挠力河湿地大型底栖动物功能特性
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摘要
为研究挠力河湿地大型底栖动物功能特性的季节变化,及其与底质、植被之间的关系,于2016年7月份—2017年5月份在挠力河湿地设置11个采样点进行大型底栖动物采集和分析。结果表明:在挠力河湿地发现大型底栖动物共9目18科42种,划分为6种摄食功能群,即捕食者(PR)、杂食者(OM)、直接集食者(GC)、过滤收集者(FC)、刮食者(SC)和撕食者(SH),其中,刮食者和捕食者是优势功能群,物种数分别为19种和11种;6种运动功能群,即漂浮者(PL)、潜水者(DI)、附着者(CN)、扩张者(SP)、攀爬者(CM)和挖掘者(BU),其中附着者为优势功能群,物种数多达25种。底质类型、水生维管束植物等均是影响大型底栖动物生长和分布的因素,同样也影响其功能群的变化。
The experiment was conducted to study the seasonal variation of functional traits for macroinvertebrates in Naolihe Wetland and the effect by environment factors,collected macroinvertebrates from 11 sampling sites from the summer of2016( July) to the spring of 2017( May). The macroinvertebrates in 42 species of 18 families of 9 orders are divided into6 feeding groups,including Predators,Omnicorous,Gathers-collectors,Filter-collectors,Scrapers and Shredders. Scrapers and Predators are dominant functional groups among them,the species number are 19 and 11. The total of 6 movement groups,including Planktonic,Divers,Clingers,Sprawlers,Climbers and Burrowers. Clingers is the main functional group of all,and the species number is 25. The sediment type,and aquatic vascular bundle are the factors affecting the growth and the variation of functional groups for macroinvertebrates.
The experiment was conducted to study the seasonal variation of functional traits for macroinvertebrates in Naolihe Wetland and the effect by environment factors,collected macroinvertebrates from 11 sampling sites from the summer of2016( July) to the spring of 2017( May). The macroinvertebrates in 42 species of 18 families of 9 orders are divided into6 feeding groups,including Predators,Omnicorous,Gathers-collectors,Filter-collectors,Scrapers and Shredders. Scrapers and Predators are dominant functional groups among them,the species number are 19 and 11. The total of 6 movement groups,including Planktonic,Divers,Clingers,Sprawlers,Climbers and Burrowers. Clingers is the main functional group of all,and the species number is 25. The sediment type,and aquatic vascular bundle are the factors affecting the growth and the variation of functional groups for macroinvertebrates.
引文
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[23] CAMACHO R,BOYERO L,CORNEJO A,et al. Local variation in shredder numbers can explain their oversight in tropical streams[J]. Biotropica,2009,41(5):625-632.
[24] ALLAN J D. Landscapes and riverscapes:the influence of land use on stream ecosystems[J]. Annual Review of Ecology,Evolution,and Systematics,2004,35(1):257-284.
[25] BENSTEAD J P,PRINGLE C M. Deforestation alters the resource base and biomass of endemic stream insects in eastern Madagascar[J]. Freshwater Biology,2004,49(4):490-501.
[26] JINGGUT T,YULE C M,BOYERO L. Stream ecosystem integrity is impaired by logging and shifting agriculture in a global megadiversity center(Sarawak,Borneo)[J]. Science of the Total Environment,2012,437(20):83-90.
[27] BAXTER C V,FAUSCH K D,SAUNDERS W C. Tangled webs:reciprocal flows of invertebrate prey link stream and riparian zones[J]. Freshwater Biology,2005,50(2):201-220.
[28] IRONS J G,OSWOOD M W,STOUT R J,et al. Latitudinal patterns in leaf litter breakdown:is temperature really important[J].Freshwater Biology,2010,32(2):401-411.
[29] BOYERO L,PEARSON R G,DUDGEON D,et al. Global patterns of stream detritivore distribution:implications for biodiversity loss in changing climates[J]. Global Ecology and Biogeography,2011,21(2):134-141.
[30] DING N,YANG W,ZHOU Y,et al. Different responses of functional traits and diversity of stream macroinvertebrates to environmental and spatial factors in the Xishuangbanna watershed of the upper Mekong River Basin,China[J]. Science of the Total Environment,2017,574:288-299.
[31] HUBLER S,HUFF D,EDWARDS P,et al. The biological sediment tolerance index:assessing fine sediments conditions in Oregon streams using macroinvertebrates[J]. Ecological Indicators,2016,67:132-145.
[32] KASKELA A M,ROUSI H,RONKAINEN M,et al. Linkages between benthic assemblages and physical environmental factors:The role of geodiversity in Eastern Gulf of Finland ecosystems[J]. Continental Shelf Research,2017,142:1-13.
[33] RENNIE M D,JACKSON L J. The influence of habitat complexity on littoral invertebrate distributions:patterns differ in shallow prairie lakes with and without fish[J]. Canadian Journal of Fisheries and Aquatic Sciences,2005,62(9):2088-2099.
[34] VAN DER VALK A G. The biology of freshwater wetlands[M].Oxford:Oxford University Press,2006:114-128.
[2] KERANS B L,KARR J R. A benthic index of biotic integrity(BIBI)for rivers of the Tennessee valley[J]. Ecological Applications,1994,4(4):768-785.
[3] FORE L S,KARR J R,WISSEMAN R W. Assessing invertebrate responses to human activities:evaluating alternative approaches[J]. Journal of the North American Benthological Society,1996,15(2):212-231.
[4]赵然,贾立明.大型无脊椎底栖动物水质生物评价国内外研究现状[J].曲阜师范大学学报,2015,41(2):62-66.
[5]李新正,刘录三,李宝泉,等.中国海洋大型底栖动物研究与实践[M].北京:海洋出版社,2010:55-57.
[6] POFF N L,OLDEN J D,VIEIRA N K M,et al. Functional trait niches of North American lotic insects:traits-based ecological applications in light of phylogenetic relationships[J]. The North American Benthological Society,2006,25(4):730-755.
[7]安睿,王凤友,于洪贤,等.三环泡湿地浮游动物功能群季节变化及其影响因子[J].生态学报,2017,37(6):1-10.
[8]王建华,田景汉,吕宪国.挠力河流域河流的B-IBI评价[J].生态学报,2009,29(12):6672-6680.
[9]侯伟,张树文,张养贞,等.三江平原挠力河流域50年代以来湿地退缩过程及驱动力分析[J].自然资源学报,2004,19(6):725-731.
[10]刘红玉,张世奎,吕宪国.20世纪80年代以来挠力河流域湿地景观变化过程研究[J].自然资源学报,2002,17(6):698-705.
[11]崔兴波,刘曼红,马玉堃.黑龙江挠力河国家级自然保护区退耕还湿工程及效益分析[J].黑龙江科学,2016,7(19):153-155.
[12] CUMMINS K W. Trophic relations of aquatic insects[J]. Annual Review of Entomology,1973,18(1):183-206.
[13]刘曼红.呼兰河口保护区及周边水域水生动物生态监测与健康评价[M].哈尔滨:东北林业大学,2012:26-31.
[14] MORSE J C,YANG L F,TIAN L X. Aquatic Insects of china useful for monitoring water quality[M]. Nanjing:Hohai University Press,1984:59-61.
[15] HOWARD J K,CUFFEY K M. The functional role of native freshwater mussels in the fluvial benthic environment[J]. Freshwater Biology,2006,51(3):460-474.
[16] VAUGHN C C. Biodiversity losses and ecosystem function in freshwaters:emerging conclusions and research directions[J].BioScience,2010,60(1):25-35.
[17] CHOWDHURY G W,ZIERITZ A,ALDRIDGE D C. Ecosystem engineering by mussels supports biodiversity and water Volume 36September 2017/679 clarity in a heavily polluted lake in Dhaka,Bangladesh[J]. Freshwater Science,2016,35:188-199.
[18] MATHURIAU C,CHAUVET E. Breakdown of leaf litter in a neotropical stream[J]. Journal of the North American Benthological Society,2002,21(3):384-396.
[19] GONALVES J F,GRAA M A F,CALLISTO M. Leaflitter breakdown in 3 streams in temperate,Mediterranean,and tropical Cerrado climates[J]. Journal of the North American Benthological Society,2006,25(2):344-355.
[20] LI A O Y,DUDGEON D. Food resources of shredders and other benthic macroinvertebrates across a range of shading conditions in tropical Hong Kong streams[J]. Freshwater Biology,2010,53(10):2011-2025.
[21] DOBSON M,MATHOOKO J M,MAGANA A,et al. Macroinvertebrate assemblages and detritus processing in Kenyan highland streams:more evidence for the paucity of shredders in the tropics[J]. Freshwater Biology,2002,47:909-919.
[22] CHESHIRE K,BOYERO L,PEARSON R G. Food webs in tropical Australian streams:shredders are not scarce[J]. Freshwater Biology,2005,50(5):748-769.
[23] CAMACHO R,BOYERO L,CORNEJO A,et al. Local variation in shredder numbers can explain their oversight in tropical streams[J]. Biotropica,2009,41(5):625-632.
[24] ALLAN J D. Landscapes and riverscapes:the influence of land use on stream ecosystems[J]. Annual Review of Ecology,Evolution,and Systematics,2004,35(1):257-284.
[25] BENSTEAD J P,PRINGLE C M. Deforestation alters the resource base and biomass of endemic stream insects in eastern Madagascar[J]. Freshwater Biology,2004,49(4):490-501.
[26] JINGGUT T,YULE C M,BOYERO L. Stream ecosystem integrity is impaired by logging and shifting agriculture in a global megadiversity center(Sarawak,Borneo)[J]. Science of the Total Environment,2012,437(20):83-90.
[27] BAXTER C V,FAUSCH K D,SAUNDERS W C. Tangled webs:reciprocal flows of invertebrate prey link stream and riparian zones[J]. Freshwater Biology,2005,50(2):201-220.
[28] IRONS J G,OSWOOD M W,STOUT R J,et al. Latitudinal patterns in leaf litter breakdown:is temperature really important[J].Freshwater Biology,2010,32(2):401-411.
[29] BOYERO L,PEARSON R G,DUDGEON D,et al. Global patterns of stream detritivore distribution:implications for biodiversity loss in changing climates[J]. Global Ecology and Biogeography,2011,21(2):134-141.
[30] DING N,YANG W,ZHOU Y,et al. Different responses of functional traits and diversity of stream macroinvertebrates to environmental and spatial factors in the Xishuangbanna watershed of the upper Mekong River Basin,China[J]. Science of the Total Environment,2017,574:288-299.
[31] HUBLER S,HUFF D,EDWARDS P,et al. The biological sediment tolerance index:assessing fine sediments conditions in Oregon streams using macroinvertebrates[J]. Ecological Indicators,2016,67:132-145.
[32] KASKELA A M,ROUSI H,RONKAINEN M,et al. Linkages between benthic assemblages and physical environmental factors:The role of geodiversity in Eastern Gulf of Finland ecosystems[J]. Continental Shelf Research,2017,142:1-13.
[33] RENNIE M D,JACKSON L J. The influence of habitat complexity on littoral invertebrate distributions:patterns differ in shallow prairie lakes with and without fish[J]. Canadian Journal of Fisheries and Aquatic Sciences,2005,62(9):2088-2099.
[34] VAN DER VALK A G. The biology of freshwater wetlands[M].Oxford:Oxford University Press,2006:114-128.
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