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. 2024 Jan 2;14(1):135.
doi: 10.1038/s41598-023-50226-w.

Association of exposure to indoor molds and dampness with allergic diseases at water-damaged dwellings in Korea

Affiliations

Association of exposure to indoor molds and dampness with allergic diseases at water-damaged dwellings in Korea

Seokwon Lee et al. Sci Rep. .

Abstract

This study aims to characterize levels of molds, bacteria, and environmental pollutants, identify the associations between indoor mold and dampness exposures and childhood allergic diseases, including asthma, allergic rhinitis, atopic dermatitis, using three different exposure assessment tools. A total of 50 children with their parents who registered in Seoul and Gyeonggi-do in Korea participated in this study. We collated the information on demographic and housing characteristics, environmental conditions, and lifestyle factors using the Korean version of the International Study of Asthma and Allergies in Childhood questionnaire. We also collected environmental monitoring samples of airborne molds and bacteria, total volatile organic compounds, formaldehyde, and particulate matter less than 10 µm. We evaluated and determined water damage, hidden dampness, and mold growth in dwellings using an infrared (IR) thermal camera and field inspection. Univariate and multivariate regression analyses were performed to evaluate the associations between prevalent allergic diseases and exposure to indoor mold and dampness. Indoor mold and bacterial levels were related to the presence of water damage in dwellings, and the mean levels of indoor molds (93.4 ± 73.5 CFU/m3) and bacteria (221.5 ± 124.2 CFU/m3) in water-damaged homes were significantly higher than those for molds (82.0 ± 58.7 CFU/m3) and for bacteria (152.7 ± 82.1 CFU/m3) in non-damaged dwellings (p < 0.05). The crude odds ratios (ORs) of atopic dermatitis were associated with < 6th floor (OR = 3.80), and higher indoor mold (OR = 6.42) and bacterial levels (OR = 6.00). The crude ORs of allergic diseases, defined as a group of cases who ever suffered from two out of three allergic diseases, e.g., asthma and allergic rhinitis, and allergic rhinitis were also increased by 3.8 and 9.3 times as large, respectively, with water damage (+) determined by IR camera (p < 0.05). The adjusted OR of allergic rhinitis was significantly elevated by 10.4 times in the water-damaged dwellings after adjusting age, sex, and secondhand smoke. Therefore, a longitudinal study is needed to characterize dominant mold species using DNA/RNA-based sequencing techniques and identify a causal relationship between mold exposure and allergic diseases in the future.

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Conflict of interest statement

The authors declare no competing interests.

Figures

Figure 1
Figure 1
A schematic diagram of the study design, key methodology, and process.
Figure 2
Figure 2
Examples of photographs with water damages and hidden dampness (dark blue colored areas) taken using an IR thermal camera at multiple locations of residential dwellings in this study.
Figure 3
Figure 3
Simple correlation matrix between water damage determined by IR thermal camera and the concentration levels of airborne molds, bacteria, TVOC, formaldehyde, PM10, temperature, and relative humidity in the indoor and outdoor environments. * Abbreviations: fungi_in (indoor mold); bac_in (indoor bacteria); fungi_out (outdoor mold); bac_out (outdoor bacteria); voc_in (indoor volatile organic compounds); hcho_in (indoor formaldehyde); pm10_in (indoor PM10), temp_in (indoor temperature); rh_in (indoor relative humidity).
Figure 4
Figure 4
Box plots of (a) indoor mold and (b) indoor bacterial concentration levels by the presence or absence of water damage using an IR thermal camera and ISAAC questionnaire survey (* p < 0.05).

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References

    1. Hwang E-S, Jung J-S, Shim I-K, Lee J-S, Lee J-C. Seasonal airborne fungal concentration and distribution in apartment buildings. J. Korean Soc Living Environ. Syst. 2019;26:825–833. doi: 10.21086/ksles.2019.12.26.6.825. - DOI
    1. Ginestet S, Aschan-Leygonie C, Bayeux T, Keirsbulck M. Mould in indoor environments: The role of heating, ventilation and fuel poverty: A French perspective. Build. Environ. 2020;169:106577. doi: 10.1016/j.buildenv.2019.106577. - DOI
    1. Vélez-Torres LN, et al. Hurricane María drives increased indoor proliferation of filamentous fungi in San Juan, Puerto Rico: A two-year culture-based approach. PeerJ. 2022;10:e12730. doi: 10.7717/peerj.12730. - DOI - PMC - PubMed
    1. Fan L, et al. Residential airborne culturable fungi under general living scenario: On-site investigation in 12 typical cities, China. Environ. Int. 2021;155:106669. doi: 10.1016/j.envint.2021.106669. - DOI - PubMed
    1. Lie SK, Vestøl GI, Høibø O, Gobakken LR. Surface mould growth on wooden claddings: Effects of transient wetting, relative humidity, temperature and material properties. Wood Mat. Sci. Eng. 2019;14:129–141. doi: 10.1080/17480272.2018.1424239. - DOI