上海交通大学学报(医学版) ›› 2023, Vol. 43 ›› Issue (1): 44-51.doi: 10.3969/j.issn.1674-8115.2023.01.006
邓云天1(), 熊文魁1, 朱芮1, 刘恩梅2,3, 李雪梅4(), 钟朝晖5()
收稿日期:
2022-08-18
接受日期:
2022-10-18
出版日期:
2023-01-28
发布日期:
2023-01-28
通讯作者:
李雪梅,钟朝晖
E-mail:dyt0307@hotmail.com;981342321@qq.com;100144@cqmu.edu.cn
作者简介:
邓云天(2000—),男,本科生;电子信箱:dyt0307@hotmail.com。
基金资助:
DENG Yuntian1(), XIONG Wenkui1, ZHU Rui1, LIU Enmei2,3, LI Xuemei4(), ZHONG Zhaohui5()
Received:
2022-08-18
Accepted:
2022-10-18
Online:
2023-01-28
Published:
2023-01-28
Contact:
LI Xuemei,ZHONG Zhaohui
E-mail:dyt0307@hotmail.com;981342321@qq.com;100144@cqmu.edu.cn
Supported by:
摘要:
目的·探讨重庆地区儿童生命早期环境因素暴露对其自身哮喘发病的潜在影响。方法·采用病例对照设计,纳入2020年9月—2022年1月在重庆市2所三级甲等儿童专科医院呼吸科门诊就诊的哮喘患儿作为病例组,将同期在儿童保健科健康体检门诊就诊的无哮喘史的健康儿童作为对照组。纳入的儿童自出生以来均居住于重庆市范围内,且3岁前的家庭居住地址未发生改变。研究采用自行研制的儿童生命早期环境因素暴露调查问卷,收集2组儿童的个人基本信息、家庭情况、儿童健康状况及出生情况、出生后至3岁的家庭室内环境(烟草烟雾暴露、卧室霉点霉斑暴露、蟑螂暴露、卧室清洁频率、空调及空气净化器使用情况、装修情况)等信息。根据儿童出生前至3岁的家庭地址信息,基于高时空分辨率模型,估计每位儿童出生前至3岁的每年细颗粒物(particular matter 2.5,PM2.5)暴露水平。运用单因素和多因素Logistic回归模型分析可能影响儿童哮喘发病的早期环境暴露因素。将单因素分析有统计学意义或有临床意义的危险因素纳入多因素模型。结果·病例组纳入患儿220例,对照组纳入健康儿童636例,平均年龄分别为(7.4±2.1)岁和(7.6±2.1)岁。2组儿童年龄、性别、胎龄、出生体质量、母亲分娩方式、家庭人口数、家庭年收入、母亲受教育年限和人均生活空间的差异均无统计学意义。多因素Logistic回归分析显示,生命早期儿童卧室霉斑霉点(OR=2.155,95%CI 1.304~3.559,P=0.003)、卧室蟑螂暴露(OR=1.830,95%CI 1.287~2.601,P=0.001)、卧室空调使用(OR=2.328,95%CI 1.098~4.937,P=0.028)、二手烟暴露(OR=1.762,95%CI 1.272~2.440,P=0.001)以及儿童1岁时环境中PM2.5暴露(OR=1.063,95%CI 1.034~1.093,P=0.000)会增加儿童哮喘的发病风险;每日开启空气净化器(OR=0.416,95%CI 0.213~0.812,P=0.010)可以降低儿童哮喘的发病风险。结论·生命早期环境因素暴露对儿童哮喘发病具有重要意义。儿童生命早期卧室内霉斑霉点暴露、蟑螂暴露,以及被动吸烟、不合理使用空调以及儿童出生后第1年环境PM2.5的长期暴露与儿童哮喘的发病相关。
中图分类号:
邓云天, 熊文魁, 朱芮, 刘恩梅, 李雪梅, 钟朝晖. 生命早期环境因素暴露与儿童哮喘关系的病例对照研究[J]. 上海交通大学学报(医学版), 2023, 43(1): 44-51.
DENG Yuntian, XIONG Wenkui, ZHU Rui, LIU Enmei, LI Xuemei, ZHONG Zhaohui. A case-control study of the relationship between early-life environmental exposure and childhood asthma[J]. Journal of Shanghai Jiao Tong University (Medical Science), 2023, 43(1): 44-51.
Item | Asthma (n=220) | Control (n=636) | χ2/t value | P value |
---|---|---|---|---|
Age | 7.4±2.1 | 7.6±2.1 | 1.299 | 0.194 |
Gender/n (%) | 0.216 | 0.642 | ||
Male | 114 (51.8) | 318 (50.0) | ||
Female | 106 (48.2) | 318 (50.0) | ||
Gestational age/n (%) | 0.520 | 0.771 | ||
<37 weeks | 8 (3.6) | 23 (3.6) | ||
≥37 weeks and ≤42 weeks | 210 (95.5) | 603 (94.8) | ||
>42 weeks | 2 (0.9) | 10 (1.6) | ||
Birth weight/n (%) | 5.896 | 0.117 | ||
<1 500 g | 2 (0.9) | 7 (1.1) | ||
≥1 500 g and <2 500 g | 24 (10.9) | 53 (8.3) | ||
≥2 500 g and <4 000 g | 185 (84.1) | 521 (81.9) | ||
≥4 000 g | 9 (4.1) | 55 (8.6) | ||
Delivery mode/n (%) | 0.100 | 0.951 | ||
Vaginal delivery | 91 (41.4) | 265 (41.7) | ||
Assisted delivery | 3 (1.4) | 7 (1.1) | ||
Caesarean delivery | 126 (57.3) | 364 (57.2) | ||
Family size①/n (%) | 4.339 | 0.114 | ||
2‒3 people | 105 (47.7) | 254 (39.9) | ||
4‒5 people | 97 (44.1) | 314 (49.4) | ||
≥6 people | 18 (8.2) | 68 (10.7) | ||
Maternal education level/n (%) | 4.580 | 0.205 | ||
≤9 years | 14 (6.4) | 33 (5.2) | ||
10‒12 years | 28 (12.7) | 66 (10.4) | ||
13‒16 years | 165 (75.0) | 472 (74.2) | ||
≥17 years | 13 (5.9) | 65 (10.2) | ||
Household annual income/n (%) | 8.218 | 0.084 | ||
<100 000 yuan | 36 (16.4) | 98 (15.4) | ||
≥100 000 yuan and <150 000 yuan | 47 (21.4) | 116 (18.2) | ||
≥150 000 yuan and <200 000 yuan | 50 (22.7) | 130 (20.4) | ||
≥200 000 yuan and <400 000 yuan | 62 (28.2) | 166 (26.1) | ||
≥400 000 yuan | 25 (11.4) | 126 (19.8) | ||
Living space per person/n (%) | 3.794 | 0.285 | ||
<10 m2 | 6 (2.7) | 10 (1.6) | ||
≥10 m2 and <20 m2 | 38 (17.3) | 84 (13.2) | ||
≥20 m2 and <40 m2 | 69 (31.4) | 223 (35.1) | ||
≥40 m2 | 107 (48.6) | 319 (50.2) |
表 1 哮喘组和对照组的一般资料比较
Tab 1 Comparison of general data between the asthma group and the control group
Item | Asthma (n=220) | Control (n=636) | χ2/t value | P value |
---|---|---|---|---|
Age | 7.4±2.1 | 7.6±2.1 | 1.299 | 0.194 |
Gender/n (%) | 0.216 | 0.642 | ||
Male | 114 (51.8) | 318 (50.0) | ||
Female | 106 (48.2) | 318 (50.0) | ||
Gestational age/n (%) | 0.520 | 0.771 | ||
<37 weeks | 8 (3.6) | 23 (3.6) | ||
≥37 weeks and ≤42 weeks | 210 (95.5) | 603 (94.8) | ||
>42 weeks | 2 (0.9) | 10 (1.6) | ||
Birth weight/n (%) | 5.896 | 0.117 | ||
<1 500 g | 2 (0.9) | 7 (1.1) | ||
≥1 500 g and <2 500 g | 24 (10.9) | 53 (8.3) | ||
≥2 500 g and <4 000 g | 185 (84.1) | 521 (81.9) | ||
≥4 000 g | 9 (4.1) | 55 (8.6) | ||
Delivery mode/n (%) | 0.100 | 0.951 | ||
Vaginal delivery | 91 (41.4) | 265 (41.7) | ||
Assisted delivery | 3 (1.4) | 7 (1.1) | ||
Caesarean delivery | 126 (57.3) | 364 (57.2) | ||
Family size①/n (%) | 4.339 | 0.114 | ||
2‒3 people | 105 (47.7) | 254 (39.9) | ||
4‒5 people | 97 (44.1) | 314 (49.4) | ||
≥6 people | 18 (8.2) | 68 (10.7) | ||
Maternal education level/n (%) | 4.580 | 0.205 | ||
≤9 years | 14 (6.4) | 33 (5.2) | ||
10‒12 years | 28 (12.7) | 66 (10.4) | ||
13‒16 years | 165 (75.0) | 472 (74.2) | ||
≥17 years | 13 (5.9) | 65 (10.2) | ||
Household annual income/n (%) | 8.218 | 0.084 | ||
<100 000 yuan | 36 (16.4) | 98 (15.4) | ||
≥100 000 yuan and <150 000 yuan | 47 (21.4) | 116 (18.2) | ||
≥150 000 yuan and <200 000 yuan | 50 (22.7) | 130 (20.4) | ||
≥200 000 yuan and <400 000 yuan | 62 (28.2) | 166 (26.1) | ||
≥400 000 yuan | 25 (11.4) | 126 (19.8) | ||
Living space per person/n (%) | 3.794 | 0.285 | ||
<10 m2 | 6 (2.7) | 10 (1.6) | ||
≥10 m2 and <20 m2 | 38 (17.3) | 84 (13.2) | ||
≥20 m2 and <40 m2 | 69 (31.4) | 223 (35.1) | ||
≥40 m2 | 107 (48.6) | 319 (50.2) |
Exposure item | Asthma (n=220) | Control (n=636) | OR (95%CI) | P value |
---|---|---|---|---|
Family second-hand smoke exposure/n (%) | 122 (55.5) | 251 (39.5) | 1.910 (1.401‒2.603) | 0.000 |
Second-hand smoke exposure level/n (%) | ||||
0 cig per day | 98 (44.5) | 385 (60.5) | Reference | ‒ |
≥1 cig per day and <5 cig per day | 52 (23.6) | 120 (18.9) | 1.702 (1.148‒2.524) | 0.008 |
≥5 cig per day and <10 cig per day | 30 (13.6) | 61 (9.6) | 1.932 (1.184‒3.154) | 0.008 |
≥10 cig per day and <20 cig per day | 31 (14.1) | 62 (9.7) | 1.964 (1.210‒3.190) | 0.006 |
≥20 cig per day | 9 (4.1) | 8 (1.3) | 4.420 (1.662‒11.751) | 0.003 |
Bedroom air conditioner use/n (%) | 211 (95.9) | 575 (90.4) | 2.487 (1.214‒5.097) | 0.013 |
Dampness and mold points in bedroom/n (%) | 37 (16.8) | 47 (7.0) | 2.689 (1.695‒4.264) | 0.000 |
Seen cockroaches in bedroom/n (%) | 84 (38.2) | 145 (21.6) | 2.245 (1.617‒3.117) | 0.000 |
Room cleaning frequency/n (%) | ||||
6‒7 times per week | 95 (43.2) | 359 (53.4) | Reference | ‒ |
3‒5 times per week | 114 (51.8) | 294 (43.8) | 1.469 (1.071‒2.015) | 0.017 |
<3 times per week | 11 (5.0) | 19 (2.8) | 2.271 (1.064‒4.846) | 0.034 |
Air purifier using frequency/n (%) | ||||
Never | 164 (74.5) | 435 (64.7) | Reference | ‒ |
Only haze days | 44 (20.0) | 171 (25.5) | 0.691 (0.473‒1.010) | 0.056 |
Every day | 12 (5.5) | 66 (9.8) | 0.471 (0.248‒0.896) | 0.022 |
Home interior decoration/n (%) | 32 (14.5) | 64 (9.5) | 1.617 (1.026‒2.548) | 0.038 |
表 2 重庆地区哮喘儿童生命早期室内环境暴露的单因素Logistic回归分析
Tab 2 Univariate Logistic regression of early-life in-door environment exposure for childhood asthma in Chongqing
Exposure item | Asthma (n=220) | Control (n=636) | OR (95%CI) | P value |
---|---|---|---|---|
Family second-hand smoke exposure/n (%) | 122 (55.5) | 251 (39.5) | 1.910 (1.401‒2.603) | 0.000 |
Second-hand smoke exposure level/n (%) | ||||
0 cig per day | 98 (44.5) | 385 (60.5) | Reference | ‒ |
≥1 cig per day and <5 cig per day | 52 (23.6) | 120 (18.9) | 1.702 (1.148‒2.524) | 0.008 |
≥5 cig per day and <10 cig per day | 30 (13.6) | 61 (9.6) | 1.932 (1.184‒3.154) | 0.008 |
≥10 cig per day and <20 cig per day | 31 (14.1) | 62 (9.7) | 1.964 (1.210‒3.190) | 0.006 |
≥20 cig per day | 9 (4.1) | 8 (1.3) | 4.420 (1.662‒11.751) | 0.003 |
Bedroom air conditioner use/n (%) | 211 (95.9) | 575 (90.4) | 2.487 (1.214‒5.097) | 0.013 |
Dampness and mold points in bedroom/n (%) | 37 (16.8) | 47 (7.0) | 2.689 (1.695‒4.264) | 0.000 |
Seen cockroaches in bedroom/n (%) | 84 (38.2) | 145 (21.6) | 2.245 (1.617‒3.117) | 0.000 |
Room cleaning frequency/n (%) | ||||
6‒7 times per week | 95 (43.2) | 359 (53.4) | Reference | ‒ |
3‒5 times per week | 114 (51.8) | 294 (43.8) | 1.469 (1.071‒2.015) | 0.017 |
<3 times per week | 11 (5.0) | 19 (2.8) | 2.271 (1.064‒4.846) | 0.034 |
Air purifier using frequency/n (%) | ||||
Never | 164 (74.5) | 435 (64.7) | Reference | ‒ |
Only haze days | 44 (20.0) | 171 (25.5) | 0.691 (0.473‒1.010) | 0.056 |
Every day | 12 (5.5) | 66 (9.8) | 0.471 (0.248‒0.896) | 0.022 |
Home interior decoration/n (%) | 32 (14.5) | 64 (9.5) | 1.617 (1.026‒2.548) | 0.038 |
Exposure item | Asthma (n=220) | Control (n=636) | OR (95%CI) | P value |
---|---|---|---|---|
PM2.5 in utero/(μg·m-3) | 61.02±10.86 | 60.08±10.63 | 1.008 (0.994‒1.023) | 0.262 |
PM2.5 at age 1/(μg·m-3) | 57.71±8.96 | 56.16±9.81 | 1.017 (1.001‒1.034) | 0.040 |
PM2.5 at age 2/(μg·m-3) | 52.78±10.13 | 51.51±11.27 | 1.010 (0.996‒1.025) | 0.144 |
PM2.5 at age 3/(μg·m-3) | 48.36±9.67 | 46.94±10.45 | 1.013 (0.998‒1.029) | 0.079 |
表 3 重庆地区儿童生命早期PM2.5 暴露水平的单因素Logistic回归分析
Tab 3 Univariate Logistic regression analysis of PM2.5 exposure in early-life of children in Chongqing
Exposure item | Asthma (n=220) | Control (n=636) | OR (95%CI) | P value |
---|---|---|---|---|
PM2.5 in utero/(μg·m-3) | 61.02±10.86 | 60.08±10.63 | 1.008 (0.994‒1.023) | 0.262 |
PM2.5 at age 1/(μg·m-3) | 57.71±8.96 | 56.16±9.81 | 1.017 (1.001‒1.034) | 0.040 |
PM2.5 at age 2/(μg·m-3) | 52.78±10.13 | 51.51±11.27 | 1.010 (0.996‒1.025) | 0.144 |
PM2.5 at age 3/(μg·m-3) | 48.36±9.67 | 46.94±10.45 | 1.013 (0.998‒1.029) | 0.079 |
Item | OR | 95%CI | P value |
---|---|---|---|
Dampness and mold points in bedroom | 2.155 | 1.304‒3.559 | 0.003 |
Seen cockroaches in bedroom | 1.830 | 1.287‒2.601 | 0.001 |
Bedroom air conditioner use | 2.328 | 1.098‒4.937 | 0.028 |
Air purifier using frequency | |||
Never | Reference | ‒ | ‒ |
Only haze days | 0.673 | 0.451‒1.005 | 0.053 |
Every day | 0.416 | 0.213‒0.812 | 0.010 |
Family second-hand smoke exposure | 1.762 | 1.272‒2.440 | 0.001 |
PM2.5 exposure at age 1 | 1.063 | 1.034‒1.093 | 0.000 |
Home interior decoration | 2.082 | 0.946‒4.581 | 0.068 |
表 4 生命早期环境因素暴露与儿童哮喘的多因素Logistic回归分析
Tab 4 Multivariate Logistic regression of early-life environment exposure for childhood asthma
Item | OR | 95%CI | P value |
---|---|---|---|
Dampness and mold points in bedroom | 2.155 | 1.304‒3.559 | 0.003 |
Seen cockroaches in bedroom | 1.830 | 1.287‒2.601 | 0.001 |
Bedroom air conditioner use | 2.328 | 1.098‒4.937 | 0.028 |
Air purifier using frequency | |||
Never | Reference | ‒ | ‒ |
Only haze days | 0.673 | 0.451‒1.005 | 0.053 |
Every day | 0.416 | 0.213‒0.812 | 0.010 |
Family second-hand smoke exposure | 1.762 | 1.272‒2.440 | 0.001 |
PM2.5 exposure at age 1 | 1.063 | 1.034‒1.093 | 0.000 |
Home interior decoration | 2.082 | 0.946‒4.581 | 0.068 |
1 | Global Asthma Network. The Global Asthma Report 2018[EB/OL]. [2022-08-05]. http://globalasthmareport.org/resources/Global_Asthma_ Report_2018.pdf. |
2 | 全国儿科哮喘协作组, 中国疾病预防控制中心环境与健康相关产品安全所.第三次中国城市儿童哮喘流行病学调查[J]. 中华儿科杂志, 2013, 51(10): 729-735. |
The National Cooperative Group on Childhood Asthma, Institute of Environmental Health and Related Product Safety, Chinese Center for Disease Control and Prevention. Third nationwide survey of childhood asthma in urban areas of China [J]. Chinese Journal of Pediatrics, 2013, 51(10): 729-735. | |
3 | BURBANK A J, SOOD A K, KESIC M J, et al. Environmental determinants of allergy and asthma in early life[J]. J Allergy Clin Immunol, 2017, 140(1): 1-12. |
4 | LITONJUA A A, CAREY V J, BURGE H A, et al. Exposure to cockroach allergen in the home is associated with incident doctor-diagnosed asthma and recurrent wheezing[J]. J Allergy Clin Immunol, 2001, 107(1): 41-47. |
5 | DOUWES J, VAN STRIEN R, DOEKES G, et al. Does early indoor microbial exposure reduce the risk of asthma? The prevention and incidence of asthma and mite allergy birth cohort study[J]. J Allergy Clin Immunol, 2006, 117(5): 1067-1073. |
6 | STOLTZ D J, JACKSON D J, EVANS M D, et al. Specific patterns of allergic sensitization in early childhood and asthma & rhinitis risk[J]. Clin Exp Allergy, 2013, 43(2): 233-241. |
7 | MILIKU K, AZAD M B. Breastfeeding and the developmental origins of asthma: current evidence, possible mechanisms, and future research priorities[J]. Nutrients, 2018, 10(8): 995. |
8 | LOEWEN K, MONCHKA B, MAHMUD S M, et al. Prenatal antibiotic exposure and childhood asthma: a population-based study[J]. Eur Respir J, 2018, 52(1): 1702070. |
9 | TOIVONEN L, SCHUEZ-HAVUPALO L, KARPPINEN S, et al. Antibiotic treatments during infancy, changes in nasal microbiota, and asthma development: population-based cohort study[J]. Clin Infect Dis, 2021, 72(9): 1546-1554. |
10 | 洪建国. 环境污染对儿童支气管哮喘的影响[J]. 中华实用儿科临床杂志, 2015, 30(4): 241-244. |
HONG J G. Impact of pollution on asthma in childhood[J]. Chinese Journal of Applied Clinical Pediatrics, 2015, 30(4): 241-244. | |
11 | ZHANG M Z, CHU S S, XIA Y K, et al. Environmental exposure during pregnancy and the risk of childhood allergic diseases[J]. World J Pediatr, 2021, 17(5): 467-475. |
12 | AKAR-GHIBRIL N, PHIPATANAKUL W. The indoor environment and childhood asthma[J]. Curr Allergy Asthma Rep, 2020, 20(9): 43. |
13 | O'CONNOR G T, LYNCH S V, BLOOMBERG G R, et al. Early-life home environment and risk of asthma among inner-city children[J]. J Allergy Clin Immunol, 2018, 141(4): 1468-1475. |
14 | ZHANG Q L, MENG X, SHI S, et al. Overview of particulate air pollution and human health in China: evidence, challenges, and opportunities[J]. Innovation (Camb), 2022, 3(6): 100312. |
15 | 中华医学会儿科学分会呼吸学组, 《中华儿科杂志》编辑委员会. 儿童支气管哮喘诊断与防治指南(2016年版)[J]. 中华儿科杂志, 2016, 54(3): 167-181. |
Respiratory Group, Society of Pediatrics, Chinese Medical Association, Editorial Board of Chinese Journal of Pediatrics. Guidelines for the diagnosis and prevention of children′s bronchial asthma (2016 edition)[J]. Chinese Journal of Pediatrics, 2016, 54(3): 167-181. | |
16 | DENG Y T, LI X M, LIU E M, et al. Associations of early-life factors and indoor environmental exposure with asthma among children: a case-control study in Chongqing, China[J]. World J Pediatr, 2022, 18(3): 186-195. |
17 | ELLWOOD P, ASHER M I, BEASLEY R, et al. The international study of asthma and allergies in childhood (ISAAC): phase three rationale and methods[J]. Int J Tuberc Lung Dis, 2005, 9(1): 10-16. |
18 | FERRIS B G. Epidemiology standardization project Ⅱ. Recommended respiratory disease questionnaires for use with adults and children in epidemiological research[J]. Am Rev Respir Dis, 1978, 118: 7-53. |
19 | BORNEHAG C G, SUNDELL J, SIGSGAARD T. Dampness in buildings and health (DBH): report from an ongoing epidemiological investigation on the association between indoor environmental factors and health effects among children in Sweden[J]. Indoor Air, 2004, 14(Suppl 7): 59-66. |
20 | MENG X, LIU C, ZHANG L N, et al. Estimating PM2.5 concentrations in Northeastern China with full spatiotemporal coverage, 2005‒2016[J]. Remote Sens Environ, 2021, 253: 112203. |
21 | XU X, TAO S Y, HUANG L, et al. Maternal PM2.5 exposure during gestation and offspring neurodevelopment: findings from a prospective birth cohort study[J]. Sci Total Environ, 2022, 842: 156778. |
22 | 王玲, 郭蓉, 杨欢, 等. 重庆地区室内环境与儿童支气管哮喘的相关性研究[J]. 中国全科医学, 2019, 22(12): 1405-1412. |
WANG L, GUO R, YANG H, et al. Analysis between indoor environment and childhood asthma and family nursing interventions in Chongqing [J]. Chinese General Practice, 2019, 22(12): 1405-1412. | |
23 | 刘丽娟, 周玉峰. 环境烟草烟雾暴露对儿童支气管哮喘的影响[J]. 世界临床药物, 2018, 39(8): 524-529. |
LIU L J, ZHOU Y F. Influence of environmental tobacco smoke exposure to bronchial asthma in children[J]. World Clinical Drug, 2018, 39(8): 524-529. | |
24 | WANG B M, CHEN H, CHAN Y L, et al. Why do intrauterine exposure to air pollution and cigarette smoke increase the risk of asthma? [J]. Front Cell Dev Biol, 2020, 8: 38. |
25 | BONNER K, SCOTNEY E, SAGLANI S. Factors and mechanisms contributing to the development of preschool wheezing disorders[J]. Expert Rev Respir Med, 2021, 15(6): 745-760. |
26 | 国家卫生健康委员会. 中国吸烟危害健康报告2020[M]. 北京: 人民卫生出版社, 2021. |
National Health Commission of the People's Republic of China. Health hazards of smoking in China 2020[M]. Beijing: People's Medical Publishing House, 2021. | |
27 | 秦小娇, 祁媛媛, 张晓波. 住院患儿家庭烟草烟雾暴露调查[J]. 环境与健康杂志, 2020, 37(3): 242-245. |
QING X J, QI Y Y, ZHANG X B. Household environment tobacco smoke exposure in hospitalized children[J]. Journal of Environment and Health, 2020, 37(3): 242-245. | |
28 | TANG J, SHEN J, ZHANG S J, et al. A pilot study on secondhand smoke exposure among pregnant women in Chongqing, China: a combined questionnaire, saliva cotinine test, and ultrasound flow index analysis[J]. Front Public Health, 2020, 8: 290. |
29 | ZHOU X D, CAI J, ZHAO Y, et al. Estimation of residential fine particulate matter infiltration in Shanghai, China[J]. Environ Pollut, 2018, 233: 494-500. |
30 | GE E J, LAI K F, XIAO X, et al. Differential effects of size-specific particulate matter on emergency department visits for respiratory and cardiovascular diseases in Guangzhou, China[J]. Environ Pollut, 2018, 243(Pt A): 336-345. |
31 | 国家卫生健康委员会. 中华人民共和国国家标准GB/T 18883—2022, 室内空气质量标准[S/OL].(2022-07-11)[2022-08-12]. http://c.gb688.cn/bzgk/gb/showGb?type=online&hcno=6188E23AE55E8F557043401FC2EDC436. |
National Health Commission of the People's Republic of China. National Standards of the People's Republic of China: GB/T 18883—2022, standards for indoor air quality[S/OL]. (2022-07-11)[2022-08-12]. http://c.gb688.cn/bzgk/gb/showGb?type=online&hcno=6188E2 3AE55E8F557043401FC2EDC436. | |
32 | WU Y H, JIN T T, HE W, et al. Associations of fine particulate matter and constituents with pediatric emergency room visits for respiratory diseases in Shanghai, China[J]. Int J Hyg Environ Health, 2021, 236: 113805. |
33 | LIU L J, LIU C, CHEN R J, et al. Associations of short-term exposure to air pollution and emergency department visits for pediatric asthma in Shanghai, China[J]. Chemosphere, 2021, 263: 127856. |
34 | NAKHLÉ M M, FARAH W, ZIADÉ N, et al. Short-term relationships between emergency hospital admissions for respiratory and cardiovascular diseases and fine particulate air pollution in Beirut, Lebanon[J]. Environ Monit Assess, 2015, 187(4): 196. |
35 | SONG J, LU M X, ZHENG L H, et al. Acute effects of ambient air pollution on outpatient children with respiratory diseases in Shijiazhuang, China[J]. BMC Pulm Med, 2018, 18(1): 150. |
36 | WU J Z, ZHONG T L, ZHU Y, et al. Effects of particulate matter (PM) on childhood asthma exacerbation and control in Xiamen, China[J]. BMC Pediatr, 2019, 19(1): 194. |
37 | LIU S, JØRGENSEN J T, LJUNGMAN P, et al. Long-term exposure to low-level air pollution and incidence of asthma: the ELAPSE project[J]. Eur Respir J, 2021, 57(6): 2003099. |
38 | GEHRING U, BEELEN R, EEFTENS M, et al. Particulate matter composition and respiratory health: the PIAMA Birth Cohort study[J]. Epidemiology, 2015, 26(3): 300-309. |
39 | YU Z B, KOPPELMAN G H, BOER J M A, et al. Ambient ultrafine particles and asthma onset until age 20: the PIAMA birth cohort[J]. Environ Res, 2022, 214(Pt 1): 113770. |
40 | CAI J, LI B Z, YU W, et al. Associations of household dampness with asthma, allergies, and airway diseases among preschoolers in two cross-sectional studies in Chongqing, China: repeated surveys in 2010 and 2019[J]. Environ Int, 2020, 140: 105752. |
41 | HU Y, LIU W, HUANG C, et al. Home dampness, childhood asthma, hay fever, and airway symptoms in Shanghai, China: associations, dose-response relationships, and lifestyle′s influences[J]. Indoor Air, 2014, 24(5): 450-463. |
42 | SHORTER C, CRANE J, PIERSE N, et al. Indoor visible mold and mold odor are associated with new-onset childhood wheeze in a dose-dependent manner[J]. Indoor Air, 2018, 28(1): 6-15. |
43 | CAI J, LI B Z, YU W, et al. Household dampness-related exposures in relation to childhood asthma and rhinitis in China: a multicentre observational study[J]. Environ Int, 2019, 126: 735-746. |
44 | HU Y B, CHEN Y T, LIU S J, et al. Increasing prevalence and influencing factors of childhood asthma: a cross-sectional study in Shanghai, China[J]. World J Pediatr, 2021, 17(4): 419-428. |
45 | FU X, NORBÄCK D, YUAN Q Q, et al. Indoor microbiome, environmental characteristics and asthma among junior high school students in Johor Bahru, Malaysia[J]. Environ Int, 2020, 138: 105664. |
46 | CASTRO-RODRIGUEZ J A, FORNO E, RODRIGUEZ-MARTINEZ C E, et al. Risk and protective factors for childhood asthma: what is the evidence? [J]. J Allergy Clin Immunol Pract, 2016, 4(6): 1111-1122. |
47 | DU C Q, LI B Z, YU W. Indoor mould exposure: characteristics, influences and corresponding associations with built environment—a review[J]. J Build Eng, 2021, 35: 101983. |
48 | WANG H, LI B Z, YU W, et al. Early-life exposure to home dampness associated with health effects among children in Chongqing, China[J]. Build Environ, 2015, 94: 327-334. |
49 | ZHAO Z H, ZHANG X, LIU R R, et al. Prenatal and early life home environment exposure in relation to preschool children′s asthma, allergic rhinitis and eczema in Taiyuan, China[J]. Chin Sci Bull, 2013, 58(34): 4245-4251. |
50 | DONG G H, QIAN Z M, WANG J, et al. Home renovation, family history of atopy, and respiratory symptoms and asthma among children living in China[J]. Am J Public Health, 2014, 104(10): 1920-1927. |
51 | 要颖慧. 十年前后住宅室内环境与儿童过敏性疾病变化特性研究[D]. 重庆: 重庆大学, 2021. |
YAO Y H. Research on the characteristics of residential indoor environment and children's allergic diseases in recent ten years[D]. Chongqing: Chongqing University, 2021. | |
52 | SUBLETT J L. Effectiveness of air filters and air cleaners in allergic respiratory diseases: a review of the recent literature[J]. Curr Allergy Asthma Rep, 2011, 11(5): 395-402. |
53 | D'AMATO G, HOLGATE S T, PAWANKAR R, et al. Meteorological conditions, climate change, new emerging factors, and asthma and related allergic disorders. A statement of the World Allergy Organization[J]. World Allergy Organ J, 2015, 8(1): 25. |
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