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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 />

Landfill History<br />

13.3.45 In<strong>for</strong>mation on the landfill was provided by Clackmannanshire Council. The south-eastern part<br />

of the site is situated on the Black Devon Landfill. The Black Devon Landfill was operated by<br />

Clackmannanshire Council as a waste disposal site from 1979 until April 2004. The site<br />

<strong>for</strong>med part of a land reclamation project to reduce the erosion of land at the junction of the<br />

Black Devon River and the Forth Estuary.<br />

13.3.46 The site was initially developed to accept the residual waste generated by the <strong>for</strong>mer adjacent<br />

Alloa Incineration Plant and other wastes from local businesses (including sludge cake from<br />

the adjacent sewage works) and other industrial activity within Clackmannanshire. The site<br />

also received untreated domestic waste when the incinerator was closed <strong>for</strong> maintenance.<br />

After the incinerator was closed, pulverised domestic waste was co-disposed with sewage<br />

sludge. Sewage sludge continued to be disposed of at the site until the Scottish Water policy<br />

changed and sewage sludge was treated at the sewage plant. When the incinerator closed in<br />

1996, the site became the disposal point <strong>for</strong> Council collected household and commercial<br />

wastes.<br />

Landfill Liner<br />

13.3.47 There is no landfill liner, however the landfill is underlain by clay superficial deposits which<br />

were noted to be intact at the time of excavation. The clay superficial deposits were also used<br />

to create bunds to separate out the landfill cells. Initially leachate from the site was discharged<br />

through flap valve discharge valves into the Black Devon River and the River Forth. However,<br />

the leachate is now collected in two subterranean tanks and pumped to the sewage treatment<br />

works. The leachate is believed to be largely confined to the site. Water ingress into the<br />

<strong>for</strong>mer landfill site is also believed to be occurring, as the volumes of leachate removed are<br />

larger than expected.<br />

13.3.48 The operational site was closed in April 2004 and restored in 2005. The restoration comprised<br />

a Geosynthetic Clay Liner (GCL) capped with 0.5m of restoration clays and soils.<br />

Site Investigation Data<br />

13.3.49 From intrusive investigations in the south-eastern part of the site, the depth to waste is<br />

between 5.9m below ground level (bgl) and 8.6m bgl (proven depth), with an unproven depth<br />

of made ground at one location to 8.8m bgl. It was noted that the majority of locations were<br />

underlain by superficial deposits of sandy clay, firm brown grey clay or firm brown gravelly clay.<br />

13.3.50 Made ground deposits typically comprised of household refuse, plastic, metal, wood, wire,<br />

timber and paving slabs.<br />

Gas and Leachate Monitoring<br />

13.3.51 The gas monitoring data shows the typical levels of methane are between 53%v/v and 66%v/v<br />

and carbon dioxide to range between 0.0%v/v and 34.3%v/v. The most recent records are<br />

from 2009.<br />

November 2010 Chapter 13 Page 15<br />

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

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