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Oct 2, 2013 geo hub workshop_air_luke naeher_final for u chile
1. July 22, 2013
Luke P. Naeher, Associate Professor
Environmental Health Science, College of Public Health
University of Georgia
October 2, 2013
Indoor air pollution in developing countries:
Challenges and opportunities in Chile and Peru
Luke P. Naeher, Profesor Asociado
Ciencias de la Salud Ambiental de la Facultad de Salud Pública de la
Universidad de Georgia
02 de octubre 2013
Contaminación intradomiciliaria en países en desarrollo:
desafíos y oportunidades en Chile y Perú
2. Outline of Presentation
1. Household Air Pollution (HAP) in the
developing world – Introduction and
Background
2. Our current HAP project in Ayacucho, Peru
3. Future directions of/opportunities for HAP
research in Chile and Peru
3. Outline of Presentation
1. Household Air Pollution (HAP)
in the developing world –
Introduction and Background
2. Our current HAP project in Ayacucho, Peru
3. Future directions of/opportunities for HAP research in Chile and
Peru
4.
5.
6. Globally, approximately 3 billion people rely on solid fuels as
their main source of domestic energy
6Picture source: WHO Household Energy Database (2010)
7. Household Air Pollution
Biomass smoke
contains 1000s of
chemicals in the form
of incomplete
combustion products
(Naeher et al. 2007; Smith and Mehta 2003; Smith
1987)
7
Picture source: http://burningissues.org/images/smokehouse1top-a.jpg
8. 8
DISTRIBUTION OF DISEASE BURDEN:
DEVELOPING COUNTRIES
Picture source: WHO 2002
4th leading risk
factor of disease
burden
9.
10. Health Effects
Biomass smoke exposure is
associated with:
Acute lower respiratory infections (ALRI),
chronic obstructive pulmonary disease (WHO 2011;
Bruce et al. 2005; Orozco-Levi et al. 2006; Regalado et al. 2006).
Increasing evidence:
low birth weight, asthma, acute upper
respiratory infections, tuberculosis and
cataracts (McCracken et al. 2011; Naeher et al. 2007; Smith and Mehta 2003).
Emerging evidence:
Oxidative stress and inflammation, adverse
respiratory health, cardiovascular disease
(Banerjee et al. 2011; Adetona et al. 2011; Romieu et al. 2009; Clark et al. 2012; McCracken et
al. 2011). 10
11. Sensitive subpopulations
Women and children in developing nations
Spend more time at home and in the kitchen1
Children < 5 years of age
56% of all indoor air pollution-attributable deaths2
1. Smith, K. R. "Deadly Household Pollution: A Call to Action," Indoor Air 16 (2006): 2.
2. Rehfuess, E., Mehta, S., and Prüss-Üstün, A. "Assessing Household Solid Fuel Use: Multiple Implications for the Millennium Development Goals," Environmental Health Perspectives
114 (2006): 373-378.
12. Global Alliance for Clean Cookstoves
Launched in September 2010 with the goal of installing
100 million improved stoves by the year 2020
13. Peru’s National Stove Program
In Peru almost 93% of the rural
population rely on biomass
fuels for cooking and heating
(INEI, 2007).
In 2009, the Peruvian
government launched a
“500,000 improved cookstoves
national campaign for a
smokeless Peru”
(http://www.ityf.org.pe/en/).
13
http://energy.gov/articles/department-energy-planning-cookstoves-research-relea
: Improved cookstove in village of Santa Cruz de Lanchi, installed through
Peru’s national cookstove program. | Photo credit: Ranyee Chiang, DOE
15. Outline of Presentation
1. Household Air Pollution (HAP) in the developing world –
Introduction and Background
2. Our current HAP project in
Ayacucho, Peru
3. Future directions of/opportunities for HAP research in Chile and
Peru
16. Briefly, I will discuss one of our recent household
air pollution studies from Peru, and then I will
discuss our current project in Ayacucho, Peru
Santiago de Chuco – HAP exposure
assessment following the installation of an
improved stove with chimney
Ayacucho – HAP in homes where wood is
used to fuel cooking stoves, and low birth
weight in a group of over 100 pregnant
women
19. Kitchen PM2.5
DUSTTRAK™ Aerosol Monitor (realtime)
SKC AirChek® 2000 Pump with Cyclone
(gravimetric)
Personal PM2.5
SKC AirChek® XR5000 Pump with Cyclone
CO
Drӓger Pac III
Air Sampling
20. Results
After three weeks of using the new stoves,
reductions in indoor air pollution were seen across
the board in all study communities, with:
Larger reduction in Kitchen vs. Personal
Consistent with other studies
26. Subject Recruitment
Subjects were recruited by Peruvian researchers and
students through local clinics (goal: 100+ subjects)
Subjects recruited after home visit
Subjects had to be in third trimester of pregnancy and cook
with wood exclusively
27.
28.
29.
30. Exposure Assessment
Done by Peruvian graduate students
who were lab and field trained for two
weeks
Kitchen and personal CO and PM2.5
measurements
CO measurement – Draeger PAC III
single gas monitor (electrochemical
sensor)
PM2.5 measurement – RTI Inc. MicroPEM
v 3.2 (laser photometer)
31. Exposure Assessment
Reasons for instrument choice
Real time capabilities + gravimetry for MicroPEM
Portability
Wearing compliance measure (on-board MicroPEM)
Capability to run for 48 hours
Simple to learn (learned within two weeks in the lab and field by
Peruvian research graduate students)
Instrument operated very well within first two months
Collection of measurements were mostly complete
Performance degraded over the last month of sampling
Many measurements were incomplete
32. Exposure Assessment
Kitchen:
Samplers were
set up in kitchen
beside cooking
stoves at
breathing height
Personal:
Subjects wore
both samplers in
vests in breathing
zone
33.
34.
35. Other Study Information/Data
Pre- and post-exposure measurement
questionnaire
Demographics
Health related information
Wearing compliance issues
Field notes
house characteristics
Clinics:
birth weight
birth related information
36. Strengths
Both kitchen and personal exposure
measurements with measure of wearing
compliance
Both real time and gravimetry measurements for
PM2.5
Relatively homogeneous population
Relatively wide range of exposure with same
fuel type
37. Limitations
Incomplete exposure measurements for
some subjects
Exposure measurement was conducted once
and only in the third trimester
Sample size
38. Outline of Presentation
1. Household Air Pollution (HAP) in the developing world –
Introduction and Background
2. Our current HAP project in Ayacucho, Peru
3. Future directions
of/opportunities for HAP
research in Chile and Peru
39. Heart Disease and Combustion Particle Doses
Solid Fuel
Zone
From “Mind the Gap,”
Smith/Peel, 2010 and Pope
et al., 2009
40. 0
5
10
15
20
25
30
35
0 200 400 600 800 1000
Annual mean PM2.5 - ug/m3
HeartDiseaseImpact
From “Mind the Gap,”
Smith/Peel, 2010 and Pope
et al., 2009
41. Smith et al. 2011
Physician-diagnosed severe pneumonia
Plancha
(Chimney)
stove
Open fire
42.
43. Kenya
the jiko stove
http://hopebuilding.pbworks.com/w/page/19222589/Kenyan-stove-manufacturer-provides-energy-efficient-cooking,-encourages-tree-planting
45. Opportunities for future household air
pollution research in Chile and Peru
Investigate the implementation of super low emissions
stoves (example: gas stoves), and study:
46. Grant currently in review at NIH/Fogarty:
TRANSFERRING ECAPACITY TO CHILE
We propose to build eCapacity in Chile by developing technological capacity
that will improve the sophistication of environmental health research there.
This effort will build on our current Fogarty planning grant “Planning for a Global
Environmental Health Hub in Chile” (1R24TW009545-01), a decade-long collaboration with
University of Chile researchers funded by the Fogarty International Training in Environmental
and Occupational Health (ITREOH) program (D43TW005746), and our current support from
Fogarty through the Human Health Impacts of Climate Change program (1R21TW009032).
By e-Capacity we refer to transferring expertise from the US to Chile
regarding information and communication technology (ICT) techniques and
software, in particular pertaining to the areas of:
exposure measurement,
epidemiology, and
geospatial technology tools for addressing health impacts.
We propose to teach courses and participate in collaborative research in
Chile in four key areas:
1) Climate Change Research,
2) Geospatial Analysis,
3) Household Air Pollution Measurement, and
4) New Epidemiologic Methods.
Editor's Notes
Potential solutions User behavior (eg fuel drying, use of stove pot lids) Living conditions (eg increased kitchen ventilation: window or ventilation holes) Fuel type (eg liquefied petroluem gas, low smoke fuels) Cookstoves (eg improved stoves with chimneys, flues) There are no internationally accepted design for biomass burning stoves.
Women and children are known to bear a vastly disproportionate burden of indoor air pollution in the developing world, as they spend much more time in the kitchen, and this proved true in our experience in Peru as well. Young children were most often carried like this on the mother’s back, effectively exposing the kids to whatever mom was exposed to
PM2.5 has been identified as the best single indicator of the health effects of combustion of biomass such as wood (Naeher et al. 2007; Perez-Padilla, Schilmann, and Riojas-Rodriguez 2010). 8hrHonduras: 1002.3 ug/3 (open fire) Clark et al 2010 24hr Guatemala: 520 ug/m3 (open fires) Naeher et al 2000: 24hr 24hrIndia: 468 and 718 ug/m3 (open fires) Mukhopadhyay et al 2012 24hrGhana: 650 ug/m3 (open fires) Pennise et al 2009 48hrMexico: 469 ug/m3 (open fires) Cynthia et al 2008 48hrPeru: 207.3 ug/m3 (open fires) Fitzgerald et al 2012 The high PM concentrations reinforce the need for interventions that reduce HAP exposures
And again, with stove 2 in chaguin/cachulla. These all actually look the exact same, because the industry subcontracted the job of their construction out to one man. This ensured that everyone received the same level of stove quality, but it also slowed the process of stove building down a bit, which set us back in our timing. In the end, we were forced to return to the states with only the pre-intervention sampling done in this region, and then train and send back a different group from UGA to finish what we started there, using the same field technicians as before.
As I mentioned before, we measured PM2.5 and CO, on the personal level and as a stationary sampling site in the kitchen near the stove. In a random subsample of the homes (since we did not have enough equipment to do every home), we captured real-time measures of PM2.5 using the Dusttrak aerosol monitor [click], which is a data-logging, light-scattering laser photometer that gives real-time aerosol mass readings. To obtain gravimetric measures, we used the SKC AirChek 2000 pump, which pulled air in at a constant rate of 1.5 liters per minute, with a BGI Triplex cyclone designed to capture PM2.5 on small, preweighed microfilters within the cyclone. Show video thing. For personal PM2.5 we used a very similar pump and cyclone setup, but the pump was a newer model with an internal lithium battery that could last 48 hours without being changed out. Finally, to measure CO in both settings, we used the Draeger Pac III, a gas measuring device with a specific CO sensor. Now, the equipment in the kitchen was placed in a box we like this, which we had constructed from local materials by a carpenter from town, with a piece of PCV tubing reaching up to approximate breathing height. The equipment sat in the box, and the sampling ends were attached to the tubing. The women all wore a vest like the one you see here, which was basically a converted firefighter radio harness, and the equipment sat in the vest with the sampling ends attached at breathing height or as near as possible. They wore these vests for the entirety of 2 days, only taking them off to bathe or to sleep, and during sleep it was set next to their beds on a chair or table.
Blah blah reading blah….statistically significan WHICH WE defined as… Even though the purpose of our study was not a comparison of stove models, we did find that they performed equally according to 2-way ANOVA testing, with the exception of the personal CO reductions in Chaguin
This is realtime CO and PM measures with the traditional stove, CO measured in ppm and PM measured in mg/m3. notice again the peaks around mealtimes
This is from the same home after the installation of a new stove. The scale was kept the same to show the gravity of the change. Peaks still line up with mealtimes, but were drastically reduced.
And now both of them together, to see the whole picture.
Visit, consent and recruitment typically took place on the same day. This was inefficient and a limitation which would be mentioned later, but was largely a factor of funding and schedule being affected by IRB.
Degradation was mostly a function of the instrument, but also some personnel performance