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Wildfire Smoke Trends and the Air Quality Index By: Anthony Barnack September 2020 This report prepared by: Oregon Department of Environmental Quality 700 NE Multnomah Street, Suite 600 Portland, OR 97232 1-800-452-4011 www.oregon.gov/deq Contact: Anthony Barnack 503-693-5708 Laboratory and Environmental Assessment Division 7202 NE Evergreen Pkwy, Suite 150 Hillsboro, OR 97006 Phone: 503-693-5708 800-452-4011 Contact: Anthony Barnack www.oregon.gov/DEQ DEQ is a leader in restoring, maintaining and enhancing the quality of Oregon’s air, land and water.

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Page 1: Wildfire Smoke Trends and the Air Quality Index · 2020. 10. 1. · 6. Trends DEQ compiled the wildfire AQI trends for “Unhealthy for Sensitive Groups,” “Unhealthy,” “Very

Wildfire Smoke Trends and the Air Quality Index By: Anthony Barnack September 2020

This report prepared by:

Oregon Department of Environmental Quality

700 NE Multnomah Street, Suite 600

Portland, OR 97232

1-800-452-4011

www.oregon.gov/deq

Contact:

Anthony Barnack

503-693-5708

Laboratory and Environmental Assessment Division 7202 NE Evergreen Pkwy,

Suite 150

Hillsboro, OR 97006 Phone: 503-693-5708

800-452-4011

Contact: Anthony Barnack

www.oregon.gov/DEQ

DEQ is a leader in

restoring, maintaining and

enhancing the quality of

Oregon’s air, land and

water.

Page 2: Wildfire Smoke Trends and the Air Quality Index · 2020. 10. 1. · 6. Trends DEQ compiled the wildfire AQI trends for “Unhealthy for Sensitive Groups,” “Unhealthy,” “Very

This report prepared by:

Oregon Department of Environmental Quality

700 NE Multnomah Street, Suite 600

Portland, OR 97232

1-800-452-4011

www.oregon.gov/deq

Contact:

Anthony Barnack

503-693-5708

DEQ can provide documents in an alternate format or in a language other than English upon request. Call DEQ at 800-

452-4011 or email [email protected].

Page 3: Wildfire Smoke Trends and the Air Quality Index · 2020. 10. 1. · 6. Trends DEQ compiled the wildfire AQI trends for “Unhealthy for Sensitive Groups,” “Unhealthy,” “Very

i

Table of Contents

Glossary .......................................................................................................................................................... i Executive Summary ...................................................................................................................................... 1 1. Introduction ........................................................................................................................................... 1 2. Scope of This Report ............................................................................................................................. 2 3. Wildfire Smoke Impacts ........................................................................................................................ 2 4. Air Quality Index .................................................................................................................................. 2 5. Calculating AQI Trends ........................................................................................................................ 2 6. Trends .................................................................................................................................................... 3 7. Discussion ............................................................................................................................................. 6 8. Conclusion ........................................................................................................................................... 10

Figure 1. Acreage burned by Wildfire in areas impacting Oregon. .............................................................. 1 Figure 2. Map of wildfire health trends across Oregon. ................................................................................ 5 Figure 3. Bend ≥ USG AQI wildfire smoke trends. ...................................................................................... 8 Figure 4. Klamath Falls ≥ USG AQI wildfire smoke trends. ........................................................................ 8 Figure 5. Medford ≥ USG AQI wildfire smoke trends. ................................................................................ 9 Figure 6. Portland ≥ USG AQI wildfire smoke trends. ................................................................................. 9 Figure 7. Albany wildfire ≥ USG AQI wildfire smoke trends. ................................................................... 11 Figure 8. Baker City wildfire ≥ USG AQI wildfire smoke trends. ............................................................. 12 Figure 9. Burns/Hines wildfire ≥ USG AQI wildfire smoke trends. ........................................................... 12 Figure 10. Cave Junction wildfire ≥ USG AQI wildfire smoke trends. ...................................................... 13 Figure 11. Corvallis wildfire ≥ USG AQI wildfire smoke trends. .............................................................. 13 Figure 12. Cottage Grove wildfire ≥ USG AQI wildfire smoke trends. ..................................................... 14 Figure 13. Enterprise wildfire ≥ USG AQI wildfire smoke trends. ............................................................ 14 Figure 14. Eugene/Springfield wildfire ≥ USG AQI wildfire smoke trends. .............................................. 15 Figure 15. Grants Pass wildfire ≥ USG AQI wildfire smoke trends. .......................................................... 15 Figure 16. John Day wildfire ≥ USG AQI wildfire smoke trends. .............................................................. 16 Figure 17. Lakeview wildfire ≥ USG AQI wildfire smoke trends. ............................................................. 16 Figure 18. La Grande wildfire ≥ USG AQI wildfire smoke trends. ............................................................ 17 Figure 19. Oakridge wildfire ≥ USG AQI wildfire smoke trends. .............................................................. 17 Figure 20. Pendleton wildfire ≥ USG AQI wildfire smoke trends. ............................................................. 18 Figure 21. Prineville wildfire ≥ USG AQI wildfire smoke trends. ............................................................. 18 Figure 22. Roseburg wildfire ≥ USG AQI wildfire smoke trends............................................................... 19 Figure 23. Salem wildfire ≥ USG AQI wildfire smoke trends. ................................................................... 19 Figure 24. Sisters wildfire ≥ USG AQI wildfire smoke trends. .................................................................. 20 Figure 25. Sweet Home wildfire ≥ USG AQI wildfire smoke trends. ........................................................ 20 Figure 26. The Dalles wildfire ≥ USG AQI wildfire smoke trends. ........................................................... 21

Table 1. The PM2.5 Air Quality Index, breakpoints, and health effects. ...................................................... 3 Table 2. Number of USG or worse days from Wildfire Smoke Impacts. ..................................................... 7

Glossary AQI – Air Quality Index, EPA Air Quality health scale.

PM2.5 – Particulate matter 2.5 microns in diameter or smaller

PM10 - Particulate matter 10 microns in diameter or smaller

≥USG – Unhealthy for Sensitive Groups, Unhealthy, Very Unhealthy, and Hazardous AQI

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Executive Summary Large wildfires have been increasing across the western United States in the last decade and are expected

to become more frequent, according to the National Interagency Fire Center. Across Oregon, smoke from

fires is causing Air Quality Index values that are unhealthy for sensitive groups or worse, or ≥USG, for

short. For example, until 2015, Portland had not had a single day with air quality that was ≥USG from

wildfire smoke since air quality monitoring began in 1985. From 2015 to 2019, Portland had three out of

five years with wildfire smoke impacts causing air quality to be ≥USG. In 2018, Klamath Falls and

Medford had five weeks where air quality was ≥USG. This was the most days with wildfire smoke impact

since monitoring began in the 1980s. Bend had three weeks of air quality that was ≥USG in 2017 and one

week in 2018. Before 2017, Bend had not had over three days of ≥USG in any year. If these trends

continue, Oregon should expect to see an increase in ≥USG during a given summer and more summers with

impacts. In other words, summers with little or no wildfire smoke, like 2016 and 2019, will be much less

commonplace.

1. Introduction Oregon and surrounding states have temperate rainforests west of the Cascade Mountains and more arid

ponderosa pine forests east of the Cascades. Fire is a natural part of the ecology of these forests and

occasional burning is healthy for forests. However, fires in these forests have become more massive and

burn more acres, according to the National Interagency Fire Center. Figure 1 shows the increasing

wildfire trends over the last decade for areas in the western United States and Canada where smoke

impacts Oregon. The fire season is longer and fires are larger than in the past.

Data provided by the National Interagency Fire Center and Washington DOE

Figure 1. Acreage burned by wildfire in areas impacting the Pacific Northwest.

0

1

2

3

4

5

6

7

8

2009 2010 2011 2012 2013 2014 2015 2016 2017 2018 2019

Mil

lio

ns o

f acre

s b

urn

ed

Acres Burned by Wildfire by State and Province

Includes Oregon, Washington, Idaho, British Columbia, and California

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2. Scope of This Report This report is limited to the presentation of the AQI health trends for PM2.5. The report can be used as a

reference for more in depth discussion of wildfire smoke causes and impacts.

3. Wildfire Smoke Impacts Oregon’s wildfire season used to start in late July and run into early September. More recently, there have

been fires starting in mid-July and lasting until early October. Fires impacting Oregon have been mainly

in the Southern, Central and Northeastern Oregon and Northern California mountains. Some recent

impacts have come from British Columbia and Central Washington.

Wildfire smoke emits a wide variety of pollutants measured as particulate matter (PM2.5 and PM10),

black carbon, nitrogen dioxide, carbon monoxide, volatile organic compounds, polycyclic aromatic

hydrocarbons and metals. According to the Oregon Health Authority’s publication, Wildfire Smoke and

Your Health, of these pollutants, PM2.5 may represent the greatest health concern since it can be inhaled

deeply into the lungs and a fraction may even reach the bloodstream. Volatile organic compounds can

cause early symptoms such as watery eyes, respiratory tract irritation and headaches. Higher levels of

ozone (smog) can also be formed from an increase in the precursor pollutants: nitrogen dioxide and

volatile organic compounds.

4. Air Quality Index PM2.5 is a criteria pollutant that is easily measured and has well established National Ambient Air

Quality Standards. The U.S. EPA created the color-coded Air Quality Index, or AQI, which is used to

convert pollutant concentrations into more useful health risk language. The AQI uses PM2.5, ozone,

PM10, nitrogen dioxide, carbon monoxide and sulfur dioxide data to calculate health indices. In Oregon,

PM2.5 and ozone measurements typically have the highest AQI and are considered the drivers of

associated health risks. In the summer, the ozone AQI in urban areas is usually higher than the PM2.5

unless there is wildfire smoke.

5. Calculating AQI Trends The AQI is useful for calculating wildfire trends because it includes health risk in its value. These AQI

trends are calculated using PM2.5 measurements because PM2.5 has the highest AQI levels of any of the

pollutants during wildfire smoke intrusions.

DEQ and the Lane Regional Air Protection Agency measure PM2.5 using Federal Reference Method

filter samplers. Air passes through a filter for 24 hours starting at midnight and samples are collected

daily or every three or six days depending on the location. The filter samplers are colocated with

nephelometers that measure continuous, real-time light scattering due to particulate matter. DEQ uses

linear regression to compare the light scattering from the nephelometer and the PM2.5 from the filter

samplers to get a correlation between the two methods. The correlation equation is used to convert the

nephelometer’s light scattering into a real-time PM2.5 estimate. The 24-hour PM2.5 average is used to

calculate the daily AQI presented in this report.

PM2.5 estimate calculations

To calculate the AQI, the PM2.5 filter data is used when available. When there is no filter data, the

nephelometer derived PM2.5 estimates are used. Most days and locations do not have filter data so the

PM2.5 estimates consist of over half of the values.

For this trend report, DEQ used the 2013 to 2015 PM2.5 Federal Reference Method/nephelometer

correlation equations to recalculate the nephelometer light scattering values. The PM2.5 estimates were

updated using a more recent correlation equation to eliminate variations from changing correlations over

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the years. Note that correlation equations changed very little, but a small change can be significant if the

PM2.5 estimate is near an AQI break point.

AQI calculations

The AQI was also updated using the most recent AQI breakpoints. The AQI breakpoints changed when

EPA updated the PM2.5 standards. In order to compare apples to apples, all the data has to be

recalculated using the same AQI breakpoints. The most recent breakpoints are based on the most current

health information. The current EPA breakpoints are in Table 6 of the EPA’s Technical Assistance

Document for the Reporting of Daily Air Quality – the Air Quality Index (AQI), May 2016. The

AQI calculation is Equation 1 in the document. The AQI categories and breakpoints are shown in Table 1

below.

Table 1. The PM2.5 Air Quality Index, breakpoints, and health effects.

AQI

Category

and Color

AQI

value

PM2.5

(µg/m3)

24-hr Aver. Air Quality and Health

Good

0

to

50

0.0

to

12.0

Air quality is satisfactory. Air pollution poses little or no health

risk.

Moderate

51

to

100

12.1

to

35.4

Air quality is acceptable; however, there may be a moderate health

concern for a very small number of people. Respiratory symptoms

are possible in people unusually sensitive to air pollution. Heart or

lung disease (such as asthma) symptoms may be aggravated in

people with cardiopulmonary disease and older adults. These

groups should consider reducing prolonged or heavy outdoor

exertion.

Unhealthy

for

Sensitive

Groups

101

to

150

35.5

to

55.4

Members of sensitive groups may experience health effects.

People with heart or lung disease may experience increased

symptoms and premature mortality; older adults, pregnant women

and children, are also among the groups most at risk of respiratory

symptoms. These groups should reduce prolonged or heavy

outdoor exertion. The general public is not likely to be affected.

Unhealthy

151

to

200

55.5

to

150.4

Everyone may begin to experience health effects; members of

sensitive groups may experience more serious health effects.

These groups should avoid prolonged or heavy exertion: People

with heart or lung disease, children, pregnant women and older

adults. Everyone else should reduce prolonged or heavy exertion.

Very

Unhealthy

201

to

300

150.5 to

250.4

Health alert: everyone may experience more serious health effects.

These groups should avoid all physical activity outdoors: People

with heart or lung disease, children, pregnant women and older

adults. Everyone else should avoid prolonged or heavy exertion.

Hazardous >300 >250.5

Health warnings of emergency conditions. The entire population is

more likely to be affected. See EPA AIRNow “Extremely High

Levels of PM2.5: Steps to Reduce Your Exposure” when PM2.5

levels are “Hazardous” or above on the AQI.

6. Trends DEQ compiled the wildfire AQI trends for “Unhealthy for Sensitive Groups,” “Unhealthy,” “Very

Unhealthy” or “Hazardous.” Collectively these categories are known as unhealthy for sensitive groups or

worse, or ≥USG for short. In Oregon, wildfire smoke occurs during the summer, so for this report values

from June 1 to Sept. 30 were selected. July 4 was removed from the trends because of fireworks. DEQ

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evaluated summertime AQI trends up to 2019 for 24 communities in Oregon. A map of wildfire related

AQI trends for various cities around the state is shown in Figure 2. The charts on the map show the ≥USG

for each city divided into blocks of five year totals. For example, the sum of ≥ USG from 1985 to 1989,

from 1990 to 1994, etc.

To simplify the discussion in this report, only four of the cities from across the state are provided in the

main body. They are Bend, Klamath Falls, Medford and Portland. The trends for the number of days

≥USG for these cities are provided in Figures 3 through 6 and in Table 2. The graphs for the remaining

cities are shown in the appendix.

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Air Quality Division

Figure 2. Map of wildfire AQI trends across Oregon.

The charts’ vertical axis are the number of days per year that have an AQI of ≥USG (Unhealthy for Sensitive Groups or worse). ND = No data collected for

these years. The charts’ horizontal axis are the five year total of the <USG for each block. The increments are shown in the key on the graph.

‘85 90 95 00 05 10 15

‘85 90 95 00 05 10 15

‘85 90 95 00 05 10 15

‘85 90 95 00 05 10 15

‘85 90 95 00 05 10 15

‘85 90 95 00 05 10 15

‘85 90 95 00 05 10 15

‘85 90 95 00 05 10 15

ND

‘85 90 95 00 05 10 15

‘85 90 95 00 05 10 15

ND

ND

ND

ND

Roseburg

Medford

Eugene

Salem

Portland

The Dalles

Bend

Klamath Falls

La Grande

Baker City

Burns

Lakeview

ND

ND ND

‘85 90 95 00 05 10 15

‘85 90 95 00 05 10 15

Axis Key:

Sum of >USG for

the five year block

‘85 = 1985 to 1989

‘90 = 1990 to 1994

‘95 = 1995 to 1999

‘00 = 2000 to 2004

‘05 = 2005 to 2009

‘10 = 2010 to 2014

‘15 = 2015 to 2019

AQI days ≥USG caused by wildfire smoke in five year totals

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Air Quality Division

7. Discussion Wildfire smoke impacts are increasing across the state. There are more ≥USG days per year

and more years with at least one ≥USG. The most significant impacts from fires are in

Southern Oregon. Eastern Oregon also experiences more ≥USG than in the past. Portland

did not experience smoke impacts at all from 1985 until 2015, and then three out of the next

five years had smoke impacts.

Based on the AQI, associated health impact levels are also increasing. There are more

“unhealthy,” “very unhealthy” and “hazardous” days than in the past.

Between 1987 and 2014, Bend had five unhealthy days. Between 2015 to 2019, Bend has

had 13 unhealthy days. In 2017, Bend had three “very unhealthy” days for the first time

since monitoring started in 1987.

Klamath Falls had 22 “unhealthy” days before 2015 and had 35 “unhealthy” days

between 2015 and 2019. Klamath Falls had two “very unhealthy” days before 2015 and

four between 2015 and 2019.

Medford had 18 “unhealthy” days between 1985 and 2014 and had 41 between 2015 and

2019. Medford had nine “very unhealthy” days between 1985 and 2014, mostly in 1987.

From 2015 to 2019, Medford had 10. Medford had one “hazardous” day in 1987 and did

not have another one until 2017.

Portland had no “unhealthy” days between 1985 and 2014 and had five from 2015 to

2019.

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Air Quality Division

Table 2. Number of USG or worse days from Wildfire Smoke Impacts.

a. Errata: Earlier data released for Portland showed one unhealthy for sensitive groups

day in 1985 and one in 1990 but these were subsequently changed to zero because they

were determined to be from field burning.

b. Data does not include July 4 Fireworks.

c. “-“ = no data collected

d. Federal Reference Method data and correlated nephelometer light scattering data used

US

G

Un

healt

hy

Very

Un

healt

hy

Su

m

% D

ata

Co

mp

lete

ness

US

G

Un

healt

hy

Very

Un

healt

hy

Su

m

% D

ata

Co

mp

lete

ness

US

G

Un

healt

hy

Very

Un

healt

hy

Hazard

ou

s

Su

m

% D

ata

Co

mp

lete

ness

US

G

Un

healt

hy

Su

m

% D

ata

Co

mp

lete

ness

1985 - - - - - - - - - - 93% 98%

1986 - - - - - - - - - - 99% 50%

1987 - - - - - - - - - - 3 8 7 1 19 99% 100%

1988 - - - - - - - - - - 99% 95%

1989 - - - - - 93% 100% 98%

1990 2 2 95% 100% 97% 98%

1991 98% - 97% 100%

1992 100% - - - - - 1 1 100% 99%

1993 90% - - - - - 97% 97%

1994 97% - - - - - 97% 100%

1995 98% - - - - - 97% 97%

1996 1 1 84% - 89% 60%

1997 97% - - - - - 93% 70%

1998 100% - - - - - 97% 98%

1999 97% 80% 88% 100%

2000 100% 100% 100% 98%

2001 100% 100% 100% 100%

2002 94% 9 13 2 24 100% 8 4 12 100% 100%

2003 100% 100% 1 100% 100%

2004 100% 100% 98% 100%

2005 100% 100% 100% 97%

2006 98% 98% 100% 98%

2007 100% 99% 100% 99%

2008 100% 1 1 100% 7 7 100% 98%

2009 1 1 91% 1 2 3 98% 1 1 2 96% 100%

2010 99% 97% 100% 100%

2011 99% 100% 98% 100%

2012 2 2 4 99% 1 3 4 100% 100% 100%

2013 100% 1 4 5 98% 1 4 2 7 98% 99%

2014 1 1 100% 1 1 100% 100% 100%

2015 1 1 2 100% 7 2 9 100% 6 7 13 100% 2 2 100%

2016 99% 100% 100% 100%

2017 4 8 3 15 94% 7 8 1 16 100% 6 9 4 1 20 100% 4 2 6 98%

2018 4 4 8 100% 10 25 3 38 99% 8 22 3 33 100% 5 1 6 100%

2019 94% 100% 3 3 6 100% 100%

Bend Klamath Falls Medford Portland

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Air Quality Division

Figure 3. Bend ≥ USG AQI wildfire smoke trends.

Figure 4. Klamath Falls ≥ USG AQI wildfire smoke trends. Notes: No data was collected during the summer from 1991 through 1995, 1997, and 1998.

12

1

4 42

1

2

8

4

3

0

2

4

6

8

10

12

14

16

198

9

1990

199

1

199

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0

200

1

200

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9

2010

201

1

201

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201

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201

5

201

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201

7

201

8

201

9

Num

ber

of D

ays

Bend Wildfire Smoke by AQI Category

USG Unhealthy Very Unhealthy

15

8

2

4

9

1 1

7 7

10

13

23 4

2

8

252

1

3

0

5

10

15

20

25

30

35

40

198

9

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0

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0

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9

Num

ber

of D

ays

Klamath Falls Wildfire Smokeby AQI Category

USG Unhealthy Very Unhealthy

24

9

16

38

34

5

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Air Quality Division

Figure 5. Medford ≥ USG AQI wildfire smoke trends.

Figure 6. Portland ≥ USG AQI wildfire smoke trends.

Note: Not included: There were four USG days in Portland in mid to late September, two in 1985, one in 1987,

and one in 1990. These were likely from field burning and are not shown here.

3

8

1

7

6 68

3

8

1

4

4

79

22

3

7

2

4

3

11

0

5

10

15

20

25

30

35

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5

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1

200

2

2003

200

4

200

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200

6

200

7

200

8

200

9

201

0

201

1

201

2

201

3

201

4

201

5

201

6

201

7

201

8

201

9

Num

ber

of D

ays

Medford Wildfire Smoke by AQI Category

USG Unhealthy Very Unhealthy Hazardous

19

12

2

7

13

20

33

6

4

5

2

2

1

0

1

2

3

4

5

6

7

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5

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201

3

201

4

201

5

201

6

201

7

201

8

201

9

Num

ber

of D

ays

Portland Wildfires Smokeby AQI Category

USG Unhealthy Very Unhealthy Hazardous

6 6

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Air Quality Division

8. Conclusion This report is intended to show the AQI trends from wildfire smoke impacts. The data shows that

AQI categories from wildfire smoke have been increasing starting around 2012 and there have been much

more frequent days at a more “unhealthy” level. If these trends continue, Oregon should expect to see an

increasing number of ≥USG during the summer, and not just in Southern Oregon but also across the state.

Learn More

EPA’s Wildland Fire Publications, Fact Sheets and Other Resources

AQI – A Guide to Air Quality and Your Health

Track current air quality on DEQ’s online Air Quality Index or the free smart phone app.

During wildfire season, you can also track air quality on the Oregon Smoke Blog.

Wildfire Smoke and Your Health, Public Health Division, Oregon Health Authority.

Alternative Formats DEQ can provide documents in an alternate format or in a language other than English upon request.

Call DEQ at 800-452-4011 or email [email protected].

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Air Quality Division

Appendix Wildfire Trends for Individual Communities The graphs below show the number of days with an AQI ≥USG for 20 communities with monitoring data.

The horizontal axis (or date) varies for each chart depending on when monitoring was started.

Figure 7. Albany wildfire ≥ USG AQI wildfire smoke trends.

1

3

3

2

3

0

1

2

3

4

5

6

7

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5

201

6

201

7

201

8

201

9

Num

ber

of D

ays

Albany Wildfire Smoke by AQI Category

USG Unhealthy

6

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Air Quality Division

Figure 8. Baker City wildfire ≥ USG AQI wildfire smoke trends.

Figure 9. Burns wildfire ≥ USG AQI wildfire smoke trends.

2 2

8

3

1

2

3

1

0

2

4

6

8

10

12

200

0

200

1

200

2

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200

7

200

8

200

9

201

0

201

1

201

2

201

3

201

4

201

5

201

6

201

7

201

8

201

9

Num

ber

of D

ays

Baker City Wildfire Smoke by AQI Category

USG Unhealthy

2

6

10

3

1

3

2

3

21

2 2

2

0

1

2

3

4

5

6

200

0

200

1

200

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3

200

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200

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200

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200

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200

8

200

9

201

0

201

1

201

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201

3

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4

201

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201

6

201

7

201

8

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9

Num

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ays

Burns Wildfire Smoke by AQI Category

USG Unhealthy

5 5

4

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13

Air Quality Division

Figure 10. Cave Junction wildfire ≥ USG AQI wildfire smoke trends.

Figure 11. Corvallis wildfire ≥ USG AQI wildfire smoke trends.

51 4

1 24

14

3

9

1 7

1

10

15

1

1

1

1

0

5

10

15

20

25

30

35

200

0

200

1

200

2

200

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200

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200

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200

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200

8

200

9

201

0

2011

2012

201

3

201

4

201

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201

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8

201

9

Num

ber

of D

ays

Cave Junction Wildfire Smoke by AQI Category

USG Unhealthy Very Unhealthy Hazardous

15

29

10

5

3

15

1

1

2 2

1

0

1

2

3

199

9

200

0

200

1

200

2

200

3

200

4

200

5

200

6

200

7

200

8

200

9

201

0

201

1

201

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201

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201

4

201

5

201

6

201

7

201

8

201

9

Num

ber

of D

ays

Corvallis Wildfire Smoke by AQI Category

USG Unhealthy

2

Page 17: Wildfire Smoke Trends and the Air Quality Index · 2020. 10. 1. · 6. Trends DEQ compiled the wildfire AQI trends for “Unhealthy for Sensitive Groups,” “Unhealthy,” “Very

14

Air Quality Division

Figure 12. Cottage Grove wildfire ≥ USG AQI wildfire smoke trends.

Figure 13. Enterprise wildfire ≥ USG AQI wildfire smoke trends.

2

1

31

1

7

0

2

4

6

8

10

12

2008

200

9

201

0

201

1

201

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201

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201

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201

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201

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201

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201

8

201

9

Num

ber

of D

ays

Cottage Grove Wildfire Smoke by AQI Category

USG Unhealthy

2

10

1

2

1

2

3

6

2

1

5

3

0

1

2

3

4

5

6

7

8

9

10

200

0

200

1

200

2

200

3

200

4

200

5

200

6

200

7

200

8

200

9

201

0

201

1

201

2

201

3

201

4

201

5

201

6

201

7

201

8

201

9

Num

ber

of D

ays

Enterprise Wildfire Smoke by AQI Category

USG Unhealthy

8

9

Page 18: Wildfire Smoke Trends and the Air Quality Index · 2020. 10. 1. · 6. Trends DEQ compiled the wildfire AQI trends for “Unhealthy for Sensitive Groups,” “Unhealthy,” “Very

15

Air Quality Division

Figure 14. Eugene/Springfield wildfire ≥ USG AQI wildfire smoke trends.

1985 and 1987 was likely field burning.

Figure 15. Grants Pass wildfire ≥ USG AQI wildfire smoke trends.

1

2 2

7

1

4

3

0

2

4

6

8

10

12

14

16

198

5

198

6

198

7

198

8

198

9

199

0

199

1

199

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199

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199

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199

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199

8

199

9

200

0

200

1

200

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3

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200

5

200

6

200

7

200

8

200

9

201

0

201

1

201

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4

201

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201

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201

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201

8

201

9

Num

ber

of D

ays

Eugene/Springfield Wildfire Smoke by AQI Category

USG Unhealthy Very Unhealthy Hazardous

14

1

2

1

12 2

9

31

6

1

9

13

2

2

4

1

1

0

5

10

15

20

25

200

0

200

1

200

2

200

3

200

4

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5

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6

200

7

200

8

200

9

201

0

201

1

201

2

201

3

201

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201

5

201

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201

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201

8

201

9

Num

ber o

f Day

s

Grants Pass Wildfire Smoke by AQI Category

USG Unhealthy Very Unhealthy Hazardous

10

2

3

16

22

5

Page 19: Wildfire Smoke Trends and the Air Quality Index · 2020. 10. 1. · 6. Trends DEQ compiled the wildfire AQI trends for “Unhealthy for Sensitive Groups,” “Unhealthy,” “Very

16

Air Quality Division

Figure 16. John Day wildfire ≥ USG AQI wildfire smoke trends.

Figure 17. Lakeview wildfire ≥ USG AQI wildfire smoke trends.

21

1

4

5

1

1

1

5

2

2

0

1

2

3

4

5

6

7

8

9

10

200

0

200

3

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200

6

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7

200

8

200

9

201

0

201

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201

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201

9

Num

ber

of D

ays

John Day Wildfire Smoke by AQI Category

USG Unhealthy

3

2

9

3

7

8

3

2

1 3

12

1

9

0

5

10

15

20

25

199

9

200

0

200

1

200

2

200

3

200

4

200

5

200

6

200

7

200

8

200

9

201

0

201

1

201

2

201

3

201

4

201

5

201

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201

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201

9

Num

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of D

ays

Lakeview Wildfire Smoke by AQI Category

USG Unhealthy

21

4

Page 20: Wildfire Smoke Trends and the Air Quality Index · 2020. 10. 1. · 6. Trends DEQ compiled the wildfire AQI trends for “Unhealthy for Sensitive Groups,” “Unhealthy,” “Very

17

Air Quality Division

Figure 18. La Grande wildfire ≥ USG AQI wildfire smoke trends.

Figure 19. Oakridge wildfire ≥ USG AQI wildfire smoke trends.

1 1 12

1

4 4

51

2

3 1

0

1

2

3

4

5

6

7

8

198

9

199

0

199

1

199

2

199

3

199

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199

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199

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199

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199

8

199

9

200

0

200

1

200

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200

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200

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200

8

200

9

201

0

201

1

201

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4

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201

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201

8

201

9

Num

ber

of D

ays

La Grande Wildfire Smoke by AQI Category

USG Unhealthy

6

3

6

7

21

1

7

2

1

1

8

1

2

0

2

4

6

8

10

12

14

16

18

199

7

199

8

199

9

200

0

200

1

200

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201

0

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ays

Oakridge Wildfire Smoke by AQI Category

USG Unhealthy Very Unhealthy

3

2

17

3

Page 21: Wildfire Smoke Trends and the Air Quality Index · 2020. 10. 1. · 6. Trends DEQ compiled the wildfire AQI trends for “Unhealthy for Sensitive Groups,” “Unhealthy,” “Very

18

Air Quality Division

Figure 20. Pendleton wildfire ≥ USG AQI wildfire smoke trends.

Figure 21. Prineville wildfire ≥ USG AQI wildfire smoke trends.

2

7

5

2

2

3

1

1

0

2

4

6

8

10

12

199

9

200

0

200

1

200

2

200

3

200

4

200

5

2006

200

7

200

8

200

9

201

0

201

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201

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201

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201

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201

5

201

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201

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201

8

2019

Num

ber

of D

ays

Pendleton Wildfire Smoke by AQI Category

USG Unhealthy Very Unhealthy Hazardous

4

10

9

13

5

3

2

2

7

2

0

2

4

6

8

10

12

14

200

9

201

0

201

1

201

2

201

3

201

4

201

5

201

6

201

7

201

8

201

9

Num

ber

of D

ays

Prineville Wildfire Smoke by AQI Category

USG Unhealthy

5

12

5

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19

Air Quality Division

Figure 22. Roseburg wildfire ≥ USG AQI wildfire smoke trends.

Figure 23. Salem wildfire ≥ USG AQI wildfire smoke trends.

1 1

42

3

0

1

2

3

4

5

6

7

8

200

6

200

7

200

8

200

9

201

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201

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Num

ber

of D

ays

Roseburg Wildfire Smoke by AQI Category

USG Unhealthy

7

1

2

4

2

0

0.5

1

1.5

2

2.5

3

3.5

4

4.5

199

3

199

4

199

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199

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199

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199

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199

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0

200

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Num

ber

of D

ays

Salem Wildfire Smoke by AQI Category

USG Unhealthy

Page 23: Wildfire Smoke Trends and the Air Quality Index · 2020. 10. 1. · 6. Trends DEQ compiled the wildfire AQI trends for “Unhealthy for Sensitive Groups,” “Unhealthy,” “Very

20

Air Quality Division

Figure 24. Sisters wildfire ≥ USG AQI wildfire smoke trends.

Figure 25. Sweet Home wildfire ≥ USG AQI wildfire smoke trends.

1 32

610

1

14

2

2

8

4

3

0

5

10

15

20

25

30

201

2

201

3

201

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201

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201

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201

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Num

ber

of D

ays

Sisters Wildfire Smoke by AQI Category

USG Unhealthy Very Unhealthy Hazardous

17

27

4

8

4

1

2

5

0

1

2

3

4

5

6

7

8

9

10

200

7

2008

200

9

201

0

201

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201

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201

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201

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ber

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ays

Sweet Home Wildfire Smoke by AQI Category

USG Unhealthy

9

Page 24: Wildfire Smoke Trends and the Air Quality Index · 2020. 10. 1. · 6. Trends DEQ compiled the wildfire AQI trends for “Unhealthy for Sensitive Groups,” “Unhealthy,” “Very

21

Air Quality Division

Figure 26. The Dalles wildfire ≥ USG AQI wildfire smoke trends.

2

6 4

1 2

8

2

1

0

2

4

6

8

10

12

14

16

200

4

200

5

200

6

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201

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201

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201

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201

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201

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Num

ber o

f Day

sThe Dalles Wildfire Smoke

by AQI Category

USG Unhealthy Very Unhealthy Hazardous

6

15

3