2005
DOI: 10.1672/0277-5212(2005)025[0051:vdicra]2.0.co;2
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Vegetation development in created, restored, and enhanced mitigation wetland banks of the United States

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Cited by 90 publications
(47 citation statements)
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“…While all three basins trended toward a more diverse and more hydrophilic community, nonnative species clearly influenced the overall floristic quality in the third year, particularly in Basins 1 and 3. Such variability is common in early successional mitigation wetlands; generally, species influx is much higher in newly created and restored wetlands than in natural systems but this influx declines over the first six years (Spieles 2005). The Dutch Fork data of this study provide a means of assessing the -relative importance of soil, seed bank, hydrologic regime, and proximity to inflow for plant community assortment in the third year.…”
Section: Discussionmentioning
confidence: 89%
“…While all three basins trended toward a more diverse and more hydrophilic community, nonnative species clearly influenced the overall floristic quality in the third year, particularly in Basins 1 and 3. Such variability is common in early successional mitigation wetlands; generally, species influx is much higher in newly created and restored wetlands than in natural systems but this influx declines over the first six years (Spieles 2005). The Dutch Fork data of this study provide a means of assessing the -relative importance of soil, seed bank, hydrologic regime, and proximity to inflow for plant community assortment in the third year.…”
Section: Discussionmentioning
confidence: 89%
“…Balcombe et al [30] and Spieles [31] reported that mitigation wetlands may take years or even decades to mature. Weaver et al [32] also indicated that very low variance in the FAMEs within the constructed wetland after 1 year operation, and reached a greater temporal stability.…”
Section: Discussionmentioning
confidence: 99%
“…Passive revegetation of Southeastern depressions might be less successful on agricultural lands, where drained depressions could have In a single-permit compensatory mitigation, failure to achieve equivalence to natural wetlands is of concern because the mitigation site is replacing a particular lost wetland type either concurrently or "after the fact". A potential advantage of mitigation banks is that if they hold a collection of restored wetlands with good ecological function (hydrology, vegetation, faunal habitat), the regulatory issue shifts to determining if an appropriate wetland type is available "before the fact" for in-kind replacement (Spieles 2005). Regardless of this advantage, the challenge remains that restoration success is rarely a simple yes/no outcome (Zedler and Callaway 2000).…”
Section: Ecological Outcomes Of Passive Restorationmentioning
confidence: 99%
“…Thus, these functional wetlands would meet or exceed the ecological performance standards advocated for mitigation-bank success (e.g., Spieles 2005;Reiss et al 2009). …”
Section: Ecological Outcomes Of Passive Restorationmentioning
confidence: 99%