加纳上西部地区 Gbele 资源保护区状况的时间分析

IF 2.7 3区 农林科学 Q2 ECOLOGY
Raymond Aabeyir, K. Peprah, Amos Amponsah
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引用次数: 0

摘要

本文评估了 1990 年至 2020 年格贝勒资源保护区森林覆盖率的变化情况。1990 年、2000 年、2010 年和 2020 年的陆地卫星图像来自美国地质服务网站。1990 年、2000 年、2010 年和 2020 年的陆地卫星图像来自美国地质局网站,并在基于网络的云计算平台 "用于土地监测的地球观测数据访问、处理和分析系统"(SEPAL)中进行了处理和分类。使用从挪威国际气候与森林计划(NICFI)3-5 米空间分辨率和近乎每日时间分辨率的行星卫星图像中获得的 50 个地面实况点,对图像的准确性进行了评估。分析结果显示,森林总面积为 55273.2 公顷。1990 年,74.9% 的保护区为疏林,24.6% 为灌木/草地。2000 年,疏林面积下降到 65.8%,2010 年进一步下降到 62.4%,而灌木/草覆盖面积在 2010 年增加到 35.7%。截至 2020 年,森林覆盖率上升至 73.6%,而灌木/草覆盖率则下降至 25.8%。这些变化的部分原因可能是本世纪初边缘地区广泛的木炭生产和红木采伐。2010 年后禁止采伐和出口花梨木可以部分解释 2010 年至 2020 年期间疏林覆盖率的急剧增加。从 1990 年到 2020 年保护区范围的变化可以看出,保护区很容易受到过度开发的影响,但如果刻意保护,保护区也能恢复活力。建议边缘区议会和市议会加强禁止采伐保护区内的红木和树木用于生产木炭的禁令。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Temporal analysis of the state of the Gbele Resource Reserve in the Upper West Region, Ghana
This paper assessed the changes in the forest cover of the Gbele Resource Reserve from 1990 to 2020. This provides a basis for strengthening management decisions to protect the resources in the Gbele Resource Reserve effectively.Landsat images for 1990, 2000, 2010 and 2020 were obtained from the United States Geological Service site. They were processed and classified in the System for Earth Observation Data Access, Processing, & Analysis for Land Monitoring (SEPAL), a web-based cloud computing platform. The accuracy of the images was assessed using 50 ground-truth points obtained from the 3-5 meter spatial and near-daily temporal resolution planet satellite images from Norway’s International Climate and Forest Initiative (NICFI). Post classification change detection was used to analyse the changes in land cover from 1990 to 2000, 2000 to 2010 and from 2010 to 2020.The analysis revealed that the total forest area was 55273.2 ha. In 1990, 74.9 % of the reserve was open forest and 24.6 % was shrubs/grass. The open forest declined to 65.8 % in 2000 and further to 62.4 % in 2010 while the shrubs/grass cover increased to 35.7 in 2010. As of 2020, the forest increased to 73.6 % while the shrub/grass cover declined to 25.8 %.These changes could be attributed partly to widespread charcoal production in the fringe districts and rose wood harvesting in the early 2000s. charcoal production and rosewood logging have been livelihood sources for fringe communities. The ban on the harvest and exportation of rosewood after 2010 could partly explain the sharp increase in the open forest cover from 2010 to 2020. The changes in the extent of the reserve from 1990 to 2020 revealed that the reserve can vulnerable to excessive exploitation and can also be resilient if deliberate efforts are made to protect it. It is recommended that the fringe district and municipal Assemblies should strengthen the enforcement of the ban on the logging of the rosewood and trees in the reserve for the production of charcoal.
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来源期刊
CiteScore
4.50
自引率
6.20%
发文量
256
审稿时长
12 weeks
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