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update standards for boron, fluoride and manganese discharges into State waters, correct a zinc standard and repeal an outdated site specific fluoride standard.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 |
|
AS (µg/L) |
CS (µg/L) |
Arsenic (trivalent, dissolved) |
|
360 X 1.0* = 360 |
190 X 1.0* = 190 |
Boron (total) |
|
40,100 |
7,600 |
Cadmium (dissolved) |
|
||
|
|
where A = -2.918 and B = 1.128 |
Where A = -3.490 and B = 0.7852 |
Chromium (hexavalent, total) |
|
16 |
11 |
Chromium (trivalent, dissolved) |
|
||
|
|
where A = 3.688 and B = 0.8190 |
where A = 1.561 and B = 0.8190 |
Copper (dissolved) |
|
||
|
|
where A = -1.464 and B = 0.9422 |
where A = -1.465 and B = 0.8545 |
Cyanide |
|
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) |
|
||
|
|
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) |
|
2.6 X 0.85* = 2.2 |
1.3 X 0.85* = 1.1 |
Nickel (dissolved) |
|
0.998* |
0.986* |
|
|
where A = 0.5173 and B = 0.8460 |
where A = -2.286 and B = 0.8460 |
TRC |
|
19 |
11 |
Zinc (dissolved) |
|
0.978* |
0.986* |
|
|
where A = 0.9035 and B = 0.8473 |
where A = -0.4456 |
Benzene |
|
4200 |
860 |
Ethylbenzene |
|
150 |
14 |
Toluene |
|
2000 |
600 |
Xylene(s) |
|
920 |
360 |
where:
µg/L |
= |
microgram per liter |
ex |
= |
base of natural logarithms raised to the x-power |
ln(H) |
= |
natural logarithm of Hardness |
* |
= |
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 |
|
(µg/L) |
Mercury (total) |
|
0.012 |
Benzene |
|
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 |
|
Standard |
Barium (total) |
mg/L |
|
5.0 |
|
|
|
|
Chloride (total) |
mg/L |
|
500 |
|
|
|
|
Iron (dissolved) |
mg/L |
01046 |
1.0 |
|
|
|
|
Phenols |
mg/L |
|
0.1 |
Selenium (total) |
mg/L |
|
1.0 |
Silver (total) |
µg/L |
|
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 |
|
CONCENTRATION (mg/1) |
Arsenic (total) |
|
0.05 |
Barium (total) |
|
1.0 |
Boron (total) |
|
1.0 |
Cadmium (total) |
|
0.010 |
Chloride (total) |
|
250 |
Chromium |
|
0.05 |
Fluoride (total) |
|
1.4 |
Iron (dissolved) |
|
0.3 |
Lead (total) |
|
0.05 |
Manganese (total) |
|
1.0 |
Nitrate-Nitrogen |
|
10 |
Oil (hexane-solubles or equivalent) |
|
0.1 |
Organics |
|
|
Pesticides |
|
|
Chlorinated Hydro- |
|
|
carbon Insecticides |
|
|
Aldrin |
|
0.001 |
Chlordane |
|
0.003 |
DDT |
|
0.05 |
Dieldrin |
|
0.001 |
Endrin |
|
0.0002 |
Heptachlor |
|
0.0001 |
Heptachlor Expoxide |
|
0.0001 |
Lindane |
|
0.004 |
Methoxychlor |
|
0.1 |
Toxaphene |
|
0.0005 |
Organophosphate |
|
|
Insecticides |
|
|
Parathion |
|
0.1 |
Chlorophenoxy Herbicides 2,4-Dichlorophenoxy-acetic acid (2,4-D) |
|
0.1 |
2-(2,4,5-Trichloro-phenoxy)-propionic acid (2,4,5-TP or Silvex) |
|
0.01 |
Phenols |
|
0.001 |
Selenuim (total) |
|
0.01 |
Sulphates |
|
250 |
Total Dissolved Solids |
|
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 |
|
Unit |
AS |
CS |
HHS |
Arsenic (Trivalent, dissolved) |
|
µg/L |
340 x 1.0* = 340 |
340 x 1.0* = 148 |
NA |
Boron (total) |
|
mg/L |
40.1 |
7.6 |
NA |
Cadmium (dissolved) |
|
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) |
|
µg/L |
16 |
11 |
NA |
Chromium (Trivalent, dissolved) |
|
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) |
|
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** |
|
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) |
|
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) |
|
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) |
|
µg/L |
NA |
5.0 |
NA |
TRC |
|
µg/L |
19 |
11 |
NA |
Zinc (dissolved) |
|
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 |
|
µg/L |
3900 |
800 |
310 |
Chlorobenzene |
|
mg/L |
NA |
NA |
3.2 |
2.4-Dimethylphenol |
|
mg/L |
NA |
NA |
8.7 |
2,4-Dinitrophenol |
|
mg/L |
NA |
NA |
2.8 |
Endrin |
|
µg/L |
0.086 |
0.036 |
NA |
Ethylbenzene |
|
µg/L |
150 |
14 |
NA |
Hexachloroethane |
|
µg/L |
NA |
NA |
6.7 |
Methylene chloride |
|
mg/L |
NA |
NA |
2.6 |
Parathion |
|
µg/L |
0.065 |
0.013 |
NA |
Pentachlorophenol |
|
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 |
|
μg/L |
2000 |
610 |
51.0 |
Trichloroethylene |
|
μg/L |
NA |
NA |
370 |
Xylene(s) |
|
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 |
* |
= |
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 |
|
Unit |
Water Quality Standard |
Barium (total) |
01007 |
mg/L |
5.0 |
|
|
|
|
Chloride (total) |
|
mg/L |
500 |
|
|
|
|
Iron (dissolved) |
|
mg/L |
1.0 |
|
|
|
|
Phenols |
|
mg/L |
0.1 |
Sulfate |
|
mg/L |
500 |
Total Dissolved Solids |
|
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 |
|
Unit |
Water Quality Standard |
Arsenic (total) |
|
μg/L |
50.0 |
Boron (total) |
|
mg/L |
1.0 |
Barium (total) |
|
mg/L |
1.0 |
Chloride (total) |
|
mg/L |
12.0 |
Fluoride (total) |
|
mg/L |
1.4 |
Iron (dissolved) |
|
mg/L |
0.30 |
Lead (total) |
|
μg/L |
50.0 |
Manganese (total) |
|
mg/L |
0.15 |
Nitrate-Nitrogen |
|
mg/L |
10.0 |
Phosphorus |
|
μg/L |
7.0 |
Selenium (total) |
|
μg/L |
10.0 |
Sulfate |
|
mg/L |
24.0 |
Total Dissolved Solids |
|
mg/L |
180.0 |
Oil (hexane solubles or equivalent) |
|
mg/L |
0.10 |
Phenols |
|
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 |
|
Unit |
Water Quality Standard |
Benzene |
|
μg/L |
12.0 |
Chlorobenzene |
|
μg/L |
470.0 |
2,4-Dimethylphenol |
|
μg/L |
450.0 |
2,4-Dinitrophenol |
|
μg/L |
55.0 |
Hexachloroethane (total) |
|
μg/L |
5.30 |
Lindane |
|
μg/L |
0.47 |
Methylene chloride |
|
μg/L |
47.0 |
|
|
|
|
Trichloroethylene |
|
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 |
|
Unit |
AS |
CS |
HHS |
WS |
Mercury (total) |
|
ng/L |
1,700 |
910 |
3.1 |
1.3 |
Chlordane |
|
ng/L |
NA |
NA |
0.25 |
NA |
DDT and metabolites |
|
pg/L |
NA |
NA |
150 |
11.0 |
Dieldrin |
|
ng/L |
240 |
56 |
0.0065 |
NA |
Hexachlorobenzene |
|
ng/L |
NA |
NA |
0.45 |
NA |
Lindane |
|
μg/L |
0.95 |
NA |
0.5 |
NA |
PCBs (class) |
|
pg/L |
NA |
NA |
26 |
120 |
2,3,7,8-TCDD |
|
fg/L |
NA |
NA |
8.6 |
3.1 |
Toxaphene |
|
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 302.102 |
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 302.102 |
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)