首页> 外文期刊>Environmental Monitoring and Assessment >THE DEVELOPMENT OF BIOLOGICAL OBJECTIVES FOR STREAMS IN A SINGLE CATCHMENT: A CASE STUDY ON THE CATCHMENT OF WESTERN PORT BAY, VICTORIA, AUSTRALIA
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THE DEVELOPMENT OF BIOLOGICAL OBJECTIVES FOR STREAMS IN A SINGLE CATCHMENT: A CASE STUDY ON THE CATCHMENT OF WESTERN PORT BAY, VICTORIA, AUSTRALIA

机译:单一流域流域生物学目标的发展:以澳大利亚维多利亚州西港湾的流域为例

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Government environment protection policies for waterways have traditionally relied on water quality indicators and their objectives. In this paper we describe the development of biological objectives based on invertebrate indicators for inclusion in a government policy for the catchment of Western Port Bay, Victoria. The first step of defining segments (areas with streams in which the same objectives are applied) was problematic, requiring two different approaches, as follows. Site groups initially based on invertebrate community composition derived using multivariate techniques (ordination and classification) proved to be unsuitable for policy segments. Segment boundaries were subsequently defined using topographical (e.g. boundary of foothills and lowland plains), climate (e.g. rainfall) and land-use (e.g. urban) features. We used information and data from reference sites inside as well outside the catchment to derive specific biological objectives based on aquatic invertebrates for these segments. Objectives were specified for the following four indicators - number of invertebrate families, the SIGNAL index, the AUSRIVAS predictive model and the number of key families.
机译:传统上,政府的航道环境保护政策依靠水质指标及其目标。在本文中,我们基于无脊椎动物指标描述了生物学目标的发展,这些指标被纳入维多利亚州西港湾流域的政府政策中。定义段的第一步(在其中应用了相同目标的流区域)存在问题,需要如下两种不同的方法。最初基于多变量技术(排序和分类)得出的无脊椎动物群落组成的场所群被证明不适合政策细分。随后使用地形特征(例如山麓和低地平原的边界),气候特征(例如降雨)和土地利用特征(例如城市特征)来定义路段边界。我们使用来自集水区内部和外部参考站点的信息和数据,基于这些部分的水生无脊椎动物得出特定的生物学目标。为以下四个指标指定了目标:无脊椎动物家庭数量,SIGNAL指数,AUSRIVAS预测模型和关键家庭数量。

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