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首页> 外文期刊>Journal of Shellfish Research >Effects of the fishery on the Northern Quahog (=hard clam, Mercenaria mercenaria L.) population in Great South Bay, New York: a modeling study.
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Effects of the fishery on the Northern Quahog (=hard clam, Mercenaria mercenaria L.) population in Great South Bay, New York: a modeling study.

机译:渔业对纽约大南湾北部Quahog(硬蛤,Mercenaria mercenaria L.)种群的影响:一项模型研究。

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摘要

A numerical bioenergetics simulation model based on the physiological processes affecting individual clams across a range of phenotypes describing a cohort has been developed and applied to the conditions in Great South Bay, New York. The clam population is relatively sensitive to food and to a lesser extent to temperature within this system. The timing of temperature and food in the spring, and more importantly in the fall, can increase population sensitivity beyond the effects of one factor operating alone. The effects of fishing on the stocks in proportion to the size structure present, and as directed fisheries on various size classes (littleneck, cherrystone, chowder) was simulated. Recruitment overfishing was responsible for the stock decline in the 1970s and 1980s, but the continued decline into the late 1990s and 2000s cannot be attributed to fishing alone. Recruit-per-adult declined after the mid 1990s. Modeled stock recovery times under constant environmental conditions are on order of 10-15 or more years depending on the exploitation rate. Under base conditions a proportional fishery that removes approximately 25% of the stock, or a littleneck fishery that removes approximately 37.5% of that size class annually would provide the best economic returns under constant average environmental conditions. Slightly less harvest would be desirable to avoid overfishing in years of less than optimal environmental conditions.
机译:已经开发了一种基于生物过程的数值生物能模拟模型,该生理过程会影响描述同一人群的一系列表型中的单个蛤类,并将其应用于纽约大南湾的条件。蛤种群对食物相对敏感,并且在该系统中对温度相对较小。春季,更重要的是秋季的温度和食物的时间安排,可以增加人口敏感性,而不仅仅是一个因素单独起作用。模拟了渔业对种群的影响,与种群的大小结构成正比,并模拟了定向渔业对各种规模类别(小颈,樱桃石,杂烩)的影响。 1970年代和1980年代,捕捞过量是造成种群减少的原因,但到1990年代末和2000年代后期的持续下降,不能仅归因于捕捞。 1990年代中期以后,成人招募人数下降。在恒定的环境条件下,模型化的库存回收时间大约为10-15年或更多,具体取决于开采率。在基本条件下,按比例减少捕捞量约占种群总量25%的小规模渔业,或每年减少约37.5%的同等规模鱼类捕捞量,在恒定的平均环境条件下可提供最佳的经济回报。为了避免在少于最佳环境条件的年份中过度捕捞,希望少收获一些。

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