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United States Department of Agriculture Natural Conservation Service What is an Airshed?

Airshed Assessment: – Not a building! Topography, and – Not a teenager! Climatology Impacts on Air Quality – Different from a watershed – Bigger than a breadbox

Airsheds Airsheds

“An airshed is a part of the atmosphere that • Scale is important! behaves in a coherent way with respect to – For some issues, very local airshed (odors) the dispersion of emissions. It typically – For some issues, regional airshed (ozone) forms an analytical or management unit. – For some issues, global concern (GHGs) Also: A geographic boundary for air • Think about all of these scales when analyzing quality standards.” potential impacts

Topography-Air Quality Relationships • Topographic Scale: Airshed Control • Microclimatic effects • Valleys: Colder at night (and sometimes even in day in winter); More inversions • Orientation important w.r.t sun, large scale flow, etc. • Winds: Up valley during day; Down valley during night

1 Topographic Analysis

• Examine local to regional topography: – Valleys – Ridges – Slope and Aspect and Scale – Sub-airsheds within larger airsheds – Analogies to watersheds • Example websites: – www.topozone.com or terraserver-usa.com – Google maps

Landscape/Land Use Air Quality, Meteorology Characteristics and Air Quality and Climatology Relationships

• Contribute to microclimatic differences: changes in the BIG 5 (weather factors), w/ consequent AQ impacts • : Vegetated, non, type, • Landuse: agricultural, urban, industrial • Types of agriculture: livestock, crops, forestry • Urban heat islands vs. rural: Night, Winter A key part of an Airshed Assessment!

Basic AQ Meteorology Weather & Climate & AQAC (and Climatology) • Huge factors in air quality and atmospheric change • Meteorological Factors (the BIG 5) – Temperature • Weather: Meteorological conditions as – Solar radiation they happen (Air Quality right now) – Wind (speed and direction) • Climate: Time integration (Typical and – Precipitation extreme air quality—statistics) – Atmospheric moisture content (humidity)

2 Temperature-AQ Relationships Vertical Temperature Profile

• Very important for AQ! Issue of Stability •O3: More in warmer temperatures (for given VOC • Typically, temperature decreases with height and NO values) • Change of temperature w/ height = “Lapse Rate” x (typical rate about 5.5F / 1000 feet) • VOCs: More pesticide (and • Strong surface heating (summer) or “adiabatic other VOC) volatilization in warming” (Chinooks) = Large positive lapse rate warmer temperatures (can be unstable) •NH: Generally more formed in • Strong surface cooling relative to above can lead to 3 inversions (very stable; almost always high pressure) warmer temperatures

Inversions

• Vertical temperature profile is altered: at some (lower) level temperatures increase with height • Result in stagnant conditions—little vertical mixing • Common in colder months, and in valleys • Associated with high pressure and light winds, though not always

Inversion Case: Donora PA, October 1948

Noon, Halloween, 1948

Morning “sounding,” Salem, OR, June 12, 2008. Note the very low level inversion Principal Pollutants: Fluoride, SO2, CO, Coal Smoke, (right white line). What is the approx. level of the top of this inversion? Is there a Zinc Smelter Dust second inversion? 20 killed; Hundreds Seriously Injured; 7,000 of 14,000 residents sick

3 See: http://www.airfire.org/vcis/ Solar Radiation

• Drives all earth processes, incl. weather/climate

• Directly related to O3 formation • May enhance other chemical reactions – Provides the for the reaction

Average mixing heights in July, evening

Wind Wind

• Higher wind speeds typically associated with • Winds generally stronger aloft than at the greater mixing (good) and transport of surface pollutants, incl. smoke and pesticides (bad) • Valleys are often the calmest locations • High winds: Wind erosion (dust), fire spread • Winds typically follow terrain orientation • Very calm conditions not best for chemical • Air is a fluid—it follows those principles application • Direction important! --Especially for odors, PM, chemical drift

Sources of Wind Data

• Tabular, summarized data • Wind maps (like OR Wind Map) • Wind roses: http://www.wcc.nrcs.usda.gov/climate/windrose.html • Winds are always indicated FROM the direction of flow • Wind roses show directional and speed frequencies (usually 16 directions and 5-6 categories of speed)

4 WIND ROSE PLOT WIND ROSE PLOT Station #24232 - SALEM/MCNARY FIELD, OR Station #24232 - SALEM/MCNARY FIELD, OR

NORTH NORTH

30% 15%

24% 12%

18% 9%

12% Wind Rose 6% Wind Rose

6% 3%

WEST EAST January WEST EAST July Salem Salem

SOUTH

SOUTH

MODELER DATE COMPANY NAME Wind Speed (m/s) Sara West 9/5/2002 USDA-ARS MODELER DATE COMPANY NAME Wind Speed (m/s) Sara West 9/5/2002 USDA-ARS > 11.06 DISPLAY UNIT COMMENTS

8.49 - 11.06 Wind Speed m/s > 11.06 DISPLAY UNIT COMMENTS

5.40 - 8.49 AVG. WIND SPEED CALM WINDS 8.49 - 11.06 Wind Speed m/s

3.34 - 5.40 4.27 m/s 17.69% 5.40 - 8.49 AVG. WIND SPEED CALM WINDS

1.80 - 3.34 ORIENTATION PLOT YEAR-DATE-TIME 3.34 - 5.40 3.53 m/s 14.43% Direction 1961 0.51 - 1.80 (blowing from) Jan 1 - Jan 31 1.80 - 3.34 ORIENTATION PLOT YEAR-DATE-TIME Midnight - 11 PM Direction 1961 0.51 - 1.80 (blowing from) Jul 1 - Jul 31 WRPLOT View 3.5 by Lakes Environmental Software - www.lakes-environmental.com Midnight - 11 PM

WRPLOT View 3.5 by Lakes Environmental Software - www.lakes-environmental.com

WIND ROSE PLOT WIND ROSE PLOT Station #24155 - PENDLETON/MUNICIPAL ARPT, OR Station #24155 - PENDLETON/MUNICIPAL ARPT, OR

NORTH NORTH

10% 15%

8% 12%

6% 9%

4% Wind Rose 6% Wind Rose

2% 3% WEST EAST January WEST EAST July Pendleton Pendleton

SOUTH SOUTH

MODELER DATE COMPANY NAME MODELER DATE COMPANY NAME Wind Speed (m/s) Sara West 9/5/2002 USDA-ARS Wind Speed (m/s) Sara West 9/5/2002 USDA-ARS

> 11.06 DISPLAY UNIT COMMENTS > 11.06 DISPLAY UNIT COMMENTS

8.49 - 11.06 Wind Speed m/s 8.49 - 11.06 Wind Speed m/s

5.40 - 8.49 AVG. WIND SPEED CALM WINDS 5.40 - 8.49 AVG. WIND SPEED CALM WINDS

3.34 - 5.40 3.56 m/s 6.80% 3.34 - 5.40 3.81 m/s 2.99%

1.80 - 3.34 ORIENTATION PLOT YEAR-DATE-TIME 1.80 - 3.34 ORIENTATION PLOT YEAR-DATE-TIME Direction 1961 Direction 1961 0.51 - 1.80 (blowing from) Jan 1 - Jan 31 0.51 - 1.80 (blowing from) Jul 1 - Jul 31 Midnight - 11 PM Midnight - 11 PM

WRPLOT View 3.5 by Lakes Environmental Software - www.lakes-environmental.com WRPLOT View 3.5 by Lakes Environmental Software - www.lakes-environmental.com

Precipitation

• Generally aids air quality: Scavenging –Lowers O3, PM, Odors • Wet deposition •Acid • Topography can enhance precipitation

5 Example of Integrating Weather Factors (Wind, Temp., Moisture Content Humidity) into Risk of Spray Drift, by Month for Eugene

• Generally reported as relative humidity or dewpoint • Can impact chemical reactions • Not necessarily a harbinger of precipitation • Drier air increases volatilization (spray in moderate to higher humidities)

Other AQ-Weather Considerations

•Air Mass – Origin, Constituency, Movement • Time of year In Review… • Time of day • System of Influence – Location relative to high and low pressure • Subsidence and calmer winds under highs • Pressure gradient (difference) controls wind speed • Regional to Local Effects (Valleys, Ridges, Water bodies, etc.)

Air Quality Psychology Integrating Meteorology, Climatology, Topography and Landscape Information • Ask this about your atmosphere: into a Local Air Quality Assessment –Are you unstable? • Consider the location and the surroundings –Are you hot (angry)? • Airshed Assessment: –Are you turbulent? – Topographic influences – Do you feel like you are going to blow? – Local to regional landscape and use – Scale of airsheds w.r.t. AQ issues – Meteorological factors – Air Quality Climatology

It is important to keep these in mind as you do an on-farm AQAC assessment, and develop a conservation plan

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