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Pumping from the White River
Present water users on the lower
White River consist of commercial navigation interests, riparian
agricultural diversions, recreation enthusiasts, and industrial
diverters. The state of Arkansas regulates the amount of water
available for diversion from the White River through the State Water Plan
(SWP). Administration of this plan and all regulation and permitting
activities are by the Arkansas Soil and Water Conservation Commission (ASWCC).
The present SWP has been in effect since 1986 when approved by the state
legislature. ASWCC is currently attempting to refine water
allocation procedures through a new SWP. At the time of this writing
(September 1996), the new SWP is only is draft form and has not yet
undergone public notice procedures.
The amount of flow in the White
River affects all river users. The ASWCC currently allocates water
from the White River basin. Present allocation limitations are
presented in the SWP: these allocations are based on mean monthly
discharges and several categories of minimum instream-flow criteria.
Instream-flow needs identified in the 1986 SWP are water quality,
fish and wildlife and navigation.
Soil Water Plan Flow for the White River
- January flow - 19,610 cfs
- February flow - 22,700 cfs
- March flow - 27,610 cfs
- April flow - 36,940 cfs
- May flow - 21,220 cfs
- June flow - 21,220 cfs
- July flow - 10,670 cfs
- August flow - 9,650 cfs
- September flow - 9,650 cfs
- October flow - 9,650 cfs
- November flow - 11,05 cfs
- December flow - 17,590 cfs
Evaluation of any impacts to the White River resulting form proposed
diversions was accomplished by HEC-5 water balance model.
Specifically, environmental and navigational impacts were analyzed.
Although minimum criteria may be refined by future updates and revisions
to the SWP, evaluation using the current SWP (1986 will identify any
potential impacts and their relative magnitude). As previously
stated, flow conditions on the White River are quite variable. This
translates into large fluctuations in water levels, or stages, with daily
changes in stage of 4-5 feet or more being possible. The relative
difference between pre- and post-diversion conditions should be viewed in
light of the natural variability.
Water Balance calculation were first based on seven minimum in-stream
flow conditions for the original project area and a maximum diversion of
1800 cfs. Use of the seven minimum in-stream flows provided data
necessary to determine the optimum pump cut-off level (i.e. minimum
in-stream flow). The minimum in-stream flows required by the SWP was
the only in-stream flow requirement evaluated for additional analyses,
because the SWP was the legal constraint and economic benefits for the
Grand Prairie Demo Project were optimized.
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