Resistance and priority analysis of landscape forest fields, lakes, and grass restoration in Dabaoshan mining basin
Following the concept of "source prevention, flow control, and sink control", taking Dabaoshan mining area in nanling, north guangdong as the source of risk and the basin as a research area, the main resistance factors of the area were analyzed and studied. This paper utilized the minimal...
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Veröffentlicht in: | Sheng tai xue bao 2019, Vol.39 (23), p.8920 |
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description | Following the concept of "source prevention, flow control, and sink control", taking Dabaoshan mining area in nanling, north guangdong as the source of risk and the basin as a research area, the main resistance factors of the area were analyzed and studied. This paper utilized the minimal cumulative resistance(MCR) model to establish the regional ecological resistance surface, analyzed ecological restoration priorities using Jenks natural breakpoint method, and proposes key points and countermeasures for regionalized governance. The results show that the comprehensive resistance coefficient of the study area was between 9 and 32, and the spatial distribution pattern of the resistance surface of each evaluation index was similar, with a large resistance value in the southeast and a small spatial pattern in the northwest. Long-term mining has polluted the ecological environment of the basin, and the closer the mining area, the higher the priority of regional ecological restoration. The study area is divided into four priority areas, and the priority of each area is in turn: Area Ⅰ > Area Ⅱ > Area Ⅲ > Area Ⅳ. Area Ⅰ focuses on water control, increasing pH, reducing the available content of heavy metals, and increasing vegetation coverage. Area Ⅱ focuses on river control and soil control, ensuring a reduction in pollution and enhancing the waste water regulation of sludge reservoirs. Areas Ⅲ and Ⅳ focus on soil control, gradually improving soil conditions. The results provide a scientific basis for the landing and scientific management of restoration projects on spatial and temporal scales. |
doi_str_mv | 10.5846/stxb201905291121 |
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This paper utilized the minimal cumulative resistance(MCR) model to establish the regional ecological resistance surface, analyzed ecological restoration priorities using Jenks natural breakpoint method, and proposes key points and countermeasures for regionalized governance. The results show that the comprehensive resistance coefficient of the study area was between 9 and 32, and the spatial distribution pattern of the resistance surface of each evaluation index was similar, with a large resistance value in the southeast and a small spatial pattern in the northwest. Long-term mining has polluted the ecological environment of the basin, and the closer the mining area, the higher the priority of regional ecological restoration. The study area is divided into four priority areas, and the priority of each area is in turn: Area Ⅰ > Area Ⅱ > Area Ⅲ > Area Ⅳ. Area Ⅰ focuses on water control, increasing pH, reducing the available content of heavy metals, and increasing vegetation coverage. Area Ⅱ focuses on river control and soil control, ensuring a reduction in pollution and enhancing the waste water regulation of sludge reservoirs. Areas Ⅲ and Ⅳ focus on soil control, gradually improving soil conditions. The results provide a scientific basis for the landing and scientific management of restoration projects on spatial and temporal scales.</description><identifier>ISSN: 1000-0933</identifier><identifier>DOI: 10.5846/stxb201905291121</identifier><language>chi ; eng</language><publisher>Beijing: Science Press</publisher><subject>Basins ; Distribution patterns ; Ecological monitoring ; Environmental regulations ; Environmental restoration ; Flow control ; Heavy metals ; Lakes ; Pollution control ; Project management ; Regional analysis ; Resistance factors ; Restoration ; Rivers ; Sediment pollution ; Sludge ; Soil conditions ; Soil improvement ; Soil pollution ; Soils ; Spatial distribution ; Wastewater ; Wastewater pollution ; Water control ; Water pollution</subject><ispartof>Sheng tai xue bao, 2019, Vol.39 (23), p.8920</ispartof><rights>Copyright Science Press 2019</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c1167-ae8168e3b259fd30a110086124edbd3b94e9bee6bc4279752f850e1f0e35d61c3</citedby></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,776,780,4010,27900,27901,27902</link.rule.ids></links><search><creatorcontrib>Zhang, Shiwen</creatorcontrib><creatorcontrib>Bu, Zhongyuan</creatorcontrib><creatorcontrib>Shen, Qiang</creatorcontrib><creatorcontrib>Yang, Shaowen</creatorcontrib><creatorcontrib>Hu, Qingqing</creatorcontrib><creatorcontrib>Zhou, Yan</creatorcontrib><creatorcontrib>Luo, Ming</creatorcontrib><title>Resistance and priority analysis of landscape forest fields, lakes, and grass restoration in Dabaoshan mining basin</title><title>Sheng tai xue bao</title><description>Following the concept of "source prevention, flow control, and sink control", taking Dabaoshan mining area in nanling, north guangdong as the source of risk and the basin as a research area, the main resistance factors of the area were analyzed and studied. This paper utilized the minimal cumulative resistance(MCR) model to establish the regional ecological resistance surface, analyzed ecological restoration priorities using Jenks natural breakpoint method, and proposes key points and countermeasures for regionalized governance. The results show that the comprehensive resistance coefficient of the study area was between 9 and 32, and the spatial distribution pattern of the resistance surface of each evaluation index was similar, with a large resistance value in the southeast and a small spatial pattern in the northwest. Long-term mining has polluted the ecological environment of the basin, and the closer the mining area, the higher the priority of regional ecological restoration. The study area is divided into four priority areas, and the priority of each area is in turn: Area Ⅰ > Area Ⅱ > Area Ⅲ > Area Ⅳ. Area Ⅰ focuses on water control, increasing pH, reducing the available content of heavy metals, and increasing vegetation coverage. Area Ⅱ focuses on river control and soil control, ensuring a reduction in pollution and enhancing the waste water regulation of sludge reservoirs. Areas Ⅲ and Ⅳ focus on soil control, gradually improving soil conditions. The results provide a scientific basis for the landing and scientific management of restoration projects on spatial and temporal scales.</description><subject>Basins</subject><subject>Distribution patterns</subject><subject>Ecological monitoring</subject><subject>Environmental regulations</subject><subject>Environmental restoration</subject><subject>Flow control</subject><subject>Heavy metals</subject><subject>Lakes</subject><subject>Pollution control</subject><subject>Project management</subject><subject>Regional analysis</subject><subject>Resistance factors</subject><subject>Restoration</subject><subject>Rivers</subject><subject>Sediment pollution</subject><subject>Sludge</subject><subject>Soil conditions</subject><subject>Soil improvement</subject><subject>Soil pollution</subject><subject>Soils</subject><subject>Spatial distribution</subject><subject>Wastewater</subject><subject>Wastewater pollution</subject><subject>Water control</subject><subject>Water pollution</subject><issn>1000-0933</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2019</creationdate><recordtype>article</recordtype><recordid>eNpdkM1LAzEQxXNQsH7cPQa8ujpJ9itHqZ9QEETPS7I7qanbpGa2YP97U-rJ0zD83jzmPcYuBdxUbVnf0vRjJQgNldRCSHHEZgIACtBKnbBTohWAAqH0jNEbkqfJhB65CQPfJB-Tn3Z5MeMuIx4dHzOh3myQu5iQJu48jgNdZ_CFeewPl8kQ8T2NyUw-Bu4DvzfWRPo0ga998GHJrSEfztmxMyPhxd88Yx-PD-_z52Lx-vQyv1sUvRB1UxhsRd2isrLSblBgRA7R1kKWONhBWV2itoi17UvZ6KaSrq0AhQNU1VCLXp2xq4PvJsXvbf6sW8Vtyrmok6rKrlLVTVbBQdWnSJTQdbmDtUm7TkC3r7P7X6f6BUmJbCs</recordid><startdate>2019</startdate><enddate>2019</enddate><creator>Zhang, Shiwen</creator><creator>Bu, Zhongyuan</creator><creator>Shen, Qiang</creator><creator>Yang, Shaowen</creator><creator>Hu, Qingqing</creator><creator>Zhou, Yan</creator><creator>Luo, Ming</creator><general>Science Press</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7SN</scope><scope>7ST</scope><scope>7UA</scope><scope>C1K</scope><scope>SOI</scope></search><sort><creationdate>2019</creationdate><title>Resistance and priority analysis of landscape forest fields, lakes, and grass restoration in Dabaoshan mining basin</title><author>Zhang, Shiwen ; Bu, Zhongyuan ; Shen, Qiang ; Yang, Shaowen ; Hu, Qingqing ; Zhou, Yan ; Luo, Ming</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c1167-ae8168e3b259fd30a110086124edbd3b94e9bee6bc4279752f850e1f0e35d61c3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>chi ; eng</language><creationdate>2019</creationdate><topic>Basins</topic><topic>Distribution patterns</topic><topic>Ecological monitoring</topic><topic>Environmental regulations</topic><topic>Environmental restoration</topic><topic>Flow control</topic><topic>Heavy metals</topic><topic>Lakes</topic><topic>Pollution control</topic><topic>Project management</topic><topic>Regional analysis</topic><topic>Resistance factors</topic><topic>Restoration</topic><topic>Rivers</topic><topic>Sediment pollution</topic><topic>Sludge</topic><topic>Soil conditions</topic><topic>Soil improvement</topic><topic>Soil pollution</topic><topic>Soils</topic><topic>Spatial distribution</topic><topic>Wastewater</topic><topic>Wastewater pollution</topic><topic>Water control</topic><topic>Water pollution</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Zhang, Shiwen</creatorcontrib><creatorcontrib>Bu, Zhongyuan</creatorcontrib><creatorcontrib>Shen, Qiang</creatorcontrib><creatorcontrib>Yang, Shaowen</creatorcontrib><creatorcontrib>Hu, Qingqing</creatorcontrib><creatorcontrib>Zhou, Yan</creatorcontrib><creatorcontrib>Luo, Ming</creatorcontrib><collection>CrossRef</collection><collection>Ecology Abstracts</collection><collection>Environment Abstracts</collection><collection>Water Resources Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Environment Abstracts</collection><jtitle>Sheng tai xue bao</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Zhang, Shiwen</au><au>Bu, Zhongyuan</au><au>Shen, Qiang</au><au>Yang, Shaowen</au><au>Hu, Qingqing</au><au>Zhou, Yan</au><au>Luo, Ming</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Resistance and priority analysis of landscape forest fields, lakes, and grass restoration in Dabaoshan mining basin</atitle><jtitle>Sheng tai xue bao</jtitle><date>2019</date><risdate>2019</risdate><volume>39</volume><issue>23</issue><spage>8920</spage><pages>8920-</pages><issn>1000-0933</issn><abstract>Following the concept of "source prevention, flow control, and sink control", taking Dabaoshan mining area in nanling, north guangdong as the source of risk and the basin as a research area, the main resistance factors of the area were analyzed and studied. This paper utilized the minimal cumulative resistance(MCR) model to establish the regional ecological resistance surface, analyzed ecological restoration priorities using Jenks natural breakpoint method, and proposes key points and countermeasures for regionalized governance. The results show that the comprehensive resistance coefficient of the study area was between 9 and 32, and the spatial distribution pattern of the resistance surface of each evaluation index was similar, with a large resistance value in the southeast and a small spatial pattern in the northwest. Long-term mining has polluted the ecological environment of the basin, and the closer the mining area, the higher the priority of regional ecological restoration. The study area is divided into four priority areas, and the priority of each area is in turn: Area Ⅰ > Area Ⅱ > Area Ⅲ > Area Ⅳ. Area Ⅰ focuses on water control, increasing pH, reducing the available content of heavy metals, and increasing vegetation coverage. Area Ⅱ focuses on river control and soil control, ensuring a reduction in pollution and enhancing the waste water regulation of sludge reservoirs. Areas Ⅲ and Ⅳ focus on soil control, gradually improving soil conditions. The results provide a scientific basis for the landing and scientific management of restoration projects on spatial and temporal scales.</abstract><cop>Beijing</cop><pub>Science Press</pub><doi>10.5846/stxb201905291121</doi></addata></record> |
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subjects | Basins Distribution patterns Ecological monitoring Environmental regulations Environmental restoration Flow control Heavy metals Lakes Pollution control Project management Regional analysis Resistance factors Restoration Rivers Sediment pollution Sludge Soil conditions Soil improvement Soil pollution Soils Spatial distribution Wastewater Wastewater pollution Water control Water pollution |
title | Resistance and priority analysis of landscape forest fields, lakes, and grass restoration in Dabaoshan mining basin |
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