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.

a)         This method shall also be used for non-BBCs when appropriately modified to consider the following factors:

1)         Selection of scientifically justified target species;

2)         Relevant routes of chemical exposure;

3)         Pertinent toxicity endpoints.

b)         Minimum data requirements:

1)         Test dose (TD).  In order to calculate a LMWC the following minimal data base is required:

A)        There must be at least one data set showing dose-response for oral, subchronic, or chronic exposure of 28 days for one bird species; and

B)        There must be at least one data set showing dose-response for oral, subchronic, or chronic exposure of 90 days for one mammal species.

2)         Bioaccumulation Factor (BAF) data requirements:

A)        For any chemical with a BAF of less than 125 the BAF may be obtained by any method; and

B)        For chemicals with a BAF of greater than 125 the BAF must come from a field measured BAF or Biota-Sediment Accumulation Factor (BSAF).

c)         Principles for development of criteria

1)         Dose standardization.  The data for the test species must be expressed as, or converted to, the form mg/kg/d  utilizing the guidelines for drinking and feeding rates and other procedures in 40 CFR 132, incorporated by reference at Section 302.510.

2)         Uncertainty factors (UF) for utilizing test dose data in the calculation of the target species value (TSV):

A)        Correction for intermittent exposure.  If the animals used in a study were not exposed to the toxicant each day of the test period, the no observed adverse effect level (NOAEL) must be multiplied by the ratio of days of exposure to the total days in the test period.

B)        Correction from the lowest observed adverse effect level (LOAEL) to NOAEL (UF₁).  For those substances for which a LOAEL has been derived, the UF₁ shall not be less than one and should not exceed 10.

C)        Correction for subchronic to chronic extrapolation (UF_s).  In instances where only subchronic data are available, the TD may be derived from subchronic data.  The value of the UF_s shall not be less than one and should not exceed 10.

D)        Correction for interspecies extrapolations (UF_a).  For the derivation of criteria, a UF_a shall not be less than one and should not exceed 100.  The UF_a shall be used only for extrapolating toxicity data across species within a taxonomic class.  A species specific UF_a shall be selected and applied to each target species, consistent with the equation in subsection (d).

d)         Calculation of TSV.  The TSV, measured in milligrams per liter (mg/L), is calculated according to the equation:

TSV =  {[TD x Wt] / [UF_a x UF_s x UF₁]}   /   {W + Σ[F_TLi x BAF_WLTLi]}

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:  Amended at 27 Ill. Reg. 166, effective December 20, 2002)