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4. Typical rain barrel setup, to collect stormwater runoff from a rooftop [source: ] 

4. Typical rain barrel setup, to collect stormwater runoff from a rooftop [source: ] 

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This research estimates nitrogen removal from stormwater runoff using a denitrifying bioretention system using the USEPA Storm Water Management Model Version 5 (SWMM-5). SWMM-5 has been used to help planners make better decisions since its development in 1971. A conventional bioretention system is a type of Low Impact Development (LID) technology,...

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... Asphalt/concrete: Fine particles are left out, to improve porosity [Bean et al., 2004]. Rain barrels are an excellent LID technology, as they are easily installed and relatively cheap; therefore making them affordable for private homeowners. Rain barrels are large contains that attach to roof gutters (Figure 2.4). A traditional home is equipped with rain gutters, which are designed to concentrate stormwater runoff to designate outlets; therefore reducing the flooding around a residential home (for example). “ ...

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Citations

... There are generally three routing methods in the SWMM model including: (a) in constant current mode (steady); (b) kinematic wave; and (c) dynamic wave [43,44]. In this study, the dynamic wave routing mode was selected to simulate the runoff routing in the study area. ...
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... The pollutant generation were modeled by use of different land-use rate, wash-off rate, event mean concentration (EMC) or reported pollutant concentrations. Several treatment equations were analyzed and used to represent different pollutant removal processes in each layer as reported in [56,80,96,109]. All the tanks were designed to perform different treatment processes, such as sedimentation, filtration, nutrient uptake and the anaerobic processes for the removal of the pollutants. A hydraulic retention time of 8-10 h was considered inside the tank for effective treatment. ...
... A hydraulic retention time of 8-10 h was considered inside the tank for effective treatment. To verify and compare the behavior of the pollutant removal equations, a similar system was described in [56], in which a bio-retention model that was developed and configured based on a development plan provided by Sarasota country in Florida was used. The aim of that study was to control the nitrogen in stormwater runoff. ...
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... In addition, stormwater models have largely focused on vegetated filtration systems, such as grass swales and bioretentions, 17,18 where extensive laboratory and field investigations are available. Siriwardene et al. (2007) 19 used the results of laboratory experiments to test two models to predict the sediment transport through a stormwater gravel filter and found the models were able to reliably predict sediment behavior in clean filters but failed once the filter accumulated sediment. ...
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... The mean effluent concentrations of nitrogen and phosphorus (mg L −1 ) for bioretention mesocosms. HRT has been reported to be crucial for nitrogen removal in BCs in many studies [57][58][59][60]. Figure 3 shows that the removal rate of nitrate was linearly related to HRT at the 1 to 3 day retention times to test, most likely reflecting first-order kinetics of denitrification in these reactors. The removal efficiencies of nitrate in each module increased with the increase in HRT. ...
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... A removal algorithm for total nitrogen (TN) will be based on Masi (2011). In this thesis research, Masi used SWMM-5 to model nitrogen removal in a proposed bioretention system in Venice, Florida. ...
... Moving forward, we plan to alter the nitrogen removal algorithm created by Masi (2011) to account for the differences between our study site and Masi's site. In particular, because SMP device C does not have a specifically designed denitrification layer, we will not use equation (6-6) to describe nitrate removal via a denitrification layer. ...
... First, the SWMM GUI allows for water quality modeling in which the pollutant reduction is a function of one or more specific parameters (hydraulic residence time, flow, depth, or surface area). As noted previously, Masi (2011) has found that TKN removal can be modeled as an exponential decay function of hydraulic residence time. ...
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The continued development of urban areas in recent decades has caused multiple issues affecting the sustainability of urban drainage systems. The increase of impervious surface areas in urban regions alters watershed hydrology and water quality. Typical impacts to downstream hydrologic regimes include higher peak flows and runoff volumes, shorter lag times, and reduced infiltration and base flow. Urban runoff increases the transport of pollutants and nutrients and thus degrades water bodies downstream from urban areas. One of the most frequently used practices to mitigate these impacts is bioretention. Despite its widespread use, research on bioretention systems remains active, particularly in terms of mix design and nitrogen treatment. Recent research focusing on bioretention is reviewed herein. The use of mesocosms provides the ability to isolate particular treatment processes and replicate variability. Computational models have been adapted and applied to simulate bioretention, offering potential improvements to their operation, maintenance, and design. Maintenance practices are important for sustained operation and have also been reviewed. Predicting maintenance is essential to assessing lifecycle costs. Within these research areas, gaps are explored, and recommendations made for future work.