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Environment, People, Prosperity: Toward A Balance We Can Live With
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A Brief History of Particulate Matter
Section 6 – Health Effects
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Outdoor Air Pollution Regulatory Categories
Criteria Pollutants Present everywhere Ambient air quality standards Widely monitored Air toxics Long list (>180) Many carcinogens Less frequent ambient measurements Section 6 – Health Effects
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Select Air Pollution Disasters
1930 Meuse River Valley, Belgium A three-day episode of severe air pollution makes 6,000 ill and kills 63. 1948 Denora, PA Oct. 26 to 31: air pollution episode leaves 20 dead out of 14,000 persons. 1952 London, England Dec. 4 to 9: “Killer Fog” leaves three to four thousand people dead. Donora, PA at noon on Oct. 29, 1948 London buses are escorted by lantern at 10:30 in the morning. Section 6 – Health Effects
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Section 6 – Health Effects
Chico Air Quality – 11/12/18 Section 6 – Health Effects
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many different sources
PM is derived from many different sources Section 6 – Health Effects
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Mouse Lung Exposed to Diesel Exhaust: What It Does
Normal mouse lung Exposed mouse lung Diesel Exhaust Particles (DEP) augment inflammation by increasing receptors for bacterial lipopolysaccharide. The effect is to make the lungs highly sensitive to the presence of normal levels of bacteria. This results in greatly heightened production of pro-inflammatory mediators from the cells. Section 6 – Health Effects
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Section 6 – Health Effects
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Section 6 – Health Effects
Human Lung Basics Air conducting Trachea Bronchi Bronchioles Gas exchange Respiratory bronchioles Alveoli Section 6 – Health Effects
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Particles Affect the Lungs
Respiratory system effects: Respiratory symptoms – irritation of airways, cough Decreased lung function Airway inflammation Asthma attacks, bronchitis Chronic bronchitis Allergies, which are inflammatory responses Section 6 – Health Effects
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Section 6 – Health Effects
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Section 6 – Health Effects
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Section 6 – Health Effects
Public Health Risks Are Significant + Health Care Costs in U.S. are at ~ 20% of Economy Particles are linked to: Premature death from heart and lung diseases Aggravation of heart and lung diseases, with increased: Hospital admissions Doctor and ER visits Medication use School and work absences Section 6 – Health Effects
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Section 6 – Health Effects
Nitrogen dioxide (NO2) Emissions from high temperature combustion processes: motor vehicle exhaust and stationary sources for power production Exposures indoors due to (unvented) gas appliances and infiltration of ambient NO2 (Complex atmospheric chemistry – can be transformed to HNO3 and nitrate particles) Section 6 – Health Effects
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Nitrogen dioxide (NO2) effects
Strong oxidant and respiratory irritant (forms nitrous and nitric acids in contact with water) NO2 irritates the nose, throat and lungs especially in people with asthma. Lowers resistance to respiratory infections such as influenza. Contributes to ozone formation (and thus to ozone effects indirectly). Section 6 – Health Effects
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Section 6 – Health Effects
Ozone (O3) Ubiquitous exposure - formed by natural processes as well as human activities Principal constituent of photochemical smog – which is not emitted directly Highly reactive, but poorly soluble, allowing deep lung penetration Acute toxicity is related to dose = Concentration x Ventilation Rate x Time – increased risk from outdoor exertion modeling/ For advanced sustainers, and those wishing to understand the systemic function of pollutants on climate, etc. Section 6 – Health Effects
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Section 6 – Health Effects
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Good (High) vs Bad Ozone (Low; smog)
Chlorofluorocarbons (CFCs) are fully halogenated paraffin hydrocarbons that contain only carbon, chlorine, and fluorine, produced as volatile derivative of methane, ethane, and propane. They are also commonly known by the DuPont brand name Freon. The most common representative is dichlorodifluoromethane. Many CFCs have been widely used as refrigerants, propellants, and solvents. Because CFCs contribute to ozone depletion in the upper atmosphere, the manufacture of such compounds has been phased out under the Montreal Protocol, and they are being replaced with other products such as hydrofluorocarbons and R-134a. Section 6 – Health Effects
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Disease risk – environmental, genetic factors
Estimates of the burden of disease attributable to environmental factors vary depending on Type of disease Vulnerability Genetics Population group Socioeconomic aspects Large differences between people living in Industrialized/developing countries East/West of Europe and others Section 6 – Health Effects
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Ozone Irritates Airways
Symptoms: Cough Sore or scratchy throat Pain with deep breath, or chest pain Fatigue Rapid onset, but effect is greater 24 hours after exposure Similar symptoms for people with or without asthma Section 6 – Health Effects
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Section 6 – Health Effects
Sulfur dioxide (SO2) Irritant gas resulting mainly from combustion of sulfur-containing fossil fuels (power plants, large industrial facilities, diesel vehicles) and metal smelting. (Is oxidized/hydrated to form sulfuric acid particles) Coal miner deaths jump in 2017 after 2016's low point – it is recommended you review this discussion for an understanding of coal mining discussions in the US Section 6 – Health Effects
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Public Health Risks Are Significant
Ozone is linked to: Aggravation of lung diseases, increased Hospital admissions Doctor and ER visits Medication use School and work absences Permanent lung changes Section 6 – Health Effects
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At-Risk Groups for Respiratory Irritants
People with heart or lung disease Greater deposition with chronic obstructive pulmonary disease (COPD) Older adults Greater prevalence of heart and lung disease Children More likely to be active Breathe more air per kg Bodies still developing Section 6 – Health Effects
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Will It Matter if Air Pollution Decreases?
The Dublin Experience Dublin’s air quality deteriorated in the 1980s after a switch from oil to cheaper bituminous coal for heating. In 1990 the Irish Government banned the use of bituminous coal within the city of Dublin, resulting in a reduction in PM concentrations. Change in age-standardized total, cause-specific, and age-specific mortality rates for Dublin County Borough for 72 months before and after ban of sale of coal in Dublin: decrease from 4.5 to 15.5 % depending on the specific risk group. Section 6 – Health Effects
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