Volume 5, Issue 1 (March 2020)                   J Environ Health Sustain Dev 2020, 5(1): 922-924 | Back to browse issues page


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jalili M. Environmental Burden of Disease from Municipal Solid Waste Incinerator. J Environ Health Sustain Dev 2020; 5 (1) :922-924
URL: http://jehsd.ssu.ac.ir/article-1-224-en.html
Environmental Science and Technology Research Center, Department of Environmental Health Engineering, School of Public Health, Shahid Sadoughi University of Medical Sciences, Yazd, Iran.
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Environmental Burden of Disease from Municipal Solid Waste Incinerator
 
Mahrokh Jalili 1*
 
1 Environmental Science and Technology Research Center, Department of Environmental Health Engineering, School of Public Health, Shahid Sadoughi University of Medical Sciences, Yazd, Iran.
 
A R T I C L E  I N F O    
LETTER TO EDITOR    
*Corresponding Author:
Mahrokh Jalili
Email:
mahro.jalili@gmail.com
Tel:
+983532838081
 
Article History:
Received: 12 December 2019
Accepted: 20 February 2020
 
 
Citation: Jalili M. Environmental Burden of Disease from Municipal Solid Waste Incinerator. J Environ Health Sustain Dev. 2020; 5(1): 922-4.
 
Ambient air near or far from a municipal solid waste incinerator (MSWI) produced more fine particles, including PM1, PM2.5, and PM10 than usually non-contaminated air. Inhalation might be the primary exposure route of heavy metals, i.e. Zn, Cu, Pb, Cd, Fe, Cr and Mn in various types of particles in ambient air, including PM1, PM2.5, and PM10 for inhabitants of places nearby these areas especially children and adolescents living in the neighborhood of MSWI1. For example, very toxic persistent organic pollutants (POPs) such as polychlorinated dibenzo-p-dioxins (PCDD) and dibenzofurans (PCDFs) can cause various health outcomes such as lung cancer2, thyroid disorder and other kinds of cancers (10.10% vs. 8.28%, p < 0.01)3. The evaluations show that albeit increase of open burning incinerators to PCDD/PCDFs discharges has been decreasing in the world's countries. However, it continued to be the principal source of emissions in Iran, according to about 45.8% out of total emissions in 1990 to 35.7% in 20102. A limited number of studies in the world noticed that heavy metals such as Zn, Pb, Cu, Cr, and Cd could be concentrated easily in fine particles, which can be constructed and transformed into fly ash during incinerators’ agitation process in the MSWI, in particles < 0.8 mm. These particles contain lower concentrations of nutrient content and higher concentrations of heavy metals 4,5 obtaining PM10 and PM2.5 fractions for physic-chemical analysis in the body. Therefore, the mentioned pollutant has been associated with fetal growth 6. Children living near an MSWI would suffer from higher determines internal exposure i.e. body burdens of PCDD/Fs 7. Significantly higher body burden of PCDD/Fs and PCBs in breastfed newborns near MSWI are observed (p < 0.05)8. The environmental burden of disease (EBD) of population attributable fraction respiratory and cardiovascular disease (CVD) is 0.12% and 0.10%, respectively. NO2 and SO2 can cause and exacerbate many public health problems such as CVD, respiratory disease9, mortality (2%)10, low-birth weight, and lung cancer11. In another study, no enhanced risk of congenital anomalies was determined concerning modeled PM10 emissions. However, , a  small amount of risk exists with regard to congenital heart diseases, genital anomalies related to MSWI12, respiratory mortality13, and cardiovascular mortality 14. Teenagers living around the MSWI area may not suffer from a significant long-term accumulation of heavy metals such as Cd or Cr. No distinct early renal impairment is observed, but urinary levels of Cd (U_Cd) which were emphatically correlated with the N-acetyl- β-D-glucosaminidase (NAG) and U_Cr levels which were positively associated with the levels of U-NAG, retinol-binding protein (U-RBP), and β2-microglobulin (U-BMG) 15 were founded in these age group. The children living near incinerator experienced increased body burdens of heavy metals, dominant genetic and epigenetic modifications, blood levels of Cr, Pb which are correlated with global DNA hypomethylation, and global DNA hypermethylation 16. More studies observed that PCDD/PCDFs are often emitted into the ambient air followed by an MSWI, and other centers affiliated with burning facilities 7. The daily intake doses were determined to be developed with the opening of new waste incinerators in Iran 17,18. Other studies evaluated the developing trend in intake doses of PCDD/PCDFs emissions and pollutants in Iran 2. Such high levels of emissions, high doses of pollutants' intake, and their developing trend in Iran are considered as the main health risks in Iran. As a result, more research is required with more rigorous methods. However, this should not circumvent taking proper management actions against these pollutants emission. Therefore, there is a requirement to pollutants emitted control from MSWI. Many methods have been used to control pollutants emitted from these centers19-21. Until now, there is no approved standard for PCDD & PCDFs emission from incinerators in Iran. Revision of the WHO concerning approved guidelines might be a suitable starting point to control PCDD & PCDFs emissions in the world. Although the one risk factor emissions, which is an incinerator, are small, the burden of disease (BE) can be notable for public health when population exposure is taken into concern. Policymakers, who are responsible for estimating and controlling from air polluting sources, should consider the enormous BE caused by toxic chemicals that are emitting from MSWI.
 
T This is an Open Access article distributed in accordance with the terms of the Creative Commons Attribution (CC BY 4.0) license, which permits others to distribute, remix, adapt and build upon this work for commercial use.
 
References
  1. Xu P, Chen Y, He S, et al. A follow-up study on the characterization and health risk assessment of heavy metals in ambient air particles emitted from a municipal waste incinerator in Zhejiang, China. Chemosphere. 2019;246:125777.
  2. Momeniha F, Faridi S, Amini H, et al. Estimating national dioxins and furans emissions, major sources, intake doses, and temporal trends in Iran from 1990-2010. J Environ Health Sci Eng. 2017;15:20.
  3. Samer CF, Gloor Y, Rollason V, et al. Cytochrome P450 1A2 activity and incidence of thyroid disease and cancer after chronic or acute exposure to dioxins. Basic Clin Pharmacol Toxicol. 2019. doi: 10.1111/bcpt.13339.
  4. Ma W, Tai L, Qiao Z, et al. Contamination source apportionment and health risk assessment of heavy metals in soil around municipal solid waste incinerator: a case study in North China. Sci Total Environ. 2018;631: 348-357.
  5. Wang P, Hu Y, Cheng H. Municipal solid waste (MSW) incineration fly ash as an important source of heavy metal pollution in China. Environ Pollut. 2019;252(Pt A):461-75
  6. Ghosh RE, Freni-Sterrantino A, Douglas P, et al. Fetal growth, stillbirth, infant mortality and other birth outcomes near UK municipal waste incinerators; retrospective population based cohort and case-control study. Environment International. 2019;122:151-8.
  7. Xu P, Chen Z, Wu L, et al. Health risk of childhood exposure to PCDD/Fs emitted from a municipal waste incinerator in Zhejiang, China. Sci Total Environ. 2019; 689:937-944.
  8. Xu P, Wu L, Chen Y, et al. High intake of persistent organic pollutants generated by a municipal waste incinerator by breast fed infants. Environ Pollut. 2019;250:662-8.
  9. Cao B, Bray F, Ilbawi A, et al. Effect on longevity of one-third reduction in premature mortality from non-communicable diseases by 2030: a global analysis of the sustainable development goal health target. Lancet Glob Health. 2018;6(12):1288-96.
  10. Romanelli AM, Bianchi F, Curzio O, et al. Mortality and morbidity in a population exposed to emission from a municipal waste incinerator. A retrospective cohort study. Int J Environ Res Public Health. 2019;16(16):2863.
  11. Kim YM, Kim JW, Lee HJ. Burden of disease attributable to air pollutants from municipal solid waste incinerators in Seoul, Korea: a source-specific approach for environmental burden of disease. Sci Total Environ. 2011;409(11):2019-28.
  12. Parkes B, Hansell AL, Ghosh RE, et al. Risk of congenital anomalies near municipal waste incinerators in England and Scotland: Retrospective population-based cohort study. Environment international. 2020;134:104845.
  13. Kim H, Lee JT, Hong YC, et al. Evaluating the effect of daily PM10 variation on mortality. Inhal Toxicol. 2004;16(1):55-8.
  14. Lee JT, Kim H, Cho YS, et al. Air pollution and hospital admissions for ischemic heart diseases among individuals 64+ years of age residing in Seoul, Korea. Arch Environ Health. 2003;58(10):617-23.
  15. Xu P, Wu L, Chen Y, et al. A cross-sectional study on school-age children living near a municipal waste incinerator: Urinary metal levels and renal impairment assessment. Chemosphere. 2020;241:125081.
  16. Xu P, Chen Z, Chen Y, et al. Body burdens of heavy metals associated with epigenetic damage in children living in the vicinity of a municipal waste incinerator. Chemosphere. 2019;229:160-8.
  17. Abedi-Varaki M, Davtalab M. Site selection for installing plasma incinerator reactor using the GIS in Rudsar county, Iran. Environ Monit Assess. 2016;188(6):353.
  18. Nikravan M, Ramezanianpour AA, Maknoon R. Study on physiochemical properties and leaching behavior of residual ash fractions from a municipal solid waste incinerator (MSWI) plant. J Environ manag. 2020;260:110042.
  19. Liu G, Yang L, Zhan J, et al. Concentrations and patterns of polychlorinated biphenyls at different process stages of cement kilns co-processing waste incinerator fly ash. Waste Manag. 2016;58:280-6.
  20. Sakurai T, Weber R, Ueno S, et al. Relevance of coplanar PCBs for TEQ emission of fluidized bed incineration and impact of emission control devices. Chemosphere. 2003;53(6):619-25.
  21. Chen JC, Fang GC, Tang JT, et al. Removal of carbon dioxide by a spray dryer. Chemosphere. 2005;59(1):99-105.

 
Type of Study: Letters to editor | Subject: Environmental pollution
Received: 2019/12/12 | Accepted: 2020/02/20 | Published: 2020/03/20

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