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自 1974 年以来,长江三角洲地区的潮滩迅速消失。

Rapid Loss of Tidal Flats in the Yangtze River Delta since 1974.

机构信息

School of Geography, Geomatics and Planning, Jiangsu Normal University, Xuzhou 221116, China.

State Key Laboratory of Remote Sensing Science, Institute of Remote Sensing and Digital Earth, Chinese Academy of Sciences, Beijing 100101, China.

出版信息

Int J Environ Res Public Health. 2020 Mar 3;17(5):1636. doi: 10.3390/ijerph17051636.

DOI:10.3390/ijerph17051636
PMID:32138286
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC7084696/
Abstract

As the home to national nature reserves and a Ramsar wetland, the tidal flats of the Yangtze River Delta are of great significance for ecological security, at both the local and global scales. However, a comprehensive understanding of the spatiotemporal conditions of the tidal flats in the Yangtze River Delta remains lacking. Here, we propose using remote sensing to obtain a detailed spatiotemporal profile of the tidal flats, using all available Landsat images from 1974 to 2018 with the help of the Google Earth Engine cloud platform. In addition, reclamation data were manually extracted from time series Landsat images for the same period. We found that approximately 40.0% (34.9-43.1%) of the tidal flats in the study area have been lost since 1980, the year in which the tidal flat area was maximal. The change in the tidal flat areas was consistent with the change in the riverine sediment supply. We also found that the cumulative reclamation areas totaled 816.6 km and 431.9 km in the Yangtze estuary zone and along the Jiangsu coast, respectively, between 1974 and 2018. Because of reclamation, some areas (e.g., the Hengsha eastern shoal and Pudong bank), which used to be quite rich, have lost most of their tidal flats. Currently, almost 70% of the remaining tidal flats are located in the shrinking branch (North Branch) and the two National Nature Reserves (Chongming Dongtan and Jiuduansha) in the Yangtze estuary zone. Consequently, the large-scale loss of tidal flats observed was primarily associated with reduced sediment supply and land reclamation at the time scale of the study. Because increasing demand for land and rising sea levels are expected in the future, immediate steps should be taken to prevent the further deterioration of this valuable ecosystem.

摘要

作为国家自然保护区和拉姆萨尔湿地的所在地,长江三角洲的潮滩对于当地和全球的生态安全都具有重要意义。然而,对于长江三角洲潮滩的时空条件,我们还缺乏全面的了解。在这里,我们提出利用遥感技术获取潮滩的详细时空概况,借助 Google Earth Engine 云平台,使用从 1974 年到 2018 年所有可用的 Landsat 图像。此外,我们还从同期的时间序列 Landsat 图像中手动提取了填海数据。我们发现,自 1980 年以来,该研究区域约有 40.0%(34.9-43.1%)的潮滩已经消失,而 1980 年正是潮滩面积最大的一年。潮滩面积的变化与河流泥沙供应的变化一致。我们还发现,在 1974 年至 2018 年间,长江口地区和江苏沿海地区的累计填海面积分别为 816.6 公里和 431.9 公里。由于填海,一些曾经非常丰富的地区(例如横沙东部浅滩和浦东岸线)已经失去了大部分的潮滩。目前,剩余的潮滩中近 70%位于长江口的萎缩分支(北支)和两个国家级自然保护区(崇明东滩和九段沙)。因此,在所研究的时间尺度上,观察到的潮滩大规模减少主要与泥沙供应减少和土地开垦有关。由于未来预计对土地的需求会增加,海平面会上升,因此应该立即采取措施防止这一宝贵生态系统的进一步恶化。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/9602ee2290be/ijerph-17-01636-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/bcf94109c2b8/ijerph-17-01636-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/f87ceb7913b4/ijerph-17-01636-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/1563d5932532/ijerph-17-01636-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/cd190bbbecb1/ijerph-17-01636-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/3ee44ec8c36f/ijerph-17-01636-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/8dc53dc5c4c5/ijerph-17-01636-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/8a06a8c182e6/ijerph-17-01636-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/488c82ec3802/ijerph-17-01636-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/37b829b9c848/ijerph-17-01636-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/9602ee2290be/ijerph-17-01636-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/bcf94109c2b8/ijerph-17-01636-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/f87ceb7913b4/ijerph-17-01636-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/1563d5932532/ijerph-17-01636-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/cd190bbbecb1/ijerph-17-01636-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/3ee44ec8c36f/ijerph-17-01636-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/8dc53dc5c4c5/ijerph-17-01636-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/8a06a8c182e6/ijerph-17-01636-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/488c82ec3802/ijerph-17-01636-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/37b829b9c848/ijerph-17-01636-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/94c0/7084696/9602ee2290be/ijerph-17-01636-g010.jpg

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