Skip to main content
Iranian Journal of Public Health logoLink to Iranian Journal of Public Health
. 2019 Mar;48(3):458–464.

Non-Fire Related Carbon Monoxide Poisoning in Sichuan, China: A 9-Year Study (2008–2016)

Fan CHEN 1, Yi YE 1, Qingtao WEI 1, Jianxia CHEN 1, Hao WU 1, Youyi YAN 1, Linchuan LIAO 1,*
PMCID: PMC6570798  PMID: 31223573

Abstract

Background:

Carbon monoxide (CO) poisoning is one of the most important intoxications in the modern world. This study aimed to identify the characteristics of CO poisoning deaths in Sichuan province in the west of China.

Methods:

Data on fatal non-fire-related carbon monoxide poisoning in Sichuan from 2008 to 2016 were obtained from the Department of Forensic Analytical Toxicology of Sichuan University and were analyzed by the month and year of registration of death, sex, age group, manner of death, source of CO, and location of CO exposure. Comparing with the previous studies carried out in Wuhan and Shanghai to identify the regional differences of CO poisoning in China.

Results:

A total of 165 non-fire related CO poisoning cases including 237 victims were recorded. Over 90% of the victims died from accidental poisoning. Non-fire related CO poisoning occurred more frequently in winter months and was most prevalent in individuals aged between 18 and 60 yr old. Showering gas accident and coal or charcoal burning was found to be the major source of CO in accident and in suicide cases, respectively. Furthermore, significant regional differences of CO poisoning have been detected in the manner of death and the source of CO.

Conclusion:

These findings will be valuable in the targeted prevention of non-fire related CO poisoning in China.

Keywords: Non-fire, Carbon monoxide, Poisoning, Retrospective study

Introduction

Carbon monoxide (CO) is a colorless, odorless, tasteless toxic gas produced by incomplete combustion of carbon-based fuel. The affinity of CO for hemoglobin is 200–250 times greater than that of oxygen (1), resulting in tissue hypoxia. CO is still responsible for numerous deaths worldwide (2). The epidemiological studies of CO poisoning had been carried out in many countries and regions, such as United States, Turkey, Greece, and European, etc. (37).

Carbon monoxide poisoning mainly resulted from accidents or suicides, and rarely resulted from homicides in forensic practice. Motor vehicle exhaust, fire, charcoal burning in confined spaces, fireplaces and defective or improperly ventilated gas-powered appliances are the common sources of CO (38). Death due to CO poisoning is identified by values of carboxyhemoglobin (COHb) saturation above 50% in postmortem blood (9). COHb levels less than 10% usually are not associated with symptoms (10). As a general rule, if two or more individuals are found dead indoors, or any type of enclosure and there is no external evidence of trauma, the most probable cause of death is an asphyxiating gas and almost invariably CO (2).

Recently, the epidemiological studies of CO poisoning in Wuhan and Shanghai were published (11, 12). The two cities are located in the central and the east of China, respectively. Due to the vast geographic expanse of China, regional differences could exist in many aspects, such as energy distribution, natural conditions, and economy, etc. Hence, the aim of the present study was to characterize the CO poisoning deaths in Sichuan (a province in western China). It could be a complementary data of the previous studies. Moreover, a comparison between this study and the previous ones would be made in order to get more comprehensive information about CO poisoning deaths in mainland China.

Methods

This retrospective study covering data collected from Jan 2008 to Dec 2016 records of Department of Forensic Analytical Toxicology of Sichuan University, in Chengdu, China. Cases where COHb saturation in postmortem blood showed CO intoxication were selected. Fire-related cases were excluded. The study was approved by the Sichuan University Ethical Committee.

Non-fire related CO poisoning deaths were analyzed and classified according to the following epidemiological parameters: the month and the year when the death happened, the age and the gender of the victims, the manner of death, the source of CO, and the location of CO exposure. Detailed information of death was provided by the police. The determination of COHb in postmortem blood samples was performed by double wavelength spectrophotometry (Shimadzu UV-2550).

Chi-squared test and Fisher’s exact test (SPSS 20.0 (Chicago, IL, USA) were used to compare the parameters between different regions. P<0.05 was considered to be significant in the comparisons.

Results

During the period Jan 2008 to Dec 2016, 165 non-fire related CO poisoning cases with 237 deaths were recorded by our department. Yearly and monthly distribution of the non-fire related CO poisoning deaths is showed in Table 1 and 2, respectively. Despite some fluctuation from year to year, there was an increase in the annual number of victims from 2008 to 2016. The highest number of deaths occurred in 2015 with 40 victims, followed by 2012 with 33 victims. The highest non-fire related CO poisoning deaths recorded was in the months of Jan and Dec with 57 victims (24.1%) and 44 victims (18.6%), respectively (Table 2).

Table 1:

Yearly distribution of the non-fire related CO poisoning (2008–2016)

Year No. of Victims No. of Cases
2008 17 13
2009 30 17
2010 19 17
2011 10 7
2012 33 21
2013 28 20
2014 32 22
2015 40 25
2016 28 23
Total 237 165

Table 2:

Monthly distribution of the non-fire related CO poisoning (2008–2016)

Month No. of victims No. of cases
January 57 41
February 34 27
March 27 18
April 17 12
May 5 5
June 14 5
July 5 3
August 6 0
September 3 4
October 7 5
November 18 12
December 44 33

Demographic characteristics of the deaths and information about CO poisoning including the manner of death, the source of CO, and the location of CO exposure are presented in Table 3. Males accounted for 53.6% (n=127) of the non-fire CO-related victims, whereas females represented 46.4% (n=110). The age of the victims ranged from 1 to 68 yr old (mean age, 29.7 yr old), and the age group of 18–60 yr old contained 80.2% of the victims. 87.8% (n=208) of the victims were the result of accidental poisoning, 10.5% (n=25) due to suicide, and the remaining due to homicide (Table 3).

Table 3:

Comparison of non-fire related CO poisoning among Sichuan, Wuhan and Shanghai

Variable Sichuan Wuhan (11) P-value Shanghai(12) P-value
Gender (%)
Male 53.6 51.8 * 52.9 *
Female 46.4% 48.2 47.1
Age (%)
<18 16.4 0 P<0.001 7.6 P<0.01
18–60 80.2 80.4 83.2
<60 3.4 19.6 9.2
Manner of death (%)
Accident 87.8 43.7 P<0.001 69.2 P<0.01
Suicide 10.5 55.2 30.8
Homicide 1.7 1.1 0
Source of CO in suicide (%)
Coal or charcoal burning 68.0 70.8 * 97.3 P<0.001
Gas leak 28.0 29.2 0
motor vehicle exhaust 4.0 0 0
CO stored in a bottle/balloon 0 0 2.7
Source of CO in accident (%)
Showering gas accident 74.5 28.9 P<0.001 62.7 P<0.001
Gas leak 16.3 42.1 4.8
Fuel generator 3.4 0 2.4
Coal or charcoal burning 3.4 28.9 18.1
motor vehicle exhaust 2.4 0 9.6
others 0 0 2.4
Location of CO exposure (%)
Hostel/daily rented room 51.5 NA * NA *
Home 43.0 NA NA
Vehicle 3.4 NA NA
Workplace 2.1 NA NA
*:

means no statistic difference

NA indicated that the data are not available

Coal or charcoal burning was the main source of CO in suicides, and showering gas accident caused the most accidental poisoning Rental house/hostel and the decedent’s home were the main location of CO exposure.

The comparisons between Sichuan and two other regions (Shanghai and Wuhan) in non-fire related CO poisoning are also shown in Table 3. Sex distribution in these three regions was similar. The frequency of victims under the age of 18 in Sichuan was higher than that in Wuhan (P<0.001) and Shanghai (P<0.01). There were significant differences between Sichuan and Shanghai in the manner of death and the source of CO. Wuhan showed difference in the manner of death and the source of CO in accident when compared with Sichuan.

Discussion

CO poisoning deaths can be divided into two types, the fire-related ones, and the non-fire related ones. Only non-fire related CO poisoning deaths were considered in the current study because many others factors (burning, oxygen deficiency, alcohol intoxication, cyanide inhalation and so on) could contribute to the cause of death in fire (1315). Overall, 165 non-fire related CO poisoning cases resulting in 237 victims were recorded by our department from 2008 to 2016. The evolution of non-fire related CO poisoning deaths showed a fluctuant increase from 2008 to 2016 (Table 1). Although these numbers might not be significant, they could reflect the situation of Sichuan Province as almost all of the cases that suspected CO poisoning in Sichuan would be sent to our department for toxicology analysis. In the present study, non-fire related CO poisonings were more frequent during winter months (Dec, Jan, and Feb), which was consistent with previous studies (35, 11, 16, 17). Unintentional CO poisonings were highly correlated with the winter months because the major cause of unintentional poisonings related to domestic heaters and these were likely to be used most heavily in cold (18). In this study, the most common CO source was showering gas accident (about 65% of victims), which may explain the seasonal distribution of CO poisoning.

Males represent a litter higher proportion of the victims (53.6%) than female (Table 3). By contrast, the proportion of male victims in non-fire related CO poisoning was much higher in other countries. For instance, males accounted for 75.6% of the non-fire related CO deaths in England and Wales (16), 75.8%% in western Turkey (4) and 77.0% in United States (3). The reason why male represents a larger proportion of CO poisoning deaths was unclear. One possible reason is that males may have a higher risk of carbon monoxide exposure due to the frequent use of CO emitting equipment or working indoors (19, 20). In this study, only a very few male victims were connected with using of CO emitting equipment for work. This may partly explain the difference in sex distribution between Sichuan and other countries. Over 80% of the victims were in the age group of 18–60-year-olds (Table 3), this age group of individuals were at greater risk of CO poisoning than other age groups. The similar age distribution was found in some countries (16). However, many other studies reported the eldest (4, 8, 17) were at the greatest risk of CO poisoning

In this study, most of the CO poisoning deaths were attributed to unintentional accidents, which was consistent with other studies (5, 21). About 65% of victims were died from showering gas accidents. According to investigations by the police, defective water heaters and/or improper installation were the primary risk factors in the most CO poisoning cases. Inadequate ventilation coupled with a longer shower in cold weather eventually caused most tragedies. This could largely explain the reason why unintentional accidents accounted for such large proportion.

CO poisoning mostly occurred indoor, hostel or rental house and the victims’ home were the most common places. Hostel or rental house especially the cheap rent ones usually had some features as follows: small space, old or inferior equipment, poor ventilation and so on. Migrant workers, needy families and many young couples preferred to stay in these places for the cheap rent. Another important reason was that people do not have to register the real names and identity card in these places. This was one of the most noticeable characteristics of CO poisoning in Sichuan.

Shanghai is a large city in eastern China, Wuhan locates in the center of China and Sichuan is in western China. There were significant regional differences in the manner of death and the source of CO. The percentage of unintentional accident was much higher than suicide in Shanghai and Sichuan. However, Wuhan was just the opposite. Based on the significant difference in the manner of death, the source of CO was divided into two groups: source of CO in suicide and in accident. In suicide cases, the source of CO in Wuhan and Sichuan were very similar. Coal or charcoal burning was the most common method, followed by gas leak. In Shanghai, nearly everyone committed suicide by burning coal or charcoal. The common methods of committing suicide vary from country to country. For example, the most common method of suicide with CO was by motor vehicle exhaust gases in Iran, Europe and United Stated (6, 17, 22). And charcoal burning has become one of the leading methods of suicide in Asia (23, 24). In accident cases, showering gas accident was the main source in Sichuan and Shanghai, but not in Wuhan. Gas leak was the first source, followed by Showering gas accident and coal or charcoal burning in Wuhan. Although what drives the differences is not clear, the findings of regional differences in CO poisoning will be useful, especially in unintentional CO poisoning precaution.

Like many other accidents and injuries, CO poisoning is considered preventable (25). Several pivotal factors associated with CO poisoning had been identified in this study. First, CO poisoning was seasonal with middle-aged people and young adults at the greatest risk. Second, rental house/hostel and home were the main sites of unintentional CO poisoning. Third, the focus for prevention in different regions should be variable according to the local features in CO poisoning. Prevention of indoor CO exposure in Sichuan can be accomplished as follows: 1) do not use inferior or improper installed water heater; 2) frequent inspection and routine maintenance of CO emitting equipment; 3) maintain indoor ventilation especially in cold weather; 4) install a CO detector; 5) spread preventive messages about potential source of CO by media especially to the high-risk groups.

Conclusion

Non-fire related carbon monoxide poisoning remains a significant cause of death in mainland China. Basing on the analysis of CO poisoning deaths in Sichuan Province, several characteristics of CO poisoning have been identified. And the regional differences of CO poisoning have been proved by comparing the data of Sichuan, Shanghai, and Wuhan. These findings were beneficial to comprehensively understand the features of CO poisoning in mainland China and valuable in the prevention of CO poisoning. Raising the public awareness on the dangers of CO and popularizing the preventive messages about potential sources of CO exposure are pivotal in reducing incidence of poisoning. At the same time, sufficient precautions should be taken in time, and attention should be paid equally to both residences and workplaces.

Ethical considerations

Ethical issues (Including plagiarism, informed consent, misconduct, data fabrication and/or falsification, double publication and/or submission, redundancy, etc.) have been completely observed by the authors.

Acknowledgments

The authors want to thank the Department of Forensic Analytical Toxicology of Sichuan University for providing data.

Footnotes

Conflict of interest

The authors declare that there is no conflict of interests.

References

  • 1.Ernst A, Zibrak JD. (1998). Carbon monoxide poisoning. N Engl J Med, 339(22):1603–8. [DOI] [PubMed] [Google Scholar]
  • 2.Stefanidou M, Athanaselis S, Koutselinis A. (2003). Carbon monoxide: old poison—recent problems. Leg Med (Tokyo), 5(4):253–4. [DOI] [PubMed] [Google Scholar]
  • 3.Hampson NB. (2016). U.S. Mortality Due to Carbon Monoxide Poisoning, 1999–2014. Accidental and Intentional Deaths. Ann Am Thorac Soc, 13(10):1768–74. [DOI] [PubMed] [Google Scholar]
  • 4.Dirlik M, Bostancioglu B. (2017). Deaths due to carbon monoxide poisoning in Aydin, western Turkey. Death Stud, 41(4):246–50. [DOI] [PubMed] [Google Scholar]
  • 5.Stefanidou ME, Maravelias CP, Dona AA, et al. (2012). Carbon Monoxide–Related Deaths in Greece. Am J Forensic Med Pathol, 33(2):128–31. [DOI] [PubMed] [Google Scholar]
  • 6.Braubach M, Algoet A, Beaton M, et al. (2013). Mortality associated with exposure to carbon monoxide in WHO European Member States. Indoor Air, 23(2):115–25. [DOI] [PubMed] [Google Scholar]
  • 7.Nielsen PR, Gheorghe A, Lynnerup N. (2014). Forensic aspects of carbon monoxide poisoning by charcoal burning in Denmark, 2008–2012: an autopsy based study. Forensic Sci Med Pathol, 10(3):390–4. [DOI] [PubMed] [Google Scholar]
  • 8.Ruas F, Mendonça MC, Real FC, et al. (2014). Carbon monoxide poisoning as a cause of death and differential diagnosis in the forensic practice: A retrospective study, 2000–2010. J Forensic Leg Med, 24:1–6. [DOI] [PubMed] [Google Scholar]
  • 9.Dimaio D, Dimaio VJM. M.D. (2001). Forensic Pathology, Second Edition Informa Healthcare. [Google Scholar]
  • 10.Raub JA, Mathieu-Nolf M, Hampson NB, Thom SR. (2000). Carbon monoxide poisoning—a public health perspective. Toxicology, 145(1):1–14. [DOI] [PubMed] [Google Scholar]
  • 11.Li F, Chan HC, Liu S, et al. (2015). Carbon monoxide poisoning as a cause of death in Wuhan, China: A retrospective six-year epidemiological study (2009–2014). Forensic Sci Int, 253:112–8. [DOI] [PubMed] [Google Scholar]
  • 12.Lu X, Li F, Chan HC, et al. (2016). Carbon monoxide poisoning deaths in Shanghai, China: A 10-year epidemiological and comparative study with the Wuhan sample. Cogent Med, 3(1):1137131. [Google Scholar]
  • 13.Teige B, Lundevall J, Fleischer E. (1977). Carboxyhemoglobin concentrations in fire victims and in cases of fatal carbon monoxide poisoning. Z Rechtsmed, 80(1):17–21. [DOI] [PubMed] [Google Scholar]
  • 14.Gormsen H, Jeppesen N, Lund A. (1984). The causes of death in fire victims. Forensic Sci Int, 24(2):107–11. [DOI] [PubMed] [Google Scholar]
  • 15.Alarifi AA, Phylaktou HN, Andrews GE. (2016). What Kills People in a Fire? Heat or Smoke? The Saudi Students Conference. [Google Scholar]
  • 16.Fisher DS, Leonardi G, Flanagan RJ. (2014). Fatal unintentional non-fire-related carbon monoxide poisoning: England and Wales, 1979–2012. Clin Toxicol (Phila), 52(3):166–70. [DOI] [PubMed] [Google Scholar]
  • 17.Sircar K, Clower J, Shin Mk, et al. (2015). Carbon monoxide poisoning deaths in the United States, 1999 to 2012. Am J Emerg Med, 33(9):1140–5. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 18.Wilson RC, Saunders PJ, Smith G. (1998). An epidemiological study of acute carbon monoxide poisoning in the West Midlands. Occup Environ Med, 55(11):723–8. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19.Hnatov MV. (2013). Incidents, Deaths, and In-Depth Investigations Associated with Non-Fire Carbon Monoxide from Engine-Driven Generators and Other Eng Sircar K ine-Driven Tools, 1999–2012. US Consumer Product Safety Commission. [Google Scholar]
  • 20.Fisher DS, Bowskill S, Saliba L, Flanagan RJ. (2013). Unintentional domestic non-fire related carbon monoxide poisoning: data from media reports, UK/Republic of Ireland 1986–2011. Clin Toxicol (Phila), 51(5):409–16. [DOI] [PubMed] [Google Scholar]
  • 21.Karapirli M, Kandemir E, Akyol S, et al. (2013). Forensic and clinical carbon monoxide (CO) poisonings in Turkey: A detailed analysis. J Forensic Leg Med, 20(2):95–101. [DOI] [PubMed] [Google Scholar]
  • 22.Sheikhazadi A, Saberi Anary SH, Ghadyani MH. (2010). Nonfire Carbon Monoxide-Related Deaths. Am J Forensic Med Pathol, 31(4):359–63. [DOI] [PubMed] [Google Scholar]
  • 23.Wu KC-C, Chen Y-Y, Yip PS. (2012). Suicide methods in Asia: implications in suicide prevention. Int J Environ Res Public Health, 9(4):1135–58. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 24.Choi Y-R, Cha ES, Chang S-S, et al. (2014). Suicide from carbon monoxide poisoning in South Korea: 2006–2012. J Affect Disord, 167:322–5. [DOI] [PubMed] [Google Scholar]
  • 25.Shie H-G, Li C-Y. (2007). Population-Based Case-Control Study of Risk Factors for Unintentional Mortality from Carbon Monoxide Poisoning in Taiwan. Inhal Toxicol, 19(10):905–12. [DOI] [PubMed] [Google Scholar]

Articles from Iranian Journal of Public Health are provided here courtesy of Tehran University of Medical Sciences

RESOURCES