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循环水养殖池塘中浮游动植物功能群特征及水质评价

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为研究循环水养殖模式对水生态环境的中长期影响和浮游动、植物群落的演替规律及相互作用,2018 和2019 年 3 月下旬,在湖南长沙新建的 12.7 hm2 池塘中修建 24 条长 22 m、宽 5 m、深 2.7 m的两端有推水、底部有集污设施的养殖水槽中,放养 2、3 龄的鲢(Hypophthalmichthys molitrix)、鳙(Aristichthys nobilis)、草鱼(Ctenopharyngodon idella)、鲤(Cyprinus carpio),密度分别为 1 200 kg·hm-2、600 kg·hm-2、120 kg·hm-2 和 480 kg·hm-2.在水槽中设 9 个采样点:推水设施区、养殖水槽中和水槽下游区各 3 个,调查分析循环水养殖模式刚投入使用和养殖一年后水质理化因子变动规律及浮游动植物群落结构变化.结果显示:浮游动植物种类与功能群数量变化较小,各功能群的相对重要性指数(IRI)变化剧烈;浮游植物优势功能群由功能群E(锥囊藻)、D(针杆藻)变化为功能群TD(丝状绿藻)、J(盘星藻、栅藻),演替原因为水流频繁紊动引起水层混合的空间差异;浮游动物优势功能群由功能群PSF(浮游小型滤食者)、PMF(浮游微型滤食者)变化为功能群PMF、PLF(浮游大型滤食者)及PSP(浮游小型捕食者),表现出更具生态稳定性的浮游动物大型化趋势,滤食性鱼类放养密度低是其重要原因;小体型滤食类浮游动物主要受耐富营养、带鞭毛、较小体型浮游植物的促进作用,在此基础上,大体型滤食类浮游动物还受到附着绿藻及适应中营养生境的硅藻等促进作用;浮游植物功能群G(空球藻)、W1(尖尾、梭形裸藻)和X(球粒藻、衣藻、小球藻)对捕食类浮游动物的促进作用既包括上行效应直接传导,也包括以小型滤食类浮游动物为食物链环节的间接传导;循环水养殖一年后,各点位水质的空间差异进一步加大,但该池塘仍处于轻-中污染状态,符合养殖水质标准且整体较稳定.
Characteristics of Zooplankton and Phytoplankton Functional Groups and Evaluation of Water Quality in Recirculating Aquaculture Ponds
In order to probe into the medium-and long-term effects of circulating aquaculture mode on aquatic ecological environment and the succession and interaction of plankton and plant communities,the changes in physical and chemical factors of water quality and the structure of plankton and plant communities were investigated and analyzed in 9 sampling points at water pushing facility area,aquaculture tank and in the downstream area of 24 breeding gutters with 22 m long,5 m wide and 2.7 m deep with pushing water at both ends and sewage collection facilities at the bottom in a 12.7 hm2 tank stocked with 2 or 3 years old silver carp(Hypophthalmichthys molitrix)at stocking density of 1 200 kg·hm-2,bighead carp(Aristichthys nobilis)at stocking density of 600 kg·hm-2,grass carp(Ctenopharyngodon idella)at stocking density of 120 kg·hm-2 and common carp(Cyprinus carpio)at stocking density of 480 kg·hm-2 in late March of 2018 and 2019 to investigate aquatic ecological environment and the succession and interaction of plankton at the initial stage of the circulating aquaculture mode and one year after the culture.The results showed that there was little change in number of phytoplankton species and functional groups,with sharp change in relative importance index(IRI)in each functional group.The dominant functional groups of phytoplankton were shown to be changed from functional groups E and D to functional groups TD and J,and the succession was derived from the spatial difference of water layer mixing caused by frequent turbulence of water flow.The dominant functional groups of zooplankton were changed from functional groups PSF and PMF to functional groups PMF,PLF and PSP,showing a trend of zooplankton enlargement with more ecological stability,and the low stocking density of filter-feeding fish may be an important reason for this phenomenon.Small filter-feeding zooplankton was mainly promoted by nutrient-tolerant,flagellated and small sized phytoplankton.On this basis,large filter-feeding zooplankton were also promoted by attached green algae and diatoms adapted to medium trophic habitats.The promotion effect of phytoplankton functional groups G,W1 and X on predatory zooplankton includes both direct conduction of upward effect and indirect conduction with small filter-feeding zooplankton as the link of the food chain.After one year of recirculating aquaculture,the spatial difference of water quality at each point was further increased,but the pond was still in the state of light-medium pollution,which met the aquaculture water quality standard and was stable as a whole.

recirculating aquaculturephytoplanktonzooplanktonfunctional groupswater quality evaluation

向劲、吴启藩、宋锐、彭治桃、李金龙、高峰、谢敏、程小飞

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湖南省水产科学研究所,湖南 长沙 410153

湖南省水产原种场,湖南 长沙 410153

循环水养殖 浮游植物 浮游动物 功能群 水质评价

湖南省科技重大专项国家大宗淡水鱼产业技术体系建设项目长沙综合试验站项目

2017NK1030CARS-45-47

2024

水产学杂志
中国水产科学研究院 黑龙江水产研究所

水产学杂志

影响因子:0.497
ISSN:1005-3832
年,卷(期):2024.37(1)
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