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Forthbank Wind Energy Development - Partnerships for Renewables

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<strong>Forthbank</strong> <strong>Wind</strong> <strong>Energy</strong> <strong>Development</strong><br />

considered to have a limited affect on background sound levels. Inspection of the data<br />

generally tends to support this, given the absence of any identifiable clear data trends that are<br />

normally characteristic of a site affected by rain related background sound levels (such as flat<br />

clusters of data on the noise versus wind plot, or sharp increases in noise followed by a<br />

progressive decrease with time). Notwithstanding this, the possibility exists that some of the<br />

measured background noise data at low wind speeds may have been increased by<br />

extraneous or rain related influences. Time-histories of the noise levels at each survey<br />

location were inspected to look <strong>for</strong> any atypical relationships when compared to the wind<br />

speeds present during that time. Any elevated levels found in this way were excluded. The<br />

trend of the data when plotted against wind speed was also inspected to look <strong>for</strong> atypical<br />

relationships or outliers within the data-set which were excluded.<br />

8.3.15 Any data removed from the analysis in the ways described above is indicated on the charts as<br />

red circles, as detailed in Appendix 8.2.<br />

8.3.16 Following removal in particular of rain-affected periods, the range of wind speeds considered<br />

in this analysis was effectively restricted to wind speeds of up to 8m/s. The background noise<br />

is thought likely to generally continue increasing with rising wind speeds, based on experience<br />

of similar environments. Nonetheless, the limits derived in this report have been limited to a<br />

constant value from the highest measured wind speeds. Similarly, when the data trendline<br />

appeared to increase at the lowest wind speeds, the limit was kept constant as this was<br />

considered more representative.<br />

8.3.17 Following the removal of the excluded data points due extraneous noise, the best-fit lines<br />

were generated using a polynomial fit of a maximum of 4 th order. These lines of fit were then<br />

used to derive the noise limits required by ETSU-R-97 that apply during the day-time and<br />

night-time periods up to 12m/s. The corresponding ETSU-R-97 noise limits are summarised in<br />

Tables 8.4 and 8.5. The noise limits have been set either at the prevailing measured<br />

background level plus 5 dB, or at the relevant fixed lower limit, whichever is the greater. The<br />

derivation of the relevant fixed lower limit value used <strong>for</strong> day-time periods is described in<br />

paragraph 8.2.16.<br />

Table 8.4 Daytime L A90,T Noise Limits (dB) Derived from the Baseline Noise Survey<br />

According to ETSU-R-97<br />

Property<br />

<strong>Wind</strong> Speed at 10m Height, m/s<br />

3 4 5 6 7 8 9 10 11 12<br />

Park Farm 35.0 35.4 37.5 40.2 43.4 46.9 46.9 46.9 46.9 46.9<br />

Dunmore Home Farm 36.9 38.3 40.8 44.3 48.0 50.1 50.1 50.1 50.1 50.1<br />

13 Riverside View 40.6 42.3 43.9 45.2 46.3 46.9 46.9 46.9 46.9 46.9<br />

Inch of Ferryton 35.0 35.4 37.5 40.2 43.4 46.9 46.9 46.9 46.9 46.9<br />

Craigrie 35.0 35.4 37.5 40.2 43.4 46.9 46.9 46.9 46.9 46.9<br />

Dunmore East 36.9 38.3 40.8 44.3 48.0 50.1 50.1 50.1 50.1 50.1<br />

Dunmore Town 36.9 38.3 40.8 44.3 48.0 50.1 50.1 50.1 50.1 50.1<br />

Bowhouse Gardens 40.6 42.3 43.9 45.2 46.3 46.9 46.9 46.9 46.9 46.9<br />

South Alloa 40.6 42.3 43.9 45.2 46.3 46.9 46.9 46.9 46.9 46.9<br />

12 Riverside View 40.6 42.3 43.9 45.2 46.3 46.9 46.9 46.9 46.9 46.9<br />

November 2010 Chapter 8 Page 10<br />

Copyright <strong>Partnerships</strong> <strong>for</strong> <strong>Renewables</strong> <strong>Development</strong> Co. Ltd 2010 ©

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