淇澳岛两种红树林区大型底栖动物群落比较

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Abstract

The macrobenthic community structures were studied in two mangroves,natural Kandelia candel and Sonneratia apetala plantation,in Qiao Island of Zhuhai.The results showed that the macrobenthic number and composition in natural Kandelia candel were very different from those in Sonneratia apetala plantation.The average macrobenthic biomass and diversity in Kandelia candel were 668.64 g·m^-2 and 8370·m^-2,while they were 511.64 g·m^-2 and 4748·m^-2 in Sonneratia apetala.There were some differences in macrobenthic community structure in different tidal zones in mangrove sections.The highest biomass and density of Kandelia candel were observed in the mid-tidal region,which were mainly influenced by the Arthropods and Mollusks.The highest density of Sonneratia apetala was also found in the mid-tidal region,but the biomass changed irregularly.The characteristics of macrobenthic community in two sections of mangroves showed obviously seasonal changes.The highest biomass was in autumn;the highest density was in winter, and the lowest in summer;the lowest diversity was in summer;the highest diversity in Kandelia candel was in spring;the highest diversity in Sonneratia apetala was in autumn.The results indicated that the factors including quality of soil environment,the height of plants and shelter,as well as the air and light conditions in forest ecosystem caused the differences in macrobenthic community.

Key words： natural Kandelia candel Sonneratia apetala plantation macrobenthos

Received: 25 October 2011

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	Articles by authors
	ZHONG Yan-ting
	ZHANG Zai-wang
	TANG Yi-jie
	CHEN Kang
	LIU Ben-han
	FANG Zhan-qiang

Cite this article:

ZHONG Yan-ting,ZHANG Zai-wang,TANG Yi-jie, et al. Comparison of the macrobenthic community in two mangrove regions in Qiao Island[J]. , 2011, 30(5): 493-499.

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http://www.ecolsci.com/EN/ OR http://www.ecolsci.com/EN/Y2011/V30/I5/493

[1] 林鹏.中国红树林种类分布和林相类型[A].李振基.环境与生态论丛[C].厦门:厦门大学出版社,1993.
[2] Sasekumar A.Distribution of macrofauna of a Malayan mangrove shore[J].J Anim Ecol,1974,43:51-69.
[3] 王树功,郑耀辉,彭逸生,陈桂珠.珠江口淇澳岛红树林湿地生态系统健康评价[J].应用生态学报,2010,21(2):391-398.
[4] 廖宝文,田广红,杨雄邦,唐国玲,章家恩.珠海淇澳岛无瓣海桑种苗天然更新与扩散分析[J].生态科学,2006,25(6):485-488.
[5] 李旭林,彭逸生,万如,伍卡兰,陈桂珠.两种相手蟹对不同红树植物叶片取食的偏好性[J].生态学报,2010,30(14):3752-3759.
[6] 叶勇,翁劲,卢昌义,陈光程.红树林生物多样性恢复[J].生态学报,2006,26(4):1243-1250.
[7] 雷振胜,李玫,廖宝文.珠海淇澳红树林湿地生物多样性现状及保护[J].广东林业科技,2008,24(5):56-60.
[8] 廖宝文,管伟,章家恩.珠海市淇澳岛红树林群落发展动态研究[J].华南农业大学学报,2008,29(4):59-64.
[9] Lee S Y The ecological role of grapsid crabs in mangrove ecosystems:implications for conservation[J].Marine and Freshwater Research,1998,49:335-343.
[10] Macnae W A.general account of the fauna and flora of mangrove swamps and forests in the Indo-West-Pacific re-gion[J].Advance in Marine Biology,1968,6:73-270.
[11] LasiakT,Dye A H.Behavioural adaptations of the man-grove whelk,Telescopium telescopium(L.),to life in asemi-terrestrial environment[J].Journal of Molluscan Study,1986,52:174-179.
[12] 林秀春,蔡立哲,马丽,高阳,杨丽,刘炜明.厦门凤林红树林湿地大型底栖动物群落[J].生物多样性,2006,14(2):128-135.
[13] 陈光程.九龙江口秋茄红树植被与主要大型底栖动物某些生态关系的研究[D].厦门:厦门大学环境科学专业,2009.
[14] 周晓,葛振鸣,施文彧,王天厚,曹丹,周立晨.长江口九段沙湿地大型底栖动物群落结构的季节变化规律[J].2006,17(11):2079-2083.
[15] 唐以杰,余世孝.广东湛江红树林保护区大型底栖动物群落的空间分带[J].2007,27(5):1704-1714.
[16] 韩淑梅,何平,黄勃,钟才荣,王先静,郭恒.东寨港典型红树林区底栖动物多样性特征指数比较研究[J].西北林学院学报,2010,25(1):123-126.
[17] 全为民,赵云龙,朱江兴,施利燕,陈亚瞿.上海市潮滩湿地大型底栖动物的空间分布格局[J].生态学报,2008,28(10):5179-5187.
[18] 林鹏著.中国红树林生态系[M].北京:科学出版社,1997.69-74.
[19] Morton B.The diurnal rhythm and the feeding responses of the southeast Asian mangrove bivalve Geloina proxima Prinie 1864(Bivalvia:Corbivulacea)[J].Forma et Function,1975,(3/4):405-419.
[20] Engle V D,Summers J K.Latitudinal gradients in benthic community composition in Western Atlantic estuaries[J].Journal of Biogeography,1999,26:1007-1023.
[21] 高爱根,陈全震,曾江宁,廖一波,杨俊毅.西门岛红树林区大型底栖动物的群落结构[J].海洋学研究,2005,25(2):33-40.