Pollutant removal from stormwater runoff by palustrine wetlands based on comprehensive budgets
References (39)
Introduction to nonpoint source pollution in the United States and prospects for wetland use
Ecol. Eng.
(1992)Designing constructed wetlands systems to treat agricultural nonpoint sourco pollution
Ecol. Eng.
(1992)Ancillary benefits and potential problems with the use of wetlands for nonpoint source pollution control
Ecol. Eng.
(1992)The role of flocculation in the filtering of particulate matter in estuaries
Landscape design and the role of created, restored, and natural riparian wetlands in controlling nonpoint source pollution
Ecol. Eng.
(1992)- et al.
Development and application of a geographic information system for wetland/watershed analysis
Computers, Environ. Urban Syst.
(1991) - et al.
Developing guidelines for constructed wetlands to remove pesticides from agricultural runoff
Ecol. Eng.
(1992) - et al.
The estuary as a filter for fine-grained suspended sediment
Water quality and fisheries issues
- et al.
Role of wetlands in the removal of suspended sediments
Bacteria and the assessment of water quality
Biological Methods for the Assessment of Water Quality, ASTM STP 528
The Use of Wetlands for Water Pollution Control
Highway runoff in the State of Washington: model verification and statistical analysis
Land Use and Water Quality: A Study of Laholm Bay's Drainage Area
Wetland systems for wastewater treatment: operating mechanisms and implications for design
A review of wetland water quality functions
Guide for water quality impact assessment of highway operations and maintenance
Wetlands and water quality
Cited by (38)
Environmental factors influencing the distribution of fecal coliform bacteria in Bandon Bay, Thailand
2023, Regional Studies in Marine ScienceManagement pathways for the successful reduction of nonpoint source nutrients in coastal ecosystems
2021, Regional Studies in Marine ScienceCitation Excerpt :Anthropogenic influence within the watershed dates back to the 1800’s when sawgrass (Cladium jamaicense) wetlands surrounding the bay were drained for agriculture and natural tidal creeks were straightened to allow for efficient drainage (Sarasota County, 2011). These modifications increased the rate of stormwater runoff into the bay (Sarasota County, 2011), reduced groundwater infiltration and natural removal of nutrients by sediments and vegetation (Reinelt and Horner, 1995). The estimated 1948 land cover was 61.7% forest, open area and park, 25% wetland, 9.5% agriculture, 3.2% open water with just 0.3% residential land use in the Roberts Bay North watershed (Sarasota County, 2011).
Modeling the hydrological significance of wetland restoration scenarios
2014, Journal of Environmental ManagementCitation Excerpt :These efforts include the development and use of tools to identify wetland restoration and conservation areas, demonstrate wetland services, and perform wetlands classifications. Although some studies have attempted to describe wetland functions using watershed models (Konyha et al., 1995; Reinelt and Horner, 1995; Hawk et al., 1999; Arnold et al., 2001; Kirk et al., 2004; Zhang and Mitsch, 2005; Liu et al., 2008, Wang et al., 2008; Melles et al., 2010; Yang et al., 2010), there are limitations primarily in over-simplification of wetland processes and understanding flood mitigation benefits based on wetland placement in a watershed (Drexier et al., 1999; Raisin et al., 1999; Wang et al., 2008; Yang et al., 2008). Efforts to simulate wetlands at the watershed scale are discussed below.
Stormwater ponds and biofilters for large urban sites: Modeled arrangements that achieve the phosphorus reduction target for Boston's Charles River, USA
2011, Ecological EngineeringCitation Excerpt :A “gardening” approach is recommended for maintenance of biofilters, as well as the vegetated areas surrounding ponds; this approach incorporates regular inspections, removal of leaf litter in the fall and of clippings post-mowing or pruning, and re-vegetating bare areas to minimize side-slope erosion. Possible explanations for the negative removals reported above—i.e., exports of P from pond and biofilter systems—which can be addressed through proper design, construction, and maintenance, include excessive soil disturbance during construction, lining systems with materials that minimize infiltration and decrease contact time between runoff and soils, applying mulch that leaches P, and allowing vegetation to decay in place (Dietz, 2007; Dietz and Clausen, 2005; Reinelt and Horner, 1995). The goals of this research are to evaluate the effects on water quality, i.e., level of phosphorus reduction from stormwater, associated with:
Mitigating nonpoint source pollution in agriculture with constructed and restored wetlands
2010, Advances in AgronomyCitation Excerpt :The discharge of agricultural runoff into surface water bodies has resulted in dramatic shifts in trophic relationships (Jeppesen et al., 2000), resulting in part from elevated P concentrations due to its limiting status in many freshwater ecosystems. CWs have become a popular management practice to remove P from agricultural runoff (Jordan et al., 2003; Raisin and Mitchel, 1995; Reinelt and Horner, 1995). However, due to the conservative nature of P in wetlands (i.e., no significant gaseous loss pathway), sustainable long-term P removal has proven to be particularly challenging given that wetland soils provide the only long-term P sink (DeBusk and DeBusk, 2000, DeBusk et al., 2005).