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BMP is being implemented and the appropriate pollutant reduction coefficients and<br />

unit costs specific to that BMP. These additional ‘units’ are b<strong>as</strong>ed on the difference<br />

between ‘existing’ and ‘future’ values (e.g. acres, stream miles) specified by the user<br />

for each BMP or pollutant reduction strategy. More specific information on the usage<br />

of PRedICT is provided in Evans (2003).<br />

POST-RESTORATION EVALUATION<br />

After restoration activities have been implemented in a watershed, the success of<br />

such activities is evaluated on the b<strong>as</strong>is of in-stream surveys conducted to verify<br />

if the health of the stream h<strong>as</strong> improved. If no improvements are noted, additional<br />

funds are provided by the State to implement more or better corrective me<strong>as</strong>ures in<br />

the watershed until the desired results are achieved. This is an iterative process that<br />

may take many years to complete in significantly degraded watersheds. However,<br />

this approach is predicated on the belief that moving towards a corrective solution is<br />

better than not moving at all.<br />

To date, few restoration projects funded through the Growing Greener programme<br />

have been in place long enough to warrant re-examination of affected streams.<br />

However, limited data from some fixed water quality monitoring stations maintained<br />

by PaDEP that are located at the mouth of watersheds where mitigation me<strong>as</strong>ures<br />

have been taken suggests that improvements in stream health are beginning to<br />

occur. Within the next 2–5 years, PaDEP plans to begin the process of re-surveying<br />

Pennsylvania’s streams to evaluate the effectiveness of mitigation me<strong>as</strong>ures that<br />

have been implemented over the p<strong>as</strong>t few years.<br />

Figure 4: Example of predicted load reductions via combined use of AVGWLF<br />

and PRedICT<br />

60

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