生物多样性保护优先区域划定方法研究——以青岛为例
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摘要
保护生物多样性已成为可持续发展研究的热点。划定生物多样性保护优先区域是可持续发展的有效途径,而划定方法的研究是关键。本研究融合了遥感解译、模型评估和物种调查技术,将生态系统和物种测度方法进行结合,提出综合性生物多样性保护优先区域划定方法,并以青岛市为例,划定了10个陆地生物多样性保护优先区域和9个海洋生物多样性保护优先区域,面积分别是873.34 km~2和707.23 km~2,主要保护对象为森林、湿地、草地、岛屿、海洋生态系统及特有物种资源、濒危物种资源、渔业资源。该划定方法可为生物多样性保护优先区域划定提供借鉴,推动生物多样性保护和生物资源可持续利用。
Biodiversity conservation has become a hot topic in the study of sustainable development. Defining priority areas for biodiversity conservation is an effective way of sustainable development, whereas, defining methods of research is the key aspect. In this study, remote sensing interpretation, model assessment and species survey were integrated, and a comprehensive method for biodiversity conservation priority areas was proposed based on ecosystem estimation and species investigation. Taking Qingdao as an example, 10 land priority areas and 9 marine priority areas for biodiversity conservation are determined, with an area of 873.34 km2 and 707.23 km2 respectively. Forests, wetlands, meadows, islands, ocean ecosystems and endemic species, endangered species and fishery resources are the main objects of protection. The defining method provided a reference for zoning priority areas of biodiversity conservation, and consequently promoted biodiversity conservation and sustainable utilization of biological resources.
Biodiversity conservation has become a hot topic in the study of sustainable development. Defining priority areas for biodiversity conservation is an effective way of sustainable development, whereas, defining methods of research is the key aspect. In this study, remote sensing interpretation, model assessment and species survey were integrated, and a comprehensive method for biodiversity conservation priority areas was proposed based on ecosystem estimation and species investigation. Taking Qingdao as an example, 10 land priority areas and 9 marine priority areas for biodiversity conservation are determined, with an area of 873.34 km2 and 707.23 km2 respectively. Forests, wetlands, meadows, islands, ocean ecosystems and endemic species, endangered species and fishery resources are the main objects of protection. The defining method provided a reference for zoning priority areas of biodiversity conservation, and consequently promoted biodiversity conservation and sustainable utilization of biological resources.
引文
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[24]张硕,施斌杰,谢斌,等.连云港海州湾海洋牧场浮游动物群落结构及其与环境因子的关系[J].生态环境学报,2017(8):1410-1418.
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[27]王仁卿,张淑萍,石竹,等.青岛耐冬山茶的多样性特征及其保护[J].山东林业科技,1998(3):1-4.
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[29]荣月静,郭新亚,杜世勋,等.基于生态系统服务功能及生态敏感性与PSR模型的生态承载力空间分析[J].水土保持研究,2019(1):323-329.
[30]黄备,孟伟杰,魏娜.基于PSR模型的山东长岛海域海洋生物多样性研究[J].水生态学杂志,2017(1):61-67.
[31]付秀梅,姜琴,王东亚,等.青岛海域海洋生物多样性现状与安全度评估研究[J].海洋环境科学,2018(1):21-27.
[2]刘磊,张青萍.中国生物多样性面临严峻挑战[J].生态经济,2016(4):6-9.
[3]马克平.试论生物多样性的概念[J].生物多样性,1993(1):20-22.
[4]武建勇,于之的,刘海鸥,等.省级生物多样性保护战略与行动计划(BSAP)编制进展和实施策略[J].中国人口·资源与环境,2015(S1):555-557.
[5]Myers N. Threatened biotas:“Hot spots” in tropical forests[J]. Environmentalist, 1988, 8(3):187-208.
[6]Myers N. The biodiversity challenge:Expanded hot-spots analysis[J]. Environmentalist, 1990, 10(4):243-256.
[7]Mittermeier R A, Myers N, Thomsen J B, et al. Biodiversity hotspots and major tropical wilderness areas:Approaches to setting conservation priorities[J]. Conservation Biology, 1998,12(3):516-520.
[8]Myers N, Mittermeier R A, Mittermeier C G, et al. Biodiversity hotspots for conservation priorities[J]. Nature, 2000,403(6772):853-858.
[9]刘敏超,李迪强,温琰茂,等.基于GIS的三江源地区物种多样性保护优先性分析[J].干旱区资源与环境,2006(4):51-54.
[10]Pérez-Quintero J C. Environmental determinants of freshwater mollusc biodiversity and identification of priority areas for conservation in mediterranean water courses[J]. Biodiversity and Conservation, 2012, 21(12):3001-3016.
[11]林金兰,陈彬,黄浩,等.海洋生物多样性保护优先区域的确定[J].生物多样性,2013(1):38-46.
[12]Minin E D, Soutullo A, Bartesaghi L, et al. Integrating biodiversity, ecosystem services and socio-economic data to identify priority areas and landowners for conservation actions at the national scale[J]. Biological Conservation, 2017, 206:56-64.
[13]田海芬,刘华民,王炜,等.大青山山地植物区系及生物多样性研究[J].干旱区资源与环境,2014(8):172-177.
[14]张增祥,汪潇,温庆可,等.土地资源遥感应用研究进展[J].遥感学报,2016(5):1243-1258.
[15]杨德彬,夏春林,黄耀欢,等.生物多样性保护优先区用地类型遥感监测研究[J].中国人口·资源与环境,2015(S2):188-192.
[16]陈涛,叶有华,孙芳芳,等.基于SPOT数据的深圳市生态系统服务功能重要性评价[J].生态经济,2018(2):151-157.
[17]生态环境部.区域生物多样性评价标准:HJ623—2011[S].北京:中国环境科学出版社,2011.
[18]万本太,徐海根,丁晖,等.生物多样性综合评价方法研究[J].生物多样性,2007(1):97-106.
[19]何勇凤,李昊成,王旭歌,等.长湖鱼类群落结构的时空变化[J].长江流域资源与环境,2016(2):265-273.
[20]闫秀婧.青岛市森林与湿地负离子的空间分布特征[J].林业科学,2010(6):65-70.
[21]韦希勤.森林覆盖率有关问题的探讨[J].世界林业研究,2011(2):76-80.
[22]江翠红.青岛地区湿地资源现状及保护建议[J].国土绿化,2014(4):39-40.
[23]林世滔,谢弟炳,刘郁林,等.景观格局特征与区域生物多样性的关系研究[J].生态环境学报,2017(10):1681-1688.
[24]张硕,施斌杰,谢斌,等.连云港海州湾海洋牧场浮游动物群落结构及其与环境因子的关系[J].生态环境学报,2017(8):1410-1418.
[25]周建国,李新旺,胡金明,等.怒江流域云南段生物多样性保护地人为干扰分析[J].热带地理,2018(4):465-474.
[26]王丽群,张志强,李格,等.北京边缘地区景观格局变化及对生态系统服务的影响评价——以牛栏山-马坡镇为例[J].生态学报,2018(3):750-759.
[27]王仁卿,张淑萍,石竹,等.青岛耐冬山茶的多样性特征及其保护[J].山东林业科技,1998(3):1-4.
[28]刘纪远,张增祥,庄大方.二十世纪九十年代我国土地利用变化时空特征及其成因分析[J].中国科学院院刊,2003(1):35-37.
[29]荣月静,郭新亚,杜世勋,等.基于生态系统服务功能及生态敏感性与PSR模型的生态承载力空间分析[J].水土保持研究,2019(1):323-329.
[30]黄备,孟伟杰,魏娜.基于PSR模型的山东长岛海域海洋生物多样性研究[J].水生态学杂志,2017(1):61-67.
[31]付秀梅,姜琴,王东亚,等.青岛海域海洋生物多样性现状与安全度评估研究[J].海洋环境科学,2018(1):21-27.