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Study of anaerobic co-digestion on wastewater treatment sludge and food waste leachate using BMP test

机译:利用BMP试验研究废水处理污泥和食品垃圾渗滤液的厌氧共消化。

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The study conducted basic component analyses including three component analyses, elementary analysis and heavy metal content and BMP test according to the mixing ratio for food waste leachate and wastewater treatment sludge(from brewery, dairy factory, bread factory, sewage sludge), and calculated biogas production speed using mathematical models. According to the elementary analysis of organic wastes, the C/N ratio, a major condition for anaerobic digestion, is 5.40-9.23, except for food waste leachate (FWL). Defined by Tchobanoglous' mathematical biogas prediction model, methane gas and biogas productions increased, depending on the mixing rate of FWL. Furthermore, anaerobic digestion of both wastewater sludge and food waste leachate based on the correct mixing ratio, increases methane gas productions compared to digesting wastewater sludge alone. In other words, co-anaerobic digestion is more likely to realize biogasification than single anaerobic digestion. We mixed food waste leachate and wastewater treatment sludge by proportion of 1:9, 3:7, and 5:5, respectively. It turns out that they produced 118, 175, 223 CH4 mL/g VS with the dairy factory, 176, 233, 263 CH(4)mL/g VS with the brewery, 268, 300, 314 CH4 mL/g VS with the bread factory and 233, 298, 344 CH4-mL/g VS with the sewage sludge of methane gas. The result proposes that as the mixing rate of food waste leachate rises, the methane gas production increases as well. In the case of co-digestion of wastewater treatment sludge and food waste leachate based on the mixing ratio, more methane gas is produced compared to single digestion of wastewater treatment sludge. Modified Gompertz and exponential models describe the BMP test results that show how methane gas is produced from organic waste. According to the test, the higher the mixing rate of food waste leachate is, the higher the methane gas production is. The mixing ratio of food waste leachate which produces the largest volume of methane gas is 1:9 for the dairy and bread facilities and 3:7 for brewery and sewage sludge. Modified Gompertz and exponential models describe the test results very well. The correlation values (R-2) that show how close the results of model prediction and experiment are 0.920-0.996.
机译:该研究根据食物垃圾渗滤液和废水处理污泥(来自啤酒厂,乳品厂,面包厂,污水污泥)的混合比例,进行了基本成分分析,包括三个成分分析,元素分析和重金属含量以及BMP测试。使用数学模型提高生产速度。根据有机废物的元素分析,除食物垃圾渗滤液(FWL)外,C / N比(厌氧消化的主要条件)为5.40-9.23。由Tchobanoglous的数学沼气预测模型定义,甲烷气体和沼气产量的增加取决于FWL的混合速率。此外,与单独消化废水污泥相比,基于正确的混合比对废水污泥和食物垃圾渗滤液进行厌氧消化可增加甲烷气体的产量。换句话说,共厌氧消化比单一厌氧消化更可能实现生物气化。我们分别以1:9、3:7和5:5的比例混合食物垃圾渗滤液和废水处理污泥。事实证明,他们通过乳品厂生产118、175、223 CH4 mL / g VS,通过啤酒厂生产176、233、263 CH(4)mL / g VS,通过啤酒厂生产268、300、314 CH4 mL / g VS.面包厂和233、298、344 CH4-mL / g VS,含甲烷气体的污水污泥。结果表明,随着食物垃圾渗滤液混合速率的提高,甲烷气体的产生也随之增加。在基于混合比例共同消化废水处理污泥和食物垃圾渗滤液的情况下,与单消化废水处理污泥相比,会产生更多的甲烷气体。改进的Gompertz模型和指数模型描述了BMP测试结果,该结果显示了如何从有机废物中产生甲烷气体。根据试验,食物垃圾渗滤液的混合速率越高,甲烷气体的产生量越高。牛奶和面包设施中产生最大甲烷气体的食物垃圾渗滤液的混合比为1:9,而啤酒厂和污水污泥的混合比为3:7。改进的Gompertz模型和指数模型很好地描述了测试结果。显示模型预测和实验结果有多接近的相关值(R-2)为0.920-0.996。

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