某制药厂恶臭污染环境影响研究
Study on Environmental Impact of Odor Pollution in a Pharmaceutical Enterprise
DOI: 10.12677/AEP.2022.123083, PDF,   
作者: 王健壮, 张 妍*:天津迪兰奥特环保科技开发有限公司,天津
关键词: 恶臭污染臭气浓度制药企业环境影响Odor Pollution Odor Concentration Pharmaceutical Companies Environmental Impact
摘要: 随着城市扩张,居民区与工业企业等恶臭污染源共建现象严重,恶臭扰民问题愈发突出,评价居民是否受到恶臭污染影响是目前管理部门问题与挑战。本研究选取某制药企业为研究对象进行采样调查,并对臭气浓度进行实验室分析,在此基础上,利用CALPUFF模型进行恶臭污染模拟,分析周边敏感点的扰民影响。结果表明,该制药企业所有排气筒臭气浓度范围为131~173,780,臭气浓度较高;该企业全年小时臭气浓度最大落地点发生在厂区内,可达355,其厂界全年最大小时臭气浓度约为320,北侧敏感点全年最大小时臭气浓度为30~140之间;该企业发酵车间及污水处理站对周边恶臭影响较为严重,需进行进一步提升改造。
Abstract: At present, public odor complaint is the prominent environmental problem because the residential areas are closer and closer from industrial enterprises and other pollution sources in China. As a result, evaluating whether residents affected by odor pollution is a great challenge for envi-ronmental management department. In this study, a pharmaceutical company was selected as the research object, the sampling analysis was carried out, and the odor concentrations were analyzed in laboratory. On this basis, CALPUFF model was used to simulate odor pollution and analyze the odor impact of surrounding sensitive points. The results showed that the odor concentration of all exhaust cylinders was 131~173,780, which was very high. The highest hourly odor concentration was up to 355, which occurred in the factory. The annual maximum hourly odor concentration of factory boundary was about 320. The annual maximum hourly odor concentrations of the sensitive area were 30~140, which was in the north of the factory. What’s more, the fermentation workshop and sewage treatment station were more serious odor emission sources, which need further upgrading and transformation.
文章引用:王健壮, 张妍. 某制药厂恶臭污染环境影响研究[J]. 环境保护前沿, 2022, 12(3): 637-643. https://doi.org/10.12677/AEP.2022.123083

参考文献

[1] 王亘, 王宗爽, 王元刚, 等. 国内外恶臭污染控制标准研究[J]. 环境科学与技术, 2012, 35(S2): 147-151.
[2] 杨伟华, 李伟芳, 韩萌, 等. 基于现场监测的异味污染暴露-效应评价[J]. 环境化学, 2019, 38(7): 1628-1635.
[3] 邹克华, 翟增秀, 李伟芳, 等. 典型生物发酵企业挥发性有机物及恶臭污染物排放特征[J]. 环境化学, 2020, 39(12): 3574-3580.
[4] 王亘, 张妍, 张超, 等. 垃圾填埋场恶臭污染对感官影响的评价研究[J]. 农业工程学报, 2019, 35(12): 232-238.
[5] 中华人民共和国生态环境部. HJ905-2017恶臭污染环境监测技术规范[S].
[6] 中华人民共和国生态环境部. HJ194-2017环境空气质量手工监测技术规范[S].
[7] 中华人民共和国生态环境部. GB/T14675-1993空气质量恶臭的测定三点比较式臭袋法[S].
[8] Zhang, Y., Yang, W.H., Schauberger, G., et al. (2021) Determination of Dose-Response Relationship to Derive Odor Impact Criteria for a Wastewater Treatment Plant. Atmosphere, 12, Article No. 371. [Google Scholar] [CrossRef
[9] 王露, 毕晓辉, 刘保双, 等. 基于CALPUFF-CMB复合模型的燃煤源精细化来源解析[J]. 中国环境科学, 2018, 38(8): 2911-2920.
[10] 孙博飞, 伯鑫, 张尚宣, 等. 钢厂烧结机烟气排放对土壤二噁英浓度的影响[J]. 中国环境科学, 2017, 37(11): 4222-4229.
[11] Capelli, L., Sironi, S., Rosso, R.D., et al. (2013) Measuring Odours in the Environment vs. Dispersion Modelling: A Review. Atmospheric Environ-ment, 79, 731-743. [Google Scholar] [CrossRef
[12] Ranzato, L., Barausse, A., Mantovani, A., et al. (2012) A Comparison of Methods for the Assessment of Odor Impacts on Air Quality: Field Inspection (VDI 3940) and the Air Dispersion Model CALPUFF. Atmospheric Environment, 61, 570-579. [Google Scholar] [CrossRef
[13] IAQM (2018) Guidance on the Assessment of Odour for Planning Version 1.1.
http://www.iaqm.co.uk/text/guidance/odour-guidance-2014.pdf
[14] New South Wales EPA. Approved Methods for the Modelling and Assessment of Air Pollutants in NSW.
http://www.epa.nsw.gov.au/your-environment/air/industrial-emissions/modelling-assessing-air-emissions/approved-methods-modelling-assessing-air-pollutants
[15] Queensland EPA. Guideline-Odour Impact Assessment from De-velopments.
https://www.publications.qld.gov.au/dataset/guideline-odour-impact-assessment-for-developments/resource/1b4ab77d-c485-4a99-ad00-b097e22b5605
[16] 中华人民共和国生态环境部. HJ2.2-2018环境影响评价技术导则大气环境[S].
[17] Zhang, Y., Ning, X., Li, Y., Wang, J., et al. (2021) Impact Assessment of Odor Nuisance, Health Risk and Variation Originating from the Landfill Surface. Waste Management, 126, 771-780. [Google Scholar] [CrossRef] [PubMed]