人工濕地強(qiáng)化技術(shù)及其效能研究
[Abstract]:The removal of nutrients (such as nitrogen and phosphorus) during the actual operation of the constructed wetland is unstable (especially when the temperature is reduced), which limits the large-scale popularization and application of the constructed wetland in China. Therefore, it is very important to study the ability of artificial wetland to remove pollutants from waste water, especially nitrogen and phosphorus. Through the establishment of different strengthening measures to improve the operation performance of the artificial wetland, the research shows that the application of the corn stalk, the iron-carbon micro-electrolysis matrix in the artificial wetland and the water circulation of the upstream flow mode can improve the running performance of the artificial wetland through the establishment of different strengthening measures. The research results provide technical support for perennial stable operation of artificial wetland, which is of great significance to the treatment of sewage in China and improvement of ecological environment. The main conclusions are as follows: (1) The operation performance of artificial wetland is obviously improved by using intermittent aeration for 12h per day, and the ammonia nitrogen (93.9%), total nitrogen (95.4%) and COD removal rate (92.8%) are obviously higher than that of non-aeration artificial wetland. 11. 0%, 12. 2% and 20. 7% higher than that of the unaerated artificial wetland, respectively. Under the condition of different C/ N ratio, the removal rate of ammonia nitrogen was 98. 4-100%, and the removal efficiency of ammonia nitrogen was not obviously decreased. However, the removal rate of COD in aeration system decreased with the increase of C/ N ratio. The study shows that the intermittent aeration for 12h per day is suitable for the treatment of sewage between C/ N and 3. 1-9. 2. When the temperature drops, the removal rate of ammonia nitrogen and COD in the artificial wetland is not obviously decreased, and the removal rate of ammonia nitrogen and COD is above 97. 7% and 80. 7-98. 0%, respectively. The removal rate of ammonia nitrogen and COD in the unaerated wetland system was greatly influenced by temperature, the removal rate of ammonia nitrogen decreased by 2.9%-11.2%, and the COD removal rate was 43. 4-75. 2%. The results of the above study indicate that the removal effect of artificial wetland can be enhanced by intermittent aeration for 12 hours per day, and better operation performance can be maintained when the temperature is reduced. (2) adding sustained-release carbon source in the artificial wetland can improve the denitrification rate of the artificial wetland. The results of different total nitrogen concentration show that the ammonia nitrogen and total phosphorus removal rate of all artificial wetland are maintained at 87. 4% and 91%, respectively. However, as the total nitrogen concentration is increased to 172.2mg/ L, the removal rate of nitrate nitrogen in artificial wetland decreases. The removal rates of nitrate and nitrogen from corn cobs, wood blocks and blank artificial wetland decreased to 86.8, 84.7 and 76.2% respectively, but the removal rate of nitrate nitrogen in maize straw artificial wetland was still higher (92.1%). The experimental study on temperature effect showed that the removal rate of ammonia nitrogen and total nitrogen in artificial wetland was decreased when the temperature of artificial wetland was decreased, but higher ammonia nitrogen, nitrate nitrogen and total nitrogen removal rate could still be maintained. In particular, the removal rates of ammonia nitrogen, nitrate nitrogen and total nitrogen were maintained at 89. 7%, 81. 0% and 82.8%, respectively, when the total nitrogen concentration was increased to 179. 2mg/ l. According to the above research results, the denitrification process can be accelerated to a certain extent by adopting a slow-release carbon source addition (especially corn straw), so that the denitrification rate of the artificial wetland can be improved, especially when the temperature is reduced, good running performance can be maintained, and is very suitable for the treatment of high total nitrogen concentration wastewater. (3) The artificial wetland of the iron-carbon micro-electrolysis substrate has strong total phosphorus adsorption capacity, and when the total phosphorus concentration of the water is increased to 32.8mg/ l, the total phosphorus removal rate of the artificial wetland can still be maintained at 96. 6%, meanwhile, the artificial wetland also has higher ammonia nitrogen, nitrate nitrogen, total nitrogen and cod removal rate. The experimental study shows that the total phosphorus removal rate of artificial wetland is less affected by temperature (total phosphorus removal rate is above 96.0%), but the removal rate of ammonia nitrogen, nitrate nitrogen and total nitrogen will fluctuate with temperature. The removal rate of ammonia nitrogen, nitrate nitrogen, total nitrogen and cod is also high, 82.8% and 81.9% respectively. 85. 8 and 80. 3%. At the same time, the COD removal rate was higher (83.8%), but also higher ammonia nitrogen (92.9%), nitrate nitrogen (94.1%), total nitrogen (95.2%) and total phosphorus (95.3%). When the concentration of nitrate nitrogen rises to 75. 8mg/ l, the iron-carbon micro-electrolysis artificial wetland can also remove nitrate nitrogen very well (the removal rate is over 92.4%), the above research results show that the iron-carbon micro-electrolysis substrate is not only suitable for the treatment of high total phosphorus concentration wastewater, and is also suitable for the treatment of organic matter concentration and high nitrate nitrogen concentration wastewater. (4) The upstream artificial wetland has excellent running performance, with the highest ammonia nitrogen (99. 7%), nitrate nitrogen (87.2%), total nitrogen (93.1%), total phosphorus (95.4%) and cod (87.7%) removal rate, followed by the second place in the downstream flow, and the rest flow artificial wetland has the worst performance. The experimental results show that the operating performance of the constructed wetland is influenced by the temperature, especially the downstream, parallel flow and static flow artificial wetland are affected by the temperature, but the upstream artificial wetland is less affected by the temperature with respect to the other artificial wetland. The removal rates of ammonia nitrogen, nitrate nitrogen, total nitrogen, total phosphorus and cod were 94.8%, 66.7%, 78.4%, 95.8% and 77.9% respectively. In general, the application of slow-release carbon source (especially maize straw), iron-carbon micro-electrolysis substrate and intensified measure adopting upstream flow can well enhance the operation performance of artificial wet land by adopting intermittent aeration for 12h/ day, adding slow-release carbon source (especially maize straw). especially when the temperature is reduced. In addition, the research results can provide reference basis for selecting appropriate strengthening measures according to different wastewater characteristics in the practical application of artificial wetland.
【學(xué)位授予單位】:中國(guó)科學(xué)院大學(xué)(中國(guó)科學(xué)院東北地理與農(nóng)業(yè)生態(tài)研究所)
【學(xué)位級(jí)別】:博士
【學(xué)位授予年份】:2017
【分類號(hào)】:X703
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