死亡谷国家公园魔鬼洞的浅层热环境

Mark B. Hausner, Kevin P. Wilson, D. Bailey Gaines, Francisco Suárez, Scott W. Tyler
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引用次数: 18

摘要

魔鬼洞是死亡谷地区地下水流动系统下碳酸盐含水层的一个裂缝,是魔鬼洞鳉(Cyprinodon diabolis)唯一现存种群的家园。自1995年以来,C. diabolis的数量出现了无法解释的下降,人们提出了一些假说来解释这一现象。在这里,我们研究了魔鬼洞的热状态及其对小鱼种群的影响。本文建立了魔鬼洞浅陆架热对流的计算流体动力学(CFD)模型,该陆架为魔鬼线虫产卵和觅食提供了重要的栖息地。在魔鬼洞收集的气象数据的驱动下,该模型使用2010年夏季记录的温度数据进行校准,并与1999年至2001年在浅大陆架观测到的温度进行验证。浅海陆架的水温经历了季节和昼夜变化,模式结果反映了这些变化。敏感性分析表明,水温对环境气温的相对较小变化(约为1°C)有响应,对当地气候数据的回顾表明,在过去30年中,莫哈韦沙漠的年平均气温增加了2°C。CFD模拟和当地气候数据表明,气候变化可能是1995年开始观测到的C. diabolis种群下降的部分原因。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

The shallow thermal regime of Devils Hole, Death Valley National Park

The shallow thermal regime of Devils Hole, Death Valley National Park

Devils Hole, a fracture in the carbonate aquifer underlying the Death Valley Regional Groundwater Flow system, is home to the only extant population of Devils Hole pupfish (Cyprinodon diabolis). Since 1995, the population of C. diabolis has shown an unexplained decline, and a number of hypotheses have been advanced to explain this. Here, we examine the thermal regime of Devils Hole and its influence on the pupfish population. We present a computational fluid dynamic (CFD) model of thermal convection on the shallow shelf of Devils Hole, which provides critical habitat for C. diabolis to spawn and forage for food. Driven by meteorological data collected at Devils Hole, the model is calibrated with temperature data recorded in the summer of 2010 and validated against temperatures observed on the shallow shelf between 1999 and 2001.The shallow shelf experiences both seasonal and diel variations in water temperature, and the model results reflect these changes. A sensitivity analysis shows that the water temperatures respond to relatively small changes in the ambient air temperature (on the order of 1 °C), and a review of local climate data shows that average annual air temperatures in the Mojave Desert have increased by up to 2 °C over the past 30 years. The CFD simulations and local climate data show that climate change may be partially responsible for the observed decline in the population of C. diabolis that began in 1995.

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