O'Connor Thomas P
Environmental Engineer, United States Environmental Protection Agency, Stormwater Management Branch, 2890 Woodbridge Ave. (MS-104), Edison, NJ 08817.
J Sustain Water Built Environ. 2023 Feb;9(1):1-12. doi: 10.1061/jswbay.0001005.
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.
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.
在美国环境保护局的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的比例,用于确定生物滞留雨水控制设施的尺寸。对三种尺寸的水力隔离生物滞留单元进行了重复测试,通过将进水墙长度的长宽比翻倍,使长度从最小的(3.7米)依次增加到最大的(14.9米),而宽度保持不变(7.1米)。集水区面积名义上相同,导致最大的重复单元的集水区与表面积之比为5.5:1,中间单元为11:1,最小单元为22:1。每个单元都安装了水分含量反射仪(WCR)和热敏电阻进行连续监测,自2009年11月起收集数据。生物滞留单元最初填充了种植介质,按体积计最初包含90%的沙子和10%的泥炭藓,按重量计分别约为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、耐旱和耐盐的本地草本植物、多年生植物、灌木和树木。2012年末,对这些生物滞留单元中种植的灌木进行了调查。已发表的关于水分含量、降雨量和灌木大小综合分析的结果表明,较小的单元灌木生长较好,因为根据WCR测量,根区的饱和频率更高,而最大单元中的植物,特别是远离径流进入的前墙的植物,可能仅依赖直接降雨。从2017年开始,在这些单元中进行了额外的监测,包括通过灼烧减量和工程种植介质的总磷进行化学分析以及对植物的额外调查。与之前的研究一样,植物在中等(11:1)和小型(22:1)生物滞留单元中比在最大单元(5.5:1)中生长得更好,并且较小单元中有机物和磷的积累更多。在远离进水口的两个最大生物滞留单元中占主导地位的一种草具有耐旱性,这表明这些单元中的植物依赖降雨而不是雨水径流。尺寸过大的单元没有完全利用雨水控制量,与较小单元中更频繁被淹没且生长更好的种植相比,许多其他原始种植生长较慢或分布不广。
确定雨水控制设施的尺寸可能很困难,因为这些结构的最终设计通常有多个目标,包括安全性和防洪。此处给出的结果表明,如果目标是创建一个植被健康的生物滞留区域,尺寸过小的控制设施可能是可以接受的,因为尺寸过小的渗透控制设施将有更健康的植被,并且在整个降雨过程中都能进行渗透。对于市政当局来说,这意味着以前认为太小而无法用于渗透雨水控制的道路用地可能会被改作此用途。这并没有使市政当局摆脱应对防洪和安全设计目标的雨水系统,但表明增加市政道路用地中的植被有助于应对雨水问题以及其他目标,如温室气体排放、减少城市热岛效应和清洁空气。应在整个市政区域内并将其纳入整体雨水控制系统中,设置分散的生物滞留控制设施,以捕获部分或全部较小、最频繁降雨事件的径流。如果担心径流造成堵塞,屋顶径流可能更适合用于生物滞留,或者可能需要采取其他措施,如沉积物捕获或增加维护。