为评估野生大鲵生境质量并促进野生大鲵资源保护,于2023年5月对广东连南大鲵省级自然保护区的溪流中开展了大型底栖无脊椎动物群落格局及驱动因素调查.结果表明,保护区溪流维系了高水平的底栖动物多样性,在32个样点中共记录180种,隶属于6门7纲16目71科167属,其中水生昆虫172种,为绝对优势类群(占总物种数的94.6%).优势种为短脉纹石蛾(Cheumatopsyche sp., 12.1%)、纹石蛾(Hydropsyche sp.,11.6%)、襟襀(Togoperla sp., 6.7%)、四节蜉(Baetis sp., 6.0%)和角石蛾(Stenopsyche sp., 5.5%)等蜉蝣目、襀翅目和毛翅目(EPT)的种类.对万坑河、三家冲河(上游,位于核心区)和排肚河(下游,位于实验区)3个区域的样点进行比较,发现底栖动物群落的物种数、密度、Simpson指数、Shannon指数和Pielou’s均匀度指数在3个区域间无显著差异;3个区域的群落组成也差异较小,均以EPT等敏感种类为主,3组样点在nMDS排序图上有较大重叠.冗余分析(Redundancy Analysis,RDA)显示,影响底栖动物群落的关键环境因子为海拔、溶解氧和底质类型等,关键空间因子则包括12项PCNM变量,有分别代表大(1、3、4、6~8)、中(10、12、13、15)和小尺度(23、28)的PCNM轴.变差分解结果表明,环境因子单独解释了4.7%的群落变化,空间因子单独解释率5.0%,二者共同解释了8.4%,环境因子和空间因子对底栖动物群落变化的解释率基本一致.整体上,连南大鲵保护区内核心区和实验区的溪流生境均为优良状态,水质清洁,底栖动物多样性高,实验区的溪流生境仅略差于核心区.保护区内溪流的优良生境及高水平的底栖动物多样性为大鲵的生存繁衍提供了优良的条件.未来应进一步加强对保护区溪流生态系统的长期监测与管理,以持续提升野生大鲵的生境质量,为大鲵种群的稳定与恢复提供科学支撑.
Abstract
To assess the habitat quality of wild Chinese giant salamanders (Andrias davidianus) and promote the conservation of their conservation, a survey on the community structure and driving factors of macroinvertebrates was conducted in May 2023 in the Guangdong Liannan Giant Salamander Provincial Nature Reserve. The results indicated that streams in the reserve maintained a high level of benthic macroinvertebrate biodiversity, with 180 species, belonging to six phyla, seven classes, 16orders, 71 families, and 167 genera recorded across 32 sampling sites. Among them, aquatic insects accounted for 94.6% (172species) of the total species richness. The dominant species included Cheumatopsyche sp. (12.1%), Hydropsyche sp. (11.6%), Togoperla sp. (6.7%), Baetis sp. (6.0%), and Stenopsyche sp. (5.5%), which all belong to the orders Ephemeroptera, Plecoptera, and Trichoptera (EPT). A comparison of sampling sites in three regions—Wankeng River, Sanjiachong River (upstream, located in the core area), and Paiduhou River (downstream, in the experimental area)—revealed no significant differences in benthic invertebrate species richness, density, Simpson index, Shannon index, and Pielou’s evenness index. The community composition was also similar across the three regions, with EPT and Diptera (sensitive taxa) being the dominant groups. The nMDS ordination plot showed substantial overlap among the three regions. Redundancy analysis (RDA) indicated that key environmental factors influencing the benthic community included altitude, dissolved oxygen, and substrate type, while key spatial factors included 12PCNM variables representing large- (PCNM axes 1, 3, 4, 6~8), medium- (10, 12, 13, 15), and small-scale (23, 28) spatial patterns. Variation partitioning analysis (VPA) showed that environmental factors alone explained 4.7% of the community variation, spatial factors alone explained 5.0%, and their combined effect explained 8.4%, indicating that environmental and spatial factors contributed similarly to the variation in benthic communities. Overall, the stream habitats in both the core and experimental zones of the Liannan giant salamander reserve were in excellent condition, with clean water and high benthic diversity, although the habitat quality in the experimental zone was slightly inferior to that of the core zone. The high-quality stream habitats and rich benthic biodiversity provide favorable conditions for the survival and reproduction of the giant salamander. In the future, long-term monitoring and management of the stream ecosystems in the reserve should be strengthened to continuously improve the habitat quality for wild giant salamanders and provide scientific support for the stability and recovery of their populations.
关键词
大鲵 /
大型无脊椎动物 /
群落结构 /
环境因子 /
冗余分析
Key words
macroinvertebrates /
community structure /
environmental factors /
spatial factors /
redundancy analysis
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参考文献
[1] 蒋志刚,江建平,王跃招,等.国家濒危物种红色名录的生物多样性保护意义 [J].生物多样性, 2020,28(5):558-565. Jiang Z G, Jiang J P, Wang Y Z, et al. Significance of country red lists of endangered species for biodiversity conservation [J]. Biodiversity Science, 2020,28(5):558-565.
[2] Yan F, Lü J, Zhang B, et al. The Chinese giant salamander exemplifies the hidden extinction of cryptic species [J]. Current Biology, 2018, 28(10):590-592.
[3] Alford R A. Bleak future for amphibians [J]. Nature, 2011,480(7378): 461-462.
[4] 丁洋,赵进勇,彭文启,等.野生大鲵栖息活动适宜水动力条件实验及适宜性曲线构建 [J].水利学报, 2024,55(12):1508-1517. Ding Y, Zhao J Y, Peng W Q, et al. Experiment on suitable hydrodynamic conditions for habitat activity of Andrias davidianus and construction of suitability curve [J]. Journal of Hydraulic Engineering, 2024,55(12):1508-1517.
[5] 蒋万胜,兰香英,王金秀,等.中国大鲵种质资源保护与利用研究进展 [J].水产学报, 2022,46(4):683-705. Jiang W S, Lan X Y, Wang J X, et al. Recent progress in the germplasm resources conservation and utilization of the Chinese giant salamander (Andrias davidianus) [J]. Journal of Fisheries of China, 2022,46(4):683-705.
[6] 余杰华,林思亮,林泽花,等.广东连南大鲵省级自然保护区及周边生物多样性及保育 [M].北京:中国林业出版社, 2022. Yu J H, Lin S L, Lin Z H, et al. Biodiversity and conservation of Guangdong Lengnan Giant Salamander Provincial Nature Reserve and its surroundings [M]. Beijing: China Forestry Publishing House, 2022.
[7] 许宝红.中国大鲵繁殖相关研究进展 [J].当代水产, 2011,(8):60-63. Xu B H. Research progress on the reproduction of the Chinese giant salamander [J]. Contemporary Fisheries, 2011,(8):60-63.
[8] Cairns J, Pratt J R. A history of biological monitoring using benthic macroinvertebrates [J]. Freshwater Biomonitoring and Benthic Macroinvertebrates, 1993,10:27.
[9] Mencio A, Boix D. Response of macroinvertebrate communities to hydrological and hydrochemical alterations in Mediterranean streams [J]. Journal of Hydrology, 2018,566:566-580.
[10] 王璐,杨海军,李昆,等.长白山源头溪流底栖动物群落结构季节动态 [J].生态学报, 2018,38(13):4834-4842. Wang L, Yang H J, Li K, et al. Seasonal dynamics of macroinvertebrate community structure in a headwater stream in the Changbai Mountains [J]. Acta Ecologica Sinica, 2018,38(13):4834- 4842.
[11] Voelz N J, Mcarthur J V. An exploration of factors influencing lotic insect species richness [J]. Biodiversity & Conservation, 2000,9:1543- 1570.
[12] González-Ortegón E, Walton M E M, Moghaddam B, et al. Flow regime in a restored wetland determines trophic links and species composition in the aquatic macroinvertebrate community [J]. Science of The Total Environment, 2015,(503-504)(Sp.Iss.SI):241-250.
[13] 易祖盛,黄元骏,易晖,等.广东车八岭国家级自然保护区大型底栖动物多样性 [J].生物多样性, 2021,29(5):680-687. Yi Z S, Huang Y J, Yi H, et al. Biodiversity of macrozoobenthos in the Chebaling National Nature Reserve, Guangdong Province [J]. Biodiversity Science, 2021,29(5):680-687.
[14] 汪兴中.神农架地区溪流底栖动物分布特征及其与环境因子关系研究 [D].北京:中国科学院研究生院, 2012. Wang X Z. Study on the Distribution characteristics of benthic macroinvertebrates and their relationship with environmental factors in streams of the Shennongjia Area [D]. Beijing: Graduate University of Chinese Academy of Sciences, 2012.
[15] Zhou S Q. Theory, method and application of nature reserves function zones [J]. Sichuan Forestry Exploration and Design, 1997,3:37-40.
[16] Jiang X, Song Z, Xiong J, et al. Can excluding non-insect taxa from stream macroinvertebrate surveys enhance the sensitivity of taxonomic distinctness indices to human disturbance?[J]. Ecological Indicators, 2014,41:175-182.
[17] Yan Y, Li X. Temporal dynamics of production and ingestion of the dominant mayflies in a subtropical stream in China [J]. Aquatic Ecology, 2008,42:657-667.
[18] 王崇瑞,梁志强,索纹纹,等.湖南张家界大鲵栖息地大型无脊椎动物组成及其与环境因子的关系 [J].应用生态学报, 2017,28(9):3032- 3040. Wang C R, Liang Z Q, Suo W W, et al. Relationship between macroinvertebrate composition and environmental factors in habitats of Chinese giant salamander in Zhangjiajie, Hunan Province, China [J]. Chinese Journal of Applied Ecology, 2017,28(9):3032-3040.
[19] 刘月英.中国经济动物志 [M].北京:科学出版社, 1979. Liu Y Y. A zoological record of China's economic animals [M]. Beijing: Science Press, 1979.
[20] Morse J C, Yang L, Tian L. Aquatic insects of China useful for monitoring water quality [M]. Nanjing: Hohai University Press, 1994.
[21] Epler J H. Identification manual for the larval Chironomidae (Diptera) of North and South Carolina [J]. 2001.
[22] Barbour M T. Rapid bioassessment protocols for use in wadeable streams and rivers: Periphyton, benthic macroinvertebrates and fish [M]. US Environmental Protection Agency, Office of Water, 1999.
[23] Jiang X M, Xiong J, Qiu J W, et al. Structure of macroinvertebrate communities in relation to environmental variables in a subtropical Asian river system [J]. International Review of Hydrobiology, 2010, 95:42-57.
[24] Beckmann L, Fischer C, Obreiter M, Rabes M, Chang-Claude J. Haplotype-sharing analysis using Mantel statistics for combined genetic effects [J]. BMC Genetics, 2005,59: 67-78.
[25] 熊晶,蒋小明,王丑明,等.宁波东钱湖大型底栖动物群落动态及水质生物学评价 [J].环境科学研究, 2012,25(3): 282-289. Xiong J, Jiang X M, Wang C M, et al. Community variation of macrozoobenthos and bioassessment of Dongqian Lake, Ningbo [J]. Research of Environmental Sciences, 2012,25(3):282-289.
[26] Lepš J, Šmilauer P. Multivariate Analysis of Ecological Data Using CANOCO [M]. Cambridge university press, 2003.
[27] Borcard D, Legendre P. All-scale spatial analysis of ecological data by means of principal coordinates of neighbour matrices [J]. Ecological modelling, 2002,153(1/2):51-68.
[28] Peres-Neto P R, Legendre P, Dray S, Borcard D. Variation partitioning of species data matrices: Estimation and comparison of fractions. Ecology, 2006,87,2614-2625.
[29] 杨强强,徐光来,章翩,等.青弋江流域大型底栖动物群落结构及水质评价 [J].生态学报, 2022,42(10):4169-4180. Yang Q Q, Xu G L, Zhang P, et al. Macroinvertebrate community structure and water quality assessment in the Qingyi River Watershed [J]. Acta Ecologica Sinica, 2022,42(10):4169-4180.
[30] 俞乃琪,张敏,樊仕宝,等.深圳市城市区域内典型生境特征溪流大型底栖动物群落结构比较 [J].应用与环境生物学报, 2022,28(4): 1034-1041. Yu N Q, Zhang M, Fan S B, et al. Comparison of macroinvertebrate community structure in urban (Shenzhen City) streams with typical habitat characteristics [J]. Chinese Journal of Applied and Environmental Biology, 2022,28(4):1034-1041.
[31] 李正飞,蒋小明,王军,等.雅鲁藏布江中下游底栖动物物种多样性及其影响因素 [J].生物多样性, 2022,30(6):123-135. Li Z F, Jiang X M, Wang J, et al. Species diversity and driving factors of benthic macroinvertebrate assemblages in the middle and lower reaches of the Yarlung Zangbo River [J]. Biodiversity Science, 2022,30(6):123-135.
[32] 张晓可,宣昊,王慧丽,等.青弋江流域不同级别河流底栖动物群落结构研究 [J].长江流域资源与环境, 2014,23(12):1659-1664. Zhang X K, Xuan H, Wang H L, et al. Macrozoobenthic community structure in different order streams of the Qingyi River Basin [J]. Resources and Environment in the Yangtze Basin, 2014,23(12):1659- 1664.
[33] 杨俊.河南西峡大鲵省级自然保护区水生生物调查及功能区调整 [D].河南师范大学, 2018. Yang J. Investigated of aquatic biological resources and readjusted of andrias davidianus protected area of Xixia in Henan Province [D]. Henan Normal University, 2018.
[34] Roy A H, Rosemond A D, Paul M J, et al. Stream macroinvertebrate response to catchment urbanisation (Georgia, USA) [J]. Freshwater biology, 2003,48(2):329-346.
[35] Walsh C J. Protection of in-stream biota from urban impacts: minimise catchment imperviousness or improve drainage design? [J]. Marine and Freshwater Research, 2004,55(3):317-326.
[36] Lemly A D. Modification of benthic insect communities in polluted streams: Combined effects of sedimentation and nutrient enrichness [J]. Hydrobiologia, 1982,87:229-245.
[37] 韩静,罗遵兰,孙光,等.潮白河流域大型底栖无脊椎动物多样性与群落格局 [J/OL].生态学杂志, 1-15[2025-02-13]. Han J, Luo Z L, Sun G, et al. Benthic macroinvertebrates diversity and community pattern in Chaobai River Basin, Beijing [J/OL]. Chinese Journal of Ecology, 1-15[2025-02-13].
[38] Atkinson C L, Capps K A, Rugenski A T, et al. Consumer-driven nutrient dynamics in freshwater ecosystems: from individuals to ecosystems [J]. Biological Reviews, 2017,92:2003-2023.
[39] Obester A N, Lusardi R A, Santos N R, et al. The use of umbrella fish species to provide a more comprehensive approach for freshwater conservation management [J]. Aquat Conserv, 2022,32:112-128.
[40] 欧阳力剑,王雷,陈冬,等.不同投喂饵料对大鲵幼体生长性能影响的研究简报 [J].饲料工业, 2013,34(22):13-15. Ouyang L J, Wang L, Chen D, et al. Brief report on the effects of different feeding diets on the growth performance of juvenile Chinese giant salamander [J]. Feed Industry, 2013,34(22):13-15.
[41] 张池莹,陈静怡,卫妮娜,等.中国大鲵及其资源保护和繁育研究概述 [J].生物学教学, 2020,45(8):67-68. Zhang C Y, Chen J Y, Wei N N, et al. Overview of research on Andrias davidianus and its resource conservation and breeding in China. Biology Teaching, 2020,45(8):67-68.
[42] 朱灵红,施诺,俞安然,等.2015~2022年中国大鲵在浙江省的发现记录及保护现状 [J].浙江师范大学学报(自然科学版), 2024,47(4): 428-436. Zhu L H, Shi N, Yu A R, et al. On the recorded discovery incidences from 2015to 2022and protection status of Chinese giant salamander in Zhejiang Province [J]. Journal of Zhejiang Normal University(Natural Sciences), 2024,47(4):428-436.
[43] 蒋万祥,贾兴焕,周淑婵,等.香溪河大型底栖动物群落结构季节动态 [J].应用生态学报, 2009,20(4):923-928. Jiang W X, Jia X H, Zhou S C, et al. Seasonal dynamics of macrozoobenthos community structure in Xiangxi River [J]. Chinese Journal of Applied Ecology, 2009,20(4):923-928.
[44] 蔡永久,姜加虎,张路,等.长江中下游湖群大型底栖动物群落结构及影响因素 [J].生态学报, 2013,33(16):4985-4999. Cai Y J, Jiang J H, Zhang L, et al. Structure of macrozoobenthos in lakes along the Yangtze River and relationships with environmental characteristics [J]. Acta Ecologica Sinica, 2013,33(16):4985-4999.
[45] 杨梅,李新正,徐勇,等.胶州湾潮下带大型底栖动物群落的季节变化 [J].生物多样性, 2016,24(7):820-830. Yang M, Li X Z, Xu Y, et al. Seasonal variations in macrobenthic communities in the subtidal zones of Jiaozhou Bay [J]. Biodiversity Science, 2016,24(7):820-830.
[46] Carvalho LK, Farias R L, Medeiros E S F. Benthic invertebrates and the habitat structure in an intermittent river of the semi-arid region of Brazil [J]. Neotropical Biology & Conservation, 2013,8(2):57-67.
[47] 渠晓东,曹明,邵美玲,等.雅砻江(锦屏段)及其主要支流的大型底栖动物 [J].应用生态学报, 2007,18(1):158-162. Qu X D, Cao M, Shao M L, et al. Macrobenthos in Jinping reach of Yalongjiang River and its main tributaries [J]. Chinese Journal of Applied Ecology, 2007,18(1):158-162.
[48] Laursen S K, Hamerlik L, Moltesen K, Christoffersen K, Jacobsen D. Diversity and composition of macroinvertebrate assemblages in high-altitude Tibetan streams [J]. Inland Waters, 2015,5:263-274.
[49] 任海庆,袁兴中,刘红,等.环境因子对河流底栖无脊椎动物群落结构的影响 [J].生态学报, 2016,35(10):3148-3156. Ren H Q, Yuan X Z, Liu H, et al. The effects of environment factors on community structure of benthic invertebrate in rivers [J]. Acta Ecologica Sinica, 2016,35(10):3148-3156.
[50] Nelson S M. Response of stream macroinvertebrate assemblages to erosion control structures in a wastewater dominated urban stream in the southwestern US [J]. Hydrobiologia, 2011,663(1):51-69.
[51] Jacobsen D, Rostgaard S, Vásconez J J. Are macroinvertebrates in high altitude streams affected by oxygen deficiency? [J]. Freshwater Biology, 2003,48,2025-2032.
[52] GB3838-2002地表水环境质量标准: [S]. GB3838-2002 Environmental quality standard for surface water [S].
[53] Heino J. Environmental heterogeneity, dispersal mode, and co- occurrence in stream macroinvertebrates [J]. Ecology and Evolution, 2013,3:344-355.
[54] Milesi SV, Dolédec S, Melo AS. Substrate heterogeneity influences the trait composition of stream insect communities: An experimental in situ study [J]. Freshwater Science, 2016,35:1321-1329.
[55] 李亚芳,杜飞雁,王亮根,等.底质类型对三亚湾潮间带大型底栖动物生态功能的影响 [J].水产学报, 2018,42(10):1559-1571. Li Y F, Du F Y, Wang L G, et al. Effects of the sediment type on ecological functions of macrobenthos in the intertidal zones of Sanya Bay [J]. Journal of Fisheries of China, 2018,42(10):1559-1571.
[56] Ormerod S J, Edwards R W. The ordination and classification of macroinvertebrate assemblages in the catchment of the River Wye in relation to environmental factors [J]. Freshwater Biology, 1987,17(3): 533-546.
[57] Jiang X, Xie Z, Chen Y. Longitudinal patterns of macroinvertebrate communities in relation to environmental factors in a Tibetan-Plateau River system [J]. Quaternary International, 2014,304:107-114.
[58] 李正飞,王军,谢志才,等.南腊河底栖动物多样性与环境因子的关系 [J].生态学杂志, 2016,35(12):3364-3373. Li Z F, Wang J, Xie Z C, Ding C Z, et al. Relationship between zoobenthos biodiversity and environmental factors in Nanla River [J]. Chinese Journal of Ecology, 2016,35(12):3364-3373.
[59] 段学花,王兆印,程东升.典型河床底质组成中底栖动物群落及多样性 [J].生态学报, 2007,(4):1664-1672. Duan X H, Wang Z Y, Cheng D S. Benthic macroinvertebrates communities and biodiversity in various stream substrata [J]. Acta Ecologica Sinica, 2007,(4):1664-1672.
[60] Heino J. Does dispersal ability affect the relative importance of environmental control and spatial structuring of littoral macroinvertebrate communities [J]. Oecologia, 2013,171:971-980.
[61] Li F, Tonkin J D, Haase P. Dispersal capacity and broad-scale landscape structure shape benthic invertebrate communities along stream networks [J]. Limnologica, 2018,71:68-74.
[62] Landeiro V L, Bini L M, Melo A S, et al. The roles of dispersal limitation and environmental conditions in controlling caddisfly (Trichoptera) assemblages [J]. Freshwater Biology, 2012,57(8):1554- 1564.
[63] Heino J, Melo AS, Siqueira T, et al. Metacommunity organization, spatial extent and dispersal in aquatic systems: Patterns, processes and prospects [J]. Freshwater Biology, 2015,60(5):845-869.
基金
“广东连南大鲵省级自然保护区-保护对象专项调查项目”资助 (ZHCG2023-101); “珠江流域渔业资源与栖息地调查”专项