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Oyster reef restoration: substrate suitability may depend on specific restoration goals

机译:牡蛎礁修复:底物的适应性可能取决于特定的修复目标

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A limited supply of oyster shell for restoration practices has prompted investigations of alternative substrates used in construction of artificial oyster reefs. The success of oyster reef restoration projects is increasingly focused not only on oyster densities, but also on habitat provisioning for associated fauna. A subtidal oyster reef complex (0.24km(2)) was restored in the Mission-Aransas Estuary, Texas, U.S.A., in July 2013 using replicated mounds of concrete, limestone, river rock, and oyster shell substrates. Oyster and reef-associated fauna characteristics were quantified quarterly for 15 months, using sampling trays that were deployed 3 months after construction. The highest densities of oyster spat occurred 9 months after tray deployment (July 2014, 1,264/m(2)), whereas juvenile oyster densities increased throughout the study period to 283/m(2). Concrete (1,022/m(2)) and limestone (939/m(2)) supported the highest number of oysters over all dates. Oyster shell (1,533/m(2)) and concrete (1,047/m(2)) substrates supported the highest densities of associated motile fauna. Faunal diversity (Hill's N1) did not vary by substrate material, but did show seasonal variation. A simple benefit-cost ratio was used to indicate the localized monetary value for each of the substrates. Oyster shell and concrete substrates returned the highest benefit-cost ratio for motile fauna, while concrete yielded the highest benefit-cost ratio for oyster abundance. Incorporating benefit-cost ratios in restoration planning will allow practitioners to better integrate substrate-specific ecological values with economic considerations and project goals to maximize return on restoration investments.
机译:用于恢复实践的牡蛎壳供应有限,促使人们研究了用于人工牡蛎礁建设的替代基质。牡蛎礁修复项目的成功越来越不仅集中在牡蛎密度上,而且也集中在为相关动物群提供栖息地方面。 2013年7月,在美国得克萨斯州的米申-阿兰萨斯河口恢复了潮下带牡蛎礁综合体(0.24km(2)),使用了成堆的混凝土,石灰石,河岩石和牡蛎壳基质。牡蛎和与珊瑚礁相关的动物区系特征在建造后3个月内使用采样盘每15个月进行一次定量。牡蛎的最高密度发生在托盘部署后9个月(2014年7月,1,264 / m(2)),而整个研究期间幼牡蛎密度增加到283 / m(2)。在所有日期中,混凝土(1,022 / m(2))和石灰石(939 / m(2))支持最多的牡蛎数量。牡蛎壳(1,533 / m(2))和混凝土(1,047 / m(2))基材支持相关活动动物的最高密度。动物的多样性(Hill's N1)没有随基质材料而变化,但确实表现出季节性变化。一个简单的成本效益比用来表示每个基材的局部货币价值。牡蛎壳和混凝土基质对活动动植物的收益成本比最高,而混凝土对牡蛎丰富度的收益成本比最高。在恢复计划中纳入利益成本比将使从业人员可以更好地将特定于底物的生态价值与经济因素和项目目标结合起来,以最大程度地提高恢复投资的回报。

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