TY - JOUR
T1 - Measuring and predicting personal and household Black Carbon levels from 88 communities in eight countries
AU - PURE-AIR study investigators
AU - Wang, Ying
AU - Shupler, Matthew
AU - Birch, Aaron
AU - Chu, Yen Li
AU - Jeronimo, Matthew
AU - Rangarajan, Sumathy
AU - Mustaha, Maha
AU - Heenan, Laura
AU - Seron, Pamela
AU - Lanas, Fernando
AU - Salazar, Luis
AU - Saavedra, Nicolas
AU - Oliveros, Maria Jose
AU - Lopez-Jaramillo, Patricio
AU - Camacho, Paul A.
AU - Otero, Johnna
AU - Perez-Mayorga, Maritza
AU - Yeates, Karen
AU - West, Nicola
AU - Ncube, Tatenda
AU - Ncube, Brian
AU - Chifamba, Jephat
AU - Yusuf, Rita
AU - Khan, Afreen
AU - Liu, Zhiguang
AU - Bo, Hu
AU - Wei, Li
AU - Tse, L. A.
AU - Mohan, Deepa
AU - Kumar, Parthiban
AU - Gupta, Rajeev
AU - Mohan, Indu
AU - Jayachitra, K. G.
AU - Mony, Prem K.
AU - Rammohan, Kamala
AU - Nair, Sanjeev
AU - Lakshmi, P. V.M.
AU - Sagar, Vivek
AU - Khawaja, Rehman
AU - Iqbal, Romaina
AU - Kazmi, Khawar
AU - Yusuf, Salim
AU - Brauer, Michael
AU - Hystad, Perry
N1 - Publisher Copyright:
© 2021
PY - 2022/4/20
Y1 - 2022/4/20
N2 - Black Carbon (BC) is an important component of household air pollution (HAP) in low- and middle- income countries (LMICs), but levels and drivers of exposure are poorly understood. As part of the Prospective Urban and Rural Epidemiological (PURE) study, we analyzed 48-hour BC measurements for 1187 individual and 2242 household samples from 88 communities in 8 LMICs (Bangladesh, Chile, China, Colombia, India, Pakistan, Tanzania, and Zimbabwe). Light absorbance (10−5 m−1) of collected PM2.5 filters, a proxy for BC concentrations, was calculated via an image-based reflectance method. Surveys of household/personal characteristics and behaviors were collected after monitoring. The geometric mean (GM) of personal and household BC measures was 2.4 (3.3) and 3.5 (3.9)·10−5 m−1, respectively. The correlation between BC and PM2.5 was r = 0.76 for personal and r = 0.82 for household measures. A gradient of increasing BC concentrations was observed for cooking fuels: BC increased 53% (95%CI: 30, 79) for coal, 142% (95%CI: 117, 169) for wood, and 190% (95%CI: 149, 238) for other biomass, compared to gas. Each hour of cooking was associated with an increase in household (5%, 95%CI: 3, 7) and personal (5%, 95%CI: 2, 8) BC; having a window in the kitchen was associated with a decrease in household (−38%, 95%CI: −45, −30) and personal (−31%, 95%CI: −44, −15) BC; and cooking on a mud stove, compared to a clean stove, was associated with an increase in household (125%, 95%CI: 96, 160) and personal (117%, 95%CI: 71, 117) BC. Male participants only had slightly lower personal BC (−0.6%, 95%CI: −1, 0.0) compared to females. In multivariate models, we were able to explain 46–60% of household BC variation and 33–54% of personal BC variation. These data and models provide new information on exposure to BC in LMICs, which can be incorporated into future exposure assessments, health research, and policy surrounding HAP and BC.
AB - Black Carbon (BC) is an important component of household air pollution (HAP) in low- and middle- income countries (LMICs), but levels and drivers of exposure are poorly understood. As part of the Prospective Urban and Rural Epidemiological (PURE) study, we analyzed 48-hour BC measurements for 1187 individual and 2242 household samples from 88 communities in 8 LMICs (Bangladesh, Chile, China, Colombia, India, Pakistan, Tanzania, and Zimbabwe). Light absorbance (10−5 m−1) of collected PM2.5 filters, a proxy for BC concentrations, was calculated via an image-based reflectance method. Surveys of household/personal characteristics and behaviors were collected after monitoring. The geometric mean (GM) of personal and household BC measures was 2.4 (3.3) and 3.5 (3.9)·10−5 m−1, respectively. The correlation between BC and PM2.5 was r = 0.76 for personal and r = 0.82 for household measures. A gradient of increasing BC concentrations was observed for cooking fuels: BC increased 53% (95%CI: 30, 79) for coal, 142% (95%CI: 117, 169) for wood, and 190% (95%CI: 149, 238) for other biomass, compared to gas. Each hour of cooking was associated with an increase in household (5%, 95%CI: 3, 7) and personal (5%, 95%CI: 2, 8) BC; having a window in the kitchen was associated with a decrease in household (−38%, 95%CI: −45, −30) and personal (−31%, 95%CI: −44, −15) BC; and cooking on a mud stove, compared to a clean stove, was associated with an increase in household (125%, 95%CI: 96, 160) and personal (117%, 95%CI: 71, 117) BC. Male participants only had slightly lower personal BC (−0.6%, 95%CI: −1, 0.0) compared to females. In multivariate models, we were able to explain 46–60% of household BC variation and 33–54% of personal BC variation. These data and models provide new information on exposure to BC in LMICs, which can be incorporated into future exposure assessments, health research, and policy surrounding HAP and BC.
KW - Black Carbon
KW - Exposure
KW - Fine particulate matter
KW - Household air pollution
KW - Measurement
UR - http://www.scopus.com/inward/record.url?scp=85120157943&partnerID=8YFLogxK
U2 - 10.1016/j.scitotenv.2021.151849
DO - 10.1016/j.scitotenv.2021.151849
M3 - Artículo Científico
C2 - 34822894
AN - SCOPUS:85120157943
SN - 0048-9697
VL - 818
JO - Science of the Total Environment
JF - Science of the Total Environment
M1 - 151849
ER -