Research articleHydrological modeling and field validation of a bioretention basin
Introduction
Concrete-lined channels have often been used to manage stormwater in the tropics. However increasing urbanization and surface imperviousness can cause channel capacity to be exceeded, resulting in increased incidence of flooding in urban areas. Floods can be mitigated by encouraging local infiltration through Best Management Practices (BMPs) such as bioretention basins (Nehrke and Roesner, 2004). More importantly, such green infrastructure also reduces non-point source pollution and eutrophication by providing a surface basin and underlying soil treatment medium to remove pollutants such as nitrogen, phosphorus, and suspended solids (Payne et al., 2014). However, insufficient storage capacity in a basin impairs its treatment potential. An undersized basin will experience a high rate of overflow and allow stormwater to bypass storage and treatment, leading to pollutant removal rates below targets (Wang et al., 2017). How to size basins effectively to meet pollutant removal targets therefore is an important research and design question.
With the accumulation of experience in working with BMPs across the world over the past 20 years, BMPs have become part of a regulatory and planning requirement for land developers. Planners are required to demonstrate that with the installation of BMPs, the post-construction runoff will be able to replicate the pre-construction hydrology as closely as possible. It is therefore necessary to quantify accurately the effects of BMPs in encouraging infiltration and reducing stormwater discharge. However, current quantification of these effects, and hence design guidelines that arise from such quantification, has mostly been based on “rules of thumb,” such as the depth of rainfall to be captured (Wang et al., 2017), rather than predictive forecasting. The need to predict basin performance prompts the development and validation of the hydrological model for bioretention basins reported in this paper.
There are few hydrological models specifically for bioretention basins. Heasom et al. (2006) employed the Green-Ampt representation of infiltration to develop a simple model of bioretention basin infiltration and culvert bypass. Infiltration is represented as a two-stage process with two constant lumped rates: a rapid infiltration stage at the start of an event in the absence of surface ponding and a second steady infiltration stage when infiltration occurs under a surface ponding condition. As noted by the authors themselves, their method of modeling could be improved by relating infiltration to physical characteristics such as soil properties or by simulating saturated and unsaturated flow with a groundwater model. The HYDRUS software packages are finite-element variably-saturated models that numerically solve for the movement of water using the Richards' equation for unsaturated water flow (Šimůnek and Van Genuchten, 2006). Although this code models infiltration with an approach that is more physically based and with higher resolution than using lumped constants as by Heasom et al. (2006), it does not have a surface water balance to account for ponded infiltration nor is it specifically built for bioretention basins. A finite-element model of variably unsaturated flow was developed by He and Davis (2011) specifically for bioretention basins but this model considers theoretical rain storms rather than actual hydrographs and was not validated against field measurements. The model also lacks a complete accounting of surface-water flow into and out of the surface basin. Another complex model, RECHARGE, is an advanced hydrological model for bioretention basins that uses high-resolution modeling of unsaturated flow using the Richards' equation coupled with a surface water balance (Dussaillant et al., 2004). Since its development, RECHARGE has been verified against single events in a controlled experimental setting, but not at field scale or over a continuous time period that includes multiple storms and inter-storm periods.
The current literature lacks a field-verified, bioretention-basin-specific, high-resolution model to simulate ponded infiltration over a continuous time period. In this paper, we aim to bridge that gap by applying the RECHARGE model in a continuous simulation over a half year and validating the model against detailed field measurements of 80 events spanning a wide variety of rainfall depths and intensities in a tropical setting (Singapore). We present research on high-resolution single-event and continuous (half-year) modeling of hydrological behaviour that predicts time series of discharges from subsurface and surface outlets as well as the surface ponding depth and the soil moisture within the subsurface filter media. We then apply an infiltration index (ID) to describe predicted model performance for a range of engineering parameters. The objectives of this study were to (i) validate the applicability of the RECHARGE hydrological model for continuous simulation at field scale, (ii) predict bioretention basin performance in terms of infiltration capability as a function of engineering design parameters such as detention depth, ratio of drainage area to basin area, and saturated hydraulic conductivity of the soil media, and (iii) recommend basin configurations that improve performance efficiency.
Section snippets
Basin description
Fig. 1 shows a cross section of the Balam Estate Rain Garden bioretention basin in Singapore that was the location of this study. With an effective treatment area of 240 m2, the basin receives runoff from a 16,800 m2 residential catchment (about 88% surface imperviousness) with a time of concentration of about 10 min (Wang et al. 2009, 2017). Basin inflow infiltrates through four soil layers consisting of (from surface to bottom): a 40-cm sandy-loam filter layer; a 10-cm fine-sand transition
Governing equations
In the RECHARGE model, the variably-saturated subsurface flow is simulated with a one-dimensional mixed form of the Richards' equation which models both saturated and unsaturated conditions in the basin during wet and dry periods (Dussaillant et al., 2004). Under the “mixed” formulation of the Richards' equation, θ is a function of both h and z. The governing equation iswhere θ = soil moisture content (cm3/cm3); t = time (hr); z = vertical depth
Model calibration
The behaviour of both the surface basin and subsurface soil layers is affected by six parameters, of which two hydraulic parameters, Ks and Cw, are primary and four soil characteristic parameters, θs, θr, α, and n, are secondary. Values of the primary parameters were determined by calibration comparing the computed values of water level in the bioretention basin WLp, culvert discharge rate qc, and, to a lesser extent, outlet discharge qo against observed values to check the overall mass
Conclusions
The following may be concluded from this study:
- 1.
The existing numerical model for bioretention basins, RECHARGE, is able to successfully simulate the hydrology of a bioretention basin in a tropical climate as demonstrated by comparisons with continuous field measurements in Singapore during 80 storm events over a half-year period.
- 2.
In our model, the weir coefficient for the overflow culvert, Cw, and the saturated hydraulic conductivity of the subsurface medium, Ks, are the main parameters affecting
Acknowledgements
This research was funded by the National Research Foundation, Prime Minister's Office, Singapore through the Singapore-MIT Alliance for Research and Technology's Center for Environmental Sensing and Modeling (CENSAM) research program. The authors thank Alejandro R. Dussaillant for providing the original RECHARGE codes.
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Present address: PUB, Singapore's National Water Agency, Water Quality Department, Raw Water System Division. 82 Toh Guan Road East, Waterhub C2-11, Singapore 608576, Singapore.