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Using Science to Develop a Sustainable Management Policy for Acid Sulfate Soils in Queensland, Australia

机译:利用科学发展澳大利亚昆士兰酸硫酸盐土壤的可持续管理政策

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Coastal acid sulfate soils (ASS) are wetland soils and unconsolidated sediments that contain iron sulfides which, when exposed to atmospheric oxygen in the presence of water, form sulfuric acid. ASS form in protected low energy environments such as barrier estuaries and coastal lakes and commonly occur in low lying coastal lands as Holocene marine muds and sands. When disturbed, the iron sulfides in these soils can oxidise and produce large volumes of sulfuric acid (essentially similar chemistry to acid rock drainage with mines) resulting in the subsequent release of toxic levels of iron, aluminium, manganese and possibly heavy metals. This results in detrimental effects on aquatic biota, plants, animals and steel/concrete structures and on human health in the surrounding environment. There are an estimated 2.3 million ha of ASS located along 6500 km of the Queensland coastline. In contrast to many mineral sulfides encountered in the mining industry, the pyrite crystals in ASS can be as small as 2 mm and commonly occur as framboids with extremely large surface area per unit mass, substantially increasing their reactivity if exposed to air (oxidation). Highly reactive iron monosulfides can also occur, particularly in drains and shallow lakes. Many coastal areas, where some 80 per cent of the population of Queensland reside, are coming under pressure for agricultural and urban development. Construction of canal estates, marinas, housing/industrial estates, roads, golf courses, aquaculture ponds, sand/gravel extraction and drainage for sugar cane can disturb ASS and release sulfuric acid, which may then drain into adjacent waterways with heavy rain. As development continues to encroach on coastal lowlands, the identification, quantification and management of ASS must be addressed as part of a commitment to the principles of Ecologically Sustainable Development (ESD). ASS can be successfully managed by adopting best practices and following guidelines, but government, community and industry must collaborate to raise awareness, avoid 'hot spots' and develop more cost-effective solutions. Scientists led the education and public awareness program showing infrastructure and environmental damages arising from ASS in Queensland. Using results from mapping and research, they convinced policy makers, industry and polititians to accept the need for legislation founded on good science. The resulting 'State Planning Policy 2/02: Planning and Managing Development Involving Acid Sulfate Soils' identifies the State's interest in acid sulfate soils. The Queensland Government considers that development involving acid sulfate soils in low-lying coastal areas should be planned and managed to avoid potential adverse effects on the natural and built environment (including infrastructure) and human health. SPP 2/02 states where the policy applies and when a development application will trigger the policy. It can also be used to assist local governments in preparing their planning schemes under the 'Integrated Planning Act 1997'. The SPP 2/02 comes with a 'State Planning Policy 2/02 Guideline' to provide advice and technical information on interpreting and implementing the SPP 2/02. This guideline has legal status in assisting in the interpretation of SPP 2/02. Those seeking more detailed technical information can now also access the 'Soil Management Guidelines' and ASS 'Sampling Guideline', available from the Department of Natural Resources and Mines website. These are some of a series of chapters being developed for the 'Queensland Acid Sulfate Soil Technical Manual'.
机译:沿海酸性硫酸盐土壤(屁股)是湿地土壤和未溶胀的沉积物,其含有硫化铁,当在水存在下暴露于大气氧时,形成硫酸。屁股形式,受保护的低能量环境,如屏障河口和沿海湖泊,通常发生在低洼的沿海地上,如全茂海洋泥浆和沙子。受到干扰时,这些土壤中的硫化硫化物可以氧化并产生大量的硫酸(基本上与矿物酸岩排水的化学)产生随后的毒性水平的铁,铝,锰和可能的重金属。这导致对周围环境中的水生生物群,植物,动物,钢/混凝土结构和人类健康产生了不利影响。据估计,距离昆士兰海岸线有6500公里的近6500公里,估计有230万公顷。与采矿工业中遇到的许多矿物硫化物形成鲜明对比,屁股中的黄铁矿晶体可以小至2mm,并且通常以每单位质量极大的表面积为极大的表面积,如果暴露于空气(氧化),则基本上增加其反应性。高反应性铁硫化物也可能发生,特别是在漏斗和浅湖中。许多沿海地区,昆士兰州占80%的居住地,正在受到农业和城市发展的压力下。运河庄园建设,马林纳斯,住房/工业庄园,道路,高尔夫球场,水产养殖池,砂/砾石提取和用于甘蔗的排水可以干扰屁股和释放硫酸,然后可以排水到大雨中的相邻水道中。由于开发继续侵占沿海低地,必须作为对生态可持续发展原则(ESD)的承诺的一部分,确定,量化和管理。可以通过采用最佳实践和以下指导方针成功管理屁股,但政府,社区和行业必须合作以提高意识,避免“热点”并开发更具成本效益的解决方案。科学家们带领教育和公众意识计划,展示了昆士兰州屁股产生的基础设施和环境损害。利用映射和研究的结果,他们相信政策制定者,行业和政治家接受了对良好科学的立法的需求。由此产生的国家规划政策2/02:涉及酸性硫酸盐土壤的规划和管理发展识别国家对酸性硫酸盐土壤的兴趣。昆士兰州政府认为,应计划和设法涉及低洼沿海地区酸性硫酸盐土壤的发展,以避免对自然和建筑环境(包括基础设施)和人类健康的潜在不利影响。 SPP 2/02状态在策略适用的情况下,当开发申请触发策略时。它也可用于协助地方政府在“1997年”的“综合规划法”下编制计划计划。 SPP 2/02附带了“国家规划政策2/02指南”,提供有关解释和实施SPP 2/02的建议和技术信息。本指南有助于解释SPP 2/02的法律地位。那些寻求更详细的技术信息的人现在还可以从自然资源和矿山网站提供的“土壤管理指南”和“采样指导方针”。这些是为“昆士兰酸性硫酸盐土壤技术手册”开发的一系列章节。

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