Journal List > J Korean Med Sci > v.40(15) > 1516090486

Park, Zoh, Cho, Park, Hwang, Choi, Koh, Choi, and Park: Roots of the Large-Scale Household Humidifier Disinfectant Poisoning Tragedy: Regulatory and Surveillance Shortcomings in Korea

Abstract

The multi-decade household humidifier disinfectant poisoning tragedy (HHDT) in South Korea highlights the importance of investigating government failures. This study aims to identify and discuss key failures and shortcomings in the South Korean authorities’ approach to regulating humidifier disinfectants (HDs) and monitoring cases of chemical poisoning. We reviewed both the HD risk prevention measures that the South Korean Ministry of Environment (KME) should have implemented under the Toxic Chemicals Control Act (TCCA) (1991–2013). Polyhexamethylene guanidine phosphate (PHMG), a new chemical, was approved for use as a disinfectant under the TCCA. KME declared PHMG non-hazardous based solely on pre-production documentation provided by the industry. In addition, the Korea Disease Control and Prevention Agency (KDCPA) failed to detect the HHDT that had accumulated each year for more than a decade. KME’s neglect of its responsibilities, coupled with KDCPA’s lack of chemical poisoning surveillance systems, led to the accumulation of widespread HHDT.

Graphical Abstract

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Approximately 10 million products of 41 household humidifier disinfectant (HD) of different brands were reported to be purchased by consumers and widely used in households in the Republic of Korea (South Korea) from 1994 to 2011.1 As of March 2025, the South Korean Ministry of Environment (KME) has confirmed that 5,861 of 7,999 reported HD poisoning cases, including 1,335 deaths, were in fact caused by HD chemicals.2 Several HDs have been clinically confirmed to cause fatal lung disease with widespread pulmonary fibrosis, affecting pregnant women, pre-school children and spreading to adults of all ages in the household.3
Among the HD chemicals used, polyhexamethylene guanidine phosphate (PHMG) led in causing the household humidifier disinfectant poisoning tragedy (HHDT), followed by those containing oligo(2-(2-ethoxy)ethoxyethyl guanidinium (PGH), a mixture of methylchloroisothiazolinone (CMIT) and methylisothiazolinone (MIT), and benzalkonium chloride (BKC).2 PHMG was the leading cause of this HHDT, accounting for the majority of victims (n = 5,810) (PHMG brand users only; 48%, PHMG and other HD brand users; 100%).2
The purpose of this brief communication is to identify any neglect of KME’s legal obligations or failure of the Korea Disease Control and Prevention Agency’s (KDCPA) surveillance system to detect HD poisoning cases accumulated each year until 2011.
We examined government failures in the prevention and monitoring of chemical poisoning related to the HHDT in the following two categories. First, we reviewed the key points on HD risk prevention in the Toxic Chemicals Control Act (TCCA) under KME, which was enacted in 1991 and repealed in 2013. Second, we identified the government’s failure to update items that are commonly regulated or otherwise controlled in other countries for chemical risk prevention and chemical poisoning surveillance through a brief review of regulatory acts and documentation. The industry’s compliance with its legal obligations regarding the manufacture and marketing of raw HD chemicals or HD products is not reviewed.
In December 1996, a company submitted PHMG as an antimicrobial agent for use in carpets with documentations supporting the case for its polymer exemption under the TCCA (Table 1). In 1997, KME classified PHMG as non-hazardous and exempted it from hazard assessment based solely on these documents by a company (Table 2). This study briefly discusses several failures to take the necessary steps to protect the public from HD poisoning, which can be considered a dereliction of government duty.
Firstly, it appears that the KME did not fulfill its legal responsibilities to conduct a substantive technical review of the PHMG documentation submitted by the company to verify the accuracy of the information provided and to ensure compliance with the polymer exemption criteria (Tables 1 and 2). At that time, the enforcement decree of the TCCA required the chemical technical review team to assess the hazards of chemicals and the analytical results submitted by industry, as well as to conduct a comprehensive literature review for toxicity evaluation as part of the legal review process.4 This technical review was intended to certify the analytical results submitted by companies and to assess related domestic and foreign information, as outlined in Items 1, 2 and 3 of Article 7 of the Enforcement Decree of the TCCA.56 In the 1990s, under the Toxic Substances Control Act (TSCA), the US EPA chemical approval process required companies to submit a Pre-Manufacture Notification, followed by inspections, risk assessments and possible restrictions or bans on polymers that pose significant risks.7
If the KME had conducted a thorough technical review of the PHMG-related documentation, including a field investigation and re-analysis that the company submitted as required under the TCCA, the tragedy caused by PHMG could have been prevented to some extent.
Second, when the regulatory elements of the polymer exemption criteria were updated around 1993, the KME failed to introduce the exclusion of cationic polymers such as PHMG and PGH, which were being broadly regulated in other countries at the time. Not only can cationic polymers pose health risks such as skin and respiratory irritation, systemic toxicity, and potential damage to internal organs,8 , 9 their reactive nature can bind to negatively charged surfaces of aquatic organisms and disrupt their biological functions. PHMG and PGH contain positively charged guanidine groups that are cationic or soluble in water and cannot be exempted or otherwise classified as non-hazardous,10 even if they have a molecular weight greater than 1,000 g/mol.
Third the TCCA failed to include a provision requiring industry to submit updated hazard assessments when changing the use of a chemical after its initial approval, which is a conventional requirement in other countries throughout its enforcement period from 1991 to 2013. First approved in 1996 for use as an antimicrobial chemical in carpets, PHMG was freely allowed to be used as a HD without any need for a hazard assessment. There is no documentation of when and how PHMG was used as a chemical disinfectant in HD products since it was originally approved as a carpet disinfectant in 1995. By 1996, both the US11 and the European Union12 had introduced regulations requiring industry to submit updated hazard assessments when the use of a chemical was changed after its initial approval.
Finally, there was a severe deficiency in the national capacity for putting into place a poison control system with early sentinel case and epidemic detection, public warning, and toxicovigilance capabilities. Significant deficiencies and a lack of chemical poisoning surveillance systems help explain the inadequate response of the South Korean government to the HHDT for the nearly 17 years leading up to the end of 2011, resulting in the persistent accumulation of thousands of HD poisoning cases. Park et al.13 analyzed the role of nine Korean government organizations with at least a partial role in chemical poisoning detection during the period of widespread use of HD biocides and concluded that those agencies failed to contribute to the detection and prevention of the HHDT that had been growing in severity for over a decade.
A key strength of this short communication is its ability to highlight the critical need for regular updating of chemicals legislation to bring it into line with international standards, thereby reducing the health risks associated with chemicals.
In conclusion, the thousands of fatal and non-fatal cases of HD poisoning are directly linked to the failure of the authorities to fulfil their legal obligations to monitor the increasing incidence of HD chemical poisoning from the early 2000s to 2011.

Notes

Disclosure: The authors have no potential conflicts of interest to disclose.

Author Contributions:

  • Conceptualization: Park DU, Park S, Koh DH, Park J.

  • Data curation: Park DU, Zoh KE, Cho DH, Choi Y.

  • Formal analysis: Park DU, Choi CH, Koh DH.

  • Investigation: Park DU, Cho DH, Hwang J, Choi Y.

  • Methodology: Park DU, Park S, Hwang J, Koh DH, Choi Y.

  • Resources: Zoh KE, Hwang J.

  • Supervision: Park DU.

  • Validation: Park DU, Whang J, Choi CH, Park J.

  • Visualization: Park DU.

  • Writing - original draft: Park DU.

  • Writing - review & editing: Park DU, Zoh KE, Park S, Choi CH, Koh DH, Choi Y, Park J.

References

1. Park DU, Lee S, Lim HK, Kim SY, Kim J, Park J, et al. Comprehensive review on humidifier disinfectant (HD) products, focusing on the number of products and their disinfectant type. J Environ Health Sci. 2020; 46(5):481–494.
2. KEITI. A portal dedicated to supporting victims of the humidifier disinfectant tragedy in South Korea. Statistical status. Updated 2024. Accessed March 31, 2025. https://healthrelief.or.kr/home/content/stats01/view.do .
3. Kim HJ, Lee MS, Hong SB, Huh JW, Do KH, Jang SJ, et al. A cluster of lung injury cases associated with home humidifier use: an epidemiological investigation. Thorax. 2014; 69(8):703–708. PMID: 24488371.
4. KME. Notice of the preparation methods for chemical substance declaration forms and required data, Korea Ministry of Environment. Enforced in Dec. 30. 4, 1996; Notice No. 1996-175. Updated 1993. Accessed July 15, 2024. https://theme.archives.go.kr/viewer/common/archWebViewer.do?singleData=N&archiveEventId=0028284321#5 .
5. Korea Ministry of Environment. Toxic Chemical Control Act. Enforced in Feb. 4, 1995; Act No. 4784; Partially amended in Aug. 3, 1994. Sejong: Korea Ministry of Environment;1995.
6. Korea Ministry of Environment. Toxic Chemical Control Act Enforcement Decree in April 6, 1996; Act No. 14971; Partially amended in Article 7 of the Enforcement Decree. Dec. 23, 1994. Sejong: Korea Ministry of Environment;1996.
7. EPA. Polymer Exemption Guidance Manual (EPA 744-B-97-001). Updated May 22, 1997. Accessed July 15, 2024. https://www.epa.gov/sites/default/files/2015-03/documents/polyguid.pdf .
8. Sanderson H, Hansen A, Brill J, Rawlings J, Lam M, Connors K, et al. Overview of aquatic risk assessment of polymers – evidence from cationic polymers. Updated 2019. Accessed July 15, 2024. https://cefic-lri.org/wp-content/uploads/2018/07/Sanderson_112_Overview-of-aquatic-risk-assessment-of-polymers.pdf .
9. Brill JL, Rawlings JM, Connors KA, Belanger SE, Lam M, Hansen AMB, et al. Progress in understanding the ecotoxicology of cationic polymers: evidence with Polyquat 10’s. Updated 2019. Accessed July 15, 2024. https://cefic-lri.org/wp-content/uploads/2018/07/Brill_ecotox-of-cat-polymers-SETAC-2019.pdf .
10. Polymer PROC. Cationic polymer: understanding its properties and applications. Updated 2024. Accessed July 15, 2024. https://polymer-process.com/cationic-polymer/ .
11. GAO. Chemical regulation. Comparison of U.S. and recently enacted European union approaches to protect against the risks of toxic chemicals (GAO - 07 - 825). Updated 2024. Accessed July 15, 2024. https://www.gao.gov/products/gao-07-825 .
12. Chemicals EU. Commission seeks views on revision of REACH, the EU’s chemicals legislation. Updated 2022. Accessed July 15, 2024. https://environment.ec.europa.eu/news/chemicals-commission-seeks-views-revision-reach-eus-chemicals-legislation-2022-01-20_en .
13. Park DU, Kim J, Nam M, Mun E, Lee Y, Ha K, et al. Recommendation for the establishment of a poison control center at the Korea Disease Control and Prevention Agency. Environ Anal Health Toxicol. 2020; 35(3):e2020017. PMID: 32979902.
Table 1

Major provisions of the Toxic Substances Control Act addressing the humidifier disinfectant chemicals that caused fatal health effects

jkms-40-e144-i001
Applicable legal provisions (effective date) Key items from applicable legal provisions Chemicals used as humidifier disinfectant
Notice of the Preparation Methods for Chemical Substance Declaration Forms and Required Data, Korea Ministry of Environment Notice No. 1996-175 (Dec. 30, 1996)4 Polymeric chemicals falling under one of the following subparagraphs may be exempted from hazard assessment based on technical review by the Chemical Review Team. PHMG and PGH as new chemicals
- Number average molecular weight and analytical results
- Residual monomer content (%) and chemical name, and CAS number
- Molecular weight fraction of 1,000 or less (%)
- Stability in acid and alkali solution
PHMG = polyhexamethylene guanidine phosphate, PGH = oligo(2-(2-ethoxy)ethoxyethyl guanidinium.
Table 2

Main contents of the documents submitted by the company to the South KME in 1996 for PHMG production and the results of the technical review of these documents

jkms-40-e144-i002
Items Results submitted by company KME technical review report
Number average of molecular weight, g/mole 1,274 1,274
Weight average molecular weight, g/mole 1,667 1,667
Concentration of monomer (1,6 Hexanediamine, %) 1 1
Proportion of molecular weight lower than 1,000 g/mole, % 27.4 27.4
Product usage Carpet antimicrobials No description of review or testing to verify the risk if used as an antimicrobial chemical in carpets
Site inspection NA No
Analysis technique GPC No description of any analysis of the PHMG sample submitted by the company
KME = Korea Ministry of Environment, PHMG = polyhexamethylene guanidine phosphate, NA = not applicable, GPC = gel permeation chromatography.
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