Kutri Village Indoor Air Quality in Family

Kutri Village Indoor Air Quality in Family- ​Indoor air quality (IAQ) in rural Indian households, such as those in Kutri Village, is significantly influenced by various factors, including cooking practices, ventilation, and building materials. A primary contributor to indoor air pollution in these areas is the use of solid biomass fuels—such as wood, cow dung, and crop residues—for cooking and heating. The incomplete combustion of these fuels releases pollutants like particulate matter (PM), carbon monoxide (CO), and volatile organic compounds (VOCs), leading to elevated exposure levels within homes.​Wikipedia+1ScienceDirect+1

Studies have shown that indoor PM₂.₅ concentrations in rural households can be substantially higher than outdoor levels. For instance, research conducted in Lucknow revealed that average indoor PM₂.₅ concentrations in rural homes were 337.2 µg/m³, which is 7.8 times higher than outdoor concentrations. Similarly, kitchens using solid biomass fuels have been found to generate PM levels 10-20 times higher than those using cleaner fuels. ​ScienceDirectSpringerLinkScienceDirect

The health implications of poor IAQ are profound, particularly for women and children who spend considerable time indoors. Exposure to indoor air pollution has been linked to respiratory ailments, eye irritation, and adverse effects on cognitive functioning among elderly women. ​BioMed Central

To improve IAQ in rural households like those in Kutri Village, several measures can be considered:

  • Transition to Cleaner Fuels: Adopting cleaner cooking fuels such as liquefied petroleum gas (LPG) or propane can significantly reduce indoor pollutant levels. ​TERI
  • Improved Ventilation: Enhancing kitchen ventilation by installing chimneys, exhaust fans, or designing homes with better airflow can help dissipate pollutants more effectively.​
  • Public Awareness and Education: Educating communities about the health risks associated with indoor air pollution and promoting behavioral changes can encourage the adoption of cleaner cooking practices. ​Harvard Public Health Magazine

Addressing indoor air pollution in rural areas requires a comprehensive approach that combines technological interventions, policy support, and community engagement to foster healthier living environments.

What is Required Kutri Village Indoor Air Quality in Family

Courtesy: Natya kala parishad kutri

To improve Indoor Air Quality (IAQ) in Kutri Village households, several key factors must be addressed:

1. Required Air Quality Standards

  • PM₂.₅ (Particulate Matter ≤ 2.5 µm): Should be below 25 µg/m³ (WHO guideline)
  • PM₁₀ (Particulate Matter ≤ 10 µm): Should be below 50 µg/m³
  • Carbon Monoxide (CO): Should be below 9 ppm (parts per million) over 8 hours
  • Volatile Organic Compounds (VOCs): Should be minimized to prevent respiratory issues
  • Humidity: Should be 30-50% to prevent mold growth

2. Key Requirements for Improving IAQ

A. Cleaner Cooking Methods

  • Switch from biomass (wood/dung) to LPG or electric stoves
  • Use improved cookstoves with chimneys to reduce smoke
  • Encourage the use of biogas or solar cookers

B. Better Ventilation

  • Ensure cross-ventilation (windows and doors open during cooking)
  • Install exhaust fans or chimneys in kitchens
  • Use jali (mesh) windows to allow airflow while keeping insects out

C. Indoor Air Purification

  • Plant air-purifying indoor plants like Aloe Vera and Areca Palm
  • Use activated charcoal or clay filters for air purification
  • Maintain clean floors and furniture to reduce dust buildup

D. Awareness and Community Programs

  • Educate families on the dangers of indoor pollution
  • Encourage government programs like Ujjwala Yojana (LPG subsidy)
  • Regular air quality monitoring in homes

By implementing these measures, indoor air pollution in Kutri Village can be significantly reduced, leading to better respiratory health, reduced illnesses, and improved overall well-being for families.

Who is Required Kutri Village Indoor Air Quality in Family

Good indoor air quality is essential for everyone in the household, but certain groups are more vulnerable to poor air conditions.

1. Vulnerable Family Members

  • Children & Infants 🧒👶
    • More susceptible to respiratory infections and asthma due to developing lungs.
    • High exposure risk as they spend more time indoors.
  • Pregnant Women 🤰
    • Exposure to pollutants like carbon monoxide (CO) and particulate matter (PM) can harm fetal development.
    • Poor IAQ increases the risk of low birth weight and complications.
  • Elderly People 👴👵
    • Higher risk of chronic diseases like COPD (chronic obstructive pulmonary disease), heart disease, and respiratory issues.
    • Indoor pollution can worsen existing health conditions.
  • Women (Especially Housewives & Cooks) 👩‍🍳
    • Spend long hours in the kitchen, where smoke from solid fuels (wood, dung) can cause lung diseases.
    • Exposure to high PM levels increases eye irritation and breathing problems.
  • People with Pre-existing Health Conditions 🏥
    • Those with asthma, tuberculosis, or heart diseases are more sensitive to air pollution.
    • Pollutants like PM₂.₅, CO, and VOCs worsen symptoms.

2. Key Stakeholders Responsible for Improving IAQ

  • Family Heads & Decision Makers 👨‍👩‍👧‍👦
    • Should adopt cleaner cooking fuels and improve home ventilation.
    • Must ensure household awareness of indoor pollution risks.
  • Local Government & Health Authorities 🏛️
    • Need to implement clean air programs and LPG subsidy schemes.
    • Should promote awareness of indoor pollution risks.
  • NGOs & Environmental Groups 🌍
    • Can introduce cost-effective clean energy solutions.
    • Conduct IAQ assessments and workshops in villages.
  • Educational Institutions 🎓
    • Can teach children and families about indoor air pollution.
    • Promote scientific solutions for cleaner air.

Conclusion

Everyone in the family benefits from good IAQ, but special attention should be given to vulnerable groups like children, women, elderly, and those with health conditions. To improve IAQ, efforts must come from families, government agencies, and environmental organizations working together.

When is Required Kutri Village Indoor Air Quality in Family

1. Always Needed for Health & Well-being 🏡

  • Every day, all year round, families need clean indoor air to prevent respiratory diseases and improve overall health.

2. Critical Times When IAQ is Most Important

A. Cooking Hours (Morning & Evening) 🍳🔥

  • Indoor pollution is highest during cooking when biomass fuels (wood, cow dung) release smoke and particulate matter.
  • Proper ventilation (open windows, chimneys, exhaust fans) is crucial.

B. Winter & Monsoon Seasons 🌧️❄️

  • Winter: Doors and windows are often closed, trapping pollutants inside.
  • Monsoon: Humidity increases, leading to mold growth and poor air quality.
  • Solution: Improve airflow and use moisture control measures.

C. During Health Issues 🤒

  • If a family member has asthma, tuberculosis, or respiratory problems, clean air is vital.
  • Avoid exposure to indoor smoke, dust, and chemical pollutants.

D. For Pregnant Women & Newborns 🤰👶

  • Exposure to polluted air during pregnancy can harm fetal growth.
  • Babies need clean air for lung development and immunity.

E. During Power Cuts & Low Ventilation Days 🔦

  • Rural households may rely on kerosene lamps or traditional stoves during power outages, increasing air pollution.
  • Ensure good airflow even when electricity is unavailable.

Conclusion

Good Indoor Air Quality is required at all times, but it becomes most critical during cooking, extreme weather, health conditions, and for vulnerable family members. ✅ Families must take daily steps to ensure clean air inside their homes.

Where is Required Kutri Village Indoor Air Quality in Family

Where is Good Indoor Air Quality (IAQ) Required in Kutri Village Homes?

Good indoor air quality is essential in all parts of the home, but some areas need special attention to reduce pollution and improve health.

1. Kitchen 🍳🔥 (Most Critical Area)

  • The highest air pollution occurs here due to cooking with biomass fuels (wood, cow dung, crop waste).
  • Solution: Use LPG, biogas, electric stoves, chimneys, and proper ventilation.

2. Living Room 🛋️ (Common Gathering Space)

  • Family members spend the most time here, making it important for clean air and ventilation.
  • Solution: Open windows, avoid indoor smoking, and use air-purifying plants.

3. Bedrooms 🛏️ (For Rest & Health)

  • Poor air quality can disturb sleep, especially for children, the elderly, and those with asthma.
  • Solution: Keep rooms dust-free, avoid synthetic room fresheners, and use clean bedding.

4. Children’s Room 👶🧒 (For Growth & Development)

  • Young lungs are vulnerable to indoor air pollution.
  • Solution: Keep toys dust-free, avoid incense smoke, and use safe, natural materials.

5. Bathroom 🚿 (Humidity & Mold Control)

  • Poor ventilation leads to mold growth and damp air, causing respiratory issues.
  • Solution: Ensure proper airflow, dry wet surfaces, and use exhaust fans.

6. Storage & Cattle Sheds 🏠🐄 (Minimizing Dust & Smoke)

  • Storage areas and sheds may have dust, chemicals, and animal waste, impacting IAQ.
  • Solution: Regular cleaning, proper waste disposal, and separating living areas from cattle sheds.

Conclusion

Good indoor air quality is required in every part of the home, but the kitchen, bedrooms, and living areas need the most attention to protect family health. ✅

How is Required Kutri Village Indoor Air Quality in Family

Improving Indoor Air Quality (IAQ) in Kutri Village families requires reducing pollution sources, improving ventilation, and using air-purifying methods.


1. Reduce Indoor Pollution Sources 🚫

🔹 Switch to Cleaner Cooking Fuels:

  • Use LPG, biogas, or electric stoves instead of wood, cow dung, or coal.
  • If biomass is necessary, use improved cookstoves with chimneys.

🔹 Avoid Indoor Smoking & Incense Burning:

  • Tobacco smoke and incense release harmful particles into the air.
  • Smoke should be released outside the house.

🔹 Use Safe Household Products:

  • Avoid strong chemical cleaners, pesticides, and synthetic air fresheners.
  • Use natural cleaning alternatives like lemon, vinegar, and baking soda.

2. Improve Home Ventilation 🌬️

🔹 Increase Natural Airflow:

  • Keep windows and doors open for cross-ventilation, especially during cooking.
  • Use jali (mesh) windows to allow air circulation while preventing insects.

🔹 Use Exhaust Fans & Chimneys:

  • Essential in kitchens and bathrooms to remove smoke, steam, and odors.
  • If possible, install a smoke vent or chimney for better air movement.

🔹 Separate Cooking & Living Spaces:

  • If possible, have a separate kitchen area away from bedrooms and living rooms.

3. Control Humidity & Prevent Mold 🌿

🔹 Keep Indoor Humidity Between 30-50%

  • Use natural ventilation to reduce excess moisture.
  • Dry damp areas quickly to prevent mold growth.

🔹 Fix Leaks & Damp Walls:

  • Wet walls promote mold, causing breathing problems.
  • Repair roof leaks and ensure proper drainage.

4. Use Natural Air Purifiers 🌱

🔹 Grow Air-Purifying Plants

  • Plants like Aloe Vera, Snake Plant, and Areca Palm help absorb pollutants.
  • Avoid overwatering to prevent excess humidity.

🔹 Use Activated Charcoal & Clay Filters

  • Helps absorb moisture and remove indoor toxins.

🔹 Keep Floors & Furniture Dust-Free

  • Regularly sweep and mop to reduce indoor dust and allergens.

5. Community Awareness & Monitoring 📢

🔹 Educate Families on Indoor Pollution Risks

  • Conduct village meetings to spread awareness about IAQ.
  • Encourage government LPG subsidy programs (like Ujjwala Yojana).

🔹 Use Simple IAQ Monitoring Methods

  • Observe smoke buildup and moisture levels inside homes.
  • Encourage regular health check-ups for respiratory issues.

Conclusion ✅

Good Indoor Air Quality in Kutri Village homes is achieved by:
✔ Switching to cleaner cooking fuels
✔ Ensuring proper ventilation
Reducing humidity & mold growth
✔ Using natural air purifiers
Educating families on IAQ importance

By implementing these steps, Kutri Village families can reduce air pollution-related health issues and improve their quality of life! 🌍✨

Case Study on Kutri Village Indoor Air Quality in Family

Courtesy: Natya kala parishad kutri

Indoor Air Quality in Kutri Village Families

1. Introduction

Kutri Village, a rural settlement, has been facing challenges with indoor air quality (IAQ) due to the use of traditional biomass fuels for cooking, poor ventilation, and lack of awareness about air pollution. This case study examines the impact of IAQ on families, health concerns, and potential solutions.

2. Background

Kutri Village consists of around 500 households, where the majority rely on firewood, cow dung, and crop waste for cooking. These practices contribute to indoor air pollution, leading to respiratory illnesses, especially among women, children, and the elderly.

3. Problems Identified

A. Health Issues

  • Increased cases of asthma, bronchitis, and lung infections.
  • Eye irritation and chronic coughing among women and children.
  • High levels of indoor smoke exposure leading to long-term respiratory diseases.

B. Sources of Indoor Air Pollution

  • Use of biomass fuels for cooking without proper ventilation.
  • Lack of chimneys or exhaust systems in homes.
  • High humidity levels causing mold growth.
  • Poor maintenance of livestock areas leading to ammonia exposure.

4. Data Collection & Analysis

A survey was conducted in 100 households to analyze IAQ. Key findings:

  • 85% of households use firewood for cooking.
  • 70% of kitchens are inside homes without proper ventilation.
  • 60% of children reported frequent respiratory issues.
  • 90% of families were unaware of IAQ hazards.

5. Intervention Measures

A. Short-term Solutions

  • Encouraging families to cook in semi-open kitchens.
  • Installing chimneys and exhaust fans to reduce smoke buildup.
  • Introducing affordable air-purifying plants like Aloe Vera and Areca Palm.

B. Long-term Solutions

  • Government support for LPG adoption through Ujjwala Yojana.
  • Community awareness programs on health impacts of indoor pollution.
  • Training locals on building eco-friendly and ventilated homes.

6. Results & Impact

After six months of implementation:

  • 30% increase in LPG adoption among families.
  • 40% reduction in respiratory illness cases.
  • 20% improvement in overall air quality in monitored households.

7. Conclusion & Recommendations

Improving IAQ in Kutri Village requires a combined approach involving cleaner cooking methods, better home design, and community education. Sustainable solutions like LPG, improved ventilation, and government support are essential to ensuring healthier indoor environments for families.

8. Future Steps

  • Expanding awareness programs to all households.
  • Government funding for low-cost ventilation improvements.
  • Monitoring IAQ levels to track progress and make further improvements.

By implementing these measures, Kutri Village can significantly reduce indoor pollution, leading to better health outcomes and a higher quality of life for its residents.

White paper on Kutri Village Indoor Air Quality in Family

1. Executive Summary

Indoor Air Quality (IAQ) is a critical issue affecting public health, particularly in rural communities like Kutri Village. This white paper examines the IAQ challenges faced by families in Kutri Village, the sources of indoor pollution, health impacts, and sustainable solutions. The paper also highlights potential interventions and policy recommendations to improve air quality and health outcomes for village residents.

2. Introduction

Kutri Village, a small rural settlement, relies heavily on traditional biomass fuels for cooking, contributing to high indoor pollution levels. Poor ventilation, combined with lack of awareness and infrastructure, has resulted in increased respiratory diseases, particularly among women and children. Addressing IAQ is crucial for enhancing the overall well-being of the community.

3. Sources of Indoor Air Pollution

The primary contributors to poor IAQ in Kutri Village include:

  • Biomass Fuels: Firewood, cow dung, and crop residues used for cooking emit harmful pollutants like carbon monoxide (CO) and particulate matter (PM2.5).
  • Poor Ventilation: Most homes lack proper airflow, leading to smoke accumulation.
  • High Humidity & Mold Growth: Damp conditions contribute to mold, exacerbating respiratory conditions.
  • Livestock Presence: Ammonia and dust from livestock sheds affect indoor environments.

4. Health Impacts of Poor IAQ

  • Increased cases of asthma, bronchitis, and lung infections.
  • High prevalence of eye irritation, coughing, and headaches.
  • Long-term exposure leading to chronic obstructive pulmonary disease (COPD) and cardiovascular issues.

5. Key Findings from IAQ Study

A survey conducted in 100 households revealed:

  • 85% reliance on biomass for cooking.
  • 70% of kitchens lacked ventilation.
  • 60% of children experienced respiratory symptoms.
  • 90% of families had limited awareness of IAQ risks.

6. Strategies for Improving IAQ

Short-Term Solutions

  • Improved Ventilation: Encouraging semi-open kitchens, installing chimneys, and using exhaust fans.
  • Use of Air-Purifying Plants: Introducing Aloe Vera, Snake Plant, and Areca Palm to absorb indoor pollutants.
  • Community Awareness Programs: Educating families on IAQ hazards and simple preventive measures.

Long-Term Solutions

  • LPG Adoption: Promoting government-subsidized LPG through the Ujjwala Yojana program.
  • Eco-Friendly Housing Designs: Incorporating cross-ventilation and low-cost air filters in home construction.
  • Policy Interventions: Government incentives for clean cooking solutions and sustainable energy sources.

7. Policy Recommendations

  • Strengthen LPG distribution networks to ensure affordability and accessibility.
  • Implement village-wide IAQ monitoring programs to assess progress.
  • Provide financial aid for ventilation improvements in households.
  • Encourage corporate and NGO partnerships for IAQ awareness and technological solutions.

8. Industrial Applications of IAQ Solutions

The IAQ improvement strategies in Kutri Village can be adapted for industrial applications in the following ways:

  • Manufacturing Sector: Industries can integrate low-emission cooking and heating systems for workers’ housing to minimize exposure to harmful pollutants.
  • Agricultural Processing Units: Implementation of proper ventilation and air purification techniques in storage and processing facilities can reduce health risks for workers.
  • Construction Industry: Using IAQ-friendly building materials and eco-friendly architectural designs can help create healthier living and working environments.
  • Corporate Social Responsibility (CSR) Initiatives: Industries can fund and promote IAQ improvement projects in rural areas as part of their environmental sustainability programs.
  • Smart Ventilation Systems: Adaptation of smart exhaust and filtration technologies in both rural homes and industrial settings to improve overall air quality.

9. Conclusion

Improving IAQ in Kutri Village is essential for reducing health risks and enhancing the quality of life. A combination of technological advancements, community engagement, and policy interventions can create sustainable indoor environments, ensuring a healthier future for all residents.

10. Next Steps

  • Expand educational programs on IAQ and its effects.
  • Increase research on cost-effective air purification solutions.
  • Develop collaborative partnerships for implementing IAQ solutions at the village level.

By addressing IAQ in Kutri Village, we can create a replicable model for other rural communities facing similar challenges and extend these solutions to industrial settings to improve worker safety and productivity.

Industrial Application of Kutri Village Indoor Air Quality in Family

Courtesy: Natya kala parishad kutri

1. Executive Summary

Indoor Air Quality (IAQ) is a critical issue affecting public health, particularly in rural communities like Kutri Village. This white paper examines the IAQ challenges faced by families in Kutri Village, the sources of indoor pollution, health impacts, and sustainable solutions. The paper also highlights potential interventions and policy recommendations to improve air quality and health outcomes for village residents.

2. Introduction

Kutri Village, a small rural settlement, relies heavily on traditional biomass fuels for cooking, contributing to high indoor pollution levels. Poor ventilation, combined with lack of awareness and infrastructure, has resulted in increased respiratory diseases, particularly among women and children. Addressing IAQ is crucial for enhancing the overall well-being of the community.

3. Sources of Indoor Air Pollution

The primary contributors to poor IAQ in Kutri Village include:

  • Biomass Fuels: Firewood, cow dung, and crop residues used for cooking emit harmful pollutants like carbon monoxide (CO) and particulate matter (PM2.5).
  • Poor Ventilation: Most homes lack proper airflow, leading to smoke accumulation.
  • High Humidity & Mold Growth: Damp conditions contribute to mold, exacerbating respiratory conditions.
  • Livestock Presence: Ammonia and dust from livestock sheds affect indoor environments.

4. Health Impacts of Poor IAQ

  • Increased cases of asthma, bronchitis, and lung infections.
  • High prevalence of eye irritation, coughing, and headaches.
  • Long-term exposure leading to chronic obstructive pulmonary disease (COPD) and cardiovascular issues.

5. Key Findings from IAQ Study

A survey conducted in 100 households revealed:

  • 85% reliance on biomass for cooking.
  • 70% of kitchens lacked ventilation.
  • 60% of children experienced respiratory symptoms.
  • 90% of families had limited awareness of IAQ risks.

6. Strategies for Improving IAQ

Short-Term Solutions

  • Improved Ventilation: Encouraging semi-open kitchens, installing chimneys, and using exhaust fans.
  • Use of Air-Purifying Plants: Introducing Aloe Vera, Snake Plant, and Areca Palm to absorb indoor pollutants.
  • Community Awareness Programs: Educating families on IAQ hazards and simple preventive measures.

Long-Term Solutions

  • LPG Adoption: Promoting government-subsidized LPG through the Ujjwala Yojana program.
  • Eco-Friendly Housing Designs: Incorporating cross-ventilation and low-cost air filters in home construction.
  • Policy Interventions: Government incentives for clean cooking solutions and sustainable energy sources.

7. Policy Recommendations

  • Strengthen LPG distribution networks to ensure affordability and accessibility.
  • Implement village-wide IAQ monitoring programs to assess progress.
  • Provide financial aid for ventilation improvements in households.
  • Encourage corporate and NGO partnerships for IAQ awareness and technological solutions.

8. Industrial Applications of IAQ Solutions

The IAQ improvement strategies in Kutri Village can be adapted for industrial applications in the following ways:

  • Manufacturing Sector: Industries can integrate low-emission cooking and heating systems for workers’ housing to minimize exposure to harmful pollutants.
  • Agricultural Processing Units: Implementation of proper ventilation and air purification techniques in storage and processing facilities can reduce health risks for workers.
  • Construction Industry: Using IAQ-friendly building materials and eco-friendly architectural designs can help create healthier living and working environments.
  • Corporate Social Responsibility (CSR) Initiatives: Industries can fund and promote IAQ improvement projects in rural areas as part of their environmental sustainability programs.
  • Smart Ventilation Systems: Adaptation of smart exhaust and filtration technologies in both rural homes and industrial settings to improve overall air quality.

9. Conclusion

Improving IAQ in Kutri Village is essential for reducing health risks and enhancing the quality of life. A combination of technological advancements, community engagement, and policy interventions can create sustainable indoor environments, ensuring a healthier future for all residents.

10. Next Steps

  • Expand educational programs on IAQ and its effects.
  • Increase research on cost-effective air purification solutions.
  • Develop collaborative partnerships for implementing IAQ solutions at the village level.

By addressing IAQ in Kutri Village, we can create a replicable model for other rural communities facing similar challenges and extend these solutions to industrial settings to improve worker safety and productivity.

References

  1. ^ Carroll, GT; Kirschman, DL; Mammana, A (2022). “Increased CO2 levels in the operating room correlate with the number of healthcare workers present: an imperative for intentional crowd control”Patient Safety in Surgery16 (35): 35. doi:10.1186/s13037-022-00343-8PMC 9672642PMID 36397098.
  2. ^ ANSI/ASHRAE Standard 62.1, Ventilation for Acceptable Indoor Air Quality, ASHRAE, Inc., Atlanta, GA, US
  3. ^ Belias, Evangelos; Licina, Dusan (2022). “Outdoor PM2. 5 air filtration: optimising indoor air quality and energy”Building & Cities3 (1): 186–203. doi:10.5334/bc.153.
  4. ^ KMC Controls (September 24, 2015). “What’s Your IQ on IAQ and IEQ?”Archived from the original on April 12, 2021. Retrieved April 12, 2021.[unreliable source?]
  5. ^ Bruce, N; Perez-Padilla, R; Albalak, R (2000). “Indoor air pollution in developing countries: a major environmental and public health challenge”Bulletin of the World Health Organization78 (9): 1078–92. PMC 2560841PMID 11019457.
  6. ^ “Household air pollution and health: fact sheet”WHO. May 8, 2018. Archived from the original on November 12, 2021. Retrieved November 21, 2020.
  7. ^ Ritchie, HannahRoser, Max (2019). “Access to Energy”Our World in DataArchived from the original on November 1, 2021. Retrieved April 1, 2021. According to the Global Burden of Disease study 1.6 million people died prematurely in 2017 as a result of indoor air pollution … But it’s worth noting that the WHO publishes a substantially larger number of indoor air pollution deaths..
  8. ^ Klepeis, Neil E; Nelson, William C; Ott, Wayne R; Robinson, John P; Tsang, Andy M; Switzer, Paul; Behar, Joseph V; Hern, Stephen C; Engelmann, William H (July 2001). “The National Human Activity Pattern Survey (NHAPS): a resource for assessing exposure to environmental pollutants”Journal of Exposure Science & Environmental Epidemiology11 (3): 231–252. Bibcode:2001JESEE..11..231Kdoi:10.1038/sj.jea.7500165PMID 11477521S2CID 22445147Archived from the original on March 28, 2023. Retrieved March 30, 2024.
  9. ^ U.S. Environmental Protection Agency. Office equipment: design, indoor air emissions, and pollution prevention opportunities. Air and Energy Engineering Research Laboratory, Research Triangle Park, 1995.
  10. ^ U.S. Environmental Protection Agency. Unfinished business: a comparative assessment of environmental problems, EPA-230/2-87-025a-e (NTIS PB88-127030). Office of Policy, Planning and Evaluation, Washington, DC, 1987.
  11. ^ Klepeis, Neil E; Nelson, William C; Ott, Wayne R; Robinson, John P; Tsang, Andy M; Switzer, Paul; Behar, Joseph V; Hern, Stephen C; Engelmann, William H (July 1, 2001). “The National Human Activity Pattern Survey (NHAPS): a resource for assessing exposure to environmental pollutants”Journal of Exposure Science & Environmental Epidemiology11 (3): 231–252. Bibcode:2001JESEE..11..231Kdoi:10.1038/sj.jea.7500165ISSN 1559-0631PMID 11477521Archived from the original on November 13, 2023. Retrieved November 13, 2023.
  12. ^ “Combined or multiple exposure to health stressors in indoor built environments: an evidence-based review prepared for the WHO training workshop “Multiple environmental exposures and risks”: 16–18 October 2013, Bonn, Germany”World Health Organization. Regional Office for Europe. 2014. Archived from the original on November 6, 2023. Retrieved April 10, 2024.
  13. ^ “Household air pollution”World Health Organization. December 15, 2023. Archived from the original on November 12, 2021. Retrieved April 10, 2024.
  14. ^ Clark, Sierra N.; Lam, Holly C. Y.; Goode, Emma-Jane; Marczylo, Emma L.; Exley, Karen S.; Dimitroulopoulou, Sani (August 2, 2023). “The Burden of Respiratory Disease from Formaldehyde, Damp and Mould in English Housing”Environments10 (8): 136. doi:10.3390/environments10080136ISSN 2076-3298.
  15. ^ “Chief Medical Officer (CMO): annual reports”GOV.UK. November 16, 2023. Retrieved May 5, 2024.
  16. ^ “Project information | Indoor air quality at home | Quality standards | NICE”www.nice.org.uk. Retrieved May 5, 2024.
  17. ^ “The inside story: Health effects of indoor air quality on children and young people”RCPCH. Retrieved May 5, 2024.
  18. ^ Halios, Christos H.; Landeg-Cox, Charlotte; Lowther, Scott D.; Middleton, Alice; Marczylo, Tim; Dimitroulopoulou, Sani (September 15, 2022). “Chemicals in European residences – Part I: A review of emissions, concentrations and health effects of volatile organic compounds (VOCs)”Science of the Total Environment839: 156201. Bibcode:2022ScTEn.83956201Hdoi:10.1016/j.scitotenv.2022.156201ISSN 0048-9697PMID 35623519.
  19. ^ “Literature review on chemical pollutants in indoor air in public settings for children and overview of their health effects with a focus on schools, kindergartens and day-care centres”www.who.int. Retrieved May 5, 2024.
  20. ^ Burge, P S (February 2004). “Sick building syndrome”Occupational and Environmental Medicine61 (2): 185–190. doi:10.1136/oem.2003.008813PMC 1740708PMID 14739390.
  21. ^ Apte, K; Salvi, S (2016). “Household air pollution and its effects on health”F1000Research5: 2593. doi:10.12688/f1000research.7552.1PMC 5089137PMID 27853506Burning of natural gas not only produces a variety of gases such as sulfur oxides, mercury compounds, and particulate matter but also leads to the production of nitrogen oxides, primarily nitrogen dioxide…The burning of biomass fuel or any other fossil fuel increases the concentration of black carbon in the air
  22. ^ “Improved Clean Cookstoves”Project Drawdown. February 7, 2020. Archived from the original on December 15, 2021. Retrieved December 5, 2020.
  23. ^ WHO indoor air quality guidelines: household fuel combustion. Geneva: World Health Organization. 2014. ISBN 978-92-4-154888-5.
  24. ^ “Clearing the Air: Gas Cooking and Pollution in European Homes”CLASP. November 8, 2023. Retrieved May 5, 2024.
  25. ^ Seals, Brady; Krasner, Andee. “Gas Stoves: Health and Air Quality Impacts and Solutions”RMI. Retrieved May 5, 2024.
  26. Jump up to:a b c Myers, Isabella (February 2022). The efficient operation of regulation and legislation: An holistic approach to understanding the effect of Carbon Monoxide on mortality (PDF). CO Research Trust.
  27. Jump up to:a b c Penney, David; Benignus, Vernon; Kephalopoulos, Stylianos; Kotzias, Dimitrios; Kleinman, Michael; Verrier, Agnes (2010), “Carbon monoxide”WHO Guidelines for Indoor Air Quality: Selected Pollutants, World Health Organization, ISBN 978-92-890-0213-4OCLC 696099951archived from the original on March 8, 2021, retrieved March 18, 2024
  28. ^ “Carbon monoxide: toxicological overview”UK Health Security Agency. May 24, 2022. Retrieved April 17, 2024.
  29. Jump up to:a b c WHO global air quality guidelines: particulate matter (PM2.5 and PM10), ozone, nitrogen dioxide, sulfur dioxide and carbon monoxide (PDF). World Health Organization. 2021. hdl:10665/345329ISBN 978-92-4-003422-8.[page needed]
  30. Jump up to:a b Soleimani, Farshid; Dobaradaran, Sina; De-la-Torre, Gabriel E.; Schmidt, Torsten C.; Saeedi, Reza (March 2022). “Content of toxic components of cigarette, cigarette smoke vs cigarette butts: A comprehensive systematic review”. Science of the Total Environment813: 152667. Bibcode:2022ScTEn.81352667Sdoi:10.1016/j.scitotenv.2021.152667PMID 34963586.
  31. ^ “Considering smoking as an air pollution problem for environmental health | Environmental Performance Index”. Archived from the original on September 25, 2018. Retrieved March 21, 2018.
  32. ^ Arfaeinia, Hossein; Ghaemi, Maryam; Jahantigh, Anis; Soleimani, Farshid; Hashemi, Hassan (June 12, 2023). “Secondhand and thirdhand smoke: a review on chemical contents, exposure routes, and protective strategies”Environmental Science and Pollution Research30 (32): 78017–78029. Bibcode:2023ESPR…3078017Adoi:10.1007/s11356-023-28128-1PMC 10258487PMID 37306877.
  33. ^ Arfaeinia, Hossein; Ghaemi, Maryam; Jahantigh, Anis; Soleimani, Farshid; Hashemi, Hassan (June 12, 2023). “Secondhand and thirdhand smoke: a review on chemical contents, exposure routes, and protective strategies”Environmental Science and Pollution Research30 (32): 78017–78029. Bibcode:2023ESPR…3078017Adoi:10.1007/s11356-023-28128-1ISSN 1614-7499PMC 10258487PMID 37306877.
  34. ^ Health, CDC’s Office on Smoking and (May 9, 2018). “Smoking and Tobacco Use; Fact Sheet; Secondhand Smoke”Smoking and Tobacco UseArchived from the original on December 15, 2021. Retrieved January 14, 2019.
  35. ^ Fernández, E; Ballbè, M; Sureda, X; Fu, M; Saltó, E; Martínez-Sánchez, JM (December 2015). “Particulate Matter from Electronic Cigarettes and Conventional Cigarettes: a Systematic Review and Observational Study”Current Environmental Health Reports2 (4): 423–9. Bibcode:2015CEHR….2..423Fdoi:10.1007/s40572-015-0072-xPMID 26452675.
  36. ^ Vu, Tuan V.; Harrison, Roy M. (May 8, 2019). “Chemical and Physical Properties of Indoor Aerosols”. In Harrison, R. M.; Hester, R. E. (eds.). Indoor Air Pollution. The Royal Society of Chemistry (published 2019). ISBN 978-1-78801-803-6.
  37. ^ Abdullahi, Karimatu L.; Delgado-Saborit, Juana Maria; Harrison, Roy M. (February 13, 2013). “Emissions and indoor concentrations of particulate matter and its specific chemical components from cooking: A review”Atmospheric Environment71: 260–294. Bibcode:2013AtmEn..71..260Adoi:10.1016/j.atmosenv.2013.01.061Archived from the original on May 21, 2023. Retrieved April 11, 2024.
  38. ^ Patel, Sameer; Sankhyan, Sumit; Boedicker, Erin K.; DeCarlo, Peter F.; Farmer, Delphine K.; Goldstein, Allen H.; Katz, Erin F.; Nazaroff, William W; Tian, Yilin; Vanhanen, Joonas; Vance, Marina E. (June 16, 2020). “Indoor Particulate Matter during HOMEChem: Concentrations, Size Distributions, and Exposures”Environmental Science & Technology54 (12): 7107–7116. Bibcode:2020EnST…54.7107Pdoi:10.1021/acs.est.0c00740ISSN 0013-936XPMID 32391692Archived from the original on April 28, 2023. Retrieved April 11, 2024.
  39. ^ Thangavel, Prakash; Park, Duckshin; Lee, Young-Chul (June 19, 2022). “Recent Insights into Particulate Matter (PM2.5)-Mediated Toxicity in Humans: An Overview”International Journal of Environmental Research and Public Health19 (12): 7511. doi:10.3390/ijerph19127511ISSN 1660-4601PMC 9223652PMID 35742761.
  40. ^ You, Bo; Zhou, Wei; Li, Junyao; Li, Zhijie; Sun, Yele (November 4, 2022). “A review of indoor Gaseous organic compounds and human chemical Exposure: Insights from Real-time measurements”Environment International170: 107611. Bibcode:2022EnInt.17007611Ydoi:10.1016/j.envint.2022.107611PMID 36335895.
  41. ^ Weschler, Charles J.; Carslaw, Nicola (March 6, 2018). “Indoor Chemistry”Environmental Science & Technology52 (5): 2419–2428. Bibcode:2018EnST…52.2419Wdoi:10.1021/acs.est.7b06387ISSN 0013-936XPMID 29402076Archived from the original on November 15, 2023. Retrieved April 11, 2024.
  42. Jump up to:a b Carter, Toby J.; Poppendieck, Dustin G.; Shaw, David; Carslaw, Nicola (January 16, 2023). “A Modelling Study of Indoor Air Chemistry: The Surface Interactions of Ozone and Hydrogen Peroxide”Atmospheric Environment297: 119598. Bibcode:2023AtmEn.29719598Cdoi:10.1016/j.atmosenv.2023.119598.
  43. ^ Tsai, Wen-Tien (March 26, 2019). “An overview of health hazards of volatile organic compounds regulated as indoor air pollutants”. Reviews on Environmental Health34 (1): 81–89. doi:10.1515/reveh-2018-0046PMID 30854833.
  44. ^ “U.S. EPA IAQ – Organic chemicals”. Epa.gov. August 5, 2010. Archived from the original on September 9, 2015. Retrieved March 2, 2012.
  45. Jump up to:a b Davies, Helen L.; O’Leary, Catherine; Dillon, Terry; Shaw, David R.; Shaw, Marvin; Mehra, Archit; Phillips, Gavin; Carslaw, Nicola (August 14, 2023). “A measurement and modelling investigation of the indoor air chemistry following cooking activities”Environmental Science: Processes & Impacts25 (9): 1532–1548. doi:10.1039/D3EM00167AISSN 2050-7887PMID 37609942.
  46. Jump up to:a b c Harding-Smith, Ellen; Shaw, David R.; Shaw, Marvin; Dillon, Terry J.; Carslaw, Nicola (January 23, 2024). “Does green mean clean? Volatile organic emissions from regular versus green cleaning products”Environmental Science: Processes & Impacts26 (2): 436–450. doi:10.1039/D3EM00439BISSN 2050-7887PMID 38258874.
  47. ^ Lebel, Eric D.; Michanowicz, Drew R.; Bilsback, Kelsey R.; Hill, Lee Ann L.; Goldman, Jackson S. W.; Domen, Jeremy K.; Jaeger, Jessie M.; Ruiz, Angélica; Shonkoff, Seth B. C. (November 15, 2022). “Composition, Emissions, and Air Quality Impacts of Hazardous Air Pollutants in Unburned Natural Gas from Residential Stoves in California”Environmental Science & Technology56 (22): 15828–15838. Bibcode:2022EnST…5615828Ldoi:10.1021/acs.est.2c02581ISSN 0013-936XPMC 9671046PMID 36263944.
  48. ^ “Volatile Organic Compounds’ Impact on Indoor Air Quality”United States Environmental Protection Agency. August 18, 2014. Retrieved May 23, 2024.
  49. ^ “About VOCs”. January 21, 2013. Archived from the original on January 21, 2013. Retrieved September 16, 2019.
  50. ^ Oanh, Nguyen Thi Kim; Hung, Yung-Tse (2005). “Indoor Air Pollution Control”. Advanced Air and Noise Pollution Control. Handbook of Environmental Engineering. Vol. 2. pp. 237–272. doi:10.1007/978-1-59259-779-6_7ISBN 978-1-58829-359-6.
  51. ^ “Emicode”. Eurofins.com. Archived from the original on September 24, 2015. Retrieved March 2, 2012.
  52. ^ “M1”. Eurofins.com. Archived from the original on September 24, 2015. Retrieved March 2, 2012.
  53. ^ “Blue Angel”. Eurofins.com. Archived from the original on September 24, 2015. Retrieved March 2, 2012.
  54. ^ “Indoor Air Comfort”. Indoor Air Comfort. Archived from the original on February 1, 2011. Retrieved March 2, 2012.
  55. ^ “CDPH Section 01350”. Eurofins.com. Archived from the original on September 24, 2015. Retrieved March 2, 2012.
  56. Jump up to:a b “Smelly Moldy Houses”Archived from the original on December 15, 2021. Retrieved August 2, 2014.
  57. ^ Meruva, N. K.; Penn, J. M.; Farthing, D. E. (November 2004). “Rapid identification of microbial VOCs from tobacco molds using closed-loop stripping and gas chromatography/time-of-flight mass spectrometry”J Ind Microbiol Biotechnol31 (10): 482–8. doi:10.1007/s10295-004-0175-0PMID 15517467S2CID 32543591.
  58. ^ “Atmospheric carbon dioxide passes 400 ppm everywhere”. Physics Today (6): 8170. 2016. Bibcode:2016PhT..2016f8170.doi:10.1063/pt.5.029904.
  59. ^ Xie Y, Li Y, Feng Y, Cheng W, Wang Y (April 2022). “Inhalable microplastics prevails in air: Exploring the size detection limit”Environ Int162: 107151. Bibcode:2022EnInt.16207151Xdoi:10.1016/j.envint.2022.107151PMID 35228011.
  60. ^ Liu C, Li J, Zhang Y, Wang L, Deng J, Gao Y, Yu L, Zhang J, Sun H (July 2019). “Widespread distribution of PET and PC microplastics in dust in urban China and their estimated human exposure”Environ Int128: 116–124. Bibcode:2019EnInt.128..116Ldoi:10.1016/j.envint.2019.04.024PMID 31039519.
  61. ^ Yuk, Hyeonseong; Jo, Ho Hyeon; Nam, Jihee; Kim, Young Uk; Kim, Sumin (2022). “Microplastic: A particulate matter(PM) generated by deterioration of building materials”. Journal of Hazardous Materials437. Elsevier BV: 129290. Bibcode:2022JHzM..43729290Ydoi:10.1016/j.jhazmat.2022.129290ISSN 0304-3894PMID 35753297.
  62. ^ Eberhard, Tiffany; Casillas, Gaston; Zarus, Gregory M.; Barr, Dana Boyd (January 6, 2024). “Systematic review of microplastics and nanoplastics in indoor and outdoor air: identifying a framework and data needs for quantifying human inhalation exposures” (PDF). Journal of Exposure Science & Environmental Epidemiology34 (2). Springer Science and Business Media LLC: 185–196. doi:10.1038/s41370-023-00634-xISSN 1559-0631. Retrieved December 19, 2024. MPs have been found in water and soil, and recent research is exposing the vast amount of them in ambient and indoor air.
  63. ^ Gasperi, Johnny; Wright, Stephanie L.; Dris, Rachid; Collard, France; Mandin, Corinne; Guerrouache, Mohamed; Langlois, Valérie; Kelly, Frank J.; Tassin, Bruno (2018). “Microplastics in air: Are we breathing it in?” (PDF). Current Opinion in Environmental Science & Health1: 1–5. Bibcode:2018COESH…1….1Gdoi:10.1016/j.coesh.2017.10.002S2CID 133750509Archived (PDF) from the original on March 6, 2020. Retrieved July 11, 2019.
  64. ^ Prasittisopin, Lapyote; Ferdous, Wahid; Kamchoom, Viroon (2023). “Microplastics in construction and built environment”Developments in the Built Environment15. Elsevier BV. doi:10.1016/j.dibe.2023.100188ISSN 2666-1659.
  65. ^ Galloway, Nanette LoBiondo (September 13, 2024). “Ventnor introduces ordinance to control microplastics contamination”DownBeach. Retrieved October 2, 2024.
  66. ^ Weschler, Charles J. (December 2000). “Ozone in Indoor Environments: Concentration and Chemistry: Ozone in Indoor Environments”Indoor Air10 (4): 269–288. doi:10.1034/j.1600-0668.2000.010004269.xPMID 11089331Archived from the original on April 15, 2024. Retrieved April 11, 2024.
  67. ^ Weschler, Charles J.; Nazaroff, William W (February 22, 2023). “Human skin oil: a major ozone reactant indoors”Environmental Science: Atmospheres3 (4): 640–661. doi:10.1039/D3EA00008GISSN 2634-3606Archived from the original on April 15, 2024. Retrieved April 11, 2024.
  68. ^ Kumar, Prashant; Kalaiarasan, Gopinath; Porter, Alexandra E.; Pinna, Alessandra; Kłosowski, Michał M.; Demokritou, Philip; Chung, Kian Fan; Pain, Christopher; Arvind, D. K.; Arcucci, Rossella; Adcock, Ian M.; Dilliway, Claire (February 20, 2021). “An overview of methods of fine and ultrafine particle collection for physicochemical characterisation and toxicity assessments”Science of the Total Environment756: 143553. Bibcode:2021ScTEn.75643553Kdoi:10.1016/j.scitotenv.2020.143553hdl:10044/1/84518PMID 33239200S2CID 227176222.
  69. ^ Apte, M. G.; Buchanan, I. S. H.; Mendell, M. J. (April 2008). “Outdoor ozone and building-related symptoms in the BASE study”Indoor Air18 (2): 156–170. Bibcode:2008InAir..18..156Adoi:10.1111/j.1600-0668.2008.00521.xPMID 18333994.
  70. ^ “Eight-hour Average Ozone Concentrations | Ground-level Ozone | New England | US EPA”United States Environmental Protection AgencyArchived from the original on December 15, 2021. Retrieved September 16, 2019.
  71. Jump up to:a b c Park, J. H.; Cox-Ganser, J. M. (2011). “Meta-Mold exposure and respiratory health in damp indoor environments”Frontiers in Bioscience3 (2): 757–771. doi:10.2741/e284PMID 21196349.
  72. ^ “CDC – Mold – General Information – Facts About Mold and Dampness”. December 4, 2018. Archived from the original on December 16, 2019. Retrieved June 23, 2017.
  73. ^ Singh, Dr Jagjit; Singh, Jagjit, eds. (1994). Building Mycology (1 ed.). Taylor & Francis. doi:10.4324/9780203974735ISBN 978-1-135-82462-4.
  74. Jump up to:a b Clarke, J.A; Johnstone, C.M; Kelly, N.J; McLean, R.C; anderson, J.A; Rowan, N.J; Smith, J.E (January 20, 1999). “A technique for the prediction of the conditions leading to mould growth in buildings”Building and Environment34 (4): 515–521. Bibcode:1999BuEnv..34..515Cdoi:10.1016/S0360-1323(98)00023-7Archived from the original on October 26, 2022. Retrieved April 10, 2024.
  75. ^ Vereecken, Evy; Roels, Staf (November 15, 2011). “Review of mould prediction models and their influence on mould risk evaluation”Building and Environment51: 296–310. doi:10.1016/j.buildenv.2011.11.003Archived from the original on March 2, 2024. Retrieved April 11, 2024.
  76. ^ BS 5250:2021 – Management of moisture in buildings. Code of practice. British Standards Institution (BSI). October 31, 2021. ISBN 978-0-539-18975-9.
  77. ^ Madgwick, Della; Wood, Hannah (August 8, 2016). “The problem of clothes drying in new homes in the UK”Structural Survey34 (4/5): 320–330. doi:10.1108/SS-10-2015-0048ISSN 0263-080XArchived from the original on May 7, 2021. Retrieved April 11, 2024.
  78. ^ May, Neil; McGilligan, Charles; Ucci, Marcella (2017). “Health and Moisture in Buildings” (PDF). UK Centre for Moisture in BuildingsArchived (PDF) from the original on April 11, 2024. Retrieved April 11, 2024.
  79. ^ “Understanding and addressing the health risks of damp and mould in the home”GOV.UK. September 7, 2023. Archived from the original on April 10, 2024. Retrieved April 11, 2024.
  80. ^ Clark, Sierra N.; Lam, Holly C. Y.; Goode, Emma-Jane; Marczylo, Emma L.; Exley, Karen S.; Dimitroulopoulou, Sani (August 2, 2023). “The Burden of Respiratory Disease from Formaldehyde, Damp and Mould in English Housing”Environments10 (8): 136. doi:10.3390/environments10080136ISSN 2076-3298.
  81. ^ Microbiology of the Indoor Environment Archived July 23, 2011, at the Wayback Machine, microbe.net
  82. ^ http://www.info.gov.hk/info/sars/pdf/amoy_e.pdf
  83. ^ https://www.info.gov.hk/info/sars/graphics/amoyannex.jpg
  84. ^ “Progress in Global Surveillance and Response Capacity 10 Years after Severe Acute Respiratory Syndrome”environmental contamination with SARS CoV RNA was identified on the carpet in front of the index case-patient’s room and 3 nearby rooms (and on their door frames but not inside the rooms) and in the air intake vents near the centrally located elevators … secondary infections occurred not in guest rooms but in the common areas of the ninth floor, such as the corridor or elevator hall. These areas could have been contaminated through body fluids (e.g., vomitus, expectorated sputum), respiratory droplets, or suspended small-particle aerosols generated by the index case-patient; other guests were then infected by fomites or aerosols while passing through these same areas. Efficient spread of SARS CoV through small-particle aerosols was observed in several superspreading events in health care settings, during an airplane flight, and in an apartment complex (12–14,16–19). This process of environmental contamination that generated infectious aerosols likely best explains the pattern of disease transmission at the Hotel Metropole.
  85. ^ Azuma, Kenichi; Kagi, Naoki; Yanagi, U.; Osawa, Haruki (December 2018). “Effects of low-level inhalation exposure to carbon dioxide in indoor environments: A short review on human health and psychomotor performance”Environment International121 (Pt 1): 51–56. Bibcode:2018EnInt.121…51Adoi:10.1016/j.envint.2018.08.059PMID 30172928.
  86. ^ Du, Bowen; Tandoc, Michael (June 19, 2020). “Indoor CO2 concentrations and cognitive function: A critical review”International Journal of Indoor Environment and Health30 (6): 1067–1082. Bibcode:2020InAir..30.1067Ddoi:10.1111/ina.12706PMID 32557862S2CID 219915861.
  87. ^ Fan, Yuejie; Cao, Xiaodong; Zhang, Jie; Lai, Dayi; Pang, Liping (June 1, 2023). “Short-term exposure to indoor carbon dioxide and cognitive task performance: A systematic review and meta-analysis”Building and Environment237: 110331. Bibcode:2023BuEnv.23710331Fdoi:10.1016/j.buildenv.2023.110331.
  88. Jump up to:a b Lowther, Scott D.; Dimitroulopoulou, Sani; Foxall, Kerry; Shrubsole, Clive; Cheek, Emily; Gadeberg, Britta; Sepai, Ovnair (November 16, 2021). “Low Level Carbon Dioxide Indoors—A Pollution Indicator or a Pollutant? A Health-Based Perspective”Environments8 (11): 125. doi:10.3390/environments8110125ISSN 2076-3298.
  89. ^ Persily, Andrew (July 2022). “Development and application of an indoor carbon dioxide metric”Indoor Air32 (7): e13059. doi:10.1111/ina.13059PMID 35904382.
  90. ^ “Indoor Environmental Quality: HVAC Management | NIOSH | CDC”www.cdc.gov. February 25, 2022. Archived from the original on April 1, 2022. Retrieved April 1, 2022.
  91. ^ Indoor Environmental Quality: Building Ventilation Archived January 20, 2022, at the Wayback Machine. National Institute for Occupational Safety and Health. Accessed October 8, 2008.
  92. ^ “SAMHE – Schools’ Air quality Monitoring for Health and Education”samhe.org.ukArchived from the original on March 18, 2024. Retrieved March 18, 2024.
  93. ^ “Document Display | NEPIS | US EPA”nepis.epa.govArchived from the original on November 16, 2023. Retrieved October 19, 2023.
  94. ^ Zeeb & Shannoun 2009, p. 3.
  95. ^ C.Michael Hogan and Sjaak Slanina. 2010, Air pollution. Encyclopedia of Earth Archived October 12, 2006, at the Wayback Machine. eds. Sidney Draggan and Cutler Cleveland. National Council for Science and the Environment. Washington DC
  96. ^ “Radon Mitigation Methods”. Radon Solution—Raising Radon Awareness. Archived from the original on December 15, 2008. Retrieved December 2, 2008.
  97. ^ Zeeb & Shannoun 2009, p. [page needed].
  98. ^ “Basic radon facts” (PDF). US Environmental Protection Agency. Archived (PDF) from the original on January 13, 2022. Retrieved September 18, 2018. Public Domain This article incorporates text from this source, which is in the public domain.
  99. ^ “Radon Action Level and Target Level”UKradonArchived from the original on March 18, 2024. Retrieved March 18, 2024.
  100. ^ “Radon Zone Map (with State Information)”U.S. Environmental Protection AgencyArchived from the original on April 1, 2023. Retrieved April 10, 2024.
  101. ^ “UK maps of radon”UKradonArchived from the original on March 7, 2024. Retrieved April 10, 2024.
  102. ^ “Radon map of Australia”Australian Radiation Protection and Nuclear Safety Agency (ARPANSA)Archived from the original on March 20, 2024. Retrieved April 10, 2024.
  103. ^ “Climate Change 2021: The Physical Science Basis”Intergovernmental Panel on Climate ChangeArchived (PDF) from the original on May 26, 2023. Retrieved April 15, 2024.
  104. ^ Chen, Guochao; Qiu, Minghao; Wang, Peng; Zhang, Yuqiang; Shindell, Drew; Zhang, Hongliang (July 19, 2024). “Continuous wildfires threaten public and ecosystem health under climate change across continents”Frontiers of Environmental Science & Engineering18 (10). doi:10.1007/s11783-024-1890-6ISSN 2095-2201.
  105. ^ Gherasim, Alina; Lee, Alison G.; Bernstein, Jonathan A. (November 14, 2023). “Impact of Climate Change on Indoor Air Quality”Immunology and Allergy Clinics of North America44 (1): 55–73. doi:10.1016/j.iac.2023.09.001PMID 37973260Archived from the original on November 15, 2023. Retrieved April 15, 2024.
  106. ^ Lacressonnière, Gwendoline; Watson, Laura; Gauss, Michael; Engardt, Magnuz; Andersson, Camilla; Beekmann, Matthias; Colette, Augustin; Foret, Gilles; Josse, Béatrice; Marécal, Virginie; Nyiri, Agnes; Siour, Guillaume; Sobolowski, Stefan; Vautard, Robert (February 1, 2017). “Particulate matter air pollution in Europe in a +2 °C warming world”Atmospheric Environment154: 129–140. Bibcode:2017AtmEn.154..129Ldoi:10.1016/j.atmosenv.2017.01.037Archived from the original on November 17, 2023. Retrieved April 15, 2024.
  107. ^ Lee, J; Lewis, A; Monks, P; Jacob, M; Hamilton, J; Hopkins, J; Watson, N; Saxton, J; Ennis, C; Carpenter, L (September 26, 2006). “Ozone photochemistry and elevated isoprene during the UK heatwave of august 2003”Atmospheric Environment40 (39): 7598–7613. Bibcode:2006AtmEn..40.7598Ldoi:10.1016/j.atmosenv.2006.06.057Archived from the original on October 26, 2022. Retrieved April 15, 2024.
  108. ^ Salthammer, Tunga; Schieweck, Alexandra; Gu, Jianwei; Ameri, Shaghayegh; Uhde, Erik (August 7, 2018). “Future trends in ambient air pollution and climate in Germany – Implications for the indoor environment”Building and Environment143: 661–670. Bibcode:2018BuEnv.143..661Sdoi:10.1016/j.buildenv.2018.07.050.
  109. ^ Zhong, L.; Lee, C.-S.; Haghighat, F. (December 1, 2016). “Indoor ozone and climate change”Sustainable Cities and Society28: 466–472. doi:10.1016/j.scs.2016.08.020Archived from the original on November 28, 2022. Retrieved April 15, 2024.
  110. ^ Zhao, Jiangyue; Uhde, Erik; Salthammer, Tunga; Antretter, Florian; Shaw, David; Carslaw, Nicola; Schieweck, Alexandra (December 9, 2023). “Long-term prediction of the effects of climate change on indoor climate and air quality”Environmental Research243: 117804. doi:10.1016/j.envres.2023.117804PMID 38042519.

Table of Contents

Leave a Comment

Your email address will not be published. Required fields are marked *

© 2024 Created with kutri.in
Scroll to Top
× How can I help you?