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作 者:王丽[1] 王保栋[2] 陈求稳[1] 汤新武 韩瑞[4]
机构地区:[1]南京水利科学研究院生态环境研究中心,南京210024 [2]国家海洋局第一海洋研究所,青岛266061 [3]三峡大学,宜昌443002 [4]中国科学院生态环境研究中心,北京100085
出 处:《生态学报》2016年第9期2505-2512,共8页Acta Ecologica Sinica
基 金:国家杰出青年科学基金(51425902);国家重点基础研究发展(973)计划项目(2010CB429004)
摘 要:根据2010年8月、11月以及2011年5月3个航次、各次24个监测点的调查数据,分析了三峡工程三期蓄水后一个水文年内长江口浮游动物优势种、湿重生物量及丰度的变化,并用BIOENV筛选出影响浮游动物分布的关键环境因子。结果表明:长江口浮游动物春季绝对优势种为夜光虫(Noctiluca scientillans)与中华哲水蚤(Calanus sinicus),夏季绝对优势种为太平洋纺锤水蚤(Acartia pacifica steuer),秋季绝对优势种为针刺拟哲水蚤(Paracalanus aculeatus);浮游动物湿重生物量夏季(970.6 mg/m^3)>秋季(613.8 mg/m^3)>春季(571.5 mg/m^3),丰度夏季(783.5个/m^3)>春季(691.3个/m^3)>秋季(399.5个/m^3);影响浮游动物分布的关键环境因子为底层盐度、底层温度及底层硅酸盐。The Three Gorges Dam (TGD) is the largest hydropower project ever built in China and worldwide. In 2010, the TGD reached the designed water level of 175 m, storing approximately 39.3 billion cubic meters of water. Impoundment of the TGD has changed the hydrological and sedimental regimes downstream, which inevitably affected the estuarine ecosystem. Therefore, a comprehensive survey and assessment after the impoundment at 175 m would be helpful for establishing benchmark values for future analyses. Community variations in zooplankton, which are at the middle level of the food chain in aquatic ecosystems, can reflect environmental changes. Therefore, this study investigated the spatial distribution of the zooplankton community and the relationships between zooplankton and environmental factors through biota-environment matching (BIOENV) based on a hydro-environmental and biological survey of the Yangtze estuary in August and November of 2010 and May of 2011. Noctiluca scientillans and Calanus sinicus were the predominant species in spring, and Acartia pacifica respectively. The spatially av autumn (613.8 mg/m^3) steuer and Paracalanus aculeatus were the predominant species in summer and autumn, eraged seasonal biomass and spring ( 571.5 mg/m^3 ) of zooplankton was highest in summer (970.6 mg/m^3) , followed by Similarly, the spatially averaged seasonal abundance of zooplankton was highest in summer ( 783.5 individuals/m^3 ), followed by spring ( 691.3 individuals/m^3 ) and autumn ( 399.5 individuals/m^3 ). Interestingly, the spatial distribution patterns of zooplankton biomass and abundance were consistent in the summer, but not the spring and autumn. The major environmental factors explaining the observed variations in the zooplankton community were temperature in the middle layer, salinity, and silicate (Si) concentrations of the bottom layer in the spring; salinity, Si, and total dissolved nitrogen of the middle layer in the summer ; and temperature of bottom layer, suspende
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