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Characteristics of zoobenthos community in constructed wetlands in subtropical hilly area |
GUO Ning-ning1,2, LI Xi1,3, ZHOU Xun-jun1,3, YE Lei1,4, MENG Cen1,3, XIA Meng-hua1,3, PENG Jian1,3, JIANG Lei1,3, Lü Dian-qing2,5, LI Yu-yuan1,3, WU Jin-shui1,3 |
1. Key Laboratory of Agro-ecological Processes in Subtropical Region, Institute of Subtropical Agroecology, Chinese Academy of Sciences, Changsha 410125, China; 2. School of Resources and Environmental Sciences, Hunan Normal University, Changsha 410006, China; 3. School of Water Conservancy and Civil Engineering, Hunan Agricultural University, Changsha 410128, China; 4. University of Chinese Academy of Sciences, Beijing 100049, China; 5. School of Chemical and Environmental Engineering, Jiangsu University of Technology, Changzhou 213001, China |
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Abstract Subtropical hilly area, Changsha, Hunan Province was selected as the experimental area in the study. The main aim was to treat rural comprehensive sewage (including livestock breeding wastewater, rural domestic sewage and farmland drainage). Through field experiment, this study was set up four treatments:Pontederia cordata, Myriophyllum elatinioides, Pontederia cordata + Myriophyllum elatinioides and CK constructed wetland. Sediment samples were collected in April, July, October and December, 2019. Seasonal variation characteristics of species composition, dominant species, abundance, biomass and diversity of zoobenthos in different plants constructed wetland were studied. The relationship between diversity of zoobenthos and environmental factors was also discussed. Results showed that 27species of zoobenthos were found in four seasons, aquatic insects dominated (22species). Limnodrilus hoffmeisteri, Branchiura sowerbyi and Chironomus flaviplumus were common species in four seasons. Annual average abundance and biomass of zoobenthos in P. cordata + M. elatinioides constructed wetlands were 522ind/m2 and 52.1g/m2, respectively, which were the lowest, compared to single plant constructed wetland. Annual average abundance and biomass of zoobenthos in CK constructed wetlands were 3665ind/m2 and 146.3g/m2, respectively, which were the highest, compared to other treatments. The Shannon-Wiener diversity index (H'), Margalef richness index (d) and Pielou evenness index (J) of zoobenthos in summer and autumn were higher than those in spring and winter. In spring, Margalef richness index in CK and P. cordata constructed wetland were significantly higher than that in the other constructed wetlands (P<0.05). In summer, Pielou evenness index in CK constructed wetland was significantly lower than that in plants constructed wetland (P<0.05), while in winter, Margalef richness index in P. cordata, P. cordata+M. elatinoides constructed wetland were significantly higher than that in the other constructed wetlands (P<0.05). Spearman correlation analysis showed that the species number of zoobenthos were significantly positively correlated with pH (P<0.05). and abundance of zoobenthos were negatively correlated with DO, while abundance of zoobenthos were positively correlated with other environmental factors (P<0.05). RDA analysis further showed that DO was the major environmental factor, influencing Gastropoda, while Oligochaeta and chironomid larvae were affected by environmental factor as TN and COD.
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Received: 15 July 2020
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