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A Comparative Evaluation of Mitigation Wetlands in Broward County, Florida, Using Chironomid (Ditera) Pupal Exuviae: A Potential Technique for Assessing Mitigation Success

机译:使用Chironomid(Ditera)Pupu Exuviae对佛罗里达州Broward县的缓解湿地进行比较评估:评估缓解成功的潜在技术

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摘要

Wetland resources in South Florida are regulated at three redundant jurisdictional levels: local or municipal regulations set forth by many independent jurisdictions, State regulations derived directly from Florida Statutes, and Federal regulations promulgated primarily under the Clean Water Act. All three levels of government can have jurisdiction over projects that affect regulated wetland resources, yet inconsistent policies and standards remain and continue to confound regulators despite decades of intensive coordination efforts and a rapidly growing scientific research base. The size of a wetland mitigation area is of primary consideration when evaluating its perceived ecological value, although wetland mitigation areas constructed in developed areas are typically isolated and generally make use of similar designs regardless of wetland size.The Chironomidae (Order: Diptera) are the most diverse and abundant faunal taxon in all healthy freshwater bodies and are generally considered to be a reliable and effective ecological indicator. I conducted a preliminary comparison of chironomid communities between a suite of natural and artificial wetlands, and also evaluated the effect of wetland size on the community structure of the insect family Chironomidae. Using the Chironomid Pupal Exuviae Technique (CPET), collections of chironomid exuviae from a total of seven natural and artificial mitigation wetlands were compared across site groups and also correlated to recorded environmental conditions at each study site.Chironomid species assemblages at nearly all sites were dominated by Parakiefferiella coronata, comprising nearly 36% of all collected exuviae. Species assemblages from mitigation wetlands exhibited strong similarity to the aggregate species assemblage from all sites. A greater abundance of exuviae was collected from artificial sites than from natural sites, and species assemblages collected from natural sites were dissimilar from those collected from artificial sites. No statistically significant differences in community structure were detected between larger and smaller wetlands. Environmental site conditions between natural and mitigation sites generally varied greatest in conductivity and pH. No significant gradient was identified in environmental conditions or chironomid community structure across wetlands of different size. A minor seasonal gradient in TP concentrations was observed and site S6 was the most enriched site included in this study while site S1 exhibited high conductivity for the duration of the project.Differences between chironomid species assemblages collected from natural and artificial communities may be explained by the relatively static topography, more consistent substrate composition, and less diverse hydrophyte communities present in the natural sites which have generally reached a greater state of homeostasis. However, statistical tests generally support the null hypothesis. No statistically significant differences were detected between sites based on collected chironomid communities when grouped by wetland origin (artificial vs. natural) or size.Observed differences between communities sampled from natural and artificial wetlands support regulatory concerns that artificial wetlands may not sufficiently emulate natural systems and that a constructed wetland system may take generations, or even centuries to sufficiently mimic its natural counterpart. Mitigation design complexity does appear to provide a diversity of microhabitats favorable to a greater variety of chironomids. However, a lack of statistical significance may support assertions that mitigation sites are successfully replacing natural wetlands. Implementation of CPET-based community structure analyses requires intensive labor and expertise and is not practical for regulatory purposes, but can provide robust data for effective and detailed site analysis.
机译:南佛罗里达州的湿地资源受三个冗余司法管辖区级别的监管:许多独立司法管辖区制定的地方或市政法规,直接从《佛罗里达州法规》衍生的州法规以及主要根据《清洁水法》颁布的联邦法规。尽管影响了数十年的协调工作和迅速发展的科学研究基础,但三级政府均可对影响受监管的湿地资源的项目拥有管辖权,但政策和标准仍然不一致,并继续困扰监管机构。尽管在发达地区建造的湿地缓解区通常是孤立的,并且无论湿地大小如何,通常都采用类似的设计,但在评估其感知的生态价值时,湿地缓解区的大小是首要考虑因素。在所有健康的淡水水中分布最丰富,种类最多的动物分类群,通常被认为是可靠而有效的生态指标。我对一组自然湿地和人工湿地之间的手足动物群落进行了初步比较,并评估了湿地大小对昆虫科天虫科的群落结构的影响。通过使用Chironomid Pupal Exuviae技术(CPET),比较了不同地点群中总共7个自然和人工缓解湿地的Chironomid exuviae的收集情况,并且还与每个研究地点的记录环境状况相关联。由冠脉旁白蚁(Parakiefferiella coronata)撰写,占所有收集的exuviae的近36%。来自缓解湿地的物种集合与来自所有地点的聚集物种集合表现出强烈的相似性。从人工场所收集的丰富的虾青虫比从自然场所收集的丰富,并且从自然场所收集的物种集合与从人工场所收集的物种集合不同。在较大和较小的湿地之间均未发现群落结构的统计学显着差异。天然位点和缓解位点之间的环境位点条件通常在电导率和pH值上变化最大。在大小不同的湿地的环境条件或手足动物群落结构中未发现明显的梯度。观测到TP浓度存在较小的季节性梯度,S6位点是该研究中最富集的位点,而S1位点在整个项目过程中显示出高电导率。相对静态的地形,更一致的底物组成以及自然位点中存在的多样性较差的水生植物群落,这些植物通常达到了更高的稳态。但是,统计检验通常支持原假设。当按湿地来源(人工与自然)或大小分组时,在基于收集的拟南芥群落的站点之间未检测到统计学显着差异。人工湿地系统可能需要几代甚至几百年才能充分模仿其自然对应物。缓解设计的复杂性似乎确实提供了有利于更多种手足动物的微生境的多样性。但是,缺乏统计意义可能会支持这样的说法,即减灾地点正在成功取代自然湿地。基于CPET的社区结构分析的实施需要大量的人力和专业知识,对于监管目的而言并不实际,但可以为有效而详细的站点分析提供可靠的数据。

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    St. George Ryan;

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