15 research outputs found

    Size distribution and lung‐deposited doses of particulate matter from household exposure to biomass smoke

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    Exposure to high concentrations of particulate matter (PM) is associated with a number of adverse health effects. However, it is unclear which aspects of PM are most hazardous, and a better understanding of particle sizes and personal exposure is needed. We characterized particle size distribution (PSD) from biomass‐related pollution and assessed total and regional lung‐deposited doses using multiple‐path deposition modeling. Gravimetric measurements of kitchen and personal PM2.5 (< 2.5 ”m in size) exposures were collected in 180 households in rural Puno, Peru. Direct‐reading measurements of number concentrations were collected in a subset of 20 kitchens for particles 0.3–25 ”m, and the continuous PSD was derived using a nonlinear least‐squares method. Mean daily PM2.5 kitchen concentration and personal exposure was 1205±942 ”g/m3 and 115±167 ”g/m3 respectively, and the mean mass concentration consisted of a primary accumulation mode at 0.21 ”m and a secondary coarse mode at 3.17 ”m. Mean daily lung‐deposited surface area (LDSA) and LDSA during cooking were 1009.6±1469.8 ”m2/cm3 and 10,552.5±8261.6 ”m2/cm3, respectively. This study presents unique data regarding lung deposition of biomass smoke that could serve as a reference for future studies, and provides a novel, more biologically‐relevant metric for exposure‐response analysis compared to traditional size‐based metrics

    Palladium(II)-Catalyzed annulation between ortho-alkenylphenols and allenes. Key role of the metal geometry in determining the reaction outcome

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    2-Alkenylphenols react with allenes, upon treatment with catalytic amounts of Pd(II) and Cu(II), to give benzoxepine products in high yields and with very good regio- and diastereoselectivities. This contrasts with the results obtained with Rh catalysts, which provided chromene-like products through a pathway involving a ÎČ-hydrogen elimination step. Computational studies suggest that the square planar geometry of the palladium is critical to favor the reductive elimination process required for the formation of the oxepine productsThis work was supported by the Spanish MINECO (grant:SAF2013-41943-R), the ERDF, the European Research Council (Advanced Grant No. 340055) and the Xunta de Galicia (grants: GRC2013-041 and 2015-CP082). We also thank the orfeo-cinqa CTQ2014-51912-REDC. K.P.D.R. thanks the Coordenaça̧o de Aperfeiçoamento de Pessoal de ̧Nıvel Superior (CAPES, Brazil) for the Ph.D scholarship. We ́thank Dr. M. Martınez for XRD analysis. All calculations were ́carried out at Centro de Supercomputación de Galicia (CESGA

    Indoor air pollution concentrations and cardiometabolic health across four diverse settings in Peru: a cross-sectional study.

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    BACKGROUND: Indoor air pollution is an important risk factor for health in low- and middle-income countries. METHODS: We measured indoor fine particulate matter (PM2.5) and carbon monoxide (CO) concentrations in 617 houses across four settings with varying urbanisation, altitude, and biomass cookstove use in Peru, between 2010 and 2016. We assessed the associations between indoor pollutant concentrations and blood pressure (BP), exhaled carbon monoxide (eCO), C-reactive protein (CRP), and haemoglobin A1c (HbA1c) using multivariable linear regression among all participants and stratifying by use of biomass cookstoves. RESULTS: We found high concentrations of indoor PM2.5 across all four settings (geometric mean ± geometric standard deviation of PM2.5 daily average in ÎŒg/m3): Lima 41.1 ± 1.3, Tumbes 35.8 ± 1.4, urban Puno 14.1 ± 1.7, and rural Puno 58.8 ± 3.1. High indoor CO concentrations were common in rural households (geometric mean ± geometric standard deviation of CO daily average in ppm): rural Puno 4.9 ± 4.3. Higher indoor PM2.5 was associated with having a higher systolic BP (1.51 mmHg per interquartile range (IQR) increase, 95% CI 0.16 to 2.86), a higher diastolic BP (1.39 mmHg higher DBP per IQR increase, 95% CI 0.52 to 2.25), and a higher eCO (2.05 ppm higher per IQR increase, 95% CI 0.52 to 3.57). When stratifying by biomass cookstove use, our results were consistent with effect measure modification in the association between PM2.5 and eCO: among biomass users eCO was 0.20 ppm higher per IQR increase in PM2.5 (95% CI - 2.05 to 2.46), and among non-biomass users eCO was 5.00 ppm higher per IQR increase in PM2.5 (95% CI 1.58 to 8.41). We did not find associations between indoor air concentrations and CRP or HbA1c outcomes. CONCLUSIONS: Excessive indoor concentrations of PM2.5 are widespread in homes across varying levels of urbanisation, altitude, and biomass cookstove use in Peru and are associated with worse BP and higher eCO

    Comparison of next-generation portable pollution monitors to measure exposure to PM2.5 from household air pollution in Puno, Peru.

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    Assessment of personal exposure to PM2.5 is critical for understanding intervention effectiveness and exposure-response relationships in household air pollution studies. In this pilot study, we compared PM2.5 concentrations obtained from two next-generation personal exposure monitors (the Enhanced Children MicroPEM or ECM; and the Ultrasonic Personal Air Sampler or UPAS) to those obtained with a traditional Triplex Cyclone and SKC Air Pump (a gravimetric cyclone/pump sampler). We co-located cyclone/pumps with an ECM and UPAS to obtain 24-hour kitchen concentrations and personal exposure measurements. We measured Spearmen correlations and evaluated agreement using the Bland-Altman method. We obtained 215 filters from 72 ECM and 71 UPAS co-locations. Overall, the ECM and the UPAS had similar correlation (ECM ρ = 0.91 vs UPAS ρ = 0.88) and agreement (ECM mean difference of 121.7 ”g/m3 vs UPAS mean difference of 93.9 ”g/m3 ) with overlapping confidence intervals when compared against the cyclone/pump. When adjusted for the limit of detection, agreement between the devices and the cyclone/pump was also similar for all samples (ECM mean difference of 68.8 ”g/m3 vs UPAS mean difference of 65.4 ”g/m3 ) and personal exposure samples (ECM mean difference of -3.8 ”g/m3 vs UPAS mean difference of -12.9 ”g/m3 ). Both the ECM and UPAS produced comparable measurements when compared against a cyclone/pump setup

    Do we need better behaved cooks? Reviewing behavioural change strategies for improving the sustainability and effectiveness of cookstove programs

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    More than 40% of the world's population still relies on traditional biomass for their cooking needs. A shift to advanced cookstoves can bring significant health and environmental benefits, but only with near exclusive use which requires significant changes in users’ behaviours. Since the emergence of the Global Alliance for Clean Cookstoves (now the Clean Cooking Alliance) in 2011, more attention has been directed to consumer and demand side factors in clean cookstove adoption and efforts to better understand individuals’ behaviours, household dynamics and decision making around the adoption of clean cookstoves and fuels have increased. This paper presents a review of the academic literature (2013–2020) and aims to identify the most successful interventions of behaviour change techniques in the adoption of improved cookstoves as well as the most common barriers to success cited in the literature. The study sourced 40 peer reviewed published academic papers from spring 2013 to summer 2020, and identified the following most commonly used behaviour change techniques in the adoption of improved cookstoves: Shaping Knowledge (n = 19), Reward & Threat (n = 13), Social Support (n = 9), Comparisons (n = 4), Identity/Self-Belief (n = 4), Regulation (n = 0), Change in the Physical Environment (n = 2), Goals & Planning (n = 6). Based on these results, we present gaps in the literature and provide policy recommendations to promote the adoption and continued use of improved cookstoves

    Nitrogen dioxide exposures from biomass cookstoves in the Peruvian Andes

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    Household air pollution from biomass cookstoves is a major contributor to global morbidity and mortality, yet little is known about exposures to nitrogen dioxide (NO ). To characterize NO kitchen area concentrations and personal exposures among women with biomass cookstoves in the Peruvian Andes. We measured kitchen area NO concentrations at high-temporal resolution in 100 homes in the Peruvian Andes. We assessed personal exposure to NO in a subsample of 22 women using passive samplers. Among 97 participants, the geometric mean (GM) highest hourly average NO concentration was 723 ppb (geometric standard deviation (GSD) 2.6) and the GM 24-hour average concentration was 96 ppb (GSD 2.6), 4.4 and 2.9 times greater than WHO indoor hourly (163 ppb) and annual (33 ppb) guidelines, respectively. Compared to the direct-reading instruments, we found similar kitchen area concentrations with 48-hour passive sampler measurements (GM 108 ppb, GSD 3.8). Twenty-seven percent of women had 48-hour mean personal exposures above WHO annual guidelines (GM 18 ppb, GSD 2.3). In univariate analyses, we found that roof, wall, and floor type, as well as higher SES, was associated with lower 24-hour kitchen area NO concentrations. Kitchen area concentrations and personal exposures to NO from biomass cookstoves in the Peruvian Andes far exceed WHO guidelines. More research is warranted to understand the role of this understudied household air pollutant on morbidity and mortality and to inform cleaner-cooking interventions for public health

    Nitrogen dioxide exposures from LPG stoves in a cleaner-cooking intervention trial

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    ‱Biomass-to-liquefied petroleum gas (LPG) intervention substantially reduced indoor NO2.‱However, NO2 concentrations exceeded annual and hourly guidelines in homes with LPG stoves.‱Personal exposures to NO2 remained within indoor air quality annual guidelines in LPG group.‱LPG stove interventions should consider NO2, which may persist at levels that pose a risk to health. Liquefied petroleum gas (LPG) stoves have been promoted in low- and middle-income countries (LMICs) as a clean energy alternative to biomass burning cookstoves. We sought to characterize kitchen area concentrations and personal exposures to nitrogen dioxide (NO2) within a randomized controlled trial in the Peruvian Andes. The intervention included the provision of an LPG stove and continuous fuel distribution with behavioral messaging to maximize compliance. We measured 48-hour kitchen area NO2 concentrations at high temporal resolution in homes of 50 intervention participants and 50 control participants longitudinally within a biomass-to-LPG intervention trial. We also collected 48-hour mean personal exposures to NO2 among a subsample of 16 intervention and 9 control participants. We monitored LPG and biomass stove use continuously throughout the trial. In 367 post-intervention 24-hour kitchen area samples of 96 participants’ homes, geometric mean (GM) highest hourly NO2 concentration was 138 ppb (geometric standard deviation [GSD] 2.1) in the LPG intervention group and 450 ppb (GSD 3.1) in the biomass control group. Post-intervention 24-hour mean NO2 concentrations were a GM of 43 ppb (GSD 1.7) in the intervention group and 77 ppb (GSD 2.0) in the control group. Kitchen area NO2 concentrations exceeded the WHO indoor hourly guideline an average of 1.3 h per day among LPG intervention participants. GM 48-hour personal exposure to NO2 was 5 ppb (GSD 2.4) among 35 48-hour samples of 16 participants in the intervention group and 16 ppb (GSD 2.3) among 21 samples of 9 participants in the control group. In a biomass-to-LPG intervention trial in Peru, kitchen area NO2 concentrations were substantially lower within the LPG intervention group compared to the biomass-using control group. However, within the LPG intervention group, 69% of 24-hour kitchen area samples exceeded WHO indoor annual guidelines and 47% of samples exceeded WHO indoor hourly guidelines. Forty-eight-hour NO2 personal exposure was below WHO indoor annual guidelines for most participants in the LPG intervention group, and we did not measure personal exposure at high temporal resolution to assess exposure to cooking-related indoor concentration peaks. Further research is warranted to understand the potential health risks of LPG-related NO2 emissions and inform current campaigns which promote LPG as a clean-cooking option
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