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dc.contributor.authorChao Guo
dc.contributor.authorQi Wang
dc.contributor.authorWei Bo
dc.contributor.authorJiake Li
dc.date.accessioned2025-08-17T22:21:58Z
dc.date.available2025-08-17T22:21:58Z
dc.date.copyright8/1/2025 12:00:00 AM
dc.date.issued2025
dc.identifier.otherJSWBAY.SWENG-588.pdf
dc.identifier.urihttp://yetl.yabesh.ir/yetl1/handle/yetl/4306830
dc.description.abstractInitial rainwater carries a large number of pollutants, easily causing urban nonpoint source pollution. Determining the concentration of pollutants in initial rainwater is crucial for controlling urban nonpoint source pollution. In this study, we monitored 38 and 46 rainfall events from March 2016 to September 2021 to study the concentration of pollutants in initial rainwater from roof and road runoffs. Moreover, we determined the volume of initial abandoned rainwater and analyzed the influences of stormwater concentration infiltration on soil. Results show that the concentrations of pollutants from road runoff are considerably higher than those from roof runoff. The concentrations of chemical oxygen demand (COD), ammonium nitrogen (NH4+-N), nitrate nitrogen (NO3−-N), total nitrogen (TN), total phosphorus (TP), and Zn from road runoff are 3.67, 2.37, 2.67, 1.99, 2.24, and 6.61 times higher than those from roof runoff. The concentrations of pollutants from road and roof runoffs decrease gradually with monitoring time. The initial abandoned rainwater from road runoff should be collected within 10–15 min from the start of a rain event, and that from roof runoff should be collected within 8–10 min. The concentrated infiltration of rainfall runoff has a great effect on the surface soil of rain gardens. The NH4+-N, TN, Zn, Cd, and Pb concentrations within the 0–30 cm soil layer are considerably higher than those in the 40–50 cm soil layer. However, TP and NO3−-N migrate downward with water infiltration. The rain garden showed a moderate mass load reduction for TP (67.23%) and TN (43.40%), respectively, mainly resulting from runoff volume reduction. In addition, the rain garden significantly reduced the NH4+-N and heavy metals mass loads of Cu, Zn, Cd, and Pb from rainfall runoff by 92.77%, 91.18%, 93.45%, 94.29%, and 92.06%, respectively. With the acceleration of urbanization and the gradual increase of the impervious area of the city, the pollutants carried by the rainfall runoff have increased dramatically. The impact of urban nonpoint source pollution of rainfall runoff is becoming more serious gradually, especially the initial rainwater. This study recommends the suggested values of initial rainwater collection standards of different underlying surfaces. The initial abandoned rainwater from road runoff should be collected within 10–15 min from the start of a rain event, and that from the roof runoff should be collected within 8–10 min. This study’s results can provide recommendations to the government for implementing stormwater management strategies to minimize stormwater pollution. Furthermore, the upper soil of a rain garden is a sensitive area under the influence of stormwater concentration infiltration. This study suggests the sustainable management of nitrogen is challenged in rain gardens, and it is likely to be achieved via biological pathways, including plant uptake and conversion to gaseous form via denitrification.
dc.publisherAmerican Society of Civil Engineers
dc.titleInitial Urban Stormwater Runoff Pollution and Its Fate in Rain Garden Soil
dc.typeJournal Article
dc.journal.volume11
dc.journal.issue3
dc.journal.titleJournal of Sustainable Water in the Built Environment
dc.identifier.doi10.1061/JSWBAY.SWENG-588
dc.journal.fristpage04025008-1
dc.journal.lastpage04025008-14
dc.page14
dc.treeJournal of Sustainable Water in the Built Environment:;2025:;Volume ( 011 ):;issue: 003
dc.contenttypeFulltext


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