开发多条证据线,降低排水与地表面积比,利用生物滞留技术有效控制暴雨规模。

Thomas P O'Connor
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引用次数: 0

摘要

在美国环境保护局爱迪生环境中心建造了生物滞留单元,以评估排水与地表径流比,从而确定生物滞留雨水控制的规模。在宽度保持不变(7.1 米)的情况下,对三种规格的水力隔离生物滞留单元进行了重复测试,通过将最小(3.7 米)到最大(14.9 米)的连续长度加倍,改变从入口墙开始的长度纵横比。流域面积名义上相同,因此最大的重复单元的流域面积与地表面积之比为 5.5:1,中间单元为 11:1,最小单元为 22:1。每个单元都安装了含水量反射仪(WCR)和热敏电阻器,以进行连续监测,并从 2009 年 11 月起收集数据。生物滞留单元最初由种植介质填充,其中沙子和泥炭藓的体积比分别为 90% 和 10%,重量比分别约为 99% 和 1%。然后,在 2010 年 5 月至 11 月期间,在这些单元中种植了各种耐淹水、耐旱和耐盐的本地草、多年生植物、灌木和树木。2012 年底,对这些生物滞留单元中种植的灌木进行了调查。对灌木的含水量、降雨量和大小进行综合分析后公布的结果表明,根据 WCR 测量,较小单元中的灌木由于根部区域更频繁地饱和而生长得更好,而最大单元中的植物,尤其是远离径流进入的前墙的植物,可能只依赖于直接降雨。从 2017 年开始,对这些单元进行了额外的监测,包括通过工程种植介质的着火损失和总磷进行化学分析,以及对植物进行额外的调查。与之前的研究一样,中型(11:1)和小型(22:1)生物滞留单元中的植物比大型单元(5.5:1)中的植物生长得更好,而且小型单元中的有机物和磷积累得更多。在远离进水口的两个最大的生物滞留单元中,有一种草很耐旱,这表明这些单元中的植物依靠降雨而不是雨水径流。过大的单元没有完全利用雨水控制量,与较小单元中的植物相比,许多其他原始植物生长较慢或分布较少,而较小单元中的植物淹水更频繁,生长也更旺盛:实际应用:确定雨水控制的大小可能很困难,因为这些结构的最终设计通常有多重目标,包括安全和防洪。本文介绍的结果表明,如果目标是创建一个具有健康植被的生物滞留区,则可以接受较小的控制区,因为较小的渗透控制区将具有更健康的植被,并在整个暴雨过程中进行渗透。对于市政当局来说,这意味着以前认为太小而不能用于雨水渗透控制的路权可以转为这种用途。这并没有使市政当局摆脱解决洪水和安全设计目标的雨水系统,而是表明在市政道路上增加植物种植有助于解决雨水问题以及其他目标,如温室气体排放、减少城市热岛和清洁空气。分布式生物滞留控制可收集部分或全部较小、最频繁降雨事件的径流,应在各城市及其整体雨水控制系统中采用。如果担心径流堵塞,屋顶径流可能更适合生物滞留,或需要采取其他措施,如沉积物捕捉或增加维护。
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Developing Multiple Lines of Evidence to Decrease Drainage-to-Surface Area Ratio for Effective Stormwater Control Sizing Using Bioretention.

Bioretention units were constructed at the US Environmental Protection Agency's Edison Environmental Center to evaluate drainage-to-surface runoff ratio for sizing of bioretention stormwater controls. Three sizes of hydraulically isolated bioretention units were tested in duplicate with changes in aspect ratio of length from inlet wall by doubling successive length from smallest (3.7 m) to largest (14.9 m) while width remained the same (7.1 m). The watershed areas were nominally the same, resulting in watershed-to-surface area ratios of 5.5:1 for largest duplicate units, 11:1 for the middle units, and 22:1 for the smallest. Each unit was instrumented for continuous monitoring with water content reflectometers (WCRs) and thermistors with data collected since November 2009. The bioretention units were filled with planting media initially comprising 90% sand and 10% sphagnum peat moss by volume and approximately 99% and 1%, respectively, by weight. These units were then planted between May and November of 2010 with a variety of native grasses, perennials, shrubs, and trees that were tolerant to inundation, drought and salt. In late 2012, a survey of the shrubs planted in these bioretention units was performed. The published results of the combined analyses of moisture content, rainfall, and size of shrubs indicated that the smaller units had superior shrub growth due to the more frequent saturation of the root zone as measured by WCR, while the plants in the largest units, particularly away from front wall where runoff entered, potentially relied on direct rainfall only. Starting in 2017, additional monitoring was performed in these units, including chemistry analysis by loss on ignition and total phosphorus of the engineered planting media and an additional survey of the plants. As in the previous study, plants did better in the medium (11:1) and small (22:1) bioretention units than in the largest units (5.5:1), and there was greater buildup of organic matter and phosphorus in the smaller units. One species of grass that dominated the two largest bioretention units away from the inlet was drought tolerant, which indicated that plants in these units relied on rainfall rather than stormwater runoff. Oversized units did not completely use the stromwater control volume, and many of the other original plantings grew slower or were less widespread in comparison to plantings in that smaller units that flooded more frequently and achieved greater growth.

Practical applications: Defining the size of stormwater controls can be difficult because there are often multiple objectives imposed on the final design of these structures, including safety and flooding. Results presented here would indicate that if the objective is to create a bioretention area with healthy vegetation, undersized controls may be acceptable because undersized infiltrating controls will have healthier plantings and infiltrate throughout the storm. For municipalities, this means that rights of way previously thought to be too small to use for infiltrative stormwater controls may be converted to such a purpose. This does not free municipalities from stormwater systems that address flooding and safety design objectives, but demonstrates that increasing plantings in the municipal right of way could help to address stormwater as well as other objectives, like greenhouse gas emissions, urban heat island reduction, and clean air. Distributed bioretention controls that capture part or all the runoff of the smaller, most frequent rainfall events should be incorporated throughout municipalities and into their overall stormwater control systems. If clogging by runoff is a concern, roof runoff may be more appropriate for bioretention, or other measures such as sediment capture or increased maintenance may need to be performed.

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