June 25–27, 2003 southeastern U.S. wildfire-smoke episode
June 25, 2003 to June 27, 2003
Daily PM2.5 peaked at 46.9 µg/m³ near Chattanooga across
5 covered metros home to 6.0 million people.
Counting the extra PM2.5 above each metro's typical day, this event handed the
average affected resident ≈ 2.9 cigarettes.
Across everyone living in the affected metros, that is the collective equivalent of
≈ 17 million cigarettes.
An awareness illustration of outdoor exposure at 22 µg/m³
per cigarette (Berkeley Earth), counting only the event's ranked days; not a
medical dose.
Why we think this happened
The basis for “Wildfire smoke”
Qualified frozen evidence supports wildfire smoke as the broad root cause and supports grouping the contemporaneous affected events into one time-bounded episode.
EPA monitor flagEPA attached an exceptional-event qualifier to the affected samples. The agency flagged the measurement itself; no separate agency record describes the event.
U.S. EPA Air Quality System and the submitting air monitoring agency · Jun 25, 2003official
EPA AQS carries an agency-submitted request-exclusion qualifier (E, Forest Fire.) on 1 PM2.5 sample in the candidate CBSA on 2003-06-25, identifying wildfire smoke as affecting the sample. A request-exclusion qualifier is an official submitting-agency causal claim, but this endpoint does not establish EPA concurrence.
U.S. EPA Air Quality System and the submitting air monitoring agency · Jun 27, 2003official
EPA AQS carries an agency-submitted request-exclusion qualifier (E, Forest Fire.) on 1 PM2.5 sample in the candidate CBSA on 2003-06-27, identifying wildfire smoke as affecting the sample. A request-exclusion qualifier is an official submitting-agency causal claim, but this endpoint does not establish EPA concurrence.
U.S. EPA Air Quality System and the submitting air monitoring agency · Jun 26, 2003official
EPA AQS carries an agency-submitted request-exclusion qualifier (E, Forest Fire.) on 3 PM2.5 samples in the candidate CBSA on 2003-06-26, identifying wildfire smoke as affecting the samples. A request-exclusion qualifier is an official submitting-agency causal claim, but this endpoint does not establish EPA concurrence.
A cause is more convincing when the record connects three things: something happened,
the air mass moved toward the region, and local instruments responded. Here is how much
of that chain is documented for this event.
EPA AQS carries an agency-submitted request-exclusion qualifier (E, Forest Fire.) on 1 PM2.5 sample in the candidate CBSA on 2003-06-25, identifying wildfire smoke as affecting the sample. A request-exclusion qualifier is an official…
Before, during, and after the episode: nearby pollutant monitors and surface-weather
stations show what changed. This context tests the “Wildfire smoke” explanation; it does
not assign the cause by itself.
Observed context · not attribution
Chattanooga, TN-GA
Monitor comparison window 2003-06-23 to 2003-06-29 · PM2.5 target: Rossville
3 pollutant signals
Fine-particle pulse41.4 µg/m³
9% above nearby days
PM1057.5 µg/m³
No adjacent-day comparison
Pollution fingerprint
Metro-wide median of reporting monitors
PM2.541.4 µg/m³
9% higher than surrounding days
Before19.2 µg/m³ Event41.4 µg/m³ After38 µg/m³
PM1057.5 µg/m³
No adjacent-day comparison
Before— Event57.5 µg/m³ After—
Ozone0.040 ppm
12% lower than surrounding days
Before0.059 ppm Event0.040 ppm After0.043 ppm
Charlotte-Concord-Gastonia, NC-SC
Monitor comparison window 2003-06-22 to 2003-06-30
6 pollutant signals
Fine-particle pulse40.3 µg/m³
59% above nearby days
Air movement1.87 kt
72% higher than surrounding days
PM1052 µg/m³
No adjacent-day comparison
Pollution fingerprint
Metro-wide median of reporting monitors
PM2.540.3 µg/m³
59% higher than surrounding days
Before19.3 µg/m³ Event40.3 µg/m³ After19.6 µg/m³
PM1052 µg/m³
No adjacent-day comparison
Before— Event52 µg/m³ After—
Carbon monoxide0.496 ppm
About the same as surrounding days
Before0.678 ppm Event0.496 ppm After0.461 ppm
Nitrogen dioxide16 ppb
About the same as surrounding days
Before20.4 ppb Event16 ppb After10.3 ppb
Sulfur dioxide4.92 ppb
151% higher than surrounding days
Before1.73 ppb Event4.92 ppb After1.13 ppb
Ozone0.065 ppm
38% higher than surrounding days
Before0.047 ppm Event0.065 ppm After0.034 ppm
Atmospheric conditions
Nearby EPA weather observations
Humidity64.8 °F
About the same as surrounding days
Pressure990 Millibars
About the same as surrounding days
Temperature77.9 °F
About the same as surrounding days
Wind1.87 kt
72% higher than surrounding days
Greensboro-High Point, NC
Monitor comparison window 2003-06-22 to 2003-06-30 · PM2.5 target: Mendenhall School
3 pollutant signals
Fine-particle pulse39.8 µg/m³
76% above nearby days
PM1046 µg/m³
No adjacent-day comparison
Pollution fingerprint
Metro-wide median of reporting monitors
PM2.539.8 µg/m³
76% higher than surrounding days
Before21.3 µg/m³ Event39.8 µg/m³ After22 µg/m³
PM1046 µg/m³
No adjacent-day comparison
Before— Event46 µg/m³ After—
Ozone0.071 ppm
59% higher than surrounding days
Before0.045 ppm Event0.071 ppm After0.032 ppm
Atmospheric conditions
Nearby EPA weather observations
Humidity66.7 %
About the same as surrounding days
Temperature77 °F
About the same as surrounding days
Greenville-Anderson-Mauldin, SC
Monitor comparison window 2003-06-22 to 2003-06-30 · PM2.5 target: TAYLORS
6 pollutant signals
Fine-particle pulse37.2 µg/m³
82% above nearby days
PM1063.5 µg/m³
55% higher than surrounding days
Pollution fingerprint
Metro-wide median of reporting monitors
PM2.537.2 µg/m³
82% higher than surrounding days
Before14.8 µg/m³ Event37.2 µg/m³ After19.2 µg/m³
PM1063.5 µg/m³
55% higher than surrounding days
Before41 µg/m³ Event63.5 µg/m³ After28 µg/m³
Carbon monoxide0.454 ppm
9% higher than surrounding days
Before0.463 ppm Event0.454 ppm After0.350 ppm
Nitrogen dioxide10.2 ppb
About the same as surrounding days
Before15.2 ppb Event10.2 ppb After9 ppb
Sulfur dioxide2.04 ppb
44% higher than surrounding days
Before1.42 ppb Event2.04 ppb After0.917 ppb
Ozone0.056 ppm
29% higher than surrounding days
Before0.043 ppm Event0.056 ppm After0.030 ppm
Winston-Salem, NC
Monitor comparison window 2003-06-22 to 2003-06-30 · PM2.5 target: Lexington water tower
6 pollutant signals
Fine-particle pulse36.9 µg/m³
42% above nearby days
Air movement3.18 kt
16% higher than surrounding days
PM1049.5 µg/m³
57% higher than surrounding days
Pollution fingerprint
Metro-wide median of reporting monitors
PM2.536.9 µg/m³
42% higher than surrounding days
Before17.8 µg/m³ Event36.9 µg/m³ After23.6 µg/m³
PM1049.5 µg/m³
57% higher than surrounding days
Before25 µg/m³ Event49.5 µg/m³ After29 µg/m³
Carbon monoxide0.696 ppm
About the same as surrounding days
Before0.679 ppm Event0.696 ppm After0.535 ppm
Nitrogen dioxide12.7 ppb
About the same as surrounding days
Before21.6 ppb Event12.7 ppb After8.75 ppb
Sulfur dioxide7.58 ppb
5% higher than surrounding days
Before11.6 ppb Event7.58 ppb After3.88 ppb
Ozone0.069 ppm
67% higher than surrounding days
Before0.041 ppm Event0.069 ppm After0.036 ppm
Atmospheric conditions
Nearby EPA weather observations
Humidity65.8 °F
About the same as surrounding days
Temperature77.1 °F
About the same as surrounding days
Wind3.18 kt
16% higher than surrounding days
Source: U.S. EPA AirData daily observations and, where available, nearby ASOS/AWOS
surface observations. Values are descriptive medians over the retained monitor set;
missing measurements remain missing. Transport and source evidence remain separate
layers because this instrument pattern does not assign a cause by itself.
Air-mass reconstruction
Where the air had been
NOAA HYSPLIT traces the air arriving at each metro backward for 72 hours. Multiple
arrival times and heights show whether the broad path is stable—or sensitive to
assumptions about when and where the polluted layer arrived.
Transport context · not source attribution
Air arriving near Charlotte-Concord-Gastonia
Peak-date arrivals · 2003-06-26
Broad historySeveral approach directions
72-hour reach0–750 km
Sensitivity runs12 modeled paths
Near surface · 100 mLower atmosphere · 500 mHigher layer · 1,000 m
Each line begins 72 hours before arrival and points toward the metro. Color represents
arrival height; repeated lines represent 00, 06, 12, and 18 UTC arrival assumptions.
A path can show where the air traveled, but it cannot prove which source added the PM2.5.
Air arriving near Greensboro-High Point
Peak-date arrivals · 2003-06-26
Broad historySeveral approach directions
72-hour reach150–700 km
Sensitivity runs12 modeled paths
Near surface · 100 mLower atmosphere · 500 mHigher layer · 1,000 m
Each line begins 72 hours before arrival and points toward the metro. Color represents
arrival height; repeated lines represent 00, 06, 12, and 18 UTC arrival assumptions.
A path can show where the air traveled, but it cannot prove which source added the PM2.5.
Air arriving near Greenville-Anderson-Mauldin
Peak-date arrivals · 2003-06-26
Broad historySeveral approach directions
72-hour reach150–800 km
Sensitivity runs12 modeled paths
Near surface · 100 mLower atmosphere · 500 mHigher layer · 1,000 m
Each line begins 72 hours before arrival and points toward the metro. Color represents
arrival height; repeated lines represent 00, 06, 12, and 18 UTC arrival assumptions.
A path can show where the air traveled, but it cannot prove which source added the PM2.5.
Air arriving near Winston-Salem
Peak-date arrivals · 2003-06-26
Broad historySeveral approach directions
72-hour reach150–600 km
Sensitivity runs12 modeled paths
Near surface · 100 mLower atmosphere · 500 mHigher layer · 1,000 m
Each line begins 72 hours before arrival and points toward the metro. Color represents
arrival height; repeated lines represent 00, 06, 12, and 18 UTC arrival assumptions.
A path can show where the air traveled, but it cannot prove which source added the PM2.5.
Air arriving near Chattanooga
Peak-date arrivals · 2003-06-26
Broad historyMostly southeast of the metro
72-hour reach350–700 km
Sensitivity runs12 modeled paths
Near surface · 100 mLower atmosphere · 500 mHigher layer · 1,000 m
Each line begins 72 hours before arrival and points toward the metro. Color represents
arrival height; repeated lines represent 00, 06, 12, and 18 UTC arrival assumptions.
A path can show where the air traveled, but it cannot prove which source added the PM2.5.
Measured daily PM2.5 at EPA monitors, as cigarette-equivalents
EPA monitors sit in metro areas, so the colour clusters there. Land between and beyond
them is unmeasured, not clean: this map shows where IAQng has readings, not the extent
of the smoke.
—
Episode peak
--cigarettes
The smoke map's scale, replayed over this event: the surface interpolates between
covered metros' daily records, framed to the affected region. Hover for a reading,
click a metro to pin it to the card. Days a monitor did not report draw nothing.
Select a metro on the map to see nearby cameras. Where an operator archive reaches
the event, drag the divider to compare two moments, adjust either date and time, or
play the available event-day frames. Camera imagery is visual context, not an
air-quality measurement or proof of smoke.
No useful public camera views are currently available within 80 km of this metro.
"Cigarettes, whole event" totals a metro's ranked event days at 22 µg/m³ per
cigarette: what a person outdoors there breathed across the event, as the
illustration. "All-time standing" is where this episode's days sit in each metro's
ranked record (worst-area measure, since 1999). Full local context is on each
metro's Air Records page.
Public evidence library
What supports this account
Each card states what a source supports—and what it does not. Official records, research, reporting, community observations, and transparent inferences remain visibly different kinds of evidence.
U.S. EPA Air Quality System and the submitting air monitoring agency · Jun 25, 2003officialgovernment
EPA AQS carries an agency-submitted request-exclusion qualifier (E, Forest Fire.) on 1 PM2.5 sample in the candidate CBSA on 2003-06-25, identifying wildfire smoke as affecting the sample. A request-exclusion qualifier is an official submitting-agency causal claim, but this endpoint does not establish EPA concurrence.
U.S. EPA Air Quality System and the submitting air monitoring agency · Jun 27, 2003officialgovernment
EPA AQS carries an agency-submitted request-exclusion qualifier (E, Forest Fire.) on 1 PM2.5 sample in the candidate CBSA on 2003-06-27, identifying wildfire smoke as affecting the sample. A request-exclusion qualifier is an official submitting-agency causal claim, but this endpoint does not establish EPA concurrence.
U.S. EPA Air Quality System and the submitting air monitoring agency · Jun 26, 2003officialgovernment
EPA AQS carries an agency-submitted request-exclusion qualifier (E, Forest Fire.) on 3 PM2.5 samples in the candidate CBSA on 2003-06-26, identifying wildfire smoke as affecting the samples. A request-exclusion qualifier is an official submitting-agency causal claim, but this endpoint does not establish EPA concurrence.
U.S. EPA Air Quality System and the submitting air monitoring agency · Jun 26, 2003officialgovernment
EPA AQS carries an agency-submitted request-exclusion qualifier (E, Forest Fire.) on 5 PM2.5 samples in the candidate CBSA on 2003-06-26, identifying wildfire smoke as affecting the samples. A request-exclusion qualifier is an official submitting-agency causal claim, but this endpoint does not establish EPA concurrence.
What remains uncertain
AQS qualifiers are submitting-agency causal flags and do not by themselves establish EPA concurrence.
Status and provenance
EPA monitor flagEPA attached an exceptional-event qualifier to the affected samples. The agency flagged the measurement itself; no separate agency record describes the event.
This episode was grouped from the monitor record by the catalog pipeline and given
its cause from the evidence listed above. It has not been individually reviewed and
signed off, so its boundaries, cause, and name may change as evidence accumulates.
Grouping policy common_sense_root_cause_grouping.v2. The cause label reflects the
assembled evidence above, not an IAQng detection formula. If it is wrong,
tell us.