长江流域资源与环境 >> 2015, Vol. 24 >> Issue (12): 2054-2060.doi: 10.11870/cjlyzyyhj201512008

• 自然资源 • 上一篇    下一篇

大型浅水湖泊太湖霍甫水丝蚓次级生产力的研究

龚志军1, 李艳2, 张敏3, 蔡永久1, 薛庆举1, 许浩1   

  1. 1. 中国科学院南京地理与湖泊研究所湖泊与环境国家重点实验室, 江苏 南京 210008;
    2. 国信招标集团股份有限 公司河南分公司, 河南 郑州 450000;
    3. 江苏省洪泽湖水利工程管理处, 江苏 淮安 223100
  • 收稿日期:2015-08-02 修回日期:2015-11-02 出版日期:2015-12-20
  • 作者简介:龚志军(1974~),男,副研究员,博士,主要从事底栖动物生态学研究:E-mail:zjgong@niglas.ac.cn.
  • 基金资助:
    国家自然科学基金重点项目(41230744,31270505)、中国科学院南京地理与湖泊研究所"一三五"重点部署项目( NIGLAS2012135002)联合资助.

A STUDY ON SECONDARY PRODUCTION OF LIMNODRILUS HOFFMEISTERI CLAPARÈDE IN A LARGE SHALLOW LAKE, LAKE TAIHU

GONG Zhi-jun1, LI Yan2, ZHANG Min3, CAI Yong-jiu1, XUE Qing-ju1, XU Hao1   

  1. 1. Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, China;
    2. Guoxin Tendering Group, Henan Branch, Zhengzhou 450000, China;
    3. Administrative Agency for Water Conservancy Projects of Hongze Lake, Huai'an 223100, China
  • Received:2015-08-02 Revised:2015-11-02 Online:2015-12-20

摘要: 作为湖泊底栖动物优势种类的霍甫水丝蚓在长江中下游湖泊分布广泛,在湖泊生态系统的能流和物流中占有十分重要的地位。为了了解霍甫水丝蚓在大型浅水湖泊中的种群动态规律、生活史和周年生产量等的状况,于2005年1~12月对太湖霍甫水丝蚓进行周年的研究,以期为了解太湖这一优势种类的生产力状况及合理利用这一资源提供理论依据。研究发现,2005年太湖霍甫水丝蚓年均密度和生物量分别为 3 274 ind./m2(0 ~13 800 ind./m2)和4.70 g/m2(0 ~29.15 g/m2),一般均在冬季达到高峰,空间分布上霍甫水丝蚓密度和生物量呈现出明显的差异性,在太湖北部梅梁湾和竺山湾及西部河口湖区分布较高,而在其它区域的现存量均较低。根据体长频数分布的周年变化特征,推测太湖霍甫水丝蚓约为一年三代,繁殖可能发生在3、7和11月份期间。2005年太湖霍甫水丝蚓年生产量为480.21 g·m-2·yr-1,P/B为14.17,与同类研究报道相比属于较高水平。分析表明太湖霍甫水丝蚓的高世代数导致其高P/B系数,而高周年生产量与其所处的营养水平相对较高有关,这对于太湖渔产潜力具有显著意义。

关键词: 霍甫水丝蚓, 次级生产力, 生活史, 种群动态, 太湖

Abstract: Limnodrilus hoffmeisteri Claparède, a dominant species of zoobenthos, is widely distributed in shallow lakes of the middle and lower basin of the Yangtze River, and it plays an important role in the energy flow and biogeochemistry cycling of the lake ecosystem. To understand population dynamics, life history and production of L.hoffmesteri in the large shallow lake, field investigation were conducted in Lake Taihu during January to December, 2015. The annual average density and biomass of this worm were 3 273.75 ind./m2 (0-13 800 ind./m2) and 4.70 g/m2 (0-29.15 g/m2), respectively, all of which peaked in winter. The highest population density and biomass of L.hoffmeisteri were found in Meiliang Bay, Zhushan Bay and western river-mouth, while the other place of the lake had very lower worm density. According to the annual dynamics of the frequency distributions of body length, the species had three generations one year and reproduced in March,July and November. The annual P/B ratio was 14.17, which was due to high generations one year. The corresponding annual production of the animal calculated by size-frequency method was 480.21 g·m-2·yr-1 in wet weight, and was highest in studies reported, which is significant for potential fishery capacity in Lake Taihu.

Key words: Limnodrilus hoffmesteri Claparède, secondary production, life history, population dynamics, Lake Taihu

中图分类号: 

  • Q958
[1] ANDERSON T J, STELZER R, DRECKTRAH H G, et al. Secondary production of Chironomidae in a large eutrophic lake: implications for lake sturgeon production[J]. Freshwater Science, 2012, 31(2): 365-378.
[2] BENKE A C. Concepts and patterns of invertebrate production in running waters[J]. Verhandlungen des Internationen Verein Limnologie, 1993, 25: 15-38.
[3] WALLACE J B,BENKE A C, LINGLE A H, et al. Trophic pathways of macroinvertebrate primary consumers in subtropical black water streams[J]. Archiv für Hydrobiologie, 1987, 74(Suppl.): 423-451.
[4] BENKE A C. Secondary production of macroinvertebrates[M]//RICHARD HAUER F, LAMBERTI G A. Methods in Stream Ecology. London: Academic Press, 1996: 557-578.
[5] BENKE A C, WALLACE J B. Trophic basis of production among riverine caddisflies: implications for food web analysis[J]. Ecology, 1997, 78(4): 1132-1145.
[6] 秦伯强,胡维平,陈伟民.太湖水环境演化过程与机理[M].北京:科学出版社,2004.
[7] HAMILTON A L, HYNES H B N. On estimating annual production[J]. Limnology and Oceanography, 1969, 14(5): 771-782.
[8] JOHNSON M G, BRINKHURST R O. Associations and species diversity in benthic macroinvertebrates of Bay of Quinte and Lake Ontario[J]. Journal of the Fisheries Research Board of Canada, 1971, 28(11): 1683-1697.
[9] MACIOROWSKI A F, BENFIELD E F, HENDRICKS A C. Species composition, distribution, and abundance of oligochaetes in the Kanawha River, West Virginia[J]. Hydrobiologia, 1977, 54(1): 81-91.
[10] LANG C. Factorial correspondence analysis of Oligochaeta communities according to eutrophication level[J]. Hydrobiologia, 1978, 57(3): 241-247.
[11] RABURU P, MAVUTI K M, HARPER D M, et al. Population structure and secondary productivity of Limnodrilus hoffmeisteri (Claparede) and Branchiura sowerbyi Beddard in the profundal zone of Lake Naivasha, Kenya[J]. Hydrobiologia, 2002, 488(1): 153-161.
[12] 黄漪平.太湖水环境及其污染控制[M].北京:科学出版社,2001.
[13] 李 江,金相灿,姜 霞,等. 太湖不同营养水平湖区沉积物理化性质和磷的垂向变化[J].环境科学研究,2007,20(4):64-69.
[14] ANLAUF K J, MOFFITT C M. Models of stream habitat characteristics associated with tubificid populations in an intermountain watershed[J]. Hydrobiologia, 2008, 603(1): 147-158.
[15] RODRIGUEZ P, MARTINEZ-MADRID M, ARRATE J A, et al. Selective feeding by the aquatic oligochaete Tubifex tubifex (Tubificidae, Clitellata)[J]. Hydrobiologia, 2001, 463(1/3): 133-140.
[16] BIRTWELL I K. Eco-physiological aspects of tubificids in the Thames Estuary[M]. London: King's College, 1974.
[17] LAZIM M N, LEARNER M A. The influence of sediment composition and leaf litter on the distribution of tubificid worms (Oligochaeta)[J]. Oecologia, 1987, 72(1): 131-136.
[18] MOSS B, TIMMS M. Predation, sediment stability and food availability as determinants of the benthic invertebrate fauna in two shallow lakes[J]. Hydrobiologia, 1989, 185(3): 249-257.
[19] 龚志军,谢 平,唐汇涓,等.水体富营养化对大型底栖动物群落结构及多样性的影响[J].水生生物学报,2001,25(3):210-216.
[20] VOLPERS M. NEUMANN D. Tolerance of two tubificid species (Tubifex tubifex and Limnodrilus hoffmeisteri) to hypoxic and sulfidic conditions in novel, long-term experiments[J]. Archiv für Hydrobiologie, 2005, 164(1): 13-38.
[21] CAI Y J, JIANG J H, ZHANG L, et al. Simplification of macrozoobenthic assemblages related to anthropogenic eutrophication and cyanobacterial blooms in two large shallow subtropical lakes in China[J]. Aquatic Ecosystem Health & Management, 2012, 15(1): 81-91.
[22] 胡忠军,孙月娟,刘其根,等.浙江千岛湖深水区大型底栖动物时空变化格局[J].湖泊科学,2010,22(2):265-271.
[23] 刘曼红,马成学,左彦东,等.镜泊湖大型底栖动物群落调查[J].水生生态学报,2009,2(4):1-7.
[24] 王银东,熊邦喜,杨学芬.武汉市南湖大型底栖动物的群落结构[J].湖泊科学,2005,17(4):327-333.
[25] 王丑明,谢志才,宋立荣,等.滇池大型无脊椎动物的群落演变与成因分析[J].动物学研究,2011,32(2):212-221.
[26] 高 峰,尹洪斌,胡维平,等.巢湖流域春季大型底栖动物群落生态特征及与环境因子关系[J].应用生态学报,2010,21(8):2132-2139.
[27] BRINKHURST R O. Observations on the biology of lake-dwelling Tubificidae[J]. Archiv für Hydrobiologie, 1964, 60: 385-418.
[28] 杞 桑.广州地区水栖寡毛类霍夫水丝蚓的繁殖周期[J].暨南大学学报(自然科学),1992,13(3):68-71.
[29] KENNEDY C R. The life history of Limnodrilus hoffmeisteri Clap. (Oligochaeta: Tubificidae) and its adaptive significance[J]. Oikos, 1966, 17(2): 158-168.
[30] LAZIM M N, LEARNER M A. The life-cycle and productivity of Tibifex tubifex (Oligochaeta; Tibificidae) in the Moat-Feeder Stream, Cardiff, South Wales[J]. Ecography, 1986, 9(3): 185-192.
[31] POTTER D W B. LEARNER M A. A study of the benthic macroinvertebrates of a shallow eutrophic reservoir in South Wales with emphasis on the Chironomidae (Diptera); their life-histories and production[J]. Archiv für Hydrobiologie, 1974, 74: 186-226.
[32] 闫云君,梁彦龄.草型湖泊与藻型湖泊大型底栖动物生产力的比较[J].湖泊科学,2004,16(1):81-84.
[33] WATERS T F. Secondary production in inland waters[J]. Advances in Ecological Research, 1977, 10: 91-164.
[34] BENKE A C. Secondary production of aquatic insects[M]//RESH V H, ROSENBERG D M. The ecology of aquatic insects. New York: Praeger Publishers, 1984: 289-322.
[35] TEAL J M. Community metabolism in a temperate cold spring[J]. Ecological Monographs, 1957, 27(3): 283-302.
[36] LIANG Y L. Annual production of Branchiura sowerbyi (Oligochaeta: Tubificidae) in the Donghu Lake, Wuhan, China[J]. Chinese Journal of Oceanology and Limnology, 1984, 2(1): 102-108.
[37] MARTINET F, JUGET J, RIERA P. Carbon fluxes across water, sediment and benthos along a gradient of disturbance intensity: adaptive responses of the sediment feeders[J]. Archiv für Hydrobiologie, 1993, 127(1): 39-56.
[38] LAFONT M. Production of Tubificidae in the littoral zone of Lake Léman near Thonon-les-Bains: a methodological approach[J]. Hydrobiologia, 1987, 155(1): 179-187.
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