Illinois Administrative Code
Title 35 - ENVIRONMENTAL PROTECTION
Part 352 - PROCEDURES FOR DETERMINING WATER QUALITY BASED PERMIT LIMITATIONS FOR NATIONAL POLLUTANT DISCHARGE ELIMINATION SYSTEM DISCHARGERS TO THE LAKE MICHIGAN BASIN
Subpart D - ASSESSMENT OF REASONABLE POTENTIAL TO EXCEED WATER QUALITY STANDARDS, CRITERIA, AND VALUES
Section 352.421 - Estimation of Projected Effluent Quality
Current through Register Vol. 48, No. 38, September 20, 2024
a) The first step in determining if a reasonable potential to exceed the water quality standard exists for any particular pollutant parameter is the estimation of the maximum expected effluent concentration for that substance. That estimation will be completed for both acute and chronic exposure periods and is termed the PEQ. The PEQ shall be derived from representative facility specific data to reflect a 95 percent confidence level for the 95th percentile value. These data will be presumed to adhere to a lognormal distribution pattern unless the actual effluent data demonstrates a different distribution pattern. If facility specific data in excess of 10 data values is available, a coefficient of variation that is the ratio of the standard deviation to the arithmetic average shall be calculated by the Agency. The PEQ is derived as the upper bound of a 95 percent confidence bracket around the 95th percentile value through a multiplier from the following table applied to the maximum value in the data set that has its quality assured consistent with Section 352.410 as appropriate for acute and chronic data sets.
PEQ = (maximum data point)(statistical multiplier)
Coefficient of Variation |
|||||||
No. Samples |
0.1 |
0.2 |
0.3 |
0.4 |
0.5 |
0.6 |
0.7 |
1 |
1.4 |
1.9 |
2.6 |
3.6 |
4.7 |
6.2 |
8.0 |
2 |
1.3 |
1.6 |
2.0 |
2.5 |
3.1 |
3.8 |
4.6 |
3 |
1.2 |
1.5 |
1.8 |
2.1 |
2.5 |
3.0 |
3.5 |
4 |
1.2 |
1.4 |
1.7 |
1.9 |
2.2 |
2.6 |
2.9 |
5 |
1.2 |
1.4 |
1.6 |
1.8 |
2.1 |
2.3 |
2.6 |
6 |
1.1 |
1.3 |
1.5 |
1.7 |
1.9 |
2.1 |
2.4 |
7 |
1.1 |
1.3 |
1.4 |
1.6 |
1.8 |
2.0 |
2.2 |
8 |
1.1 |
1.3 |
1.4 |
1.6 |
1.7 |
1.9 |
2.1 |
9 |
1.1 |
1.2 |
1.4 |
1.5 |
1.7 |
1.8 |
2.0 |
10 |
1.1 |
1.2 |
1.3 |
1.5 |
1.6 |
1.7 |
1.9 |
11 |
1.1 |
1.2 |
1.3 |
1.4 |
1.6 |
1.7 |
1.8 |
12 |
1.1 |
1.2 |
1.3 |
1.4 |
1.5 |
1.6 |
1.7 |
13 |
1.1 |
1.2 |
1.3 |
1.4 |
1.5 |
1.6 |
1.7 |
14 |
1.1 |
1.2 |
1.3 |
1.4 |
1.4 |
1.5 |
1.6 |
15 |
1.1 |
1.2 |
1.2 |
1.3 |
1.4 |
1.5 |
1.6 |
16 |
1.1 |
1.1 |
1.2 |
1.3 |
1.4 |
1.5 |
1.6 |
17 |
1.1 |
1.1 |
1.2 |
1.3 |
1.4 |
1.4 |
1.5 |
18 |
1.1 |
1.1 |
1.2 |
1.3 |
1.3 |
1.4 |
1.5 |
19 |
1.1 |
1.1 |
1.2 |
1.3 |
1.3 |
1.4 |
1.5 |
20 |
1.1 |
1.1 |
1.2 |
1.2 |
1.3 |
1.4 |
1.4 |
30 |
1.0 |
1.1 |
1.1 |
1.1 |
1.2 |
1.2 |
1.2 |
40 |
1.0 |
1.0 |
1.1 |
1.1 |
1.1 |
1.1 |
1.1 |
50 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
60 or greater |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
Coefficient of Variation |
|||||||
0.8 |
0.9 |
1.0 |
1.1 |
1.2 |
1.3 |
||
10.1 |
12.6 |
15.5 |
18.7 |
22.3 |
26.4 |
||
5.4 |
6.4 |
7.4 |
8.5 |
9.7 |
10.9 |
||
4.0 |
4.6 |
5.2 |
5.8 |
6.5 |
7.2 |
||
3.3 |
3.7 |
4.2 |
4.6 |
5.0 |
5.5 |
||
2.9 |
3.2 |
3.6 |
3.9 |
4.2 |
4.5 |
||
2.6 |
2.9 |
3.1 |
3.4 |
3.7 |
3.9 |
||
2.4 |
2.6 |
2.8 |
3.1 |
3.3 |
3.5 |
||
2.3 |
2.4 |
2.6 |
2.8 |
3.0 |
3.2 |
||
2.1 |
2.3 |
2.4 |
2.6 |
2.8 |
2.9 |
||
2.0 |
2.2 |
2.3 |
2.4 |
2.6 |
2.7 |
||
1.9 |
2.1 |
2.2 |
2.3 |
2.4 |
2.5 |
||
1.9 |
2.0 |
2.1 |
2.2 |
2.3 |
2.4 |
||
1.8 |
1.9 |
2.0 |
2.1 |
2.2 |
2.3 |
||
1.7 |
1.8 |
1.9 |
2.0 |
2.1 |
2.2 |
||
1.7 |
1.8 |
1.8 |
1.9 |
2.0 |
2.1 |
||
1.6 |
1.7 |
1.8 |
1.9 |
1.9 |
2.0 |
||
1.6 |
1.7 |
1.7 |
1.8 |
1.9 |
1.9 |
||
1.6 |
1.6 |
1.7 |
1.7 |
1.8 |
1.9 |
||
1.5 |
1.6 |
1.6 |
1.7 |
1.8 |
1.8 |
||
1.5 |
1.5 |
1.6 |
1.6 |
1.7 |
1.7 |
||
1.3 |
1.3 |
1.3 |
1.3 |
1.4 |
1.4 |
||
1.1 |
1.2 |
1.2 |
1.2 |
1.2 |
1.2 |
||
1.1 |
1.1 |
1.1 |
1.1 |
1.1 |
1.1 |
||
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
b) If facility-specific data of 10 or less data values is available, an alternative PEQ shall be derived using the table in Section 352.421(a), assuming a coefficient of variation of 0.6, applied to the maximum value in the data set that has its quality assured consistent with Section 352.410.
c) The Agency shall compare monthly average effluent data values, when available, with chronic aquatic life, human health and wildlife standards to evaluate the need for monthly average WQBELs. The Agency shall use daily effluent data values to determine whether a potential exists to exceed acute aquatic life water quality standards.
d) The Agency may apply other scientifically defensible statistical methods for calculating PEQ at the 95th percentile value for use in the reasonable potential analysis as provided for in Procedure 5.b.2 of Appendix F to 40 CFR 132.
e) Regardless of the statistical procedure used, if the PEQ for the parameter is less than or equal to the water quality standard for that parameter, the Agency shall deem the discharge not to have a reasonable potential to exceed, and a water quality based effluent limit (WQBEL) shall not be required unless otherwise required under Section 352.430.