首页> 外文会议>Environmental Problems in Coastal Regions VI: including Oil Spill Studies; WIT Transactions on Ecology and the Environment; vol.88 >Effect of wrack accumulation on salt marsh vegetation, Baruch Institute, Georgetown County, South Carolina
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Effect of wrack accumulation on salt marsh vegetation, Baruch Institute, Georgetown County, South Carolina

机译:残骸堆积对盐沼植被的影响,南卡罗来纳州乔治敦县巴鲁克研究所

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In March 2004, four arrays in different types of salt marsh vegetation were covered with 15-20 cm of wrack secured in place, in an attempt to duplicate the natural deposition of wrack on the marsh by tides and storms, and to quantify and extend anecdotal observations and the results of previous studies. A control plot in each array was left uncovered; another plot was covered with only 2-3 cm. The wrack was removed from one plot in each array at one, two, four and seven month intervals. One month of wrack coverage appeared to have little effect on either density or standing crop, recorded seven months after initial covering, of the principal marsh species. Above ground parts of these species, with the exception of Spartina patens and Borrichia frutescens, appeared to be killed or extremely inhibited after two months of wrack coverage or longer. Wrack 2-3 cm thick (never removed) appeared to have inhibited the marsh species after seven months, but not as much as the 15-20 cm wrack mat. These results are fairly consistent with those of an earlier study at Jamaica Bay Wildlife Refuge, New York City, that focused on responses to wrack of Spartina altemiflora only, except that two months' coverage seemed necessary to kill back most of the S altemiflora in that study. However, in another study at Jamaica Bay encompassing several species and vegetation types, most species declined gradually with increased length of wrack coverage over a six-month period. Future studies will focus on recovery of the vegetation once the wrack has been removed, and on chemical changes in the soil caused by the decaying wrack, which may in turn affect the future course of vegetation development.
机译:2004年3月,盐沼植被类型不同的四个阵列被固定在适当位置的15-20厘米沉船覆盖,试图通过潮汐和风暴复制沉船在沼泽上的自然沉积,并量化和扩展轶事观察和先前研究的结果。保留每个阵列中的对照图。另一个地块仅覆盖2-3厘米。分别在一个,两个,四个和七个月的时间间隔内,从每个阵列的一个小区中清除残骸。初次覆盖后七个月,记录到一个月的沉船覆盖对密度或立木作物几乎没有影响,而主要沼泽物种。这些物种的地上部分,除草柏和博氏疏螺旋体外,在两个月或更长时间的残骸覆盖后似乎被杀死或被极度抑制。 2-3厘米厚的残骸(从未移除)似乎在七个月后抑制了沼泽物种,但不及15-20厘米残骸垫。这些结果与纽约市牙买加湾野生动物保护区较早的一项研究相当一致,该研究仅关注对米色斯巴迪菌的残骸的反应,只是似乎需要两个月的时间才能杀死其中的大部分米色斯藻。研究。但是,在牙买加湾的另一项研究中,涵盖了几种物种和植被类型,随着六个月内残骸覆盖时间的延长,大多数物种逐渐减少。一旦残骸被清除,未来的研究将集中在植被的恢复上,以及残骸的腐烂引起的土壤化学变化上,这反过来可能会影响植被的未来发展。

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