Viktoria Wechselberger, Marlies Hrad, Marcel Bühler, Thomas Kupper, Bernhard Spangl, Anders Michael Fredenslund, Marion Huber-Humer, Charlotte Scheutz
{"title":"厌氧消化工厂全厂甲烷排放评估:为各种工厂配置确定排放系数。","authors":"Viktoria Wechselberger, Marlies Hrad, Marcel Bühler, Thomas Kupper, Bernhard Spangl, Anders Michael Fredenslund, Marion Huber-Humer, Charlotte Scheutz","doi":"10.1016/j.wasman.2024.11.021","DOIUrl":null,"url":null,"abstract":"<p><p>This study examines methane (CH<sub>4</sub>) emission factors from biogas and wastewater treatment plants, based on primary and secondary data collected from 109 facilities. Primary emission data were measured at 19 facilities representing prevalent plant configurations across Europe. Statistical analysis highlights two categorical variables, namely primary feedstock and plant size, expressed as CH<sub>4</sub> production (≤250 kgh<sup>-1</sup>: small and medium-sized plants, >250 kgh<sup>-1</sup>: large plants), each of which has a significant impact on whole-site CH<sub>4</sub> emissions. Additionally, digestate storage (gastight vs. not-gastight) has a meaningful effect when considering CH<sub>4</sub> production as a continuous variable in the statistical analysis. Our results indicate that wastewater treatment plants have the highest average CH<sub>4</sub> losses (7.0 % of CH<sub>4</sub> produced, n = 31 or 0.10 kgpopulation equivalent(PE)<sup>-1</sup>yr<sup>-1</sup>, n = 28), followed by manure-based plants (3.7 %, n = 49), biowaste treatment facilities (2.8 %, n = 11) and energy crop-processing plants (1.9 %, n = 14). Furthermore, small and medium-sized plants have elevated emissions (5.6 %, n = 67) compared to larger counterparts (2.2 %, n = 42), primarily attributed to the absence of gastight digestate storage. Emissions tend to be lower with gastight digestate storage (2.7 %, n = 61) than not-gastight storage options (6.2 %, n = 48). Emission factors were determined for normal operating conditions, with a further investigation into other-than-normal operating conditions revealing temporal or constant emission peaks in eight out of 19 facilities. These peaks, suggesting potential areas for targeted mitigation strategies, were attributed to pressure relief valves, flare ignition problems and major leakages.</p>","PeriodicalId":23969,"journal":{"name":"Waste management","volume":"191 ","pages":"253-263"},"PeriodicalIF":7.1000,"publicationDate":"2024-11-20","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Assessment of whole-site methane emissions from anaerobic digestion plants: Towards establishing emission factors for various plant configurations.\",\"authors\":\"Viktoria Wechselberger, Marlies Hrad, Marcel Bühler, Thomas Kupper, Bernhard Spangl, Anders Michael Fredenslund, Marion Huber-Humer, Charlotte Scheutz\",\"doi\":\"10.1016/j.wasman.2024.11.021\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<p><p>This study examines methane (CH<sub>4</sub>) emission factors from biogas and wastewater treatment plants, based on primary and secondary data collected from 109 facilities. Primary emission data were measured at 19 facilities representing prevalent plant configurations across Europe. Statistical analysis highlights two categorical variables, namely primary feedstock and plant size, expressed as CH<sub>4</sub> production (≤250 kgh<sup>-1</sup>: small and medium-sized plants, >250 kgh<sup>-1</sup>: large plants), each of which has a significant impact on whole-site CH<sub>4</sub> emissions. Additionally, digestate storage (gastight vs. not-gastight) has a meaningful effect when considering CH<sub>4</sub> production as a continuous variable in the statistical analysis. Our results indicate that wastewater treatment plants have the highest average CH<sub>4</sub> losses (7.0 % of CH<sub>4</sub> produced, n = 31 or 0.10 kgpopulation equivalent(PE)<sup>-1</sup>yr<sup>-1</sup>, n = 28), followed by manure-based plants (3.7 %, n = 49), biowaste treatment facilities (2.8 %, n = 11) and energy crop-processing plants (1.9 %, n = 14). Furthermore, small and medium-sized plants have elevated emissions (5.6 %, n = 67) compared to larger counterparts (2.2 %, n = 42), primarily attributed to the absence of gastight digestate storage. Emissions tend to be lower with gastight digestate storage (2.7 %, n = 61) than not-gastight storage options (6.2 %, n = 48). Emission factors were determined for normal operating conditions, with a further investigation into other-than-normal operating conditions revealing temporal or constant emission peaks in eight out of 19 facilities. These peaks, suggesting potential areas for targeted mitigation strategies, were attributed to pressure relief valves, flare ignition problems and major leakages.</p>\",\"PeriodicalId\":23969,\"journal\":{\"name\":\"Waste management\",\"volume\":\"191 \",\"pages\":\"253-263\"},\"PeriodicalIF\":7.1000,\"publicationDate\":\"2024-11-20\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"0\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"Waste management\",\"FirstCategoryId\":\"93\",\"ListUrlMain\":\"https://doi.org/10.1016/j.wasman.2024.11.021\",\"RegionNum\":2,\"RegionCategory\":\"环境科学与生态学\",\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"Q1\",\"JCRName\":\"ENGINEERING, ENVIRONMENTAL\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"Waste management","FirstCategoryId":"93","ListUrlMain":"https://doi.org/10.1016/j.wasman.2024.11.021","RegionNum":2,"RegionCategory":"环境科学与生态学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"ENGINEERING, ENVIRONMENTAL","Score":null,"Total":0}
Assessment of whole-site methane emissions from anaerobic digestion plants: Towards establishing emission factors for various plant configurations.
This study examines methane (CH4) emission factors from biogas and wastewater treatment plants, based on primary and secondary data collected from 109 facilities. Primary emission data were measured at 19 facilities representing prevalent plant configurations across Europe. Statistical analysis highlights two categorical variables, namely primary feedstock and plant size, expressed as CH4 production (≤250 kgh-1: small and medium-sized plants, >250 kgh-1: large plants), each of which has a significant impact on whole-site CH4 emissions. Additionally, digestate storage (gastight vs. not-gastight) has a meaningful effect when considering CH4 production as a continuous variable in the statistical analysis. Our results indicate that wastewater treatment plants have the highest average CH4 losses (7.0 % of CH4 produced, n = 31 or 0.10 kgpopulation equivalent(PE)-1yr-1, n = 28), followed by manure-based plants (3.7 %, n = 49), biowaste treatment facilities (2.8 %, n = 11) and energy crop-processing plants (1.9 %, n = 14). Furthermore, small and medium-sized plants have elevated emissions (5.6 %, n = 67) compared to larger counterparts (2.2 %, n = 42), primarily attributed to the absence of gastight digestate storage. Emissions tend to be lower with gastight digestate storage (2.7 %, n = 61) than not-gastight storage options (6.2 %, n = 48). Emission factors were determined for normal operating conditions, with a further investigation into other-than-normal operating conditions revealing temporal or constant emission peaks in eight out of 19 facilities. These peaks, suggesting potential areas for targeted mitigation strategies, were attributed to pressure relief valves, flare ignition problems and major leakages.
期刊介绍:
Waste Management is devoted to the presentation and discussion of information on solid wastes,it covers the entire lifecycle of solid. wastes.
Scope:
Addresses solid wastes in both industrialized and economically developing countries
Covers various types of solid wastes, including:
Municipal (e.g., residential, institutional, commercial, light industrial)
Agricultural
Special (e.g., C and D, healthcare, household hazardous wastes, sewage sludge)