北京大学学报(医学版) ›› 2022, Vol. 54 ›› Issue (2): 227-235. doi: 10.19723/j.issn.1671-167X.2022.02.005

• 论著 • 上一篇    下一篇

兰州市臭氧对儿童哮喘的短期影响及其季节性差异

张宏1,(),董继元2,王建军3,范临夏3,曲强3,刘洋1   

  1. 1.甘肃省人民医院哮喘防治中心,兰州 730000
    2.兰州大学公共卫生学院劳动卫生与环境卫生学研究所,兰州 730000
    3.甘肃省人民医院儿科,兰州 730000
  • 收稿日期:2020-06-08 出版日期:2022-04-18 发布日期:2022-04-13
  • 通讯作者: 张宏 E-mail:zhanghong2020lz@163.com
  • 基金资助:
    甘肃省人民医院院内科研基金(18GSSY4-24)

Short-term effects and seasonal variation of ozone on daily hospital outpatient visits for childhood asthma in Lanzhou

ZHANG Hong1,(),DONG Ji-yuan2,WANG Jian-jun3,FAN Lin-xia3,QU Qiang3,LIU Yang1   

  1. 1. Asthma Center, Gansu Provincial Hospital, Lanzhou 730000, China
    2. Institute of Occupational and Environmental Health, School of Public Health, Lanzhou University, Lanzhou 730000, China
    3. Department of Pediatrics, Gansu Provincial Hospital, Lanzhou 730000, China
  • Received:2020-06-08 Online:2022-04-18 Published:2022-04-13
  • Contact: Hong ZHANG E-mail:zhanghong2020lz@163.com
  • Supported by:
    Research Fund Project of Gansu Provincial Hospital(18GSSY4-24)

摘要:

目的: 分析不同季节不同度量方式的臭氧(ozone, O3)浓度对儿童哮喘门诊就诊人次的影响,探讨该影响在不同类型人群中的差异。方法: 收集兰州市三所三级甲等综合医院2014年1月1日至2017年12月31日儿童哮喘门诊的就诊资料,收集同期空气污染数据和气象数据,考虑到O3浓度与儿童哮喘门诊就诊人次及气象因素之间的非线性关系,利用广义相加时间序列模型分析O3浓度变化与儿童哮喘门诊就诊人次的短期关联性,同时进一步对性别、年龄进行分层分析,考虑到O3在1 d内浓度变化情况,同时采用每日1 h最大值浓度(O3max1h)、每日8 h最大值浓度(O38h)以及每日24 h均值浓度(O324h)这三种O3暴露的不同度量方式作为O3短期暴露指标,并分别开展模型分析。结果: 夏季时,O3短期暴露水平的升高对于儿童哮喘门诊就诊人次的增加有显著影响。在滞后当天(lag0)的情况下,大气O3max1h浓度每增加10 μg/m3,儿童哮喘门诊就诊人次增加3.351% (95%CI:1.231%~5.516%);O38h浓度每增加10 μg/m3,儿童哮喘门诊就诊人次增加3.320% (95%CI:0.197%~3.829%);O324h浓度每增加10 μg/m3,夏季儿童哮喘门诊就诊人次增加6.600% (95%CI:0.914%~12.607%);此外,O3max1h暴露增加也会引起0~5岁儿童及男性哮喘门诊就诊人次的显著增加。结论: 兰州市夏季时O3短期暴露水平的升高对于儿童哮喘门诊就诊风险的增加有显著影响,O3max1h与儿童哮喘门诊就诊人次增加的关联更密切。

关键词: 臭氧, 空气污染物, 儿童, 哮喘, 门诊病人

Abstract:

Objective: To analyze the effects of ozone (O3) concentrations measured with different approaches across different seasons on the total number of childhood asthma-related clinical visits, as well as the differentiation of such effects across different groups of patients. Methods: The outpatient data of three grade A tertiary hospitals in Lanzhou City spanning from 1 January 2014 to 31 December 2017, as well as air pollution and meteorological data during the same period were collected. Considering the nonlinear relationship between O3 concentrations and the total number of childhood asthma-related clinical visits and meteorological factors, a generalized additive temporal sequence model was employed to analyze the short-term association between changes in O3 concentrations and the total number of childhood asthma-related clinical visits. Taking into account of the variations in O3 concentrations within 1 day, this study adopted different measurement approaches to address the three types of O3 exposures, namely, the maximum 1 h daily concentration (O3max1h), the maximum 8 h daily concentration (O38h) and the mean 24 h daily concentration (O324h) as the short term exposure indicators to O3, followed by a model-based analysis. Results: The increase in short-term exposure levels to O3 in summer had a significant effect on the increase in the total number of childhood asthma-related clinical visits. With lag0 for the current day, every 10 μg/m3 increase in atmospheric concentration of O3max1h was associated with an increase in the total number of childhood asthma-related clinical visits by 3.351% (95%CI: 1.231%-5.516%); for every 10 μg/m3 increase in O38h concentration, the total number of childhood asthma-related clinical visits increased by 3.320% (95%CI: 0.197%-3.829%); for every 10 μg/m3increase in O324h concentration, the total number of childhood asthma-related clinical visits in summer increased by 6.600% (95%CI: 0.914%-12.607%); moreover, an increase in exposure to O3max1h also led to a significant rise in the total number of childhood asthma-related clinical visits among the males. Conclusion: The increase in short-term exposure levels to O3 in summer in Lanzhou City has a significant effect on the increase in the total number of childhood asthma-related clinical visits; O3max1h is more closely correlated with the increase in the total number of childhood asthma-related clinical visits.

Key words: Ozone, Air pollutants, Child, Asthma, Outpatients

中图分类号: 

  • R725.6

表1

2014—2017年兰州市儿童哮喘日门诊就诊人次的描述性分析"

Category x -±s Minimum Percentile Maximum
P25 P50 P75
0-14 years 6±3 1 3 5 7 31
Male 4±2 1 2 3 5 20
Female 2±1 1 1 2 3 12
0-5 years 4±2 1 2 3 5 15
6-14 years 2±1 1 1 2 4 17
Spring 4±2 1 2 4 6 18
Summer 6±4 1 3 5 8 22
Autumn 5±3 1 3 5 8 31
Winter 3±1 1 2 4 6 14

表2

2014—2017年兰州市气象因素各指标和空气污染物的描述性分析"

Category x -±s Minimum Percentile Maximum
P25 P50 P75
Meteorological factors
Temperature/℃ 11.28±9.64 -12.30 2.45 12.90 19.80 29.90
Relative humidity/% 50.83±15.15 18.00 39.00 50.02 61.74 96.09
Air pollutants
PM2.5/(μg/m3) 53.30±27.19 12.73 35.40 45.69 63.59 269.43
PM10/(μg/m3) 122.90±78.25 18.98 81.00 107.94 145.25 1484.54
SO2/(μg/m3) 22.39±14.47 3.54 10.88 18.29 30.42 81.87
NO2/(μg/m3) 45.98±15.74 7.80 36.40 45.36 52.90 146.60
CO/(mg/m3) 1.34±0.73 0.34 0.83 1.09 1.62 4.65

表3

2014—2017年兰州市臭氧浓度不同度量方式的描述性分析"

Category x -±s Minimum Percentile Maximum
P25 P25 P25
O3max1h/(μg/m3) 77.59±33.44 15.00 57.20 69.40 82.40 252.60
Spring 83.38±33.80 36.50 62.00 72.60 86.90 197.80
Summer 87.28±41.93 28.40 63.20 71.00 87.50 252.60
Autumn 73.15±28.77 15.00 54.40 68.00 82.80 195.20
Winter 66.29±21.59 15.80 52.20 62.00 77.20 158.60
O38h/(μg/m3) 84.03±36.53 8.00 56.00 78.00 106.00 221.00
Spring 99.23±32.82 20.00 78.00 98.00 118.00 221.00
Summer 104.43±39.93 10.00 76.00 103.00 134.00 197.00
Autumn 72.02±29.93 8.00 51.00 67.00 87.00 182.00
Winter 59.94±19.88 15.00 46.00 58.00 71.00 140.00
O324h/(μg/m3) 38.70±19.97 4.94 24.52 33.96 48.31 126.11
Spring 44.81±20.36 14.30 29.18 40.60 56.59 116.26
Summer 48.36±22.78 17.23 32.22 40.61 56.21 126.11
Autumn 31.42±14.5 8.03 20.75 28.51 38.01 84.56
Winter 29.91±13.74 4.94 19.17 26.96 38.25 78.58

表4

不同滞后天数O3max1h浓度每升高10 μg/m3儿童哮喘门诊就诊人次的超额危险度"

Lag days ER (95%CI)
Spring Summer Autumn Winter
Lag0 1.358 (0.126 to 2.606)* 3.351 (1.231 to 5.516)* 2.359 (1.052 to 3.683)* 1.972 (0.484 to 3.482)*
Lag1 0.233 (-0.978 to 1.458) -1.312 (-3.078 to 0.486) -1.868 (-3.180 to 0.539) -0.878 (-2.268 to 0.531)
Lag2 -0.122 (-1.377 to 1.149) -0.450 (-1.961 to 1.084) -1.431 (-2.776 to 0.068) 0.229 (-1.152 to 1.630)
Lag3 -1.070 (-2.429 to 0.308) 0.136 (-1.504 to 1.803) -0.311 (-1.606 to 1.002) -1.055 (-2.613 to 0.529)
Lag4 -0.024 (-1.257 to 1.225) -0.662 (-2.318 to 1.022) 0.035 (-1.287 to 1.375) 0.626 (-0.837 to 2.110)
Lag5 0.542 (-0.744 to 1.844) 1.419 (-0.164 to 3.027) -0.191 (-1.537 to 1.175) -0.136 (-1.543 to 1.291)
Lag6 0.301 (-0.906 to 1.523) 0.491 (-1.216 to 2.227) -0.131 (-1.496 to 1.253) -0.932 (-2.349 to 0.506)
Lag7 0.474 (-0.832 to 1.797) -2.552 (-4.981 to 0.062) -0.740 (-2.037 to 0.575) 0.506 (-1.054 to 2.090)
Lag01 1.536 (-0.163 to 3.264) 0.929 (-1.510 to 3.428) -2.687 (-4.375 to 0.969) 0.814 (-1.030 to 2.694)
Lag02 1.961 (-0.216 to 4.186) 0.304 (-2.679 to 3.379) -2.884 (-4.943 to 0.779) 0.884 (-1.221 to 3.033)
Lag03 1.419 (-1.192 to 4.100) 0.528 (-3.179 to 4.377) -3.018 (-5.423 to 0.551) 0.270 (-2.221 to 2.824)
Lag04 1.347 (-1.671 to 4.457) -0.656 (-5.24 to 4.149) -1.678 (-4.610 to 1.344) 1.293 (-2.044 to 4.743)
Lag05 2.298 (-1.314 to 6.043) 1.651 (-4.132 to 7.782) -2.068 (-5.560 to 1.552) 1.399 (-2.970 to 5.964)
Lag06 1.769 (-2.055 to 5.743) 3.614 (-3.852 to 11.659) -2.254 (-6.414 to 2.092) -0.008 (-5.804 to 6.145)
Lag07 0.982 (-2.616 to 4.712) 1.127 (-7.630 to 10.714) -3.721 (-8.703 to 1.533) 0.765 (-6.056 to 8.082)

表5

不同滞后天数O38h浓度每升高10 μg/m3儿童哮喘门诊就诊人次的超额危险度"

Lag days ER (95%CI)
Spring Summer Autumn Winter
Lag0 -0.383 (-1.579 to 0.828) 3.320 (0.197 to 3.829)* 0.552 (-1.149 to 2.283) -2.203 (-3.787 to -0.593)
Lag1 0.360 (-0.855 to 1.590) -1.689 (-3.761 to 0.428) 0.046 (-1.53 to 1.648) -0.232 (-1.869 to 1.432)
Lag2 -1.449 (-2.869 to -0.008) -1.106 (-3.083 to 0.912) 0.272 (-1.324 to 1.895) 1.171 (-0.359 to 2.724)
Lag3 0.590 (-0.805 to 2.005) 1.074 (-1.636 to 3.860) -0.511 (-2.148 to 1.154) 0.166 (-1.401 to 1.757)
Lag4 1.367 (-0.001 to 2.753) 2.747 (-1.046 to 6.685) 0.299 (-1.281 to 1.903) 0.762 (-0.767 to 2.315)
Lag5 -0.400 (-1.672 to 0.888) -3.538 (-7.437 to 0.525) 0.261 (-1.279 to 1.825) -0.841 (-2.353 to 0.695)
Lag6 0.313 (-0.91 to 1.552) -0.361 (-4.213 to 3.646) 0.273 (-1.242 to 1.811) -0.362 (-1.941 to 1.243)
Lag7 0.060 (-1.497 to 1.641) -0.597 (-4.584 to 3.557) 1.038 (-0.566 to 2.667) -0.895 (-2.404 to 0.637)
Lag01 0.251 (-1.248 to 1.772) 0.542 (-2.186 to 3.346) 0.550 (-1.652 to 2.801) -2.429 (-4.610 to 0.197)
Lag02 0.575 (-1.169 to 2.349) -0.559 (-4.371 to 3.406) 0.813 (-1.801 to 3.496) -1.481 (-4.234 to 1.35)
Lag03 0.052 (-2.056 to 2.206) 1.880 (-3.507 to 7.568) 0.822 (-2.172 to 3.907) -2.040 (-5.409 to 1.448)
Lag04 0.140 (-2.718 to 3.081) 2.916 (-2.582 to 8.724) 1.124 (-2.367 to 4.74) -2.219 (-6.268 to 2.004)
Lag05 0.864 (-2.969 to 4.848) 0.377 (-5.828 to 6.991) 1.251 (-2.773 to 5.441) -4.524 (-9.092 to 0.274)
Lag06 -2.218 (-6.916 to 2.716) -1.961 (-8.973 to 5.591) 1.300 (-3.317 to 6.137) -5.045 (-10.445 to 0.680)
Lag07 -2.271 (-7.518 to 3.273) -3.019 (-11.132 to 5.835) 2.307 (-3.077 to 7.990) -6.712 (-8.969 to 0.050)

表6

不同滞后天数O324h浓度每升高10 μg/m3儿童哮喘门诊就诊人次的超额危险度"

Lag days ER (95%CI)
Spring Summer Autumn Winter
Lag0 -1.055 (-2.897 to 0.821) 6.600 (0.914 to 12.607)* 1.752 (-0.647 to 4.209) -2.261 (-6.110 to 1.745)
Lag1 -0.498 (-2.373 to 1.413) 3.552 (-0.338 to 7.593) -2.468 (-5.130 to 0.269) -4.455 (-8.325 to 0.421)
Lag2 -1.088 (-3.358 to 1.236) -2.162 (-5.842 to 1.662) -0.634 (-3.473 to 2.289) -0.220 (-3.861 to 3.559)
Lag3 -0.751 (-2.996 to 1.546) -0.539 (-4.299 to 3.369) 2.593 (-1.779 to 7.160) 1.874 (-1.838 to 5.726)
Lag4 -0.196 (-2.382 to 2.038) 1.187 (-2.568 to 5.087) 3.030 (-2.183 to8.520) 2.030 (-1.794 to 6.004)
Lag5 -0.033 (-2.051 to 2.027) -2.107 (-5.866 to 1.802) 3.273 (-2.055 to 8.891) -0.651 (-4.319 to 3.156)
Lag6 1.091 (-0.798 to 3.016) 0.511 (-3.342 to 4.518) 1.103 (-4.161 to 6.656) -2.145 (-5.963 to 1.829)
Lag7 1.067 (-1.232 to 3.418) 1.505 (-2.498 to 5.672) -1.963 (-6.748 to 3.067) -0.133 (-3.848 to 3.726)
Lag01 -0.509 (-2.745 to 1.779) 8.115 (-2.446 to 14.098) -0.117 (-3.645 to 3.542) -6.442 (-11.553 to 1.036)
Lag02 -0.801 (-3.425 to 1.895) 6.567 (-0.357 to 13.972) -2.218 (-7.136 to 2.960) -6.086 (-12.403 to 0.686)
Lag03 -1.475 (-4.674 to 1.831) 6.014 (-1.878 to 14.54) -1.225 (-7.883 to 5.915) -4.232 (-11.895 to 4.098)
Lag04 -1.773 (-5.757 to 2.38) 6.749 (-2.012 to 16.294) -0.938 (-9.439 to 8.360) -2.028 (-11.291 to 8.204)
Lag05 -2.023 (-6.667 to 2.851) 3.623 (-6.055 to 14.299) 0.186 (-10.06 to 11.600) -2.631 (-13.478 to 9.575)
Lag06 -1.232 (-6.561 to 4.400) 4.382 (-6.527 to 16.564) 2.964 (-10.017 to 17.817) -6.308 (-12.75 to 8.038)
Lag07 0.816 (-5.114 to 7.117) 4.637 (-7.882 to 18.858) -1.652 (-14.032 to 12.511) -6.538 (-11.281 to 9.966)

表7

O3max1h浓度每升高10 μg/m3时不同性别和年龄儿童哮喘门诊就诊人次的超额危险度"

Variables ER(95%CI)
Spring Summer Autumn Winter
Male 0.382 (-1.478 to 2.277) 1.997 (0.197 to 3.829)* 4.877 (0.818 to 9.099)* 2.030 (1.794 to 6.004)*
Female 0.639 (-0.556 to 1.849) 1.752 (-0.647 to 4.209) 0.552 (-1.149 to 2.283) 0.762 (-0.767 to 2.315)
0-5 years 1.551 (-0.314 to 3.451) 3.351 (1.231 to 5.516)* 5.805 (0.686 to 11.185)* 2.162 (0.556 to 3.794)*
6-14 years -0.250 (-2.683 to 2.244) 2.945 (-0.033 to 6.012) 0.939 (-0.578 to 2.480) 1.367 (-3.392 to6.361)

表8

O38h浓度每升高10 μg/m3时不同性别和年龄儿童哮喘门诊就诊人次的超额危险度"

Variables ER(95%CI)
Spring Summer Autumn Winter
Male 1.713 (-0.626 to 4.108) 1.973 (-1.581 to 5.656) 1.987 (-0.092 to 4.108) 1.215 (-0.825 to 3.297)
Female 0.486 (-2.410 to 3.468) -1.249 (-5.536 to 3.232) 1.713 (-4.501 to 8.331) -0.727 (-7.147 to 6.137)
0-5 years 0.226 (-1.662 to 2.150) 3.521 (0.806 to 6.309)* 2.926 (1.250 to 4.629)* 1.394 (-0.378 to 3.198)
6-14 years 1.669 (-0.135 to 3.506) -0.606 (-3.688 to 2.574) 0.331 (-2.276 to 3.007) 0.973 (-1.884 to 3.913)

表9

O324h浓度每升高10 μg/m3时不同性别和年龄儿童哮喘门诊就诊人次的超额危险度"

Variables ER(95%CI)
Spring Summer Autumn Winter
Male 1.576 (-0.050 to 3.126) 5.805 (-0.686 to 11.185) 1.310 (-0.733 to 3.395) 1.603 (-2.120 to 5.469)
Female 1.948 (-0.588 to 4.549) 4.342 (-4.905 to 14.489) 0.579 (-1.416 to 2.613) 0.759 (-1.557 to 3.130)
0-5 years -0.595 (-4.263 to 3.213) 7.106 (-4.832 to 20.542) 0.379 (-5.174 to 6.257) 2.610 (-1.229 to 6.599)
6-14 years 0.262 (-1.938 to 2.512) 3.499 (-4.179 to 11.791) -0.280 (-2.530 to 2.023) -0.102 (-4.990 to 5.038)

表10

双污染物模型O3浓度每升高10 μg/m3时儿童哮喘门诊就诊人次的超额危险度"

Variables ER(95%CI)
O3max1h O38h O324h
Single model 3.351 (1.231 to 5.516) 3.320 (0.197 to 3.829) 6.600 (0.914 to 12.607)
O3+PM2.5 3.127 (1.513 to 5.195) 3.193 (0.124 to 3.768) 6.456 (0.637 to 11.208)
O3+PM10 3.191 (1.581 to 5.255) 3.055 (0.148 to 3.794) 6.573 (0.733 to 10.137)
O3+NO2 3.477 (1.501 to 5.310) 3.446 (0.136 to 3.789) 6.671 (0.724 to 12.428)
O3+ SO2 3.085 (1.239 to 4.985) 3.342 (0.092 to 3.609) 6.774 (1.028 to 12.834)
O3+ CO 3.338 (1.644 to 5.484) 3.415 (0.216 to 3.846) 6.929 (1.386 to 13.202)
O3+SO2+NO2 3.329 (1.167 to 5.321) 3.120 (0.169 to 3.629) 6.687 (1.014 to 11.307)
O3+SO2+PM10 3.253 (1.118 to 5.476) 3.097 (0.117 to 3.466) 6.471 (0.971 to 11.671)
O3+SO2+PM2.5 3.355 (1.138 to 5.383) 3.155 (0.127 to 3.491) 6.565 (0.833 to 10.782)
O3+SO2+CO 3.402 (1.136 to 5.289) 3.421 (0.135 to 3.742) 6.524 (0.901 to 11.763)
O3+NO2+PM10 3.338 (1.192 to 5.409) 3.351 (0.102 to 3.573) 6.684 (1.012 to 12.213)
O3+NO2+PM2.5 3.385 (1.216 to 5.446) 3.285 (0.187 to 3.446) 6.529 (1.206 to 12.102)
O3+NO2+CO 3.379 (1.197 to 5.229) 3.460 (0.201 to 3.733) 6.721 (1.314 to 12.786)
O3+PM10+PM2.5 3.293 (1.124 to 5.268) 3.172 (0.144 to 3.776) 6.456 (0.637 to 10.208)
O3+PM10+CO 3.275 (1.148 to 5.294) 3.155 (0.141 to 3.664) 6.473 (0.704 to 10.375)
O3+PM2.5+CO 3.401 (1.136 to 5.789) 3.246 (0.151 to 3.704) 6.571 (0.745 to 11.123)

表11

不同时间自由度O3浓度每升高10 μg/m3时儿童哮喘门诊就诊人次的超额危险度的敏感性分析"

Items ER(95%CI)
O3max1h O38h O324h
df=6 3.330 (1.345 to 5.354) 3.463 (0.267 to 3.924) 6.676 (0.868 to 11.371)
df=7 3.351 (1.231 to 5.516) 3.320 (0.197 to 3.829) 6.600 (0.914 to 12.607)
df=8 3.502 (1.449 to 5.597) 3.464 (0.247 to 3.955) 6.562 (0.843 to 11.426)
df=9 3.238 (1.435 to 5.385) 3.249 (0.104 to 3.832) 6.452 (1.007 to 11.833)
df=10 3.279 (1.258 to 5.488) 3.399 (0.158 to 3.886) 6.712 (0.945 to 12.030)
[1] 徐甜, 王志远, 张兵, 等. 中国环境保护重点城市空气质量指数时空变化特征[J]. 中国公共卫生, 2016, 32(8):1027-1031.
[2] Ferrante G, Antona R, Malizia V, et al. Asthma and air pollution[J]. Ital J Pediatr, 2014, 40(S1):A75.
doi: 10.1186/1824-7288-40-S1-A75
[3] Zhang YW, Ni H, Bai LJ, et al. The short-term association between air pollution and childhood asthma hospital admissions in urban areas of Hefei City in China: A time-series study[J]. Environ Pollut, 2019, 169:510-516.
[4] Ding L, Zhu DJ, Peng DH, et al. Air pollution and asthma attacks in children: A case-crossover analysis in the city of Chongqing, China[J]. Environ Pollut, 2017, 220(PtA):348-353.
doi: 10.1016/j.envpol.2016.09.070
[5] Dai YR, Qiu H, Sun SZ, et al. Age-dependent effect of ambient ozone on emergency asthma hospitalizations in Hong Kong[J]. J Allergy Clin Immun, 2018, 141(4):1532-1534.
doi: 10.1016/j.jaci.2018.01.006
[6] 杨春雪. 细颗粒物和臭氧对我国居民死亡影响的急性效应研究[D]. 上海: 复旦大学, 2012.
[7] 闫美霖. 广州市越秀区臭氧短期暴露与人群死亡风险的时间序列研究及健康风险评估[D]. 北京: 北京大学, 2013.
[8] 尹伊. 基于CMAQ模式、MEIC清单对兰州市主城区臭氧污染特征的初步研究[D]. 兰州: 兰州大学, 2019.
[9] Ko FWS, Tam W, Wong TW, et al. Effects of air pollution on asthma hospitalization rates in different age groups in Hong Kong[J]. Clin Exp Allergy, 2007, 37(9):1312-1319.
pmid: 17845411
[10] 班婕, 李湉湉. 北京市不同度量方式下臭氧短期暴露人群急性健康效应研究[J]. 环境与健康杂志, 2016, 33(4):287-291.
[11] Capraz O, Deniz A, Dogan N, et al. Effects of air pollution on respiratory hospital admissions in Istanbul, Turkey, 2013 to 2015[J]. Chemosphere, 2017, 181:544-550.
doi: 10.1016/j.chemosphere.2017.04.105
[12] Chang Q, Liu S, Chen ZJ, et al. Association between air pollutants and outpatient and emergency hospital visits for childhood asthma in Shenyang City of China[J]. Int J Biometeorol, 2020, 64(9):1539-1548.
doi: 10.1007/s00484-020-01934-9 pmid: 32388688
[13] Lee JT, Cho YS, Son JY. Relationship between ambient ozone concentrations and daily hospital admissions for childhood asthma/atopic dermatitis in two cities of Korea during 2004-2005[J]. Int J Environ Health Res, 2010, 20(1):1-11.
doi: 10.1080/09603120903254033
[14] Petroeschevsky A, Simpson RW, Thalib L, et al. Associations between outdoor air pollution and hospital admissions in Brisbane, Australia[J]. Arch Environ Health, 2001, 56(1):37-52.
doi: 10.1080/00039890109604053
[15] Li TT, Yan ML, Ma WJ, et al. Short-term effects of multiple ozone metrics on daily mortality in a megacity of China[J]. Environ Sci Pollut Res Int, 2015, 22(11):8738-8746.
doi: 10.1007/s11356-014-4055-5
[16] Yang CX, Yang HB, Guo S, et al. Alternative ozone metrics and daily mortality in Suzhou: The China Air Pollution and Health Effects Study (CAPES)[J]. Sci Total Environ, 2012, 426:83-89.
doi: 10.1016/j.scitotenv.2012.03.036
[17] 刘金悦. 济南市大气污染与儿童呼吸系统疾病住院量的相关性分析[D]. 济南: 济南大学, 2019.
[18] 陈浪. 石家庄市空气污染对儿童呼吸系统疾病门诊影响及温度的修饰效应[D]. 石家庄: 华北理工大学, 2019.
[19] 马依拉·尔肯. 乌鲁木齐市大气污染物,气象因素与儿童哮喘住院人数的相关研究[D]. 乌鲁木齐: 新疆医科大学, 2014.
[1] 闫辉,逄璐,李雪迎,杨文双,蒋世菊,刘平,闫存玲. 单中心就诊2~18岁儿童胆固醇水平异常发生率及病因分析[J]. 北京大学学报(医学版), 2022, 54(2): 217-221.
[2] 冯莎蔚,国慧,王勇,赵一姣,刘鹤. 乳牙数字化参考牙冠模型的初步构建[J]. 北京大学学报(医学版), 2022, 54(2): 327-334.
[3] 王子靖,李在玲. 有幽门螺杆菌感染家族史儿童胃部菌群的特点[J]. 北京大学学报(医学版), 2021, 53(6): 1115-1121.
[4] 刘雅菲,宋琳琳,邢茂炜,蔡立新,王东信. 全身麻醉下小儿开颅术术中心脏前负荷动态指标的一致性分析[J]. 北京大学学报(医学版), 2021, 53(5): 946-951.
[5] 陈曼曼,杨招庚,苏彬彬,李艳辉,高迪,马莹,马涛,董彦会,马军. 中山市儿童青少年青春期身高生长突增规律[J]. 北京大学学报(医学版), 2021, 53(3): 506-510.
[6] 杨雪,孙伟,王哲,姬爱平,白洁. 儿童和青少年牙外伤急诊患者临床分析[J]. 北京大学学报(医学版), 2021, 53(2): 384-389.
[7] 毕书红,李紫繁,汪涛,王悦,张晨,计虹,石菊. 肾病患者医疗花费趋势研究——基于北京市某三甲医院的分析[J]. 北京大学学报(医学版), 2021, 53(1): 215-219.
[8] 张子一,夏斌,徐明明,李毅萍,唐瞻贵,陈泳清. 湖南韶山地区儿童口腔卫生干预效果评价[J]. 北京大学学报(医学版), 2020, 52(5): 913-918.
[9] 陈小贤,钟洁,闫文娟,张红梅,姜霞,黄芊,薛世华,刘星纲. 树脂冠修复乳前牙的临床效果评价[J]. 北京大学学报(医学版), 2020, 52(5): 907-912.
[10] 陈嘉惠,胡大宇,贾旭,牛薇,邓芙蓉,郭新彪. 大气臭氧短期监测指标与健康年轻人肺功能和气道炎症的关联[J]. 北京大学学报(医学版), 2020, 52(3): 492-499.
[11] 张维宇,夏秋翔,胡浩,陈京文,孙屹然,许克新,张晓鹏. 门诊女性下尿路症状患者尿动力学检查结果分析及逼尿肌无力患者的随访[J]. 北京大学学报(医学版), 2019, 51(5): 856-862.
[12] 李军,顾芳,李在玲,吕愈敏. 北京单中心回顾性分析儿童肠镜临床特点及疾病谱12年演变[J]. 北京大学学报(医学版), 2019, 51(5): 819-823.
[13] 陶春燕,李红霞,李雪迎,唐朝枢,金红芳,杜军保. 体位性心动过速综合征儿童及青少年在直立试验中血流动力学变化[J]. 北京大学学报(医学版), 2019, 51(3): 414-421.
[14] 高玲,刘云,杨旭东. 鼻喷右美托咪定在儿童口腔门诊全身麻醉前的镇静效果[J]. 北京大学学报(医学版), 2018, 50(6): 1078-1082.
[15] 盖晓燕,常春,王娟,梁瀛,李美娇,孙永昌,贺蓓,姚婉贞. 中性粒细胞型哮喘患者的气道炎症与小气道重构分析[J]. 北京大学学报(医学版), 2018, 50(4): 645-650.
Viewed
Full text


Abstract

Cited

  Shared   
  Discussed   
[1] 成刚, 钱振华, 胡军. 艾滋病项目自愿咨询检测的技术效率分析[J]. 北京大学学报(医学版), 2009, 41(2): 135 -140 .
[2] 卢恬, 朱晓辉, 柳世庆, 郑杰, 邱晓彦. 白细胞介素2促进宫颈癌细胞系HeLaS3免疫球蛋白G的表达[J]. 北京大学学报(医学版), 2009, 41(2): 158 -161 .
[3] 张燕, 韩志慧, 钟延丰, 王盛兰, 李玲玲, 郑丹枫. 骨骼肌活组织检查病理诊断技术的改进及应用[J]. 北京大学学报(医学版), 2009, 41(4): 459 -462 .
[4] Jian-wei GU, Emily YOUNG, Zhi-jun PAN, Kevan B. TUCKER, Megan SHPARAGO, Min HUANG, Amelia Purser BAILEY. SD大鼠长期高盐饮食可导致其高血压并改变肾细胞因子基因表达谱[J]. 北京大学学报(医学版), 2009, 41(5): 505 -515 .
[5] 李宏亮*, 安卫红*, 赵扬玉, 朱曦. 妊娠合并高脂血症性胰腺炎行血液净化治疗1例[J]. 北京大学学报(医学版), 2009, 41(5): 599 -601 .
[6] 赵奇, 薛世华, 刘志勇, 吴凌云. 同向施压测定自酸蚀与全酸蚀粘接系统粘接强度[J]. 北京大学学报(医学版), 2010, 42(1): 82 -84 .
[7] 马明信. 重视并提高疑难/罕见淋巴瘤的诊治[J]. 北京大学学报(医学版), 2007, 39(4): 342 .
[8] 常杏芝, 卢红梅, 张月华, 秦炯. 以高血压与红斑肢痛为主要表现的汞中毒一例[J]. 北京大学学报(医学版), 2007, 39(4): 377 -380 .
[9] 朱炳梅, 李婷, 周玉玲, 宋泉声, 王露. 新的潜在的雄激素受体协同抑制因子CMTM1-v17[J]. 北京大学学报(医学版), 2007, 39(4): 388 -393 .
[10] 赵会, 唐顺, 曲华毅, 郭卫, 李晓, 彭长亮. 四种不同尤文肉瘤树突状细胞免疫疫苗的体内外抗肿瘤免疫应答研究[J]. 北京大学学报(医学版), 2007, 39(4): 403 -408 .