诱饵类型和同种吸引对小菱鲆副渔获的影响

A. J. Carpenter, M. Thomas, K. Cecala
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引用次数: 1

摘要

介绍Malaclemys terrapin (Diamondback terrapin;(以下简称龟)是一种独特的河口龟,生活在美国大西洋和墨西哥湾沿岸,受到与沿海开发有关的活动的威胁,如商业和娱乐捕蟹,栖息地丧失和车辆死亡(Ernst和Lovich, 2009)。小菱形龟是河口食物网的重要组成部分,因为它们通过食用放牧的长春花螺对生物量生产和部分维持沼泽草种群做出了贡献(Silliman和Bertness, 2002)。由于生物多样性和沼泽稳定性的丧失,目前龟类数量的大范围下降可能会导致沿海盐沼生态系统的崩溃(Gibbons等人,2001;Dorcas et al., 2007;引用,2013;世界自然保护联盟,2019)。商业和娱乐蟹笼的附带捕获和随后的溺水似乎是种群下降的一个主要因素(Bishop, 1983;Roosenburg et al., 1997;木,1997;rosenburg and Green, 2000;Tucker et al., 2001;Grosse et al., 2009;2011;Rook et al., 2010;埋葬,2011;Hart and Crowder, 2011;哈登和威利亚德,2012)。由于明显的两性二态性导致雌性龟体型较大,因此雄性和幼龟在盆中的死亡率很高,造成老年雌性龟的偏倚种群(Lovich和Gibbons, 1990;Dorcas et al., 2007)。水龟种群的稳定性在很大程度上取决于繁殖成虫的存活和幼龟的招募,或进入繁殖种群。因此,蟹笼造成的死亡率可以通过改变年龄和性别比例来摧毁种群(Dorcas et al., 2007;Grosse et al., 2009;Crawford et al., 2014a)。减少雄性和年轻雌性进入繁殖种群可能会对小菱纹龟种群的稳定性产生不利影响,正如在密切相关的物种中所记录的那样(Congdon等人,1993;Heppell, 1998;Gibbons et al., 2001;Dorcas et al., 2007;Crawford et al., 2014)。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Effects of Bait Type and Conspecific Attraction in Diamondback Terrapin (Malaclemys terrapin) Bycatch
Publication date: January 2020 INTRODUCTION Malaclemys terrapin (Diamondback terrapin; hereafter referred to as terrapins) are a uniquely estuarine turtle on the Atlantic and Gulf coasts of the United States threatened by activities associated with coastal development, such as commercial and recreational crabbing, habitat loss, and vehicle mortality (Ernst and Lovich, 2009). Diamondback terrapins are an important component in estuarine food webs because of their contribution to biomass production and partial maintenance of marsh grass populations through consumption of grazing periwinkle snails (Silliman and Bertness, 2002). The current range-wide declines in terrapin populations could contribute to collapses in coastal salt marsh ecosystems through the loss of biodiversity and marsh stability (Gibbons et al., 2001; Dorcas et al., 2007; CITES, 2013; IUCN, 2019). Bycatch and subsequent drowning in both commercial and recreational crab pots appears to be a major factor in population decline (Bishop, 1983; Roosenburg et al., 1997; Wood, 1997; Roosenburg and Green, 2000; Tucker et al., 2001; Grosse et al., 2009; 2011; Rook et al., 2010; Bury, 2011; Hart and Crowder, 2011; Harden and Williard, 2012). Due to pronounced sexual dimorphism which results in significantly larger females, the mortality rates of males and juveniles in pots are high, creating biased populations of older female terrapins (Lovich and Gibbons, 1990; Dorcas et al., 2007). Terrapin population stability is highly dependent on the survival of breeding adults and juvenile recruitment, or entry into the breeding population. Therefore, mortality resulting from crab pots can devastate populations by altering age and sex ratios (Dorcas et al., 2007; Grosse et al., 2009; Crawford et al., 2014a). Reduced recruitment of males and young females into the breeding population will likely have detrimental effects on the stability of Diamondback terrapin populations, as has been documented in closely-related species (Congdon et al., 1993; Heppell, 1998; Gibbons et al., 2001; Dorcas et al., 2007; Crawford et al., 2014b).
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