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Montgomery Canal Conservation Management Strategy (1.2MB PDF)

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12<br />

Changes in combined predicted frequency of occurence of all marginal and emergent species on<br />

the <strong>Montgomery</strong> <strong>Canal</strong> with increasing boat traffic<br />

Total predicted frequency of occurrence (per 150m length)<br />

10<br />

8<br />

6<br />

4<br />

2<br />

Average Section 1<br />

Section 2<br />

Section 3<br />

Section 4<br />

Section 5<br />

Section 6<br />

0<br />

0<br />

1,000 2,000 3,000 4,000 5,000 6,000 7,000<br />

Boat passages per year<br />

Changes in predicted frequency of occurence of all nationally scarce and uncommon aquatic species<br />

on the <strong>Montgomery</strong> <strong>Canal</strong> with increasing boat traffic<br />

Average total number of predicted frequency of ‘rare’ aquatic spp (per 150m length)<br />

2<br />

1.6<br />

1.2<br />

0.8<br />

0.4<br />

0<br />

0<br />

Average Section 1<br />

Section 2<br />

Section 3<br />

Section 4<br />

Section 5<br />

Section 6<br />

1,000 2,000 3,000 4,000 5,000 6,000 7,000<br />

Boat traffic (passages per year)<br />

Figure 3.11. Eaton and Willby Research Predictions for aquatic and marginal plant species.<br />

Research is based on vegetation data from 592 different canal sites, including the <strong>Montgomery</strong> <strong>Canal</strong>, and 14 environmental variables include annual<br />

boat movements, Environment Agency water quality class, dredging and time since dredging, channel profile and geographical location. Analysis<br />

follows similar systems to those used for river invertebrate prediction and classification system (RIVPACS), and predictive results have been tested<br />

and found accurate on two separate canal locations. Results are based on a dredged canal profile, and represent a final stable state.<br />

46

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