LID-Based Ecological Planting Groove for Road Runoff Purification Research

Author(s):  
Xuexin Liu ◽  
Xueping Chen ◽  
Shaoyong Lu ◽  
Xinzhu Xiong ◽  
Shuohan Gao ◽  
...  
2012 ◽  
Vol 48 (4) ◽  
pp. 133-140
Author(s):  
KOUGA SHIGEIZUMI ◽  
CHIKAKO MARUO ◽  
MUNEHIRO NOMURA ◽  
YOSHIO AIKAWA ◽  
OSAMU NISHIMURA ◽  
...  
Keyword(s):  

2016 ◽  
Vol 102 ◽  
pp. 453-463 ◽  
Author(s):  
Maximilian Huber ◽  
Harald Hilbig ◽  
Sophia C. Badenberg ◽  
Julius Fassnacht ◽  
Jörg E. Drewes ◽  
...  

2005 ◽  
Vol 51 (9) ◽  
pp. 31-37 ◽  
Author(s):  
B. Shutes ◽  
J.B. Ellis ◽  
D.M. Revitt ◽  
L.N.L. Scholes

This paper presents the outcome of an inventory of planted wetland systems in the UK which are classified according to land use type and are all examples of sustainable drainage systems. The introduction of constructed wetlands to treat surface runoff essentially followed a 1997 Environment Agency for England and Wales report advocating the use of “soft engineered” facilities including wetlands in the context of sustainable development and Agenda 21. Subsequently published reports by the UK Construction Industry Research and Information Association (CIRIA) have promoted the potential benefits to both developer and the community of adopting constructed wetlands and other vegetated systems as a sustainable drainage approach. In addition, the UK Environment Agency and Highways Agency (HA) have recently published their own design criteria and requirements for vegetative control and treatment of road runoff. A case study of the design and performance of a constructed wetland system for the treatment of road runoff is discussed. The performance of these systems will be assessed in terms of their design criteria, runoff loadings as well as vegetation and structure maintenance procedures. The differing design approaches in guidance documents published in the UK by the Environment Agency, CIRIA and HA will also be evaluated.


Water ◽  
2017 ◽  
Vol 9 (10) ◽  
pp. 779 ◽  
Author(s):  
Rajendra Singh ◽  
Jiaguo Wu ◽  
Alagarasan Kumar ◽  
Dafang Fu

2006 ◽  
Vol 362 (1-3) ◽  
pp. 143-156 ◽  
Author(s):  
Camilla Westerlund ◽  
Maria Viklander
Keyword(s):  

Author(s):  
Chris Flynn

This paper has been developed from a third year dissertation written as part of the Diploma in Horticulture course at the Royal Botanic Gardens, Kew. It serves as an overview of the subject of ecological planting and its potential applications within public gardens. It also outlines some scientific benefits regarding ecological studies, the impact that this type of planting may have on horticulture (both in gardens and the nursery trade), and the educational benefits for the public and school groups. The case study below looks at the viability of representing a section of Snow Gum Grassy Woodland (a vegetation type found in New South Wales, Australia) outside in Coates Wood, Wakehurst Place, UK.


2021 ◽  
Author(s):  
Qiyue Hu ◽  
Song Zhu ◽  
Zanfang Jin ◽  
Aijing Wu ◽  
Xiaoyu Chen ◽  
...  

Abstract Increased nitrogen (N) from urban stormwater runoff aggravates the deterioration of aquatic ecosystems as urbanisation develops. In this study, the sources and transport of nitrate (NO3−) in urban stormwater runoff were investigated by analysing different forms of N, water isotopes (δD-H2O and δ18O-H2O), and NO3− isotopes (δ15N-NO3− and δ18O-NO3−) in urban stormwater runoff in a residential area in Hangzhou, China. The results showed that the concentrations of total N and nitrate N in road runoff were higher than those in roof runoff. Moreover, high concentrations of dissolved organic N and particulate N in road runoff led to significantly different TN concentrations in road runoff (mean: 3.76 mg/L) and roof runoff (mean: 1.23 mg/L). The high δ18O-NO3− values (mean: 60 ± 13.1‰) indicated that atmospheric deposition was the predominant NO3− source in roof runoff, as confirmed by the Bayesian isotope mixing model (SIAR model), contributing 83.6–97.8% to NO3−. The SIAR model results demonstrated that atmospheric deposition (34.2–91.9%) and chemical fertilisers (6.27–54.3%) were the main NO3− sources for the road runoff. The proportional contributions from soil and organic N were smaller than other sources in both the road runoff and roof runoff. For the initial period, the NO3− contributions from atmospheric deposition and chemical fertilisers were higher and lower, respectively, than those in the middle and late periods in road runoff during storm events 3 and 4, while an opposite trend of road runoff in storm event 7 highlighted the influence of short antecedent dry weather period. It was suggested that reducing impervious areas and more effective management of fertiliser application in urban green land areas were essential to minimize the presence of N in urban aquatic ecosystems.


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