首页> 外文学位 >The effects of land-use change on water quality and speleogenesis in Ozark cave systems: A paired cave study of Civil War and Copperhead Caves, northwestern Arkansas.
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The effects of land-use change on water quality and speleogenesis in Ozark cave systems: A paired cave study of Civil War and Copperhead Caves, northwestern Arkansas.

机译:Ozark洞穴系统中土地利用变化对水质和成虫的影响:阿肯色州西北部内战和Copperhead洞穴的配对洞穴研究。

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摘要

Civil War Cave is located in a rapidly developing and highly impacted area of Benton County, Arkansas. This area is covered by shallow mantled karst. In this setting, caves typically are well connected hydraulically to the surface and show a rapid response to surface water changes. Land use may affect the water quality and speleogenesis of a cave. The delicate ecosystem of caves makes them an excellent indicator of changes in ground water conditions. Civil War Cave is home to the threatened Ozark cavefish (Amblyopsis rosae ), making any impact on Civil War Cave more significant. This study characterizes the effects of land use change on water quality and speleogenesis using a paired cave study. In this paired cave study, two caves were evaluated: Civil War Cave, located in a rapidly developing and highly-impacted area in Benton County, Arkansas and Copperhead Cave, which lies within a nearly pristine forested watershed of the Buffalo National River in Newton County, Arkansas. The geological characteristics of Civil War and Copperhead caves are similar, with both caves contained in the Boone Formation. The hydrology of the two caves is similar, with both caves being recharged through the Springfield Plateau aquifer. In both caves, the actual recharge area is larger than the apparent topographic recharge area. The topographic recharge areas are 0.18 square kilometers (km2) for Civil War Cave and 0.35 km 2 for Copperhead Cave. Using normalized base flow approximation, the recharge area was determined to be approximately 7.5 km2 for Civil War Cave, with a possible range of 4.7-10 km2. The normalized base flow indicates a recharge area of 1.75-3.7 km2 for Copperhead Cave. In both cases, the regional flow is modified and/or enhanced by fractures and karst features and groundwater flow-paths cross topographic divides. Sedimentation was observed to be a problem in Civil War Cave beginning in 2005. The sedimentation is likely a result of surface excavation in the immediate recharge area and has subsided since this excavation ended. Copperhead Cave exhibits only minimal sedimentation. Since Civil War Cave is developed in the epikarst, the cave is more vulnerable to sedimentation. Examination of the water quality corroborates the idea that both caves are recharged through the Springfield Plateau Aquifer. Using nitrate as nitrogen (NO3-) to evaluate human impact, Civil War Cave was determined to be impacted, with NO3 - values averaging 6.33 mg/L in the upper level and 6.49 mg/L in the lower level. Copperhead Cave is not impacted, with less than 0.2 mg/L N0 3-. Civil War Cave is developed entirely in the epikarst and as a result contains speleothems formed by a stream flowing on the cave floor. No active speleogenesis was observed in the cave, erosion of speleothems is common, and large amounts of sediment are entering the cave. Copperhead Cave was developed in a deeper karst setting with drip-waters being abundant and, therefore, has speleothems on the ceilings and walls of the cave. Active speleogenesis is observed in Copperhead Cave. At Civil War Cave, development has increased the hydrologic threat, the threat of nutrient stress, and the threat of chemical pollution. In addition, increased sediment related to development presents a threat to the cave ecosystem. The greatest threat in Copperhead Cave is human interaction by visitation. Despite this, the biodiversity in both Civil War and Copperhead Caves are great. Several species that were observed historically were also observed during the present study. Land-use around Civil War Cave has impacted the hydrology, sedimentation, and water quality of the cave. The only impact observed in Copperhead Cave was the result of direct human interference within the cave.
机译:内战洞穴位于阿肯色州本顿县快速发展且受灾严重的地区。该区域被浅浅的喀斯特岩溶所覆盖。在这种情况下,洞穴通常在水力上很好地连接到地表,并显示出对地表水变化的快速响应。土地使用可能会影响水质和洞穴的形成。精致的洞穴生态系统使其成为地下水状况变化的极佳指标。内战洞穴是受到威胁的奥扎克洞穴鱼(Amblyopsis rosae)的所在地,对内战洞穴的任何影响都更加显着。这项研究使用配对洞穴研究来表征土地利用变化对水质和成虫的影响。在这项成对的洞穴研究中,评估了两个洞穴:内战洞穴,位于阿肯色州本顿县快速发展且受到高度影响的地区;铜穴洞穴则位于牛顿县布法罗国家河流域近原始森林流域内,阿肯色州。内战和科波海德洞穴的地质特征相似,两个洞穴都包含在布恩岩层中。两个洞穴的水文状况相似,两个洞穴都通过斯普林菲尔德高原含水层进行补给。在两个洞穴中,实际补给面积都大于表观地形补给面积。内战洞穴的地形补给面积为0.18平方公里(km2),科珀黑德洞穴的补给面积为0.35 km 2。使用归一化基本流量近似值,确定内战洞穴的补给面积约为7.5 km2,可能的范围为4.7-10 km2。归一化的基本流量指示铜头洞的补给面积为1.75-3.7 km2。在这两种情况下,裂缝和喀斯特地貌以及地下水的流动路径都跨越了地形鸿沟,从而改变和/或增强了区域水流。从2005年开始,人们就在南北战争洞穴中发现了泥沙淤积的问题。泥沙淤积很可能是由于直接补给区的地表开挖造成的,并且自开挖结束以来一直在减少。铜头洞仅表现出最小的沉积。由于内战岩洞是在岩溶岩中发育的,因此该岩洞更容易沉积。对水质的检查证实了两个洞穴都通过斯普林菲尔德高原含水层进行补给的想法。使用硝酸盐作为氮(NO3-)评估对人类的影响,确定内战洞穴受到了影响,NO3-的平均值在上层为6.33 mg / L,下层为6.49 mg / L。小于0.2 mg / L N0 3-不会影响Copperhead Cave。内战洞穴完全在表层岩溶中发育,因此包含由在洞穴底部流动的溪流形成的蛇鞘。在该洞穴中未观察到活跃的成虫作用,常见的是鞘脂的侵蚀,并且有大量沉积物进入该洞穴。 Copperhead洞穴是在更深的喀斯特环境中开发的,滴水很丰富,因此,在洞穴的天花板和墙壁上都有蛇鞘。在铜斑蛇洞中观察到活跃的发生。在南北战争洞穴,发展增加了水文威胁,营养胁迫的威胁和化学污染的威胁。此外,与发展有关的沉积物增加对洞穴生态系统构成了威胁。铜海洞的最大威胁是人与人之间的互动。尽管如此,南北战争和科波海德洞穴的生物多样性都很棒。在本研究中还观察到历史上观察到的几种物种。南北战争洞穴周围的土地利用已经影响了该洞穴的水文,沉积和水质。在科波黑德洞穴中观察到的唯一影响是洞穴内人为直接干扰的结果。

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