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Page 18 of 40<br />

Because EPA disapproved the omission of specifically named waterbodies, EPA put out<br />

for <strong>public</strong> notice and comment an amendment <strong>to</strong> Missouri’s 2002 Section 303(d) list that<br />

includes the waterbodies and pollutants added by EPA. EPA received the following <strong>comments</strong><br />

regarding the listing of those waterbodies:<br />

General Comments Regarding EPA’s Evaluation of Consent Decree Waterbodies:<br />

Comment:<br />

1. Three letters of comment that EPA received regarding the listing of 13 out of the 26<br />

Attachment B waters, contended that EPA’s Community Tolerance Index (CTI) is fundamentally<br />

flawed. Commenters said the single metric approach is not appropriate and only considers<br />

<strong>to</strong>lerance, and does not consider relative abundance among <strong>to</strong>lerance groups, as do other<br />

<strong>to</strong>lerance based metrics. MDNR’s Visual/Benthic reference key is not an appropriate level of<br />

taxonomic resolution <strong>to</strong> impose accurate <strong>to</strong>lerance values. The Visual/Benthic Surveys provided<br />

a rapid and inexpensive method for screening large numbers of waterbodies for obvious water<br />

quality problems and <strong>to</strong> determine where more intensive moni<strong>to</strong>ring is needed. Visual/Benthic<br />

Surveys consist of small amounts of chemical data, qualitative sampling of invertebrates or fish,<br />

and visual observations of streams, and therefore, are Level One data, according <strong>to</strong> the State’s<br />

2002 Listing Methodology. MDNR uses only Level Two or higher data <strong>to</strong> list waterbodies. The<br />

impairment scoring cut-off value of 6.5 was not explained by EPA and appears <strong>to</strong> be arbitrary.<br />

The Visual/Benthic Survey lacks proper QA/QC. EPA was quoted as having said in earlier<br />

correspondence with the State that “it was not clear whether or not benthic macro-invertebrates<br />

and fish are being identified at the survey sites by a qualified taxonomist, with samples verified<br />

in the lab with appropriate changes made for misidentification. One commenter added that it<br />

believes the differences of CTI values between waterbodies on either side of the 6.5 cu<strong>to</strong>ff value<br />

are insignificant and that the CTI values are contradic<strong>to</strong>ry <strong>to</strong> the stated evaluation for determining<br />

the quality of the flow in a stream and is, therefore, not a valid application of the testing data.<br />

2. One commenter asserted that the visual/benthic surveys do not indicate impairment.<br />

For instance, EPA’s justification for listing waters include: “large amounts of algae” (commonly<br />

occurs in even pristine streams due <strong>to</strong> edaphic and hydrologic variables); “slight turbidity” (this<br />

occurs in all streams including the most pristine streams in the state); “elevated conductance” (is<br />

a measure of dissolved solids, but no exceedence of the state <strong>to</strong>tal dissolved solids (TDS) or<br />

sulfate + chloride standard data was provided); and “reduced aquatic diversity” (East Honey<br />

Creek and Sandy Creek were placed on the list for poor aquatic diversity but McCarty Creek,<br />

which had virtually the same aquatic life, was not listed because EPA judged it had acceptable<br />

AQL diversity).<br />

3. It was asserted that EPA made several decisions regarding attainment of Missouri’s<br />

general water quality criteria based on observations made by MDNR field personnel that cannot<br />

be supported by any factual evidence or measurements, and that other specific waterbody

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