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| Name | Class |
|---|---|
| University of North Carolina, Chapel Hill | OTHER |
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The goal of this clinical trial is to compare indoor air quality and health in people exposed to air pollution, including possible exposure to wildfire smoke. The study will test the effect of using a do-it-yourself (DIY) air cleaner when air pollution is present to answer the following questions:
Participants will be asked to do the following:
The investigators will measure air quality in participating homes and measure health outcomes for participants. The investigators will compare outcomes of participants who use a DIY air cleaner with filters that work well to those of participants who use a DIY air cleaner with a placebo filter (one that does not work well to remove the air pollutants of concern). The goal of the study is to see if using the effective air cleaner leads to better health outcomes and indoor air quality.
Background and rationale: The motivation for this research is that wildfires have been increasing in frequency and severity in recent years. Wildfire smoke is associated with numerous adverse health outcomes. Public health guidance during wildfire events has included recommendations to stay indoors, close doors and windows, and use portable air cleaners (PACs) to clean the smoke that infiltrates the indoor environment. Studies support the effectiveness of PACs in reducing indoor fine particulate matter, (PM2.5=fine particles 2.5 micrometers in diameter or smaller), one of the main components of concern in wildfire smoke.
Evidence of whether PAC use is associated with health benefits is mixed. In addition, commercially-available PACs can be expensive and hard to access. An affordable alternative that gained attention during the COVID-19 pandemic is a Do-It-Yourself (DIY) PAC, made from a box fan and high efficiency filter(s). Laboratory studies have shown DIY PACs to have excellent clean air delivery rates (CADR, a measure of effectiveness) with respect to fine particulate matter. However, their evidence in real-world settings is limited. Researchers have acknowledged that behaviors, such as turning on/off the fans, could have major impacts on efficacy.
The current study aims to examine the effect of PACs on indoor air quality and health during wildfire smoke exposure. The investigators will conduct this research in an agricultural community in central California that has experienced wildfire smoke exposure and routinely experiences dust. According to local partners, most residents of this county do not already own PACs. One risk of planning a Randomized Control Trial (RCT) of wildfire smoke exposure is that wildfire smoke will not occur. For this reason, the investigators selected a community with historically elevated levels of particle pollution (PM2.5, PM10, dust) in the fall and winter months as the study site. If wildfire smoke exposure does not occur during the study period, the efficacy of the DIY PACs on indoor air quality and health will be tested during periods of dust/high particle pollution exposure (anticipated October 2023).
Up to 120 recruited and consented study participants will be randomly divided into 2 groups. One group will use an effective DIY air cleaner (intervention); the other group will use a sham DIY air cleaner (control). All groups will have the same basic exposure to ambient air pollution.
Qualified participants will agree to have air quality sensors and door monitors placed in their home (bedroom and main exterior door). Air quality will be measured continuously during the study period. Other study activities will occur intermittently, during 5 visits by study staff to the participant's home. These activities will include completing 2 symptom and demographic questionnaires, collecting air and dust samples from inside the homes and collecting biological samples at 3 visits (capillary blood (by fingerstick) and nasal epithelial lining fluid). Blood and nasal fluid collected will be assessed for markers of inflammation and immune system activation. The investigators hypothesize that subjects in the intervention group will have reduced concentrations of measured air pollutants in their indoor air samples and lower levels of markers of inflammation compared to those in the control group. The investigators further hypothesize that symptoms, particularly related to respiratory inflammation, will differ between intervention (air filtration) and control (sham filtration) groups. Baseline measurements and post-intervention period measurements will be compared for intra-individual change and differences between study groups.
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| Label | Type | Description | Intervention Names |
|---|---|---|---|
| Intervention arm | Active Comparator | Subjects in the treatment arm will use a DIY portable air cleaner made by attaching a highly effective furnace filter (MERV 13) and carbon absorbent to a box fan. |
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| Control arm | Sham Comparator | Subjects in the control arm will use a DIY portable air cleaner with a sham filter. All subjects will receive education on air quality, wildfire smoke, and health. |
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| Name | Type | Description | Arm Group Labels | Other Names |
|---|---|---|---|---|
| DIY portable air cleaner with a highly effective filter | Other | A portable air filtration device that can be homemade ("DIY"), constructed by attaching a highly effective air filter (MERV13 rating or higher) to a 20 inch box fan to filter air pollutants including particulate matter of size 2.5 micrometers diameter or greater. |
| Measure | Description | Time Frame |
|---|---|---|
| Difference in change in concentrations of biomarkers of inflammation between treatment and control groups | Markers of inflammation include C-reactive protein obtained from fingerstick blood samples | Measured at baseline (pre-intervention) and at two timepoints, at least 3 days apart, during the portable air cleaner usage period (intervention) |
| Measure | Description | Time Frame |
|---|---|---|
| Difference in change in concentrations of biomarkers of inflammation between treatment and control groups | Markers of inflammation obtained from nasal epithelial lining fluid analyses | Measured at Baseline and at two timepoints, at least 3 days apart, during the portable air cleaner usage period (intervention) |
| Measure | Description | Time Frame |
|---|---|---|
| air quality measurements | Concentrations of PM2.5, PM10 and volatile organic compounds in air inside participants' homes | Continuous measurement lasting up to 15 weeks |
Inclusion Criteria:
Exclusion Criteria:
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| Name | Affiliation | Role |
|---|---|---|
| Ann N Chelminski, MD, MPH | Environmental Protection Agency (EPA) | Principal Investigator |
| Nayamin Martinez, MPH | Central California Environmental Justice Network | Principal Investigator |
| Facility | Status | City | State | ZIP | Country | Contacts |
|---|---|---|---|---|---|---|
| Central California Environmental Justice Network | Fresno | California | 93727 | United States |
| PubMed Identifier | Type | Citation | Retractions |
|---|---|---|---|
| 29272827 | Background | Cascio WE. Wildland fire smoke and human health. Sci Total Environ. 2018 May 15;624:586-595. doi: 10.1016/j.scitotenv.2017.12.086. Epub 2017 Dec 27. | |
| Background | 2. U.S. Environmental Protection Agency. Create a Clean Room to Protect Indoor Air Quality During a Wildfire. 2022; https://www.epa.gov/indoor-air-quality-iaq/create-clean-room-protect-indoor-air-quality-during-wildfire. Accessed September 30, 2022. | ||
| 33121763 |
| Label | URL |
|---|---|
| Create a clean room to protect indoor air quality during a wildfire | View source |
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| ID | Term |
|---|---|
| D012140 | Respiratory Tract Diseases |
| D002318 | Cardiovascular Diseases |
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Participants will be randomized to the intervention or control group.
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The control air filtration device will have a filter that looks like the intervention filter but is much less effective. A cover "shroud" will be placed over the air filtration device so that differences in components will not be noticeable to participants.
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| DIY portable air cleaner with sham filtration | Other | A portable air filtration device that can be homemade ("DIY") by attaching an air filter to a 20 inch box fan. The portable air cleaner with sham filtration with have a filter that is not effective for filtration of fine particulate matter, including that in wildfire smoke. |
|
| Symptom data |
Symptom/clinical data obtained from questionnaires |
| At baseline and at one timepoint during portable air cleaner use |
| Background |
| Cheek E, Guercio V, Shrubsole C, Dimitroulopoulou S. Portable air purification: Review of impacts on indoor air quality and health. Sci Total Environ. 2021 Apr 20;766:142585. doi: 10.1016/j.scitotenv.2020.142585. Epub 2020 Sep 30. |
| Background | 4. Program CTAQ. Box fan filter, a DIY users guide. 2022; https://www.cct-enr.com/box-fan-filter. Accessed September 16, 2022. |
| Background | 5. Puget Sound Clean Air Agency. DIY Air Filter. https://pscleanair.gov/525/DIY-Air-Filter. Accessed September 16, 2022. |
| 35580674 | Background | Srikrishna D. Can 10x cheaper, lower-efficiency particulate air filters and box fans complement High-Efficiency Particulate Air (HEPA) purifiers to help control the COVID-19 pandemic? Sci Total Environ. 2022 Sep 10;838(Pt 1):155884. doi: 10.1016/j.scitotenv.2022.155884. Epub 2022 May 14. |
| 36437679 | Background | Holder AL, Halliday HS, Virtaranta L. Impact of do-it-yourself air cleaner design on the reduction of simulated wildfire smoke in a controlled chamber environment. Indoor Air. 2022 Nov;32(11):e13163. doi: 10.1111/ina.13163. |
| 22145709 | Background | Batterman S, Du L, Mentz G, Mukherjee B, Parker E, Godwin C, Chin JY, O'Toole A, Robins T, Rowe Z, Lewis T. Particulate matter concentrations in residences: an intervention study evaluating stand-alone filters and air conditioners. Indoor Air. 2012 Jun;22(3):235-52. doi: 10.1111/j.1600-0668.2011.00761.x. Epub 2012 Feb 4. |