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Review of best management practices for aquatic vegetation control in stormwater ponds, wetlands, and lakes

机译:审查雨水池塘,湿地和湖泊中水生植物控制的最佳管理方法

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摘要

Auckland Council (AC) is responsible for the development and operation of a stormwater network across the region to avert risks to citizens and the environment.Within this stormwater network, aquatic vegetation (including plants, unicellular and filamentous algae) can have both a positive and negative role in stormwater management and water quality treatment. The situations where management is needed to control aquatic vegetation are not always clear, and an inability to identify effective, feasible and economical control options may constrain management initiatives. AC (Infrastructure and Technical Services, Stormwater) commissioned this technical report to provide information for decision- making on aquatic vegetation management with in stormwater systems that are likely to experience vegetation-related issues.Information was collated from a comprehensive literature review, augmented by knowledge held by the authors. This review identified a wide range of management practices that could be potentially employed. It also demonstrated complexities and uncertainties relating to these options that makes the identification of a best management practice difficult. Hence, the focus of this report was to enable users to screen for potential options, and use reference material provided on each option to confirm the best practice to employ for each situation.The report identifies factors to define whether there is an aquatic vegetation problem (Section 3.0), and emphasises the need for agreed management goals for control (e.g. reduction, mitigation, containment, eradication). Resources to screen which management option(s) to employ are provided (Section 4.0), relating to the target aquatic vegetation, likely applicability of options to the system being managed, indicative cost, and ease of implementation. Initial screening allows users to shortlist potential control options for further reference (Section 5.0).Thirty-five control options are described (Section 5.0) in sufficient detail to consider applicability to individual sites and species. These options are grouped under categories of biological, chemical or physical control. Biological control options involve the use of organisms to predate, infect or control vegetation growth (e.g. classical biological control) or manipulate conditions to control algal growth (e.g. pest fish removal, microbial products). Chemical control options involve the use of pesticides and chemicals (e.g. glyphosate, diquat), or the use of flocculants and nutrient inactivation products that are used to reduce nutrient loading, thereby decreasing algal growth. Physical control options involve removing vegetation or algal biomass (e.g. mechanical or manual harvesting), or setting up barriers to their growth (e.g. shading, bottom lining, sediment capping).Preventative management options are usually the most cost effective, and these are also briefly described (Section 6.0). For example, the use of hygiene or quarantine protocols can reduce weed introductions or spread. Catchment- based practices to reduce sediment and nutrient sources to stormwater are likely to assist in the avoidance of algal and possibly aquatic plant problems. Nutrient removal may be a co-benefit where harvesting of submerged weed biomass is undertaken in stormwater systems. It should also be considered that removal of substantial amounts of submerged vegetation may result in a sudden and difficult-to-reverse s witch to a turbid, phytoplankton dominated state. Another possible solution is the conversion of systems that experience aquatic vegetation issues, to systems that are less likely to experience issues.The focus of this report is on systems that receive significant stormwater inputs, i.e. constructed bodies, including ponds, amenity lakes, wetlands, and highly-modified receiving bodies. However, some information will have application to other natural water bodies.
机译:奥克兰市议会(AC)负责整个地区的雨水网络的开发和运营,以防止对公民和环境的风险。在这个雨水网络中,水生植物(包括植物,单细胞和丝状藻类)可以具有积极作用在雨水管理和水质处理中起负面作用。需要进行管理以控制水生植物的情况并不总是很清楚,无法确定有效,可行和经济的控制选择可能会限制管理措施。 AC(暴雨水基础设施和技术服务)委托本技术报告,以为可能在雨水系统中遇到与植被有关问题的雨水系统中的水生植被管理决策提供信息。信息来自全面的文献综述,并以知识为基础由作者持有。这次审查确定了可能被采用的广泛管理实践。它还显示了与这些选项相关的复杂性和不确定性,这使得难以确定最佳管理实践。因此,本报告的重点是使用户能够筛选潜在的选项,并使用每个选项提供的参考材料来确认针对每种情况采用的最佳做法。该报告确定了定义是否存在水生植被问题的因素(第3.0节),并强调需要商定的管理目标以进行控制(例如减少,缓解,遏制,根除)。提供了用于筛选要采用的管理选项的资源(第4.0节),涉及目标水生植被,选项对所管理系统的可能适用性,指示性成本以及易于实施。初步筛选使用户可以选择潜在的控制方案以供进一步参考(第5.0节)。其中有35种控制方案(第5.0节)进行了足够详细的描述,以考虑对单个场所和物种的适用性。这些选项分为生物,化学或物理控制类别。生物控制选择包括使用生物提前,感染或控制植物生长(例如经典生物控制)或操纵条件以控制藻类生长(例如去除害虫鱼,微生物产品)。化学控制选择包括使用农药和化学药品(例如草甘膦,敌草快)或使用絮凝剂和营养灭活产品,以减少营养物质的含量,从而减少藻类的生长。物理控制方案包括去除植被或藻类生物量(例如机械或人工收获),或设置阻碍其生长的屏障(例如遮光,底衬,沉积物封盖)。预防性管理方案通常是最具成本效益的,而且简短描述(第6.0节)。例如,使用卫生或检疫协议可以减少杂草的引入或扩散。以流域为基础的减少雨水沉积物和养分来源的做法可能有助于避免藻类和可能的水生植物问题。在雨水系统中进行淹没杂草生物量的收获时,去除养分可能是一项共同利益。还应考虑到,大量淹没植被的清除可能导致突然而难以逆转的状态转变为浑浊的浮游植物为主的状态。另一个可能的解决方案是将遇到水生植被问题的系统转换为不太可能遇到问题的系统。本报告的重点是接受大量雨水输入的系统,即人工构造的物体,包括池塘,舒适性湖泊,湿地,和高度修改的接收机构。但是,某些信息将适用于其他天然水体。

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