Alafia River Minimum Flows and Levels - Southwest Florida Water ...
Alafia River Minimum Flows and Levels - Southwest Florida Water ...
Alafia River Minimum Flows and Levels - Southwest Florida Water ...
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<strong>River</strong>, Myakka <strong>River</strong>, Withlacoochee <strong>River</strong>). This, in large part, prompted an<br />
evaluation of multidecadal differences in flow patterns.<br />
As a result of findings in, "<strong>Florida</strong> <strong>River</strong> Flow Patterns <strong>and</strong> the Atlantic<br />
Multidecadal Oscillation" (Kelly 2004), the District has identified two benchmark<br />
periods. One benchmark period corresponds to the warm phase of the AMO,<br />
<strong>and</strong> is correlated with a multidecadal period of higher rainfall <strong>and</strong> thus increased<br />
river flows, <strong>and</strong> one corresponds to the cool phase of the AMO, <strong>and</strong> is correlated<br />
with a multidecadal period of lower rainfall <strong>and</strong> thus climatically lower river flows.<br />
One of several approaches could be used in developing MFLs given that two <strong>and</strong><br />
not one benchmark period exists. If permitting or allowing consumptive water<br />
use (i.e., withdrawals) on a volume basis (a fixed withdrawal; e.g., 50 mgd) rather<br />
than on a percent of flow approach (e.g., 10% of the preceding day's flow), the<br />
more conservative approach toward ecology <strong>and</strong> aquatic resources of a system<br />
would be to use the drier period as the benchmark period, since this would yield<br />
the lowest withdrawal recommendation. This approach would protect from<br />
significant harm during the low flow period, <strong>and</strong> provide even greater protection<br />
during the higher flow period. If, however, permitting on a "percent of flow"<br />
approach, the more conservative approach would be to base permitting on the<br />
benchmark period that produces the lower percent recommendation. This would<br />
allow the recommended percent to be used in either benchmark period <strong>and</strong><br />
would allow the actual volume withdrawn to increase when flow enters the higher<br />
flow period. While it might seem intuitive that the lower flow period would always<br />
produce a lower recommended percent of flow reduction, this does not have to<br />
be the case.<br />
A third option would be to adjust either the permitted volume or percent of flow<br />
recommendation according to the AMO period that one happens to be in. From<br />
a water supply perspective, this would probably be the most desirable approach,<br />
since it would allow the maximum amount of water to be withdrawn consistent<br />
with multidecadal climatic conditions. This option, however, would be difficult to<br />
apply since there is currently no method for determining when a step change to a<br />
new climatic regime has occurred except in hindsight. Given the difficulty of<br />
determining when a step change has occurred <strong>and</strong> given that there are several<br />
advantages to the "percent of flow" approach (e.g., maintenance of the shape<br />
<strong>and</strong> seasonality of the natural hydrograph) over the fixed quantity approach, we<br />
have proposed flow reductions that would yield the lowest recommended percent<br />
withdrawal regardless of the benchmark period used. We in essence use two<br />
benchmark periods in developing our MFLs recommendations.<br />
Although some (e.g., Stoker et al. 1995, SDI 2003) have reported that <strong>Alafia</strong><br />
<strong>River</strong> flows have declined due to anthropogenic factors, we have demonstrated<br />
that much of the reported flow decline is attributable to either a natural climatic<br />
oscillation (step change) or to removal or reduction of mine related discharges.<br />
For this reason, we believe that the entire flow record for the mutidecadal period<br />
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