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FLINT RIVER TOPICS

The Upper Flint River Basin

South Fork.

A number of factors make the upper Flint River Basin an appropriate setting for developing science to address water and ecosystem management issues. The upper Flint River flows unimpeded by major impoundments for about 195  river miles from its Piedmont headwaters onto the Coastal Plain Province and harbors habitats and biologically diverse communities that have been lost from impounded reaches of many other eastern rivers. The upper Flint River Basin also supplies water to a growing population in the Atlanta metropolitan area and is a major recreational resource for the region, providing canoeing, white-water rafting, and sportfishing opportunities.

Long-term streamflow gaging stations have provided flow data for more than 90  years in the upper Flint River Basin. Recently completed investigations of freshwater mussel distributions and fish-habitat relations in the upper mainstem, and an aquatic Gap Analysis Program (GAP), provide baseline data for the system. Continued growth in the Atlanta area will increase pressure on the ecological systems of the Flint River Basin because of the potential for increased water withdrawals, reservoir construction for water storage, urban runoff, and additional wastewater loadings. Thus, this setting incorporates problems common to many regions and rivers in the Eastern United States — how to balance water-supply development with protection of diverse aquatic ecosystem — and provides an opportunity for interdisciplinary innovation in providing science-based solutions.

CHARACTERISTICS OF THE UPPER FLINT RIVER BASIN

The Flint River begins beneath Hartsfield – Jackson International Airport on the south side of Atlanta and flows southward across the Georgia Piedmont and Coastal Plain to its junction with the Chattahoochee River, later forming the Apalachicola River. The upper Flint River Basin has a drainage area of about 2,630  square miles. Land use in the basin, which includes parts of the upper Coastal Plain, consists of about 57  percent forest, 17  percent agriculture, and 12  percent urban, with most of the urban land concentrated in the extreme northern part of the basin (Georgia Land Use Trends, 1998).

Population growth in the six-county Upper Flint Water Supply Management Area (UFWSMA, shown below) has increased more than 200 percent since 1970, from 133,470 to 302,714 during 2000 (CH2MHill, 2003). Predictions are that more than 550,000 persons will live in the six-county UFWSMA by 2030.

Water-Supply and Instream-Flow Issues

Most of the water supply in the upper Flint River Basin comes primarily from the Flint River or its tributaries. Withdrawal from the 32 permitted municipal and industrial water-supply intakes totals about 108 million gallons per day (Mgal/d) and agricultural interests are permitted to remove an additional 90  Mgal/d from streams in the basin (Victoria P. Trent, Georgia Environmental Protection Division, written commun., 2005). Proposals have been submitted to increase surface-water supply capacity in the upper Flint River Basin by 12.7  Mgal/d (about 7  percent) by building two additional reservoirs and expanding an existing reservoir (Georgia Department of Natural Resources, 2003a). Under an interim State policy, required minimum flows below new reservoirs or stream withdrawals must adhere to one of three guidelines. Provide a minimum of:

  • the monthly 7Q10 (the 7-day, consecutive low flow with a 10-year return frequency);
  • 30 percent of the mean-annual flow for unregulated streams; or
  • seasonally adjusted percentage of mean-annual flow for regulated streams.

The guidelines also suggest that site-specific studies can be used to determine minimum flows.

Stormwater Runoff

Stormwater runoff increases as impervious surface increases. This affects stream geomorphology, water quality, temperature, aquatic ecosystems, and stream baseflows. No statewide policy currently exists to manage stormwater runoff except related to construction. Some municipal and county governments have implemented, or are in the process of implementing, stormwater-management programs.

Federally and State-Listed Aquatic Species

The upper Flint River Basin contains extensive shoal habitat that supports riverweed (Podostemum ceratophyllum), waterwillow (Justicia sp.), and shoal lily (Hymenocalis coronaria). At least five fish species that are endemic to the Apalachicola River Basin occur in the upper Flint River Basin. The upper Flint River Basin historically supported at least 25  species of mussels including 6 federally listed species. Recent surveys have reported only 20 species of native mussels remaining in the basin.

Water Quality and Aquatic Biological Integrity

Urban development in the upper Flint River Basin has resulted in water-quality problems in the headwaters. Studies in the early 1970s noted severe water- quality problems due to high levels of bacteria and nutrients in many of the tributaries and the mainstem reaches of the upper Flint River. During the period between 1972 and 1990, ammonia, dis- solved nitrate, and phosphorous decreased in the mainstem reaches due to improve- ments in the quality of wastewater dis- charges. A study conducted during 1992 found that nutrient levels in the mainstem of the Flint River decreased by almost an order of magnitude from those found during the mid-1980s (Frick and others, 1996). From 1998 to 2002, 28 stream seg- ments in the Flint River Basin were listed as not supporting or only partially sup- porting their designated water uses. Of the 28 stream segments, 14 are located in the upper Flint River Basin and were listed as having poor or very poor fish and inverte- brate communities (Georgia Department of Natural Resources, 2003b).

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