Illinois Administrative Code
Title 35 - ENVIRONMENTAL PROTECTION
Part 302 - WATER QUALITY STANDARDS
Subpart D - CHICAGO AREA WATERWAY SYSTEM AND LOWER DES PLAINES RIVER WATER QUALITY STANDARDS AND INDIGENOUS AQUATIC LIFE STANDARDS
Section 302.407 - Chemical Constituents
Current through Register Vol. 48, No. 12, March 22, 2024
a) The acute standard (AS) for the chemical constituents listed in subsection (e) must 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) must not be exceeded by the arithmetic average of at least four consecutive samples collected over any period of four days, except 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 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 sample was collected. To calculate the attainment status of chronic standards, the concentration of the chemical constituent 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) must not be exceeded, on a 12-month rolling average based on at least eight samples, collected in a manner representative of the sampling period, except as provided in subsection (d).
d) In waters where mixing is allowed under Section 302.102, the following apply:
e) Numeric Water Quality Standards for the Protection of Aquatic Organisms
Constituent |
AS (µg/L) |
CS (µg/L) |
Arsenic (trivalent, dissolved) |
340 X 1.0 *=340 |
150 X 1.0*=150 |
Benzene |
4200 |
860 |
Cadmium (dissolved) |
eA+B ln(H) X {1.138672 -[(ln(H))(0.041838) ]}*, where A=-2.918 and B=1.128 |
eA+B ln(H) X {1.101672 -[(ln(H))(0.041838)]}*, where A= -3.490 and B=0.7852 |
Chromium (hexavalent, total) |
16 |
11 |
Chromium (trivalent, dissolved) |
eA+B ln(H) X 0.316 *, where A=3.7256 and B=0.8190 |
eA+B ln(H) X 0.860 *, where A=0.6848 and B=0.8190 |
Copper (dissolved) |
eA+B ln(H) X 0.960 *, where A=-1.645 and B=0.9422 |
eA+B ln(H) X 0.960*, where A=-1.646 and B=0.8545 |
Cyanide** |
22 |
10 |
Ethylbenzene |
150 |
14 |
Fluoride (total) |
eA+B ln(H), where A=6.7319 and B=0.5394 |
eA+B ln(H), but must not exceed 4.0 mg/L, where A=6.0445 and B=0.5394 |
Lead (dissolved) |
eA+B ln(H) X {1.46203 -[(ln(H))(0.145712) ]}*, where A=-1.301 and B=1.273 |
eA+B ln(H) X {1.46203-[(ln(H))(0.145712)]}*, where A=-2.863 and B=1.273 |
Manganese (dissolved) |
eA+B ln(H) X 0.9812 *, where A=4.9187 and B=0.7467 |
eA+B ln(H) X 0.9812*, where A=4.0635 and B=0.7467 |
Mercury (dissolved) |
1.4 X 0.85 *=1.2 |
0.77 X 0.85*=0.65 |
Nickel (dissolved) |
eA+B ln(H) X 0.998 *, where A=0.5173 and B=0.8460 |
eA+B ln(H) X 0.997 *, where A=-2.286 and B=0.8460 |
Toluene |
2000 |
600 |
TRC |
19 |
11 |
Xylene(s) |
920 |
360 |
Zinc (dissolved) |
eA+B ln(H) X 0.978 *, where A=0.9035 and B=0.8473 |
eA+B ln(H) X 0.986 *, where A=-0.4456 and B=0.8473 |
where:
µg/L |
= |
microgram per liter |
H |
= |
Hardness concentration of receiving water in mg/L as CaCO3 |
ex |
= |
base of natural logarithms raised to the x-power |
ln(H) |
= |
natural logarithm of hardness in mg/L as CaCO3 |
* |
= |
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 |
HHS (µg/L) |
Benzene |
310 |
Mercury (total) |
0.012 |
Phenols |
860,000 |
where:
µg/L |
= |
microgram per liter |
g) Numeric Water Quality Standards for Other Chemical Constituents
Concentrations of the following chemical constituents must not be exceeded except in waters for which mixing is allowed under Section 302.102.
Constituent |
Unit |
Standard |
Chloride |
mg/L |
500 |
Iron (dissolved) |
mg/L |
1.0 |
Selenium (total) |
mg/L |
1.0 |
Silver (dissolved) |
µg/L |
eA+B ln(H) X 0.85*, where A=-6.52 and B=1.72 |
Sulfate (where H is [GREATER THAN OR EQUAL TO] 100 but [LESS THAN OR EQUAL TO] 500 and C is [GREATER THAN OR EQUAL TO] 25 but [LESS THAN OR EQUAL TO] 500) |
mg/L |
[1276.7 +5.508(H) -1.457(C)] X 0.65 |
Sulfate (where H is [GREATER THAN OR EQUAL TO] 100 but [LESS THAN OR EQUAL TO] 500 and C is [GREATER THAN OR EQUAL TO] 5 but < 25) |
mg/L |
[-57.478 + 5.79(H) + 54.163(C)] X 0.65 |
Sulfate (where H > 500 and C [GREATER THAN OR EQUAL TO] 5) |
mg/L |
2,000 |
where:
mg/L |
= |
milligram per liter |
µg/L |
= |
microgram per liter |
H |
= |
hardness concentration of receiving water in mg/L as CaCO3 |
C |
= |
chloride concentration of receiving water in mg/L |
ex |
= |
base of natural logarithms raised to the x-power |
ln(H) |
= |
natural logarithm of hardness in milligrams per liter |
* |
= |
conversion factor multiplier for dissolved metals |
h) Concentrations of other chemical constituents in the South Fork of the South Branch of the Chicago River (Bubbly Creek) must not exceed the following standards:
CONSTITUENT |
CONCENTRATION (mg/L) |
Ammonia Un-ionized (as N*) |
0.1 |
Arsenic (total) |
1.0 |
Barium (total) |
5.0 |
Cadmium (total) |
0.15 |
Chromium (total hexavalent) |
0.3 |
Chromium (total trivalent) |
1.0 |
Copper (total) |
1.0 |
Cyanide (total) |
0.10 |
Fluoride (total) |
15.0 |
Iron (total) |
2.0 |
Iron (dissolved) |
0.5 |
Lead (total) |
0.1 |
Manganese (total) |
1.0 |
Mercury (total) |
0.0005 |
Nickel (total) |
1.0 |
Oil, fats and grease |
15.0** |
Phenols |
0.3 |
Selenium (total) |
1.0 |
Silver |
1.1 |
Zinc (total) |
1.0 |
Total Dissolved Solids |
1500 |
* For purposes of this Section, the concentration of un-ionized ammonia must be computed according to the following equation:
where:
U |
= |
Concentration of un-ionized ammonia as N in mg/L |
N |
= |
Concentration of ammonia nitrogen as N in mg/L |
T |
= |
Temperature in degrees Celsius |
** Oil must be analytically separated into polar and non-polar components if the total concentration exceeds 15 mg/L. In no case may either of the components exceed 15 mg/L (i.e., 15 mg/L polar materials and 15 mg/L non-polar materials).