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. Author manuscript; available in PMC: 2019 Jan 1.
Published in final edited form as: Sci Total Environ. 2017 Aug 18;610-611:802–809. doi: 10.1016/j.scitotenv.2017.08.024

Table 2.

Premature deaths and illnesses attributable to wildfire-related PM2.5 concentrations in each year calculated using alternative concentration-response functions (95% confidence intervals)

Endpoint Year
2008 2009 2010 2011 2012
Respiratory Hospital Admissions
  Delfino et al. (2009) 8,500 5,200 6,200 6,300 6,400
(4,400—12,000) (2,700—7,700) (3,200—9,100) (3,300—9,300) (3,300—9,400)
  Zanobetti et al. (2009) 6,300 3,900 4,600 4,700 4,800
(3,600—9,000) (2,300—5,500) (2,600—6,500) (2,700—6,700) (2,800—6,800)

Cardiovascular Hospital Admissions
  Delfino et al. (2009) 2,800 1,700 2,100 2,100 2,100
(−500−−6,000) (−320−−3,700) (−380−−4,400) (−380−−4,500) (−390−−4,600)

Premature deaths from short-term exposure to PM2.5
  Zanobetti & Schwartz (2009) 2,500 1,500 1,700 1,900 1,800
(1,900—3,000) (1,100—1,800) (1,300—2,100) (1,400—2,200) (1,400—2,200)

Premature deaths from long-term exposure to PM2.5
  Krewski et al. (2009) 14,000 8,700 10,000 11,000 11,000
(9,700—19,000) (5,800—11,000) (6,900—14,000) (7,300—14,000) (7,600—15,000)
  Lepeule et al. (2012) 32,000 19,000 23,000 24,000 25,000
(16,000—48,000) (9,800—29,000) (12,000—35,000) (12,000—36,000) (13,000—38,000)
A

Values rounded to two significant figures; all functions estimated for populations ages 0–99