首页> 外文会议>Eighth international heavy minerals conference 2011. >Setting Restoration Goals for Restoring Pit Lakes as Aquatic Ecosystems – A Case Study from Southwest Australia
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Setting Restoration Goals for Restoring Pit Lakes as Aquatic Ecosystems – A Case Study from Southwest Australia

机译:为恢复深水湖泊作为水生生态系统制定恢复目标–来自澳大利亚西南部的案例研究

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摘要

Pit lakes may form when open cut mining leaves a pit void that then fi lls with ground and surfacernwaters. This often replaces terrestrial ecosystems that existed prior to mining with an aquaticrnecosystem, affording an opportunity to improve regional aquatic biodiversity values through targetedrnaquatic restoration (McCullough and van Etten, 2011). Restoration theory provides guidance whenrnrestoring disturbed systems towards landscapes that are of regional value and relevance. But how dornwe identify a restoration target for a novel aquatic habitat that only exists in the new post-miningrnlandscape? This paper presents a process of fi rst identifying and then surveying local representativernaquatic systems, to provide a direction for pit lake restoration efforts and achievement criteria for pitrnlake relinquishment, using a case study from a sand mining operation amongst wetlands in southwesternrnAustralia.rnThe company mines silica sands following mechanical removal of topsoil and then extraction ofrnthe ore from below the watertable by dredging. Assessment of wetland and riparian vegetation wasrnachieved through the establishment and measurement of temporary monitoring transects acrossrnfi ve natural wetlands in the Kemerton area. Several more regional wetlands were also visited andrnobservations made to supplement and validate these data.rnDistinct vegetation zonation was found across each wetland, although typically wetland basinsrnwere unvegetated or fi lled with younger woody plants with patchy distributions. Fringing riparianrnvegetation consisted of few species (commonly the paperbark Melaleuca rhaphiophylla and the sedgernLepidosperma longitudinale), but community composition and structure were variable betweenrnwetlands. The pattern of vegetation seen across natural wetlands was best explained by topographyrnand soil chemistry, with low lying wetland areas more likely to experience regular fl ooding andrnaccumulate organic matter and nutrients.rnIn conclusion, where they are available, regional natural waterbodies may constitute the best validrnrestoration goal. Nevertheless, the goal may need to consist of a range of closure design opportunities,rnrather than a single target.
机译:当露天开采留下一个坑洞,然后充满地下水和地表水时,可能​​会形成坑湖。这通常用水生生态系统代替采矿前存在的陆地生态系统,从而提供了通过有针对性的水生恢复来改善区域水生生物多样性价值的机会(McCullough and van Etten,2011)。在将受干扰的系统恢复为具有区域价值和相关性的景观时,恢复理论提供了指导。但是,我们如何确定仅存在于新的采矿后景观中的新型水生生境的恢复目标呢?本文以澳大利亚西南部湿地中的一个采砂作业为例,提出了一个首先识别然后调查当地代表性水生系统的过程,以为坑湖修复工作提供指导,并确定坑湖放水的实现标准。机械去除表土后,通过疏ging从地下水位以下提取矿石。通过建立和测量凯默顿地区五个自然湿地上的临时监测断面,对湿地和河岸植被进行了评估。还访问了另外几个区域湿地,并进行了保育观察,以补充和验证这些数据。尽管每个湿地通常都没有植被或充满了片状分布的年轻木本植物,但在每个湿地上都发现了不同的植被带。边缘的河岸植被由很少的物种组成(通常是树皮的美白千层树和莎草纵树),但是在湿地之间群落组成和结构是可变的。可以通过地形和土壤化学来最好地解释整个自然湿地上的植被格局,低洼湿地地区更容易出现规律的洪水,有机物质和养分积累。rn总之,区域自然水体可能是最好的有效恢复方法。目标。尽管如此,目标可能需要包括一系列的封闭设计机会,而不是单个目标。

著录项

  • 来源
  • 会议地点 Perth(AU);Perth(AU)
  • 作者单位

    Terrestrial Ecology Research Group, 270 Joondalup Drive, Perth WA 6027. Email: e.van_etten@ecu.edu.au;

    Principal Environmental Scientist, Golder Associates, West Perth WA 6005. Email: cmccullough@golder.com.au Mine Water and Environment Research Centre (MiWER), 270 Joondalup Drive, Perth WA 6027. Email: c.mccullough@ecu.edu.au;

    Mine Water and Environment Research Centre (MiWER), 270 Joondalup Drive, Perth WA 6027. Email: m.lund@ecu.edu.au;

  • 会议组织
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类 矿物学;矿物学;
  • 关键词

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