POLLUTION CONTROL BOARD

NOTICE OF ADOPTED AMENDMENTS

1) Heading of the Part: Water Quality Standards

2) Code Citation: 35 Ill. Adm. Code 302

3)

Section Numbers:

Adopted Action:

 

302.208

Amend

 

302.303

Amend

 

302.304

Amend

 

302.504

Amend

 

302.510

Amend

 

302.553

Amend

 

302.595

Amend

 

302.648

Amend

 

302.657

Amend

 

302.669

Amend

4) Statutory Authority: Implementing Sections 5, 10, 13, 21, 22, 22.01, and 22.2 and authorized by Sections 27 of the Environmental Protection Act [415 ILCS 5/5, 10, 13, 21, 22, 22.01, 22.2, and 27]

5) Effective Date of Amendments: December 12, 2012

6) Does this rulemaking contain an automatic repeal date? No

7) Does this rulemaking contain incorporations by reference? Yes

8) A copy of the adopted rulemaking, including any material incorporated by reference, is on file in the Board's Chicago office at the James R. Thompson Center, 100 W. Randolph Street, Suite 11-500, and is available for public inspection.

9) Notice of Proposal Published in Illinois Register: April 13, 2012; 36 Ill. Reg. 5721

10) Has JCAR issued a Statement of Objection to this rulemaking? No

11) Differences between Proposal and Final Version: Section 302.208(a) - Changed "applies" to "has been approved by the Agency". Section 302.208(b),(c) and (d) - changed "allowed mixing" to "in which mixing is allowed". Section 302.510(a) - Corrected the address of the American Public Health Association. Sections 302.595(a) and 302.669(a) - Changed the 2nd sentence to "This list shall be made available to the public and updated whenever a new criterion or value is derived periodically but no less frequently than quarterly, and shall be published when updated in the Illinois Register. Some technical, nonsubstantive changes were made in Sections 302.510(a) and (b), 302.595(a) and 302.669(a).

12) Have all the changes agreed upon by the agency and JCAR been made as indicated in the agreements letter issued by JCAR? Yes

13) Will this rulemaking replace any emergency rulemaking currently in effect? No

14) Are there any proposed rulemakings pending on this Part? No

15) Summary and Purpose of Amendments: These amendments to 35 Ill. Adm. Code 302 update standards for boron, fluoride and manganese discharges into State waters, correct a zinc standard and repeal an outdated site specific fluoride standard. Also, the schedule for publishing derived water quality criteria in the Illinois Register is changed from at least quarterly to whenever a new criterion or value is derived. An incorporation by reference to a USEPA publication is added to include a new cyanide testing method and the incorporation of an American Public Health Association standard method for waste and wastewater examination is updated to the 21st edition (2005).

16) Information and questions regarding these adopted amendments shall be directed to:

Kathleen Crowley
Illinois Pollution Control Board
100 W. Randolph Street, Suite 11-500
Chicago, IL 60601

312/814-6929
Kathleen.Crowley@illinois.gov

Copies of the Board's opinions and orders may be requested from the Clerk of the Board at the address listed in #8 above or by calling 312/814-3620. Please refer to the docket number R11-18 in your request. The Board order is also available from the Board's website (www.ipcb.state.il.us).

The full text of the Adopted Amendments begins on the next page:

TITLE 35: ENVIRONMENTAL PROTECTION

SUBTITLE C: WATER POLLUTION

CHAPTER I: POLLUTION CONTROL BOARD

PART 302

WATER QUALITY STANDARDS

SUBPART A: GENERAL WATER QUALITY PROVISIONS

Section

 

302.100

Definitions

302.101

Scope and Applicability

302.102

Allowed Mixing, Mixing Zones and ZIDs

302.103

Stream Flows

302.104

Main River Temperatures

302.105

Antidegradation

SUBPART B: GENERAL USE WATER QUALITY STANDARDS

Section

 

302.201

Scope and Applicability

302.202

Purpose

302.203

Offensive Conditions

302.204

pH

302.205

Phosphorus

302.206

Dissolved Oxygen

302.207

Radioactivity

302.208

Numeric Standards for Chemical Constituents

302.209

Fecal Coliform

302.210

Other Toxic Substances

302.211

Temperature

302.212

Total Ammonia Nitrogen

302.213

Effluent Modified Waters (Ammonia) (Repealed)

SUBPART C: PUBLIC AND FOOD PROCESSING WATER SUPPLY STANDARDS

Section

 

302.301

Scope and Applicability

302.302

Algicide Permits 12

302.303

Finished Water Standards

302.304

Chemical Constituents

302.305

Other Contaminants

302.306

Fecal Coliform

302.307

Radium 226 and 228

SUBPART D: SECONDARY CONTACT AND INDIGENOUS AQUATIC LIFE STANDARDS

Section

 

302.401

Scope and Applicability

302.402

Purpose

302.403

Unnatural Sludge

302.404

pH

302.405

Dissolved Oxygen

302.406

Fecal Coliform (Repealed)

302.407

Chemical Constituents

302.408

Temperature

302.409

Cyanide

302.410

Substances Toxic to Aquatic Life

SUBPART E: LAKE MICHIGAN BASIN WATER QUALITY STANDARDS

Section

 

302.501

Scope, Applicability, and Definitions

302.502

Dissolved Oxygen

302.503

pH

302.504

Chemical Constituents

302.505

Fecal Coliform

302.506

Temperature

302.507

Thermal Standards for Existing Sources on January 1, 1971

302.508

Thermal Standards for Sources Under Construction But Not In Operation on January 1, 1971

302.509

Other Sources

302.510

Incorporations by Reference

302.515

Offensive Conditions

302.520

Regulation and Designation of Bioaccumulative Chemicals of Concern (BCCs)

302.521

Supplemental Antidegradation Provisions for Bioaccumulative Chemicals of Concern (BCCs)

302.525

Radioactivity

302.530

Supplemental Mixing Provisions for Bioaccumulative Chemicals of Concern (BCCs)

302.535

Ammonia Nitrogen

302.540

Other Toxic Substances

302.545

Data Requirements

302.550

Analytical Testing

302.553

Determining the Lake Michigan Aquatic Toxicity Criteria or Values - General Procedures

302.555

Determining the Tier I Lake Michigan Acute Aquatic Toxicity Criterion (LMAATC): Independent of Water Chemistry

302.560

Determining the Tier I Lake Michigan Basin Acute Aquatic Life Toxicity Criterion (LMAATC): Dependent on Water Chemistry

302.563

Determining the Tier II Lake Michigan Basin Acute Aquatic Life Toxicity Value (LMAATV)

302.565

Determining the Lake Michigan Basin Chronic Aquatic Life Toxicity Criterion (LMCATC) or the Lake Michigan Basin Chronic Aquatic Life Toxicity Value (LMCATV)

302.570

Procedures for Deriving Bioaccumulation Factors for the Lake Michigan Basin

302.575

Procedures for Deriving Tier I Water Quality Criteria and Values in the Lake Michigan Basin to Protect Wildlife

302.580

Procedures for Deriving Water Quality Criteria and Values in the Lake Michigan Basin to Protect Human Health - General

302.585

Procedures for Determining the Lake Michigan Basin Human Health Threshold Criterion (LMHHTC) and the Lake Michigan Basin Human Health Threshold Value (LMHHTV)

302.590

Procedures for Determining the Lake Michigan Basin Human Health Nonthreshold Criterion (LMHHNC) or the Lake Michigan Basin Human Health Nonthreshold Value (LMHHNV)

302.595

Listing of Bioaccumulative Chemicals of Concern, Derived Criteria and Values

SUBPART F: PROCEDURES FOR DETERMINING WATER QUALITY CRITERIA

Section

 

302.601

Scope and Applicability

302.603

Definitions

302.604

Mathematical Abbreviations

302.606

Data Requirements

302.612

Determining the Acute Aquatic Toxicity Criterion for an Individual Substance - General Procedures

302.615

Determining the Acute Aquatic Toxicity Criterion - Toxicity Independent of Water Chemistry

302.618

Determining the Acute Aquatic Toxicity Criterion - Toxicity Dependent on Water Chemistry

302.621

Determining the Acute Aquatic Toxicity Criterion - Procedure for Combinations of Substances

302.627

Determining the Chronic Aquatic Toxicity Criterion for an Individual Substance - General Procedures

302.630

Determining the Chronic Aquatic Toxicity Criterion - Procedure for Combinations of Substances

302.633

The Wild and Domestic Animal Protection Criterion

302.642

The Human Threshold Criterion

302.645

Determining the Acceptable Daily Intake

302.648

Determining the Human Threshold Criterion

302.651

The Human Nonthreshold Criterion

302.654

Determining the Risk Associated Intake

302.657

Determining the Human Nonthreshold Criterion

302.658

Stream Flow for Application of Human Nonthreshold Criterion

302.660

Bioconcentration Factor

302.663

Determination of Bioconcentration Factor

302.666

Utilizing the Bioconcentration Factor

302.669

Listing of Derived Criteria

302.APPENDIX A

References to Previous Rules

302.APPENDIX B

Sources of Codified Sections

302.APPENDIX C

Maximum total ammonia nitrogen concentrations allowable for certain combinations of pH and temperature

302.TABLE A

pH-Dependent Values of the AS (Acute Standard)

302.TABLE B

Temperature and pH-Dependent Values of the CS (Chronic Standard) for Fish Early Life Stages Absent

302.TABLE C

Temperature and pH-Dependent Values of the CS (Chronic Standard) for Fish Early Life Stages Present

302.APPENDIX D

Section 302.206(d): Stream Segments for Enhanced Dissolved Oxygen Protection

AUTHORITY: Implementing Section 13 and authorized by Sections 11(b) and 27 of the Environmental Protection Act [415 ILCS 5/13, 11(b), and 27].

SOURCE: Filed with the Secretary of State January 1, 1978; amended at 2 Ill. Reg. 44, p. 151, effective November 2, 1978; amended at 3 Ill. Reg. 20, p. 95, effective May 17, 1979; amended at 3 Ill. Reg. 25, p. 190, effective June 21, 1979; codified at 6 Ill. Reg. 7818; amended at 6 Ill. Reg. 11161, effective September 7, 1982; amended at 6 Ill. Reg. 13750, effective October 26, 1982; amended at 8 Ill. Reg. 1629, effective January 18, 1984; peremptory amendments at 10 Ill. Reg. 461, effective December 23, 1985; amended at R87-27 at 12 Ill. Reg. 9911, effective May 27, 1988; amended at R85-29 at 12 Ill. Reg. 12082, effective July 11, 1988; amended in R88-1 at 13 Ill. Reg. 5998, effective April 18, 1989; amended in R88-21(A) at 14 Ill. Reg. 2899, effective February 13, 1990; amended in R88-21(B) at 14 Ill. Reg. 11974, effective July 9, 1990; amended in R94-1(A) at 20 Ill. Reg. 7682, effective May 24, 1996; amended in R94-1(B) at 21 Ill. Reg. 370, effective December 23, 1996; expedited correction at 21 Ill. Reg. 6273, effective December 23, 1996; amended in R97-25 at 22 Ill. Reg. 1356, effective December 24, 1997; amended in R99-8 at 23 Ill. Reg. 11249, effective August 26, 1999; amended in R01-13 at 26 Ill. Reg. 3505, effective February 22, 2002; amended in R02-19 at 26 Ill. Reg. 16931, effective November 8, 2002; amended in R02-11 at 27 Ill. Reg. 166, effective December 20, 2002; amended in R04-21 at 30 Ill. Reg. 4919, effective March 1, 2006; amended in R04-25 at 32 Ill. Reg. 2254, effective January 28, 2008; amended in R07-9 at 32 Ill. Reg. 14978, effective September 8, 2008; amended in R11-18 at 36 Ill. Reg. 18871, effective December 12, 2012.

SUBPART B: GENERAL USE WATER QUALITY STANDARDS

Section 302.208 Numeric Standards for Chemical Constituents

a) The acute standard (AS) for the chemical constituents listed in subsection (e) shall not be exceeded at any time except for those waters for which a zone of initial dilution (ZID) has been approved by the Agency pursuant to Section 302.102 as provided in subsection (d).

b) The chronic standard (CS) for the chemical constituents listed in subsection (e) shall not be exceeded by the arithmetic average of at least four consecutive samples collected over any period of at least four days, except for those waters in which the Agency has approved a mixing zone or in which mixing is allowed pursuant to Section 302.102 as provided in subsection (d). The samples used to demonstrate attainment or lack of attainment with a CS must be collected in a manner that assures an average representative of the sampling period. For the chemical constituents metals that have water quality based standards dependent upon hardness, the chronic water quality standard will be calculated according to subsection (e) using the hardness of the water body at the time the metals sample was collected. To calculate attainment status of chronic metals standards, the concentration of the chemical constituent metal in each sample is divided by the calculated water quality standard for the sample to determine a quotient. The water quality standard is attained if the mean of the sample quotients is less than or equal to one for the duration of the averaging period.

c) The human health standard (HHS) for the chemical constituents listed in subsection (f) shall not be exceeded when the stream flow is at or above the harmonic mean flow pursuant to Section 302.658 nor shall an annual average, based on at least eight samples, collected in a manner representative of the sampling period, exceed the HHS except for those waters in which the Agency has approved a mixing zone or in which mixing is allowed pursuant to Section 302.102 as provided in subsection (d).

d) The standard for the chemical constituents of subsections (g) and (h) shall not be exceeded at any time except for those waters in which the Agency has approved a mixing zone or in which mixing is allowed pursuant to Section 302.102. In waters where mixing is allowed pursuant to Section 302.102, the following apply:

1) The AS shall not be exceeded in any waters except for those waters for which the Agency has approved a zone of initial dilutions (ZID) pursuant to Section 302.102.

2) The CS shall not be exceeded outside of waters in which mixing is allowed pursuant to Section 302.102.

3) The HHS shall not be exceeded outside of waters in which mixing is allowed pursuant to Section 302.102.

e) Numeric Water Quality Standards for the Protection of Aquatic Organisms

Constituent

STORET Number

AS (µg/L)

CS (µg/L)

Arsenic (trivalent, dissolved)

22680

360 X 1.0* = 360

190 X 1.0* = 190

Boron (total)

 

40,100

7,600

Cadmium (dissolved)

01025

 

 

where A = -2.918 and B = 1.128

Where A = -3.490 and B = 0.7852

Chromium (hexavalent, total)

01032

16

11

Chromium (trivalent, dissolved)

80357

 

 

where A = 3.688 and B = 0.8190

where A = 1.561 and B = 0.8190

Copper (dissolved)

01040

 

 

where A = -1.464 and B = 0.9422

where A = -1.465 and B = 0.8545

Cyanide

00718

22

5.2

Fluoride (total)

 

, but shall not exceed 4.0 mg/L

 

 

where A = 6.7319 and B = 0.5394

where A = 6.0445 and B = 0.5394

Lead (dissolved)

01049

 

 

where A = -1.301 and B = 1.273

where A = -2.863 and B = 1.273

Manganese

 

0.9812*

0.9812*

 

 

where A = 4.9187 and B = 0.7467

where A = 4.0635 and B = 0.7467

Mercury (dissolved)

71890

2.6 X 0.85* = 2.2

1.3 X 0.85* = 1.1

Nickel (dissolved)

01065

0.998*,

0.986*,

 

 

where A = 0.5173 and B = 0.8460

where A = -2.286 and B = 0.8460

TRC

500600

19

11

Zinc (dissolved)

01090

0.978*,

0.986*,

 

 

where A = 0.9035 and B = 0.8473

where A = -0.4456A = 0.8165 and B = 0.8473

Benzene

78124

4200

860

Ethylbenzene

78113

150

14

Toluene

78131

2000

600

Xylene(s)

81551

920

360

where:

µg/L

=

microgram per liter

ex

=

base of natural logarithms raised to the x-power

ln(H)

=

natural logarithm of Hardness (STORET 00900)

*

=

conversion factor multiplier for dissolved metals

**

=

standard to be evaluated using either of the following USEPA approved methods, incorporated by reference at 35 Ill. Adm. Code 301.106: Method OIA-1677, DW: Available Cyanide by Flow Injection, Ligand Exchange, and Amperometry, January 2004, Document Number EPA-821-R-04-001 or Cyanide Amenable to Chlorination, Standard Methods 4500-CN-G (40 CFR 136.3)

f) Numeric Water Quality Standard for the Protection of Human Health

Constituent

STORET Number

(µg/L)

Mercury (total)

71900

0.012

Benzene

78124

310

where:

µg/L

=

micrograms per liter

g) Single-value standards apply at the following concentrations for these substances: Concentrations of the following chemical constituents shall not be exceeded except in waters for which mixing is allowed pursuant to Section 302.102.

Constituent

Unit

STORET Number

Standard

Barium (total)

mg/L

01007

5.0

Boron (total)

mg/L

01022

1.0

Chloride (total)

mg/L

00940

500

Fluoride

mg/L

00951

1.4

Iron (dissolved)

mg/L

01046

1.0

Manganese (total)

mg/L

01055

1.0

Phenols

mg/L

32730

0.1

Selenium (total)

mg/L

01147

1.0

Silver (total)

µg/L

01077

5.0

where:

mg/L

=

milligram per liter and

µg/L

=

microgram per liter

h) Water quality standards for sulfate are as follows The following concentrations for sulfate must not be exceeded except in receiving waters for which mixing is allowed pursuant to Section 302.102:

1) At any point where water is withdrawn or accessed for purposes of livestock watering, the average of sulfate concentrations must not exceed 2,000 mg/L when measured at a representative frequency over a 30 day period.

2)The results of the following equations provide sulfate water quality standards in mg/L for the specified ranges of hardness (in mg/L as CaCO3) and chloride (in mg/L) and must be met at all times:

A) If the hardness concentration of receiving waters is greater than or equal to 100 mg/L but less than or equal to 500 mg/L, and if the chloride concentration of waters is greater than or equal to 25 mg/L but less than or equal to 500 mg/L, then:

C = [1276.7 + 5.508 (hardness) -1.457 (chloride)] * 0.65

where: Where,

C

=

sulfate concentration

B) If the hardness concentration of waters is greater than or equal to 100 mg/L but less than or equal to 500 mg/L, and if the chloride concentration of waters is greater than or equal to 5 mg/L but less than 25 mg/L, then:

C = [-57.478 + 5.79 (hardness) + 54.163 (chloride)] * 0.65

where: Where

C

=

sulfate concentration

3) The following sulfate standards must be met at all times when hardness (in mg/L as CaCO3) and chloride (in mg/L) concentrations other than specified in (h)(2) are present:

A) If the hardness concentration of waters is less than 100 mg/L or chloride concentration of waters is less than 5 mg/L, the sulfate standard is 500 mg/L.

B) If the hardness concentration of waters is greater than 500 mg/L and the chloride concentration of waters is 5 mg/L or greater, the sulfate standard is 2,000 mg/L.

C) If the combination of hardness and chloride concentrations of existing waters are not reflected in subsection (h)(3)(A) or (B), the sulfate standard may be determined in a site-specific rulemaking pursuant to section 303(c) of the Federal Water Pollution Control Act of 1972 (Clean Water Act), 33 USC 1313, and Federal Regulations at 40 CFR 131.10(j)(2).

(Source: Amended at 36 Ill. Reg. 18871, effective December 12, 2012)

SUBPART C: PUBLIC AND FOOD PROCESSING WATER SUPPLY STANDARDS

Section 302.303 Finished Water Standards

Water shall be of such quality that with treatment consisting of coagulation, sedimentation, filtration, storage and chlorination, or other equivalent treatment processes, the treated water shall meet in all respects the requirements of Part 611604.

(Note: Prior to codification, Table I, Rule 304 of Ch 6: Public Water Supplies)

(Source: Amended at 36 Ill. Reg. 18871, effective December 12, 2012)

Section 302.304 Chemical Constituents

The following levels of chemical constituents shall not be exceeded:

CONSTITUENT

STORET NUMBER

CONCENTRATION (mg/1)

Arsenic (total)

01002

0.05

Barium (total)

01007

1.0

Boron (total)

 

1.0

Cadmium (total)

01027

0.010

Chloride (total)

00940

250.

Chromium

01034

0.05

Fluoride (total)

 

1.4

Iron (dissolved)

01046

0.3

Lead (total)

01051

0.05

Manganese (total)

01055

1.00.15

Nitrate-Nitrogen

00620

10.

Oil (hexane-solubles or equivalent)

00550, 00556 or 00560

0.1

Organics

 

 

Pesticides

 

 

Chlorinated Hydro-

 

 

carbon Insecticides

 

 

Aldrin

39330

0.001

Chlordane

39350

0.003

DDT

39370

0.05

Dieldrin

39380

0.001

Endrin

39390

0.0002

Heptachlor

39410

0.0001

Heptachlor Expoxide

39420

0.0001

Lindane

39782

0.004

Methoxychlor

39480

0.1

Toxaphene

39400

0.0005

Organophosphate

 

 

Insecticides

 

 

Parathion

39540

0.1

Chlorophenoxy Herbicides 2,4-Dichlorophenoxy-acetic acid (2,4-D)

39730

0.1

2-(2,4,5-Trichloro-phenoxy)-propionic acid (2,4,5-TP or Silvex)

39760

0.01

Phenols

32730

0.001

Selenuim (total)

01147

0.01

Sulphates

00945

250.

Total Dissolved Solids

70300

500.

(Source: Amended at 36 Ill. Reg. 18871, effective December 12, 2012)

SUBPART E: LAKE MICHIGAN BASIN WATER QUALITY STANDARDS

Section 302.504 Chemical Constituents

The following concentrations of chemical constituents must not be exceeded, except as provided in Sections 302.102 and 302.530:

a) The following standards must be met in all waters of the Lake Michigan Basin. Acute aquatic life standards (AS) must not be exceeded at any time except for those waters for which the Agency has approved a zone of initial dilution (ZID) pursuant to Sections 302.102 and 302.530. Chronic aquatic life standards (CS) and human health standards (HHS) must not be exceeded outside of waters in which mixing is allowed pursuant to Sections 302.102 and 302.530 by the arithmetic average of at least four consecutive samples collected over a period of at least four days. The samples used to demonstrate compliance with the CS or HHS must be collected in a manner which assures an average representation of the sampling period.

Constituent

STORET Number

Unit

AS

CS

HHS

Arsenic (Trivalent, dissolved)

22680

µg/L

340 x 1.0* = 340

340 x 1.0* = 148

NA

Boron (total)

 

mg/L

40.1

7.6

NA

Cadmium (dissolved)

01025

µg/L

exp[A+B1n(H)]x {1.138672-[(1nH) (0.041838)]}*,

exp[A+B1n(H)]x {1.101672-[(1nH) (0.041838)]}*,

NA

 

 

 

where A = - 3.6867 and B = 1.128

where A = -2.715 and B = 0.7852

 

Chromium (Hexavalent, total)

01032

µg/L

16

11

NA

Chromium (Trivalent, dissolved)

80357

µg/L

exp[A+B1n(H)]x 0.316*,

exp[A+B1n(H)]x 0.860*,

NA

 

 

 

where A = 3.7256 and B = 0.819

where A = 0.6848 and B = 0.819

 

Copper (dissolved)

01040

µg/L

exp[A+B1n(H)]x 0.960*,

exp[A+B1n(H)]x 0.960*,

NA

 

 

 

where A = -1.700 and B = 0.9422

where A = -1.702 and B = 0.8545

 

Cyanide**(Weak acid dissociable)

00718

µg/L

22

5.2

NA

Fluoride (total)

 

µg/L

exp[A+B1n(H)]x

exp[A+B1n(H)]x but shall not exceed 4.0 mg/L

NA

 

 

 

where A = 6.7319 and B = 0.5394

where A = 6.0445 and B = 0.5394

 

Lead (dissolved)

01049

μg/L

exp[A+B1n(H)]x {1.46203-[(1nH) (0.145712)]}*,

exp[A+B1n(H)]x {1.46203-[(1nH) (0.145712)]}*,

NA

 

 

 

where A = -1.055 and B =1.273

where A = -4.003 and B = 1.273

 

Manganese (dissolved)

 

µg/L

exp[A+B1n(H)]x 0.9812*

exp[A+B1n(H)]x 0.9812*

NA

 

 

 

where A = 4.9187 and B = 0.7467

where A = 4.0635 and B = 0.7467

 

Nickel (dissolved)

01065

µg/L

exp[A+B1n(H)]x 0.998*,

exp[A+B1n(H)]x 0.997*,

NA

 

 

 

where A = 2.255 and B = 0.846

where A = 0.0584 and B = 0.846

 

Selenium (dissolved)

01145

µg/L

NA

5.0

NA

TRC

50060

µg/L

19

11

NA

Zinc (dissolved)

01090

µg/L

exp[A+B1n(H)]x 0.978*,

exp[A+B1n(H)]x 0.986*,

NA

 

 

 

where A = 0.884 and B = 0.8473

where A = 0.884 and B = 0.8473

 

Benzene

78124

µg/L

3900

800

310

Chlorobenzene

34301

mg/L

NA

NA

3.2

2.4-Dimethylphenol

34606

mg/L

NA

NA

8.7

2,4-Dinitrophenol

03756

mg/L

NA

NA

2.8

Endrin

39390

µg/L

0.086

0.036

NA

Ethylbenzene

78113

µg/L

150

14

NA

Hexachloroethane

34396

µg/L

NA

NA

6.7

Methylene chloride

34423

mg/L

NA

NA

2.6

Parathion

39540

µg/L

0.065

0.013

NA

Pentachlorophenol

03761

µg/L

exp B ([pH]+A),

exp B ([pH]+A),

NA

 

 

 

where A = -4.869 and B = 1.005

where A = -5.134 and B = 1.005

 

Toluene

78131

μg/L mg/L

2000

610

51.0

Trichloroethylene

39180

μg/L

NA

NA

370

Xylene(s)

81551

μg/L

1200

490

NA

where Where:

NA

=

Not Applied

exp[x]

=

base of natural logarithms raised to the x-power

ln(H)

=

natural logarithm of Hardness (STORET 00900)

*

=

conversion factor multiplier for dissolved metals

**

=

standard to be evaluated using either of the following USEPA approved methods, incorporated by reference at 35 Ill. Adm. Code 302.510: Method OIA-1677, DW: Available Cyanide by Flow Injection, Ligand Exchange, and Amperometry, January 2004, Document Number EPA-821-R-04-001 or Cyanide Amenable to Chlorination, Standard Methods 4500-CN-G (40 CFR 136.3).

b) The following water quality standards must not be exceeded at any time in any waters of the Lake Michigan Basin, unless a different standard is specified under subsection (c) of this Section.

Constituent

STORET Number

Unit

Water Quality Standard

Barium (total)

01007

mg/L

5.0

Boron (total)

01022

mg/L

1.0

Chloride (total)

00940

mg/L

500

Fluoride

00951

mg/L

1.4

Iron (dissolved)

01046

mg/L

1.0

Manganese (total)

01055

mg/L

1.0

Phenols

32730

mg/L

0.1

Sulfate

00945

mg/L

500

Total Dissolved Solids

70300

mg/L

1000

c) In addition to the standards specified in subsections (a) and (b) of this Section, the following standards must not be exceeded at any time in the Open Waters of Lake Michigan as defined in Section 302.501.

Constituent

STORET Number

Unit

Water Quality Standard

Arsenic (total)

01002

μg/L

50.0

Boron (total)

 

mg/L

1.0

Barium (total)

01007

mg/L

1.0

Chloride (total)

00940

mg/L

12.0

Fluoride (total)

 

mg/L

1.4

Iron (dissolved)

01046

mg/L

0.30

Lead (total)

01051

μg/L

50.0

Manganese (total)

01055

mg/L

0.15

Nitrate-Nitrogen

00620

mg/L

10.0

Phosphorus

00665

μg/L

7.0

Selenium (total)

01147

μg/L

10.0

Sulfate

00945

mg/L

24.0

Total Dissolved Solids

70300

mg/L

180.0

Oil (hexane solubles or equivalent)

00550, 00556 or 00560

mg/L

0.10

Phenols

32730

μg/L

1.0

d) In addition to the standards specified in subsections (a), (b) and (c) of this Section, the following human health standards (HHS) must not be exceeded in the Open Waters of Lake Michigan as defined in Section 302.501 by the arithmetic average of at least four consecutive samples collected over a period of at least four days. The samples used to demonstrate compliance with the HHS must be collected in a manner which assures an average representation of the sampling period.

Constituent

STORET Number

Unit

Water Quality Standard

Benzene

34030

μg/L

12.0

Chlorobenzene

34301

μg/L

470.0

2,4-Dimethylphenol

34606

μg/L

450.0

2,4-Dinitrophenol

03757

μg/L

55.0

Hexachloroethane (total)

34396

μg/L

5.30

Lindane

39782

μg/L

0.47

Methylene chloride

34423

μg/L

47.0

Toluene

78131

mg/L

5.60

Trichloroethylene

39180

μg/L

29.0

e) For the following bioaccumulative chemicals of concern (BCCs), acute aquatic life standards (AS) must not be exceeded at any time in any waters of the Lake Michigan Basin and chronic aquatic life standards (CS), human health standards (HHS), and wildlife standards (WS) must not be exceeded in any waters of the Lake Michigan Basin by the arithmetic average of at least four consecutive samples collected over a period of at least four days subject to the limitations of Sections 302.520 and 302.530. The samples used to demonstrate compliance with the HHS and WS must be collected in a manner that assures an average representation of the sampling period.

Constituent

STORET Number

Unit

AS

CS

HHS

WS

Mercury (total)

71900

ng/L

1,700

910

3.1

1.3

Chlordane

39350

ng/L

NA

NA

0.25

NA

DDT and metabolites

39370

pg/L

NA

NA

150

11.0

Dieldrin

39380

ng/L

240

56

0.0065

NA

Hexachlorobenzene

39700

ng/L

NA

NA

0.45

NA

Lindane

39782

μg/L

0.95

NA

0.5

NA

PCBs (class)

79819

pg/L

NA

NA

26

120

2,3,7,8-TCDD

03556

fg/L

NA

NA

8.6

3.1

Toxaphene

39400

pg/L

NA

NA

68

NA

where Where:

mg/L

=

milligrams per liter (10-3 grams per liter)

µg/L

=

micrograms per liter (10-6 grams per liter)

ng/L

=

nanograms per liter (10-9 grams per liter)

pg/L

=

picograms per liter (10-12 grams per liter)

fg/L

=

femtograms per liter (10-15 grams per liter)

NA

=

Not Applied

(Source: Amended at 36 Ill. Reg. 18871, effective December 12, 2012)

Section 302.510 Incorporations by Reference

a) The Board incorporates the following publications by reference:

American Public Health Association et al., Standard Methods for the Examination of Water and Wastewater, 21st Edition, 2005. Available from the American Public Health Association, 800 I Street, NW, Washington, D.C. 20001-3710, (202)777-2742.

American Public Health Association et al., 1015 Fifteenth Street, N.W., Washington, D.C. 20005, Standard Methods for the Examination of Water and Wastewater, 18th Edition, 1996. Available from the American Public Health Association, 1015 Fifteenth St., NW, Washington, D.C. 20005 (202)789-5600.

USEPA. United States Environmental Protection Agency, Office of Health and Environmental Assessment, Washington, D.C. 20460, Method OIA-1677, DW: Available Cyanide by Flow Injection, Ligand Exchange, and Amperometry, January 2004, Document Number EPA-821-R-04-001.

b) The Board incorporates the following federal regulations by reference. Available from the Superintendent of Documents, U.S. Government Printing Office, Washington, D.C. 20402, (202) 783-3238:

40 CFR 136 (1996)

40 CFR 141 (1988)

40 CFR 302.4 (1988)

The Sections of 40 CFR 132 (1996) listed below:

Appendix A

Section I A

Section II

Section III C

Section IV D, E, F, G, H, and I

Section V C

Section VI A, B, C, D, E, and F

Section VIII

Section XI

Section XVII

Appendix B

Section III

Section VII B and C

Section VIII

Appendix C

Section II

Section III A (1 through 6 and 8), B (1 and 2)

Appendix D

Section III C, D, and E

Section IV

cd) This Section incorporates no future editions or amendments.

(Source: Amended at 36 Ill. Reg. 18871, effective December 12, 2012)

Section 302.553 Determining the Lake Michigan Aquatic Toxicity Criteria or Values - General Procedures

The Lake Michigan Aquatic Life Criteria and Values are those concentrations or levels of a substance at which aquatic life is protected from adverse effects resulting from short or long term exposure in water.

a) Tier I criteria and Tier II values to protect against acute effects in aquatic organisms will be calculated according to procedures listed at Sections 302.555, 302.560 and 302.563. The procedures of Section 302.560 shall be used as necessary to allow for interactions with other water quality characteristics such as hardness, pH, temperature, etc. Tier I criteria and Tier II values to protect against chronic effects in aquatic organisms shall be calculated according to the procedures listed at Section 302.565.

b) Minimum data requirements. In order to derive a Tier I acute or chronic criterion, data must be available for at least one species of freshwater animal in at least eight different families such that the following taxa are included:

1) The family Salmonidae in the class Osteichthyes;

2) One other family in the class Osteichthyes;

3) A third family in the phylum Chordata;

4) A planktonic crustacean;

5) A benthic crustacean;

6) An insect;

7) A family in a phylum other than Arthropoda or Chordata; and

8) A family from any order of insect or any phylum not already represented.

c) Data for tests with plants, if available, must be included in the data set.

d) If data for acute effects are not available for all the eight families listed above, but are available for the family Daphnidae, a Tier II value shall be derived according to procedures in Section 302.563. If data for chronic effects are not available for all the eight families, but there are acute and chronic data available according to Section 302.565(b) so that three acute to chronic ratios (ACRs) can be calculated, then a Tier I chronic criterion can be derived according to procedures in Section 302.565. If three ACRs are not available, then a Tier II chronic value can be derived according to procedures in Section 302.565(be).

e) Data must be obtained from species that have reproducing wild populations in North America except that data from salt water species can be used in the derivation of an ACR.

(Source: Amended at 36 Ill. Reg. 18871, effective December 12, 2012)

Section 302.595 Listing of Bioaccumulative Chemicals of Concern, Derived Criteria and Values

a) The Agency shall maintain a listing of toxicity criteria and values derived pursuant to this Subpart. This list shall be made available to the public and updated whenever a new criterion or value is derived periodically but no less frequently than quarterly, and shall be published when updated in the Illinois Register.

b) A criterion or value published pursuant to subsection (a) of this Section may be proposed to the Board for adoption as a numeric water quality standard.

c) The Agency shall maintain for inspection all information including, but not limited to, assumptions, toxicity data and calculations used in the derivation of any toxicity criterion or value listed pursuant to subsection (a) of this Section until adopted by the Board as a numeric water quality standard.

(Source: Amended at 36 Ill. Reg. 18871, effective December 12, 2012)

SUBPART F: PROCEDURES FOR DETERMINING WATER QUALITY CRITERIA

Section 302.648 Determining the Human Threshold Criterion

The HTC is calculated according to the equation:

HTC = ADI/[W + (F x BCF)]

where Where:

HTC

=

Human health protection criterion in milligrams per liter (mg/L);

ADI

=

Acceptable daily intake of substance in milligrams per day (mg/d) as specified in Section 302.645;

W

=

Per capita daily water consumption equal to 2 liters per day (L/d) for surface waters at the point of intake of a public or food processing water supply, or equal to 0.01 liters per day (L/d) which represents incidental exposure through contact or ingestion of small volumes of water while swimming or during other recreational activities for areas which are determined to be public access areas pursuant to Section 302.102302.201(b)(3), or 0.001 liters per day (L/d) for other General Use waters;

F

=

Assumed daily fish consumption in the United States equal to 0.020 kilograms per day (kg/d); and

BCF

=

Aquatic organism Bioconcentration Factor with units of liter per kilogram (L/kg) as derived in Sections 302.660 through 302.666.

(Source: Amended at 36 Ill. Reg. 18871, effective December 12, 2012)

Section 302.657 Determining the Human Nonthreshold Criterion

The HNC is calculated according to the equation:

HNC = RAI/[W + (F x BCF)]

where Where:

HNC

=

Human Nonthreshold Protection Criterion in milligrams per liter (mg/L);

RAI

=

Risk Associated Intake of a substance in milligrams per day (mg/d) which is associated with a lifetime cancer risk level equal to a ratio of one to 1,000,000 as derived in Section 302.654;

W

=

Per capita daily water consumption equal to 2 liters per day (L/d) for surface waters at the point of intake of a public or food processing water supply, or equal to 0.01 liters per day (L/d) which represents incidental exposure through contact or ingestion of small volumes of water while swimming or during other recreational activities for areas which are determined to be public access areas pursuant to Section 302.102302.201(b)(3), or 0.001 liters per day (L/d) for other General Use waters;

F

=

Assumed daily fish consumption in the United States equal to 0.020 kilograms per day (kg/d); and

BCF

=

Aquatic Life Bioconcentration Factor with units of liter per kilogram (L/kg) as derived in Section 302.663.

(Source: Amended at 36 Ill. Reg. 18871, effective December 12, 2012)

Section 302.669 Listing of Derived Criteria

a) The Agency shall develop and maintain a listing of toxicity criteria pursuant to this Subpart. This list shall be made available to the public and updated whenever a new criterion is derived periodically but no less frequently than quarterly, and shall be published when updated in the Illinois Register.

b) A criterion published pursuant to subsection (a) may be proposed to the Board for adoption as a numeric water quality standard.

c) The Agency shall maintain for inspection all information including, but not limited to, assumptions, toxicity data and calculations used in the derivation of any toxicity criterion listed pursuant to subsection (a) until adopted by the Board as a water quality standard.

(Source: Amended at 36 Ill. Reg. 18871, effective December 12, 2012)