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Appendix CRF - Part 3 - Northamptonshire County Council

Appendix CRF - Part 3 - Northamptonshire County Council

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Radiological Assessment 0820-2<br />

Version 2<br />

Following deposit of the waste the material is levelled and compacted and<br />

intermediate inert cover materials placed over the top. Cover materials are currently<br />

sourced on site and are primarily made up of waste clays from the mineral excavation<br />

operations. Alternative cover materials are being investigated. Wastes are deposited<br />

in controlled layers to ensure adequate compaction and minimise settlement.<br />

Leachate forms in both open and capped cells as rainwater infiltrates through the cap,<br />

if present, and the waste. Leachate levels are monitored through a series of boreholes<br />

across the site, and excess leachate is removed by pumping. The leachate can be<br />

managed by recirculation in Cells 1 and 2 but is otherwise removed by tanker for<br />

treatment off site. The amount of leachate allowed to accumulate is regulated, with<br />

trigger levels of 2 m head in the sumps and 1 m in the monitoring wells. The Annual<br />

Monitoring Report for 2007 shows that these levels are maintained except during<br />

periods of unusually high rainfall.<br />

The “Kings Cliffe Landfill Site Annual Monitoring Report 2007” (ENRMF was<br />

formerly known as Kingscliffe or Slipe Clay pit) reports that approximately<br />

5000 tonnes of leachate were abstracted from the site during 2007 and transferred to a<br />

disposal facility. The “Pollution Inventory reporting form” submitted to the<br />

Environment Agency for the site reports 5402 tonnes of landfill leachate (EWC code<br />

19 07 03) being discharged in 2007.<br />

Leachate abstracted from the site is transferred by tanker to an off-site facility for<br />

treatment and discharge. The current arrangement is for transfer to a biological<br />

treatment plant at Avonmouth, discharge to trade effluent sewer and further treatment<br />

at a water treatment plant. There are feasibility studies underway for use of an<br />

alternative off-site facility and for construction of an on-site leachate treatment plant.<br />

The closed cells are capped with a composite cap consisting of a gas drainage layer,<br />

clay regulating layer, geotextile protector, geosynthetic clay liner, LDPE<br />

geomembrane liner and soil cover.<br />

There are lagoons on site that receive surface water that does not enter the disposal<br />

cells. Water from one lagoon is used for dust suppression. After capping, surface<br />

water will be directed to settling ponds and then discharged to a swallow hole<br />

(northern slopes) or surface water (southern areas).<br />

Following capping, the landfill site will enter a post closure managed stage. This stage<br />

will include the maintenance of leachate levels and gas abstraction, and will continue<br />

until it can be confirmed that the site no longer represents a significant risk of<br />

pollution of the environment or harm to human health. Leachate, surface water and<br />

groundwater quality will be monitored throughout the post closure managed stage.<br />

2.1.2 Geology and hydrogeology<br />

The regional geology comprises a sequence of Jurassic sedimentary rocks, including<br />

limestones, clays and mudstones (Table 2.2). On higher ground, the Jurassic rocks<br />

are overlain by Pleistocene glacial clays.<br />

Galson Sciences Limited 6 14 July 2009<br />

WS010001/ENRMF/CONSAPP<strong>CRF</strong> 556

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