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市政污泥处理处置工艺碳排放核算及碳减排路径OA

Carbon Emission Accounting and Reduction Path of Municipal Sludge Treatment and Disposal Processes

中文摘要英文摘要

[目的]目前,我国已经形成了深度脱水-填埋、好氧发酵-土地利用、厌氧消化-土地利用、干化焚烧-建材利用这4条主流的市政污泥处理处置工艺路线,每种工艺路线都有各自的优缺点和适用条件,但每种路线的碳排放水平尚不明确,致使碳排放难以作为工艺比选测算指标落地应用.[方法]根据联合国政府间气候变化专门委员会指南,采用排放因子法,在确定核算边界后,全面核算了污泥从污水处理厂外运直至最终消纳的全流程碳排放量,包括处理处置过程中因甲烷(CH4)和一氧化二氮(N2O)释放所产生的碳排放,因电耗、药耗、能耗、运输等所产生的碳排放,以及资源能源替代所产生的碳减排,然后基于该核算结果探讨了污泥处理处置碳减排路径.[结果]污泥深度脱水-填埋、好氧发酵-土地利用、厌氧消化-土地利用、干化焚烧-建材利用的碳排放强度分别为1 465.75、933.46、880.35、752.33 kg CO2/(tDS).[结论]通过对比发现,在相同核算边界下,干化焚烧-建材利用是碳排放最少的污泥处理处置工艺,在新建项目工艺比选时可优先考虑.此外,当污泥因适用条件或处置方法受限,必须采用某种工艺时,还可从污泥源头减量、关键技术参数优化、资源能源回收等方面实现碳减排.

[Objective]Currently,four mainstream municipal sludge treatment and disposal process routes have been formed in China,namely,deep dewatering-landfill,aerobic fermentation-land use,anaerobic digestion-land use,and drying incineration-construction materials utilization.Each process has its own advantages,disadvantages and applicable conditions.However,the carbon emission level of each process is not clear,which makes it difficult to implement carbon emission as a measurement index for process comparison.[Methods]According to the guidelines of Intergovernmental Panel on Climate Change,the carbon emission amounts of the whole sludge treatment and disposal processes,from sludge transportation out of the wastewater treatment plant to final disposal,are comprehensively calculated by the emission factor method after determining the accounting boundary.It includes the carbon emission caused by the release of methane(CH4)and dinitrogen monoxide(N2O)during the treatment and disposal processes,the carbon emission caused by electricity consumption,drug consumption,energy consumption,transportation,etc.,and the carbon emission reduction caused by resource and energy substitution.Moreover,based on the calculation results,the carbon emission reduction path of sludge treatment and disposal is discussed.[Results]The carbon emission intensities of sludge deep dewatering-landfill,aerobic fermentation-land use,anaerobic digestion-land use,and drying incineration-construction materials utilization are 1 465.75,933.46,880.35,752.33 kg CO2/(t DS),respectively.[Conclusion]It is found that under the same accounting boundary,drying incineration-construction materials utilization is the sludge treatment and disposal process with the least carbon emission by comparison,which can be given priority in the process selection of new projects.In addition,when the applicable condition or disposal route of sludge is restricted and a certain process must be adopted,carbon emission can also be reduced through measures such as sludge reduction at the source,key technical parameters optimization,resources and energy recovering.

王侨;王光辉;胡啸;刘芳;许世伟;郑鹏凯

北京恒润慧创环境技术有限公司,北京 100044北京首创生态环保集团股份有限公司,北京 100044北京恒润慧创环境技术有限公司,北京 100044北京恒润慧创环境技术有限公司,北京 100044北京首创生态环保集团股份有限公司,北京 100044北京恒润慧创环境技术有限公司,北京 100044

资源环境

市政污泥污泥处理处置碳排放核算排放因子法碳减排

municipal sludgesludge treatment and disposalcarbon emission accountingemission factor methodcarbon emission reduction

《净水技术》 2026 (1)

10-18,9

10.15890/j.cnki.jsjs.2026.01.002

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