-107 Cd-109 Cd-111m

Cd-113m Cd-113 Cd-115m Cd-115 Cd-117

Cd-117m Ce-139 Ce-141 Ce-142 Ce-143

Ce-144 Cf-249 Cf-250 Cf-251 Cf-252

Cl-36 Cm-241 Cm-242 Cm-243 Cm-244

Cm-245 Cm-246 Cm-247 Cm-248 Cm-250

Co-56 Co-57 Co-58 Co-60 Co-60m

Cr-49 Cr-51 Cr-55 Cs-131 Cs-132

Cs-134 Cs-134m Cs-135 Cs-136 Cs-137

Cs-138 Cs-139 Cs-140 Cs-141 Cu-64

Cu-66 Dy-159 Dy-165 Dy-169 Er-169

Er-171 Es-254 Eu-150 Eu-152 Eu-152m

Eu-154 Eu-155 Eu-156 Eu-157 F-18

Fe-55 Fe-59 Fr-221 Fr-223 Ga-67

Ga-68 Ga-70 Ga-72 Gd-148 Gd-149

Gd-151 Gd-152 Gd-153 Ge-68 Ge-71

Ge-71m Ge-75 Ge-77 Ge-77m H-3

Hf-175 Hf-178m Hf-179m Hf-181 Hf-182

Hg-203 Ho-163 Ho-166 Ho-166m I-122

I-123 I-125 I-126 I-128 I-129

I-130 I-130m I-131 I-132 I-132m

I-133 I-133m 1-134 I-134m I-135

In-106 In-111 In-113m In-114m In-114

In-115 In-115m In-116 In-116m In-117

In-117m Ir-192 K-40 K-42 Kr-81

Kr-81m Kr-83m Kr-85 Kr-85m Kr-87

Kr-88 Kr-89 Kr-90 La-137 La-138

La-140 La-141 La-142 La-144 Lu-177

Lu-177m Mg-27 Mg-28 Mn-52 Mn-54

Mn-56 Mo-103 Mo-104 Mo-105 Mo-93

Mo-99 N-13 Na-22 Na-24 Na-24m

Nb-100 Nb-101 Nb-103 Nb-91 Nb-91m

Nb-92 Nb-93m Nb-94 Nb-95 Nb-95m

Nb-97 Nb-97m Nb-98 Nd-144 Nd-147

Ni-56 Ni-59 Ni-63 Ni-65 Np-235

Np-236 Np-237 Np-238 Np-239 Np-240

Np-240m 0-15 0-19 Os-191 P-32

P-33 Pa-231 Pa-233 Pa-234 Pa-234m

Pb-209 Pb-210 Pb-211 Pb-212 Pb-214

Pd-103 Pd-107 Pd-109 Pm-143 Pm-144

Pm-145 Pm-146 Pm-147 Pm-148m Pm-148

DOE/RL-2017-02 Rev. 0

B-341

Pm-149 Pm-151 Po-208 Po-209 Po-210

Po-211 Po-212 Po-213 Po-214 Po-215

Po-216 Po-218 Pr-143 Pr-144 Pr-144m

Pu-234 Pu-236 Pu-237 Pu-238 Pu-239

Pu-240 Pu-241 Pu-242 Pu-243 Pu-244

Pu-246 Ra-223 Ra-224 Ra-225 Ra-226

Ra-228 Rb-81 Rb-83 Rb-84 Rb-86

Rb-87 Rb-88 Rb-89 Rb-90 Rb-90m

Re-186 Re-187 Re-188 Rh-101 Rh-102

Rh-102m Rh-103m Rh-104 Rh-105 Rh-105m

Rh-106 Rn-219 Rn-220 Rn-222 Rn-224

Ru-103 Ru-105 Ru-106 Ru-97 S-35

Sb-122 Sb-124 Sb-125 Sb-126 Sb-126m

Sb-127 Sb-129 Sc-44 Sc-46 Sc-47

Se-75 Se-79 Se-79m Si-31 Si-32

Sm-145 Sm-146 Sm-147 Sm-148 Sm-151

Sm-153 Sm-157 Sn-113 Sn-117m Sn-119m

Sn-121m Sn-121 Sn-123 Sn-125 Sn-126

Sr-85 Sr-87m Sr-89 Sr-90 Sr-91

Sr-92 Ta-179 Ta-180 Ta-182 Ta-182m

Ta-183 Tb-157 Tb-158 Tb-160 Tb-161

Tc-101 Tc-103 Tc-106 Tc-95m Tc-95

Tc-97 Tc-97m Tc-98 Tc-99 Tc-99m

Te-121m Te-121 Te-123 Te-123m Te-125m

Te-127m Te-127 Te-129m Te-129 Te-131

Te-131m Te-132 Te-133 Te-133m Te-134

Th-227 Th-228 Th-229 Th-230 Th-231

Th-232 Th-233 Th-234 Ti-44 Ti-45

Ti-51 Tl-201 Tl-204 Tl-206 Tl-207

Tl-208 Tl-209 Tm-168 Tm-170 Tm-171

U-232 U-233 U-234 U-235 U-236

U-237 U-238 U-239 U-240 V-48

V-49 W-181 W-185 W-187 W-188

Xe-122 Xe-123 Xe-125 Xe-127 Xe-127m

Xe-129m Xe-131m Xe-133 Xe-133m Xe-135

Xe-135m Xe-137 Xe-138 Xe-139 Y-88

Y-90 Y-90m Y-91 y-91m Y-92

Y-93 Yb-164 Yb-169 Yb-175 Yb-177

Zn-65 Zn-69 Zn-69m Zr-100 Zr-88

Zr-89 Zr-93 Zr-95 Zr-97 Zr-98

Zr-99

The potential release rates described in this Condition were used

to determine control technologies and monitoring requirements

for this approval.

DOE must notify the Department of a "modification" to the

emission unit, as defined in WAC 246-247-030(16). DOE must

notify the Department of any changes to a NESHAP major

emission unit when a specific isotope is newly identified as

contributing greater than l 0% of the potential TEDE to the



Department of any changes to potential release rates as required

by state or federal regulations including changes that would

constitute a significant modification to the Air Operating Permit

DOE/RL-2017-02 Rev. 0

B-342

under WAC 173-401-725(4). Notice will be provided

according to the particular regulation under which notification is

required.

If the applicable regulation(s) does not address manner and type




4) Inventory- The radiological material used in this emission

unit will be tracked using the Pacific Northwest National

Laboratory Radiological Material Tracking system.

Continuous

CDM: Verified that this

emission unit was included in

the NESHAP reports

generated by RMT for 2016.

5) RELEASE RATE - Emission unit will be limited to an

unabated gross alpha release rate of l .93E-05 Curies/year for

alpha emitting isotopes.

Continuous


emissions data for the CY

2016 were reviewed to verify

that the gross alpha emissions

for this emission unit were less

than the NOC limit.

6) RELEASE RATE - Emission unit will be limited to an

unabated gross beta release rate of 5.1OE-05 Curies/year for

beta emitting isotopes.

Intermittent


emissions data for the CY

2016 were reviewed. The

Appendix D calculations for

gross beta emissions for this

emission unit were 1.19E-04

Ci, which is over the NOC

limit.

Comment: The sources at this

location are liquid scintillation

counter (LSC) standards that

were previously certified as

sealed sources. These sources

have not been opened, so they

really have no potential to

emit.

7) MONITORING -The gross alpha and gross beta rates wiil be

confirmed via 40 CFR 61, Appendix D calculations in lieu of

monitoring.

Continuous

CDM: Radioactive gases

released are tracked by the

Radioactive Gas

Inventory/Database.

Radionuclide emissions were

evaluated during the annual

NESHAPS inventory

assessment.

DOE/RL-2017-02 Rev. 0

B-343




Status


Method


Zone or Area :


Required Units : 1

Add'l Description: Passive breather filters















61.93[b][4][i] & WAC 246-247-075[3]






NOC: Operation of 200 W-MARS-003




Individual (WAC 246-24-7-040(5)). The total limit on the



(WAC 246-247-030(21)).







MOBILE ARM RETRIEVAL SYSTEM

The Mobile Arm Retrieval System (MARS) is a waste

retrieval system used to retrieve waste from single-shell tanks

(SSTs) and move the waste to the double-shell tanks (DSTs).

The MARS employs two design options similar to currently

permitted systems: 1) a sluicing retrieval option is intended for

retrieval of non-leaker tanks and 2) a vacuum retrieval option

which is intended for retrieval of assumed leaker tanks. Both

options use an arm and sluicing jets and/or a high pressure

water scarifier to break up the waste. The sluicer uses waste

supernatant recycled from the DST to form a liquid jet using a

nozzle. The scarifier uses filtered, pressurized water that



DOE/RL-2017-02 Rev. 0

B-344

comes from a high pressure water skid.

The equipment portion of the MARS includes a vertical,

carbon steel mast (square cross section) as the main structural

member. Attached to the vertical mast is a carbon fiber robotic

arm. The arm is attached to a traveler that raises and lowers

the arm relative to the vertical mast. The arm rotates 360

degrees - 380 degrees on a turntable located in the

containment box. The arm also pivots up and down from an

elbow at the traveler (hydraulic system) and extends and

retracts (hydraulic system). The end of the arm articulates. The

arm thus provides for a large range of motion such that the

sluicing devices (recycle sluicer, vacuum, water scarifier)

located at the end of the arm can aim at most portions of the

tank and from varying (e.g., short) distances.



Ac-227 Alpha-0 8.68E+03 Am - 241

All Alpha activity was attributed to Am-241

Am - 243 Ba -137 m Beta - 0 2.91E+06

All Beta radioactivity was attributed to Sr-90

C – 14 Cd-113 m Cm – 242 Cm – 243 Cm – 244

Co -60 Cs -134 Cs – 137 Eu – 152 Eu – 154

Eu – 155 H-3 I – 129 Nb - 93 m Ni - 59

Ni -63 Np – 237 Pa – 231 Pu – 238 Pu – 239

Pu – 240 Pu – 241 Pu – 242 Ra -226 Ra – 228

Ru – 106 Sb – 125 Se – 79 Sm – 151 Sn - 126

Sr – 90 Tc-99 Th – 229 Th – 232 U – 232

U – 233 U -234 U – 235 U – 236 U -238

Y- 90 Zr- 93



ALTERNATIVE APPROVAL-Annual Replacement

Approval is given to replace the filter on an annual basis with

the manufacturer tested and certification of HEPA filter with a

tested rating of 99.97% efficiency. Records of this testing shall

be maintained on file. (WAC 246- 247-040(5), WAC 246-247-

060(5), WAC 246-247-075(4))



EMISSION UNITS IDENTIFIED

The emission unit will be clearly identified. (WAC 246-247-

040(5))



ALTERNATE APPROVAL-Confirmatory Measurements

Confirmatory measurements of stack emissions shall be in

accordance with Hanford's Near-facility Environmental

Monitoring Program and augmented by smear surveys of the

filter unit during annual replacement. See Monitoring

Requirements above. (WAC 246-247-040(5)) and (WAC 246-

247-060(5)).



WDOH NOTIFICATION-Retrieval Under Passive Ventilation

Conditions

Retrieval activities shall occur under passive ventilation only

when an exhauster can no longer be operated on a single shell

tank due to structural concerns. The justification for structural

concerns with the single shell tank shall be documented and

provided to WDOH upon request. WAC 246-247-040(5)) and

(WAC 246-247-060(5)).



DOE/RL-2017-02 Rev. 0

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Status


Method


Zone or Area :


Required Units : 1

Add'l Description: Passive breather filters















61.93[b][4][i] & WAC 246-247-075[3]






NOC: Operation of 200 W-MARS 004




Individual (WAC 246-24-7-040(5)). The total limit on the



(WAC 246-247-030(21)).







MOBILE ARM RETRIEVAL SYSTEM

The Mobile Arm Retrieval System (MARS) is a waste

retrieval system used to retrieve waste from single-shell tanks

(SSTs) and move the waste to the double-shell tanks (DSTs).

The MARS employs two design options similar to currently

permitted systems: 1) a sluicing retrieval option is intended for

retrieval of non-leaker tanks and 2) a vacuum retrieval option

which is intended for retrieval of assumed leaker tanks. Both

options use an arm and sluicing jets and/or a high pressure

water scarifier to break up the waste. The sluicer uses waste

supernatant recycled from the DST to form a liquid jet using a

nozzle. The scarifier uses filtered, pressurized water that



DOE/RL-2017-02 Rev. 0

B-346

comes from a high pressure water skid.

The equipment portion of the MARS includes a vertical,

carbon steel mast (square cross section) as the main structural

member. Attached to the vertical mast is a carbon fiber robotic

arm. The arm is attached to a traveler that raises and lowers

the arm relative to the vertical mast. The arm rotates 360

degrees - 380 degrees on a turntable located in the

containment box. The arm also pivots up and down from an

elbow at the traveler (hydraulic system) and extends and

retracts (hydraulic system). The end of the arm articulates. The

arm thus provides for a large range of motion such that the

sluicing devices (recycle sluicer, vacuum, water scarifier)

located at the end of the arm can aim at most portions of the

tank and from varying (e.g., short) distances.



Ac-227 Alpha-0 8.68E+03 Am - 241

All Alpha activity was attributed to Am-241

Am – 243 Ba-137 m Beta – 0 2.91E+06


C – 14 Cd-113 m Cm – 242 Cm – 243 Cm - 244

Co -60 Cs -134 Cs – 137 Eu – 152 Eu – 154

Eu – 155 H-3 I – 129 Nb - 93 m Ni - 59

Ni -63 Np – 237 Pa – 231 Pu - 238 Pu – 239

Pu – 240 Pu – 241 Pu – 242 Ra -226 Ra – 228

Ru – 106 Sb – 125 Se – 79 Sm – 151 Sn - 126

Sr – 90 Tc-99 Th – 229 Th – 232 U – 232

U – 233 U -234 U – 235 U – 236 U -238

Y- 90 Zr- 93



ALTERNATIVE APPROVAL-Annual Replacement

Approval is given to replace the filter on an annual basis with

the manufacturer tested and certification of HEPA filter with a

tested rating of 99.97% efficiency. Records of this testing shall

be maintained on file. (WAC 246- 247-040(5), WAC 246-247-

060(5), WAC 246-247-075(4))




The emission unit will be clearly identified. (WAC 246-247-

040(5))



ALTERNATE APPROVAL-Confirmatory Measurements

Confirmatory measurements of stack emissions shall be in

accordance with Hanford's Near-facility Environmental

Monitoring Program and augmented by smear surveys of the

filter unit during annual replacement. See Monitoring

Requirements above. (WAC 246-247-040(5)) and (WAC 246-

247-060(5)).



WDOH NOTIFICATION-Retrieval Under Passive Ventilation

Conditions

Retrieval activities shall occur under passive ventilation only

when an exhauster can no longer be operated on a single shell

tank due to structural concerns. The justification for structural

concerns with the single shell tank shall be documented and

provided to WDOH upon request. WAC 246-247-040(5)) and

(WAC 246-247-060(5)).



DOE/RL-2017-02 Rev. 0

B-347

W-SXPWET-001 WDOH Emission Unit ID : 1391




NOC: SX Farm Pore Water Extraction Test Project



W-AZ-301 Tanker-001 WDOH Emission Unit ID : 1406



Status


Method


Zone or Area :

Abatement Technology : Radial HEPA Filter

Required Units : 1

Add'l Description: Tanker trailer breather, Radial HEPA

filter



Required Sampling: Smear survey on the outside of the

outlet of the vent.

Sampling Frequency: Annually at a minimum

Radionuclide Requiring Measurement: Total Alpha and

Total Beta/Gamma.


Reports.


61.93[b][4][i] & WAC 246-247-075[3]



Continuous



Comment: 40 CFR 61,







NOC: Operation of the AZ-301 Tanker for Condensate Collection and Transport







(WAC 246-247-030(21)).

Continuous






NOC limit.


No additional activities or variations on the approved activities Continuous



DOE/RL-2017-02 Rev. 0

B-348



The AZ-301 Tanker project consists of operation of a pumping

system to transport condensate from catch tank AZ- 30 1 into

the tanker. A tanker would be deployed outside of the 241-A

Y/ AZ Tank Farm. The condensate is transported to another

permitted facility, such as Liquid Effluent Retention Facility,

or Effluent Treatment Facility.

241-A Y and 241-AZ Tank farms are ventilated by the 296-A-

42 primary exhauster. Condensate from various points in the

primary exhauster are collected and routed to the AZ-301

catch tank. The AZ-301 catch tank has a nominal 1,200 gallon

capacity and condensate is currently routed to AZ-102 or A Y-

101. Alternate options are needed as AY and AZ tanks are

nearing capacity.

Emission from the AZ-301 Tanker project, in conjunction with

other operations on the Hanford site, will not exceed the

National Emission Standard of 10 millirem (mrem) per year

(40 CFR 61, Subpart H). The pumping operation shall follow

As Low As Reasonably Achievable (ALARA) practices. The

hose from AZ-301 to the tanker shall be hose in hose design so

that any leak in the primary hose is contained. The hose is also

elevated with a slant back toward the tank. The tanker has a

catch basin.

The AZ-301 Tanker Project is designed to minimize potential

emissions. A radial HEPA filter is used to vent the tanker

while it is being filled. To prevent the potential for inadvertent

release during the connection and disconnection of the hoses

"dry-break" type connections are used. The top of the tanker

where the condensate is pumped into the truck has a catch

basin so that any condensate does not reach the ground.

ALARA practices are employed during pumping operations

and the loading and unloading of the tanker.

The truck loading area might have a tent like enclosure for

weather protection and to retain heat in the winter.



Alpha-0 | 9.57E-01

All Alpha radioactivity was attributed to Pu-239

Beta-0 | 9.36E+01



ABATEMENT CONTROL-Tanker Loading Activities

All work shall be performed in accordance with approved

radiological control methods and ALARA program

requirements. These requirements shall be carried out through

work packages, operating procedures, radiological work

permits, or other work instructions. The general chemical and

physical processes associated with tanker loading activities



DOE/RL-2017-02 Rev. 0

B-349

shall consist of the following.

Appropriate hookups shall be made between the source and

the tanker (e.g., pumps, hoses, etc.). Connections will be

periodically surveyed to verify that no leaks are occurring.

Spill prevention measures shall be in place to mitigate release

of condensate to the atmosphere and/or to the ground during

hookup, transfer, and disconnect operations. These measures

include provisions to catch and retain any inadvertent release

of liquid (e.g. the catch basin and the connection to the tanker)

and the use of dry-break type connections to connect the

transfer line to the truck. The tanker shall be equipped with a

High Efficiency Particulate Filter (HEPA) to allow for venting

while the tanker is being filled. (WAC 246-247-040(5))

ABATEMENT CONTROL-Prior to Transport

After filling the tanker, fittings shall be disconnected and

closed and shall remain closed until commencement of

unloading operations at LERF and or ETF. In the case that the

condensate is taken to a different receiving facility, WDOH

requires notification as to which facility shall receive the

condensate.

All liquid/gas release points where the tanker contents could

escape to the atmosphere shall be closed prior to transport.

The valve under the HEPA filter shall be closed during

transport to ensure that the liquid does not wet the HEPA filter

during transport.

Appropriate decontamination measures shall be performed to

reduce residual external smearable radioactive contamination

to transport release criteria before releasing the tanker for

overland transport. Removable contamination levels on the

truck must be less than or equal to 1,000 dpm/100 cmA2

beta/gamma and less than or equal to 20 dpm/100 cm^2 alpha

prior to transport. Inspections of the tanker vents and valves

shall be performed and documented prior to transport. Waste

liquid shall be characterized (at a minimum of annually), and

acceptability at LERF and or ETF (or receiving facility

specified in the notification to WDOH) shall be

documented.(WAC 246-247-040(5)).



EFFLUENT MONITORING-WDOH documentation:

a) A single WDOH approved record shall be maintained, of

the tanker shipments and an estimate of annual emissions shall

be reported. Records of the operator rounds (which shall serve

as the WDOH approved record) can be used for this

documentation. (WAC 246-247-040(5))

b) Information from shipment records shall be used to estimate

annual emissions. These records shall be retained at the

facility and shall be available for audits. The estimated

emissions shall be determined using one of the following

methods:


loaded, gross alpha and gross beta/gamma activities shall be

determined. The emission shall be determined using the

volume of liquid transferred, an assumed release fraction of

0.00l, the most recent location-specific dose conversion

Continuous


WRPS work documents. WRPS



DOE/RL-2017-02 Rev. 0

B-350

factors of 1.88E-01 mrem/Ci beta/gamma and 4.00E+00

mrem/Ci alpha, assuming gross alpha is Pu-239 and gross

beta/gamma is Sr-90


loaded, a complete isotopic distribution of radionuclides shall

be determined. The emission shall be determined using the

volume of liquid transferred, an assumed release fraction of

0.001, the most recent location-specific dose conversion

factors of 1.88E-0l mrem/Ci beta/gamma and 4.00E+00

mrem/Ci alpha for the known isotopes. (WAC 246-247-

040(5), WAC 246-247-080(7), WAC 246-247-075(3))


The emission unit shall be clearly identified by Emission Unit

ID and AEI ID number (WAC 246-247-040(5))

Continuous CDM: Identification placed on

tanker.

ABATEMENT CONTROL-Fill level limits

The tanker has an 8,000 gallon capacity. The condensate will

be periodically transported when the tanker is filled with

approximately 7,000 gallons. (WAC 246-247-040(5))

Continuous





ABATEMENT CONTROL-Air flow rates

The HEPA filter shall be rated for a flow rate higher than the

maximum flow rate when being filled. (WAC 246-247-

040(5))

Continuous





ABATEMENT CONTROL-Volume documentation

Volume of tanker contents shall be documented each day of

filling operations. (WAC 246-247-040(5))





DOE/RL-2017-02 Rev. 0

B-351


Vents on Single Shell Tanks. (2 sheets)

Emission Unit (EU ID) Emission Unit (EU ID) Emission Unit (EU ID) Emission Unit (EU ID)

P-241A101-001 (92) P-241BY101-001 (283) P-241S110-001 (138) P-241TX105-001 (116

P-241A102-001 (90) P-241BY102-001 (286) P-241S111-001 (202) P-241TX106-001 (126)

P-241A103-001 (87) P-241BY103-001 (288) P-241S304-001 (1227) P-241TX107-001 (114)

P-241A104-001 (88) P-241BY104-001 (289) P-241SX101-001 (1219) P-241TX108-001 (123)

P-241A105-001 (91) P-241BY105-001 (284) P-241SX102-001 (1220) P-241TX109-001 (128)

P-241A106-001 (94) P-241BY106-001 (285) P-241SX103-001 (1221) P-241TX110-001 (121)

P-241AX101-001 (305) P-241BY107-001 (294) P-241SX104-001 (1222) P-241TX111-001 (130)

P-241AX102-001 (303) P-241BY108-001 (291) 1 P-241SX105-001 (1223) P-241TX112-001 (115)

P-241AX103-001 (304) P-241BY109-001 (290) P-241SX106-001 (1224) P-241TX113-001 (117)

P-241AX104-001 (302) P-241BY110-001 (293) P-241SX107-001 (1207) P-241TX114-001 (119)

P-241B101-001 (269) P-241BY111-001 (292) P-241SX108-001 (1208) P-241TX115-001 (125)

P-241B102-001 (270) P-241BY112-001 (287) P-241SX109-001 (1209) P-241TX116-001 (122)

P-241B103-001 (279) P-241C104-001 (716) P-241SX110-001 (1210) P-241TX117-001 (113)

P-241B104-001 (272) P-241C105-001 (717) P-241SX111-001 (1211) P-241TX118-001 (129)

P-241B105-001 (266) P-241C106-001 (712) P-241SX112-001 (1212) P-241TY101-001 (86)

P-241B106-001 (281) P-241C101-001 (247) P-241SX113-001 (201) P-241TY102-001 (82)

P-241B107-001 (275) P-241C102-001 (237) P-241SX114-001 (1213) P-241TY103-001 (85)

P-241B108-001 (268) P-241C103-001 (737) 2 P-241SX115-001 (200) P-241TY104-001 (84)

P-241B109-001 (277) P-241C107-001 (230) P-241T101-001 (79) P-241TY105-001 (83)

P-241B110-001 (278) P-241C108-001 (231) P-241T102-001 (68) P-241TY106-001 (81)

P-241B111-001 (276) P-241C109-001 (245) P-241T103-001 (78) P-241U101-001 (103)

P-241B112-001 (274) P-241C110-001 (244) P-241T104-001 (71) P-241U102-001 (101) 1

P-241B201-001 (267) P-241C111-001 (1) P-241T105-001 (65) P-241U103-001 (97) 1

P-241B202-001 (280) P-241C112-001 (232) P-241T106-001 (66) P-241U104-001 (109)

P-241B203-001 (282) P-241C201-001 (233) P-241T107-001 (69) P-241U105-001 (112) 1

P-241B204-001 (271) P-241C202-001 (246) P-241T108-001 (73) P-241U106-001 (111) 1

P-241BX101-001 (259) P-241C203-001 (242) P-241T109-001 (67) P-241U107-001 (99)

P-241BX102-001 (262) P-241C204-001 (235) P-241T110-001 (76) P-241U108-001 (98) 1

P-241BX103-001 (257) P-241S-001 (203) P-241T111-001 (70) P-241U109-001 (105)

P-241BX104-001 (255) 1 P-241S101-001 (132) P-241T112-001 (72) P-241U110-001 (110)

P-241BX105-001 (273) P-241S102-001 (134) P-241T201-001 (80) P-241U111-001 (107)

P-241BX106-001 (261) P-241S103-001 (133) P-241T202-001 (77) P-241U112-001 (108) 1

P-241BX107-001 (258) P-241S104-001 (131) P-241T203-001 (74) P-241U201-001 (102)

P-241BX108-001 (265) P-241S105-001 (137) P-241T204-001 (75) P-241U202-001 (106)

P-241BX109-001 (263) P-241S106-001 (139) P-241TX101-001 (127) P-241U203-001 (100)

P-241BX110-001 (256) P-241S107-001 (140) P-241TX102-001 (124) P-241U204-001 (104)

P-241BX111-001 (264) P-241S108-001 (135) P-241TX103-001 (120)

P-241BX112-001 (260) P-241S109-001 (136) P-241TX104-001 (118)

DOE/RL-2017-02 Rev. 0

B-352


Vents on Single Shell Tanks.


Status

Compliance Demonstration

Method

Zone or Area :


Required Units : 1


Continuous CDM: Field interviews and WRPS

work documents.

Required Sampling: Smear survey on the inside

surface of the ducting and downstream of the HEPA

filter or on the outside of the screen covering the outlet

of the vent.





10,000 dpm/100 cm2 beta/gamma and 200 dpm/100 cm2

alpha will verify low emissions.


Reports.


61.93(b)(4)(i) & WAC 246-247-075(3)

Permit Monitoring and Testing Procedure: 40 CFR

61, Appendix B Method 114

Continuous


work documents.

Comment: 40 CFR 61, Appendix

B Method 114 does not apply, as

clarified in Attachment 2 Section

4.0, because this EU does not use


Alternate Requirements

1 Alternate Sampling Requirements: An alternate sampling method for breather filters with stack extensions may

be performed by removing the test port cap downstream of the HEPA filter, surveying the cap and inserting smear

media (e.g. swab, masslin) in the opening and smearing the interior ducting surface on the opposite side of the test

port cap opening. Breather filters shall be aerosol tested every 365 days.

2 Alternate Compliance Status: Intermittent

CDM: Radiological Survey Reports, WRPS work documents, WRPS notification procedure and notification

logbook.

Comment: Radial filter was found uninstalled on 12/21/15 and was reinstalled early in CY 2016. Reported per


DOE/RL-2017-02 Rev. 0

B-353

Table 2. Attachment 2 Emission Units That Did Not Operate

During this Certification Period. (2 sheets)

DOH

EU ID Emission Unit

Compliance

Status CDM

57 W-296P043-001 Continuous Field interviews. This emission unit did not


58 W-296P044-001 Continuous Field interviews. This emission unit did not


96 P-204AR-001 Continuous Field interviews. This emission unit did not


163 P-242S-001 Continuous Field interviews. This emission unit did not


175 EP-318-01-S Continuous This emission unit was not utilized during the

reporting period.

308 P-213W-001 Continuous

This emission unit is inactive and will require

an NOC to resume operation or a report of

closure to de-register.

384 P-296A010-001 Continuous This emission unit did not operate during the

reporting period.

395 P-FFTFRESB-001 Continuous This emission unit did not operate during the

reporting period.

396 P-FFTFHTTR-001 Continuous This emission unit did not operate during the

reporting period.

398 Sodium Storage Facility Continuous This emission unit did not operate during the

reporting period.

461 W-PORTEX 011 Continuous This emission unit did not operate during the

reporting period.

749 W-296P048-001 Continuous This emission unit did not operate during the

reporting period.

755 DVS – Active Continuous This emission unit did not operate during the

reporting period.

756 DVS - Passive Continuous This emission unit did not operate during the

reporting period.

878 P-BULKVIT-001 Not

Applicable

Emission unit not constructed and initial

operational startup did not occur during the

reporting period.

885 W-296P049-001 Not

Applicable

Emission unit not installed and initial


reporting period.

886 W-296P050-001 Not

Applicable



reporting period.

1176 FFTF PTRAEUs Continuous The emission unit did not operate during the

reporting period.

1181 Drum Venting System 2 Continuous The emission unit did not operate during the

reporting period.

DOE/RL-2017-02 Rev. 0

B-354

Table 2. Attachment 2 Emission Units That Did Not Operate


DOH

EU ID Emission Unit

Compliance

Status CDM

1183 S-MO444-001 Continuous The emission unit did not operate during the

reporting period.

1249 P-241S102-002 Continuous The emission unit did not operate during the

reporting period.

1250 J-HAMMER-001 Continuous The emission unit did not operate during the

reporting period.

1289 Decon Trailer 200E (Int. Power

Exhaust)

Not

Applicable No requirement specified.

1290 Decon Trailer 200W (Int. Power

Exhaust)

Not

Applicable

No requirement specified.

1291 Decon Trailer 200E (Collection

Tank Vent)

Not

Applicable


1292 Decon Trailer 200W (Collection

Tank Vent)

Not

Applicable


1322 W-PES-001 Continuous The emission unit did not operate during the

reporting period.

1326 Vapor Extraction System Continuous

No activities were conducted requiring the use

of the NOC during the reporting period;

therefore, no emission were generated by the

emission unit.

1327 Next Generation Retrieval

(Active) Continuous

No activities were conducted requiring the use

of the NOC during the reporting period;

therefore, no emission were generated by the

emission unit.

1335 P-296S26-001 Not

Applicable



reporting period.

1342 P-296S27-001 Not

Applicable



reporting period.

1391 W-SXPWET-001 Continuous The emission unit did not operate during the

reporting period.

DOE/RL-2017-02 Rev. 0

B-355

Table 3. Attachment 2 NOC Approvals That Were Not Utilized


NOC ID Page in AOP Approval Number Compliance

Status CDM

665 EU0384-001

AIR 06-1026

Reactivation of PUREX

Storage Tunnel Number 2

Continuous

No activities were conducted requiring

the use of this NOC during the reporting

period.

719 EU0455-004

AIR 11-1006-A

Operation of the

Transuranic Waste

Retrieval Project

Continuous



period.

749 EU1250-001

AIR 09-903

Use of Radioactive

Materials at the

Volpentest

HAMMER/Hanford

Training and Education

Center

Continuous



period.

774 EU0476-001

AIR 10-506

Operation of the Guzzler

in Tank Farm Facilities

Continuous



period.

804

EU 0455-004

AIR 11-1006 – A

Operation of the

Transuranic Waste

Retrieval Project

Continuous



period.

EU0486-001 AIR 11-1006 – B

EU0755-001 AIR 11-1006 – C

EU0756-001 AIR 11-1006 – D

EU1181-001 AIR 11-1006 – E

EU1322-001 AIR 11-1006 – F

EU1326-001 AIR 11-1006 – G

EU1327-001 AIR 11-1006 – H

805 EU0486-009

AIR 11-914

241-SY Tank Farm

Ventilation System

Upgrades Installation and

Pre Operational Permit

for 241-SY/AP/AY/AZ

Tank Farm Exhauster

Upgrade

Not Applicable Installation and initial operational startup

did not occur during the reporting period.

810 EU1183-001

AIR 12-301 – C

Waste Receiving and

Processing Facility

Continuous



period.

811 EU0443-001

AIR 12-302

300 Area Excavation

Activities

Continuous



period.

817 EU1335-001

AIR 11-915 – A

241-SY Tank Farm

Ventilation System

Upgrade Operational



DOE/RL-2017-02 Rev. 0

B-356




Status CDM

Permit for 241-

SY/AP/AY/AZ Tank

Farm Exhauster Upgrade

EU1342-001 AIR 11-915 – B

823 EU0486-021

AIR 11-918

241-AP Tank Farm

Ventilation System

Upgrades Installation and

Pre Operational Permit

for 241-SY/AP/AY/AZ

Tank Farm Exhauster

Upgrade



825 EU0486-021

AIR 12-307 – D

Categorical Tank Farm

Facility Waste Retrieval

and Closure: Phase II

Waste Retrieval

Operations

Continuous



period.

827 EU0227-001

AIR 12-309

Installation and Operation

of a Waste Retrieval

System in Tanks 241-

AN-101,102,103, 104,

105, 106 and 107

Continuous



period.

828 EU0204-001

AIR 12-310


of Waste Retrieval

System in Tanks 241-AP-

102 and 241-AP-104

Continuous



period.

830 EU0447-001

AIR 12-312 – B

Consolidated T Plant

Operations

Continuous



period.

833 EU1176-001

AIR 12-314 – F

Sodium Residual

Reaction/Removal and

other Deactivation Work

Activities at the Fast Flux

Test Reactor

Continuous



period.

838

EU0447-006

AIR 12-317 – A

Roof Replacement

Activities Involving

Radioactive

Contamination at

Facilities on the Central

Plateau

Continuous



period.

EU0455-008 AIR 12-317 – B

EU0476-004 AIR 12-317 – C

DOE/RL-2017-02 Rev. 0

B-357




Status CDM

EU0486-038 AIR 12-317 - D

839 EU0447-008

AIR 12-318 – A


Facility Entry and

Surveillance Continuous



period.

EU0486-040 AIR 12-318 - B

841

EU0447-010

AIR 12-320 – A

Tank Farm Restoration

and Safe Storage Continuous



period. EU0476-006 AIR 12-320 - B

EU0486-042 AIR 12-320 - C

842 EU0398-001

AIR 12-321

Construction and

Operation of Sodium

Storage Facility

Continuous



period.

843 EU0486-045

Air 12-322

Vapor Sampling of

Miscellaneous

Underground Units

Continuous



period.

845 EU0486-048

AIR 12-324

241-AN Tank Farm


of a New Ventilation

System

Continuous



period.

846 EU0486-050

AIR 12-325

241-AW Tank Farm


of a New Ventilation

System

Continuous



period.

848 EU0486-056

AIR 12-327

Operation of the

Integrated Disposal

Facility (IDF)

Continuous



period.

849 EU0486-063

AIR 12-328

Cleaning Radiologically

Contaminated Vehicles

Continuous



period.

850 EU0486-065

AIR 12-329 – B

Removal of Liquid from

Catch Tank 241-ER-311 Continuous



period.

EU0910-001 AIR 12-329 – C

851

EU0486-067

AIR 12-330 – A

Decontamination Trailer

at the Transuranic Waste

Retrieval Project Continuous



period. EU1243-001 AIR 12-330 – B

EU1244-001 AIR 12-330 – C

DOE/RL-2017-02 Rev. 0

B-358




Status CDM

852

EU0476-009

AIR 12-331 – A


Facility Waste Retrieval

and Closure: Phase 1 -

Site Preparation and

system Installation

Continuous



period.

EU486-053

AIR 12-331 – B

Tank Farms - Phase 1-

Waste Retrieval and

Closure

Continuous



period.

853

EU0476-013

AIR 12-332 – A

244-CR Vault Isolation

and Interim Stabilization Continuous



period. EU0486-074 AIR 12-332 – B

EU0498-006 AIR 12-332 – C

EU 0713-001 AIR 12-332 – D

854 EU0486-066

AIR 12-333

Tank Waste Remediation

System Vadose Zone

Characterization

Continuous



period.

856

EU0486-089

AIR 12-335 – A

Tank Farm


East Continuous



period. EU1289-001 AIR 12-335 – B

EU1291-001 AIR 12-335 – C

857 EU1290-001

AIR 12-336 – B

Tank Farm


West Continuous



period.

EU1292-001 AIR 12-336 – C

863 EU0486-075

AIR 12-1001 – A

E-525 Double-Shell Tank

(DST) Transfer System

Modifications Project

Continuous



period.

898 EU0486-078

AIR 13-807

Sidewall Coring of Single

Shell Tanks

Continuous



period.

904 EU1391-001

AIR 13-1001

SX Farm Pore Water

Extraction Test

Continuous



period.

915 EU0486-081

AIR 14-306

Diffuse and Fugitive

Operations at LERF and

ETF

Continuous



period.

DOE/RL-2017-02 Rev. 0

B-359




Status CDM

932 EU0486-086

AIR 14-910

Removal and Disposal of

the Obsolete 242A

Evaporator Building K-1

Exhauster

Continuous



period.

DOE/RL-2017-02 Rev. 0

B-360


DOE/RL-2017-02, Rev. 0

C-i

APPENDIX C



DOE/RL-2017-02, Rev. 0

C-ii


DOE/RL-2017-02, Rev. 0

C-iii

CONTENTS

Asbestos Compliance ...................................................................................................................C-1 Open Burning Compliance ..........................................................................................................C-2

DOE/RL-2017-02, Rev. 0

C-iv


DOE/RL-2017-02, Rev. 0

C-1

Asbestos Compliance

Page in AOP: 3-001

Permit: Asbestos Requirements Issue Date: 01-01-07 Date In AOP: 04-01-13

NOC: General Asbestos Requirement



Condition: The National Emissions Standards for Hazardous

Air Pollutants (NESHAP), 40 Code of Federal Regulations

(CFR) Part 61, Subpart M, "National Emission Standard for

Asbestos," and the Benton Clean Air Authority (BCAA)

Regulation 1, Article 8, "Asbestos" require the Department of

Energy, its contractors, or its subcontractors to file a

notification prior to commencement of a demolition or

renovation activity at an affected facility. Pursuant to the

authorities delegated by the State of Washington, Department

of Ecology (Ecology) and the U.S. Environmental Protection

Agency (EPA), the BCAA is the responsible authority to

conduct day-to-day regulatory responsibility and ensure

compliance with 40 CFR 61 Subpart M and Article 8 of

Regulation 1 of BCAA, adopted by reference in this air

operating permit (AOP), for the Hanford Site. BCAA shall

inform Ecology prior to taking any final permitting or

enforcement actions at Hanford.

Model ID: Not applicable.

EPA Test Method: Not specified.

EPA Test Method Frequency: Not applicable.

Periodic Monitoring: Not Applicable.

Required Records: Not Applicable.

Continuous

CDM: Conducted reasonable inquiry of

personnel engaged in asbestos related work

activities to verify appropriate procedures

implemented and documentation is in place.

DOE/RL-2017-02, Rev. 0

C-2

Open Burning Compliance

Page in AOP: 3-001

Permit: AOP Outdoor Burning Issue Date: 01-01-07 Date In AOP: 04-01-13

NOC: AOP Outdoor Burning Standards



Condition: Chapter 173-425 Washington Administrative

Code (WAC) and BCAA Regulation 1, Article 5, "Outdoor

Burning," require the Department of Energy, its contractors,

or its subcontractors to follow these rules regulating outdoor

burning, including obtaining special outdoor burning permits

if required. The BCAA, pursuant to the authorities delegated

by Ecology, is the responsible authority to ensure compliance

with WAC 173-425 and Article 5 of Regulation 1 of BCAA

adopted by reference in this AOP for the Hanford Site.

Model ID: Not applicable.

EPA Test Method: Not specified.

EPA Test Method Frequency: Not applicable.



Continuous

CDM: Conducted a reasonable inquiry of

individuals charged with approving and

supervising open burning on the Hanford

Site.

DOE/RL-2017-02, Rev. 0

Distr-1

DISTRIBUTION

OFFSITE

U.S. Environmental Protection Agency, Region 10

Air Permits Office

1200 Sixth Avenue

Seattle, WA 98101-3140

D. Dossett

Washington State Department of Health

State of Washington Department of Health

The Division of Environmental Health

The Office of Radiation Protection

Radioactive Air Emissions Section

309 Bradley Blvd, Suite 201

Richland, WA 99352

P. J. Martell

Benton Clean Air Agency

526 S. Steptoe St.

Kennewick, WA 99336

R. Priddy

Confederated Tribes of the Umatilla Indian Reservation

Nixyáawii Governance Center

46411 Timine Way

Pendleton, Oregon 97801

R. Skeen

Nez Perce Tribe

P.O. Box 365

Lapwai, Idaho 83540

G. Bohnee

Yakama Nation

Environmental Restoration/Waste Management Program

P.O. Box 151

Toppenish, WA 98948

R. Jim, Manager

ONSITE All onsite distribution will be made electronically unless otherwise noted.

MSIN

Washington State Department of Ecology

P. M. Gent

DOE/RL-2017-02, Rev. 0

Distr-2

Ecology Library (Hardcopy and CD ROM) H0-57

Washington State Department of Health

J. W. Schmidt

U.S. Department of Energy, Richland Operations Office

E. T. Faust

C. E. Clark

M. K. Marvin

DOE-RL Public Reading Room (CD ROM) H2-53

U.S. Department of Energy, Office of River Protection

D. W. Bowser

B. R. Trimberger

U.S. Department of Energy, Pacific Northwest Site Office

T. M. McDermott

Bechtel National, Inc.

C. Dobie

R. D. Haggard

CH2M HILL Plateau Remediation Company

F. J. Carleo

P. T. Karschnia

J. A. Lerch

Johnson Controls, Inc.

J. G. Burrell

Mission Support Alliance, LLC

D. H. Butler

G. M. Fritz

R. A. Kaldor

^Environmental Portal

MSIN

Pacific Northwest National Laboratory

J. M. Barnett

C. J. Duchsherer

K. M. McDonald

J. P. Rishel

M. J. Stephenson

PNNL Reference Library (CD ROM) P8-55

Washington River Protection Solutions, LLC

M. D. Gerle

B. E. Nichols

further dissemination unlimited approved for public release;...rpp river protection project rtr...

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