Unit 7 - Air Pollution
Unit 7 Air Pollution
7.1 Introduction to Air Pollution (Pollutants)
Air Pollution Basics
Write about air pollutants (specific molecules/particles) not just air “pollution” as an idea
Clean Air Act (1980) identified 6 criteria air pollutants that the EPA is required to set acceptable limits for, monitor, and enforce
SO2 - Sulfur dioxide: coal combustion (electricity), respiratory irritation, smog, acid precipitation
NOx – Nitrogen Oxides (NO & NO2): all fossil fuel combustion, O3 photochemical smog, acid precipitation
CO – Carbon monoxide: incomplete combustion, O3, lethal to humans
PM – Particulate matter: fossil fuel/biomass combustion, respiratory irritation, smog
O3 – Ozone (tropospheric): photochemical oxidation of NO2, respiratory irritation, smog, plant damage
Pb – Lead: metal plants, waste incineration, neurotoxicant
Air Pollutants vs. Greenhouse Gasses
CO2 is not one of 6 criteria pollutants in Clean Air Act
CO2 does not directly lower air quality from a human health standpoint
Not toxic to organisms to breath
Not damaging to lungs/ eyes
Does not lead to smog, decreased visibility
CO2 is a greenhouse gas; it does lead to earth warming, and thus environment and human health consequences
Bottom line: in APES, CO2 has not typically been included on FRQ scoring guides as an air pollutant (stick to SO2, NOx, O3, PM)
Coal Combustion
Releases more air pollutants than other fossil fuels
Releases CO, CO2, SO2, NOx, toxic metals (mercury, arsenic, lead), and PM (0ften carries the toxic metals)
Impacts of SO2
Respiratory irritant (inflammation of bronchioles, lungs), worsens asthma and bronchitis
Sulfur aerosols (suspended sulfate particles) block incoming sun, reducing visibility and photosynthesis
Forms sulfurous (grey) smog
Combines with water and O2 in atmosphere to form sulfuric acid 🡪 acid precipitation
Nitrogen Oxides (NOx)
Released by combustion of anything, especially FFs and biomass
NOx refers to nitrogen oxides (both NO and NO2)
NO forms when N2 combines with O2 (especially during combustion)
NO can become NO2 by reacting with O3 or O2
Sunlight converts NO2 back into NO
Environment and Human Health Impacts
Respiratory irritant
Leads to tropospheric ozone (O3) formation, which leads to photochemical smog
Combines with water and O2 in atmosphere to form nitric acid 🡪 acid precipitation
EPA and Lead
Before CAA< lead was a common gasoline additive; EPA began phaseout of lead from gasoline in 1974. Vehicles made after 1974 are required to have catalytic converters to reduce NOx, CO, and hydrocarbon emissions (lead damages catalytic converters)
Primary vs. Secondary Air Pollutants
Primary
Emitted directly from sources such as vehicles, power plants, factories, or natural sources (volcanoes, forest fires)
NOx, CO, CO2, VOCs, SO2, PM, and hydrocarbons
Secondary
Primary pollutants that have transformed in presence of sunlight, water, O2
Occur more during the day (since sunlight often drives formation
Tropospheric O3 (ozone)
Sulfuric acid (H2SO4) and sulfate (SO42-)
Nitric acid (HNO3) and nitrate (NO3-)
7.2 Photochemical Smog
Photochemical Smog Precursors and Conditions
Precursors
NO2 – broken by sunlight into NO + O (free O + O2 🡪 O3)
VOCs - volatile organic compounds (hydrocarbons) that bind with NO and form photochemical oxidants
Carbon-based compounds that volatize (evaporate) easily (this makes them “smelly”)
Sources: gasoline, formaldehyde, cleaning fluids, oil-based paints, even coniferous trees (pine smell)
O3 – forms when NO2 is broken by sunlight and free O binds to O2
Respiratory irritant in troposphere (at earth’s surface)
Damaging to plants stomata, limiting growth
Conditions
Sunlight - drives O3 formation by breaking down NO2 🡪 NO + O; then free O atom binds with O2
Warmth – hotter atmosphere temperature speeds O3 formation, evaporation of VOCs and thus smog formation
Normal O3 Formation
Morning commute leads to high NO2 levels from car exhaust
Sunlight breaks NO2 into NO + O
O bonds with O2 to form O3
O3 formation typically peaks in afternoon when sunlight is most direct and NO2 emissions from morning traffic have peaked
At night, O3 reacts with NO to form NO2 and O2 once again; O3 levels drop overnight
Photochemical Smog Formation
Sunlight breaks NO2 into NO + O
O bonds with O2 to form O3
VOCs bonds with NO to form photochemical oxidants
Without NO to react with, O3 builds up instead of returning to O2 and NO2 overnight
O3 combines with photochemical oxidants (NO + VOCs) to form photochemical smog
Factors that Increase Smog Form
Increased vehicle traffic; increases NO2 emissions and therefore O3 formation
Higher VOCs emissions (gas stations, laundromats, petrochemicals, and plastic factories)
More sunlight (summer, afternoon) = more O3
Warmer temperature, speeds evaporation of VOCs and reaction that lead to O3
Urban areas have more smog due to all of these factors
Impacts of Smog
Environment (reduces sunlight; limiting photosynthesis, O3 damages plants stomata and irritates animal respiratory tracts)
Humans (respiratory irritant; worsens asthma, bronchitis, COPD; irritates eyes)
Economic (increased health care costs to treat asthma, bronchitis, COPD, lost productivity due to sick workers missing work or dying, decreased agriculture yields due to less sunlight reaching crops and damage to plant stomata)
Reduction of Smog
Vehicles (decreasing the number of vehicles on road decreases NO2 emissions, fewer vehicles = less gas = fewer VOCs)
Energy (increased electricity production from renewable sources that don’t emit NOx (solar, wind, hydro), natural gas power plants release far less NOx than coal)
7.3 Thermal Inversion
Urban Heat Island Effect
Urban areas tend to have higher surface and air temperature than surrounding suburban and rural areas due to:
Lower albedo: concrete and asphalt absorb more of sun’s energy than areas with more vegetation (absorbed sunlight is given off as IR radiation – heat)
Less evapotranspiration: water evaporating from surfaces and transpiration from plants carries heat from surface into the atmosphere
this cools off rural and suburban areas which have more vegetation
Thermal Inversion
Normally the atmosphere is warmest at earth’s surface, and cools as altitude rises. Because warm air rises, air convection carries air pollutants away from earth’s surface and distributes them higher into the atmosphere
During a thermal inversion, a cooler air mass becomes trapped near earth’s surface
due to a warm front moving in over it
or due to hot urban surfaces colling overnight while IR radiation absorbed during the day is still being released
because cold air at the surface is trapped beneath the warmer mass above, convection doesn’t carry pollutants up and away.
Effects of Thermal Inversion
Air pollutants (smog, PM, ozone, SO2, NOx) trapped closer to earth
Respiratory irritation: asthma flare ups leading to hospitalization, worsened COPD, emphysema
Decreased tourism revenue
Decreased photosynthetic rate
7.4 Atmospheric CO2 and PM
Natural Sources of Air Pollutants
Lighting strikes (convert N2 in atmosphere to NOx)
Forest fires (CO, PM, NOx, combustion of biomass also releases CO2 and H2O vapor) (greenhouse gasses)
Plants (especially conifers) (plants emit VOCs)
Volcanoes (SO2, PM, CO, NOx)
Natural Sources of CO2 and PM
Respiration (all living thins release CO2 through respiration)
Natural PM Sources (sea salt, pollen, ash from forest fires, volcanoes, and dust leads to haze)
Aerobic Decomposition (decomposition of organic matter by bacteria and decomposers in the presence of oxygen 🡪 releases CO2)
Anaerobic decomposition (decomposition of organic matter by bacteria and decomposers in low or oxygen-free conditions 🡪 releases CH4 (methane))
PM10 vs PM2.5
Particulate matter: solid or liquid particles suspended in air (also referred to as “particulates”)
PM10 (< 10 micrometers)
Particles or droplets like dust, pollen, ash, or mold
Too small to be filtered out by nose hairs and trachea cilia; can irritate respiratory tract and cause inflammation
PM2.5 (< 2.5 micrometers)
Particles from combustion (especially vehicles) smaller dust particles
More likely to travel deep into the lungs due to smaller size
Associated with chronic bronchitis and increased risk of lung cancer
7.5 Indoor Air Pollutants
Developing Countries
Developing nations use more subsistence fuels such as wood, manure, charcoal (biomass)
These biomass fuels release CO, PM, NO2, VOCs (can also cause deforestation)
Often combusted indoors with poor ventilation, leading to high concentrations
Developed Countries
Developed nations use more commercial fuels (coal, oil, natural gas) supplied by utilities
Typically burned in closed, well ventilated furnaces, stoves, etc.
Major indoor air pollutants in developed nations come from chemicals in products: adhesives in furniture, cleaning supplies, insulation, lead paint
PM and Asbestos
Particulates (PM) are common indoor air pollutant
Asbestos is a long, silicate particle previously used in insulations (since been linked to lung cancer and asbestosis)
CO (Carbon Monoxide)
CO is an asphyxiant: causes suffocation due to CO binding to hemoglobin in blood, displacing O2
Lethal to humans in high concentrations, especially with poor ventilation (odorless and colorless – hard to detect)
Developed nations: CO released into home by malfunctioning natural gas furnace ventilation
Developing nations: CO emitted from indoor biomass combustion for heating/cooking
VOCs (Volatile Organic Compounds)
Chemicals used in a variety of home products that easily vaporize, enter air, and irritate eyes, lungs, bronchioles
Adhesives/sealants: chemicals used to glue carpet down, hold furniture together, seals panels
Formaldehyde is a common adhesive in particle board and carpet glues
Cleaners: common household cleaners and deodorizers such as Febreze
Plastics and Fabrics: both can release VOCs themselves, or from adhesives used in production
Radon Gas
Radioactive gas released by decay of uranium naturally found in rocks underground (granite especially)
Usually enters homes through cracks in the foundation and then disperse up from basement/foundation through home
can also seep into groundwater sources and enter body through drinking water
Dust and Mold
Natural indoor air pollutants that can worsen asthma, bronchitis, COPD, emphysema
Dust settles in homes naturally, is disturbed by movement, entering air and then respiratory tract
Mold develops in areas that are dark and damp and aren’t well ventilated
Lead
Found in paint in old homes
Paint chips off walls/windows and is eaten by small children or inhaled as dust
7.6 Reduction of Air Pollutants
Reducing Emissions
Reducing emissions = reducing air pollutants
Law/Regulations
Clean Air Act
Allows EPA to set acceptable levels for criteria air pollutants
Monitor emissions levels from power plants and other facilities
Tax/sue/fine corporations that release emissions above levels
CAFE Vehicle Standards
(Corporate Average Fuel Economy) standards require the entire US fleet of vehicles to meet certain average
Requires vehicle manufacturers to work to make more efficient vehicles
More efficient vehicles burn less gasoline and release less NOx, PM, CO, and CO2
Pollution Credits
Similar to ITQs for fish
Companies that reduce emissions below EPA-set levels earn pollution credits
Reducing Vehicle Air Pollutants
Vapor Recovery Nozzle
Capture hydrocarbon VOCs released from gasoline fumes during refueling
Separate tubes inside nozzle captures vapors and returns them to underground storage tank beneath the gas station
Reduces VOCs, which contribute to smog and irritate respiratory tracts
Reduces benzene (carcinogen) released from gasoline vapors
Catalytic Converter (CC)
Required on all vehicles after 1975
Contains metals (platinum and palladium) that bind to NOx and CO
CC converts NOx, CO, and other hydrocarbons into CO2, N2, O2, and H2O
Reducing SOx and NOx
Crushed Limestone (SO2)
Used to reduce SO2 from coal power plants
Crushed coal mixed with limestone (calcium carbonate) before being burned in boiler
Calcium carbonate in limestone combines with SO2 to produce calcium sulfate, reducing the SO2 being emitted
Calcium sulfate can be used to make gypsum wallboard or sheetrock for home foundations
Fluidized Bed Combustion (NOz)
Fluidizing jets of air pumped into combustion “bed”
Jets of air bring more 02 into reaction, making combustion more efficient and bringing SO2 into more contact with calcium carbonate in limestone
Also allows coal to be combusted at lower temperature, which emits less NOx
Wet and Dry Scrubbers
Dry Scrubbers (NOx, SOx, VOCs)
Large column/tube/pipe filled with chemicals that absorb or neutralize oxides (NOx, SOx, VOCs_ from exhaust streams (emissions)
Calcium oxide is a common dry scrubber additive which reacts with SO2 to form calcium sulfite
Wet Scrubbers (NOx, SOx, VOCs + PM)
May involve chemical agents that absorb or neutralize NOx, SOx, VOCs, but also include mist nozzles that trap PM in water droplets as well
Reducing Particulate Matter
Electrostatic Precipitator
Power plant/factory emissions passed through device with a negative charge electrode, giving particles a negative charge
Negative charged particles stick to positive charged collection plates, trapping them
Plates discharged occasionally so particles fall down into collection hopper for disposal in landfills
Baghouse Filter (PM)
Large fabric bag filters that trap PM as air from combustion/industrial process passes through
Shaker device knocks trapped particles loose into collection hopper below
7.7 Acid Rain
Sources of NOx and SO2
NOx and SO2 are the primary pollutants that cause most acid precipitation
Major Sources
SO2 – coal fired power plants, metal factories, vehicles that burn diesel fuel
NOx – vehicle emissions, diesel generators, coal power plants
Limiting Acid Rain
Reducing NOx and SO2 emissions reduces acid deposition
Higher CAFE standards
More public transit
Renewable energy sources
More efficient electricity use
Since passage of Clean Air Act, acid deposition has decreased significantly
NOx and SO2 react with O2 and H2O in the atmosphere, forming nitric and sulfuric acid
Sulfuric acid and nitric acid dissociate in the presence of water into sulfate and nitrate ions, and hydrogen ions (H+)
Acidic rain water (higher H+ concentration) decreases soil and water pH; can limit tree growth in forests down wind from major SO2 and NOx sources
Environmental Effects of Acid Rain
Acidity= higher H+ ion concentration, lower pH
Soil/water acidification
H+ ions displace or leech other positive charged nutrients (Ca2+, K+) from soil
H+ ions also make toxic metals like aluminum and mercury more soluble in soil and water
pH Tolerance
as pH decreases (more acidic) outside optimal range for a species, population declines
when pH leaves range of tolerance, they cannot survive at all due to aluminum toxicity and disrupted blood osmolarity
indicator species can be surveyed and used to determine conditions of an ecosystem
Mitigating Acid Rain
Limestone (calcium carbonate) is a natural base that can neutralize acidic soil/water
Limestone
Calcium carbonate (CaCO3) reacts with H+ ions, forming HCO3 and giving off Ca2+
This “neutralizes” acidic water/soil, moving it closer to a pH of 7
Regions with limestone bedrock have some natural buffering of acid rain
Humans can also add crushed limestone to soils/waters to neutralize
Acid rain can corrode human structures, especially those made from limestone
Limiting SOx and NOx
Decreasing these primary pollutants that drive acid rain can reduce it
Renewable energy sources, decreasing coal comb.
Fluidized bed combustion and lower burning temperature for existing coal power plants
Dry or wet scrubbers
7.8 Noise Pollution
Urban Noise Pollution
Any noise at great enough volume to cause physiological stress (difficulty communicating, headaches, confusion) or hearing loss
Construction: jack hammers, trucks, concrete pouring
Transportation: cars, busses, trains
Industrial activity: manufacturing plants
Domestic activity: neighbor’s music, lawn mowing, home projects
Wildlife Effects (land)
Noise pollution can disrupt animal communication, migration, and damage hearing
Physiological stress: caterpillar hearts beat faster when exposed to simulated highway noise pollution
Hearing: can prevent predators from hearing prey and vice versa; can prevent mates from locating each other (both decrease chances of survival)
Wildlife Effects (aquatic)
Aquatic noise pollution comes from the noise of ship engines, military sonar, and seismic air blasts from oil and gas surveying ships
Physiological stress: hearing loss, disrupted communication, mating calls, predator and prey navigation
whales are especially prone to having migration routes disrupted as their vocal communication is disrupted
Seismic surveying: ships send huge air blasts down into the water, searching for oil by recording how the echo is returned from ocean floor
So loud that researchers off the coast of Virginia can detect blasts from coast of Brazil