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自 1900 年以来人为活动对潮汐溪沉积物的影响。

Anthropogenic impacts on tidal creek sedimentation since 1900.

机构信息

Institute of Marine Sciences, University of North Carolina at Chapel Hill, Morehead City, North Carolina, United States of America.

National Oceanic and Atmospheric Administration, National Centers for Coastal Ocean Science, Beaufort, North Carolina, United States of America.

出版信息

PLoS One. 2023 Jan 18;18(1):e0280490. doi: 10.1371/journal.pone.0280490. eCollection 2023.

DOI:10.1371/journal.pone.0280490
PMID:36652445
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC9847910/
Abstract

Land cover and use around the margins of estuaries has shifted since 1950 at many sites in North America due to development pressures from higher population densities. Small coastal watersheds are ubiquitous along estuarine margins and most of this coastal land-cover change occurred in these tidal creek watersheds. A change in land cover could modify the contribution of sediments from tidal creek watersheds to downstream areas and affect estuarine habitats that rely on sediments to persist or are adversely impacted by sediment loading. The resilience of wetlands to accelerating relative sea-level rise depends, in part, on the supply of lithogenic sediment to support accretion and maintain elevation; however, subtidal habitats such as oyster reefs and seagrass beds are stressed under conditions of high turbidity and sedimentation. Here we compare sediment accumulation rates before and after 1950 using 210Pb in 12 tidal creeks across two distinct regions in North Carolina, one region of low relief tidal-creek watersheds where land cover change since 1959 was dominated by fluctuations in forest, silviculture, and agriculture, and another region of relatively high relief tidal-creek watersheds where land-use change was dominated by increasing suburban development. At eight of the creeks, mass accumulation rates (g cm-2 y-1) measured at the outlet of the creeks increased contemporaneously with the largest shift in land cover, within the resolution of the land-cover data set (~5-years). All but two creek sites experienced a doubling or more in sediment accumulation rates (cm yr-1) after 1950 and most sites experienced sediment accumulation rates that exceeded the rate of local relative sea-level rise, suggesting that there is an excess of sediment being delivered to these tidal creeks and that they may slowly be infilling. After 1950, land cover within one creek watershed changed little, as did mass accumulation rates at the coring location, and another creek coring site did not record an increase in mass accumulation rates at the creek outlet despite a massive increase in development in the watershed that included the construction of retention ponds. These abundant tidal-creek watersheds have little relief, area, and flow, but they are impacted by changes in land cover more, in terms of percent area, than their larger riverine counterparts, and down-stream areas are highly connected to their associated watersheds. This work expands the scientific understanding of connectivity between lower coastal plain watersheds and estuaries and provides important information for coastal zone managers seeking to balance development pressures and environmental protections.

摘要

自 1950 年以来,由于人口密度的增加带来的发展压力,北美的许多河口边缘地区的土地覆盖和利用发生了变化。小型沿海流域在河口边缘普遍存在,而这种沿海土地覆盖的变化主要发生在这些潮汐溪流域。土地覆盖的变化可能会改变潮汐溪流域沉积物对下游地区的贡献,并影响依赖沉积物生存或受到沉积物负荷不利影响的河口栖息地。湿地对加速相对海平面上升的恢复能力部分取决于为支持淤积和维持海拔而提供的陆源沉积物的供应;然而,在高浑浊度和沉积物沉降条件下,潮下带生境,如牡蛎礁和海草床,会受到压力。在这里,我们使用 210Pb 在北卡罗来纳州的两个不同地区的 12 条潮汐溪中比较了 1950 年前后的沉积物积累速率,一个地区是低起伏潮汐溪流域,该地区自 1959 年以来的土地覆盖变化主要是森林、造林和农业的波动,另一个地区是相对高起伏的潮汐溪流域,该地区的土地利用变化主要是由不断增加的郊区开发所主导。在其中的 8 条溪流中,在溪流出口处测量的质量积累速率(g cm-2 y-1)与土地覆盖数据集中的最大变化(~5 年)同时增加。除了两个溪流外,所有溪流的沉积物积累速率(cm yr-1)在 1950 年后都增加了一倍或更多,而且大多数溪流的沉积物积累速率超过了当地相对海平面上升的速率,这表明有大量的沉积物被输送到这些潮汐溪,这些潮汐溪可能正在慢慢淤塞。1950 年后,一个流域内的土地覆盖变化很小,而在取芯地点的质量积累率也没有变化,另一个溪流的取芯地点在流域内的大量开发包括建造蓄水池的情况下,尽管在溪流出口处的质量积累率没有增加。尽管这些丰富的潮汐溪流域的地势起伏小、面积小、流量小,但与更大的河流流域相比,它们受到土地覆盖变化的影响更大,在流域面积百分比方面受到的影响更大,而下游地区与它们相关的流域高度相连。这项工作扩展了对下沿海平原流域和河口之间连通性的科学认识,并为寻求平衡发展压力和环境保护的沿海地区管理者提供了重要信息。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7ca1/9847910/26bf983c034c/pone.0280490.g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7ca1/9847910/697229d45d75/pone.0280490.g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7ca1/9847910/43acd2a45e96/pone.0280490.g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7ca1/9847910/90953d82a449/pone.0280490.g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7ca1/9847910/fad9d001003c/pone.0280490.g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7ca1/9847910/d23bea309dbc/pone.0280490.g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7ca1/9847910/f7b302d8a8f6/pone.0280490.g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7ca1/9847910/26bf983c034c/pone.0280490.g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7ca1/9847910/697229d45d75/pone.0280490.g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7ca1/9847910/43acd2a45e96/pone.0280490.g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7ca1/9847910/90953d82a449/pone.0280490.g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7ca1/9847910/fad9d001003c/pone.0280490.g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7ca1/9847910/d23bea309dbc/pone.0280490.g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7ca1/9847910/f7b302d8a8f6/pone.0280490.g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7ca1/9847910/26bf983c034c/pone.0280490.g007.jpg

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