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M 366

DEPOSITED

B.C. REG. __________

October 31, 2017

196/2017

APPENDIX

1 Section 8 (a), (b) and (c) of B.C. Reg. 25312016 is repealed and the following substituted:

(a) by repealing subsection (2) and substituting the following:

(2) For the purposes of this Part, a source site is deemed to be a contaminated site if a contaminated soil relocation agreement is required in respect of contaminated soil, as described in section 46.1 (1 ), that is or will be relocated from the source site to a receiving site., and

(b) in subsection (3) by striking out "Despite subsection (2), the" and substituting "The".

2 Sections 46.1 and 46.2 of the Contaminated Sites Regulation, B.C. Reg. 375196, as enacted by section 13 of B. C. Reg. 25312016, are repealed and the following substituted:

Standards for contaminated soil relocation

46.1 (1) The relocation of soil from a source site to a receiving site requires a contami-nated soil relocation agreement if the soil that is or will be relocated is contaminated by having any substance with a concentration that, subject to subsections (2) and (3), exceeds the following numerical standards, prescribed for the purposes of section 55 (3) of the Act, for either soil or vapour:

(a) in respect of the land use of the receiving site, the lowest value of the soil standards set out in Part 1, 2 or 3, as applicable, of Schedule 3.1 of this regulation;

(b) in respect of the land use, or other use, of the receiving site, the lowest value of the vapour standards set out in Schedule 3.3 of this regulation.

(2) As an exception to subsection (1 ), if contaminated soil has any substance with a concentration that exceeds a soil standard protective of groundwater in respect of the: land use of the receiving site set out in Part 1 of Schedule 3.1 of this regulation, the numerical standards for soil protective of groundwater are not to be considered exceeded if either of the following applies:

(a) the site-specific soil standard protective of groundwater, derived in accordance with a director's protocol, is not exceeded;

(b) the water standard for groundwater set out in Schedule 3.2 of this regulation, based on the concentration resulting from a leachate test conducted in accordance with the director's protocol, is not exceeded.

(3) As an exception to subsection (1), numerical standards are not to be considered exceeded for the purposes of that subsection if either of the following applies:

(a) in respect of the numerical standards for soil, the background concentration in the soil of the receiving site, as determined in accordance with the director's protocol, is not exceeded;

(b) in respect of the numerical standards for soil or vapour, a director's interim standard for soil or vapour, as applicable, is satisfied.

page 2 of 137

(4) If the prescribed risk-based standards referred to in subsection (5) are met after the deposit of the relocated contaminated soil, the quality of the soil at the receiving site is suitable for the use intended.

(5) In respect of a background risk estimate, or a background risk-based concentration, for a receiving site, the risk-based standards prescribed for the purposes of section 55 (3) (a) of the Act are those set out in

(a) section 18 of this regulation, or

(b) section 18. l of this regulation, if the receiving site is a wide area receiving site.

Procedures for contaminated soil relocation

46.2 For the purposes of section 55 (3) of the Act, the following procedures, if required by the director, are prescribed in respect of the relocation of soil under a contaminated soil relocation agreement:

(a) testing, in accordance with a director's protocol, the leachate from the soil to be relocated to determine whether the leachate from the soil contains a substance with a concentration that exceeds

(i) the water quality standards applicable to the receiving site set out in Schedule 3.2 of this regulation,

(ii) the site-specific numerical water standard of the receiving site, or

(iii) a risk-based concentration for water at the receiving site;

(b) if risk-based standards are applied at the receiving site, the following procedures:

(i.) monitoring impacts of the substances in the relocated soil;

(ii) inspecting and maintaining works considered necessary to manage contamination at the receiving site and to protect human health or the environment;

(iii) site registry notations;

(iv) preparation and registration of a covenant under section 219 of the Land Title Act.

3 Schedules 2.1, 3.1, 3.2, 3.3 and 3.4 of the Contaminated Sites Regulation, as enacted by section 18 of B.C. Reg. 25312016, are repealed and the attached Schedules 2.1, 3.1, 3.2, 3.3 and 3.4 substituted.

page 3 of 137

Item

1

2

3

4

5

6

7

8

9

10

11

12

SCHEDULE 2.1 PROTECTED AREAS

Column 1 Column 2 Area Act

a national marine conservation area Canada National Marine Conservation Areas reserve Act

a national park or a national park Canada National Parks Act reserve

a public :land required for wildlife Canada Wildlife Act research, conservation or interpretation

a management area Creston Valley Wildlife Act

an ecological reserve Ecological Reserve Act

an area that is subject to an order the Environment and Land Use Act Lieutenant Governor in Council considern necessary or advisable in respect of the environment or land use for the preservation or maintenance of the natural environment

the Flathead watershed area Flathead Watershed Area Conservation Act

(a) an ungulate winter range or Forest and Range Practices Act a wildlife habitat area in respect of which there is to be no timber harvesting, but not in respect of which there may be conditional timber harvesting, or

(b) a fisheries sensitive watershed area

an old growth zone Forest Practices Code of British Columbia Act

an area that is subject to an order by the Land Act minister responsible for administering the Land Act, which order establishes objectives in respect of old growth management

a migratory bird sanctuary Migratory Birds Convention Act, 1994 (Canada)

the Muskwa-Kechika Management Muskwa-Kechika Management Area Act Area

page 4 of 137

Item

13 (<

(t

(<

14 (<

(t

(<

15 (<

(t

(<

16 an area ic respect o approach but not b

17 a wildlif(

18 an area d managen bear habi watershe

c olumn 1 Area

ngulate winter range or Oldlife habitat area in

L) an u a WJ

resp be n

but ther timt

ect of which there is to o timber harvesting, not in respect of which e may be conditional >er harvesting,

heries sensitive >) a fi s wat ershed area, or

~ ) an o Id-growth management area

nservancy,

rk, or

L) a co

>) a pa

~) a de signated wildland area witt iin a recreation area

cological reserve

rk, or

nservancy

d as a critical habitat in

L) an e

>) a pa

~) a co

lentifie f whicl 1 the critical habitat is bas<:

ased 01

~don a site or area level, 1 a landscape level

gement area

ted as a special forest

~ mana

esigna 1ent an tat or<

~a in respect of a grizzly L fisheries sensitive

d

Column 2 Act

Oil and Gas Activities Act

Park Act

Protected Areas of British Columbia Act

Species at Risk Act (Canada)

Wildlife Act

Great Bear Rainforest (Forest Management) Act

page 5 of 137

'O

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0\ 0 ......,

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-..l

COLUMN 1

Site-specific Factor

HUMAN HEALTH PROTECTION Intake of contaminated soil

Groundwater used for drinking water

ENVIRONMENT AL PROTECTION Toxicity to soil invertebrates and plants

Livestock ingesting soi l and fodder

Major microbial functional impairment

Groundwater flow to surface water used by aquatic life

Groundwater used for livestock watering

Groundwater used for irrigation

Notes

SCHEDULE 3.1- PART 1

MATRIX I -NUMERICAL SOIL STANDARDS1

ANTHRACENE (CHEMICAL ABSTRACT SERVICE NUMBER 120-12-7)

COLUMN COLUMN COLUMN COLUMN COLUMN COLUMN 2 3 4 5 6 7

Wild lands Wild lands Residential Residential Natural Reverted Agricultural Urban Park Low Density High Density (Wt_,.) (Wt_,.) (AL) (PL) (RLLD) (Rl,.o)

25 000 25 000 10000 25 000 IO 000 25 000

NS NS NS NS NS NS

1.5 2.5 2.5 2.5 2.5 30

NS

NS

NS NS NS NS NS NS

NS

NS

COLUMN COLUMN 8 9

Commercial Industrial (CL) (IL)

75 000 > I 000 mg/g

NS NS

30 30

NS NS

1. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from time to time, a director's protocol or alternate methods acceptable to a director.

2. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. NS - no standard. Soil to groundwater transport model predicts applicable water use standard for the substance will not be exceeded at the point of receptor exposure.

Note

2

3

4

5

6

6

4

6

6

'O ~

OQ ~

-.J

0 ......,

VJ -.J

5. AL, PL CL and IL standards are set equal to the corresponding 2010 Canadian Council of Ministers or the Environment (CCME) soil quality criteria. WLN standard is derived by dividing the

2010 CCME parkland soil quality criterion by the Protocol 28, "2016 Standards Derivation Methods", Wildlands divisor. WLR standard is set equal to the 2010 CCME parkland soil quality

criterion. RLw standard is set equal to the 20 l 0 CCME residential soil quality criterion. RLtto standard is set equal to the 20 I 0 CCME commercial soil quality criterion. 6. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard or no appropriate standard, guideline or criterion exists to develop a soil quality standard.

"O P>

(Jq ~

00

0 ....., ....... VJ -....J

MATRIX 2- NUMERICAL SOIL STANDARDS1

ARSENIC (CHEMICAL ABSTRACT SERVICE NUMBER 7440-38-2)

j COL1UMN ___ - , COL.,UMN , -C-OL~MN-j----COL,,UMN i--COL!'MN j COL~MN j COL;'MN j COL~MN j COL~MN j Note j

- - ~ - - - -Wildlands Wild lands Residential Residential

Site-specific Factor Natural Reverted Agricultural Urban Park Low Density High Density Commercial Industrial /WI\ {WL,.) (AL) CPU (RLLD) (RLHJ (CL) (IL) \••-N/

HUMAN HEAL TH PROTECTION Intake of contaminated soil 40 40 20 40 20 40 I50 400

Groundwater used for drinking water IO IO IO IO IO IO IO IO

ENVIRONMENT AL PROTECTION Toxicity to soil invertebrates and I5 25 25 25 25 40 40 40 plants

Livestock ingesting soil and fodder 25

Major microbial functional impairment NS


Freshwater 10 10 10 IO 10 10 IO 10

Marine 10 10 IO IO IO IO IO IO

Groundwater used for livestock 10 watering

Groundwater used for irrigation 10 IO IO IO

Notes I . All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 20I5 British Columbia Environmental Laboratory Manual, as updated

from time to time, a director's protocol or alternate methods acceptable to a director. 2. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential

land use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children ' s playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. Standards have been adjusted using the 2012 US EPA OSWER Directive 9200.1-113 default Relative Bioavailability Factor (0.6) for arsenic in soil.

2

3,4

5

6

5

5

5

"O p)

Qq (1>

"' 0 ........

I.;.)

-.l

5. Standards have been adjusted based on 2016 reference Provincial background soil concentration for the substance. 6. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard or no appropriate standard, guideline or criterion exists to develop a soil quality standard.

"O ~

(IQ (1)

0 0 ......,

UJ -..)

MATRIX 3- NUMERICAL SOIL STANDARDS' BARIUM (CHEMICAL ABSTRACT SERVICE NUMBER 7440-39-3)

I COLUMN I COL2UMN COLUMN COLUMN COLUMN COLUMN COLUMN I COLUMN I COLUMN I Note I ~ 3 4 5 6 ? 8 g

Wildlands Wild lands Residential Residential Site-specific Factor Natural Reverted Agricultural Urban Park Low Density High Density Commercial Industrial 2

(WL,.} (WLR) (AL) (PL) {RL._o) {Rl,.o) (CL) (IL)

HUMAN HEAL TH PROTECTION Intake of contaminated soil 15 000 15 000 8 500 15 000 8 500 15 000 50 000 >I 000 mg/g 3

Groundwater used for drinking water 350 350 350 350 350 350 350 350

ENVIRONMENT AL PROTECTION Toxicity to soil invertebrates and 350 700 700 700 700 I 500 I 500 1 500 plants


Major microbial functional impairment NS 4


Freshwater 3 500 3 500 3 500 3 500 3 500 3 500 3 500 3 500

Marine I 500 1 500 l 500 I 500 I 500 1500 I 500 1 500

Groundwater used for livestock NS 4 watering

Groundwater used for irrigation NS NS NS NS 4

Notes 1. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from time

to time, a director's protocol or alternate methods acceptable to a director. 2. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land

use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children 's playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard or no appropriate standard, guideline or criterion exists to develop a soil quality standard.

"Cl I":>

(JC/ ("!)

0 ...., \,;..) -...J

COLUMN I 1


HUMAN HEAL TH PROTECTION Intake of contaminated soil


ENVIRONMENTAL PROTECTION Toxicity to soil invertebrates and plants

Livestock ingesting soil and fodder



Freshwater

Marine



Notes

MATRIX 4- NUMERICAL SOIL STANDARDS' BENZENE (CHEMICAL ABSTRACT SERVICE NUMBER 71-43-2)

COLUMN I COLUMN I COLUMN I COLUMN I COLUMN COLUMN 2 3 4 5 6 7

Wildlands Wildlands Residential Residential Natural Reverted Agricultural Urban Park Low Density High Density

(WLN) (WL,,) (AL) (PL) (RLLD) (RLHD)

350 350 150 350 150 350

O.o35 0.035 O.o35 0.035 0.035 0.035

35 100 100 100 100 250

NS

NS

2.5 2.5 2.5 2.5 2.5 2.5

6.5 6.5 6.5 6.5 6.5 6.5

NS

NS NS NS NS

I COLUMN I COLUMN I Note I 8 9

Commercial Industrial 2 (CL) (IL)

1000 6 500 3

O.o35 O.o35

250 250

4

4

2.5 2.5

6.5 6.5

4

4



3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard or no appropriate standards, guideline or criterion exists to develop a soil quality standard.

"O s::.:>

O'Q (n

N 0 ....., (.;.) -....)

COLUMN 1










Notes


BENZO(A)PYRENE (CHEMICAL ABSTRACT SERVICE NUMBER 50-32-8)


Wild lands Wildlands Residential Residential Natural Reverted Agricultural Urban Park Low Density High Density (WLN) (WL,.) (AL) (PL) (RlLD) (RLHJ

10 10 5 10 5 10

NS NS NS NS NS NS

15 20 20 20 20 70

NS

NS

NS NS NS NS NS NS

NS

NS NS NS NS

COLUMN COLUMN 8 9

Commercial Industrial (Cl) (IL)

30 50

NS NS

70 70

NS NS

I. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from time to time, a director's protocol or alternate methods acceptable to a director.


3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. NS - no standard. Soil to groundwater transport model predicts applicable water use standard for the substance will not be exceeded at the point of receptor exposure.

Note

2

3

4

5

6

6

4

6

6

5. AL, PL CL and IL standards are set equal to the corresponding 2010 Canadian Council of Ministers or the Environment (CCME) soil quality criteria. WLN standard is derived by dividing the


criterion. RLw standard is set equal to the 2010 CCME residential soil quality criterion. RLtto standard is set equal to the 2010 CCME commercial soil quality criterion. 6. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard or no appropriate standard, guideline or criterion exists to develop a soil quality standard.

'O p.,

()'q (1>

........ VJ

0 ......, ........ VJ -..J

COLUMN 1



Groundwater used for drinking water pH< 5.5 pH 5.5 - < 6.0 pH 6.0- < 6.5 pH 6.5 - < 7.0 pH7.0-<7.5 pH 7.5 - < 8.0 pH~ 8.0





Freshwater pH< 6.5 pH 6.5 -< 7.0 pH 7.0-< 7.5 pH 7.5 - < 8.0 pH~ 8.0

Marine pH< 5.0 pH 5.0-< 5.5 pH 5.5 -< 6.0 oH 6.0-< 6.5

MA TRIX 6 - NUMERICAL SOIL STANDARDS1

BERYLLIUM (CHEMICAL ABSTRACT SERVICE NUMBER 7440-41-7)


Wild lands Wildlands Residential Residential Natural Reverted Agricultural Urban Park Low Density High Density

(WLJ (WL~) (AL) (PL) (R~) (RLMo)

150 150 85 150 85 150

1 l l l l l l.5 1.5 1.5 1.5 1.5 1.5 4 4 4 4 4 4 20 20 20 20 20 20 150 150 150 150 150 150

l 000 1000 l 000 1 000 1 000 I 000 2 500 2 500 2 500 2 500 2 500 2 500

75 150 150 150 150 350

NS

NS

l 1 l 1 1 l 4 4 4 4 4 4 30 30 30 30 30 30

250 250 250 250 250 250 500 500 500 500 500 500

85 85 85 85 85 85 100 100 100 100 100 100 200 200 200 200 200 200 550 550 550 550 550 550

COLUMN COLUMN Note 8 9


500 15 000 3

l l 4,5 1.5 1.5 4 4 4 4 20 20 4 150 150 4

1 000 1 000 4 2 500 2 500 4

350 350

6

6

1 1 4,5 4 4 4 30 30 4

250 250 4 500 500 4

85 85 4 100 100 4 200 200 4 550 550 4

"d ~

(JQ ~

~

0 ......,

VJ -....J

COLUMN COLUMN COLUMN COLUMN COLUMN COLUMN COLUMN COLUMN COLUMN 1 2 3 4 5 6 7 8 9

Wild lands Wild lands Residential Residential Site-soecific Factor Natural Reverted Agricultural Urban Park Low Density High Density Commercial Industrial

(WLN) (WLR) (AL) (PL) (RLLO) (RLHD) (CL) (IL)

pH 6.5 - < 7.0 2 500 2 500 2 500 2 500 2 500 2 500 2500 2 500 pH 7.0- < 7.5 20 000 20 000 20 000 20 000 20 000 20 000 20 000 20000 pH 7.5 - < 8.0 L50 000 150000 150 000 150 000 150 000 L50 000 L50 000 L50 000 pH::>:8.0 350 000 350 000 350 000 350 000 350 000 350 000 350 000 350 000


pH< 5.0 8.5 pH 5.0- < 5.5 10 pH 5.5 - < 6.0 20 pH 6.0- < 6.5 55 pH 6.5 - < 7.0 250 pH 7.0- < 7.5 2 000 pH 7.5- < 8.0 15 000 pH::>:8.0 35 000

Groundwater used for irrigation pH < 5.0 8.5 8.5 8.5 8.5 pH 5.0- < 5.5 LO LO 10 10 pH 5.5 - < 6.0 20 20 20 20 pH 6.0- < 6.5 55 55 55 55 pH 6.5 - < 7.0 250 250 250 250 pH 7.0- < 7.5 2 000 2000 2 000 2000 pH 7.5 - < 8.0 15 000 15 000 15 000 15 000 pH::>: 8.0 35 000 35 000 35 000 35 000

Notes 1. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual , as updated from

time to time, a director's protocol, or alternate methods acceptable to a director. 2. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land

use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. The pH is the pH of the soil at a site. 5. Standards have been adjusted based on 2016 reference Provincial background soil concentration for the substance. 6. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard or no appropriate standard, guideline or criterion exists to develop a soil quality standard.

Note

2

4 4 4 4

4 4 4 4 4 4 4 4

4 4 4 4 4 4 4 4

"O

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VI

0 ......,

\.;.) -.l

COLUMN 1



Groundwater used for drinking water pH < 7.0 pH 7.0- < 7.S pH 7.5 - < 8.0 pH2:8 .0




Groundwater flow to surface water used by aquatic Ii fe

Freshwater pH < 7.0 pH 7.0- < 7.S pH 7.5 - < 8.0 pH 2:8.0

Marine pH < S.5 pH S.S - < 6.0 pH 6.0- < 6.S pH 6.5 - < 7.0 pH 7.0- < 7.5 pH 7.S - < 8.0 pH 2: 8.0

Groundwater used for livestock

MATRIX 7 - NUMERICAL SOIL ST ANDARDS1

CADMIUM (CHEMICAL ABSTRACT SERVICE NUMBER 7440-43-9)


Wild lands Wild lands Residential Residential Natural Reverted Agricultural Urban Park Low Density High Density

(WLN) (Wl;;) (AL) (PL) (RL,_,) (RLHD)

40 40 20 40 20 40

1 1 1 I 1 1 4.S 4.S 4.S 4 .S 4 .S 4.5 30 30 30 30 30 30 70 70 70 70 70 70

JS 30 30 30 30 7S

JO

55

1 1 1 I 1 1 3 3 3 3 3 3

20 20 20 20 20 20 so so so 50 50 50

I 1 1 1 1 1 1.5 l.S l.5 l.S 1.5 1.5 2 2 2 2 2 2

3.5 3.5 3.S 3.5 3.S 3.S 15 15 15 IS lS 15 9S 9S 9S 9S 9S 95 200 200 200 200 200 200



150 3 500 3

I 1 4,5 4 .S 4.5 4 30 30 4 70 70 4

75 75

6

1 1 4,5,7 3 3 4,7

20 20 4,7 so so 4,7

1 1 4,5 1.5 1.5 4 2 2 4

3.S 3.5 4 15 IS 4 9S 9S 4 200 200 4

"O

~ (1l -0\ 0 ...,., (.;.) -..J


Wild lands Wild lands Residential Residential Site-specific Factor Natural Reverted Agricultural Urban Park Low Density High Density Commercial Industrial

(WL.) (WLR) (AL) (PL) (RLLD) (Rl,.o) (CL) (IL)

watering pH< 5.0 4.5 pH 5.0-< 5.5 6 pH 5.5 -< 6.0 8.5 pH 6.0 - < 6.5 10 pH 6.5 - < 7.0 20 pH7.0-<7.5 75 pH 7.5 -< 8.0 500 pH ~8.0 l 000

Groundwater used for irrigation pH< 7.0 I l l I pH 7.0-< 7.5 4.5 4 .5 4.5 4.5 pH 7.5- < 8.0 30 30 30 30 pH~ 8.0 70 70 70 70

Notes 1. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from

time to time, a director's protocol, or alternate methods acceptable to a director. 2. The site-specific factors of human intake of contaminated soil and toxicity to soi l invertebrates and plants specified in this matrix apply at all sites. The high density residential land


3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. The pH is the pH of the soil at a site. 5. Standards have been adjusted based on the 2016 reference Provincial background soil concentration for the substance. 6. Standard is set equal to 1999 Canadian Council of Ministers of the Environment, "Nutrient and energy cycling check value". 7. Standard varies with receiving water hardness (H). H = 150 to < 210 mg/L as CaC03 is assumed. Consult director for further advice.

Note

2

4 4 4 4 4 4 4 4

4,5 4 4 4

"O ~

(IQ ~

-J

s, VJ -J

COLUMN 1

I Site-specific Factor









Notes


CHLORIDE ION (CHEMICAL ABSTRACT SERVICE NUMBER 16887-00-6)

COLUMN COLUMN COLUMN COLUMN COLUMN COLUMN COLUMN 2 3 4 5 6 7 8

Wildlands Wild lands

I ... .,.,i;,1 I R~Jd.,U•I I

Natural Reverted Agricultural Urban Park Low Density High Density Commercial (WLN) (WLR) (AL) (PL) (Rt.,,) (RL"0 ) (CL)

> l 000 mg/g > l OOOmg/g >I 000 mg/g > l 000 mg/g > l OOOmg/g > l 000 mg/g > 1 000 mg/g

100 100 100 100 100 100 100

200 350 350 350 350 2 500 2 500

NS

NS

600 600 600 600 600 600 600

250

40 40 40

COLUMN 9

Industrial (IL)

> l 000 mg/g

100

2 500

600

!. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from time to time, a director' s protocol or alternate methods acceptable to a director.

I

2. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, sports field , picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. Standard varies with Kd for chloride ion in the soil of a site. Standard is appropriate to a chloride:soi l Kd range of 0 to 0.1 mL/g. Consult a director for further advice. 5. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard or no appropriate standard, guideline or criterion exists to develop a soil quality standard. 6. Standard to protect freshwater aquatic life.

Note

2

I 3

4

5

5

4,6

4

4

"O ~

{JQ ~

00

0 .......,

V.l -..J

I

COLUMN 1


I HUMAN HEALTH PROTECTION Intake of contaminated soil

Groundwater used for drinking water ENVIRONMENT AL PROTECTION Toxicity to soil invertebrates and plants




Freshwater

Marine



MATRIX 9- NUMERICAL SOIL STANDARDS1'2

CHROMIUM (CHEMICAL ABSTRACT SERVICE NUMBER 7440-47-3) COLUMN COLUMN COLUMN COLUMN COLUMN COLUMN

2 3 4 5 6 7

Wild lands

I Wildlands

I I Residential 1-;d~U•I I Natural Reverted Agricultural Urban Park Low Density High Density

(WL..) (WLR) (AL) (PL) (R'-co) (RLHO)

250 250 100 250 100 250

60 60 60 60 60 60 > 1 000 mg/g > I 000 mg/g > 1 000 mg/g > I 000 mg/g > 1 000 mg/g > 1 000 mg/g

100 200 200 200 200 250

150 60

60

60 60 60 60 60 60 300 000 300 000 300 000 300 000 300 000 300 000

60 60 60 60 60 60 > 1 000 mg/g > 1 000 mg/g > 1 OOOmg/g > 1 000 mg/g > 1 OOOmg/g > 1 000 mg/g

60 150 000

60 60 60 60 15 000 15 000 15 000 15 000


I I I Commercial Industrial 3

(CL) (IL)

750 20000 4,5

60 60 6,7 > I 000 mg/g > 1 000 mg/g 8

250 250 5

6 7,8

7,9

60 60 6,7 300 000 300 000 8

60 60 6,7 > 1 000 mg/g > 1 000 mg/g 8

6,7 8

6,7 8

'O

~ ('1>

\0 0 ....., \.>.) -..)

Notes I. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from time

to time, a director's protocol, or alternate methods acceptable to a director. 2. Analytical results fo r chromium (all species) in soil may be used to demonstrate compliance with the standards of this matrix. Where the standards cannot be met based on analytical

resuits for chromium (ali species), determination of chromium, trivaient and chromium, hexavaiem concentrations in soii may be necessary. 3. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land use

standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

4. Intake pathway of exposure modelled is inadvertent ingestion of soil. 5. Standard is based on chromium (all species). 6. Standard is for chromium, hexavalent. 7. Standard has been adjusted based on 2016 reference Provincial background soil concentration for the substance. 8. Standard is for chromium, trivalent. 9. Standard is set equal to 1999 Canadian Council of Ministers of the Environment, "Nutrient and energy cycling check value".

"O

~ (n

N 0 0 .....,

VJ -....]

MATRIX 10 - NUMERICAL SOIL STANDARDS1

COBALT (CHEMICAL ABSTRACT SERVICE NUMBER 7440-48-4)

COLUMN 1

COLUMN I COLUMN I COLUMN I COLUMN I COLUMN I COLUMN 2 3 4 5 6 7

COLUMN 8

COLUMN I Note 9

Site-specific Factor Wild lands

Natural

(WLN)

Wildlands Reverted

(WL,.)

Agricultural (Al)

Urban Park (PL)

Residential Low Density

(Rlu,)

Residential High Density

(Rl,.o)

Commercial (CL)

Industrial I 2 I (IL)

HUMAN HEALTH PROTECTION Intake of contaminated soi l 25 25 25 25 25 25 75 2 000


ENVIRONMENT AL PROTECTION Toxicity to so il invertebrates and 25 45 45 45 45 200 200 200 plants



Groundwater flow to surface water 25 25 25 25 25 25 25 25 used by aquatic life


Groundwater used for irrigation 25 25 25 25

Notes I . All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from

time to time, a director's protocol, or alternate methods acceptable to a director. 2. The site-specific factors of human intake of contaminated soi l and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land


3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. Some standards have been adjusted based on 2016 reference Provincial background soi l concentration for the substance. 5. Standards have been adjusted based on 2016 reference provincial background soil concentration for the substance. 6. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to use to develop a soil quality standard.

3,4

5

6

5

5

"O

~ (1)

N

0 ......, -V.l -..J

I

COLUMN 1


I HUMAN HEAL TH PROTECTION Intake of contaminated soil

Groundwater used for drinking water pH < 5.0 pH 5.0 - < 5.5 pH 5.5 - < 6.0 pH 6.0 - < 6.5 pH 6.5 -< 7.0 pH2:7.0





Freshwater pH < 5.5 pH 5.5 - < 6.0 pH 6.0- < 6.5 pH 6.5 - < 7.0 pH 7.0 - < 7.5 pH 2:7.5

Marine pH < 6.0 pH 6.0- < 6.5 pH 6.5 - < 7.0 pH 2: 7.0


COPPER (CHEMICAL ABSTRACT SERVICE NUMBER 7440-50-8)


COLUMN 8

I I

!

Wild lands Wild lands ........... I ... ; ... ,,.;., I I Natural Reverted Agricultural Urban Park Low Density High Density Commercial

(WL.) (WLR) (AL) (PL) (Rt.,,) (Rl,..,) (CL)

7 500 7 500 3 500 7 500 3 500 7 500 25 000

250 250 250 250 250 250 250 500 500 500 500 500 500 500

2 000 2 000 2 000 2 000 2000 2 000 2 000 10 000 10 000 10 000 10 000 10000 10 000 10000 50000 50 000 50 000 50 000 50 000 50 000 50000 100 000 100 000 100000 100 000 100 000 100 000 JOO 000

85 150 150 150 150 300 300

150

350

75 75 75 75 75 75 75 100 100 100 100 100 100 100 700 700 700 700 700 700 700

3 000 3 000 3 000 3 000 3 000 3 000 3 000 6 500 6 500 6 500 6 500 6 500 6 500 6 500 7 500 7 500 7 500 7 500 7 500 7 500 7 500

75 75 75 75 75 75 75 150 150 150 150 150 150 150 650 650 650 650 650 650 650

1 500 1 500 1 500 I 500 I 500 1 500 1 500

COLUMN Note 9

!

I ,,." .. ;,, I 2

(IL)

700000 3

250 4 500 4

2 000 4 10000 4 50 000 4 100 000 4

300

5

75 4,6,7 100 4,7 700 4,7

3 000 4,7 6 500 4,7 7 500 4,7

75 4,6 150 4 650 4

I 500 4

"O ~

(Jt1 ~

N N 0 .......,

\.>.)

-..I


Wildlands Wild lands Residential Residential Site-specific Factor Natural Reverted Agricultural Urban Park Low Density High Density Commercial Industrial

(WLN) (WLR) iALj (PLi (RLLD) (RLHo) (CL) \ .... ,


pH < 5.0 75 pH 5.0 - < 5.5 100 pH 5.5 - < 6.0 400 pH 6.0 - < 6.5 2 500 pH 6.5-< 7.0 10 000 pH 7.0- < 7.5 20 000 pH 2: 7.5 25 000

Groundwater used for irrigation pH < 5.5 75 75 75 75 pH 5.5 - < 6.0 300 300 300 300 pH 6.0- < 6.5 I 500 I 500 1500 1 500 pH 6.5 - < 7.0 6500 6 500 6500 6 500 pH 2:7.0 15 000 15 000 15 000 15 000


time to time, a director's protocol or alternate methods acceptable to a director. 2. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land

use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children ' s playground, sports field , picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. The pH is the pH of the soi l at a site. 5. Standard is set equal to 1999 Canadian Council of Ministers of the Environment, "Nutrient and energy cycl ing check value". 6. Standards have been adjusted based on 2016 reference Provincial background soi l concentration for the substance. 7. Standard varies with receiving water hardness (H). H ~ 200 mg/Las CaC03 is assumed. Consult a director for further advice.

Note

2

4,6 4 4 4 4 4 4

4,6 4 4 4 4

'O p.:>

(JO ~

N w 0 ......,

w -....]

COLUMN COLUMN 1 2

MATRIX 12- NUMERICAL SOIL STANDARDS1,i

CYANIDE (CHEMICAL ABSTRACT SERVICE NUMBER 57-12-5)

COLUMN COLUMN COLUMN COLUMN 3 4 5 6

COLUMN COLUMN 7 8

! I I ! I

COLUMN 9

I

I I Wildlands Wildlands I R~;,_,, I ~.;~m;,, I I

Site-specific Factor Natural Reverted .•. ;, .... ". I Urban Park Low Density High Density Commercial .. , ..... ; .. I (Wl,.) (WLR) (AL) (PL) (RLLD) (RLH

0) (CL) (IL)

HUMAN HEAL TH PROTECTION Intake of contaminated soil 50 50 25 50 25 50 I50 4000

Groundwater used for drinking water 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5

ENVIRONMENT AL PROTECTION Toxicity to soil invertebrates and 2 3 3 3 3 10 IO 10 plants

Livestock ingesting soil and fodder II



Freshwater 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5

Marine 0.35 0.35 0.35 0.35 0.35 0.35 0.35 0.35

Groundwater used for livestock NS watering

Groundwater used for irrigation NS NS NS NS

Notes I. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 20I 5 British Columbia Environmental Laboratory Manual, as updated from

time to time, a director's protocol or alternate methods acceptable to a director. 2. Standards are for the sum of DDT (2,4' = 4,4' isomers) and DDE (2,4' = 4,4' isomers). 3. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land


4. Intake pathway of exposure modelled is inadvertent ingestion of soil.

Note

I

3

I 4

5

6

6

6

'O

~ (t>

~ 0 .......,

(.;.) -....)

5. Standard is set equal to the 1997 CCME agricultural soil & food ingestion criterion. 6. NS - No standard. Insufficient acceptable scientific data exists to calculate a standard or no appropriate standard, guideline or criterion exists to develop a soil quality standard.

'O !:>)

(1q en tv VI

0 .......,

w -.J

MATRIX 13- NUMERICAL SOIL STANDARDS1,2

DICHLORODIPHENYLTRICHLOROETHANE, TOT AL [DDT) (CHEMICAL ABSTRACT SERVICE NUMBER not applicable)

j CO\UMN ! COL'lUMN I COL~MN I COL.lUMN ! CO~UMN ! COL~UMN COL~MN I COL~MN I COL0UMN I Note I

~ - ~ - - - -Wild lands Wildlands Residential Residential

Site-specific Factor Natural Reverted Agricultural Urban Park Low Density High Density Commercial Industrial (WL,.) (WLR) (AL) (PL) (Rlu) (RLHO) (CL) (IL)

HUMAN HEAL TH PROTECTION Intake of contaminated soil 40 40 20 40 20 40 150 I 000

Groundwater used for drinking water NS NS NS NS NS NS NS NS

ENVIRONMENT AL PROTECTION Toxicity to soil invertebrates and 0.45 0.7 0.7 0.7 0.7 10 10 IO plants

Livestock ingesting soi l and fodder NS


Groundwater flow to surface water NS NS NS NS NS NS NS NS used by aquatic life


Groundwater used for irrigation NS

Notes 1. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated

from time to time, a director's protocol or alternate methods acceptable to a director. 2. Standards are for the sum of DDT (2,4' + 4,4' isomers), DDD (2,4' + 4,4" isomers) and DOE (2,4' + 4,4 ' isomers). 3. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land


4. Intake pathway of exposure modelled is inadvertent ingestion of soil. 5. NS - no standard. No appropriate soil to groundwater model is available to predict the subsurface fate and transport of complex mixtures.

3

4

5

6

7

7

5

5

5,7

6. AL and PL standards are set equal to the corresponding 1999 Canadian Council of Ministers or the Environment (CCME) secondary consumer soil & food ingestion criteria. CL and IL

standards are set equal to the corresponding 1999 CCME soil contact criteria. WLN standard is derived by dividing the I 999 CCME parkland secondary consumer soil & food ingestion

"O Pl

(1Q (ll

N 0\ 0 ....., ...... w -.l

criterion by the Protocol 28, "2016 Standards Derivation Methods", Wildlands divisor. WLR standard is set equal to the 1999 CCME parkland secondary consumer soil & food ingestion

criterion. RLw standard is set equal to the 1999 CCME residential secondary consumer soil & food ingestion criterion. RLHD standard is set equal to the 1999 CCME commercial soil contact criterion.

7. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soil quality standard.

'O PJ

OQ (!)

N -J 0 ......,

\.>-l -J


DIISOPROPANOLAMINE (DIPA] (CHEMICAL ABSTRACT SERVICE NU:vIBER 110-97-4)

COLUMN COLUMN COLUMN COLUMN 1 2 3 4

COLUMN COLUMN 5 6

COLUMN 7

COLUMN 8

COLUMN I Note 9

Wildlands

I Wild lands

Site-specific Factor I Natural Reverted I Agri'""""' I (WLN) (WL,.) (AL)

I Res;d~U•I Urban Park Low Density

(PL) (Rlu,)


(Rl,.o)

Commercial (CL)


HUMAN HEAL TH PROTECTION Intake of contaminated soil 30 000 30 000 15 000 30 000 15 000 30 000 100 000 > I 000 mg/g


ENVIRONMENT AL PROTECTION Toxicity to soi l invenebrates and 600 750 750 750 750 1 000 1000 1 000 plants

Livestock ingesting soil and fodder NS




Groundwater used for irri!!ation 15 15 15 15


time to time, a director's protocol or alternate methods acceptable to a director. 2. The site-specific factors of human intake of contaminated soi l and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land

use standards of th is matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, spons field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvenent ingestion of soil. 4. Standards apply to a site used for an industrial or commercial purpose or activity as set out in Schedule 2 as item F2, F3, F7 or FlO. 5. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soil quality standard.

3

4

5

5

4

4

4

"O

~ ('1>

N 00

0 .....,

w -..I

COLUMN 1








Freshwater

Marine


Groundwater used for irrigation Notes


ETHYLBENZENE (CHEMICAL ABSTRACT SERVICE NUMBER 100-41-4)


Wild lands

I Wildlands

I I I ~.; .. ~., I -"-·' I I Natural Reverted Agricultural Urban Park Low Density High Density Commercial

(W~) (WLR) (AL) (PL) (R~) (RL"J (CL)

8 500 8 500 4 000 8 500 4000 8 500 25 000

15 15 15 15 15 15 15

100 200 200 200 200 650 650

NS

NS

200 200 200 200 200 200 200

200 200 200 200 200 200 200

NS

NS NS NS NS

COLUMN 9

I Industrial

(IL)

700 000

15

650

200

200

I. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 20 I 5 British Columbia Environmental Laboratory Manual, as updated from time to time, a director's protocol or alternate methods acceptable to a director.

2. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, sports field , picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard., or no appropriate standard, guideline or criterion exists to develop a soil quality standard. 5. Standard has been adjusted based on a modelled leachate concentration equivalent to the substance solubi lity limit for use in the soil to groundwater transport model.

Note

2

I 3

4

4

5

5

4

4

'O ~

00 ~

N \0

g, VJ -....)

COLUMN 1

MATRIX 16- NUMERICAL SOIL STANDARDS' ETHYLENE GLYCOL (CHEMICAL ABSTRACT SERVICE NUMBER 107-21-1)


COLUMN 8

COLUMN 9

Note

Site-specific Factor Wild lands

Natural

(WI.,,)

Wild lands Reverted

(Wl,,)

Agricultural (AL)

Urban Park (PL)


(RLLD) -


(RLHD) I Commercial I

(CL) Industrial

(IL) I , I

HUMAN HEAL TH PROTECTION Intake of contaminated soil 150 000 150 000 85 000 150 000 85 000 150 000 500 000 > l 000 mg/g


ENVIRONMENT AL PROTECTION Toxicity to soil invertebrates and 3 000 4000 4 000 4000 4000 6000 6 000 6 000 plants






Notes l. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated

from time to time, a director's protocol or alternate methods acceptable to a director. 2. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land


3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. Standards have been adjusted based on 2016 British Columbia Environmental Laboratory Technical Advisory Committee reference analytical detection limit for the substance. 5. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soil quality standard.

3

4

5

5

5

5

"O

~ ~ \,>.)

0 0 .......,

\,>.) -...)

COLUMN 1

I Site-specific Factor I HUMAN HEAL TH PROTECTION Intake of contaminated soil








Notes


FLUORANTHENE (CHEMICAL ABSTRACT SERVICE NUMBER 206-44-0)


Wildlands I Wildlands I 1-~·~" I R~;~m;•r I I Natural Reverted Agricultural Urban Park Low Density High Density Commercial

(WLN) (Wl,,) (AL) (PL) (RLLD) (RLH.,) (CL)

3 500 3 500 I 500 3 500 I 500 3 500 10 000

NS NS NS NS NS NS NS

30 50 50 50 50 200 200

NS

NS


NS

NS

COLUMN 9

Industrial (IL)

300 000

NS

200

NS

l. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from time to time, a director's protocol or alternate methods acceptable to a director.

2. The site-specific factors of human intake of contaminated soil and toxicity to soi l invertebrates and plants specified in this matrix apply at all sites. The high density residential land use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. NS- no standard. Soil to groundwater transport model predicts applicable water use standard for the substance will not be exceeded at the point of receptor exposure.

Note

I 2 I 3

4

5

6

6

4

6

6

5. AL, PL CL and IL standards are set equal to the corresponding 20 I 0 Canadian Council of Ministers or the Environment (CCME) soil quality criteria. WLN standard is derived by dividing the


criterion. RLw standard is set equal to the 2010 CCME residential soil quality criterion. RLHo standard is set equal to the 20 I 0 CCME commercial soil quality criterion. 6. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soil quality standard.

'O i::.i

(1q ~

VJ

0 .....,

VJ -.J

I

COLUMN 1

S ite-specific Factor


Groundwater used for drinking water pH< 5.5 pH 5.5 - <6.0 pH 6.0-<6.5 pH 6.5- < 7.0 pH7.0-<7.5 pH~ 7.5





Freshwater pH < 5.0 pH5.0 - <5.5 pH 5.5-<6.0 pH 6.0- < 6.5 pH6.5- < 7.0 pH 7.0- < 7.5 pH~ 7.5

Marine pH < 5.5 pH 5.5- < 6.0 pH 6.0 - < 6.5

COLUMN 2

I Wild lands

Natural (WLN)

120

120 150 800

3 500 7 500 8 500

400

200 350

1 500 8 500 35 000 80000 90000

MATRIX 18 - NUMERICAL SOIL STANDARDS 1

LEAD (CHEMICAL ABSTRACT SERVICE NUMBER 7 439-92-1)


I ! I I ! I Wildla nds I R~m•~•I I R~dom;., I I Reverted I ··"'""""' I Urban Pa rk Low Dens ity High Density Commerc ial

(WLR) (AL) (PL) (RL<.0) (RLHJ (CL)

120 120 120 120 120 150

120 120 120 120 120 120 150 150 150 150 150 150 800 800 800 800 800 800

3 500 3 500 3 500 3 500 3 500 3 500 7 500 7 500 7 500 7 500 7 500 7 500 8 500 8 500 8 500 8 500 8 500 8 500

550 550 550 550 1 000 I 000

350

700

200 200 200 200 200 200 350 350 350 350 350 350

1 500 1 500 1500 1 500 l 500 1 500 8 500 8 500 8 500 8 500 8 500 8 500

35 000 35 000 35 000 35 000 35 000 35 000 80 000 80000 80 000 80 000 80 000 80 000 90 000 90000 90 000 90 000 90 000 90 000

120 120 120 120 120 120 300 300 300 300 300 300

l 500 I 500 1 500 1 500 1 500 1 500

COLUMN Note 9

I

I

I Indust rial 2

(IL)

4 000 3

120 4,5 150 4 800 4

3 500 4 7 500 4 8 500 4

I 000

6

200 4,7 350 4,7 I 500 4,7 8 500 4,7

35 000 4,7 80000 4,7 90000 4,7

120 4,5 300 4

1 500 4

"O P.:l

(Jq ~

VJ N

g, VJ ..._J



, .. ~, /\All\ \••'-A/

{AL) (PL) {RLLD} (R'="u} (CL) (IL)

pH 6.5-< 7.0 6 500 6 500 6 500 6 500 6 500 6 500 6 500 pH~ 7.0 15 000 15 000 15 000 15 000 15 000 15 000 15 000


pH< 5.0 150 pH 5.0 - < 5.5 350 pH 5.5 - < 6.0 1500 pH 6.0-< 6.5 8 000 pH 6.5-< 7.0 35 000 pH 7.0- < 7.5 75 000 pH~ 7.5 85 000

Groundwater used for irrigation pH < 5.0 350 350 350 350 pH 5.0 - < 5.5 650 650 650 650 pH 5.5- < 6.0 3 000 3 000 3 000 3 000 pH 6.0- < 6.5 15 000 15 000 15 000 15 000 pH 6.5 - < 7.0 65 000 65 000 65 000 65 000 pH~7.0 150 000 150 000 150 000 150 000

Notes \. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from



3. Intake pathway of exposure modelled is inadvertent ingestion of soil. Standards for: WLN, WLR, AL, PL, RLw and RLHo have been adjusted based on 2016 reference Provincial background soi 1 concentration for the substance.

4. The pH is the pH of the soil at a site. 5. Standards have been adjusted based on 2016 reference Provincial background soil concentration for the substance. 6. Standard is set equal to 1999 Canadian Council of Ministers of the Environment, Nutrient and energy cycling check value. 7. Standard varies with receiving water hardness (H). H = 200 to < 300 mg/Las CaC03 is assumed. Consult director for further advice.

Note

2

4 4

4 4 4 4 4 4 4

4 4 4 4 4 4

'O p.:i

(1q (D

(.;.) (.;.)

0 ,_,.,

(.;.) -..l

COLUMN 1

S ite-specific Factor









Notes


MANGANESE (CHEMICAL ABSTRACT SERVICE NUMBER 7439-96-5)


Wild lands Wildlands

I I I R~;dom;., I R~;••"U•I I I Natural Reverted Agricultural Urban Park Low Density High Density Commercial

(WL,,) (WI,,) (AL) (PL) (RL..o) (Rl,,0

) (CL)

10000 10 000 6000 10000 6 000 10 000 35 000

2 000 2 000 2 000 2 000 2 000 2000 2 000

2 000 2 000 2 000 2 000 2 000 2000 2 000

NS

NS


NS

2 000 2000 2 000 2 000

COLUMN 9

Industrial (IL)

> I 000 mg/g

2 000

2 000

NS


2. The site-specific factors of human intake of contaminated soi l and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children' s playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. Standards apply to a site used for an industrial or commercial purpose or activity set out in Schedule 2 as

(a) item Bl, (b) item Cl, C3 or C4, (c) item 0 2, 03, D5 or 06, (d) item E4, or (e) itemH3 orH14.

Note

I 2

I 3

4,5,6

6

7

7

7

7

4,5,6

"'O

~ (1)

l.;J

~

g, -l.;J -.l

5. Standards apply to a site used for an industrial or commercial purpose or activity set out in Schedule 2 as item Hl 1 or H20 but only if the site was used for that purpose or activity in conjunction with or as a result of the site also being used for at least one of the purposes or activities set out in Note 4.

6. Standards have been adjusted based on 2016 reference Provincial background soil concentration for the substance. 7. NS- no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to use to develop a soil quality

standard.

"O

cf6 (t)

VJ VI

g, ...... VJ -.J

COLUMN 1

-


HUMAN HEAL TH PROTECTION Intake of contaminated soi l







Groundwater used for irri2ation

Notes

MATRIX 20 - NUMERICAL SOIL ST ANDARDS1.2

MERCURY (CHEMICAL ABSTRACT SERVICE NUMBER 7439-97-6)


I I I Wildlands Wildlands I "~"'",;," I R~;''"""' Natural Reverted Agricultural Urban Park Low Density High Density

(WLN) (WLR) (AL) (PL) (RLLO) (RLH0)

25 25 IO 25 IO 25

NS NS NS NS NS NS

25 40 40 40 40 75

0.6

20

NS NS NS NS NS NS

NS

NS NS NS NS

COLUMN COLUMN 8 9

Comm~l•I I Industrial (CL) (IL)

75 2 000

NS NS

75 75

NS NS

1. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from time to time, a director' s protocol or alternate methods acceptable to a director.

2. Analytical results for mercury (all species) in soi l may be used to demonstrate compliance with the standards of this matrix. 3. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land

use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a chi ldren's playground, sports field, picnic area or any other use that promotes frequent contact by chi ldren. Consult a director for further advice.

4. Intake pathway of exposure modelled is inadvertent ingestion of soil. 5. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to use to develop a soil quality

standard. 6. Standard is set equal to 1999 Canadian Council of Ministers of the Environment, "Nutrient and energy cycling check value".

Note

I 3

4

5

6

5

5

5

"t:I ~

(JQ ('t>

VJ 0\

0 ......, ....... w -J

COLUMN 1


HUMAN HEAL TH PROTECTION Intake of contaminated soi l


ENVIRONMENT AL PROTECTION Toxicity to soi l invertebrates and plants






Notes


METHANOL (CHEMICAL ABSTRACT SERVICE NUMBER 67-56-1)


I

Wildlands Wildlands -~.,,.., I """'""' Natural Reverted Agricultural Urban Park Low Density High Density

(WLN) (WLR) (AL) (PL) (RL,_,,) (RLH0 )

40000 40000 20 000 40 000 20000 40000

3 3 3 3 3 3

750 I 000 I 000 I 000 I 000 I 500

NS

NS

NS NS NS NS NS NS

NS

NS NS NS NS

COLUMN COLUMN 8 9

I

Comm•"'''' I Industrial (CL) (IL)

150 000 > I 000 mg/g

3 3

I 500 I 500

NS NS




Note

I

2

I 3

4

5

5

5

5

5

4. AL, PL, CL and IL standards are set equal to the corresponding 2016 Draft Canadian Council of Ministers of the Environment (CCME) soil quality criteria. WLN standard is derived by dividing the 2016 CCME parkland soi l quality criterion by the Protocol 28, "2016 Standards Derivation Methods", Wildlands divisor. WLR standard is set equal to the 2016 Draft CCME parkland soil quality criterion. RLw standard is set equal to the 2016 Draft CCME residential soil quality criterion. RLHo standard is set equal to the 2016 Draft CCME commercial soil quality criterion.


'O ~

(1Q (1)

VJ -J 0 ......,

VJ -J

COLUMN 1






Major microbial functional impainnent




Notes


MOLYBDENUM (CHEMICAL ABSTRACT SERVICE NUMBER 7439-98-7)


Wildlands

I Wildlands

I I ~m~••I I •·•-•" I I Natural Reverted Agricultural Urban Park Low Density High Density Commercial

(WLN) (WL,.) (AL) (PL) (Rl..o) (RLH0

) (CL)

400 400 200 400 200 400 I 500

15 15 15 15 15 15 15

60 80 80 80 80 150 150

NS

NS

650 650 650 650 650 650 650

3.5

3 3 3 3

COLUMN 9

Industrial (IL)

35 000

15

150

650

I. All values in µg/g unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from time to time, a director's protocol or alternate methods acceptable to a director.

2. The site-specific factors of human intake of contaminated soil and toxicity to soi l invertebrates and plants specified in this matrix apply at all sites. The high density residential

I

land use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soil quality standard. 5. Standards have been adjusted based on the 2016 reference Provincial background soil concentration for the substance. 6. Water standard for irrigation water (lW) used in the soi l to groundwater transport model to derive the groundwater used for irrigation soil standard varies with crop, soil drainage

and Mo:Cu ratio. An IW standard of l 0 µg/L was assumed in deriving the groundwater used for irrigation soil standards. Consult a director for further advice.

Note

2

I 3

4

4

5,6

'"Cl I):>

(1q ('1)

(..>-) 00

0 ..., VJ -....)

COLUMN 1







Groundwater flow to surface water used by aquatic Ii fe




NAPHTHALENE (CHEMICAL ABSTRACT SERVJCE NUMBER 91-20-3)


Wildlands

I Wild lands

I 1-~'"ti•I I Ros;dooti•I

Natural Reverted Agricultural Urban Park Low Density High Density

(WLN) (Wl,,) (AL) (Pl) (R~) (RLH0 )

1500 l 500 850 I 500 850 I 500

100 100 100 100 100 100

0.4 0.6 0.6 0.6 0.6 20

NS

NS

75 75 75 75 75 75

NS

NS NS NS NS

COLUMN COLUMN 8 9


5 000 150 000

100 100

20 20

75 75


2. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children' s playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. Standard has been adjusted based on a modelled leachate concentration equivalent to the substance solubility limit for use in the soil to groundwater transport model.

Note I

I 2

I 3

4

5

6

6

6

6

5. AL, PL, CL and IL standards are set equal to the corresponding 1997 Canadian Council of Ministers of the Environment (CCME) provisional soil quality criteria. WLN standard is derived by dividing the 1997 CCME parkland provisional soil quality criterion by the Protocol 28, "2016 Standards Derivation Methods", Wildlands divisor. WLR standard is set equal to the 1997 CCME parkland provisional soil quality criterion. RLw standard is set equal to the 1997 CCME residential provisional soil quality criterion. RLHo standard is set equal to the 1997 CCME commercial provisional soil quality criterion.

6. NS -no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soil quality standard.

'O ~

(]Q (!)

VJ \0

0 ...., ....... VJ -..)

I

COLUMN 1

Site-s pecific Factor


Groundwater used for drinking water pH < 7.5 pH 7.5- < 8.0 pH2:8.0





Freshwater pH < 5.0 pH 5.0 - < 5.5 pH 5.5 - < 6.0 pH 6.0 - < 6.5 pH 6.5- < 7.0 pH7.0- < 7.5 pH 7.5- < 8.0 pH 2: 8.0

Marine pH < 7.5 pH 7.5 - < 8.0 pH2:8.0

Groundwater used for livestock

COLU MN 2

I Wildlands

Natural (WL,.)

900

70 250 500

100

90 100 150 200 300 900

5 000 9 500


NICKEL (CHEMICAL ABSTRACT SERVICE NUMBER 7440-02-0)

COLUMN COLUMN COLUMN COLUMN COLUMN 3 4 5 6 7

I I Wild lands I R~idom;,1 I Ro•id•"" ' Reverted Agricultural Urban Park Low Dens ity High Density

(WLR) (AL) (PL) (RLLD) (RLHJ

900 450 900 450 900

70 70 70 70 70 250 250 250 250 250 500 500 500 500 500

150 150 150 150 250

250

150

90 90 90 90 90 100 100 100 100 100 150 150 150 150 150 200 200 200 200 200 300 300 300 300 300 900 900 900 900 900

5 000 5 000 5 000 5 000 5 000 9 500 9 500 9 500 9 500 9 500

70 70 70 70 70 250 250 250 250 250 500 500 500 500 500

COLUMN COLUM N Note 8 9

I

l

I Commercia l Industrial 2

(CL) (IL)

3 000 80 000 3

70 70 4,5 250 250 4 500 500 4

250 250

6

90 90 4,7 100 100 4,7 150 150 4,7 200 200 4,7 300 300 4,7 900 900 4,7

5 000 5 000 4,7 9 500 9 500 4,7

70 70 4,5 250 250 4 500 500 4

'O ~

QO (D

.p.. 0 0 ......., ....... UJ -.l


Wild lands Wildlands Residential Residential Site-specific Factor Natural Reverted Agricultural Urban Park Low Density High Density Commercial Industrial

(WLN) (WLR) (ALj (FLj (RLLD) (RLH0i ''"' .... , \II-/

watering pH < 5.0 70 pH5.0- < 5.5 80 pH 5.5 - < 6.0 100 pH 6.0- < 6.5 150 pH 6.5- < 7.0 200 pH7.0- < 7.5 600 pH7.5 - < 8.0 3 500 pH2:8.0 6 500

Groundwater used for irrigation pH < 7.0 70 70 70 70 pH7.0-<7.5 100 100 100 !00 pH 7.5- < 8.0 650 650 650 650 oH2:8.0 1 500 1 500 l 500 1500




3. Intake pathway of exposure mode lled is inadvertent ingestion of soil. 4. The pH is the pH of the soil at a site. 5. Standards have been adjusted based on 2016 reference Provincial background soil concentration for the substance. 6. Standard is set equal to 2015 Canadian Council of Ministers of the Environment. Nutrient and energy cycling check value. 7. Standard varies with receiving water hardness (H). H > 180 mg/L as CaC03 is assumed. Consult director for further advice.

Note

2

4,5 4 4 4 4 4 4 4

4,5 4 4 4

'O ~

Otl (1)

~

0 .....,

U.l -..)

MA TRIX 25 - NUMERICAL SOIL STANDARDS1.2

NONYLPHENOL AND NONYLPHENOL ETHOXYLATES (CHEMICAL ABSTRACT SERVlCE NUMBER 84852-15-3)

! COLUMN I COL_UMN ! COL_UMNl COLUMN - ! COL~MN ! COLUMN I COLUMN I COLUMN I COLUMN I Note I l 2 3 4 5 ij 7 ti ~


(WLN) (WLR) (AL) (PL) (RL,_,,) (RLHJ (CLi (IL)

HUMAN HEAL TH PROTECTION Intake of contaminated soil 400 400 200 400 200 400 I 000 35 000


ENVIRONMENTAL PROTECTION Toxicity to soil invertebrates and 3.5 5.5 5.5 5.5 5.5 15 15 15 plants



Groundwater flow to surface water used by aquatic li fe

Freshwater 4 4 4 4 4 4 4 4

Marine 3 3 3 3 3 3 3 3



Notes I. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from

time to time, a director's protocol or alternate methods acceptable to a director. 2. Nonylphenol includes related nonylphenolic and octylphenolic compounds, including ethoxylates and ethoxycarboxylates. Consult a director for further advice. 3. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential

land use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3

4

5

6

7

7

5

5

7

7

'O ~

(1Q (1)

~ tv 0 >-+,

VJ -...}

4. Intake pathway of exposure modelled is inadvertent ingestion of soil. 5. Standards apply to a site used for an industrial or commercial purpose or activity set out in Schedule 2 as

(a) item A6, A8, AIO or A12, (b) item HI I, Hl8 or Hl9, or (c) item 12 or 13.

6. AL, i'L , CL and IL standards are set equai to the corresponding 2002 Canadian Councii ofMinisit:ns ufihc fa1vi1\J1iinent (CCME) soil quality criteria. \VLN staudard is dcfr;cd by dividi~g the 2002 CCME parkland soil quality criterion by the Protocol 28, "2016 Standards Derivations Methods", Wildlands divisor. WLR standard is set equal to the 2002 CCME parkland soil quality criterion. RLw standard is set equal to the 2002 CCME residential soil quality criterion. RLHo standard is set equal to the 2002 CCME commercial soil quality criterion.


"O

~ ~

~ VJ

0 .....,

VJ -....)

COLUMN ~

Site-specific Facto r

HUMAN HEAL TH PROTECTION intake of contaminated soil

Groundwater used for drinking water pH < 5.0 pH 5.0 - < 5.5 pH 5.5 - < 6.0 pH 6.0-<6.5 pH 6.5-< 7.0 pH:': 7.0





pH< 5.0 pH5.0- < 5.5 pH 5.5 - < 6.0 pH 6.0-<6.5 pH:':6.5


pH < 5.0 pH 5.0 - < 5.5 pH 5.5 - < 6.0 oH 6.0- < 6.5


PENT ACHLOROPHENOL (PCP) (CHEMICAL ABSTRACT SERVICE NUMBER 87-86-5)

COLUM N COLUMN COLUMN COLUMN COLUMN COLU MN 2 3 4 5 6 7

Wildlands Wildlands Residential Residential Natural Reverted Agricultu ral Urban Park Low Density High Density

{WLN) (Wl,.) (AL) (PL) (RL..:,) (RLHo)

200 200 90 200 90 200

300 300 300 300 300 300 200 200 200 200 200 200 75 75 75 75 75 75 9 9 9 9 9 9

2.5 2.5 2.5 2.5 2.5 2.5 1.5 1.5 l.5 1.5 1.5 1.5

10 25 25 25 25 55

NS

NS

300 300 300 300 300 300 150 150 150 150 150 150 2 2 2 2 2 2

0.25 0.25 0.25 0.25 0.25 0.25 0.1 0. 1 0.1 0. 1 0.1 0.1

300 200 65 4.5

COLUMN COLUM N Note 8 9

Commerc ial Ind us trial 2 (CL) (IL)

550 900 3

300 300 4,5 200 200 4,5 75 75 4 9 9 4

2.5 2.5 4 1.5 1.5 4

55 55

6

6

300 300 4,5,7 150 150 4,7 2 2 4,7

0.25 0.25 4,7 0. 1 0. 1 4,7

4,5 4,5 4 4

'O

~ (ll

~ ~

0 .....,

V.l -.)


Wildlands Wild lands Residential Residential Site-specific Factor Natural Reverted Agr~~~~ural Urban Park Low Density High Density Commercial Industrial

(WLNj (WL,.i {PL} IOI ' fC:I\ (IL) \nLLO/ \n.'-Ho/ ,- - ,

pH 6.5 - < 7.0 1.5 pH?:7.0 0.75


Notes 1. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 20 l 5 British Columbia Environmental Laboratory Manual, as updated from

time to time, a director's protocol, or alternate methods acceptable to a director. 2. The site-specific factors of human intake of contaminated soil and toxicity to so il invertebrates and plants specified in this matrix app ly at all sites. The high density residential land

use standards of thi s matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. The pH is the pH of the soil at a site. 5. Standard has been adjusted based on a modelled leachate concentration equivalent to the substance solubility limit for use in the soil to groundwater transport model. 6. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soil quality standard. 7. Water standard for aquatic life (AW) used in the soil to groundwater transport model to derive the groundwater flow to surface water used by aquatic life soil standards varies with

Note

2

4 4

6

the temperature of the surface water used by aquatic life. A surface water temperature of20°C was assumed in deriving the groundwater flow to surface water used by aquatic life soil standard . Consult a director for further advice.

"Cl ~

OQ (1)

+>VI

0 ......,

VJ -...l

I

Notes

MATRIX 27- NUMERICAL SOIL STANDARDS' PERFLUOROOCTANE SULFONATE [PFOS) (CHEMICAL ABSTRACT SERVICE NUMBER 1763-21-1)

COLUMN COLUMN COLUMN COLUMN COLUMN COLUMN COLUMN COLUMN 1 2 3 4 5 6 7 8

I I I

I R~;d'"U•I I R~ld'"U'I I I Wildlands Wildlands Site-specific Factor Natural Reverted Agricultural Urban Park Low Density High Density Commercial

(WLN) (WL~) (AL) (PL) (RL.,,) (RLH0

) (CL)

HUMAN HEAL TH PROTECTION Intake of contaminated soil 2.5 2.5 I 2.5 I 2.5 7.5

Groundwater used for drinking water 0.35 0.35 0.35 0.35 0.35 0.35 0.35

ENVIRONMENTAL PROTECTION Toxicity to soil invertebrates and 40 60 60 60 60 150 150 plants



Groundwater flow to surface water 9 9 9 9 9 9 9 used by aquatic life



COLUMN 9

Industrial (IL)

200

0.35

150

9

I. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from time to time, a director' s protocol or alternate methods acceptable to a director.

2. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential

I

land use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, sports field , picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4 . Standards apply to a site used for an industrial or commercial purpose or activity set out in Schedule 2 as

(a) itemA4, (b) itemC3, (c) item EIO, or (d) item GI.

5. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soil quality standard. 6. Standard has been adjusted based on a modelled leachate concentration equivalent to the substance solubility limit for use in the soil to groundwater transport model.

Note

I

2

I

3

4

5

5

4,6

5

5

'O p.J

()'Cl ('1)

+>°' 0 >-+>

(.;) -...)

COLUMN COLUMN 1 2

I Wild lands

Site-specific Factor Natural

(WL,J

HUMAN HEAL TH PROTECTION Intake of contaminated soil 25 000

Groundwater used for drinking water 7.5

ENVIRONMENT AL PROTECTION Toxicity to soil invertebrates and 80 plants



Groundwater flow to surface water 15 used by aquatic life




PHENOL (CHEMICAL ABSTRACT SERVICE NUMBER 108-95-2)


Wildlands

I I -~·"·;., " .. ; ....... , I

Reverted Agricultural Urban Park Low Density High Density Commercial (WL,,) (AL) (PL) (RLLD) (RLH

0) (Cl)

25 000 10000 25 000 10 000 25 000 75 000

7.5 7.5 7.5 7.5 7.5 7.5

150 150 150 150 200 200

NS

NS

15 15 15 15 15 15

NS

NS NS NS NS

COLUMN 9

Industrial (IL)

>I 000 mg/g

7.5

200

15


2. The site-specific factors of human intake of contaminated soi l and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soi l quality standard.

Note

I 2

I 3

4

4

4

4

'O p)

(1Q ~

~ -...)

0 .....,

V.l -..)

MATRIX 29- NUMERICAL SOIL STANDARDS1'2

POLYCHLORINATED BIPHENYLS, TOT AL [PCBSI (CHEMICAL ABSTRACT SERVICE NUMBER 1336-36-3)

! COLUMN T COL_UMN ! COLUMN COLUMN ! COLffMN ! COLUMN COL_UMNTCOL~UMNTCOL_UMN j Note j 1 2 3 4 5 6 7 8 \:I

Wildlands Wild lands Residential Residential Site-specific Factor Natural Reverted Agricultural Urban Park Low Density High Density Commercial Industrial 3

(WLN) (WLR) (AL) (PL) (R~) (RLHD) (CL) (iL)

HUMAN HEAL TH PROTECTION Intake of contaminated soil IO 10 5 10 5 10 35 900 4

Groundwater used for drinking water NS NS NS NS NS NS NS NS 5

ENVIRONMENT AL PROTECTION Toxicity to soil invertebrates and 0.8 1.5 1.5 1.5 1.5 35 35 35 6 plants

Livestock ingesting soi l and fodder NS 5

Major microbial functional impairment NS 5

Groundwater flow to surface water NS NS NS NS NS NS NS NS 5 used by aquatic life

Groundwater used for livestock NS 5 watering

Groundwater used for irrigation NS NS NS NS 5

Notes 1. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from time to time, a

director's protocol or alternate methods acceptable to a director. 2. PCBs, total in soil represent the sum of Aroclors I 016, 1221, 1232, 1242, 1248, 1254, 1260, 1262, and 1268. Dioxin-like polychlorinated biphenyls must also be evaluated as polychlorinated dioxins

and furans. 3. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land use standards of

this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, sports field , picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

4. Intake pathway of exposure modelled is inadvertent ingestion of soil. 5. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soil quality standard. 6. AL and PL standards are set equal to the corresponding 1999 Canadian Council of Ministers of the Environment (CCME) tertiary consumer soil & food ingestion criteria. CL and IL standards

are set equal to the corresponding 1999 CCME soi l contact criteria. WLN standard is derived by dividing the 1999 CCME parkland tertiary consumer soil & food ingestion criterion by the

"O

~ (1)

.j:::.. 00

0 .....,.,

VJ -J

Protocol 28, "2016 Standards Derivations Methods", Wildlands divisor. WLR standard is set equal to the l 999 CCME parkland tertiary consumer soil & food ingestion criterion. RLw standard is set equal to the 1999 CCME residential tertiary consumer soil & food ingestion criterion. RL1m standard is set equal to the 1999 CCME commercial soil contact criterion.

"O P:>

()'Q (I)

~ \.0

0 ......., ....... w -J

COLUMN 1










Notes

MA TRIX 30 - NUMERICAL SOIL ST AND ARDS 1•2

POL YCHLORINATED DIOXINS AND FURANS, TOTAL [PCDDs AND PCDFs) (CHEMICAL ABSTRACT SERVICE NUMBER 1746-01-6)


Wi!d!ands Wi!d!ands Residential Residential Natural Reverted Agricultural Urban Park Low Density High Density (WL,.) (WLR) (AL) (PL) (R~) (RLHD)

0.0002 0.0002 0.000095 0.0002 0.000095 0.0002

NS NS NS NS NS NS

0.00065 0.001 0.00001 0.001 0.001 0.0025

NS

NS

NS NS NS NS NS NS

NS

NS NS NS NS

COLUMN COLUMN 8 9


0.0006 0.015

NS NS

0.0025 0.0025

NS NS


2. Polychlorinated dibenzo-p-dioxins (PCDDs) and polychlorinated dibenzofurans (PCDFs) expressed as 2,3,7,8-tetrachlorodibenzo-p-dioxin (2,3,7,8-TCDD) toxicity equivalent

Note

3

4

5

6

5

5

5

5

5

includes those substances for which 2005 World Health Organization, International Programme on Chemical Safety, 2,3,7,8-TCDD Toxicity Equivalency Factors (IPCS-TEFs) are provided below:

'O !).)

()'q (1)

VI 0 0 ......., ........ w -..J

I

WHO, 2005 2,3,7,8-TCDD Toxicity Equivalency Factors (IPCS-TEFs) for Dioxins, Furans and

Dioxin-like Polychlorinated Biphenyls (PCBs)

Polychlorinated dibenzo-p-dioxins IPCS-TEF Polychlorinated dibenzofurans lPCS-TEF

2,3,7,8-T4CDD 1.0 2,3 ,7,8-T4CDF 0.1

l,2,3,7,8-P5CDD 1.0 l ,2,3,7,8-P5CDF 0.03

1,2,3,4, 7 ,8-H6CDD 0.1 2,3,4,7,8-P5CDF 0.3

l ,2,3,6,7,8-H6CDD 0.1 1,2,3,4,7,8-~CDF 0.1

1,2,3, 7 ,8,9-H6CDD 0.1 1,2,3,6, 7,8-~CDF 0.1

1,2,3,4,6, 7 ,8,-H7CDD 0.01 1,2,3, 7 ,8,9-H6CDF 0.1

OsCDD 0.0003 2,3,4,6, 7 ,8-H6CDF 0.1

1,2,3,4,6, 7,8-H7CDF 0.01

l ,2,3,4,7,8,9-H7CDF 0.01

OsCDF 0.0003

Non-onho substituted PCBs IPCS-TEF Mono-onlw substituted PCBs IPCS-TEF

3,3',4,4'-T4CB (PCB 77) 0.0001 2,3,3',4,4' -P5CB (PCB 105) 0.00003

3,4,4',5- T4CB (PCB 81) 0.0003 2,3,4,4',5-P5CB (PCB 11 4) 0.00003

3,3',4,4',5-P5CB (PCB 126) 0.1 2,3',4,4',5-P5CB (PCB 118) 0.00003

3,3',4,4',5,5'-H6CB (PCB 169) 0.03 2',3,4,4',5-H6CB (PCB 123) 0.00003

2,3,3',4.4',5 -~CB (PCB 156) 0.00003

2,3,3',4,4',5'-H6CB (PCB 157) 0.00003

2,3',4,4',5,5'-~CB (PCB 167) 0.00003

2,3,3',4,4',5,5 '-H,CB (PCB 189) 0.00003

3. The site-specific factors of human intake of contaminated soil and toxicity to so il invertebrates and plants specified in this matrix apply at all sites. The high density residential land use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children 's playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

4. Intake pathway of exposure modelled is inadvertent ingestion of soil. 5. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soil quality standard. 6. AL, PL, CL and IL standards are set equal to the corresponding 1991 Canadian Council of Ministers of the Environment (CCME) interim soil quality criteria. WLN standard is

derived by dividing the 1991 CCME interim parkland soi l quality criterion by the Protocol 28, "20 16 Standards Derivations Methods", Wildlands divisor. WLR standard is set equal to the 1991 CCME interim parkland soil quality criterion. RLLD standard is set equal to the 1991 CCME interim residential soil quality criterion. RLtto standard is set equal to the 1991 CCME interim commercial soil quality criterion.

'O f:l:>

(]"Cl ~

UI

0 .......,

UJ -.)

COLUMN 1

-·-










Notes


SELENIUM (CHEMICAL ABSTRACT SERVICE NUMBER 7782-49-2)

COLUMN 1 COL3UMN COLUMN COLUMN COLUMN COLUMN

2 4 5 6 7

I Wildlands I WHdlood• I R6;dMt;., I ... ;.,.,.;,,

Natural Reverted Agricultural Urban Park Low Density High Density

(WLN) (Wl,,) (AL) (PL) (Rlw) (Rl,,o)

400 400 200 400 200 400

1 1 1 1 I 1

1.5 1.5 1.5 1.5 1.5 2

2

NS

l l I I I I

1

1 1 I 1

COLUMN COLUMN 8 9

I I Commercial Industrial

(CL) (IL)

I 500 35 000

1 1

2 2

1 1

I. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual , as updated from time to time, a director' s protocol, or alternate methods acceptable to a director.

2. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children ' s playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. Standards have been adjusted based on 2016 reference Provincial background soil concentration for the substance. 5. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to use to develop a soil quality standard. 6. Standard applies where irrigation water is used for continuous or intermittent irrigation of crops.

Note

2

I 3

4

5

4

4

6

"O

~ (!>

Vl N

g, VJ -.!


SODIUM ION (CHEMICAL ABSTRACT SERVICE NUMBER 17341-25-2)

COLUMN 1


COLUMN 8

COLUMN I Note 9

Site-specific Factor Wildlands

Natural

(Wl,.)

Wildlands Reverted

(Wl,,)

Agricultural (AL)

Urban Park (PL)


(RLLD)


(RLHD)

Commercial (CL)


HUMAN HEAL TH PROTECTION Intake of contaminated soi l > l 000 mg/g > l 000 mgig > I 000 mg/g > l 000 mg/g > 1 000 mg/g > 1 000 mg/g > 1 000 mg/g > 1 000 mg/g

Groundwater used for drinking water 15 000 15 000 15 000 15 000 15 000 15 000 15 000 15 000

ENVIRONMENT AL PROTECTION Toxicity to soil invertebrates and 150 200 200 200 200 I 000 1 000 1 000 plants



Groundwater flow to surface water NS NS NS NS NS NS NS NS used by aquatic life


Groundwater used for irrigation NS NS NS NS Notes 1. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated FROM

time to time, a director's protocol or alternate methods acceptable to a director. 2. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land

use standards of this marrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soil quality standard.

3

4

4

4

4

4

"O ~

(JQ Ct> UI w

s, w -..l

COLUMN 1


SULFOLANE (CHEMICAL ABSTRACT SERVICE NUMBER 126-33-0)


COLUMN COLUMN 8 9

I

I I I I I Wild lands Wildlands 1-;,~, .. I ·~;_,.,

Site-specific Factor Natural Reverted Agricultural Urban Park Low Density High Density Commercial '"'"·"·' I (Wl,.) (WLR) (AL) (PL) (R'-u,) (RLHol (CL) (IL)

HUMAN HEAL TH PROTECTION Intake of contaminated soil 800 800 400 800 400 800 2 500 70 000


ENVIRONMENT AL PROTECTION Toxicity to soil invertebrates and 250 350 350 350 350 500 500 500 plants




Groundwater used for livestock 5.5 watering

Groundwater used for irri11:ation 3 3 3 3


time to time, a director' s protocol or alternate methods acceptable to a director. 2. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land

use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children ' s playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. Standards apply to a site used for an industrial or commercial purpose or activity set out in Schedule 2 as item F2, F3, F7 or FIO. 5. Standard has been adjusted based on the 2016 British Columbia Environmental Laboratory Technical Advisory Committee reference analytical detection limit for the substance. 6. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soil quality standard.

Note

2 I 3

4,5

6

6

4

4

4

'O $:>)

crq (1)

Vl .+:>. 0 ....., (.;..)

-..l

COLUMN 1


TETRACHLOROETHYLENE (CHEMICAL ABSTRACT SERVICE NUMBER 127-18-4)

COLUMN COLUMN COLUMN COLUMN COLUMN COLUM N 2 3 4 5 6 7

COLUMN COLUMN 8 9

I I

I I I I Wildlands Wildlands I Res;d~U•I I R~~·"""

Site-specific Factor Natural Reverted Agricultural Urban Park Low Density High Density Commore;., I '"'"'"''·' I (WLN) (WLR) (AL) (PL) (RLL.C) (RLH0 ) (CL) (IL)

HUMAN HEALTH PROTECTION Intake of contaminated soil 500 500 250 500 250 500 1 500 40000


ENVIRONMENT AL PROTECTION Toxicity to soil invertebrates and 6 15 15 15 15 30 30 30 plants



Groundwater flow to surface water 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 used by aquatic life



Notes I. All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from

time to time, a director's protocol or alternate methods acceptable to a director. 2. The site-specific factors of human intake of contaminated soi l and toxicity to soil invertebrates and plants specified in this matrix apply at all sites. The high density residential land

use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a chi ldren's playground, sports field, picnic area or any other use that promotes frequent contact by chi ldren. Consult a director for further advice.


Note

I

2

I 3

4

4

4

4

"O p.)

(IQ (!)

VI VI

0 ......, ....... VJ -...)

COLUMN 1


HUMAN HEAL TH PROTECTION !make of contaminated soil






Freshwater

Marine



Notes


TOLUENE (CHEMICAL ABSTRACT SERVICE NUMBER 108-88-3)


Wild lands

I

Wildlands

I I 1

.... ;...... I ·~; .. m; •• Natural Reverted Agricultural Urban Park Low Density High Density (WL,.) (Wl,.) (AL) (PL) (RL..o) (RLH0 )

6 500 6 500 3 500 6 500 3 500 6 500

6 6 6 6 6 6

90 150 150 150 150 450

NS

NS

0.5 0.5 0.5 0.5 0.5 0.5

200 200 200 200 200 200

NS

NS NS NS NS

COLUMN COLUMN 8 9

Com~~;., I Industrial (CL) (IL)

20 000 550 000

6 6

450 450

0.5 0.5

200 200


2. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in th is matrix apply at all sites. The high density residential land use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground., sports field., picnic area or any other use that promotes frequent contact by chi ldren. Consult a director for further advice .

.J. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soil quality standard.

Note

I 2

I

3

4

4

4

4

'O ~

OQ (!)

VI 0\ 0 ....., (j.)

-.J

COLUMN 1










MATRIX 36- NUMERlCAL SOIL STANDARDS1

TRICHLOROETHYLENE (CHEMICAL ABSTRACT SERVICE NUMBER 79-01-6)


I I Wildlands Wildlands I Res;d~ti" I R6;dom;,1 I

Natural Reverted Agricultural Urban Park Low Density High Density Commercial (Wl,;) (Wl,,) (AL) (PL) (RLLO) (Rl,.

0) (CL)

40 40 20 40 20 40 150

8 15 15 15 15 25 25

NS

NS

0.3 0.3 0.3 0.3 0.3 0.3 0.3

NS NS NS NS

COLUMN 9

I Industrial

(IL)

3 500

25

0.3




Note

I

2

I 3

4

4

4

"O ~

()q (1)

Ul -....J 0 ......,

(.;.) -....J

COLUMN 1










Notes

MATRIX 37 - NUMERICAL SOIL ST ANDARDS 1

URANIUM (CHEMICAL ABSTRACT SERVICE NUMBER 7440-61-1)


Wildlands Wild lands

I I I ""'"''"u" I •~;dooU•I Natural Reverted Agricultural Urban Park Low Density High Density

(Wl,,) (WLR) (AL) (PL) (RLLC) (RL"0 )

250 250 LOO 250 LOO 250

30 30 30 30 30 3040

300 500 500 500 500 2000

35

NS

150 150 L50 150 150 150

300

15 15 15 15

COLUMN COLUMN 8 9

Comm,.,;,; I Industrial (CL) (IL)

750 20 000

30 30

2 000 2000

150 150




Note

I 2

3

4

5

6

4. AL, PL, CL and IL standards are set equal to corresponding 2007 Canadian Council of Ministers of the Environment (CCME) soil contact criteria. WLN standard is derived by dividing the 2007 CCME parkland soil contact criterion by the Protocol 28, "2016 Standards Derivation Methods", Wildlands divisor. WLR standard is set equal to 2007 CCME parkland soil contact criterion. RLw standard is set equal to the 2007 CCME residential so il contact criterion. RLtto standard is set equal to the 2007 CCME commercial soil contact criterion.

5. Standard is set equal to the 2007 CCME agriculrural soil & food ingestion criterion. 6. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soil quality standard.

I

"O

~ ('1)

VI 00

0 ....., (.;.) -....J

COLUMN 1










Notes


VANADIUM (CHEMICAL ABSTRACT SERVICE NUMBER 7440-62-2)


Wildlands

I Wildlands

I I I R6;dooU" I R6;doort01 I

Natural Reverted Agricultural Urban Park Low Density High Density Commercial

{WLN) {WLR) {AL) (PL) {RLLD) (RLHJ (CL)

400 400 200 400 200 400 I 500

100 100 100 100 100 100 100

100 150 150 150 150 300 300

NS

250


350

350 350 350 350

COLUMN 9

I Industrial

(IL)

35 000

JOO

300

NS

I . All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual , as updated from time to time, a di rector's protocol or alternate methods acceptable to a director.


3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. Standards have been adjusted based on the 2016 reference Provincial background soil concentration for the substance. 5. NS - no standard. Insufficient acceptable scientific data exists to calculate a standard, or no appropriate standard, guideline or criterion exists to develop a soil quality standard. 6. Standard is set equal to 1997 Canadian Council of Ministers of the Environment, ''Nutrient and energy cycling check value".

Note

2

3

4

5

6

5

'O

~ ('!)

VI \0 0 ~ -VJ -....J

COLUM N 1




ENVIRONMENT AL PROTECTION Toxicity to soi l invertebrates and plants






MATRIX 39 - NUMERICAL SOIL ST ANDARDS1

XYLENES (CHEMICAL ABSTRACT SERVICE NUMBER 1330-20-7)

COLUM N COLUMN COLUMN COLUMN COLUMN COLUMN COLUMN 2 3 4 5 6 7 8

Wild lands

I Wild lands

I I I ""'"""U•I ""'®ml.i I I Natura l Reverted Agricultural Urban Park Low Dens ity High Dens ity Commercia l

(WLN) (WLR) (AL) (PL) (RI.,,,) (RLH0

) (CL)

15 000 15 000 8 500 15 000 8 500 15 000 50 000

6.5 6.5 6.5 6.5 6.5 6.5 6.5

100 150 150 150 150 600 600

NS

NS

20 20 20 20 20 20 20

NS

NS NS NS NS

COLUMN 9

Industrial (IL)

> 1 000 mg/g

6.5

600

20


2. The site-specific factors of human intake of contaminated soil and toxicity to soil invertebrates and plants specified in th is matrix apply at all sites. The high density residential land use standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, sports fie ld, picnic area or any other use that promotes frequent contact by chi ldren. Consult a director for further advice.


Note

I 2

3

4

4

4

4

'O p;

(IQ (!>

0\ 0

g, ...... w -..)

I

COLUM N 1



Groundwater used fo r drinking water pH < 5.0 pH 5.0- < 5.5 pH 5.5 - < 6.0 pH 6.0 - < 6.5 pH 6.5 - < 7.0 pH 7.0-< 7.5 pH 7.5 - < 8.0 pH~ 8.0



Major microbial funct ional impairment

Groundwaier flow ro surface water used by aquatic life

Freshwater pH < 6.0 pH 6.0- < 6.5 pH 6.5 - < 7.0 pH7.0- < 7.5 pH 7.5 - < 8.0 pH ~ 8.0

Marine pH < 8.0 pH ~ 8.0

COLUMN 2

I Wild la nds

Natural (WLN)

25 000

200 250 300 450 600

1 000 3 000 5 500

300

150 250 350 600

1500 3 000

150 200

MATRIX 40 - NUMERICAL SOIL ST ANDARDS 1

ZINC (CHEMICAL ABSTRACT SERVICE NUMBER 7440-66-6)

COLUMN COLUMN COLUM N COLUMN 3 4 5 6

I I

! I

Wildlands

I ""'"'""'''' Reverted Agrio" ltural I Urban Park Low De nsity

(WL,.) (AL) (PL) (Rlu)

25 000 10 000 25 000 10000

200 200 200 200 250 250 250 250 300 300 300 300 450 450 450 450 600 600 600 600 I 000 I 000 1 000 I 000 3 000 3 000 3 000 3 000 5 500 5 500 5 500 5 500

450 450 450 450

200

200

150 150 150 150 250 250 250 250 350 350 350 350 600 600 600 600

I 500 1 500 1 500 I 500 3 000 3 000 3 000 3 000

150 150 150 150 200 200 200 200

COLUMN COLUMN COLUMN Note 7 8 9

I

I

I

R~idontiol I I

High Dens ity Commerc ial Industrial 2 (RLHJ (CL) (IL)

25 000 75 000 > I 000 mg/g 3

200 200 200 4 250 250 250 4 300 300 300 4 450 450 450 4 600 600 600 4

I 000 I 000 I 000 4 3 000 3 000 3 000 4 5 500 5 500 5 500 4

450 450 450

5

150 150 150 4,6,7 250 250 250 4,7 350 350 350 4.7 600 600 600 4,7

1 500 I 500 I 500 4,7 3 000 3 000 3 000 4,7

150 150 150 4,6 200 200 200 4

'O

~ (!>

0\ ...... g, ...... V.l -..)

COLUMN COLUMN COLUMN COLUMN COLUMN COLUMN COLUMN COLUMN COLU MN Note 1 2 3 4 5 6 7 8 9

Wild lands Wildlands Residential Residential Site-specific Factor Natural Reverted Agricultural Urban Park Low Density High Density Commercial Industrial

(WLN) (WLR) {AL) \rl...J (RLLDj (RLHoi /l""'I\ /II\ , __ , ,.-,


pH < 5.5 150 pH 5.5 - < 6.0 200 pH 6.0-< 6.5 300 pH 6.5 -< 7.0 400 pH 7.0-< 7.5 750 pH 7.5- < 8.0 2 000 pH~ 8.0 3 500

Groundwater used for irrigation pH < 6.0 150 150 150 150 pH 6.0- < 6.5 300 300 300 300 pH 6.5 - < 7.0 400 400 400 400 pH 7.0-< 7.5 2 000 2 000 2000 2 000 pH 7.5-< 8.0 5 000 5 000 5 000 5 000 pH > 8.0 9 000 9 000 9000 9 000

Notes I . All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laborarory Manual, as updated from

time to time, a director's protocol, or alternate methods acceptable to a director. 2. The site-specific factors of human intake of contaminated so il and toxicity to so il invertebrates and plants specified in this matrix apply at all sites. The high density residential land use

standards of this matrix assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children 's playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3. Intake pathway of exposure modelled is inadvertent ingestion of soil. 4. The pH is the pH of the soil at a site. 5. Standard is set equal to 1999 Canadian Council of Ministers of the Environment, Nutrient and energy cycling check value. 6. Standards have been adjusted based on 2016 reference Provincial background soil concentration for the substance. 7. Standard varies with receiving water hardness (H). H = 200 to < 300 mg/L as CaC03 is assumed. Consult director for further advice.

2

4,6 4 4 4 4 4 4

4,6 4 4 4 4 4

'"O

~ ())

°' N 0 ...., UJ -J

COLUMN 1

Substance

acenaphthene

acephate

acetic acid, 2-methyl-4-

chlorophenoxy- [MCPA)

acetochlor

acetone

acetophenone

acrolein

acrylamide

acrylic acid

acrylonitrile

adipic acid

alachlor

aldicarb

aldicarb sulfone

aldrin

allyl alcohol

allyl chloride

aluminum

ametryn

aminobiphenyl, 4-

aminophenol, 3-

aminophenol, 4-

amitraz

aniline

anthraquinone, 9, 10-

antimony

aramite

SCHEDULE3.l-PART 2

GENERIC NUMERICAL SOIL STANDARDS TO PROTECT HUMAN HEALTH1' 2

COLUMN 2 I COLUMN 3 I COLUMN 4 I COLUMN 5 I COLUMN 6 I COLUMN 7 COLUMN 8 COLUMN 9 I COLUMN 10

Chemical Abstract Service Number (CAS)

83-32-9

30560-19-1

94-74-6

34256-82-1 67-64-1

98-86-2

107-02-8

79-06-1

79-10-7

107-13-1

124-04-9

15972-60-8

116-06-3

1646-88-4

309-00-2

107-18-6

107-05-1

7429-90-5

834-12-8

92-67-1

591-27-5

123-30-8

33089-61-1

62-53-3

84-65-1

7440-36-0

140-57-8

I Wildlands I

Natural (WL,.)

2 000

100

15

650 30 000

3 0003

15

6

15 000

25

65 0004

250

30

30

0.8

150

650

40 000

300

0.65

2 500

650

80

200

65

5005

550

Wild lands Reverted

(WL.)

2 000

100

15

650

30 000

3 0003

15

6

15 000

25

65 0004

250

30

30

0.8

150

650

40 000

300

0.65

2 500

650

80

200

65

500'

550

Agricultural Urban Park 0;~~y High Density Commercial

I I I. Res!dent!a!1· Residentiai I I

(AL) (PL) (RLLO) (RLtt0) (CL)

950 2 000 950 2 000 15 000

60 100 60 100 950

8 15 8 15 100

300 650 300 650 4 500

15 000 30 000 15 000 30 000 200 ooo.J·4

I 5003 3 0003 I 500

3 3 000

3 25 0003'4

8 15 8 15 100

3 6 3 6 65

8 000 15 000 8 000 15 000 100 000

15 25 15 25 60

30 0004

65 ooo" 30 0004

65 0004

450 0004

100 250 100 250 600

15 30 15 30 250

15 30 15 30 250

0.4 0.8 0.4 0.8 2

80 150 80 150 1 000

350 650 350 650 1 500

40 000 40 000 40 000 40 000 250 0004

150 300 150 300 2 000

0.35 0.65 0.35 0.65 1.5

l 500 2 500 I 500 2 500 20 000

300 650 300 650 4 500

40 80 40 80 600

100 200 100 200 I 500

30 65 30 65 450

250) 500) 250) 500) 1 500)

300 550 300 550 1 500

Industrial (IL)

15 000

950

100

4 500

200 000j '4

25 0003'4

100

65

100 000

60

450 0004

600

250

250

2

1 000

I 500

250 0004

2 000

1.5

20 000

4 500

600

I 500

450

40 000)

1 500

'O ~

(/Cl (1)

0\ (.;.)

0 ........ ....... (.;.)

-..J

I

COLUMN 1

Substance

asbestos

asulam

atrazine

auramine

avennectin Bl (a+ b)

azinphos-methyl

azobenzene

azodicarbonamide

benfluralin

benomyl

bensulfuron-methyl

bentazon

benz( a )anthracene

benzidine

benzo(b+j)fluoranthenes

benzo(k)fluoranthene

benzoic acid

benzotrichloride

benzyl alcohol

benzyl chloride

bifenox

bifenthrin

biphenyl, 1,1'-

bis(2-chloroethoxy) methane

bis(2-chloro-1-methylethyl) ether

bis(2-ethylhexyl) adipate


GENERIC NUMERICAL SOIL STANDARDS TO PROTECT HUMAN HEALTH1

'2

COLUMN 2 COLUMN3 COLUMN 4 COLUMN 5 COLUMNS COLUMN7 COLUMNS COLUMN 9

I Chemical I I I I o--·~-... J I Abstract I Se<Vke I w;ldlands w;ldlands I I I "00

'"

0 """'1 Res;dential I Number Natural Reverted Agricultural Urban Park 0 Lo~ High Density Commercial

(CAS) (WL,.) (WLJ (AL) (PL) (~~s~;y (RLH0 ) (CL)

1332-21-4 1%" 1%" 1%(> 1%(> 1%(> 1%(> 1%(>

3337-71 -1 I 500 1 500 800 1 500 800 I 500 10 000

1912-24-9 60 60 30 60 30 60 150

492-80-8 15 15 8 15 8 15 35

71751-41-2 JO 10 6 10 6 10 95

86-50-0 90 90 45 90 45 90 700

103-33-3 150 150 65 150 65 150 300

123-77-3 30 000 30 000 15 000 30 000 15 000 30 000 250 000

1861-40-1 9 000 9 000 4 500 9 000 4 500 9 000 70 0004

17804-35-2 1 500 1 500 800 I 500 800 1 500 10 000

83055-99-6 6 500 6 500 3 000 6 500 3 000 6 500 45 0004

25057-89-0 900 900 450 900 450 900 7 000

56-55-3 95),/ 95),/ 50),/ 95),/ 50), / 95 ),/ 300),/

92-87-5 0.015 0.015 0.0065 0.015 0.0065 0.015 0.15

205-99-2 95),/ 95),/ 50),/ 95), / 50),/ 95 )'7 3005'7

& 205-82-3

207-08-9 955,7 955,7 505,1 95),/ 50

5"

955,1 3005'7

65-85-0 100 0004

100 ooo" 60 ooo" 100 ooo" 60 0004

100 0004

950 0004

98-07-7 1 1 0.55 I 0.55 1 2.5

100-51-6 3 000 3 000 1 500 3 000 I 500 3 000 25 000

100-44-7 65 65 30 65 30 65 200

42576-02-3 300 300 150 300 150 300 2 000

82657-04-3 500 500 250 500 250 500 3 500

92-52-4 15 000 15 000 8 000 15 000 8 000 15 000 100 000

ll 1-91-l 90 90 45 90 45 90 700

108-60-1 1 000 1 000 600 1 000 600 1 000 9 500

103-23-1 10 000 10 000 6000 10 000 6000 10 000 25 000

COLUMN 10

I

I Industrial

(IL)

1%(>

10 000

150

35

95

700

300

250 000

70 0004

10 000

45 0004

7 000 500), /

0.15

5005'7

5005

'1

950 0004

2.5

25 000

200

2 000

3 500

100 000

700

9 500

25 000

'"O s::>:>

()'Q ~

0\ +:>. 0 ......,

UJ -..J

I

COLUMN 1

Substance

bis(2-ethylhexyl) phthalate [DEHP]

bis(chloroethyl) ether

bisphenol A

boron

bro mate

bromo-2-chloroethane, 1-

bromobenzene

bromodichloromethane

bromoform

bromomethane

bromophos

bromoxynil

butadiene, 1,3-

butanoic acid, 4-(4-chloro-2-methylphenoxy)- (MCPB]

butanol, 2-

butanol, n-

butoxy ethanol, 2-

butyl benzyl phthalate

butyl phthalyl butyl glycolate

butylate

butylated hydroxytoluene

[BHT]

butylbenzene, n-

butylbenzene, sec-

butylbenzene, tert-

cacodylic acid

SCHEDULE 3.1 - PART 2

GENERIC NUMERICAL Son, STANDARDS TO PROTECT HUMAN HEALTH1'

2

COLUMN 2 COLUMN 3 COLUMN 4 COLUMNS COLUMNS COLUMN 7 COLUMNS

I Chemical

I I I I o--=~-~·J Abstract I s..v;ce w;ldlands I w;ldlands I I I ""°[_-.. ·-·1 Res;denUal Number Natural Reverted Agricultural Urban Park De~;ty High Density (CAS) (WLJ (WLJ (AL) (PL) (RLLD) (RL"0 )

117-81-7 350' 3505 150' 3505

1505 3505

111-44-4 2.5 2.5 1.5 2.5 1.5 2.5 80-05-7 1 500 I 500 800 1 500 800 1 500

7440-42-8 15 000) 15 000) 8 500) 15 000) 8 500) 15 000)

15541-45-4 20 20 10 20 10 20

107-04-0 7 7 3.5 7 3.5 7 108-86-1 250 250 150 250 150 250

75-27-4 200 200 100 200 100 200 75-25-2 650 650 300 650 300 650

74-83-9 45 45 20 45 20 45

2104-96-3 150 150 80 150 80 150

1689-84-5 650 650 300 650 300 650

106-99-0 4 4 2 4 2 4

94-81-5 300 300 150 300 150 300

78-92-2 65 000 65 000 30 000 65 000 30 0003'4 65 000,·4

71-36-3 3 0003 3 000

3 1 5003 3 oooj I 5003

3 0003

111-76-2 3 000 3 000 1 500 3 000 1 500 3 000

85-68-7 6 500 6 500 3 000 6 500 3 000 6 500

85-70-1 30 000 30 000 15 000 30 000 15 000 30 000

2008-41-5 1 500 1 500 800 I 500 800 I 500

128-37-0 4 000 4 000 2 000 4 000 2 000 4 000

104-51-8 1 500j 1 5ooj 800) 1 500j 800j 1 500,

135-98-8 3 oooj 3 oooj 1 500j 3 oooj 1 500.i 3 000)

98-06-6 3 oooj 3 oooj 1 500j 3 oooj 1 500.i 3 oooj

75-60-5 650 650 300 650 300 650

COLUMN9 COLUMN 10

I

I Comme•dall Industrial

(CL) (IL)

1 0005 30 0005

6 6

10 000 10 000

50 000) > 1 000 mg!g'

45 45

15 15

2 000) 2 oooj

550 550 4 000 4 000

300 300

1 000 1 000

4 500 4 500

9.5 9.5

2500 2500

450 000 450 000

25 0003'4 25 0003

'4

25 000 25 000

15 000 15 000

250 0004

250 0004

10 000 10 000

9 000 9 000

10 000) 10 oooj

25 oooj·4 25 000j'4

25 oooj·4 25 oooj·4

4500 4500

"O ~ (ll

0\ VI

0 ......, -VJ -..l

I

COLUMN 1

Substance

caprolactam

captafol

cap tan

carbaryl

carbofuran

carbon disulfide

carbon tetrachloride

carbosulfan

carboxin

chloramben

chloranil

chlordane (cis +trans)

chlordecone

chlorfenvinphos

chlorimuron, ethyl

chloro-2-methylaniline, 4-

chloroacetaldehyde, 2-

chloroaniline, p-

chlorobenzene

chlorobenzilate

chlorobenzoic acid, 4-

chlorobenzotrichloride, 4-

chlorobenzotrifluoride, 4-

chlorobutane, 1-

chloroethanol, 2-

chloroform

chloronaphthalene, 2-

SCHEDULE 3.1-PART 2

GENERIC NUMERICAL SOIL ST AND ARDS TO PROTECT HUMAN HEAL TH1' 2

COLUMN 2 COLUMN3 COLUMN4 COLUMNS COLUMN 6 COLUMN7 COLUMN 8 COLUMNS

I Chemical I I I I ~--'~--·J I I Abstract I Se<Vke I Wildlands I Wildlands I I •-

00"-"'"'I Residential I I Number Natural Reverted Agricultural Urban Park 0;~;y High Density Commercial (CAS) (WL,.) (WLJ (AL) (PL) (RLLD) (RLHD) (CL)

105-60-2 15 000 15 000 8 000 15 000 8 000 15 000 100 0004

2425-06-1 65 65 30 65 30 65 200

133-06-2 4 000 4 000 2 000 4 000 2 000 4 000 15 000

63-25-2 3 000 3 000 1 500 3 000 1 500 3 000 25 000

1563-66-2 150 150 80 150 80 150 I 000

75-15-0 3 0003 3 0003

I 5003 3 000

3 I 5003 3 000

3 25 0003

56-23-5 350) 350) 150) 350) 150) 3505 I 000)

55285-14-8 300 300 150 300 150 300 2 500

5234-68-4 3 000 3 000 I 500 3 000 I 500 3 000 25 000

133-90-4 500 500 250 500 250 500 3 500

118-75-2 35 35 15 35 15 35 80

5103-71-9 15 15 8 15 8 15 95

& 5103-74-2

143-50-0 1.5 1.5 0.7 1.5 0.7 1.5 3.5

470-90-6 20 20 10 20 10 20 150

90982-32-4 650 650 300 650 300 650 4 500

95-69-2 90 90 45 90 45 90 350

107-20-0 50 50 25 50 25 50 100

106-47-8 70 70 35 70 35 70 150

108-90-7 I 500) I 500) 850) I 500) 850) 1 500) 5 000)

510-15-6 150 150 65 150 65 150 300

74-11-3 900 900 450 900 450 900 7 000

5216-25-1 0.7 0.7 0.35 0.7 0.35 0.7 1.5

98-56-6 90 90 45 90 45 90 7003

109-69-3 1 oooj 1 oooj 600j 1 0003 600~ 1 000.l 9 500

3

107-07-3 650 650 300 650 300 650 4 500

67-66-3 850) 850) 400) 850) 400) 850) 2 500)

91-58-7 2 500 2 500 I 500 2 500 I 500 2 500 20 000

COLUMN10

I Industrial

(IL)

100 0004

200

15 000

25 000

I 000

25 0003

5 000)

2 500

25 000

3 500

80

95

3.5

150

4 500

350

100

150

150 000)

300

7 000

1.5

700.l

9 500.l

4 500

70 000)

20 000

"O s:;.)

(TQ (1)

0\ 0\ 0 .....,

(.;.) -J

COLUMN 1

Substance

chloronitrobenzene, 2-chloronitrobenzene, 4-

chlorophenol, 2-

chlorophenol,3-

chlorophenol, 4-

chloroprene

chlorothalonil

chlorotoluene, 2-

chlorotoluene, 4-

chlorpropham

chlorpyrifos

chlorpyrifos-methyl

chlorsulfuron

chlorthal-dimethyl

chlorthiophos

chrysene

clofentezine

crotonaldehyde, trans-

cyanazine

cyanogen

cyclohexane, 1,2,3,4,5-pentabromo-6-chloro-

cyclohexanone

cyclohexene

cyclohexylamine

cyfluthrin

cyhalothrin



COLUMN 2 I COLUMN 3 I COLUMN 4 I COLUMN 5 I COLUMN 6 I COLUMN 7 COLUMN 8 COLUMN 9 I COLUMN 10

Chemical Abstract . . , , , _ . ._ _ .. _.

Service I Wildlands I Wildlands I I I nes~oenui:1•1 Residential I I Number Natural Reverted Agricultural Urban Park

0 °~ High Density Commercial

(CAS) (WL,.) (WL") (AL) (PL) (~~s~;y (RL"°) (CL)

88-73-3 45 45 25 45 25 45 100 100-00-5 30 30 15 30 15 30 250

95-57-8 400) 400) 200) 400) 200) 400) 1 500)

108-43-0 250).~ 250).~ 100) ,~ 250),~ 100)'~ 250).~ 750).~

106-48-9 2505'8 250)'~ 100) .~ 250).~ 100) '~ 250)'~ 750) '8

126-99-8 650 650 300 650 300 650 4 500

1897-45-6 500 500 250 500 250 500 3 500

95-49-8 650j 650j 300j 650j 300j 650j 4 500j

106-43-4 650j 650j 300j 650j 300j 650j 4 500j

101-21-3 6 500 6 500 3 000 6 500 3 000 6 500 45 ooo" 2921-88-2 30 30 15 30 15 30 250

5598-13-0 300 300 150 300 150 300 2 500

64902-72-3 1 500 1 500 800 1 500 800 1 500 JO 000

1861-32-1 300 300 150 300 150 300 2 500

60238-56-4 25 25 15 25 15 25 200

218-01-9 400 400 200 400 200 400 4 500

74115-24-5 400 400 200 400 200 400 3 000

123-73-9 7.5 7.5 3.5 7.5 3.5 7.5 15

21725-46-2 15 15 8.5 15 8.5 15 40

460-19-5 30 30 15 30 15 30 250

87-84-3 600 600 300 600 300 600 1 500

108-94-1 150 0005 150 OOOJ 80 000

5 150 0005 80 oooj 150 000

5 1000000

5'4

110-83-8 1505

1505

805

1505

805

1505 1 000

108-91-8 6 500 6 500 3 000 6 500 3 000 6 500 45 ooo" 68359-37-5 800 800 400 800 400 800 6000

68085-85-8 150 150 80 150 80 150 1 000

Industrial (IL)

100 250

35 000)

20 000),~

20 000),~

4 500

3 500

4 500j

4 5003

45 ooo" 250

2 500

10 000

2 500

200

4 500

3 000

15

40

250

1 500

10000005'4

1 000

45 ooo" 6 000

1 000

'O s:.:i

(IQ ~

0\ -..)

0 ~

(.,.) -....]

I

COLUMN 1

Substance

cyperrnethrin cyromazine

dalapon

daminozide

demeton

diallate

diaminotoluene, 2,5-

diazinon

dibenz( a,h )anthracene

dibenzo( a,e )pyrene

dibenzofuran

dibenzothiophene

dibromo-3-chloropropane, 1,2-

dibromobenzene, 1,3-


dibromochloromethane

[DBCM)

dibromoethane, 1,2-

dibutyl phthalate [DBP)

dibutyltin

dicamba

dichloroacetic acid

dichlorobenzene, 1,2-

dichlorobenzene, 1,3

dichlorobenzene, 1,4

dichlorobenzidine, 3,3'-

dichlorodifluoromethane

dichlorodiphenyl sulfone, 4,4'-


GENERIC NUMERICAL SOIL STANDARDS TO PROTECT HUMAN HEALTH1'2

COLUMN 2 COLUMN 3 COLUMN 4 COLUMN 5 COLUMN 6 COLUMN7 COLUMN 8 COLUMN 9 COLUMN 10

I Chemical I I I I I Res;dentia; I I

Abstract Rtu::itii:mti;:il I s..v;ce I w;101ands I Wlldlands I I , --l_--

I

Number Natural Reverted Agricultural Urban Park 0

°v:"t High Density Commercial Industrial (CAS) (WL,.) (WLJ (AL) (PL) (~nL:t (RLHO) (CL) (IL)

52315-07-8 300 300 150 300 150 300 2 500 2 500

66215-27-8 250 250 100 250 100 250 2 000 2 000

75-99-0 900 900 450 900 450 900 7 000 7 000

1596-84-5 800 800 400 800 400 800 2 000 2 000

8065-48-3 1 I 0.6 1 0.6 I 9.5 9.5

2303-16-4 200 200 100 200 100 200 550 550

95-70-5 6.5 6.5 3 6.5 3 6.5 45 45

333-41-5 20 20 10 20 10 20 150 150

53-70-3 105,7 105,7 5),/ 105,7 55,7 10),/ 305,7 50

5"

192-65-4 1 1 0.6 I 0.6 1 2.5 2.5

132-64-9 30 30 15 30 15 30 250 250

132-65-0 300 300 150 300 150 300 2 500 2 500

96-12-8 4 4 2 4 2 4 40 40

108-36-1 10 10 6 10 6 10 95.l 95.l

106-37-6 300 300 150 300 150 300 2 500 2 500

124-48-1 150 150 85 150 85 150 400 400

106-93-4 7 7 3.5 7 3.5 7 15 15

84-74-2 8 5005

8 5005

4 0005

8 5005

4 0005

8 5005

25 0005

700 0005

14488-53-0 9 9 4.5 9 4.5 9 70 70

1918-00-9 900 900 450 900 450 900 7 000 7 000

79-43-6 100 100 60 100 60 100 650 650

95-50-1 7 5005

7 5005

3 5005 7 500) 3 500) 7 500

5 25 000) 650 000)

541-73-1 2 5005

2 5005

1 0005 2 500) 1 000) 2 500) 7 500) 200 000)

106-46-7 9 0005 9 000 4 500) 9 000) 4 500) 9 000) 30 000) 800 000)

91-94-1 30 30 15 30 15 30 75 75

75-71-8 6 500 6 500 3 000 6 500 3 000 6 500 45 000 45 000

80-07-9 25 25 15 25 15 25 200 200

"C !:»

(Jq ~

0\ 00

0 ......,

VJ -..)

I

COLUMN 1

Substance

dichloroethane, 1,1-


dichloroethylene, I, 1-

dichloroethylene, 1,2-cis-

dichloroethylene, 1,2-trans-

dichloromethane

dichlorophenol, 2,3-






dichlorophenoxy acetic acid, 2,4- (2,4-D]

dichlorophenoxy butyric acid,

2,4- [2,4-DB]

dichloropropane, 1,2-


dichloropropanol, 2,3-

dichloropropene, 1,3-

(cis +trans)

dichlorvos

dicrotophos

dicyclopentadiene

dieldrin

diethanolamine

SCHEDULE3.l-PART 2


COLUMN 2 COLUMN 3 COLUMN4 COLUMN 5 COLUMN 6 COLUMN? COLUMN 8 COLUMN9

Chemical Ah~trl'llr.t

I -- .-· 1 I I I I Mesldoot~ll . I I Service W1ldlands Wlldlands L Res1dent1al Number Natural Reverted Agricultural Urban Park

0 °~t High Density Commercial

(CAS) (WL.J (WLJ (AL) (PL) (~Ls~/ (RL"°) {CL)

75-34-3 15 000° 15 000° 8 500' 15 ooo' 8 500' 15 ooo' 50 000)

107-06-2 150) 150) 755 150

5 75° 150° 350°

75-35-4 4 000° 4 000° 2 ooo' 4 0005 2 000) 4 ooo' 15 000)

156-59-2 150° 150° 85° 150' 85) 150) 500)

156-60-5 1 500° I 500° 850) 1 500) 850) 1 500' 5 000)

75-09-2 500) 500) 250) 500) 250' soo' 1 soo'

576-24-9 250),lS 250),lS 1005,8 2505'8 100'·8 250' ·11 750°'8

120-83-2 250° 250° 100) 250' 100) 250° 750)

583-78-8 250J,O 250),0 100'·11 250'·11 100),lS 250),lS 750),lS

87-65-0 250°'0 250J,O 100'·8 250),lS 100),lS 250°'8 750°'8

95-77-2 250J,O 250°'0 100'·11 250' ·11 100),lS 250),lS 750°'0

591-35-5 250' ·11 250),lS 100°·11 250°'8 1005,M 250°'0 750J ,O

94-75-7 300 300 150 300 150 300 2 500

94-82-6 250 250 150 250 150 250 2 000

78-87-5 1 000) I 000) 6005

1 0005 600° 1 ooo' 3 500'

142-28-9 650j 650j 3003

6503 300j 650j 4 5ooj

616-23-9 90 90 45 90 45 90 700

542-75-6 2 500° 2 500° r ooo' 2 500° 1 000) 2 500) 7 500)

62-73-7 15 15 8 15 8 15 100 141-66-2 3 3 1.5 3 1.5 3 25

77-73-6 2 500 2 500 I 500 2 500 1 500 2 500 20 000

60-57-1 0.85 0.85 0.45 0.85 0.45 0.85 2

111-42-2 65 65 30 65 30 65 450

COLUMN 10

I Industrial

{IL)

> 1 000 mg/g)

350°

350 ooo'

15 000)

150 000°

40 ooo'

20 000),lS

20 000)

20 000),lS

20 000) ,lS

20 000°'8

20 000°·0

2 500

2 000

10 ooo'

4 50oj

700

200 000)

100

25

20 000

2

450

'O

~ n 0\ \0 0 ,_,.,

V.l -...J

I

COLUMN 1

Substance

diethyl ether

diethyl phthalate

diethyldithiocarbamate

diethylene glycol monobutyl

ether

diethylene glycol monoethyl

ether

diethylformamide

diflubenzuron

diisobutylene

dimethipin

dimethoate

dimethoxybenzidine, 3,3'-

dimethyl methylphosphonate

dimethylamino azobenzene, 4-

[DAB]

dimethylaniline, 2,4-

dimethylaniline, N,N-

[OMA)

dimethylbenz(a)anthracene,

7,12-

dimethylbenzidine, 3,3'-

dimethylformamide

dimethylhydrazine, I, 1-

dimethylphenol, 2,4-


dimethylphenol , 3,4-

dimethylterephthalate


GENERIC NUMERICAL SOIL ST AND ARDS TO PROTECT HUMAN HEAL TH1'

2

COLUMN 2 COLUMN 3 COLUMN 4 COLUMN 5 COLUMN6 COLUMN 7 COLUMN 8

I Chemical

Wlldlands I I I Res~dent;all nos~entra; Abstract

I se.,,ke Wild lands Number Natural Reverted Agricultural Urban Park De~~y High Density (CAS) (WL,J (WL.) (AL) (PL) (RLco) (RLH0 )

60-29-7 6 500j 6 500j 3 0005 6 500° 3 000

3 6 5003

84-66-2 25 000 25 000 15 000 25 000 15 000 25 000

392-74-5 10 10 5 10 5 IO

112-34-5 900 900 450 900 450 900

111-90-0 2 000 2 000 950 2 000 950 2 000

617-84-5 30 30 15 30 15 30

35367-38-5 650 650 300 650 300 650

25167-70-8 3003 300j 150j 300j 1505 300j

55290-64-7 650 650 300 650 300 650

60-51-5 6.5 6.5 3 6.5 3 6.5

119-90-4 8.5 8.5 4.5 8.5 4.5 8.5

756-79-6 2 000 2 000 950 2 000 950 2 000

60-11-7 3 3 1.5 3 1.5 3

95-68-1 65 65 30 65 30 65

121-69-7 65 65 30 65 30 65

57-97-6 0.02 0.02 0.02 0.02 0.02 0.02

119-93-7 1.5 1.5 0.65 1.5 0.65 1.5

68-12-2 3 000 3 000 I 500 3 000 I 500 3 000

57-14-7 3 3 1.5 3 1.5 3

105-67-9 1 500) 1 500) 850) 1 500) 850) 1 5005

576-26-1 50) 50) 25) 505 25) 50

5

95-65-8 85) 85) 40) 855

405

855

120-61-6 3 000 3 000 1 500 3 000 1 500 3 000

COLUMN 9 COLUMN 10

I Comme.cra1 I Industrial

(CL) (IL)

45 0003

'4

45 0003

'4

200 0004 200 0004

25 25

7 000 7 000

15 000 15 000

250 250

4 500 4 500

2 5003 2 500j

4 500 4 500

45 45

20 20

15 000 15 000

7 7

150 150

4505

4505

0.025 0.025

3 3

25 000 25 000

25 25

5 0005 150 000)

1505 4 000

5

2505

7 0005

25 0004

25 0004

'O s:.:i

()'q ('1)

-..J 0 0 ......,

VJ -..)

I

COLUMN 1

Substance

dinitrobenzene, 1,2-



dinitro-o-cyclohexyl phenol, 4,6-

dinitrophenol, 2,4-

dinitrotoluene, 2,4-


dinitrotoluene, 2-amino-4,6-


dinoseb

dioxane, 1,4-

diphenamid

diphenyl sulfone

diphenyl- J ,4-benzenediamine, N, N-diphenylamine

diquat (as dibromide)

Direct Black 38

Direct Blue 6

Direct Brown 95

disulfoton

diuron

dodine

endosulfan (I + II)

endothall

endrin

EPTC ethanol, 2-(2-methoxyethoxy)-


GENERIC NUMERICAL SOIL ST AND ARDS TO PROTECT HUMAN HEALTH1'

2

COLUMN 2 COLUMN 3 COLUMN 4 COLUMNS COLUMN 6 COLUMN 7 COLUMN 8 COLUMN 9 COLUMN 10

I Chemical

WHdlands I Wlldlands I I I R•~d-lall Resroeni~I I Abstract

I SeNlce

I Number Natural Reverted Agricultural Urban Park

0 °~ High Density Commercial Industrial

(CAS) (WL,J (WLJ (AL) (PL) (~nL:;v (RLHD) (CL) (IL)

528-29-0 3 3 1.5 3 1.5 3 25 25

99-65-0 3 3 1.5 3 1.5 3 25 25

J00-25-4 3 3 1.5 3 1.5 3 25 25

131-89-5 65 65 30 65 30 65 450 450

51-28-5 J505 150) 855 1505 855 1505 500

5 15 0005

12l- J4-2 45 45 20 45 20 45 100 JOO

606-20-2 9 9 4.5 9 4.5 9 20 20

35572-78-2 65 65 30 65 30 65 450 450

J9406-51-0 65 65 30 65 30 65 450 450

88-85-7 30 30 15 30 J5 30 250 250

123-91-1 150 150 70 J50 70 150 350 350

957-51-7 900 900 450 900 450 900 7 000 7 000

127-63-9 25 25 15 25 15 25 200 200

74-31-7 9 9 4.5 9 4.5 9 70 70

122-39-4 800 800 400 800 400 800 6 000 6 000

85-00-7 70 70 35 70 35 70 500 500

1937-37-7 2 2 1 2 I 2 4.5 4.5

2602-46-2 2 2 0.95 2 0.95 2 4.5 4.5

1607J-86-6 2 2 1 2 I 2 5 5

298-04-4 1 J 0.6 J 0.6 1 9.5 9.5

330-54-1 65 65 30 65 30 65 450 450

2439-10-3 100 JOO 60 100 60 100 950 950

l J5-29-7 5005 500) 250

5 500

5 250

5 500

5 1 500

5 40 000

5

145-73-3 650 650 300 650 300 650 4 500 4 500

72-20-8 9 9 4.5 9 4.5 9 70 70

759-94-4 800 800 400 800 400 800 6 000 6 000

111-77-3 1 000 I 000 600 1 000 600 1 000 9 500 9 500

'"O

~ (1)

-.J

0 ....,.,

VJ -.J

I

COLUMN 1

Substance

ethephon

ethion

ethoxyethanol acetate, 2-

ethoxyethanol, 2-

ethyl acetate

ethyl acrylate

ethylene cyanohydrin

ethylenediamine

ethylene thiourea

ethyleneimine

ethyl-p-nitrophenyl

benzenethionophosphonate

[EPN]

fenamiphos

fenpropathrin

fenvalerate

fluometuron

fluorene

fluoride

fluridone

flurprimidol

flusilazole

flutolanil

fluvalinate

folpet

fomesafen

fonofos

formaldehyde

formic acid



COLUMN 2 COLUMN 3 COLUMN 4 COLUMN 5 COLUMN 6 COLUMN7 COLUMN 8 COLUMN9

I Chemical

. I . I Abstract Residential I Se.,,;ce W•ldlands I Wddlands I Low I Res;de"';"; I I Number Natural Reverted Agricultural Urban Park Density

High Density Commercial (CAS) (WL,.) (WL.) (AL) (PL)

(RLLD) (RL"°) (CL)

16672-87-0 150 150 80 150 80 150 1 000

563-12-2 15 15 8 15 8 15 100

111-15-9 3 000 3 000 1 500 3 000 1 500 3 000 25 000

110-80-5 3 000 3 000 1500 3 000 1 500 3 000 20 000

141-78-6 30 000 30 000 15 000 30 000 15 000 30 000 200 000

140-88-5 150 150 80 150 80 150 l 000

109-78-4 2 000 2 000 1 000 2 000 1 000 2 000 15 000

107-15-3 3 000 3 000 1 500 3 000 1 500 3 000 20 0004

96-45-7 2.5 2.5 1.5 2.5 1.5 2.5 20

151-56-4 0.2 0.2 0.1 0.2 0.1 0.2 0.5

2104-64-5 0.3 0.3 0.15 0.3 0.15 0.3 2.5

22224-92-6 8 8 4 8 4 8 60

39515-41-8 800 800 400 800 400 800 6 000

51630-58-1 800 800 400 800 400 800 6 000

2164-17-2 400 400 200 400 200 400 3 000

86-73-7 I 000 I 000 600 1 000 600 1 000 9 500

16984-48-8 8 500) 8 500) 4 500) 8 500) 4 5005

8 5005

25 0005

59756-60-4 2 500 2 500 1 500 2 500 1 500 2 500 20 000

56425-91-3 650 650 300 650 300 650 4 500

85509-19-9 20 20 10 20 10 20 150

66332-96-5 2 000 2 000 950 2 000 950 2 000 15 000

69409-94-5 300 300 150 300 150 300 2 500

133-07-3 3 000 3 000 I 500 3 000 1 500 3 000 9 500

72178-02-0 75 75 35 75 35 75 150

944-22-9 65 65 30 65 30 65 450

50-00-0 6 500 6 500 3 000 6 500 3 000 6 500 45 000

64-18-6 30000 30 000 15 000 30 000 15 000 30 000 200 000

COLUMN10

I Industrial

(IL)

I 000

100

25 000

20 000

200 000

1 000

15 000

20 0004

20

0.5

2.5

60

6 000

6 000

3 000

9 500

750 000)

20 000

4 500

150

15 000

2 500

9 500

150

450

45 000

200 000

"Cl p:i

cro (1>

-..l N 0 .....,.,

V.l -.J

COLUMN 1

Substance

fosetyl

furan

furazolidone

furfural

furmecyclox

furothiazole

glufosinate

glycidaldehyde

glyphosate

guanidine

haloxyfop, methyl

HEPHs9

heptachlor

heptachlor epoxide

hexabromobenzene

hexabromobiphenyl, 2,2',4,4',5,5'-

hexachlorobenzene

hexachlorobutadiene

hexachlorocyclohexane, alpha-

hexachlorocyclohexane, beta-

hexachlorocyclohexane, gamma

hexachlorocyclopentadiene

hexachloroethane

hexachlorophene

hexahydro- l ,3,5-trinitro-1 ,3,5-

triazine [RDX]

hexamethylphosphor-amide


GENERIC NUMERICAL SOIL STANDARDS TO PROTECT HUMAN HEALTH1'

2

COLUMN 2 I COLUMN 3 I COLUMN 4 I COLUMN 5 I COLUMN 6 I COLUMN 7


15845-66-6

110-00-9

67-45-8

98-01-1

60568-05-0 531-82-8

53369-07-6

765-34-4

1071-83-6 113-00-8

69806-40-2

NA10

76-44-8

1024-57-3

87-82-1

59536-65-1

118-74-1

87-68-3

319-84-6

319-85-7

58-89-9

77-47-4

67-72-1

70-30-4

121-82-4

680-31-9

I

Wildlands I Natural (WL,J

90 0004

30

3.5

90

450

9

10

10

3 000

300

1.5

1 OOOTT

3

0.4

65

0.09

655

30

2

8

255

200

20

9

90

JO

Wild lands Reverted

(WLJ

90 0004

30

3.5

90

450

9

10

IO

3 000

300

1.5

1 00011

3

0.4

65

0.09

655

30

2

8

255

200

20

9

90

10

I I

. . Residential

Agricultural Urban Park I Lo~ I (AL) (PL) Density

(RL.,,)

45 0004

90 0004

45 0004

15 30 15

2 3.5 2

45 90 45

250 450 250

4.5 9 4.5

6 10 6

6 10 6

1 500 3 000 1 500

150 300 150

0.8 1.5 0.8

I 00012

1 000 12 1 000

13

1.5 3 1.5

0.2 0.4 0.2

30 65 30

0.045 0.09 0.045

35' 65' 35'

15 30 15

1 2 1

4 8 4

10' 25) 105

95 200 95

IO 20 10

4.5 9 4.5

45 90 45

6 10 6

COLUMN 8 COLUMN 9 I COLUMN 10

Rasklantic:;l I I High Density Commercial (RLH0) (CL)

90 0004

700 0004

30 250

3.5 8.5

90 700

450 1 000

9 20

10 95

10 95

3 000 25 000

300 2 500

1.5 10

1 ooou 5 000 12

3 7.5

0.4 3

65 450

0.09 0.2

655

2005

30 250

2 5

8 20

255 755

200 1 500

20 150

9 70

90 300

10 95

Industrial (IL)

700 0004

250

8.5

700

1 000 20

95

95

25 000

2 500

10

5 00012

7.5

3

450

0.2

4505

250

5

20

2505

1 500

150

70

300

95

'O

~ ~

-...J (.;.J

0 ......,

(.;.J

-...J

I

COLUMN 1

Substance

hexanone, 2-hexazinone

hexythiazox

hydramethylnon

hydrazine

hydroquinone

imazalil

imazaquin

imazethapyr

indeno( 1,2,3-cd)pyrene

iprodione

iron

isobutanol

isophorone

isopropalin

isopropanol

isopropylbenzene

isoxaben

lactofen

LEPHs14

linuron

lithium

malathion

malononitrile

mancozeb

maneb

mecoprop [MCPP]

merphos



COLUMN 2 COLUMN 3 COLUMN4 COLUMN 5 COLUMN 6 COLUMN 7 COLUMNS COLUMN9

I Chemical

_ I ~ . I Residential '"'---~- •. , Abstract

I Se<vice W"dlands I W"dlands I I I L I n=;u.o,;g, I I Number Natural Reverted Agricultural Urban Park 0

°~t High Density Commercial (CAS) (Wl,,) (WL,j (AL) (PL) (~n~~t (RLHO) (CL)

591-78-6 150 150 80 150 80 150 1 000 51235-04-2 1 000 1 000 500 1 000 500 I 000 8 000

78587-05-0 800 800 400 800 400 800 6 000

67485-29-4 9 9 4.5 9 4.5 9 70

302-01-2 4.5 4.5 2.5 4.5 2.5 4.5 10

123-31-9 250 250 100 250 100 250 550

35554-44-0 400 400 200 400 200 400 3000

81335-37-7 8 000 8 000 4 000 8 000 4 000 8 000 60 000

81335-77-5 8 000 8 000 4 000 8 000 4 000 8 000 60 000

193-39-5 95),/ 95), / 50), / 95),/ 50), / 95).i 300),/

36734-19-7 l 000 1 000 600 l 000 600 I 000 9 500

7439-89-6 35 000 35 000 35 000 35 000 35 000 35 000 150 000

78-83-1 9 oooj 9 000.l 4 500° 9 oooj 4 500° 9 oooj 10 oooj 78-59-1 6 500 6 500 3 000 6 500 3 000 6 500 35 000

33820-53-0 500 500 250 500 250 500 3 500

67-63-0 65 000 65 000 30 000 65 000 30 000 65 000 450 000

98-82-8 3 oooj 3 oooj 1 500J 3 oooj I 500J 3 000° 25 oooj 82558-50-7 1 500 1500 800 1 500 800 1 500 10 000

77501-63-4 65 65 30 65 30 65 450 NAIU 1 000

11 1 000

11 I 000

12 1 000

12 1 000 13

l 00013 2 000 12

330-55-2 65 65 30 65 30 65 450

7439-93-2 65 65 30 65 30 65 450

121-75-5 650 650 300 650 300 650 4 500

109-77-3 3 3 1.5 3 1.5 3 25

8018-01-7 900 900 450 900 450 900 7 000

12427-38-2 150 150 . 80 150 80 150 1 000

93-65-2 30 30 15 30 15 30 250

150-50-5 0.9 0.9 0.45 0.9 0.45 0.9 7

COLUMN 10

I Industrial

(IL)

l 000

8 000

6 000

70

10 550

3 000

60 0004

60 0004

500), /

9 500

150 0004

10 oooj 35 000

3 500

450 000

25 oooj 10 000

450

2 00012

450

450

4 500

25

7 000

I 000

250

7

'O ~

(JQ (1)

--i ~

0 ......,

VJ -.J

I

COLUMN 1

Substance

metalaxyl methacrylonitrile

methamidophos

methidathion

methomyl methoxy-5-nitroaniline, 2-

methoxychlor

methoxyethanol, 2-

methoxyethanol acetate, 2-

methyl acetate

methyl ethyl ketone [MEK]

methyl hydrazine

methyl mercury

methyl methacrylate

methyl tert-butyl ether [MTBE]

methyl-5-nitroaniline, 2-

methylaniline, 2-

methylaniline, 4-

methylcholanthrene, 3-

methylene-bis(2-chloroani 1 ine ), 4,4'-

methylene-bis(N, N-dimethyl) aniline, 4,4'-

methylenebisbenzenamine, 4,4'-

methylnaphthalene, I-

methylnaphthalene, 2-

methylphenol, 2-


GENERIC NUMERICAL SOIL ST AND ARDS TO PROTECT HUMAN HEALTH1' 2

COLUMN 2 COLUMN 3 COLUMN 4 COLUMN 5 COLUMN 6 COLUMN 7 COLUMNS COLUMN 9

Chemical Ah!';tr;ict

I s~~;c~ I WUdlandsl w;1dlands I I I """~"""""'I Res;dential I I Number Natural Reverted. Agricultural Urban Park De~;ty High Density Commercial (CAS) (WL") (WL0 ) (AL) (PL) (RLLD) (RL"0 ) (CL)

57837-19-1 2 000 2 000 950 2 000 950 2 000 15 000 126-98-7 3 3 1.5 3 1.5 3 25

10265-92-6 1.5 1.5 0.8 1.5 0.8 1.5 10

950-37-8 30 30 15 30 15 30 250

16752-77-5 800 800 400 800 400 800 6 000 99-59-2 300 300 150 300 150 300 650

72-43-5 150 150 80 150 80 150 I 000

109-86-4 150 150 80 150 80 150 I 000

110-49-6 250 250 150 250 150 250 2 000

79-20-9 30 oooj 30 oooj 15 oooj 30 0003

15 0003 30 0003 250 0003

' q

78-93-3 20 000 20 000 9 500 20 000 9 500 20 000 150 000

60-34-4 30 30 15 30 15 30 250

22967-92-6 3 3 1.5 3 1.5 3 25

80-62-6 45 oooj 45 0003 20 oooj 45 0003 20 0003

45 0003 300 0003

1634-04-4 8 000 8 000 4 000 8 000 4 000 8 000 20 000

99-55-8 650 650 300 650 300 650 3 500

95-53-4 20 20 10 20 10 20 50

106-49-0 100 100 60 100 60 100 950

56-49-5 0.15 0.15 0.07 0.15 0.07 0.15 1.5

101-14-4 30 30 15 30 15 30 350

101-61-1 300 300 150 300 150 300 700

101-77-9 8.5 8.5 4.5 8.5 4.5 8.5 20

90-12-0 500 500 250 500 250 500 1 000

91-57-6 100 100 60 100 60 100 950

95-48-7 4 000) 4 000) 2000) 4 000) 2 0005 4 000

5 15 0005

COLUMN 10

I Industrial

(IL)

15 000 25

10

250

6 000 650

I 000

1 000

20 00

250 0003'4

150 OOO.l'4

250

25

300 0003

20 000

3 500

50

950

1.5

350

700

20

I 000

950

350 0005

"O ll:>

oq (l>

-J VI

0 ......., ........ \.;.) -..)

I

COLUMN 1

Substance

methylphenol, 3-

methylphenol, 4-

methylphenol, 4-chloro-3-

methylstyrene, alpha-

metolachlor

metribuzin

metsulfuron-methyl

mirex

molinate

monomethylarsonic acid

methylaniline, N-

myclobutanil

naled

naphthylamine, 2-

napropamide

nitrate (as N)

nitrite (as N)

nitroaniline, 2-

nitroaniline, 4-

nitrobenzene

nitrofurazone

nitroglycerin

nitroguanidine

nitrophenol , 2-

nitrophenol, 4-

nitropyrene, 4-

nitrosodiethanolamine, N-



2

COLUMN 2 COLUMN 3 COLUMN 4 COLUMN 5 COLUMNS COLUMN7 COLUMN 8 COLUMN9

I Chemical

I _ _ ___ _ _ I Residential .,, ..... ~· , Abstract

I Se"'ice Wlldlanas I wna~n•s I I I L I ne5'uen.••· 1 I Number Natural Reverted Agricultural Urban Park De~;ty High Density Commercial (CAS) (WLJ (WLJ (AL) (PL) (RL'°) (RLtt0 ) (CL)

108-39-4 4 ooo' 4 ooo' 2 ooo' 4 0005 2 000) 4 ooo' 15 000)

I 06-44-5 400) 400) 200) 400) 200) 400' I 500'

59-50-7 3 000 3 000 I 500 3 000 1 500 3 000 25 000

98-83-9 2 oooj 2 0003

1 0003 2 000

3 1 0003 2 000° 15 000

3

51218-45-2 5 000 5 000 2 500 5 000 2 500 5 000 35 000

21087-64-9 800 800 400 800 400 800 6 000

74223-64-6 8 000 8 000 4 000 8 000 4 000 8 000 60 0004

2385-85-5 0.8 0.8 0.4 0.8 0.4 0.8 2

2212-67-1 65 65 30 65 30 65 450

124-58-3 300 300 150 300 150 300 2 500

100-61-8 65 65 30 65 30 65 450

88671-89-0 800 800 400 800 400 800 6 000

300-76-5 65 65 30 65 30 65 450

91-59-8 8 8 4 8 4 8 20

15299-99-7 3 000 3 000 1 500 3 000 1 500 3 000 25 000

14797-55-8 50 0004

50 0004

25 ooo" 50 0004

25 0004

50 0004

400 0004

14797-65-0 3 000 3 000 1 500 3 000 I 500 3 000 25 0004

88-74-4 300 300 150 300 150 300 2 500

100-01-6 100 100 60 100 60 100 950

98-95-3 65 65 30 65 30 65 450

59-87-0 10 10 5.5 10 5.5 10 25

55-63-0 3 3 LS 3 1.5 3 25

556-88-7 3 000 3 000 1 500 3 000 I 500 3 000 25 000

88-75-5 212 21 2 0-112 212 1'.l 21.l 101.l

100-02-7 21.l 2'.l 0.11.l 21.l 1'.l 2'.l JOIL

57835-92-4 10 10 6 10 6 10 25

1116-54-7 5 5 2.5 5 2.5 5 10

COLUMN 10

I Industrial

(IL)

350 0005

35 000)

25 000

15 0003

35 000

6 000

60 0004

2

450

2 500

450

6 000

450

20

25 000

400 0004

25 0004

2 500

950

450

25

25

25 000 10'.l

10' .l

25

10

'O i:l:l

(IQ (I)

-..J 0\ 0 ......,

VJ -..J

I

COLUMN 1

Substance

nitrosodiethylamine, N-[NDEA]

nitrosodimethylamine, N-[NDMA]

nitroso-di-N-butylamine, N-

nitroso-di-N-propylamine, N-

nitrosodiphenylamine, N-

nitrosomethylethylamine, N-

nitrosomorpholine, N-

nitrosopiperidine, N-

nitrosopyrrolidine, N-

nitrotoluene, 2-

nitrotoluene, 3-

nitrotoluene, 4-

nonane, n-

nonaqueous phase liquids!)

norflurazon

octahydro-1,3,5,7-tetranitro-1,3,5,7-tetrazocine [HMX]

octamethylpyrophosphoramide [OMPA]

octyl phthalate, di-n- [DNOP]

odorous substances 10

oryzalin

oxadiazon

oxamyl

oxyfluorfen

paclobutrazol

paraquat (as dichloride)


GENERIC NUMERICAL SOIL ST AND ARDS TO PROTECT HUMAN HEALTH1' 2

COLUMN 2 COLUMN 3 COLUMN 4 COLUMNS COLUMN6 COLUMN7 COLUMN 8 COLUMN9 COLUMN 10

I Chemical

w;ldlands I w;ldlands I I I Ros~dentlall tt05;aen1;•; I Abstract

I s. .. ;.,. Number Natural Reverted Agricultural Urban Park De~;ty High Density Commercial Industrial (CAS) (WLJ (WL.) (AL) (PL) (RLLD) (RL"0 ) (CL) (IL)

55-18-5 0.02 0.02 0.01 0.02 0.01 0.02 0.2 0.2

62-75-9 0.06 0.06 0.03 0.06 0.03 0.06 0.65 0.65

924-16-3 2.5 2.5 1.5 2.5 1.5 2.5 6 6 621-64-7 2 2 1 2 1 2 4.5 4.5 86-30-6 3 000 3 000 1 500 3 000 l 500 3 000 6 500 6 500

10595-95-6 0.65 0.65 0.3 0.65 0.3 0.65 1.5 1.5

59-89-2 2 2 l 2 l 2 5 5

100-75-4 1.5 1.5 0.75 1.5 0.75 1.5 3.5 3.5

930-55-2 6.5 6.5 3.5 6.5 3.5 6.5 15 15

88-72-2 30 30 15 30 15 30 150 150

99-08-1 3 3 1.5 3 1.5 3 25 25

99-99-0 100 100 60 100 60 100 950 950

111-84-2 9j 9j 4.5j 9j 4.5j 9j 703

703

NAIU not present not present not present not present not present not present not present not present

27314-13-2 1 000 I 000 600 I 000 600 1 000 9 500 9 500

2691-41-0 I 500 l 500 800 I 500 800 l 500 10 000 10 000

152-16-9 65 65 30 65 30 65 450 450

117-84-0 300 300 150 300 150 300 2 500 2 500 NAIU not present not present not present not present not present not present not present not present

19044-88-3 1 500 1 500 800 1 500 800 1500 10 000 10 000

19666-30-9 150 150 80 150 80 150 1 000 1 000

23135-22-0 800 800 400 800 400 800 6 000 6 000

42874-03-3 90 90 45 90 45 90 700 700

76738-62-0 400 400 200 400 200 400 3 000 3 000

1910-42-5 150 150 70 150 70 150 1 000 l 000

'O

~ (1)

-.J -.J 0 ......,

\.;.)

-.J

I

COLUMN 1

Substance

parathion parathion methyl

pebulate

pendimethalin

pentachlorobenzene, 1,2,3,4,5-

pentachloroethane

pentachloronitrobenzene

[PCNB)

pentaerythritol tetranitrate fPETNl perchlorate

perfluorobutane sulfonate [PFBS)

permethrin (cis +trans)

phenanthrene

phenmedipham

phenol, 2-methyl-4,6-dinitro-

phenothiazine

phenylenediamine, m- [MPD]

phenylenediamine, o- [OPD]

phenylenediamine, p- [PPD]

phenylphenol, 2-

phorate

phosmet

phthalic acid, p-

picloram

picramic acid

picric acid



COLUMN 2 COLUMN3 COLUMN 4 COLUMN 5 COLUMN 6 COLUMN7 COLUMNS COLUMN 9 COLUMN 10

I Chemical I I I ~--'J--~J I I

I

Abstract

I s~;,,;.,. w;1dlands I w;ldlands I I n0>•o•u•~•1 Res;dential I I Number Natural Reverted Agricultural Urban Park 0 Lo~t High Density Commercial Industrial

(CAS) (WL.) (WLJ (AL) (PL) ensi y (RL ) (CL) (IL) (RLLD) HO

56-38-2 200 200 95 200 95 200 1 500 1 500 298-00-0 8 8 4 8 4 8 60 60

1114-71-2 1 500 1 500 800 1 500 800 1 500 10 000 10 000

40487-42-1 1 000 1 000 600 I 000 600 1 000 9 500 9 500

608-93-5 65' 65' 35' 655 35' 65

5 2005 5 5005

76-01-7 150 150 75 150 75 150 350 350

82-68-8 55 55 25 55 25 55 150 150

78-11-5 65 65 30 65 30 65 450 450

14797-73-0 20 20 10 20 10 20 150 150

375-73-5 650 650 300 650 300 650 4 500 4 500

52645-53-1 1 500 I 500 800 I 500 800 1 500 10 000 10 000

85-01-8 3 500' 3 500' 1 500' 3 500' I 5005 3 500' 10 000

5 300 ooo'

13684-63-4 8 000 8 000 4 000 8 000 4 000 8 000 60 000 60 0004

534-52-1 2.5 2.5 1.5 2.5 1.5 2.5 20 20

92-84-2 15 15 8 15 8 15 100 100

108-45-2 200 200 95 200 95 200 I 500 1 500

95-54-5 300 300 150 300 150 300 700 700

106-50-3 6 000 6 000 3 000 6 000 3000 6 000 45 000 45 000

90-43-7 7 000 7 000 3 500 7 000 3 500 7 000 15 000 15 000

298-02-2 6.5 6.5 3 6.5 3 6.5 45 45

732-11-6 650 650 300 650 300 650 4 500 4 500

100-21-0 30 000 30 000 15 000 30 000 15 000 30 000 250 0004 250 000

4

1918-02-1 2 000 2 000 1 000 2 000 l 000 2 000 15 000 15 000

96-91-3 3 3 1.5 3 1.5 3 25 25

88-89-1 30 30 15 30 15 30 200 200

'O

~ (l>

-..) 00

0 ......,

UJ -..)

I

COLUMN 1

Substance

pirimiphos- methyl prochloraz

protluralin

prometon

prometryn propachlor

propanil

propargite

propargyl alcohol

propazine

prop ham

propiconazole

propylbenzene, 1-

propylene glycol monomethyl

ether

propylene oxide

propyzamide

pyrene

pyridine

quinalphos

quinoline

quizalofop-ethyl

resmethrin

ronnel

rotenone

selenious acid

sethoxydim

silver



2

COLUMN 2 COLUMN 3 COLUMN 4 COLUMN 5 COLUMNS COLUMN? COLUMN 8

I Chemical I I I I ___ ,, __ J Ah~tract

I~~ Wildlands Wildlands nt:~~u~uua• Residential

Natu<al Reverted I Ag,;cultu<al I U•ban Pa"' I 0e.:.y I High Density (WL.J (WLJ (AL) (PL) (ALLI>) (RLH0 )

29232-93-7 300 300 150 300 150 300

67747-09-5 90 90 45 90 45 90

26399-36-0 200 200 95 200 95 200

1610-18-0 500 500 250 500 250 500

7287-19-6 100 100 60 100 60 100 1918-16-7 400 400 200 400 200 400

709-98-8 150 150 80 150 80 150

2312-35-8 650 650 300 650 300 650

107-19-7 65 65 30 65 30 65

139-40-2 650 650 300 650 300 650

122-42-9 650 650 300 650 300 650

60207-90-1 400 400 200 400 200 400

103-65-1 3 0003

3 0003 1 500

3 3 oooj I 5003 3 0003

107-98-2 20 0003'4 20 0003

'4 10 000

3'4

20 0003'4

10 0003'4 20 0003

'4

75-56-9 60 60 30 60 30 60

23950-58-5 2 500 2 500 l 000 2 500 l 000 2 500

129-00-0 2 500) 2 5005 l 000) 2 500) l 000) 2 500)

110-86-1 30 30 15 30 15 30

13593-03-8 15 15 8 15 8 15

91-22-5 4.5 4.5 2.5 4.5 2.5 4.5

76578-14-8 300 300 150 300 150 300

10453-86-8 900 900 450 900 450 900

299-84-3 1 500 1 500 800 1 500 800 1 500

83-79-4 100 100 60 100 60 100

7783-00-8 150 150 80 150 80 150

74051-80-2 3 000 3 000 1 500 3 000 1 500 3 000

7440-22-4 4005 400) 200

5 400

5 200

5 400)

COLUMN 9 COLUMN 10

I I Comme<c;al I

(CL) lndust"al I

(IL)

2 500 2 500 200 200

I 500 I 500

3 500 3 500

950 950

3 000 3 000

1 000 I 000

4 500 4 500

450 450

4 500 4 500

4 500 4 500

3 000 3 000

25 0003 25 0003

150 0003'4

150 0003'4

150 150

20 000 20 000

7 500) 200 000)

250 250

100 100

10 10

2 000 2 000

7 000 7 000

10 000 10 000

950 950

I 000 1 000

20 000 20 000

1 500) 35 000)

'O

~ (0

-.) \0 0 .....,

VJ -....J

I COLUMN 1

Substance

silvex simazine

strontium

strychnine

styrene

styrene-acrylonitrile [SAN]

trimer (all isomers)

sulfotep

sulfur, elemental

TCMTB

tebuthiuron

temephos

terbacil

terbufos

terbutryn

tetrachlorobenzene, 1,2,3,4-



tetrachloroethane, 1, 1, 1,2-

tetrachloroethane, I , 1,2,2-

tetrachlorophenol, 2,3,4,5-


tetrachlorophenol, 2,3,5,6

tetrachlorovinphos

tetraethyl lead

tetrahydrofuran

tetryl

thallium



2

I COLUMN 2 I COLUMN 3 I COLUMN 4 I COLUMN 5 I COLUMN 6 I COLUMN 7

Service Number (CAS)

93-72-1 122-34-9

7440-24-6

57-24-9

100-42-5

NA11

3689-24-5

7704-34-9

21564-17-0

34014-18-1

3383-96-8

5902-51-2

13071-79-9

886-50-0

634-66-2

634-90-2

95-94-3

630-20-6

79-34-5

4901-51-3

58-90-2

935-95-5

961-11-5

78-00-2

109-99-9

479-45-8

7440-28-0

I I Ri:>~irli:>nti::il I

Wildlands I Wildlands I I I Natural Reverted Agricultural Urban Park (WLJ (WL") (AL) (PL)

Low Density (RLLD)

250 250 150 250 150 100 100 60 100 60

20 000 20 000 9 500 20 000 9 500

9 9 4.5 9 4.5

15 ooo' 15 ooo' 8 500' 15 ooo' 8 500'

90 90 45 90 45

15 15 8 15 8

2 000

900 900 450 900 450

2 000 2 000 I 000 2 000 1 000

650 650 300 650 300

400 400 200 400 200

0.8 0.8 0.4 0.8 0.4

30 30 15 30 15

300' 300' 150' 300' 150'

40' 40' 20' 40' 20'

9 9 4.5 9 4.5

550 550 250 550 250

70 70 35 70 35

250' 250' 100' 250' 100'

2 500' 2 500' 1 ooo' 2 500' 1 ooo' 250' 250' 100' 250' 100'

600 600 300 600 300

0.003 0.003 0.0015 0.003 0.0015

30 000 30 000 15 000 30 000 15 000

65 65 30 65 30

21L

COLUMN 8 COLUMN9

---•I ··-·

I nt:,,.1uern1a1 I I

High Density Commercial (RLH0 ) (CL)

250 2 000 100 250

20 000 150 0004

9 70

15 ooo' 50 ooo' 90 700

15 100

900 7000

2 000 15 000

650 4 500

400 3 000

0.8 6 30 250

300' 850'

40' 150'

9 70

550 l 500

70 150

250' 750'

2 5005 7 500'

250' 750'

600 1 500

0.003 0.025

30 000 200 000

65 450

COLUMN10

Industrial (IL)

2 000

250

150 ooo" 70

> 1 000 mglg'

700

100

7000

15 000

4 500

3 000

6 250

25 ooo' 3 500'

70

1 500

150

20 ooo' 200 ooo' 20 000

5

1 500

0.025

200 000

450

'O ~

oq (1)

CXl 0 0 ......,

(.;.) -..)

I

COLUMN 1

Substance

thifensulfuron-methyl thiobencarb

thiocyanate

thiodiglycol

thiofanox thiophanate- methyl

thiophenol

thiram

tin

toxaphene (all isomers)

tralomethrin

triadimefon

triallate

triasulfuron

tribenuron-methyl

tribromobenzene, 1,2,4-

tribufos

tributyl phosphate

tributyltin

trichloro-1 ,2,2-trifluoroethane,

1,1,2-

trichloroacetic acid

trichloroaniline, 2,4,6-

trichlorobenzene, 1,2,3-



trichloroethane, 1, 1, I-

trichloroethane, I, 1,2-



2

COLUMN 2 COLUMN 3 COLUMN 4 COLUMN 5 COLUMN 6 COLUMN 7 COLUMN 8 COLUMN 9

Chemical I I I I I rl I Abstract Rociti<>nti::il _ _ _ _ __

s..,,;ce I WHdlands I w;ldlands I I 1 ··--c-- ·-1 Hesoaenua• I I Number Natural Reverted Agricultural Urban Park 0

°~t High Density Commercial (CAS) (WL,.) (WLR) (AL) (PL) (~:s~t (RLHO) (CL)

79277-27-3 400 400 200 400 200 400 3 000 28249-77-6 300 300 150 300 150 300 2 500

302-04-5 6.5 6.5 3 6.5 3 6.5 45

111-48-8 2 000 2 000 I 000 2 000 1 000 2 000 15 000

39196-18-4 9 9 4.5 9 4.5 9 70 23564-05-8 2 500 2 500 I 500 2 500 1 500 2 500 20000

108-98-5 30 30 15 30 15 30 250 137-26-8 150 150 80 150 80 150 I 000

7440-31-5 50 0005

50 ooo' 25 ooo' 50 ooo' 25 ooo' 50 ooo' 150 0005

8001-35-2 15 15 6.5 15 6.5 15 30

66841-25-6 250 250 100 250 100 250 2 000

43121-43-3 900 900 450 900 450 900 7 000

2303-17-5 400 400 200 400 200 400 3 000

82097-50-5 300 300 150 300 150 300 2 500

101200-48-0 250 250 150 250 150 250 2 000

615-54-3 150 150 80 150 80 150 1 000

78-48-8 0.9 0.9 0.45 0.9 0.45 0.9 7

126-73-8 300 300 150 300 150 300 2 500

36643-28-4 9 9 4.5 9 4.5 9 70

76-13-1 900 0005 900 000.l 450 000.l 900 000

5 450 000.l 900 000° > 1 000 mg!g3

76-03-9 200 200 100 200 100 200 450

634-93-5 0.9 0.9 0.45 0.9 0.45 0.9 7

87-61-6 100' 100' 60' 100' 60' 100' 400'

120-82-1 850' 850' 400' 850' 400' 850' 2 soo'

108-70-3 650' 650' 350' 650' 350' 650' 2 ooo'

71-55-6 150 ooo' 150 ooo' 85 ooo' 150 ooo' 85 ooo' 1so ooo' 500 ooo'

79-00-5 350' 350' ISO' 350' 150' 350' 1 ooo'

COLUMN 10

I Industrial

(IL)

3 000 2 500

45

15 000

70

20 000

250

1 000

> 1 000 mg!g5

30

2 000

7 000

3 000

2 500

2 000

1 000

7

2 500

70

> 1 000 mglg°

450

7

10 ooo'

70 ooo'

55 ooo'

> I 000 mg!g'

30 ooo'

"O !:>)

Otl ~

00 >-'

0 .......,

VJ -..I

I

COLUMN 1

Substance

trichlorofluoromethane

trichlorophenol, 2,3,4-






trichlorophenoxyacetic acid, 2,4,5- [2,4,5-T]

trichloropropane, 1,1,2-


trichloropropene, 1,2,3-

tricresyl phosphate [TCP]

tridiphane

triethylene glycol

trifluralin

trimethyl phosphate

trimethylbenzene, 1,3,5-

trinitrobenzene, 1,3,5-

trinitrotoluene, 2,4,6-

tris( 1,3-dichloro-2-propyl)

phosphate [TDCPP]

tris( l-chloro-2-propyl)phosphate [TCPP]

tris(2,3-dibromopropyl)

phosphate

tris(2-chloroethyl)phosphate [TCEP]


GENERIC NUMERICAL Son, STANDARDS TO PROTECT HUMAN HEALTH1' 2

COLUMN 2 COLUMN3 COLUMN 4 COLUMNS COLUMNS COLUMN7 COLUMNS

I Chemical I WUdlands I I I Res~denUal I Residenlial

Abstract

I Sen<ice I Wlldlands Number Natural Reverted Agricultural Urban Park

0 °~t . High Density

(CAS) (WL.) (WLJ (AL) (PL) ensr y (RL ) (RLLD) HO

75-69-4 9 0003

9 0003 4 500

3 9 0003

4 5003 9 000

3

15950-66-0 35'·1' 35'·1/ 40'· 1

' 85),l / 40' ·1

' 35'· 1'

933-78-8 855,17 85' ' 1 1 405, 17 855,17 405, 17 85),17

933-75-5 855,17 855,17 405,11 855,17 405,11 85),l/

95-95-4 8 500) 8 5005 4 000) 8 500

5 4 000) s 500'

88-06-2 85' 855 40

5 85' 405

855

609-19-8 855,17 855' 11 40'· 1'

85),17 405, 17 85),11

93-76-5 300 300 150 300 150 300

598-77-6 150 150 80 150 80 150

96-18-4 0.1 0.1 0.05 0.1 0.05 0.1

96-19-5 90 90 45 90 45 90

1330-78-5 650 650 300 650 300 650

58138-08-2 90 90 45 90 45 90

112-27-6 65 0004

65 0004

30 0004

65 ooo" 30 ooo" 65 ooo" 1582-09-8 250 250 100 250 100 250

512-56-1 300 300 150 300 150 300

108-67-8 300,; 300j 150,; 300j 150j 300,;

99-35-4 900 900 450 900 450 900

118-96-7 15 15 8 15 8 15

13674-87-8 650 650 300 650 300 650

13674-84-5 300 300 150 300 150 300

126-72-7 6 6 3 6 3 6

115-96-8 200 200 100 200 100 200

COLUMN 9 COLUMN 10

I Commercial Industrial

(CL) (IL)

70 0003'4 70 0005

'4

250),l/ 7 000'·1

'

250'· 11 7 000)'17

2505,11 7 000),l/

25 ooo' 700 000)

250' 7 ooo' 2505,17 7 000), l /

2 500 2 500

l 000 l 000

1 l

700 700

4 500 4 500

700 700

450 0004

450 ooo" 2 000 2 000

l 500 1 500

2 500,; 2 500°

7 000 7 000

100 100

4 500 4 500

2 500 2 500

15 15

1 500 1 500

"d

~ (1)

00 N 0 ....., (.;.)

-.I



COLUMN 1 COLUMN 2 COLUMN3 COLUMN 4 COLUMNS COLUMNS COLUMN7 COLUMN 8 COLUMN 9 COLUMN 10

I

Chemical

Wildlands I Wildlands I I I Res~dentiall R•sideotidi I Abstract Service Number Natu,al Reverted Ag,icullural Urt>an Pa'k 0 °~ High Density Comme<eiall Industrial

Substance (CAS) (WLJ (WLJ (AL) (PL) (~nLs~;y (RLHD) (CL) (IL)

tris(2-ethylhexyl)phosphate 78-42-2 3 000 3 000 1 500 3 000 1 500 3 000 10 000 10 000 tungsten 7440-33-7 25 25 15 25 IS 25 200 200 vemolate 1929-77-7 30 30 15 30 15 30 250 250 vinclozolin 50471-44-8 800 800 400 800 400 800 6 000 6 000 vinyl acetate 108-05-4 30 000 30 000 15 000 30 000 15 000 30 000 250 000:; 250 000

3

vinyl chloride 75-01-4 2 2 0.95 2 0.95 2 45 45

VPHs 1 ~ NAw 20011 20011

200 12 20012

20010 200u 200 12

20012

warfarin 81-81-2 9 9 4.5 9 4.5 9 70 70 zineb 12122-67-7 1500 1 500 800 I 500 800 1500 10 000 IO 000

Notes I All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as

updated from time to time, a director' s protocol or alternate methods acceptable to a director. · 2 Standards are based on the 2015 United States (US) Environmental Protection Agency (EPA) "Regional Screening Levels" for soil ingestion. The EPA Regional

Screening Levels for non-carcinogentic substances are adjusted to reflect the 1996 "Overview ofCSST Procedures for the Derivation of Soil Quality Matrix Standards for Contaminated Sites" Soil Allocation Factor (SAF = 0.2) and for carcinogenic substances, a human lifetime cancer risk of less than or equal to one in 100 000, in accordance with section 18 (3) of this regulation, unless otherwise noted. The high density residential land use standards of this schedule assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children' s playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

3 Standard is based on the US EPA Regional Ingestion Screening Level saturation limit for the substance in soil. 4 Standard is based on the US EPA Regional Ingestion Screening Level ceiling limit for the substance in soil. 5 Standard is derived in accordance with Protocol 28 " 2016 Standards Derivation Methods". 6 Standard is not derived based on the toxicology of the substance. Standard is based on the Hazardous Waste Regulation, B.C. Reg. 63/88, definition for waste asbestos.

Note that I% by weight is equivalent to l 0 000 µgig . 7 Standard represents a "Benzo(a)Pyrene Toxicity Equivalent Quotient (BaP TEQ)". Standard is set equal to the corresponding land use, Human Health Protection -

Intake of contaminated soil, matrix soil standard for benzo(a)pyrene divided by the the 1998 World Health Organization "Benzo(a)Pyrene Toxicity Equivalent Factor (BaP TEF)" for the substance. The sum of the concentrations of: benz(a)anthracene, benzo(b+j)fluoranthenes, benzo(k)fluoranthene, dibenzo(a,h)anthracene, and indeno(l ,2,3-cd)pyrene in soil, multiplied by each substance' s respective 1998 World Health Organization "BaP TEF" must not exceed the corresponding land use, Human Health Protection - Intake of contaminated soil , matrix soil standard for benzo(a)pyrene. Consult a director for further advice.

8 Standard is derived using either the respective 2001 Rijks Instituut voor Volksgezondheid en Milieu (RIVM) Tolerable Daily Intake (TOI) for monochlorophenols (total) or dichlorophenols (total). The sum of the concentrations in soil, of monochlorophenol or dichlorophenol (all isomers) substances prescribed in this schedule must not exceed the standard. Consult a director for further advice.

9 HEPHs - Heavy Extractable Petroleum Hydrocarbons in soil, as defined in 2015 British Columbia Environmental Laboratory Manual, as updated from time to time.

I

"Cl

~ (t)

00 VJ

0 ......, ..... VJ -....J

10 NA- not applicable. No CAS number exists for the substance. 11 Standard is set equal to the Urban Park (PL) land use soil standard for the substance in Schedule 4 of this regulation, as it was before the repeal of that schedule. 12 Standard is set equal to the corresponding land use soil standard for the substance in Schedule 4 of this regulation, as it was before the repeal of that schedule. 13 Standard has been set to equal the Residential (RL) land use soil standard for the substance in Schedule 4 of this regulation, as it was before the repeal of that schedule. 14 LEPHs - Light Extractable Petroleum Hydrocarbons in soil, as defined in 2015 British Columbia Environmental Laboratory Manual, as updated from time to time. 15 Soil must be remediated so that nonaqueous phase liquids are not present in quantities in excess of that acceptable to a director. 16 Soil must be remediated so that odorous substances are not present in quantities in excess of that acceptable to a director. 17 Standard has been set equal to the standard for 2,4,6-trichlorophenol. 18 VPHs - Volatile Petroleum Hydrocarbons in soil, as defined in the 2015 British Columbia Environmental Laboratory Manual, as updated from time to time.

"O i:.>

(Jq ('!>

00 ~

0 .......,

(.;.)

-J

COLUMN 1

Substance

acenaphthene acephate

acetic acid, 2-methyl-4-

chlorophenoxy- [MCP A]

acetochlor

acetone

acetophenone

acrolein

acrylamide

acrylic acid

acrylonitrile

adipic acid

alachlor

aldicarb

aldicarb sulfone

aldrin

ally! alcohol

ally! chloride

aluminum

ametryn

aminobiphenyl, 4-

aminophenol, 3-

aminophenol, 4-

amitraz

aniline

anthraquinone, 9, I 0-

antimony

aramite

asbestos


GENERIC NUMERICAL Son. ST AND ARDS TO PROTECT ECOLOGICAL HEALTH'·:

COLUMN 2 I COLUMN 3 I COLUMN 4 I COLUMN 5 I COLUMN 6


83-32-9 30560-19-1

94-74-6

34256-82-1 67-64-1

98-86-2

107-02-8

79-06-1

79-10-7

107-13-1

124-04-9

15972-60-8

116-06-3

1646-88-4

309-00-2

107-18-6

107-05-1

7429-90-5

834-12-8

92-67-1

591-27-5

123-30-8

33089-61 -1

62-53-3

84-65-1

7440-36-0

140-57-8

1332-21-4

Wildlands

Natural3

lWL,) ... NS NS NS

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 15

NS NS

Wildlands

Reverted3

CWL) n-

NS NS NS


NS NS

I Agricultural

4 I (AL)

NS NS NS


NS NS

Urban Park4

(PL)

NS NS NS


NS NS

COLUMN7 COLUMN 8 I COLUMN 9 I COLUMN 10

I Residential I Residential I I

Low Density5

High Density6

. Commercial4

(Rt,_0 ) . (R~0) (CL)

NS NS NS NS NS NS NS NS NS

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 20 40 40

NS NS NS NS NS NS

lndustrial4

(IL)

NS NS NS


NS NS

"O P:>

(1q (D

00 Vl

g, l>J -....)

I

COLUMN 1

Substance

I asulam

atrazine

auramine

avermectin B 1 (a+ b)

azinphos-methyl

azobenzene

azodicarbonamide

benfluralin

benomyl

bensulfuron-methyl

bentazon

benz(a)anthracene

benzidine


benzo(k)fluoranthene

benzoic acid

benzotrichloride

benzyl alcohol

benzyl chloride

bifenox

bifenthrin

biphenyl, 1,1'-


bis(2-chloro- l-methylethyl) ether

bis(2-ethylhexyl) adipate bis(2-ethylhexyl) phthalate

[DEHP]



GENERIC NUMERICAL SOIL STANDARDS TO PROTECT ECOLOGICAL HEALTH1'2

COLUMN 2 COLUMN 3 COLUMN 4 COLUMN 5 COLUMN 6 COLUMN 7 COLUMN 8 COLUMN 9 COLUMN 10

Chemical I I I I I I I I Abmract I Wildlands

WUdloods I I I Ros;dooU" I Ros;dootraJ I I Service Natural

3 Reverted

3 Agricultural

4 Urban Park

4 Low Densit/ High Densit/ Commercial

4 lodostrial' I

Number (WLR) (AL) (PL) (RL,_o) (R'-tto) (CL) (IL)

(CAS) (Wl,J

3337-71-1 NS NS NS NS NS NS NS NS 1912-24-9 NS NS NS NS NS NS NS NS 492-80-8 NS NS NS NS NS NS NS NS

71751-41-2 NS NS NS NS NS NS NS NS 86-50-0 NS NS NS NS NS NS NS NS 103-33-3 NS NS NS NS NS NS NS NS 123-77-3 NS NS NS NS NS NS NS NS


56-55-3 0.65 1 0.1 1 1 10 10 10

92-87-5 NS NS NS NS NS NS NS NS 205-99-2 0.65 1 0.1 l 1 10 10 10

& 205-82-3

207-08-9 0.65 1 0.1 I 1 10 10 IO


42576-02-3 NS NS NS NS NS NS NS NS 82657-04-3 NS NS NS NS NS NS NS NS

92-52-4 NS NS NS NS NS NS NS NS 111-91-1 NS NS NS NS NS NS NS NS 108-60-1 NS NS NS NS NS NS NS NS 103-23- 1 NS NS NS NS NS NS NS NS 117-81-7 30

111-44-4 NS NS NS NS NS NS NS NS

"O P:>

oq (!>

00 0\ 0 .....,

VJ -...)

I

I

COLUMN 1

Substance

bisphenol A boron

boron (hot water soluble)

bromate


bromobenzene bromodichloromethane

bromoform

bromomethane

bromophos

bromoxynil

butadiene, 1,3-

butanoic acid, 4-(4-chloro-2-methvlohenoxv)- rMCPBl butanol , 2-

butanol, n-

butoxv ethanol, 2-butyl benzyl phthalate


butylate

butylated hydroxytoluene (BHT]

butylbenzene, n-

butylbenzene, sec-

butylbenzene, tert-

cacodylic acid

caprolactam

captafol

captan

carbaryl

carbofuran

SCHEDULE 3.1- PART 3 GENERIC NUMERICAL Soll.. STANDARDS TO PROTECT ECOLOGICAL HEAL rn'.2

COLUMN 2

Chemical l Abstract I Service Number (CAS)

80-05-7

7440-42-8

NA'

15541-45-4

107-04-0

108-86-1

75-27-4

75-25-2

74-83-9

2104-96-3

1689-84-5

106-99-0

94-81 -5

78-92-2

71-36-3

111-76-2

85-68-7

85-70-1

2008-41-5

128-37-0

104-51-8

135-98-8

98-06-6

75-60-5

105-60-2

2425-06-1

133-06-2

63-25-2

1563-66-2

COLUMN 3 I COLUMN 4 I COLUMN 5

Wildlands

Natural3

(WLN)

NS NS

NS NS NS NS NS NS NS NS NS NS

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS

. I W1ldlands I

3 . 4 Reverted Agricultural

(Wli:r) (AL)

NS NS NS NS

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS

COLUMN 6 I COLUMN 7

I _ ..... I

I

11es1oenm11 I 4 . 5

Urban Park Low Density

(PL) (RLLD)

NS NS NS NS



COLUMN 8

nesh:ie11tia;

High Densit/

(R~0)

NS NS

NS NS NS NS NS NS NS NS NS NS

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS

COLUMN 9 I COLUMN 10

I Commercial

4 I lndustrial4

(CL) (IL)

NS NS NS NS



'O ~

{1Q ('])

00 -....}

0 ......,

VJ -....}

COLUMN 1

Substance

carbon disulfide carbon tetrachloride

carbosulfan

carboxin

chloramben

chloranil


chlordecone

chlorfenvinphos

chlorimuron, ethyl



chloroaniline, p-

chlorobenzene

chlorobenzilate




chlorobutane, 1-

chloroethanol, 2-

chloroform


chloronitrobenzene, 2-


chlorophenol, 2-

chlorophenol, 3-

chlorophenol, 4-

chloroprene

SCHEDULE3.l-PART 3

GENERIC NUMERICAL SOIL STANDARDS TO PROTECT ECOLOGICAL HEALTH1.z



75-15-0 56-23-5

55285-14-8

5234-68-4

133-90-4

118-75-2

5103-71-9 & 5103-74-2

143-50-0

470-90-6

90982-32-4

95-69-2

107-20-0

106-47-8

108-90-7

510-15-6

74-11-3

5216-25-1

98-56-6

109-69-3

107-07-3

67-66-3

91-58-7

88-73-3

100-00-5

95-57-8

108-43-0

106-48-9

126-99-8

Wildlands 3

Natural

lWL .. ) ....

NS 3

NS NS NS NS NS

NS NS NS NS NS NS 0.65

NS NS NS NS NS NS 3

NS NS NS 0.3

0.3

0.3

NS

Wild lands

Reverted3

(WL) f-F

NS 5

NS NS NS NS NS

NS NS NS NS NS NS

1

NS NS NS NS NS NS 5

NS NS NS 0.5

0.5

0.5

NS

I

Agricultural4

1·

(AL)

NS 0.1

NS NS NS NS NS



NS NS NS

0.05

0.05

0.05

NS

Urban Park4

(PL)

NS 5

NS NS NS NS NS

NS NS NS NS NS NS

1

NS NS NS NS NS NS 5

NS NS NS 0.5

0.5

0.5

NS

COLUMN 7 COLUMN 8 I COLUMN 9 I COLUMN 10


Low Density5

. High Density6

Commercial4

(Rl,_0

) (RLHo) (CL)

NS NS NS 5 50 50

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS

l 10 10

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 5 50 50

NS NS NS NS NS NS NS NS NS 0.5 5 5

0.5 5 5

0.5 5 5

NS NS NS

lndustrial4

(IL)

NS 50

NS NS NS NS NS

NS NS NS NS NS NS 10

NS NS NS NS NS NS 50 NS NS NS 5

5

5

NS

'"O ~ ~

00 00

0 .....,.,

v.i -...J

COLUMN 1

Substance

chlorothalonil chlorotoluene, 2-

chlorotoluene, 4-

chlorpropham

chlorpyrifos ch lorpyri fos-methy 1

chlorsulfuron

chlorthal-dimethyl

chlorthiophos

chrysene

clofentezine


cyanazine

cyanogen

cyclohexane, 1,2,3,4,5-

pentabromo-6-chloro-

cyclohexanone

cyclohexene

cyclohexylamine

cyfluthrin

cyhalothrin

cyperrnethrin

cyromazine

dalapon

daminozide

demeton

diallate


diazinon


GENERIC NUMERICAL Son, STANDARDS TO PROTECT ECOLOGICAL HEALTH1'2


Chemical Abstract Service Number

(CASj

1897-45-6 95-49-8

106-43-4

101-21-3

2921-88-2

5598-13-0

64902-72-3

1861-32- 1

60238-56-4

218-01-9

74115-24-5

123-73-9

21725-46-2

460-19-5

87-84-3

108-94-1

110-83-8

108-91-8

68359-37-5

68085-85-8

52315-07-8

66215-27-8

75-99-0

1596-84-5

8065-48-3

2303-16-4

95-70-5

333-41-5

Wildlands

Natural3

(WL,.,) ... NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS

NS NS NS NS NS NS NS NS NS NS NS NS NS

Wild lands

Reverted3

(WL,,) .. NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS


I Agricultural

4 I (AL)



Urban Park4

(PL)





Low Density5

High Density6

Commercial4

(Rli_0 ) (R'-.io) (CL)

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS

lndustrial4

(IL)



"O

~ 0 00 l.O

0 ......,

VJ -..)

COLUMN 1

Substance

dibenz(a,h)anthracene

dibenzo( a,e )pyrene

dibenzofuran

dibenzothiophene




dibromochloromethane [DBCM]

dibromoethane, 1,2-

dibutyl phthalate [DBP]

dibutyltin

dicamba

dichloroacetic acid







dichloroethane, I , I-


dichloroethylene, 1, 1-



dichloromethane dichlorophenol, 2,3-


dichlorophenol, 2,5-dichlorophenol, 2,6-


GENERIC NUMERICAL Son, ST AND ARDS TO PROTECT ECOLOGICAL HEALTH'"


Chemic.a! Abstract Service Number (CAS)

53-70-3 192-65-4

132-64-9

132-65-0

96-12-8

108-36-1

106-37-6

124-48-1

106-93-4 84-74-2

14488-53-0

1918-00-9

79-43-6

95-50-1 541-73-1

I06-46-7

91-94-1

75-71-8

80-07-9

75-34-3

107-06-2

75-35-4

156-59-2

156-60-5

75-09-2

576-24-9 120-83-2

583-78-8

87-65-0

Wildlands 3

Natural

(Wl.-w\ , -- ~,

0.65 NS NS NS NS NS NS NS NS

NS NS NS

0.65

0.65

0.65

NS NS NS 3

3 3 3 3

3 0.3

0.3

0.3 0.3

Wildlands

Reverted3

lW!,;\ "'

I

NS NS NS NS NS NS NS NS

NS NS NS 1

I

1

NS NS NS 5

5

5

5

5

5 0.5

0.5 0.5

0.5

I Agricultural

4 I (AL)

0.1 NS NS NS NS NS NS NS NS 30

NS NS NS 0.1

0.1

0.1

NS NS NS 0.1

0.1

0.1

0.1

0.1

0.1

0.05

0.05

0.05 0.05

Urban Park4

(PL)

1 NS NS NS NS NS NS NS NS

NS NS NS

I

1

1

NS NS NS 5

5

5

5

5

5

0.5 0.5

0.5

0.5



Low Densit/ . High Densit/ Commercial4

(RL._,.,) (RLHn) (CL)

1 IO IO NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS

NS NS NS NS NS NS NS NS NS 1 10 10

1 10 IO 1 10 IO

NS NS NS NS NS NS NS NS NS 5 50 50

5 50 50

5 50 50

5 50 50

5 50 50

5 50 50 0.5 5 5

0.5 5 5

0.5 5 5

0.5 5 5

lndustrial4

(IL)

IO NS NS NS NS NS NS NS NS

NS NS NS 10

IO 10

NS NS NS 50

50

50

50

50

50

5 5

5

5

'O

~ (1>

"' 0 0 ....,.,

U.l -....)

COLUMN 1

Substance

dichlorophenol, 3.4-dichlorophenol, 3,5-

dichlorophenoxy acetic acid, 2,4-(2,4-D]

dichlorophenoxy butyric acid, 2,4-[2,4-08]




dichloropropene, 1,3-

(cis +trans)

dichlorvos

dicrotophos

dicyclopentadiene

dieldrin

diethanolamine

diethyl ether

diethyl phthalate


diethylene glycol monobutyl ether

diethylene glycol monoethyl ether

diethylforrnamide

diflubenzuron

diisobutylene

dimethipin

dimethoate



SCHEDULE 3.1- PART 3 GENERIC NUMERICAL SOIL STANDARDS TO PROTECT ECOLOGICAL HEALTH

1•2


Chemical Abstract Service Number - --------(CAS)

95-77-2 591-35-5

94-75-7

94-82-6

78-87-5

142-28-9

616-23-9

542-75-6

62-73-7

141-66-2

77-73-6

60-57-1

111-42-2

60-29-7

84-66-2

392-74-5

112-34-5

111-90-0

617-84-5

35367-38-5

25167-70-8

55290-64-7

60-51-5

119-90-4

756-79-6

Wildlands

Natural3

(Wl.,.i)

0.3 0.3

NS

NS

3

NS NS 3

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS

I Wildlands I I

Reverted3

Agricultural4

/Al\

Urban Park4

(W~) \l"'\L/ , .... , 0.5 0.05 0.5 0.5 0.05 0.5

NS NS NS

NS NS NS

5 0.1 5

NS NS NS NS NS NS 5 0.1 5

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS

COLUMN 7 I COLUMN 8 I COLUMN 9 I COLUMN 10

Residential I Residential I I I Low Densit/ High Densit/ Commercial

4 lndustrial

4

·-· ' {(':I\ {IL\ (R4_oj ,--, \ · - ; \M'-Ho/

0.5 5 5 5 0.5 5 5 5

NS NS NS NS

NS NS NS NS

5 50 50 50

NS NS NS NS NS NS NS NS 5 50 50 50

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS

"O cffl ~

\0

0 .......,

V.l -....J

I

COLUMN 1

Substance

dimethylamino azobenzene, 4-[DAB)


dimethylaniline, N,N- [DMA]

dimethylbenz(a)anthracene, 7, 12-


dimethylformamide

dimethylhydrazine, I, 1-









dinitrophenol , 2,4-





dinoseb

dioxane, 1,4-

diphenamid

diphenyl sulfone

diphenyl-1 ,4-benzenediamine, N,N'-

diphenylamine




COLUMN 2 COLUMN 3 COLUMN 4 COLUMN 5 COLUMN 6 COLUMN 7 COLUMN 8 COLUMN 9 COLUMN10

Chemical

I

I I I I I I I Abstract Wildlands

WUdlaod• I I I R~ldeMal I ~~dMtlal I I I Service Natural3 3 • 4

Urban Park4

Low Density5

High Density6 Commercial4

lndustrial4

Reverted Agricultural Number

(WI,..) (WI,;) (AL) (PL) (RLLD) (RLHo) (CL) (IL) (CAS)








105-67-9 0.65 l 0.1 1 I 10 10 10








51-28-5 0.65 I 0.1 1 I 10 10 10












'O p)

(1Q ct> \0 N 0 ......, -VJ -..)

COLUMN 1

Substance

Direct Black 38

Direct Blue 6

Direct Brown 95

disulfoton

diuron dodine

endosulfan 1 + I1

endothall

endrin

EPTC

ethanol, 2-(2-methoxyethoxy)-

ethephon

ethion

ethoxyethanol acetate, 2-

ethoxyethanol, 2-

ethyl acetate

ethyl acrylate


ethylenediamine

ethylene thiourea

ethyleneimine

ethyl p-nitrophenyl benzenethionophosphonate [EPN] fenamiphos

fenpropathrin

fenvalerate

fluometuron

fluorene

fluoride

fluridone

SCHEDULE 3.1 - PART 3 GENERIC NUMERICAL SOIL STANDARDS TO PROTECT ECOLOGICAL HEALTH

1'2


Chemical Abstract Service Number ICAS) ,-- --,

1937-37-7

2602-46-2

16071-86-6

298-04-4

330-54-1

2439-10-3

115-29-7

145-73-3

72-20-8

759-94-4

111-77-3

16672-87-0

563-12-2

11 1-15-9

110-80-5

141-78-6

140-88-5

109-78-4

107-15-3

96-45-7

151 -56-4

2104-64-5

22224-92-6

39515-41-8

51630-58-1

2164-17-2

86-73-7 16984-48-8

59756-60-4

Wildlands

Natural3

(WLN)

NS

NS

NS

NS

NS

NS NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

250

NS

Wildlanas

Revertel

(Wl,i)

NS

NS

NS

NS

NS NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

400

NS

I Agricultural

4 I (AL)

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

200

NS

Urban Park4

(PL)

NS

NS

NS

NS

NS

NS NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

400 NS


Re:sicierliiai I nt::s1uem1a1 I I Low Densit/ High Density

6 Commercial

4

(R'-i_0

) (R~0) (CL)

NS NS NS

NS NS NS NS NS NS

NS NS NS

NS NS NS

NS NS NS NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

400 2000 2000

NS NS NS

lndustrial4

(IL)

NS

NS NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

2000

NS

"O

~ (1)

l.O (.;.)

0 ...., ....... (.;.) -.J

I

COLUMN 1

Substance

I flurprimidol flusilazole

flutolanil

fluvalinate

folpet

fomesafen

fonofos

formaldehyde

formic acid

fosetyl

furan

furazolidone

furfural

furmecyclox

furothiazole

glufosinate

glycidaldehyde

glyphosate

guanidine

haloxyfop, methyl HEPHsH

heptachlor

heptachlor epoxide

hexabromobenzene


hexachlorobenzene

hexachlorobutadiene

hexachlorocyclohexane, alpha

hexachlorocyclohexane, beta


GENERIC NUMERICAL Son, STANDARDS TO PROTECT ECOLOGICAL HEALTH1'2

COLUMN 2 COLUMN3 COLUMN4 COLUMN 5 COLUMN 6 COLUMN 7 COLUMNS COLUMN 9 COLUMN 10

Chemical I I I I I I I I Absl<aot I Wildlan':5 I WUdlands I I I Res;d..,Uol I Res;oen1;• Service Revertei Agricultura1

4 Urban Park

4 Low Densit/ High Density

6

. · 1 · 1

Natural Commercial Industrial Number

(WL,;) (Wln) (AL) (PL) (Rli_o) (R~o) (CL) (IL) (CAS)


133-07-3 NS NS NS NS NS NS NS NS 72178-02-0 NS NS NS NS NS NS NS NS 944-22-9 NS NS NS NS NS NS NS NS 50-00-0 NS NS NS NS NS NS NS NS 64-18-6 NS NS NS NS NS NS NS NS




69806-40-2 NS NS NS NS NS NS NS NS NA' 650 l 000 1 000 I 000 I 000 5 000 5000 5 000


59536-65-1 NS NS NS NS NS NS NS NS 118-74-1 1.5 2 0.05 2 2 10 10 10 87-68-3 NS NS NS NS NS NS NS NS


'O $l)

QCl ('ll

\0 .+::-. 0 ......,

VJ -..)

I

COLUMN 1

I Substance

I hexachlorocyclohexane, gamma


hexachloroethane

hexachlorophene

hexahydro-1 ,3,5-trinitro-l ,3,5-triazine [RDX]

hexamethylphosphoramide

hexanone, 2-

hexazinone

hexythiazox

hydramethylnon

hydrazine

hydroquinone

imazalil

imazaquin

imazethapyr

indeno( 1,2,3-cd)pyrene

iprodione

isobutanol

isophorone

isopropalin

isopropanol

isopropylbenzene

isoxaben

lactofen

LEPHs9

linuron

lithium

malathion




Chemical I I I I I I I l Abstract

I Wildlao~• I w;1dl•n~ I I I Reoldenti•I I Re•;d•nfi•I

Service 3 . 4 Urban Park

4 Low Density

5 High Density

6 . I . I Natural Reverted Agricultural Commercial Industrial Number

(Wl,;) (Wli;) (AL) (PL) (Rli_o) (Rl,io) (CL) (IL) (CAS)

58-89-9 0.01 77-47-4 NS NS NS NS NS NS NS NS 67-72-1 NS NS NS NS NS NS NS NS 70-30-4 NS NS NS NS NS NS NS NS 121-82-4 NS NS NS NS NS NS NS NS

680-31-9 NS NS NS NS NS NS NS NS 591 -78-6 NS NS NS NS NS NS NS NS

51235-04-2 NS NS NS NS NS NS NS NS 78587-05-0 NS NS NS NS NS NS NS NS 67485-29-4 NS NS NS NS NS NS NS NS 302-01-2 NS NS NS NS NS NS NS NS 123-31-9 NS NS NS NS NS NS NS NS


193-39-5 0.65 1 0.1 1 I 10 10 10




NA1 650 1000 1 000 I 000 1 000 2000 2 000 2000


'O II)

!JCI (1)

\0 VI

0 .....,

VJ -.J

I

COLUMN 1

Substance

I malononitrile mancozeb

maneb

mecoprop [MCPP]

merphos metalaxyl

methacrylonitrile

methamidophos

methidathion

methomyl

methoxy-5-nitroaniline, 2-

methoxychlor

methoxyethanol, 2-


methyl acetate


methyl hydrazine

methyl mercury

methyl methacrylate



rnethylaniline, 2-

methylaniline, 4-

methylaniline, N-


methylene-bis(2-chloroaniline), 4,4'-

methylene-bis(N, N-dimethyl)

aniline, 4,4'-




~=:~· I I I I I I I Wildlands

WUdlaods I I I Roslde"tlal I Reslde"Ual Service Natural

3 3 • 4 Urban Park

4 Low Density

5 High Density

6 Comme<clal' I .... ~ ... ··· I Reverted Agricultural

Number (WLR) (AL) (Pl) (Rlw) (RLH

0) (Cl) (IL)

(CAS) (WLN)

109-77-3 NS NS NS NS NS NS NS NS 8018-01 -7 NS NS NS NS NS NS NS NS 12427-38-2 NS NS NS NS NS NS NS NS














'O ~

(Jq ("!)

\0 0\ 0 ......, _. \.>.)

-.I

I

COLUMN 1

Substance

I methylenebisbenzenamine, 4,4'-methylnaphthalene, 1-


methylphenol, 2-

methylphenol, 3-methylphenol, 4-

methvlphenol, 4-chloro-3-methylstyrene, alpha-

metolachlor

metribuzin

metsulfuron-methyl

mirex

molinate

monomethylarsonic acid

myclobutanil

naled

naphthylamine, 2-

napropamide

nitrate (as N)

nitrite (as N)

nitroaniline, 2-

nitroaniline, 4-

nitrobenzene

nitrofurazone

nitroglycerin

nitroguanidine

nitrophenol, 2-

nitrophenol, 4-

nitropyrene, 4-


GENERIC NUMERICAL Son, ST AND ARDS TO PROTECT ECOLOGICAL HEALTH1'2

COLUMN2 COLUMN3 COLUMN4 COLUMN 5 COLUMN 6 COLUMN 7 COLUMN 8 COLUMN 9 COLUMN 101

Chemical I I I I I I I I ·-act I wno"n~s I w;ldlonds I I I R,.;dentiol I Res;dMtral Service 3 • 4

Urban Park4

Low Density5

High Density6

Comm&c;o1' I lndu,.riol' I Natural Reverted Agricultural Number

(WLN) (Wl,;) (AL) (PL) (RLuil (RLHo) (CL) (IL) (CAS)


95-48-7 0.65 l 0.1 I 1 10 10 IO

108-39-4 0.65 I 0.1 I 1 10 IO IO

106-44-5 0.65 I 0.1 I I 10 10 10

















88-75-5 0.65 I 0.1 1 1 10 10 10 100-02-7 0.65 1 0.1 l 1 10 IO 10


"O ll:>

()'Q (1>

\0 -....l 0 ......, -l>.l -....l

I

COLUMN 1

Substance

I nitrosodiethanolamine, N-

nitrosodiethylamine, N- [NDEA]

nitrosodimethylamine, N-

[NOMA]








nitrotoluene, 2-

nitrotoluene, 3-

nitrotoluene, 4-

nonane, n-

nonaqueous phase liquids'"

norflurazon

octahydro-1,3,5, 7-tetranitro-1,3,5,7-tetrazocine [HMX]

octamethylpyrophosphoramide

[OMPA]

octyl phthalate, di-n- [DNOP]

odorous substances11

oryzalin

oxadiazon

oxamyl

oxyfluorfen

paclobutrazol


SCHEDULE3.l-PART 3


COLUMN 2 COLUMN3 COLUMN4 COLUMN 5 COLUMN 6 COLUMN 7 COLUMN 8 COLUMN 9 COLUMN 10

Chemical

I

I I I I I Abstract Wildlands

WlldlMd• I I R.,;dontial I Re•;d•ntlal I I Service Natural

3 3 • 4 Urban Park

4 Low Densit/ High Densit/ Commercial

4 lndustrial

4 Reverted Agricultural

Number (WL,..) (WLR) (AL) (PL) (R'-t_o) (R~o) (CL) (IL)

(CAS)















NA 7 not present" not present not present not present not present not present not present not present


2691-41 -0 NS NS NS NS NS NS NS NS



NA ' not present" not present not present not present not present not present not present not present







"O ~ (0

\0 00

0 ....,., ....... \.;.l -....J

COLUMN 1

Substance

parathion parathion methyl

pebulate

pendimethalin

pentachlorobenzene, 1,2,3, 4 ,5-pentachloroethane

pentachloronitrobenzene [PCNB]

pentaerythritol tetranitrate [PETN]

perchlorate

perfluorobutane sulfonate [PFBS]

permethrin (cis +trans)

phenanthrene

phenmedipham

phenol, 2-methyl-4,6-dinitro-

[DNOC]

phenothiazine


phenylenediamine, o- (OPD]

phenylenediamine, p- (PPD]

phenylphenol, 2-

phorate

phosmet

phthalic acid, p-

picloram

picramic acid

picric acid

pirimiphos- methyl

prochloraz

profluralin

SCHEDULE 3.1- PART 3 GENERIC NUMERICAL SOIL STANDARDS TO PROTECT ECOLOGICAL HEALTH1

'2


Chemical Abstract Service Number {CASj

56-38-2

298-00-0

1114-71-2

40487-42-1

608-93-5

76-01-7

82-68-8

78-11-5

14797-73-0

375-73-5

52645-53-1

85-01-8

13684-63-4

534-52-1

92-84-2

108-45-2

95-54-5

106-50-3

90-43-7

298-02-2

732-11-6

100-21-0

1918-02-1

96-91-3

88-89-1

29232-93-7

67747-09-5

26399-36-0

Wildlands

Natural3

(WL.,)

NS NS

NS

NS

1.5

NS

NS

NS

NS

NS

NS

3

NS

0.65

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

Wildlands I I 3 • • Reverted . Agricultural

(W~) (Al)

NS NS NS NS

NS NS

NS NS

2 0.05

NS NS

NS NS

NS NS

NS NS

NS NS

NS NS

5 0.1

NS NS

1 0.1

NS NS

NS NS

NS NS

NS NS

NS NS

NS NS

NS NS

NS NS

NS NS

NS NS

NS NS

NS NS

NS NS

NS NS

Urban Park4

(Pl)

NS NS

NS

NS

2

NS

NS

NS

NS

NS

NS

5

NS

I

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS



Low Densit/ High Densit/ Commercial4

(RLLD) (R~0) (Cl)

NS NS NS NS NS NS

NS NS NS

NS NS NS

2 10 10

NS NS NS NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

5 50 50

NS NS NS

I 10 IO

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

NS NS NS

Industrial•

(IL)

NS NS

NS

NS

10

NS

NS

NS

NS

NS

NS

50

NS

10

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

NS

"Cl p.:i

()q (l>

'° '° g, VJ -.J

COLUMN 1

Substance

pro met on prometryn

propachlor

propanil

propargite

propargyl alcohol

propazine

prop ham

propiconazole

propylbenzene, 1-

propylene glycol monomethyl

ether

propylene oxide

propyzamide

pyrene

pyridine

quinalphos

quinoline

quizalofop-ethyl

resmethrin

ronnel

rotenone

selenious acid

sethoxydim

silver

silvex

simazine

strontium

strychnine

SCHEDULE 3.1 - PART 3 GENERIC NUMERICAL SOIL STANDARDS TO PROTECT ECOLOGICAL HEALTH1

'2



1610-18-0 7287-19-6

1918-16-7

709-98-8

2312-35-8

107-19-7

139-40-2

122-42-9

60207-90-1

103-65-1

107-98-2

75-56-9

23950-58-5

129-00-0

110-86-1

13593-03-8

91-22-5

76578-14-8

10453-86-8

299-84-3

83-79-4

7783-00-8

74051-80-2

7440-22-4

93-72-1

122-34-9

7440-24-6

57-24-9

Wildlands

Natural3

(WI,_) N•

NS NS NS NS NS NS NS NS NS NS NS

NS NS 6.5

NS NS NS NS NS NS NS NS NS 15

NS NS NS NS

..

Wildlands I I 3 • 4 4 Reverted . Agricultural Urban Park

(WL) (AL) (PL)

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS

NS NS NS NS NS NS 10 0.1 10

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 20 20 20

NS NS NS NS NS NS NS NS NS NS NS NS


-I Residential I Residential I I


(RL, n) (RLHn) (CL)

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS

NS NS NS NS NS NS 10 100 100

NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 20 40 40

NS NS NS NS NS NS NS NS NS NS NS NS

lndustrial4

(IL)

NS NS NS NS NS NS NS NS NS NS NS

NS NS 100

NS NS NS NS NS NS NS NS NS 40

NS NS NS NS

"O P:>

(IQ ('!)

....... 0 0 0 . ......,

VJ -....J



COLUMN 1 COLUMN 2 COLUMN 3 COLUMN 4 COLUMN 5 COLUMN 6 COLUMN 7 COLUMN 8 COLUMN 9 COLUMN 10

I I Chem!~! I I I I I I

I I Abstract Wildlands I Wildlands I I Residential I Residential I I

Substance Service Natural3 Reverted 3 Agricultural4

Urban Park 4


lndustrial4

Number 'W' } 'WL ) (AL) (PL) (RI ) lRL ) (CL) (IL) (CAS) ' ~ ' R , -i.o , rlO·

styrene 100-42-5 3 5 0.1 5 5 50 50 50 styrene-acrylonitrile [SAN) trimer NA7 NS NS NS NS NS NS NS NS (all isomers) sulfotep 3689-24-5 NS NS NS NS NS NS NS NS sulfur, elemental 7704-34-9 2 000 TCMTB 21564-17-0 NS NS NS NS NS NS NS NS tebuthiuron 34014-18-1 NS NS NS NS NS NS NS NS temephos 3383-96-8 NS NS NS NS NS NS NS NS terbacil 5902-51-2 NS NS NS NS NS NS NS NS terbufos 13071-79-9 NS NS NS NS NS NS NS NS terbutryn 886-50-0 NS NS NS NS NS NS NS NS tetrach!orobenzene, 1,2,3,4- 634-66-2 1.5 2 0.05 2 2 10 10 10 tetrachlorobenzene, 1,2,3,5- 634-90-2 1.5 2 0.05 2 2 10 10 10 tetrachlorobenzene, 1,2,4,5- 95-94-3 1.5 2 0.05 2 2 IO 10 10 tetrachloroethane, 1,1,1,2- 630-20-6 NS NS NS NS NS NS NS NS tetrachloroethane, 1,1,2,2- 79-34-5 NS NS NS NS NS NS NS NS tetrachlorophenol, 2,3 ,4,5- 4901-51-3 0.3 0.5 0.05 0.5 0.5 5 5 5 tetrachlorophenol, 2,3,4,6- 58-90-2 0.3 0.5 0.05 0.5 0.5 5 5 5 tetrachlorophenol , 2,3,5,6- 935-95-5 0.3 0.5 0.05 0.5 0.5 5 5 5 tetrachlorovinphos 961-11-5 NS NS NS NS NS NS NS NS tetraethyl lead 78-00-2 NS NS NS NS NS NS NS NS tetrahydrofuran I 09-99-9 NS NS NS NS NS NS NS NS

tetryl 479-45-8 NS NS NS NS NS NS NS NS thallium 1

' 7440-28-0 5.5 9 9 9 9 25 25 25 thifensulfuron-methyl 79277-27-3 NS NS NS NS NS NS NS NS thiobencarb 28249-77-6 NS NS NS NS NS NS NS NS thiocyanate 302-04-5 NS NS NS NS NS NS NS NS thiodiglycol 111-48-8 NS NS NS NS NS NS NS NS

thiofanox 39196-18-4 NS NS NS NS NS NS NS NS

"O ~

CICI (1)

0

0 ......,

w -....J

I

COLUMN 1

Substance

I thiophanate- methyl thiophenol

thiram

tin

toxaphene (all isomers) tralomethrin

triadimefon

triallate

triasulfuron

tribenuron-methyl


tribufos

tributyl phosphate

tributyltin

trichloro-1,2,2-trifluoroethane,

1,1,2-

trichloroacetic acid


trichlorobenzene. l ,2.3-trichlorobenzene, 1,2,4-


trichloroethane, 1,1 ,1-trichloroethane, 1,1,2-


trichlorophenol, 2,3,4-trichlorophenol, 2,3,5-

trichlorophenol , 2,3,6-


trichlorophenol, 2,4,6-trichlorophenol, 3,4,5-


GENERIC NUMERICAL SOIL ST AND ARDS TO PROTECT ECOLOGICAL HEALTH'"

COLUMN 2 COLUMN3 COLUMN 4 COLUMNS COLUMN 6 COLUMN 7 COLUMN 8 COLUMNS COLUMN 10

Chemical Abstract

I Wildlan~• I .. ,.,., .. 1 I I Reo;dem;a; I Reo;dooUa; I I

Service Reverted3

Agricultural4

Urban Park4

Low Oensity5

High Densit/ Commercial4

· 1

Natural Industrial Number

(Wl,i) (AL) (PL) (R'-i_o) (RLHo) (CL) (IL) (CAS) (WLN)


7440-31-5 30 50 5 50 50 300 300 300

8001-35-2 NS NS NS NS NS NS NS NS 66841 -25-6 NS NS NS NS NS NS NS NS 43121-43-3 NS NS NS NS NS NS NS NS 2303-17-5 NS NS NS NS NS NS NS NS

82097-50-5 NS NS NS NS NS NS NS NS l 01200-48-0 NS NS NS NS NS NS NS NS



76-03-9 NS NS NS NS NS NS NS NS 634-93-5 NS NS NS NS NS NS NS NS 87-61-6 l.5 2 0.05 2 2 lO 10 lO 120-82-1 l.5 2 0.05 2 2 10 IO 10 108-70-3 1.5 2 0.05 2 2 10 lO lO 71-55-6 3 5 0.1 5 5 50 50 50 79-00-5 3 5 0.1 5 5 50 50 50 75-69-4 NS NS NS NS NS NS NS NS

15950-66-0 0.3 0.5 0.05 0.5 0.5 5 5 5 933-78-8 0.3 0.5 0.05 0.5 0.5 5 5 5 933-75-5 0.3 0.5 0.05 0.5 0.5 5 5 5 95-95-4 0.3 0.5 0.05 0.5 0.5 5 5 5 88-06-2 0.3 0.5 0.05 0.5 0.5 5 5 5

609-19-8 0.3 0.5 0.05 0.5 0.5 5 5 5

'O ~

(IQ (!>

0 N 0 ......., -VJ -...l

I

COLUMN 1

I Substance

I trichlorophenoxyacetic acid, 2,4,5-[2,4,5-T)

trichloropropane, 1, 1,2-




tridiphane

triethylene glycol

trifluralin

trimethyl phosphate




tris(l ,3 -dichloro-2-propyl)

phosphate [TDCPP)

tris( 1-chloro-2-propyl)phosphate

[TCPP]

tris(2,3-dibromopropyl)phosphate


tris(2-ethylhexyl)phosphate

tungsten

vemolate

vinclozolin

vinyl acetate

vinyl chloride

VPHs 14

warfarin

zineb

SCHEDULE 3.1- PART 3 GENERIC NUMERICAL Son. STANDARDS TO PROTECT ECOLOGICAL HEALTH'"

COLUMN 2 COLUMN3 COLUMN4 COLUMNS COLUMN 6 COLUMN 7 COLUMN 8 COLUMN 9 COLUMN10

Chemical I I I I _ _ I _ _ _ .. I I I A~ract I WHdlao~s I WHdlaods I I Ros•••ooao I ~~"'"'~' I I I Service 3 • 4

Urban Park 4


lndustrial4

Natural Reverted Agricultural Number

(WLN) (WLR) (AL) (PL) (RLLD) (RLHo) (CL) (IL) (CAS)




112-27-6 NS NS NS NS NS NS NS NS 1582-09-8 NS NS NS NS NS NS NS NS 512-56-1 NS NS NS NS NS NS NS NS 108-67-8 NS NS NS NS NS NS NS NS 99-35-4 NS NS NS NS NS NS NS NS 118-96-7 NS NS NS NS NS NS NS NS






NA ' 150 200 200 200 200 200 200 200


'O ~

(JQ Cb

0 w 0 ......,

L>.l -.!

Notes I All values in µgig unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual, as

updated from time to time, a director's protocol, or alternate methods acceptable to a director. The high density residential land use standards of this schedule assume the prohibition of the use of the land (a) to grow plants for human consumption, and (b) as a children's playground, sports field, picnic area or any other use that promotes frequent contact by children. Consult a director for further advice.

2 NS - Insufficient acceptable scientific data exists to calculate a standard or no appropriate standard, guideline or criterion exists to develop a soil quality standard. 3 Standard is derived in accordance with Protocol 28, "2016 Standards Derivation Methods, unless otherwise noted. 4 Standard is set equal to the corresponding land use soil standard for the substance in Schedule 4 of this regulation, as it read before the repeal of that schedule, unless

otherwise noted. Standard has been set to equal the Residential (RL) land use soil standard for the substance in Schedule 4 of this regulation, as it read before the repeal of that schedule, unless otherwise noted.

6 Standard has been set to equal the Commercial (CL) land use soil standard for the substance in Schedule 4 of this regulation, as it read before the repeal of that schedule, unless otherwise noted.

7 NA - not applicable. No CAS number exists for the substance. 8 HEPHs - Heavy Extractable Petroleum Hydrocarbons in soil, as defined in 2015 British Columbia Environmental Laboratory Manual and updated from time to time. 9 LEPHs - Light Extractable Petroleum Hydrocarbons in soil, as defined in 2015 British Columbia Environmental Laboratory Manual and updated from time to time. 10 Soil must be remediated so that nonaqueous phase liquids are not present in quantities in excess of that acceptable to a director. 11 Standard is set equal to the Urban Park (PL) land use soil standard for the substance in Schedule 4 of this regulation, as it read before the repeal of that schedule. 12 Soil must be remediated so that odorous substances are not present in quantities in excess of that acceptable to a director. 13 Standards have been derived in accordance with Protocol 28, "2016 Standards Derivation Methods". 14 VPHs - Volatile Petroleum Hydrocarbons in soil, as defined in 2015 British Columbia Environmental Laboratory Manual and updated from time to time.

'O !):>

Qq ~

0 .j::>.

0 ""+)

\,;) -...!

COLUMN 1

Subs!~mce

acenaphthene

acephate

acetic acid, 2-methyl-4-chlorophenoxy-rMCPAl acetochlor

acetone

acetophenone

acridine

acrolein

acrylamide

acrylic acid

acrylonitrile

adipic acid

alachlor

aldicarb

a ldicarb sulfone

aldrin

ally! alcohol

ally! chloride

aluminum

ametryn

aminobiphenyl, 4-

aminophenol, 3-

aminophenol, 4-

amitraz

SCHEDULE 3.2 - - -- --- - - - - ---- -- --GENERIC NUMERICAL WATER STANDARDS'

COLUMN 2 COLUMN 3 COLUMN 4 Chemical Abstract Service# Aquatic Life

2 Irrigation

2

(CAS) \M.H I {!W}

83-32-9 60

30560-19-1

94-74-6 265, 426 0.025

34256-82-1

67-64-1

98-86-2

260-94-6 0.5

107-02-8 IO

79-06-1

79-10-7

107-13-1

124-04-9

15972-60-8

116-06-3 105, 1.56 54 .9~ , 67.5 10

1646-88-4

309-00-2 0.0411

107-18-6

107-05-1

7429-90-5 5 000

834-12-8

92-67-1

591-27-5

123-30-8

33089-61-1

COLUMN 5 COLUMN 6

Livestock2

Drinking Water3

(LW) (DW)

2504

154

25 1001

804

3 5004

4004

38 34,8

0.14

2 0004

5"'"

8 0004

34

JI 44

44

0.711 0.0094

204

7.54

5 000 9 500 1 ~.u

354

0.00754

3004

804

104

'O i:>l

()Q (b

0 Vl

0 .....,

UJ -.!

COLUMN 1

c .. kro.+-. ... ,...,..

ammonia, total (as N)

anil ine

anthracene

anthraquinone, 9, 10-

antimony

arami te

arsenic

asbestos

asulam

atrazine

auramine

azinphos-methyl

azobenzene

azodicarbonamide

barium

benfluralin

benomyl

bensulfuron-methyl

bentazon

SCHEDULE 3.2 GENERIC NUMERICAL WATER STANDARDS'


2 Irrigation

2

{CAS) (AW) \IH'J

7664-4 1-7 1 310 @ pH '.'.'.. 8.5) ' 14

3 700 @ pH 8.0 - < 8.55

'14

11 300 @ pH 7.5 - < 8.05'14

18 500 @ pH 7.0 - < 7.55'14

18 400 @ pH < 7.05'14

2 300 @ pH'.'.'.. 8.56

'15

6 850 @ pH 8.0 - < 8.56'15

20 000 @ pH 7.5 - < 8.06'15

64 000 @ pH 7.0 - < 7.56'15

200 000 fa! pH < 7.06'15

62-53-3 20

120-1 2-7 1

84-65-1

7440-36-0 90), 2 5006

140-57-8

7440-38-2 50), 125° 100

1332-21-4

3337-71-1

19 12-24-9 20), 100° 10

492-80-8

86-50-0

103-33-3

123-77-3

7440-39-3 10 000), 5 000°

1861-40- 1

17804-35-2

83055-99-6

25057-89-0

COLUMN 5 COLUMN 6

Livestock2

Drinking Water3

11\At\ 1n'"" \'-••1 \-··1

304

10004

44

67

64

25 10 '

7 m.f./Llh

2004

60 57

0.24

20 201

1.54

4 0004

1 0007

1 0004

2004

8004

1004

"O ~

O'Q (0

0 0\ 0 ....., ,_. VJ -.I

COLUMN 1

S:..:bst~:-:ce

benz(a)anthracene

benzene

benzidine

benzo( a )pyrene


benzoic acid

benzotrichloride

benzyl alcohol

benzyl chloride

beryllium

bifenox

biphenyl, I , 1 '-


bis(2-chloro-1-methylethyl) ether

bis(2-ethylhexyl) adipate

bis(2-ethylhexyl) phthalate [DEHP]


bisphenol A

boron

bromacil

bromate


bromobenzene

bromodichloromethane [BDCM]

bromofonn

bromomethane

bromophos



2 Irrigation

2

{CAS} (AWj \IHJ

56-55-3 1

71-43-2 4005

, 1 000°

92-87-5

50-32-8 0.1

205-99-2 & 205-82-3 65-85-0

98-07-7

100-51-6

100-44-7

7440-41-7 1.5), I 0006 100

42576-02-3

92-52-4

111-91-1

108-60-1

103-23-1

117-81-7 160

111-44-4

80-05-7

7440-42-8 12 000 500-600017

314-40-9 50 0.218

, 0.61"

15541 -45-4

I 07-04-0

108-86-1

75-27-4

75-25-2

74-83-9

2104-96-3

COLUMN 5 COLUMNS

Livestock2

Drinking Water3

11\AI\ ln\AI\ \'-UJ ,_ .. ,

0.074

5 '

0.1 4'~

0.011

0.074

15 0004

0.54,8

4004

0.94

100 84

354

2 0004

104

1504

1504

104

0.154

2004

5 000 5 0007

I 100

10 ' 14,8

304

JOO 1007,20

100 100 1'.lU

5.54

204

'O ~

()q (l)

0 -.J 0 .....,

VJ -..l

COLUMN 1

~ ........... ____

bromoxynil

butadiene, 1,3-

butanoic acid, 4-(4-chloro-2-methylphenoxv)- fMCPBl butanol, 2-

butanol, n-

butoxy ethanol , 2-

butyl benzyl phthalate


butylate

butylated hydroxytoluene [BHT]

butylbenzene, n-

butylbenzene, sec-

butylbenzene, tert-

cacodylic acid

cadmium

calcium

caprolactam

captafol

cap tan

carbaryl

carbofuran

carbon disulfide

carbon tetrachloride

SCHEDULE 3.2 GENERIC NUMERICAL WATER STANDARDS

1


2 Irrigation

2

(CAS} (A.Wj (i'VY)

1689-84-5 50 0 .35 1U

106-99-0

94-81-5

78-92-2

71-36-3

111-76-2

85-68-7

85-70-1

2008-41-5

128-37-0

104-51-8

135-98-8

98-06-6

75-60-5

7440-43-9 0.5 @ H < 30~ '.t 1 5

1.5 @ H 30 - < 905

'21

2.5 @ H 90- < 1505

'21

3.5 @ H 150- < 2105

'21

4 @ H:;:: 2105

'21

156

7440-70-2

105-60-2

2425-06-1

133-06-2 15

63-25-2 z5, 30

1563-66-2 18

75-15-0

56-23-5 130

COLUMN 5 COLUMN 6

Livestock2

Drinking Water3

,~ ... , in"·" \-··1

11 5 ' 14,~

404

8 0004

4004

4004

804

4 0004

2004

454

2004

4004

4004

804

80 57

I 000 mg/L

2 0004

14

10 704

l 100 901

45 901

4004

5 27

"O ll:l

OQ n

0 00

0 ..-+,

VJ -J

COLUMN 1

~··""-·- ... -carbosulfan

carboxin

catechol

chloramben

chloranil


chlordecone

chlorfenvinphos

chloride ion

chlorimuron, ethyl-

chlorine (Cl2)L)



chloroaniline, p-

chlorobenzene

chlorobenzilate




chlorobutane, 1-

chloroethanol, 2-

chlorofonn




chlorophenol, 2-

chlorophenol, 3-


COLUMN 2 COLUMN 3 COLUMN4 Chemical Abstract Service# Aquatic Life

2 Irrigation

2

{CAS} (AW) (iW)

55285-14-8

5234-68-4

120-80-9 2000u

133-90-4

118-75-2

5103-71-9 & 0.06 5103-74-2 143-50-0

470-90-6

16887-00-6 I 500 mg!L' 100 mg/LLj

90982-32-4

7782-50-5 20', 30° l 000

95-69-2

107-20-0

106-47-8

108-90-7 13', 250°

510-15-6

74-11-3

5216-25-1

98-56-6

109-69-3

107-07-3

67-66-3 20

91-58-7

88-73-3

100-00-5

95-57-8 J9.5-2600Lo

108-43-0 17 -2 300.l(}

COLUMN 5 COLUMN 6

Livestock2

Drinking Water3

\LWYJ '"""'" ,..., .. , 404

4004

604

0.44

7 0.454

0.0154

3"

600 mg/L 250 mg/L7'24

804

1.54

0.64

0.84

80 1' u

1.54

1004

0. 054'~ 104

1504

804

100 100 /,.lU

3004

0.54

44

0.124,27 4512,13

0.1L4,LI

"Cl

~ (!)

0 ID 0 .......,

VJ -.)

COLU MN 1

St.:bstance

chlorophenol, 4-

ch1oroprene

chlorothalonil

chlorotoluene, 2-

chlorotoluene, 4-

chlorpropham

chlorpyrifos

chlorpyrifos-methyl

chlorsulfuron

chlorthal-dimethyl

chlorthiophos

chromium, hexavalentL~

chromium, trivalentL~ chrysene

clofentezine

cobalt

copper


cyanazine

cyanide

cyanogen

SCHEDULE 3.2 G ENERIC NUMERICAL WATER ST ANDARDS

1


2 Irrigation

2

(CAS} (AVv) , ... , 106-48-9 8.5 - I 180L(J

126-99-8

1897-45-6 2), 4b 5.8

95-49-8

106-43-4

10 1-21-3

292 1-88-2 0.02

SS98-1 3-0

64902-72-3

186 1-32-1

60238-56-4

18540-29-9 10), !St> 8

1606S-83-1 90), S60° s 2 18-0 1-9 I

74 115-24-5

7440-48-4 40 50

7440-50-8 20@ H < S05'!

1 200

30 @ H = 50 - < 7S5'21

40 @ H = 75 - < 1005,2

1

50 @H = JOO - < 12S5'21

60 @ H = 125 - < 1505'21

70 @ H = 150 - < 1755

'21

80 @ H = 175 - < 2005

'21

90@ H :'.':. 2005'21

206

123-73-9

21725-46-2 20 0.5

57-12-5 50s,29, 100,2\1

460-1 9-5

COLUMN 5 COLUMN 6

Livestock2

Drinking Water3

/l \AI\ (OW} , ..... ... ... , 0.124,27

804

170 504

804

804

8004

24 907

404

2004

404

34

so so ' 50 6 000

4

74

504

I 000 14

300 I soo IL,lj

54.~

10 0.24

2001·j

0

44

'"O ~

()Q (ll

0 0 .......,

VJ -...!

COLUMN 1

S:..:bstar:ce

cyclohexane, 1,2,3,4,5-pentabromo-6-chloro-cyclohexanone

cyclohexene

cyclohexylamine

cyfluthrin

cyhalothrin

cypermethrin

cyromazine

dalapon

daminozide

de1 tamethrin

demeton

diallate


diazinon

dibenz(a,h)anthracene

dibenzofuran

dibenzothiophene




dibromochloromethane [DBCM)

dibromoethane, 1,2-

dibutyl phthalate [DBP]

dibutyltin

dicamba



1

COLUMN2 COLUMN 3 COLUMN4 Chemical Abstract Service# Aquatic Life

2 Irrigation

2

(CAS) (AVv) \ IU'J

87-84-3

108-94-1

11 0-83-8

108-91-8

68359-37-5

68085-85-8

523 15-07-8

66215-27-8

75-99-0

1596-84-5

5291 8-63-5 0 . 1 ~

8065-48-3

2303-16-4

95-70-5

333-4 1-5 0.03

53-70-3

132-64-9

132-65-0

96-12-8

108-36-1

106-37-6

124-48-1

106-93-4

84-74-2 190

14488-53-0 0.8

1918-00-9 100 0. 18

95-50-1 75, 420°

COLUMN 5 COLUMNS

Livestock2

Drinking Water3

,~ ... , Jn\11.1\ , ....... , 74

20 0004

204

8004

1004

204

404

304

1004

8.5"

2.5

0.154

2.54

14

14 201

0.0 1 4 '~

4"

404

0.54'8

l.5"

404

100 1001,lU

0.54,8

4004

122 1201

2001' 1.l

"O i:>:>

(Jq (!)

0 .......,

\>.) -...J

COLUMN 1

Substance


dich!orobenzene, 1,4-




dichlorodiphenyltrichloroethane, total

[DDTJ31



dichloroethylene, 1, 1-



dichloromethane


dichlorophenol , 2,4-

dichlorophenol , 2,5-




dichlorophenoxyacetic acid, 2,4-[2,4-Dl dichlorophenoxy(2,4-)butyric acid, 4-[2,4-DB]




dichloropropene, 1,3- (cis +trans)

dichlorvos

diclofop-methyl



2 Irrigation

2

{C~ .. S) (AWj (i'W/

541-73-1 1 500

106-46-7 260

91-94-1

75-71-8

80-07-9

NA54 0.01

75-34-3

107-06-2 I 000

75-35-4

156-59-2

156-60-5

75-09-02 980

576-24-9 5.5 - 76026

120-83-2 3 - 400Lb

583-78-8 2.5 - 340l 0

87-65-0 10 - 1 36026

95-77-2 3 - 40026

591-35-5 2.5 - 300Lo

94-75-7 40

94-82-6

78-87-5

142-28-9

616-23-9

542-75-6

62-73-7

51338-27-3 61 0.18

COLUMN 5 COLUMNS

Livestock2

Drinking Water3

\L..H'J lr"\UI\ \UH/

51, 10

0.354

8004

34

30 0.454

304

5 51

141

84

804

50 so ' 0.324,33

0 .324,33 900 1' 1'

0.3L4,5.l

0.3l4,.l5

0.324,oo

0.324,33

100 1001

304

4.54

804

104

1.54

0.554

9 9 1

'O p.)

(IQ (1)

N 0 .....,

VJ -.J

COLUMN 1

.;;)UU~lCll lt,,~

dicrotophos

dicyclopcntadiene

dieldrin

diethanolamine

diethyl ether

diethyl phthalate


diethylene glycol monobutyl ether

diethylene glycol monoethyl ether

diethylformamide

diflubenzuron

diisobutylene

diisopropanolamine [DIP A ]34

dimethipin

dimethoate



dimethylaminoazobenzene, 4- [DAB]


dimethylaniline, N,N- [DMA]

dimethy lbenz( a )anthracene, 7, I 2-


dimethylformamide

dimethyl hydrazine, 1, I-





SCHEDULE 3.2 GENERIC NUMERICAL WATER 8TANDARDS1


2 Irrigation

2

I r-AC>\

(AW) (iWj \'-'-'-"/

141-66-2

77-73-6

60-57-1 0.04 11

111-42-2

60-29-7

84-66-2

392-74-5

I 12-34-5

1I1-90-0

617-84-5

35367-38-5

25167-70-8

110-97-4 15 000 39 000

55290-64-7

60-51-5 62

I 19-90-4

756-79-6

60-11-7

95-68-1

121-69-7

57-97-6

I 19-93-7

68-12-2

57-1 4-7

105-67-9

576-26-1

95-65-8

120-61-6

COLUMN 5 COLUMNS

Livestock2

Drinking Water3

(L'W) \LIHJ

0.44

3004

0.7 0.0 14

84

8004

3 0004

0.64

1004

2504

44

804

404

38 000 3 5001Z

804

3 201

0.14

904

O.Q354

0.84

84

0.024'~

0.0154

4004

0.024'~

804

2.54

44

4004

'O $:))

(IQ (1)

l;.l

0 ......,

l;.l -J

COLUMN 1

St?bstar!c~





dinitrophenol, 2,4-





dinoseb

dioxane, 1,4-

diphenamid

diphenyl sulfone

diphenyl-1,4-benzenediamine, N,N'-

diphenylamine


Direct Black 38

Direct Brown 95

disulfoton

diuron

dodine

endosul fan I + II

endothall

endrin

EPHw10-1 937 '3 ~ EPTC

ethanol, 2-(2-methoxyethoxy)-

ethephon

SCHEDULE 3.2 G ENERIC NUMERICAL WATER STANDARDS'

COLUMN 2 COLUMN 3 COLUMN 4 Chemical Abstract Service # Aquatic Life

2 Irrigation

2

(GAS) \#" HJ {!W}

528-29-0

99-65 -0

100-25-4

131-89-5

5 1-28-5 2000u

12 1-14-2

606-20-2

35572-78-2

19406-5 1-0

88-85-7 0.5 J 6LJ, 46j) , 93 l ~

123-9 1-1

957-51-7

127-63-9

74-3 1-7

122-39-4

85-00-7

1937-37-7

16071-86-6

298-04-4

330-54-1

2439-10-3

115-29-7 0.01 ) , ~ , 0.01 5°

145-73-3

72-20-8 0.023

NA32 5 000 5 000

759-94-4

111-77-3

16672-87-0

COLUMNS COLUMN6

Livestock2

Drinking Water3

{LW) (DW)

0.44

0.44

0.44

84

84

0.54

0.14

84

84

150j () 44

1.54

1004

34

14

1004

70 701

0.024

0.0254

0. 154

150 1501

154

254

804

0.2 14

5 000 5 000

1004

1504

204

'O

~ (ti

~

~ VJ -..J

COLUMN 1

S~bs!a~ce

ethinylestradiol, 17-alpha [EE2t'

ethicn

·ethoxyethanol acetate, 2-

ethoxyethanol, 2-

ethyl acetate

ethyl acrylate

ethyl p-nitrophenyl benzenethionophosphonate fEPNl ethyl benzene


ethylenediamine

ethylene glycol

ethylene thiourea

ethyleneimine

fenamiphos

fenpropathrin

fenvalerate

fluometuron

fluoranthene

fluorene

fluoride

fluridone

flurprimidol

flusilazole

flutolanil

fluvalinate

folpet

SCHEDULE 3.2 GENERIC NUMERICAL WATER STANDARDS1


2 Irrigation

2

(CAS) (AY''V) /l\An , ... , 57-63-6 0.005

563-12-2

111-15-9

110-80-5

141-78-6

140-88-5

2104-64-5

100-41-4 2 0005, 2 5006

109-78-4

107-15-3

107-21-1 I 920 mg/L

96-45-7

151-56-4

22224-92-6

39515-41-8

51630-58-1

2164-17-2

206-44-0 2

86-73-7 120

16984-48-8 2 000 @ H < 505'21 1 000

3 000 @ H ?: 505'21

15 0006

59756-60-4

56425-91-3

85509-19-9

66332-96-5

69409-94-5

133-07-3

COLUMN 5 COLUMN 6

Livestock2

Drinking Water3

(LW} (DW)

24

4004

3504

3 5004

204

0.044

14o '· u

3004

3504

8 0004

0.34

0 . 1 4 ' ~

1"

1004

1004

504

1504

1504

I 00040

1 5001

3004

804

3"

2504

404

454

'O ~

(1Q (t)

Vl

0 ......,

VJ -...J

COLUMN 1

S!.!bSt:!r!Ca::!

fomesafen

fonofos

formaldehyde

formic acid

fosetyl

furan

furazolidone

furfural

furmecyclox

furothiazole

glufosinate

glycidaldehyde

glyphosate

guanidine

haloxyfop, methy l

heptachlor

heptachlor epoxide


hexachlorobenzene

hexachlorobutadiene

hexachlorocyclohexane, alpha

hexachlorocyclohexane, beta

hexachlorocyclohexane, gamma


hexachloroethane

hexachlorophene

hexahydro-1 ,3,5-trinitro-l ,3 ,5-triazine [RDX]



2 Irrigation

2

(GAS) /A\11\ {!W) \l"'"'•J

72178-02-0

944-22-9

50-00-0

64-18-6

15845-66-6

110-00-9

67-45-8

98-01-1

60568-05-0

531-82-8

53369-07-6

765-34-4

1071-83-6 5 000

113-00-8

69806-40-2

76-44-8 0.141

1024-57-3 0.141

59536-65-1

118-74-1

87-68-3 15

319-84-6 0.142

319-85-7 0.142

58-89-9 0.142

77-47-4

67-72-1

70-30-4

121-82-4

COLUMN 5 COLUMN 6

Livestock2

Drinking Water3

(LW} (DW)

0.84

84

8004

3 5004

10 0004

44

0.044

104

54

0.14

1.54

1.54

280 2807

404

o.2'' 341 0.035

4

341 0.0 154

0.0054

0.5 0.14

24

44L

0.0254

44L

0.0854

44L

0.154

254

34

14

1.54

"O !))

(Jq (1)

°' g, (.;.)

-.l

COLUMN 1

~ •• &.... .......... __

hexamethylphosphoramide

hexanone, 2-

hexazinone

hexythiazox

hydramethylnon

hydrazine

hydroquinone

imazalil

imazaquin

imazethapyr

iprodione

iron 43'44

isobutanol

isophorone

isopropalin

isopropanol

isopropylbenzene

isoxaben

Jactofen

lead

LEPHw4)

linuron

lithium


1


2 Irrigation

2

{CAS} (A'Yvj (i'W)

680-3 1-9

59 1-78-6

51235-04-2

78587-05-0

67485-29-4

302-01-2

123-3 1-9 4522

35554-44-0

81335-37-7

81335-77-5

36734- 19-7

7439-89-6 5 000

78-83-1

78-59- l

33820-53-0

67-63-0

98-82-8

82558-50-7

77501-63-4

7439-92-1 40 @ H < 50),.l l 200

50 @ H = 50 - < 1005,2

1

60 @ H = 100 - < 2005

'21

11 0 @ H = 200 - < 3005

'21

160 @ H;:: 3005'21

206

NA 32 500

330-55-2 70 0.07 1 ~, 3.3 1\1

7439-93-2 2 5002:,

COLUMN 5 COLUMNS

Livestock2

Drinking Water3

l'-"J Fn\AI\ \LIHJ

1.54

204

1504

1004

14

0.054

2.54

504

1 0004

1 0004

1504

6 500 lL,U

1 0004

1504

604

8 0004

4004

2004

84

100 10 '

84

5 000 84

"O ~

(1q en

-..)

0 .....,.,

UJ -.J

COLUMN 1

St!bstanc~

malathion

ma!ononitri!e

mancozeb

maneb

manganese 40'41

mecoprop (MCPP]

mercury

merphos

metalaxyl

methacrylonitrile

methamidophos

methanol

methidathion

methomyl

methoxy-5-nitroaniline, 2-

methoxychlor


methoxyethanol, 2-

methyl acetate


methyl hydrazine

methyl mercury

methyl methacrylate



methylaniline, 2-

methylaniline, 4-

methylaniline, N-


COLUMN 2 COLUMN3 COLUMN 4 Chemical Abstract Service# Aquatic Ufe

2 Irrigation

2

(GAS) \'"'"'I

/l\AI\ , ... , 121-75-5 1

109-77-3

80 18-01-7

12427-38-2

7439-96-5 200

93-65-2

7439-97-6 0.25 1

150-50-5

57837-19-1

126-98-7

10265-92-6

67-56-1

950-37-8

16752-77-5

99-59-2

72-43-5

110-49-6

109-86-4

79-20-9

78-93-3

60-34-4

22967-92-6 0.04

80-62-6

1634-04-4 34 0005

, 4 4006

99-55-8

95-53-4

106-49-0

100-61-8

COLUMN 5 COLUMNS

Livestock2

Drinking Water3

(LW} {DW)

190 190 1

0.44

1004

204

I 500 1L , IJ

44

2 1'

0.14

2504

54 .~

0.24

8 0004

44

1004

3'1

900 204

304

204

4 0004

2 5004

44

0.44

5 5004

11 000 95lL,l.J

154

14

54

84

'O P:l

OCI (1)

00 0 _,., UJ -..l

COLUMN 1

S!..!bstanc~


methylene-bis(2-chloroaniline), 4,4'-

methylene-bis(N,N-dimethyl) aniline, 4.4'-methylenebisbenzenarnine, 4,4'-



methylphenol, 2-

rnethylphenol, 3-

methylphenol, 4-

methylphenol, 4-chloro-3-

methylstyrene, alpha-

metolachlor

metribuzin

metsulfuron-methyl

mirex

molinate

molybdenum

monochloraminel5

monochloroacetic acid

rnonomethylarsonic acid

myclobutanil

naled

naphthalene

naphthylarnine, 2-

napropamide

SCHEDULE 3.2 GENERIC NUMERICAL WATER STANDARDS' - - --- - --


2 Irrigation

2

(GAS) /A\AI\ (!W} V'"""'

56-49-5

101-14-4

101-61-1

101-77-9

90-12-0

91-57-6

95-48-7 2 50022

108-39-4 80022

106-44-5 70022

59-50-7

98-83-9

51218-45-2 80 28

21087-64-9 10 0.5

74223-64-6

2385-85-5

2212-67-1

7439-98-7 10 000 10 - 304~

10599-90-3 5

79-11-8

124-58-3

88671 -89-0

300-76-5

91-20-3 IO

91-59-8

15299-99-7

COLUMN 5 COLUMN 6

Livestock2

Drinking Wate/ (LW} (DW)

0.024

'8

0.54

3.54

0.14

5.54

154

2004

2004

4004

4004

3004

50 507

80 801

I 0004

0.00854

84

50 250-"Y

3 0001

80 7,50

404

1004

84

804

0.0854

4004

"O P:>

()'q ~

'° 0 ......,

VJ -..)

COLUMN 1

S~bsta!"'!ce

nickel

nitrate (as N)

nitrate and nitri te (as N)

nitrilotriacetic acid [NT A)

nitrite (as N)

nitroani line, 2-

nitroaniline, 4-

nitrobenzene

nitrofurazone

ni troglycerin

nitroguanidine

nitropyrene, 4-

nitrosodiethanolamine, N-

nitrosodiethylamine, N- (NDEA]

nitrosodimethylamine, N- [NOMA]






SCHEDULE 3.2 G ENERIC NUMERICAL WATER STANDARDS'


2 Irrigation

2

(GAS) \""'

/ l\A/\ , ... , 7440-02-0 250@ H < 605.2 1 200

650@ H 60 - < 1205'2 1

I 100 @ H 120 - < 1805

'2 1

1500@H2'. 1805'2 1

836

14797-55-8 400 mg/L) I

NAj.l 400 mg/L) I

139-13-9

14797-65-0 200 (Cl < 2 mg/L))J

400 (Cl 2 - < 4 mg/L) 53

600 (Cl 4 - < 6 mg/L) 53

800 (Cl 6 - < 8 mg/L) 53

1 000 (Cl 8 - < 10 mg/L) 53

2 000 (Cl ~ 10 mg/L) 53

88-74-4

100-0 1-6

98-95-3

59-87-0

55-63-0

556-88-7

57835-92-4

1116-54-7

55-18-5

62-75-9

924-1 6-3

62 1-64-7

86-30-6

10595-95-6

59-89-2

COLUMN 5 COLUMNS

Livestock2

Drinking Water3

{LW} {DW)

I 000 804

1oomg1e.l 10 mg/L 1').l

100 mg/L).l 10 mg/L 1''.l

4001

IO 000 1 ooo'

404

84

84

0.14

0.4'+

4004

0. 154

0.0554

0.0054 '~

0.041

0.034

0.024

304

o.oot 0.025

4

"Cl ~

(1Q (D

........ N 0 0 ....., ........ (.;.)

--.J

COLUMN 1

Substance



nitrotoluene, 2-

nitrotoluene, 3-

nitrotoluene, 4-

nonane, n-

nonaqueous phase liquids0 1

' )4

nonylphenol and nonylphenol

ethoxylates55

'56

norflurazon

octahydro-1 ,3,5, 7-tetrani tro-1,3 ,5, 7-tetrazocine fHMXl octamethylpyrophosphoramide roMPAl octyl phthalate, di-N- [DNOP]

oryzalin

oxadiazon

oxamyl

oxyfluorfen

paclobutrazol


parathion

parathion, methyl

pebulate

pendimethal in

pentachlorobenzene, 1,2,3,4,5-

pentachloroethane

pentachloronitrobenzene [PCNB]

pentachlorophenol [PCP]



2 Irrigation

2

(CAS} (AWj \11Y I

100-75-4

930-55-2

88-72-2

99-08-1

99-99-0

111-84-2

NAjl not present not present

84852-15-3 10) , l'

27314-13-2

2691-41-0

152-16-9

117-84-0

19044-88-3

19666-30-9

23135-22-0

42874-03-3

76738-62-0

1910-42-5

56-38-2

298-00-0

1114-71-2

40487-42-1

608-93-5 60

76-01-7

82-68-8

87-86-5 I - llOLO

COLUMN 5 COLUMN 6

Livestock2

Drinking Water3

11\AI\ 1nul\ \L..'t''I'/ ,_ .. ,

0.0154

0.0754

0.74

0.44

104

14

not present not present

451L

1504

2004

84

404

2004

204

1004

104

504

IO 10 '

50 254

14

2004

1504

34

1.54

0.64

3024 607,13

'O s:i:>

OQ (1)

N

0 ......,

VJ -..J

COLUMN 1

~UUO:.lc:lll~

pentaerythritol tetranitrate (PETN]

perchlorate

perfluorobutane sulfonate [PFBS] Yi

perfluorooctane sulfonate [PFOSf'

perfluorooctanoic acid (PFOAJ' 1

pennethrin (cis +trans)

phenanthrene

phenmedipham

phenol

phenol, 2-methyl-4,6-dinitro (DNOC]

phenothiazine


phenylenediamine, o- [OPD]

phenylenediamine, p- (PPD]

phenylphenol, 2-

phorate

phosmet

phthalic acid, p-

picloram

picramic acid

picric acid

pirimiphos, methyl

prochloraz

profluralin

prometon

prometryn

propachlor

propanil


COLUMN 2 COLUMN 3 COLUMN 4 Chemical Abstract Service# Aquatic Life2 Irrigation

2

/,....AC\

(AW) (iW) , ___ ,

78-11-5

14797-73-0

375-73-5

1763-23-1 60

335-67-1

52645-53-1 0.04', 0.016°

85-01-08 3

13684-63-4

108-95-2 2000u

534-52-1 750u

92-84-2

108-45-2

95-54-5

106-50-3

90-43-7

298-02-2

732-11-6

100-21-0

1918-02-1 290 0.5

96-91-3

88-89-1

29232-93-7

67747-09-5

26399-36-0

1610-18-0

7287-19-6

1918-16-7

709-98-8

COLUMNS COLUMN 6

Livestock2

Drinking Water3

(LW) \Ll'IWJ

84

34

804

0.3 1l

0.2 1L

4501.l

1 0004

I 0004

14.~

24

254

3.54

7504

804

2 2'

804

4 0004

190 1901

0.44

3.54

404

14

254

604

154

504

204

"O p:>

(1q ~ ...... N N 0 ......,

w -...J

COLUMN 1

Subst:::~ce

propargite

propargyl alcohol

propazine

propham

propiconazole

propylbenzene, 1-

propylene glycol, 1,2-

propylene glycol monomethyl ether

propylene oxide

propyzamide

pyrene

pyridine

quinalphos

qui no line

quizalofop-ethyl

resmethrin

resorcinol

ronnel

rotenone

salinity)~

selenious acid

selenium

sethoxydim



2 Irrigation

2

(CAS) (Av"V) , ... , 2312-35-8

107-19-7

139-40-2

122-42-9

60207-90-1

103-65-1

57-55-6 5 000 mg/L

107-98-2

75-56-9

23950-58-5

129-00-0 0.2

110-86-1

13593-03-8

91-22-5 34

76578-14-8

10453-86-8

108-46-3 15022

299-84-3

83-79-4

NA.iL 155,59,60

10 if natural salinity is 0 - < 3.56,59,61

20 if natural salinity is 3.5 - < 13.56,59,6 1

40 ifnatural salinity is 13.5 - > 356,59,61

7783-00-8

7782-49-2 20 20°i, 50°.l

74051-80-2

COLUMN 5 COLUMN 6

Livestock2

Drinking Water3

/I \Al\ {DW) \ ..... , 80

4

84

804

804

504

4004

80 mg/L 4

3 0004

0.654

3004

1004

44

24

o.o5•

354

1004

4 500u

2004

154

204

30 10(>4

3504

'"O i:.:i

(1Q (1l

N VJ

0 .......,

VJ -....)

COLUMN 1

S~bstar!ce

si lver

si lvex

simazine

sodium ion

strontium

strychnine

styrene

styrene-acrylonitrile [SAN) trimer (all isomers) sulfate

sulfide (as H2S) 0'

sulfo lanej4

sul fotep

TCMTB

tebuthiuron

temephos

terbaci l

terbufos

terbutryn



tetrachloroethane, l , I, 1,2-

tetrachloroethane, 1, 1,2,2-

tetrachloroethylene



2 Irrigation

2

(CAS) \M1'Y/

Jl\AI\ , ... , 7440-22-4 0.5 @ H S 1005

.21

15 @ H > 1005,2

1

156

93-72-1

122-34-9 100 0.5

17341-25-2

7440-24-6

57-24-9

100-42-5 720

NAj 2

14808-79-8 1 280 mg/L @ H ~ 3021

2 180 rng/L @ H 31 - 7521

3 090 mg/L @ H 76- 18021

4 290 mg/L ~ H > 18021

7783-06-4 20

126-33-0 500 000 8 400

3689-24-5

21564- 17-0

340 14- 18-1 16 0.25 1y

3383-96-8

5902-51-2

13071 -79-9

886-50-0

634-66-2 18

95-94-3

630-20-6

79-34-5

127-1 8-4 1 100

COLUMN 5 COLUMNS

Livestock2

Drinking Water3 {LW) (DW)

204

304

10 101

200 mg/L12

2 5004

14

8004

104

1 000 rng/L 500 rng/L 7'24

501,L4

14 000 90 1l

24

1004

130 3004

280 804

504

1 11

44

14

64

0.84

301

"O PJ

(IQ (t>

~ 0 ......,

VJ -..J

COLUMN 1

S!.!bs!a~~-e




tetrachlorovinphos

tetraethyl lead

tetrahydrofuran

tetryl

thall ium

thifensulfuron-methyl

thiobencarb

thiocyanate

thiodiglycol

thiofanox

thiophanate, methyl

thiophenol

thiram

tin

titanium

toluene

toxaphene (all isomers)

tralomethrin

triadimefon

triallate

triasulfuron

tribenuron-methyl


tribufos

tributyl phosphate

SCHEDULE 3.2 - ... -- . . -GENERIC NUMERICAL WATER STANDARDS'


2 Irrigation

2

(CAS) V"'UJ

11\11.1\ , ... , 4901 -51-3 2 - 260'lb

58-90-2 5.5 - 720.lb

935-95-5 2.5 - 340.lb

96 1-1 1-5

78-00-2

109-99-9

479-45-8

7440-28-0 3

79277-27-3

28249-77-6

302-04-5

111-48-8

39196-1 8-4

23564-05-8

108-98-5

137-26-8

7440-3 1-5

7440-32-6 1 000

108-88-3 5~, 2 ooo<> 8001 -35-2 0.08

66841 -25-6

4312 1-43-3

2303- 17-5 2.4

82097-50-5

10 1200-48-0

6 15-54-3

78-48-8

126-73-8

COLUMN 5 COLUMN 6

Livestock2

Drinking Water3

(LW) (DW)

l .l4,66

l .l4,b(J 1007,13

1.l4,b(J

6.54

0.00 1 4'~

3 5004

84

504

404

0.84

3004

1"

3004

44

204

2 5004

607,13

5 0. 154

304

1004

230 504

404

304

204

0.14

154

'O ll:>

oq (l>

N Vl

0 ......,

VJ -..}

COLUMN 1

.-:JUU~ldlU, .. '1::

tributyltin

trichloro-1,2,2-trifluoroethane, 1, l ,2-




trichloroethane, l, l , 1-

trichloroethane, I , 1,2-

trichloroethylene








trichlorophenoxy acetic acid, 2,4,5-f2 ,4,5-Tl trichloropropane, 1, 1,2-




tricyclohexyltin

tridiphane

triethylene glycol

triethyltin

trifluralin

trimethyl phosphate




2 Irrigation

2

lr>AC>\

(AVV) (iWj \"-'-'-'/

36643-28-4 0.08:>, 0.05("~

76-13-1

634-93-5

87-61-6 80

120-82-1 240), 54°

71-55-6

79-00-5

79-01-06 200

75-69-4

15950-66-0 2.5 - 32016

933-78-8 2.5 - 34026

933-75-5 8 - 1 08026

95-95-4 2.5 - 30026

88-06-02 6 - 80020

609-19-8 I - 12816

93-76-5

598-77-6

96-18-4

96-19-5

1330-78-5

NA32

58138-08-2

112-27-6

NA3l 4

1582-09-8 2

512-56-1

108-67-8

COLUMN 5 COLUMN 6

Livestock2

Drinking Water3

(L'W) \UH/

250

100 0004

0.14

34

5.54

s ooo" 34

50 5'

1 ooo" 2L4,b l

224,67

224,6/

224,67 4004

224,67 57,13

2L4,b/

20 404

204

o.54 '~

104

so"

250

104

8 0004

45 45 1

8"

404

'O c:>

(JQ (D

N 0\ 0 ......,

w -...)

COLUMN 1

S!.!bsta!'?c~



triphenyltin

tris( 1,3-dichloro-2-propyl)phosphate fTDCPP] tris( l-chloro-2-propyl)phosphate fTCPPl tris(2,3-dibromopropyl)phosphate


tris(2-ethylhexyl)phosphate

tungsten

uranium

vanadium

vemolate

VHw6-10j'• 68

Vinclozolin

vinyl acetate

vinyl chloride

VPHw0~

warfarin

xylenes, total

zinc

zineb



2 Irrigation

2

(GAS) \l"\H/

/l\A/\ , ..... ,

99-3S-4

118-96-7

668-34-8 0.2

13674-87-8

13674-84-5

126-72-7

l lS-96-8

78-42-2

7440-33-7

7440-61-1 85 10

7440-62-2 100

1929-77-7

NA.l.t 15 000 JS 000

S0471-44-8

108-0S-4

7S-01-04

NAJ.t I SOO

81-81-2

1330-20-7 300

7440-66-6 75 @ H < 90~'1 1 1 000 @ pH < 6.0 10

150 @ H = 90 - < 1005'21

2 000 @ pH 6.0 - < 7.070

900 @ H = JOO- < 2005'21

5 000 @ pH > 7.070

1 650@ H = 200- < 3005

'21

2 400 @ H = 300 - < 4005'21

1006

12122-67-7

COLUMN 5 COLUMNS

Livestock2

Drinking Water3

{LW) (DW)

1004

24

800

804

404

0.074

8"

S04

34

200 20 '

100 204

44

15 000 JS 000

1004

4 0004

2 '

14

90 1

2 000 3 000 1.l

2004

"d P:>

oq (1)

;:::; -..J

0 ......,

;:::; -...)

Notes I All values are in µg/L unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental

Laboratory Manual, as updated from time to time, a director's protocol or alternate methods acceptable to a director. 2(a) Aquatic life standards assume minimum 1: 10 dilution is available. Aquatic life standards are to protect freshwater and marine life unless otherwise

indicated. 2(b) Standards for all organic substances are for total substance concentrations. Any water sample to be analyzed for organic substances should not be

filtered. 2(c) Standards for surface water samples to be analyzed for heavy metals, metalloids and inorganic ions are total substance concentrations. In addition, it

is recommended that surface water samples being analyzed for heavy metals, metalloids and inorganic ions should also be analyzed for dissolved substance concentrations.

2(d) Standards for groundwater samples for heavy metals, metaiioids and inorganic ions are for dissolved substance concentrations. In addition, it is recommended that groundwater samples being analyzed for heavy metals, metalloids and inorganic ions should also be analyzed for total substance concentrations.

2(e) Standards for irrigation water apply to irrigation of all soil types, unless otherwise indicated.

4

5 6 7 8

':J

10 11 12

13

14

15 16

17

Drinking water standards are for unfiltered samples obtained at the point of consumption. Heavy metals, metalloids and inorganic ions are expressed as total substance concentrations unless otherwise indicated. Standard is based on the 2015 United States (US) Environmental Protection Agency (EPA) "Regional Screening Levels'' for tapwater. The EPA Regional Screening Levels for both non-carcinogenic and carcinogenic substances reflect the 1996 "Overview of CSST Procedures for the Derivation of Soil Quality Matrix Standards for Contaminated Sites" 20% (i.e., 0.2) Toxicity Reference Value (TRY) apportionment for drinking water exposure. For carcinogenic substances, the EPA Regional Screening Level is also adjusted to reflect section 18 (3) (a) of this regulation, with a human lifetime cancer risk of less than or equal to one in JOO 000. Standard to protect freshwater aquatic life. Standard to protect marine and estuarine aquatic life. Standard is set equal to the 2014 Health Canada "Guidelines for Canadian Drinking Water Quality" for the substance. Standard is set equal to the 2016 British Columbia Environmental Laboratory Technical Advisory Committee reference analytical detection limit for the substance. Standard to protect crops other than legumes. Standard to protect legumes. Standard is applicable to the sum of the concentration of aldrin and dieldrin. Standard is specific to protection of human health. Standard is derived with TRY protective of adults. Standard may not adequately protect other age groups. Standard may not address aesthetic (organoleptic) concerns related to drinking water quality. Water treatment may be required.

Standard varies with pH and temperature. I0°C is assumed. Consult a director for further advice.

Standard varies with pH, temperature and salinity. 10 °C and 10 practical salinity units (psu) are assumed. Consult a director for further advice. Standard is expressed in million fibres> lOµm/L (m.f./L). Standard is set equal to the 2010 US EPA Safe Drinl..,"ing Water Act. National Primary Drinking Water Regulations standard for the substance. Standard varies depending on crop as follows:

Crop Standards (µg/L)

blackberry 500 barley, cherry, cowpea, garlic, grape, Jerusalem artichoke, kidney bean, lima bean, mung bean, onion, peach, plum, 1000 sesame, strawberry, sunflower. sweet potato, wheat carrot, cucumber, pea, ootato, radish, red oeooer 2000

18 19 20

21 n

D ~

~

~ n ~

~ ~ ~ ~ ~

N ~

00

~ 31 n ~

~

TI ~

~

~

n ~

w ~

41 ~

~

Standard to protect crops other than cereals, tame hays and pasture. Standard to protect cereals, tame hays and pasture crops. Standard is specific for total oihalomethanes. Sum of the concentrations of bromodichloromethane (BDCM), dibromochloromethane (DBCM), brcmcforrc (uibrcmcmethane), and chloroform (trich!oromethane) m1_1st not e:xr:e.eci the standard specified. H mean water hardness in mg/L CaCO,_ Standard derived by the British Columbia Ministry of Environment, Land Remediation Section in accordance with CSR 2016 Protocol 28, "Standards Derivation Methods". Standard to protect all types of crops. Standard to protect against taste and odour concerns. Substance is extremely labile in water. Extended hold times are inappropriate. It is recommended that samples be analyzed in the field or immediately upon receipt by the laboratory. Standard varies with pH, temperature and substance isomer. Consult a director for further advice. Standard is applicable to the sum of concentrations of all chlorophenol isomers. Analytical results for chromium (all species) in water may be used to demonstrate compliance with the standards. Where the standards cannot be met based on analytical results for chromium (all species), chromium speciation may be necessary. To demonstrate compliance with the aquatic life (AW) standard, samples for cyanide in water must be analyzed using the appropriate "Cyanide Weak Acid Dissociable (WAD)" analytical method for water specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from time to time. To demonstrate compliance with the drinking water (DW) standard, samples for cyanide in water must be analyzed using the appropriate "Cyanide Strong Acid Dissociable (SAD)" analytical method for water specified in the 2015 British Columbia Environmental Laboratory Manual, as updated from time to time. Standards are for the sum of DDT (2,4' + 4,4" isomers), DDD (2,4' + 4,4" isomers), and DDE(2,4' + 4,4" isomers). NA - not applicable. No CAS number exists for the substance. Standard is applicable to the sum of concentrations of all dichlorophenol isomers. Standards apply to a site used for an industrial or commercial purpose or activity set out in Schedule 2 as item F2, F3, F7, or FIO. Standard to protect cereal crops and hay. Standard to protect lactating dairy animals. Standard is applicable at all sites, irrespective of water use. EPHw!0-19 - Extractable Petroleum Hydrocarbons (nC!O-nC 19) in water, as defined in the 2015 British Columbia Environmental Laboratory Manual, as updated from time to time. Standards apply to a site used for an indusoial or commercial purpose or activity set out in Schedule 2 as item H 18orH19. Standard varies with type of livestock. Consult a director for further advice. Standard is applicable to the sum of the concentrations of heptachlor and heptachlor epoxide. Standard is applicable to the sum of the concentrations of all hexachlorocyclohexane isomers. Standards apply to a site used for an industrial or commercial purpose or activity set out in Schedule 2 as (a) item A6, A7, A8, or All , (b) item Cl, C2, C3 , C4, or C6, (c) item D2, D3, D5 or D6, (d) item E4, or (e) item Hl4.

"O ~

(lq en

t3 \0 0 ......, -U.) -.]

44 Standards apply to a site used for an industrial or commercial purpose or activity set out in Schedule 2 as item H 11 or H20, but only if the site was used for that purpose or activity in conjunction with, or as a result of, the site also being used for at least one of the purposes or activities set out in Note 43.

45 LEPHw - Light Extractable Petroleum Hydrocarbons in water, as defined in the 2015 British Columbia Environmental Laboratory Manual, as updated from time to time.

46 Standards apply to a site used for an industrial or commercial purpose or activity set out in Schedule 2 as (a) item Bl,

47

48 49 50

51 52 53 54 55

56

57

(h) item Cl, C3 or C4. (c) item D2, D3, D5 or D6, (d) item E4, or (e) item H3 or Hl4. Standards apply to a site used for an industrial or commercial purpose or activity set out in Schedule 2 <is item H 11 or H20 but only if the site was used for that purpose or activity in conjunction with, or as a result of, the site also being used for at least one of the purposes or activities set out in Note 46. Standard varies with crop, soil drainage and Mo:Cu ratio. Consult a director for further advice. Standard is set equal to 1986 British Columbia Ministry of Environment drinking water quality guideline for the substance. Standard is specific for total haloacetic acids. Sum of the concentrations of monchloroacetic acid (MCA), dichloroacetic acid (DCA). trichloroacetic acid (TCA), monobromoacetic acid (MBA) and dibromoacetic acid (DBA) must not exceed the standard specified. Standard may not protect all amphibians. Consult a director for further advice. Where nitrate and nitrite are present, total nitrate plus nitrite-nitrogen should not exceed this value. Standard varies with chloride concentration. Consult a director for further advice. Water must be remediated so that nonaqueous phase liquids are not present in quantities in excess of that acceptable to a director. Nonylphenol includes related nonylphenolic and octylphenolic compounds, including ethoxylates and ethoxycarboxylates. Consult a director for further advice. Standards apply to a site used for an industrial or commercial purpose or activity set out in Schedule 2 as (a) item A6, A8, AIO or Al2, (b) item HI I, Hl8 or Hl9, or (c) item 12 or I3. Standards apply to a site used for an industrial or commercial purpose or activity set out in Schedule 2 as (a) item A4, (b) item C3, (c) item EIO, or (d)itemGl.

58 Standard is for salinity measurements be electrical conductivity or density methods using the Practical Salinity Scale, which closely equates to concentration units c 59 Standard applies only if minimum I: IO dilution is available in receiving waterbody. 60 Freshwater is defined as water having a natural salinity < 1.5 psu. 61 Standard varies with natural salinity of receiving waterbody. 62 Standard for continuous applications on crops. 63 Standard for intermittent application on crops. 64 Standard is set equal to 2014 British Columbia Ministry of Environment drinking water quality guideline for the substance. 65 Standard is for un-ionized sulfide (as l-1,S). Measurement of either total or dissolved sulfide (as l-1,S) may be used to demonstrate compliance with the

standards. Where the standards cannot be met by measuring total or dissolved sulfide (as H2S), determination of un-ionized sulfide (as l-1,S) may be necessary.

66 Standard is applicable to the sum of concentrations of all tetrachlorophenol isomers. 67 Standard is applicable to the sum of concentrations of all trichlorophenol isomers. 68 VHw6-IO- Volatile Hydrocarbons (nC6-nCIO) in water, as defined in the 2015 British Columbia Environmental Laboratory Manual, as updated from time to time.

"O ~ ~ ~

VJ 0 0 !-+)

VJ -J

69 VPHw - Volatile Petroleum Hydrocarbons in water, as defined in the 2015 British Columbia Environmental Laboratory Manual , as updated from time to time. 70 Standard varies with soil pH.

't:S c:>

(Jq (1)

,_. (.;.l

0 ....,.,

(.;.l -..J

I

I

COLUMN 1

Substance

acetaldehyde acetone acetone cyanohydrin acetonitrile acrolein acrvlonitrile allvl chloride ammonia (as N) benzene benzotrichloride benzvl chloride bis(2-chloro-1 -methvlethyl) ether bis(2-chloroethyl) ether bis(2-chloromethvl) ether bromobenzene bromodichloromethane fBOCMl bromofonm bromomethane butadiene, 1,3-carbon disulfide carbon tetrachloride chlorine (Cl,) chloro-1 , 1-difluoroethane, I-ch lorobenzene chlorobenzotrifluoride, 4-chlorobutane, 1-chlorodifluoromethane chloroethane chlorofonm ch loromethane chloronitobenzene, 4-chloroohenol, 2-chloroprene

SCHEDULE 3.3 GENERIC NUMERICAL VAPOUR STANDARDS1

•2

.3•4•5

COLUMN 2 COLUMN3 COLUMN4

I

Chemical Agricultural, Abstract Service Urban Park,

Number Residential Commercial (CAS) Use Standard6 Use Standard 7

75-07-0 4.5 15 67-64-l 2000 5 500 75-86-5 2 6 75-05-8 60 200 107-02-8 0.2'" 0.2'" 107-13-1 0.5'" 0.5'" 107-05-1 1 3

7664-41-7 100 300 71-43-2 1.5 4 98-07-7 I'" l'" 100-44-7 0.2 0.6 108-60-1 80 250 11 1-44-4 1'" l'" 542-88-1 l'" I'" 108-86-1 60 200 75-27-4 40 100 75-25-2 9 30 74-83-9 5 15 106-99-0 2'" 2'" 75-15-0 700 2 000 56-23-5 1.5 5

7782-50-5 20'" 201"

75-68-3 50 000 150 000 108-90-7 10 30 98-56-6 15 40 109-69-3 80 250 75-45-6 50 000 150 000 75-00-3 10000 30 000 67-66-3 100 300 74-87-3 90 250 100-00-5 1'" 2 95-57-8 10 30 126-99-8 I'" 1'"

COLUMN 5 COLUMN 6

I I I Industrial Parkade

Use Standard8

Use Standard9

40 35 35 000 15 000

20 15 550 500 0.2'" 0.2 '"

1.5 I 9 8

900 800 IO IO 1'" 1'" 2 1.5

1 500 650 I'" I'" I '" I'"

550 500 800 300 85 75 45 40 3 2.5

6 500 5 500 15 15

20'" 20 111

450 000 400 000 90 80 100 100

1 500 650 450 000 400 000 90000 80 000

900 800 800 700 5.5 5 200 80 l'" I'"

'"d ~

(IQ n

VJ N 0 '""" (..,.)

-.J

I

I

COLUMN 1

Substance I

chloroorooane, 2-chlorotoluene, 2-crotonaldehvde, trans-cvanide cyano_gen cyanogen bromide cyanogen chloride dibromo-3-chloroorooane, 1,2-dibromobenzene, 1,4-dibromochloromethane fDBCMl dibromoethane, 1,2-dibromomethane dichloro-2-butene, 1,4-dichlorobenzene, J ,2-dichlorobenzene, 1,3-dichlorobenzene, 1,4-dichlorofluoromethane dichloroethane, l , 1-dichloroethane, 1,2-dichloroethylene, 1,1-dichloroethvlene, 1,2- cis dichloroethylene, 1.2- trans dichloromethane dichloroorooane, 1,2-dichloropropane, 1,3-dichloroorooene, 1,3- (cis +trans) dicvclopentadiene diethyl ether dimethvlamine dimethylaniline, N,N- fDMAl epichlorohydrin eooxvbutane, 1,2-ethvl acetate

SCHEDULE 3.3 GENERIC NUMERICAL VAPOUR ST ANDA RDS i,z.3,4•

5

COLUMN2 COLUMN3 COLUMN4

I I Chemical Agricultural,

Abstract Service Urban Park, Number Residential Commercial (CAS) Use Standard

6 Use Standard7

75-29-6 60 150 95-49-8 40 100 123-73-9 2 6 57-12-5 2 1U 3.5

460-19-5 10'" 10'" 506-68-3 200 550 506-77-4 JOO 300 96-12-8 JIU 1'" 106-37-6 20 60 124-48-1 40 100 106-93-4 0.5'" 0.5' " 74-95-3 4 10

764-41-0 l'"·" l '"· '' 95-50-1 200 600

541-73-1 60 200 106-46-7 800 2 500 75-71-8 JOO 300 75-34-3 500 1 500 107-06-2 7 20 75-35-4 200 600 156-59-2 60 200 156-60-5 60 200 75-09-2 600 2000 78-87-5 4 10 142-28-9 1 3 542-75-6 2.5 7.5 77-73-6 1'" !'" 60-29-7 400 1000 124-40-3 l'" l'" 121-69-7 4 10 106-89-8 l 3 106-88-7 20 60 141-78-6 70 200

COLUMNS COLUMN 6

I Industrial Parkade

Use Standard8

Use Standard9

1000 450 800 300 40 15 25 9.5 40 15

3 500 1500 2000 800

2 1.5 400 150 800 300

0.5'" 0.5'" 35 30

llU.11 l '"·" 2 000 l 500 1 000 500 7 500 6 500 900 800

4 500 4 000 65 55

2 000 I 500 550 500 550 500

5 500 5 000 35 30 20 8 25 20 2.5 2.5

8 000 3 000 I'" JIU

80 30 9 8

200 150 650 550

"Cl P'

()q (1)

l;.) l;.)

0 .......,

l;.) -..)

COLUMN 1

Substance I ethyl acrylate ethvl methacrv late ethyl benzene ethylene oxide furan hexachlorobutadiene hexachlorocvclooentadiene hexachloroethane isopropylbenzene methacrvlonitrile methvl acetate methvl acrvlate methyl ethyl ketone rMEKl methyl isobutvl ketone rMIBKl methvl mercaptan methyl methacrylate methyl tert-butvl ether rMTBEl methylcyclohexane methvlstvrene, alpha-naphthalene n-decane n-hexane nitrobenzene nitrotoluene, 2-phosphine oroPvlene oxide pyridine strvrene tetrach loroethane, 1, 1, 1,2-tetrachloroethane, I, 1,2,2-tetrachloroethvlene tetrahvdrofuran toluene

SCHEDULE 3.3 GENERIC NUMERICAL VAPOUR STANDARDS1,z.3,4,s

COLUMN 2 COLUMN3 COLUMN4

Chemical

I

Agricuicurai,

I

Abstract Service Urban Park, Number Residential Commercial (CAS) Use Standard

6 Use Standard

7

140-88-5 8 25 97-63-2 300 900 100-41-4 1000 3 000 75-21 -8 10'0 IO'" 110-00-9 2 6 87-68-3 l '" 1.5 77-47-4 I '" I'" 67-72-1 30 90 98-82-8 400 I 000 126-98-7 30 90 79-20-9 2 000 6 000 96-33-3 20 60 78-93-3 5 000 15 000 108-10-1 3 000 9 000 74-93-1 2'" 3.5 80-62-6 700 2 000

1634-04-4 3 000 9 000 108-87-2 1 500 5 000 98-83-9 150 400 91 -20-3 3 9 124-18-5 2 500 8 000 110-54-3 700 2 000 98-95-3 l'" l'" 88-72-2 2 5.5

7803-51-2 10 '" 10'" 75-56-9 2.5 8 110-86-1 100 350 100-42-5 1 000 3 000 630-20-6 1.5 4 79-34-5 40 100 127- 18-4 40 100 109-99-9 3.5 10 108-88-3 5 000 15 000

COLUMN 5 COLUMNS

I I I

Industrial P•<k•d< I Use Standard

8 Use Standard

9

75 65 2 500 2 500 9 000 8 000 IO'" 10'" 40 15 4 3.5 2 1.5

250 250 3 500 3 000 250 250

40000 15 000 200 150

45 000 40000 25 000 25 000

20 9 6 500 5 500

25 000 25 000 35 000 15 000 2 500 I 000

25 25 25 000 20 000 6 500 5 500

2.5 2 35 15 IO'" 10'" 25 20

I 000 950 9 000 8 000

10 10 800 300 350 300 30 25

45 000 40 000

"O p)

Otl ('1>

(.;.) .j:::.

0 .....,.,

(.;.)

-.:r

SCHEDULE 3.3 GENERIC NUMERICAL VAPOURSTANDARDS1.2,3,

4,s --- - - - · - - - - - - - -

COLUMN 1 COLUMN 2 COLUMN3 COLUMN4 COLUMN 5 COLUMN 6

Chemical

I Agriculturai,

I I I

Abstract Service Urban Park, Number Residential Commercial Industrial Parkade

Substance (CAS) Use Standard6 Use Standard7 Use Standard8

Use Standard9

trichloro-1,2,2-trichloroethane, 1 1,2- 76-13-1 30000 90000 250 000 250 000 trichlorobenzene, 1.2.4- 120-82-1 7 20 65 55 trichloroethane, 1,1,1- 71-55-6 5 000 15 000 45 000 40 000 trichloroethane, 1, 1,2- 79-00-5 0.5 1

" 0.6 2 1.5 trichloroethylene 79-01-06 2 6 20 15 trichlorofluoromethane 75-69-4 700 2 000 6 500 5 500 trichloroorooane, 1, 1,2- 598-77-6 10 30 200 80 trichloroorooane, 1,2,3- 96-18-4 0.5 1

" 0.9 2.5 2.5 trichloroorooene, 1,2,3- 96-19-5 0.5'" 0.9 2.5 2.5 triethylamine 121-44-8 7 20 65 55 trimethylbenzene, 1,2,4- 95-63-6 7 20 65 55 trimethvlbenzene, 1,3,5- 108-67-8 3.5 10 65 25 vinyl acetate 108-05-4 200 600 2 000 1500 vinyl bromide 593-60-2 I'" l'" 3 2.5 vinvl chloride 75-01-4 1 3.5 10 9 VPH" NAU 1 000 3 000 11500 8 000 xylenes, total" 1330-20-7 100 300 900 800 Notes 1 All values in µg/m 3 unless otherwise stated. Substances must be analyzed using methods specified in the 2015 British Columbia Environmental Laboratory Manual,

as updated from time, a director's protocol or alternate methods acceptable to a director. Vapour standards of this schedule are specific to human health only. It is the responsibility of the responsible person for the site to ensure that use of the vapour standards of this schedule do not constitute a significant risk or hazard to ecological health.

3 Soil, sediment or water giving rise to vapours must be remediated to the applicable vapour use standard for the substance. 4 Vapour standards applied to soil vapour may be adjusted for depth dependent attenuation as specified in a director's protocol. 5 Vapour standards apply to water at any site, irrespective of the water or site use, which gives rise to contaminated vapours. 6 Vapour standards agricultural, urban park and residential uses apply to soi l at agricultural land use, urban park land use and residential land use sites, as well as

freshwater or marine sediment at sensitive sediment sites, that give rise to contaminated vapours. Residential use vapour standards apply at both residential low density land use and residential high density land use sites, that give ri se to contaminated vapours. Vapour standards for commercial use apply to soil vapour at commercial land use sites that give risk to contaminated vapours. Vapour standards for industrial use apply to soil vapour at industrial land use sites and to freshwater or marine sediment at typical sediment sites, that give rise to contaminated vapours. Vapour standards for parkade use apply to soil vapour adjacent to parkades, irrespective of the site use that gives rise to contaminated vapours.

10 Standard is adjusted based on the 2016 British Columbia Environmental Laboratory Technical Advisory Committee reference analytical detection limit for the substance.

"d Po:>

(/q (P

..... t.>J Ul

0 .....,

u.i -....)

11 Standard for the substance applies to the sum of cis and trans isomers vapour concentrations. 12 VPHv - Volatile Petroleum Hydrocarbons in vapour includes the sum of those compounds that elute on a I 00% polydimethylsiloxane gas chromatographic column

beti.veen the retention times for n-hexane (nC6) and n-tridecane (nCI 3) minus the sum of benzene, ethylbenzene, n-decane, n-hexane, styrene, toluene and xylenes. 13 NA - not applicable. No CAS number exists for the substance. 14 Standard for the substance applies to the sum of ortho, meta and para isomers vapour concentrations.

SCH EDULE 3.4

GENERIC NUMERICAL SEDIMENT STANDARDS

COLUMN I COLUMN II COLUMN Ill COLUMN IV COLUMN V COLUMN VI

Marine and Ma ri ne and Freshwater Freshwater Estuarine Estuarine

Chemical Sediment2

Sediment2

Sediment3

Sediment3

Abstract Standard Standard Stand ard Standard Service for for for for Number 4 6 4

Substance (CAS} Sensiti ve Use Typical Us e Sensitive Use Typical Use

acenaphthene 83-32-9 0.055 0.11 0.055 0. 11 acenaphthv lene 208-96-6 0.08 0. 15 0.079 0.15 anthracene 120-1 2-7 0.15 0.29 0.15 0.29 arsenic 7440-38-2 11.0 20.0 26.0 50.06

benz( a )anthracene 56-55-3 0.24 0.46 0.43 0.83 benzo(a)pyrene 50-32-8 0.48 0.94 0.47 0.92 cadmium 7440-43-9 2.2 4.2 2.6 5.0 chlordane (cis + trans) 5103-71-9 0.0055 0.011 0.003 0.0057

& 5103-74-2 chromium 7440-47-3 56.0° 110.0 99.0 190.0

chrvsene 218-09-8 0.53 1.0 0.52 1.0 copper 7440-50-8 120.0 240.0 67.0 130.0 dibenz(a,h)anthracene 53-70-3 0.084 0.16 0.084 0.16 dichlorodiphenyldichloroethane 53- 19-0 0.0053 0.0 1 0.0048 0.0094 (2,4' + 4,4' isomers) [DDD] & 72-54-8 dich lorodiphenyldichloroethylene 3424-82-6 0.0042 0.0081 0.23 0.45 (2,4 ' + 4,4 ' isomers) [DDEl & 72-55-9 dich lorodiphenyltrich loroethane 789-02-6 0.003 0.0057 0.003 0.0057 (2,4' + 4,4' isomers) [DDT] & 50-29-3 die ldrin 60-57-1 0.0041 0.008 0.0027 0.0052 endrin 72-20-8 0.039 0.075° 0.039 0.075° fluoranthene 206-44-0 1.5 2.8 0.93 1.8 fl uorene 86-73-7 0.089 0.17 0.089 0. 17 heptach tor and 76-44-8 0.0017 0.0033° 0.0017 0.0033° heptachlor epoxide & 1024-57-3 hexachlorocyc:lohexane, gamma 58-89-9 0.00086° 0.00 17° 0 .0006} 0.0012

6

lead 7439-92-1 57.0 11 0.0 69.0 130.0 methylnaphthalene, 2- 9 1-57-6 0. 12 0.24 0.12 0.24 mercury 7439-97-6 0.3 0.58 0.43 0.84 naphthalene 91 -20-3 0.24 0.47 0.24 0.47 pentachlorophenol [PCP] 87-86-5 0.4' 0.8 1 0 . 36~ 0.69M

phenanthrene 85-01-8 0.32 0.62 0.34 0.65 polycycl ic aromat ic NA'" 10.0 20.0 10.0 20.0 hydrocarbons, total9 [PAHsl polychlorinated biphenyls, tota l' ' 1336-36-3 0.17 0.33 0.12 0.23 [PCBs] polychlorinated diox ins and furans 12 [PCDDs and PCDFs]

1746-01-6 0.00013° 0.00026° 0.00013 0.000266

pyrene 129-00-0 0.54 I. I 0.87 1.7 zinc 7440-66-6 200.0 380.0 170.0 330.0

Notes I . All values in ug/g dry weight (dwt) unless otherwise stated. Substance must be analyzed using methods specified in

the 2015 British Columbia Environmental Laboratory Manua l, as updated from time, a director's protocol or a lternate methods acceptable to a di rector.

2. Standards are specific to the protection of freshwater life. It is the responsibility of the responsible person for the site to ensure that use of the standards of this schedule does not constitute a signi fi cant risk or hazard to human heal th.

3. Standards are specific to the protection of marine and estuarine aquat ic life. rt is the responsibility of the responsible person for the site to ensure that the use of the standards of this schedule does not constitute a significant risk or hazard to he.man health.

4. Sensitive sediment use means the use of a site containing sediment as habitat for sensitive components of freshwater, marine or eHuar ine aquatic ecosystems. Consult a director for further advice.

page 136 of 137

5

5. Typical sediment use mt:ans the use ofa site containing sediment for a use that is not a sensitive sediment use . Consult a director for further advice.

6. Denotes a sediment standard which is considered less reliable or that could not be fully evaluated. 7. Standard has been set equal to the 1994 State of New York, Department of Environmental Conservation criterion for

the substanct:. 8. Standard has been set equal to the 1991 Washington State, Department of Ecology criterion for the substance. 9. PAHs, total in sediment includes:

acenaphthene, acenaphthylene, anthracene, benz( a )anthracene, benzo(a)pyrene, chrysene, dibenz(a,h)anthracene, fluoranthene, fluorene, methylnaphthalene, 2-naphthalene, phenanthrene , and pyrene.

10. NA - not applicable. No CAS number exists for the substance. 11. PCBs, total in sediment includes the sum of Arochlors 1016, 1221, 1232, 1242, 1248, 1254, 1260, 1262 and 1268. 12. Calculated using data for PCDDs, PCDFs, PCBs and associated PCDD, PCDF, PCB toxicity equivalency factors.

Consult a director for further advice.

page 137 of 137

m 366 · pdf filethe director, are prescribed in ... substances must be analyzed using methods...

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