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Table 4 Associations of oil spill exposure characteristics and nonfatal MI occurring after December 31st 2010. GuLF STUDY 2010–2013

From: Deepwater Horizon oil spill exposures and nonfatal myocardial infarction in the GuLF STUDY

 

MI cases/ total Na

RRb (95% CI)

 

Among workers and non-workers (N = 30,946; 135 cases)

Worked on clean-up

 Yes

112/23362

1.83 (1.13, 2.94)

 No

20/6852

ref

Residential proximity to oil spillc

 Direct/indirect

95/18444

1.17 (0.79, 1.74)

 Away from the spill

37/11770

ref

 

Among clean-up workers only (n = 23,896; 114 cases)

Maximum exposure jobd

 Response Work

14/4305

0.61 (0.29, 1.27)

 Operations Work

25/4200

0.97 (0.50, 1.89)

 Clean-up on Water

17/3603

0.76 (0.38, 1.55)

 Decontamination

26/3436

1.66 (0.87, 3.16)

 Clean-up on Land

14/3484

0.88 (0.43, 1.82)

 Administrative Support

16/4334

ref

Work duration

  > 180 days

33/5157

1.99 (0.98, 4.04)

 91–180 days

38/8038

1.35 (0.67, 2.70)

 31–90 days

31/7314

1.27 (0.63, 2.59)

 1–30 days

10/2853

ref

Ever had to stop work due to heatd

 Yes

51/7201

1.85 (1.25, 2.73)

 No

55/13827

ref

Worked near burning oild

 Yes

9/2068

0.93 (0.47, 1.84)

 No

103/21294

ref

Maximum overall THC exposure

  ≥ 3.00 ppm

16/3315

1.34 (0.65, 2.76)

 1.00–2.99 ppm

35/7169

1.05 (0.56, 1.96)

 0.30–0.99 ppm

46/7662

1.65 (0.91, 2.99)

  < 0.30 ppm

15/5190

ref

  1. aNumber of observations included in the fully adjusted model, by exposure status
  2. bRisk ratios (RR) adjusting for age, gender, BMI, education, smoking and residential proximity to the oil spill
  3. cModels adjust for duration of clean-up work in addition to the confounders age, gender, BMI, education, and smoking
  4. dModels adjust for duration of clean-up work in addition to the confounders age, gender, BMI, education, smoking and residential proximity to the oil spill