广州流溪河与生态修复塘底栖动物群落结构特征及生态健康评估
[Abstract]:Liu Xi River is located in the northwest of Conghua District of Guangzhou city. As an important source of drinking water protection in Guangzhou City, its water quality has a vital role in the safety of drinking water source in Guangzhou. Therefore, the long-term monitoring and health assessment of the river water environment in the convective river is the basic guarantee for the maintenance of the health of the citizens of Guangzhou and the protection of the river. As an important way of aquatic organisms, as the key biological element of the river ecosystem, the species composition and community structure of the benthic animal (Zoobenthos) are closely related to water environmental factors, and because of their long life, weak migration ability and sensitivity to reaction, the assessment of water environment health by benthic animals in recent years has become an ecological study. Liu Xi River is a typical subtropical climate zone, and the distribution and ecosystem in the basin have strong regional characteristics. In addition, influenced by the rapid development of the city, the natural environment in the basin is increasingly disturbed by human disturbance. In view of this, the community structure of the convection stream and benthic animals is studied in the field. The internal relationship between water environmental factors and the structure of benthic animal community in the basin was analyzed from time and space, and the ecological health status of the convective river ecosystem was evaluated comprehensively by the construction of the benthic animal integrity index (B-IBI) system. This study enriches the basic data of benthic Zoobenthos in large and medium rivers in Southern China and provides a model reference for the river biological evaluation method with benthic animals as the core. The main results and conclusions of this paper are as follows: (1) in 2016 (April) The water quality of the 14 river sections of the river river in the flood season (July) and the low water period (October) was investigated. The water quality of the 14 reaches of the Guangzhou river was gradually changed from the upstream source to the lower reaches (EC 40.8-327.7 mg/L, EC 40.8-327.7 s/cm, TN 0.11-6.46 mg/L, NH4+-N 0.04-5.29 mg/L). The water quality of the upstream source of the river is low, the water quality is I-II water standard, and the water quality of the tributaries is better than the main stream. To the lower reaches, the sewage discharge and the industrial pollution are increased, the water quality is reduced to the IV-V water standard, and the water quality is superior to the tributaries. (2) 144 species of benthic animals were found, belonging to 134 genera, 52 families, 4 doors, 8 classes, 22 orders, and benthic animals. The average density and biomass of 217.35 ind./m2 and 20.38 g/m2. were the highest in the upper reaches of the upstream species. The number of species represented by the genus Andromeda and four is the dominant species, and the number of species decreased gradually in the lower reaches, and the pollution resistant groups represented by the water worms were dominant. The diversity index difference showed that the number of upstream species was more abundant than the downstream. The correlation analysis between the indexes of benthos and the environmental parameters showed that the density of benthic animals in April was negatively correlated with DO, and was positively correlated with CODMn; the density of Zoobenthos in July was positively correlated with BOD5 (P0.05), and the density of benthic animals in October showed a significant difference with EC. The results showed that the environmental factors affecting the distribution of benthic animals in different periods were different, and on the whole, the upstream to downstream, with the decrease of DO content, the increase of EC and nutrient content, the diversity of benthic animals were negatively affected. (3) there were 19 species of scrapers and 10 tearing predators in the stream stream. There are 64 species of collector, 10 species of filter collector and 41 predator. The total average density of each feeding group is 5-2098 ind./m2, the most of the direct collector and the tearing person are the least. The total average biomass is 0.05-228.28 g/m2, the most of the shavers and the tearing is the least. On the space scale, the decrease of the whole number of functional feeding groups is mainly by the rip and filter. The influence of the food collector was reduced and the pollution of the lower reaches was aggravated. Only the.5 functional groups were found in the tributaries with only the oligohairs (water silk worms). There were only 4 main streams in the main stream, indicating that the missing tearing is an important indicator of the water quality and habitat degradation. The species composition, diversity, and density of biomass were significantly reduced, indicating that the current river ecosystem was affected seriously by the decline of water quality and the degradation of coastal habitat. (4) the 5 core indexes of the B-IBI evaluation system in the stream River, including biomass, EPT, chironomid and pollution resistant groups The health standards are as follows: B-IBI value 3.24 is healthy; 3.24-2.43 is subhealth; 2.43-1.62 is general; 1.62-0.81 is poor; 0.81-0 is the worst. The number of health points in the basin is 14.3%, the sub health accounts for 50%. Generally, the number of 21.4%.EPT taxa and the sensitive group individual% contribute the highest to the B-IBI value of the upstream river, which reflects healthy condition and tolerance. The number of contaminated group units has the highest contribution to the B-IBI value of the lower reaches, reflecting a significant positive correlation between the.B-IBI value of the health deterioration and the concentration of dissolved oxygen (P0.01), which is negatively correlated with the total nitrogen, ammonia nitrogen, total phosphorus concentration and electrical conductivity value (P0.05). The evaluation results show that, as a typical urban river, the middle and lower reaches of the fluvial river are disturbed by human interference. The ecological health condition worsened, especially the downstream dry, and the benthic Zoobenthos Community declined seriously in the branch river section. The application results from different geographical regions found that the B-IBI system had good applicability in the tropical and subtropical regions. (5) the restoration of benthic animals for the restoration of submerged plants and the restoration of benthic animals There are 11 species of benthic animals, belonging to 3 families, 4 classes, 6 orders, 9 families and 10 genera. Before the submerged plants are planted, there are only 4 species of benthic animals. After half a year, 11 species can be collected. The results of correlation analysis show that NH4+-N, TP, CODcr and Chl.a have significant influence on the community structure of benthic animals, indicating the improvement of water quality in the pond. On the whole, the number, biomass and species diversity of benthic animals were significantly increased after the restoration of submerged plants, and there was a significant positive correlation with the changes in the biomass of submerged plants (P0.05), indicating that the water quality of the plant has obviously improved the water quality in the demonstration project area. And biological condition.
【学位授予单位】:暨南大学
【学位级别】:硕士
【学位授予年份】:2017
【分类号】:X826;Q958.8
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