Organisations in Different Renewables

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amount of the copper flux entering the new storage. The work involved passive diversion of some flows to the already heavily polluted Queen River, and the sealing and revegetation of old tailings dumps to reduce leaching by rain water. The Queen River joins the King River downstream of the power station (see Map 2). Timber Salvage 48,900 m 3 of timber was salvaged from Mt Jukes Road and the storage area in conjunction with the Tasmanian Forestry Commission. The storage area was cleared from full supply level to two metres below the minimum operating level, to avoid unsightly dead trees and remove water hazards for boats using the lake. By maximising timber salvage, Hydro Tasmania generated favourable publicity, created jobs, provided the state government with revenue and minimised the areas that remained for storage clearing. Land Rehabilitation Immense effort was directed towards ensuring that the scheme should be as invisible as possible. Many environmental management plans were drawn up and adhered to from design through to construction and commissioning. Measures included stockpiling of peat and topsoil generated during construction for later re-use, use of native species for revegetation, and developing and utilising hydro-mulching for rocky and steep sites. 7. COMMISSIONING The most important considerations in commissioning of the King River Power Development were environmental. These were, in particular, concerns with: • heavy metals and water quality associated with the filling of the storage, Lake Burbury; • rescuing of stranded animals during lake filling; and • oxygen levels in the power station discharges. Water Quality in Lake Burbury Hydro Tasmania, working with the Inland Fisheries Commission Biological Consultancy (IFCBC), began a Lake Burbury water quality monitoring program with the commencement of filling of the lake in August 1991. The program was implemented in response to concerns about heavy metal contamination via polluted Linda and Comstock Creeks, which drained into the new storage, and as a means to monitor the effectiveness of ameliorative measures such as diversion works which had been put in place. The main objectives of the program included: • monitoring the development of the physico-chemical environment of the new storage, including changes associated with thermal stratification and decay of flooded vegetation; • assessing the spatial and temporal distribution of metal contamination in the water and sediments of Lake Burbury; • assessing the affect of any contamination on the productivity of the lake;

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