|


Introduction
Section 303(d) of the Clean Water Act requires that States identify waters which do not meet or
are not expected to meet applicable water quality standards. These water bodies are compiled into a list known
as the 303(d) list. The regulation (40 CFR 130.7) requires that each 303(d) list be prioritized and identify
waters targeted for Total Maximum Daily Load (TMDL) development in the next two years. The list is due every
even numbered year on the first of April.
As a result of several lawsuits concerning past 303(d)/TMDL processes, EPA has issued numerous
administrative interpretations, administrative procedures, policies and guidance (some still in draft form) from
both headquarters and regional offices for preparation of the 1998, 303(d) list. These documents serve primarily
to stimulate questions about how this "new" process relates to existing and future programs.


Methodology
Development of the 303(d) list is a byproduct of the preparation of the "Water Quality
Inventory Report" which is another requirement of the Clean Water Act. It is required by Section 305(b). Both of
these required documents were developed using extensive data from the fixed-station, ambient water quality
monitoring network operated by the Arkansas Department of Environmental Quality. This network currently includes
133 stations that are sampled monthly and an additional 103 stations that were sampled quarterly. More than 30
parameters are analyzed each time these stations are sampled. Additionally, 32 sites on the Buffalo River and
its tributaries have been sampled periodically for the last several years and provide excellent assessment data
for certain parameters. Data from special projects such as the Illinois River and Tributaries Project and TMDL
investigations on six small watersheds were used in this assessment. In addition, letters requesting information
and data concerning impaired waters within the State were sent to the United States Geological Service, the Soil
and Water Conservation Commission, the Arkansas Game and Fish Commission, the Ozark and Ouachita National
Forest, and the Arkansas Water Resources Center. Only limited data was submitted by these agencies.
The support or non-support of designated uses was assessed by comparing monitor data with
specific water quality criteria protective of those uses. The guidelines used for making monitored assessments
were modified from the EPA guidance document for the 1998 State Water Quality Assessment. The guidance used is
shown in Table 1. The criteria used in the guidance were from the ecoregion-based Water Quality Standards of
Arkansas, EPA's Quality Criteria for Water and the Safe Drinking Water Act Standards.
A significant modification was made from the EPA guidance and from previous assessments. The
modification includes the elimination of the "partially supporting" category. Since this category was ambiguous,
we have chosen to eliminate the category. This results in a definitive assessment of either "supporting" or
"non-supporting". However, there remained a need for a category of waters for which data indicate that the
quality may be of some concern, but which there is no quantitative criteria to measure against, e.g. nutrients,
storm flow turbidity or suspended solids. Also, in many instances there is substantial uncertainty about the
magnitude or frequency of exceeding a criteria which would result in nonsupport. We therefore established a
category for waters of concern. This category is basically equivalent to the category of "partial support" as we
used it in previous reports. That category was used when the "support" or "non-support" could not be accurately
determined for reasons listed above. The waters of concern category provides a "flag" for waters which will be
closely scrutinized in future assessments or in special assessment projects to determine subsequent listing of
these waters as "support" or "non-support".
Generally, only the current data was used to monitor a specific river reach on which the data
was generated. Other reaches within the segment where no monitoring data exists were placed in the unassessed
category. In some cases, professional judgment, personal knowledge, historical data and/or current data from
adjacent stream reaches allowed for determination of an evaluated assessment of some stream reaches.


Table 1 - Assessment Guidance
| PARAMETER |
SUPPORT |
NON-SUPPORT |
WATERS OF CONCERN |
| |
DATA POINTS EXCEEDING CRITERIA |
| Temperature |
≤ 25% |
>25% |
|
| Dissolved Oxygen |
≤ 10% |
>10% |
|
| pH |
≤ 10% |
>10% |
|
| Total Ammonia-N |
≤ 10% |
>10% |
|
| NO3-Nitrogen (Drinking Water) |
≤ 10% |
>10% |
|
| NO3-Nitrogen (Aquatic Life) |
|
|
>Ecoregion Mean1 |
| Total Phosphorus |
|
|
>Ecoregion Mean1 |
| CL/SO4/TDS (Ecoregion)2 |
≤ 50% |
>50% |
|
| CL/SO4/TDS (Drinking Water) |
≤ 10% |
>10% |
|
| Dissolved Metals3 |
Acute4 |
Chronic |
Acute4 |
Chronic |
|
| Cadmium (Cd) |
≤ 1 |
≤ 10% |
>1 |
>10% |
|
| Chromium (Cr) |
≤ 1 |
≤ 10% |
>1 |
>10% |
|
| Copper (Cu) |
≤ 1 |
≤ 10% |
>1 |
>10% |
|
| Lead (Pb) |
≤ 1 |
≤ 10% |
>1 |
>10% |
|
| Zinc (Zn) |
≤ 1 |
≤ 10% |
>1 |
>10% |
|
| Bacteria |
|
|
|
| Primary Contact |
≤ 25% |
>25% |
|
| Secondary Contact |
≤ 25% |
>25% |
|
| Turbidity |
|
|
|
| Base Flows |
≤ 25% |
>25% |
>10% |
| Storm Flow5 |
≤ 10% |
>10% |
|
| Fish Consumption |
No restrictions or limited consumption |
No consumption for any group of user |
|
1 Except for >1.0 ppm
immediately below the discharge of a STP.
2 Except for site specific standards.
3 Based on ecoregion hardness.
4 Refers to number of data points instead of percentages (i.e. greater than one
value exceeding criteria = non-support)
5 Criteria based on 90th percentile of ecoregion values. |


Table 2 - Water Quality Limited Waterbodies (303d) Prioritized and
Targeted for TMDL for FY 99-00 (PDF File) |