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_Ols~~~t~~ ^ORNL/RASA-86/70(LN006V)

OAK RIDGENATIONALLABORATORYLABORATORY RESULTS OF THE

INDEPENDENT RADIOLOGICAL'i * rf-if nVERIFICATION SURVEY

AT121 AVENUE F,

LODI, NEW JERSEY (LN006V)

M. G. YalcintasC. A. Johnson

Access to the information in this report is limited to thoseindicated on the distribution list and to Department of Energy

OPfRATED BY and Department of Energy Contractors

MARTIN MARIETTA ENERGY SYSTEMS, INC.FOR THE UNITED STATESDEPARTMENT OF ENERGY

This report was prepared as an account of work sponsored by an agency of theUnited States Government. Neither the U nited States Government norany agencythereof, nor any of their employees, makes any warranty, express or implied, orassumes any legal liability or responsibility for the accuracy, completeness, orusefulness of any information, apparatus, product, or process disclosed, orrepresents that its use would not infringe privately owned rights. Reference hereinto any specific commercial product, process, or service by trade name, trademark,manufacturer, or otherwise, does not necessarily constitute or imply itsendorsement, recommendation, or favoring by the United States Government orany agency thereof. The views and opinions of authors expressed herein do notnecessarily state or reflect those of the United States Government or any agencythereof.

ORNL/RASA-86/70(LN006V)

HEALTH AND SAFETY RESEARCH DIVISION

Nuclear and Chemical Waste Programs(Activity No. AH 10 05 00 0; ONLWC01)

RESULTS OF THE INDEPENDENTRADIOLOGICAL VERIFICATION SURVEY

AT121 AVENUE F, LODI,

NEW JERSEY (LN006V)

M. G. YalcintasC. A. Johnson*

*Biology Division

Date of Issue - December 1986

Investigation Team

B. A. Berven - RASA Program ManagerW. D. Cottrell - FUSRAP Project DirectorM. G. Yalcintas - Field Survey Supervisor

Work performed as part of theRADIOLOGICAL SURVEY ACTIVITIES PROGRAM

Prepared by theOAK RIDGE NATIONAL LABORATORY

Oak Ridge, Tennessee 37831operated by

MARTIN MARIETTA ENERGY SYSTEMS, INC.for the

U.S. DEPARTMENT OF ENERGYunder Contract No. DE-AC05-840R21400

CONTENTS

Page

LIST O F FIG U R ES ......................................................... v

LIST OF TABLES .......................................................... vii

ACKNOW LEDGM ENTS .................................................... ix

INTRODUCTION .......................................................... 1

PROCEDURES .............................................. .............. 2

O bjectives ................................................... ........... 2Document Reviews ...................................................... 2

VERIFICATION SURVEY AND ANALYSIS ................................. 2

G am m a M easurem ents ................................................... 3Soil Sampling .................... ................... ............. 3

CONCLUSION '............................................................ 3

R E FE R E N C E S ............................................................. 4

iii

LIST OF FIGURES

Figure Page

1 Location of the Maywood site and vicinity properties inin Rochelle Park, Maywood, and Lodi, New Jersey ..................... 5

2 Vicinity properties in the Lodi, New Jersey, area ....................... 6

3 Diagram showing excavated areas on the property at121 Avenue F, Lodi, New Jersey (LN006V)........................... 7

4 Locations of soil samples on the property at 121 Avenue F,Lodi, New Jersey (LN006V) ..................................... 8

v

LIST OF TABLES

Table Page

1 Summary of residual contamination guidelines for the Maywood,New Jersey, site ................................................... 9

2 Background radiation levels in the Maywood, New Jersey, area .......... 11

3 Results of soil sample analysis at 121 Avenue F, Lodi,New Jersey (LN006V) ............................................. 11

vii

ACKNOWLEDGMENTS

Research for this project was sponsored by the Division of Facility and Site Decommis-sioning Projects, U.S. Department of Energy. The authors wish to acknowledge the sup-port of J. E. Baublitz, Deputy Director, Office of Remedial Action and Waste Technology;E. G. DeLaney, Director, Division of Facility and Site Decommissioning Projects; andmembers of their staff. The authors recognize the valuable contributions of C. Leichtweisof Bechtel National, Inc. (BNI), for providing the data collected by BNI during the reme-dial action and T. R. Stewart of the RASA group for preparation of graphics. In addi-tion, the authors appreciate the manuscript preparation by J. M. Wyrick, Biology Division,and S. W. Hawthorne, F. C. Littleton, and B. C. Littleton, Information ResourcesOrganization.

ix

RESULTS OF THEINDEPENDENT RADIOLOGICAL VERIFICATION SURVEY AT

121 AVENUE F, LODI, NEW JERSEY (LN006V)*

INTRODUCTION

Processing of thorium ores was performed in Maywood, New Jersey, between 1916 and1956 by the Maywood Chemical Works. l During the course of thorium processing thewastes from the operations were pumped to diked areas west of the plant. Additionalmaterial was placed in two piles surrounded by earthen dikes. In 1932, Route 17 was builtthrough this disposal area. The Maywood Chemical Works ceased thorium processing in1956 and subsequently was sold to Stepan Chemical Company in 1959. After 1963, onseveral occasions wastes were removed from the west side of New Jersey Route 17. Thisarea is now owned by Ballod and Associates. In 1984, the U.S. Department of Energy(DOE) was assigned the responsibility by Congress for the decontamination project involv-ing the site and vicinity properties in Maywood, Rochelle Park, and Lodi, New Jersey,under the Formerly Utilized Sites Remedial Action Program (FUSRAP).

This site, referred to as the Maywood site, had surface and subsurface radionuclideconcentrations in excess of the DOE criteria listed in Table 1. It has been identifiedthrough radiological assessment procedures by Oak Ridge Associated Universities andNuclear Safety Associates, Inc., 1'2 for the purpose of decontamination based on DOE'sremedial action objectives. The Maywood site and vicinity properties, which include theresidential properties in Lodi, were assigned by DOE to FUSRAP although the contami-nation at the Maywood site did not result from the Atomic Energy Program. A diagram ofthe Maywood site and vicinity properties is shown in Fig. 1.

During 1985, Bechtel National, Inc. (BNI), the project management contractor desig-nated by DOE, performed remedial action on this residential property. This remedialaction is on one of eight designated properties on Trudy Dr., Hancock St., and Avenues Cand F in the Lodi area (Fig. 2). Based on drawings showing the extent of contamination,the property was excavated and the contaminated material transported to the MaywoodInterim Storage Site (MISS), adjacent to the Stepan Company plant3 (see Fig. 1). Afterremoval of all contaminated soil, the property was restored to its original condition. Byusing a combination of procedures, the contamination was controlled and prevented fromspreading to other areas. A post-remedial radiological survey was conducted by BNI toensure compliance with DOE remedial action guidelines. 4

The DOE adopted a policy to assign an independent verification contractor to ensurethe effectiveness of remedial actions performed within FUSRAP. The Radiological SurveyActivities Group of Oak Ridge National Laboratory (ORNL) has been assigned theresponsibility for this task at the Maywood site. This report describes the methods andresults of that verification.

*The survey was performed by members of the Radiological Survey Activities Group of theHealth and Safety Research Division at Oak Ridge National Laboratory under DOE contractDE-AC05-840R21400 with Martin Marietta Energy Systems, Inc.

I

2

From January to June, 1986, ORNL conducted the verification activity for theMaywood vicinity properties, including this location at 121 Avenue F, Lodi, locatedsouthwest of the Maywood site. A diagram of the property showing the approximate prop-erty boundaries and excavated areas is shown in Fig. 3. This location is one in a series ofvicinity properties near the Maywood site that was suspected of being radioactively con-taminated and that has been surveyed by BNI 3 to identify horizontal and vertical bound-aries of radionuclide concentrations exceeding remedial action criteria. (Verification ofthese properties will be completed in 1986.) A contaminated area of -150 m 2 thatexceeded the guidelines was located in the yard around the house, including part of thefront sidewalk, and was excavated.

PROCEDURES

Objectives

The objective of the verification activities was to confirm (1) that available documenta-tion adequately and accurately describes the post-remedial action radiological conditionsof the entire property that is to be certified and (2) that the remedial action reduced con-tamination levels to within authorized limits.

Document Reviews

Review of the designation/characterization report 3 prepared by BNI indicates that thecontaminated areas were shallow deposits of thorium-bearing residues (considered at thetime to be nonhazardous organic mulch) that had been removed from the MaywoodChemical Works site and used as fill around and under the residence. Thus, it wasappropriate to designate this property for remedial action.

The post-remedial action report 4 indicates that the area excavated on this property wasas identified in the designation report. The post-remedial action survey was performed onthis property as described for a generic site in Ref. 5. This survey consists of ground-levelbeta-gamma measurements, surface gamma measurements, and systematic soil sampling.From the review of the post-remedial action report, it can be concluded that the BNI sur-vey procedure used for this property is satisfactory. All reported 238U, 226Ra, and 232Thsoil sample concentrations are below the average guideline limits set by DOE (Table 1).

VERIFICATION SURVEY AND ANALYSIS

Typical background radiation levels for the Maywood, New Jersey, area are presentedin Table 2. The data are provided for purposes of comparison with the survey resultspresented in this section.

All measurements presented in this report are gross readings; background radiation lev-els have not been subtracted. Similarly, background concentrations have not been sub-tracted from radionuclide concentrations in soil samples.

3

Gamma Measurements

Results of gamma measurements made by BNI are presented in the confirmatoryreport (Ref. 4). Gamma scans were conducted using a sodium iodide detector in a walk-over scan of the excavated area, and after all contamination was removed measurementswere made with a lead-shielded detector at 10-ft intervals.4

Four pressurized ionization chamber (PIC) readings were taken at this property byBNI. The results and the locations of these readings are presented in the confirmatoryreport.

Gamma exposure rate measurements were made by ORNL at the ground surfaceand at 1 m above the surface. Gamma exposure rates ranged from 5 to 8 UR/h(microroentgens* per hour) and averaged 7 iR/h both at 1 m and at the surface.

Soil Sampling

Before backfilling, eleven soil samples were taken by BNI in the excavated area. Theprocedures used for soil sample analysis have been described in Ref. 3. Locations of thesoil samples are shown in Fig. 4.

The samples were analyzed by BNI to determine the concentrations of 238U, 226Ra,and 232Th in the soil.4 Concentrations of 238U in the samples ranged from 0.7 to 2.9 pCi/g(picocuriest per gram) and averaged 1.6 pCi/g. Concentrations of 226Ra ranged from 0.6to 1.2 pCi/g and averaged 0.84 pCi/g. Concentrations of 232Th in the soil samples rangedfrom 0.8 to 3.0 pCi/g and averaged 1.7 pCi/g. Results of the soil sample analysis aregiven in Table 3.

CONCLUSION

Measurements of the gamma exposure levels taken from the excavated area beforebackfilling determined that the exposure rate at 1 m above the ground surface rangedfrom 5 to 8 uR/h and averaged 7 iR/h. For comparison, the background for the state ofNew Jersey7- 9 averages -8 iR/h and ranges from 6 to 11 R/h based on 1968 measure-ments. The results of soil radionuclide analyses for 238U, 226Ra, and 232Th show that allsoil concentration measurements are within the limits prescribed by DOE radiologicalguidelines. 10

Based upon the results of the post-remedial action data and confirmed by the verifica-tion survey data, these radiological measurements fall below the limits prescribed by DOEguidelines established for this site. It is concluded that the site successfully meets the DOEremedial action objectives.

*The roentgen (R) is a unit which was defined for radiation protection purposes for peopleexposed to penetrating X rays or gamma radiation. A microroentgen (pR) is one millionth of aroentgen. A milliroentgen (mR) is one thousandth of a roentgen or one thousand microroentgens.

tThe curie is a unit used to define the radioactivity in a substance and equals that quantity ofany radioactive isotope undergoing 2.2 X 1012 disintegrations per minute. The picocurie is onemillion-millionth of a curie or that amount yielding 2.2 disintegrations per minute.

4

REFERENCES

1. L. W. Cole, J. Berger, P. Cotten, R. Gosslee, L. Sowell, and C. Weaver, RadiologicalAssessment of Ballod Associates Property (Stepan Chemical Company), Maywood,New Jersey, Oak Ridge Associated Universities, Oak Ridge, Tenn., July 30, 1981.

2. H. W. Morton, Natural Thorium in Maywood, New Jersey, Nuclear Safety Associ-ates, Inc., Potomac, Md., September 29, 1982.

3. Radiological Survey Report for Maywood Vicinity Properties on Grove Avenue andPark Way, Maywood, New Jersey, Bechtel National, Inc., Advanced TechnologyDivision, Oak Ridge, Tenn., DOE/OR/20722-11, June 1984.

4. Post-Remedial Action Report for Lodi Residential Properties-1985, Lodi, New Jer-sey, Bechtel National, Inc., Advanced Technology Division, Oak Ridge, Tenn.,DOE/OR/20722-89, January 1986.

5. Remedial Action Work Plan for the Maywood Site, U.S. Department of Energy, OakRidge Operations, Oak Ridge, Tenn., ORO-850, Rev. 1, April 1985.

6. T. E. Myrick, B. A. Berven, W. D. Cottrell, W. A. Goldsmith, and F. F. Haywood,Procedures Manual bfr the Remedial Action Survey and Certification Activities(RASCA) Program, Oak Ridge National Laboratory, ORNL/TM-8600, September1982.

7. U.S. Department of Energy, Radiological Survey of the Middlesex Municipal Land-fill, Middlesex, New Jersey, DOE/EV-0005/20, April 1980.

8. S. G. Levin, R. K. Stoms, E. Kuerze, and W. Huskisson, "Summary of NaturalEnvironmental Gamma Radiation Using a Calibrated Portable Scintillation Counter,"Radiological Health Data Report 9:679-695 (1968).

9. C. L. Lindekin, K. R. Peterson, D. E. Jones, and R. E. McMillen, "GeographicalVariations in Environmental Radiation Background in the United States."Proceedings of the Second International Symposium on the Natural RadiationEnvironment, CONF-720805-P-1, pp. 317-331 (1972).

10. U.S. Department of Energy, Guidelines for Residual Radioactivity at Formerly Uti-lized Sites Remedial Action Program and Remote Surplus Facilities ManagementProgram Sites, Rev. 1, July 1985.

5

"\\ - k 7 I< I PASSAIC ST \

8 RESIDENTIAL o\\ '- PROPERTIES \\

MAYWOOD(DAVISON & LATHAM; ;

MAYWOOD INTERIM \\\ ' STORAGE SITE \\

',\\ 'CENTRAL AVE "

\ PROPERT\ ' \

_A ''''."\ ''* STEPAN CO

SEARS AREA I

8 RESIDENCESO\\ S ROCHELLE PARK f AS. \ \\ SCANELR< .>_ e(GROVE & PARK WAY \

· = < i K tODI ESSEX ST.

INTERSTATE 80

BRANCA CT

Fg\\ 1 LONGVALLEtI REDSTONE LA /// LLERD v'

TRUDY DR

,oi \New |ersey.*\ I 1 - AVENUE F /

: \\ l~ =o l//N0 SCALE \\ -1K ---- nJ INDUSTRIAL RD ///

NO SCALE \XI _IL;____ u //\ Ir-1 - - -AVENUE C /

Fig. 1. Location of the Maywood site and vicinity properties in Rochelle Park, Maywood, andLodi, New Jersey.

M ESSEXT.

FEET__________ _ _ __^KTERSTAt E 8O

on : I1

| AVENUE C

g.Vcntprprsn taI500. -

Fig. 2. Vicinity properties in the Lodi, New Jersey, area.

15 4

I X

~~~I !j FEE'Ti ........ 0 5 it- 20E *:".".'.'.'.'.'::.".

~Aio '--- 1 --. '-.:...... :'':":":.:' ' c ' 6, ~ .......... ....

Fig.. . D_............v.. _ '

*-.0 '--.'."'.".':'--. .....-· : 0 . : :. ................... : ...

...... ........ ....r .: ..: .........

:==========:==.::=;L~L ::::::::"::......... ......

I ....... ..·:· '.*... ....

*I. - . I

4VEH!jE F

Fig. 3. Diagram showing excavated areas on the property at 121 Avenue F, Lodi, New Jersey(LN006V).

(LN006V)...-::::.:....:- ".

8

~ Y .

-^ 3

Ii FE~.bFE.T;010 5 1 _

:I @ . - - 1 3 s

4L i I

I .. - - -v-

II -' I

* _ ! _6 lt' d_ .- _ _ _ _,*

I I.

'-, ,*

F 4a .t 1I-3 . 4.I r-.; . f

Fig. 4. Locations of soil samples on the property at 121 Avenue F, Lodi, New Jersey (LN006V).

9

Table 1. Summary of residual contamination guidelinesfor the Maywood, New Jersey, site

Soil (Land) Guidelines (Maximum Limits for Unrestricted Use)

Radionuclide Soil concentration (pCi/g) above backgrounds

226Ra 5 pCi/g, averaged over the first 15 cm of soil below the surface;28Ra 15 pCi/g when averaged over any 15-cm-thick soil layer below

23 Th the surface layer232Th

Other radionuclides Soil guidelines will be calculated on a site-specific basis usingthe DOE manual developed for this use

Structure Guidelines (Maximum Limits for Unrestricted Use)

Indoor Radon Decay Products

For 222Ra and 220Rn concentrations in buildings, the average annual radon decay productconcentration (including background) due to uranium or thorium by-products should notexceed 0.02 WL after remedial action. When remedial action has been performed and itwould be unreasonably difficult and costly to reduce the level below 0.03 WL, the reme-dial action may be terminated, and the reasons for termination should be documented.Remedial action shall be undertaken for any building that exceeds an annual averageradon decay product concentration (including background) of 0.03 WL.

Indoor Gamma Radiation

The indoor gamma radiation after decontamination shall not exceed 20 microroentgen perhour (20 MR/h) above background in any occupied or habitable building.

Indoor/Outdoor Structure Surface Contamination

Allowable Surface Residual Contaminationc(dpm/100 cm2 )

Radionuclided AverageeJ Maximumfn Removable/

Transuranics, 226Ra, 228Ru, 230Th, 228Th, 100 300 202 3 1Pa, 22 7Ac, 125I, 129I

Natural Th, 232Th, Sr, 223Ra, 224Ra, 1,000 3,000 200232U, 1261, 131I, 133I

Natural U, 235U, 238U, and associated 5,000 15,000 1,000decay products

10

Table 1 (continued)

Indoor/Outdoor Structure Surface Contamination

Allowable Surface Residual Contamination'(dpm/100 cm2)

Radionuclided AverageeJ Maximumg Removablef

Beta-gamma emitters (radionuclides 5,000 15,000 1,000with decay modes other than alphaemission or spontaneous fission)except 9Sr and others noted above

aIn the event of occurrence of mixtures of radionuclides, the fraction contributed byeach radionuclide to its limit shall be determined, and the sum of these fractions shall notexceed 1.

bThese guidelines represent unrestricted-use residual concentrations above backgroundaveraged across any 15-cm-thick layer to any depth and over any contiguous 100-m 2 sur-face area.

CAs used in this table, dpm (disintegrations per minute) means the rate of emission byradioactive material as determined by correcting the counts per minute observed by anappropriate detector for background, efficiency, and geometric factors associated with theinstrumentation.

dWhere surface contamination by both alpha- and beta-gamma-emitting radionuclidesexists, the limits established for alpha- and beta-gamma-emitting radionuclides shall applyindependently.

'Measurements of average contaminant should not be averaged over more than 1 m2.For objects of less surface area, the average shall be derived for each such object.

fThe average and maximum radiation levels associated with surface contaminationresulting from beta-gamma emitters should not exceed 0.2 mrad/h at 1 cm and 1.0mrad/h at 1 cm, respectively, measured through not more than 7 mg/cm2 of totalabsorber.

gThe maximum contamination level applies to an area of not more than 100 cm2 .

11

Table 2. Background radiation levels in theMaywood, New Jersey, area

Radiation level orType of radiation measurement radionuclide concentration

or sampleRange Average

Gamma exposure rate at 1 m above 8-11 9floor or ground surface (lR/h) a

Concentration of radionuclidesin soil (pCi/g)b

238U 0.13-1.4 0.86226Ra 0.24-1.4 0.8723 2 Th 0.31-1.5 0.9

'Values obtained from 35 locations in the Rochelle Park area. 8

bSoil samples obtained from locations around the Maywoodarea.6

Table 3. Results of soil sample analysis at 121 Avenue F,Lodi, New Jersey (LN006V)

Radionuclide concentration

Sample' Depth (pCi/g ± 1 sigma)(cm)

226Ra 232Th 238U

01 15-30 0.8 1.3 2.402 15-30 0.6 1.0 1.003 15-30 0.7 1.1 1.1

04 15-30 0.6 0.8 1.405 15-30 0.7 1.3 1.4

06 15-30 1.1 2.5 2.3

07 15-30 1.2 2.7 1.808 15-30 0.8 1.5 0.7

09 15-30 0.6 1.7 1.4

10 15-30 1.1 2.2 1.1

11 15-30 1.1 3.0 2.9

aLocations of soil samples are shown on Fig. 4.

13

ORNL/RASA-86/70(LN006V)

INTERNAL DISTRIBUTION

1. B. A. Berven 7. P. T. Owen2. R. O. Chester 8. T. H. Row3. W. D. Cottrell 9-13. M. G. Yalcintas4. C. A. Johnson 14. IR&A Publications Office5. S. V. Kaye 15. Laboratory Records - RC6. J. L. Marley

EXTERNAL DISTRIBUTION

16-20. S. W. Ahrends, U.S. Department of Energy, Technical Services Division, OakRidge Operations Office, Oak Ridge, TN 37831

21. J. D. Berger, Oak Ridge Associated Universities, P.O. Box 117, Oak Ridge, TN37831

22-24. E. G. DeLaney, U.S. Department of Energy, Director, Division of Facilities andSite Decommissioning Projects, Office of Nuclear Energy, 19901 GermantownRoad, Germantown, MD 20874

25-27. C. E. Miller, U.S. Department of Energy, Director, Surplus Facilities Manage-ment, Richland Operations Office, P.O. Box 550, Richland, WA 99352

28-29. J. F. Nemec, Bechtel National, Inc., 800 Oak Ridge Turnpike, Oak Ridge, TN37831

30. J. W. Wagoner II, U.S. Department of Energy, Division of Facilities and SiteDecommissioning Projects, Office of Nuclear Energy, 19901 Germantown Road,Germantown, MD 20874

31. A. Wallo, Aerospace Corporation, Environmental and Conservation Directorate,955 L'Enfant Plaza, SW, Suite 4000, Washington, DC 20024

32. Office of Assistant Manager, Energy Research and Development, Oak RidgeOperations Office, Oak Ridge, TN 37831

33-34. Office of Scientific and Technical Information, U.S. Department of Energy, OakRidge, TN 37831