中国海洋大学学报（自然科学版）
中國海洋大學學報（自然科學版）
중국해양대학학보（자연과학판）
PERIODICAL OF OCEAN UNIVERSITY OF CHINA
2009年
4期
705-711
,共7页
傅秀梅%王亚楠%邵长伦%王长云%李国强%刘光兴%孙世春%曾晓起%叶振江%管华诗
傅秀梅%王亞楠%邵長倫%王長雲%李國彊%劉光興%孫世春%曾曉起%葉振江%管華詩
부수매%왕아남%소장륜%왕장운%리국강%류광흥%손세춘%증효기%협진강%관화시
中国红树林%物种分布%资源状况%保护策略%管理措施
中國紅樹林%物種分佈%資源狀況%保護策略%管理措施
중국홍수림%물충분포%자원상황%보호책략%관리조시
Chinese mangroves%species distribution%resources status%protection strategy%management countermeasures
对中国红树林物种组成、资源状况和分布特征进行了调查和评价.结果表明,中国红树林天然分布南界为海南三亚(18°12′N),北界为福建福鼎(27°20′N)(人工引种北界为浙江乐清28°25′N).中国红树林区系有红树植物20科26属37种.广东、广西和海南沿海是中国红树林的主要分布地区.近50 年来,红树林面积先是锐减(1950年,48 266 hm2;1997年,14 877 hm2),2000年后略有回升(2002年,22 024.9 hm2;2008年,23 081.5 hm2).合理评估红树林湿地生态效价,完善红树林保护区制度,推进红树林湿地生态修复工程,构建红树林湿地保护网络系统,是中国红树林资源保护性开发利用的可行对策.
對中國紅樹林物種組成、資源狀況和分佈特徵進行瞭調查和評價.結果錶明,中國紅樹林天然分佈南界為海南三亞(18°12′N),北界為福建福鼎(27°20′N)(人工引種北界為浙江樂清28°25′N).中國紅樹林區繫有紅樹植物20科26屬37種.廣東、廣西和海南沿海是中國紅樹林的主要分佈地區.近50 年來,紅樹林麵積先是銳減(1950年,48 266 hm2;1997年,14 877 hm2),2000年後略有迴升(2002年,22 024.9 hm2;2008年,23 081.5 hm2).閤理評估紅樹林濕地生態效價,完善紅樹林保護區製度,推進紅樹林濕地生態脩複工程,構建紅樹林濕地保護網絡繫統,是中國紅樹林資源保護性開髮利用的可行對策.
대중국홍수림물충조성、자원상황화분포특정진행료조사화평개.결과표명,중국홍수림천연분포남계위해남삼아(18°12′N),북계위복건복정(27°20′N)(인공인충북계위절강악청28°25′N).중국홍수림구계유홍수식물20과26속37충.엄동、엄서화해남연해시중국홍수림적주요분포지구.근50 년래,홍수림면적선시예감(1950년,48 266 hm2;1997년,14 877 hm2),2000년후략유회승(2002년,22 024.9 hm2;2008년,23 081.5 hm2).합리평고홍수림습지생태효개,완선홍수림보호구제도,추진홍수림습지생태수복공정,구건홍수림습지보호망락계통,시중국홍수림자원보호성개발이용적가행대책.
The species composition, resources status and distribution characters of mangroves in China were investigated and evaluated by field survey and data analysis together with literature. It indicated that the natural distribution south boundary of Chinese mangroves is at 18°12′N(Sanya, Hainan province), and the north boundary is at 27°20′N(Fuding, Fujian province) with an artificial planting north boundary at 28°25′N(Yueqing, Zhejiang province). A total of 37 species of mangrove plants belonging to 26 genera in 20 families were found in China. The coasts of Guangdong, Guangxi and Hainan are the main areas of Chinese mangroves. In the past 50 years, the mangrove area in China decreased acutely from 48 266 hm2 in 1950 to 14 877 hm2 in 1997, whereas since 2000 the area has increased slightly from 22 024.9 hm2 in 2002 to 23 081.5 hm2 in 2008. The feasible strategies for protective exploitation of Chinese mangrove resources should be to evaluate the ecological effects of mangrove wetlands reasonably, to improve the natural reserves system, to promote the ecological restoration engineering, as well as to establish a network for mangrove conservation.
