1. SUBPART B: GENERAL USE WATER QUALITY STANDARDS
      1. Section 302.208Numeric Standards for Chemical Constituents
      2. Section 302.504Chemical Constituents
      3. Section 302.575Procedures for Deriving Tier I Water Quality Criteria and Values in the Lake Michigan Basin to Protect Wildlife

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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 Nondegradation
 
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
Ammonia Nitrogen and Un-ionized Ammonia
302.213
Effluent Modified Waters (Ammonia)
 
SUBPART C: PUBLIC AND FOOD PROCESSING WATER SUPPLY
STANDARDS
 
Section
302.301
Scope and Applicability

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302.302 Algicide Permits
302.303
Finished Water Standards
302.304 Chemical Constituents
302.305 Other Contaminants
302.306 Fecal Coliform
 
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Fecal Coliform (Repealed)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 BCCs
302.525 Radioactivity

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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 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

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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 - Procedures 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
Combination 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
 
 
APPENDIX A
References to Previous Rules
APPENDIX B
Sources of Codified Sections
 
 
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

 
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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 20 Ill.
Reg. 370, effective December 23, 1996; expedited correction at 20 Ill. Reg. 6273,
effective December 23, 1996; amended in R97-25 at 21 Ill. Reg. 1356, effective
December 24, 1997; amended in R99-8 at 23 Ill. Reg. 11249, effective August 26, 1999;
amended in __________ at __________ Ill. Reg. _______________, effective
________________, 2002.
 
 
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 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 as provided in subsection (d). The samples used to demonstrate
compliance or lack of compliance with a CS must be collected in a manner
which assures an average representative of the sampling 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 as provided
in subsection (d).
 
d) 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 ZID pursuant to
Section 302.102.
 

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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) (ug/L)
CS
(μg/L) (ug/L)
Arsenic
(trivalent, dissolved)
(total)
22680 01002
360 X 1.0* = 360
190 X 1.0* = 190
 
Cadmium
(dissolved) (total)
01025 01027 exp[A+Bln(H)]
X
{1.138672-
[(lnH)(0.041838)]}*, but
not to exceed 50 ug/L,
where A=-2.918 and
B=1.128
exp[A+Bln(H)] X
{1.101672-
[(lnH)(0.041838)]}*,
where A=-3.490 and
B=0.7852
Chromium
(hexavalent, total)
(total hexavalent)
01032 16
11
Chromium (trivalent,
dissolved) (total
trivalent)
80357 01033 exp[A+Bln(H)]
X
0.316*
where A=3.688, and
B=0.8190
exp[A+Bln(H)] X
0.860*
where A=1.561, and
B=0.8190
Copper
(dissolved) (total)
01040 01042 exp[A+Bln(H)]
X
0.960*
where A=-1.464, and
B=0.9422
exp[A+Bln(H)] X
0.960*
where A=-1.465, and
B=0.8545
Cyanide (weak acid
dissociable)
00718 49 22
9.9 5.2
Lead
(dissolved) (total)
01049 01051 exp[A+Bln(H)]
X
{1.46203-
[(lnH)(0.145712)]}*
exp[A+Bln(H)] X
{1.46203-
[(lnH)(0.145712)]}*
where A=-2.863, and

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where A=-1.301, and
B=1.273
B=1.273
Mercury (dissolved) 71890 71900
2.6 X 0.85* = 2.2
1.3 X 0.85* = 1.1
Nickel (dissolved) 01065
exp[A+Bln(H)] X
0.998*
where A=0.5173, and
B=0.8460
exp[A+Bln(H)] X
0.997*
where A=-2.286, and
B=0.8460
TRC 500600
19
11
Zinc (dissolved) 01090 exp[A+Bln(H)] X
0.978*
where A=0.8875, and
B=0.8473
exp[A+Bln(H)] X
0.986*
where A=-0.8227, and
B=0.8473
Benzene 78124 4200 860
Ethylbenzene 78113 150 14
Toluene 78131 2000 600
Xylene(s) 81551 920 360
  
where: μg/L ug/L = microgram per liter,
 
exp[x] = base natural neutral logarithms raised to the x- power, and
 
ln(H) = natural logarithm of Hardness (STORET 00900).
 
* = conversion factor multiplier for dissolved metals
 
 
f) Numeric Water Quality Standard for the Protection of Human Health
 
 
Constituent
STORET
Number
 
(μg/L) (ug/L)
 
Mercury
 
71900
 
0.012
Benzene 78124 310

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Where μg/L ug/L = micrograms per liter
 
g) 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
Nickel (total) mg/L 01067
1.0
Phenols
mg/L
32730
0.1
Selenium (total)
mg/L
01147
1.0
Silver (total)
μg/L ug/L
01077
5.0
Sulfate mg/L
00945
  
500.
Total Dissolved
Solids
mg/L 70300
1000.
Zinc (total) mg/L 01092
1.0
where: mg/L = milligram per liter and
μg/L ug/L = microgram per liter
   
(Source: Amended at 20 Ill. Reg.7682, effective May 24, 1996; amended in __________
at __________ Ill. Reg. _______________, effective ________________, 2002)
 
 
SUBPART E: LAKE MICHIGAN BASIN WATER QUALITY STANDARDS
 

 
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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 Section
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
µ
g/L
340 X 1.0* =
340
148 X 1.0* =
148
NA
Cadmium (dissolved)
01025
µ
g/L
exp[A
+Bln(H)] X
{1.38672-
[(lnH)(0.0418
38)]}*
A=-3.6867,
and
B=1.128
exp[A
+Bln(H)] X
{1.101672-
[(lnH)(0.0418
38)]}*
A = -2.715,
and
B = 0.7852
 
NA
Chromium
(Hexavalent, total)
 
01032
µ
g/L
16 11
NA
Chromium
(Trivalent, dissolved)
80357
µ
g/L
exp[A
+Bln(H)] X
0.316* where
A = 3.7256,
and
exp[A
+Bln(H)] X
0.860* where
A = 0.6848,
and
NA

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Constituent STORET
Number
Unit AS CS HHS
B =0.819
 
B = 0.819
Copper
(dissolved)
01040
µ
g/L
exp[A
+Bln(H)] X
0.960* where
A = -1.700,
and
B = 0.9422
exp[A
+Bln(H)] X
0.960* where
A = -1.702,
and
B = 0.8545
 
NA
Cyanide
(Weak acid dissociable)
 
00718
µ
g/L
22 5.2
NA
Lead
(dissolved)
01049
µ
g/L
exp[A
+Bln(H)] X
{1.46203-
[(lnH)(0.1457
12)]}* where
A = -1.055,
and
B = 1.273
exp[A
+Bln(H)] X
{1.46203-
[(lnH)(0.1457
12)]}* where
A = -4.003,
and
B = 1.273
 
NA
Nickel
(dissolved)
01065
µ
g/L
exp[A
+Bln(H)] X
0.998* where
A = 2.255, and
B = 0.846
 
exp[A
+Bln(H)] X
0.997* where
A = 0.0584,
and
B = 0.846
NA
Selenium
(dissolved)
01145
µ
g/L
NA
 
5.0 NA
TRC
 
50060
µ
g/L
19 11
NA
Zinc
(dissolved)
01090
µ
g/L
exp[A
+Bln(H)] X
0.978* where
exp[A
+Bln(H)] X
0.986* where
NA

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Constituent STORET
Number
Unit AS CS HHS
A = 0.884, and
B = 0.8473
A = 0.884, and
B = 0.8473
 
Benzene
  
78124
34030
µ
g/L
3900 NA
800 NA
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
µ
g/L
0.086 0.036
NA
Ethylbenzene 78113 μg/L 150 14 NA
Hexachloroethane
 
34396
µ
g/L
NA NA
6.7
Methylene chloride
 
34423 mg/L
NA
NA
2.6
Parathion
 
39540
µ
g/L
0.065 0.013
NA
Pentachlorophenol
 
03761
µ
g/L
exp B ([pH]
+A) where
A = -4.869,
and
B = 1.005
 
exp B ([pH]
+A) where
A = -5.134,
and
B = 1.005
NA
Toluene
 
78131 mg/L
2000 NA
610 NA
51.0
Tricholroethylene
 
39180
µ
g/L
NA NA
370
Xylene(s) 81551
µ
g/L
1200 490 NA
 

 
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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
 
(Source: Amended at 21 Ill. Reg. 1356, effective December 24, 1997, amended in
__________ at __________ Ill. Reg. _______________, effective ________________,
2002)
 
 
Section 302.575 Procedures for Deriving Tier I Water Quality Criteria and
Values in the Lake Michigan Basin to Protect Wildlife
 
The Lake Michigan Basin Wildlife Criterion (LMWC) is the concentration of a substance
which if not exceeded protects Illinois wild mammal and bird populations from adverse
effects resulting from ingestion of surface waters of the Lake Michigan Basin and from
ingestion of aquatic prey organisms taken from surface waters of the Lake Michigan
Basin. Wildlife criteria calculated under this Section protect against long-term effects
and are therefore considered chronic criteria. The methodology involves utilization of
data from test animals to derive criteria to protect representative or target species: bald
eagle, herring gull, belted kingfisher, mink and river otter. The lower of the geometric
mean of species specific criteria for bird species or mammal species is chosen as the
LMWC to protect a broad range of species.
 
d) Calculation of TSV. The TSV, measured in milligrams per liter (mg/L), is
calculated according to the equation:
 
TSV = { [TD x Wt] / [UFa x UFs x UFl] } / { W +
Σ
[FTLi x BAFWLTLi] }
 
Where:
 
TSV = target species value in milligrams of substance per liter (mg/L).
TD = test dose that is toxic to the test species, either NOAEL or LOAEL.

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UFa = the uncertainty factor for extrapolating toxicity data across species
(unitless). A species-specific UFa shall be selected and applied to each
target species, consistent with the equation
UFs = the uncertainty factor for extrapolating from subchronic to chronic
exposures (unitless)
UFl = the uncertainty factor for extrapolation from LOAEL to NOAEL
(unitless)
Wt = average weight in kilograms (kg) of the target species
W = average daily volume of water in liters consumed per day (L/d) by
the target species
FTLi = average daily amount of food consumed by the target species in
kilograms (kg/d) for trophic level i
BAFWLTLi = aquatic life bioaccumulation factor with units of liter per
kilogram (L/kg), as derived in Section 302.570 for trophic level
 
e) Calculation of the Lake Michigan Basin Wildlife Criterion. TSVs are
obtained for each target species. The geometric mean TSVs of all
mammal species is calculated and also of all bird species. The LMWC is
the lower of the bird or mammal geometric mean TSV.
 
(Source: Added at 21 Ill. Reg. 1356, effective December 24, 1997, amended in
__________ at __________ Ill. Reg. _______________, effective ________________,
2002)

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