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Table 5 Combined effects of habitual physical activity, long-term PM2.5 exposure, and COPD incidence in the UK Biobank

From: Risk/benefit tradeoff of habitual physical activity and air pollution on chronic pulmonary obstructive disease: findings from a large prospective cohort study

PA levels a

PM2.5 levels (HR, 95% CI) a, b

RERI c

P for interaction d

High

Moderate

Low

Moderate PM2.5 level

Low PM2.5 level

 

Self-reported PA

     

0.805

 Low

1.000

1.026 (0.909, 1.159)

0.955 (0.840, 1.085)

   

 Moderate

0.792 (0.711, 0.881)

0.753 (0.674, 0.840)

0.747 (0.667, 0.836)

− 0.01 (− 0.18, 0.17)

0.02 (− 0.14, 0.19)

 

 High

0.745 (0.668, 0.831)

0.736 (0.658, 0.822)

0.681 (0.607, 0.764)

0.01 (− 0.16, 0.18)

0.02 (− 0.15, 0.19)

 

Objectively measured PA

     

0.998

 Low

1.000

1.088 (0.885, 1.337)

0.923 (0.740, 1.152)

   

 Moderate

0.755 (0.592, 0.963)

0.790 (0.620, 1.006)

0.735 (0.573, 0.943)

− 0.05 (− 0.35, 0.25)

0.06 (− 0.23, 0.34)

 

 High

0.693 (0.527, 0.911)

0.653 (0.492, 0.866)

0.574 (0.432, 0.764)

− 0.13 (− 0.44, 0.18)

0.02 (− 0.14, 0.19)

 
  1. Abbreviations: HR hazard ratio, CI confidence interval, RERI relative excess risk due to interaction, PA physical activity, PM2.5 particulate matter with aerodynamic diameter < 2.5 μm, COPD chronic obstructive pulmonary disease
  2. a: PM2.5 exposure levels (low, moderate, and high) were defined by PM2.5 tertiles (< 9.48 μg/m3, 9.48 to 10.27 μg/m3, and ≥10.27 μg/m3), self-reported PA levels were defined according to a standard scoring criteria of International Physical Activity Questionnaire (IPAQ): low (< 600 MET-min/week), moderate (600 to 3000 MET-min/week), and high (≥3000 MET-min/week), and objectively measured PA levels were defined by objectively measured PA tertiles (< 24.32 milli-gravity (mg), 24.32 to 30.70 mg, and ≥ 30.70 mg)
  3. bAll results were calculated based on covariates in Model 3: age at enrolment, sex, ethnicity, BMI, education, household income, employment status, smoking status, alcohol drinking, fruit and vegetable intake, secondhand smoke exposure, and Townsend deprivation index
  4. c The estimates of RERI were calculated based on the reference group with high level of PM2.5 exposure and low level of PA
  5. d Likelihood tests were applied to test the significance of interaction term by comparing the model with and without the interaction term