Daily PM2.5 peaked at 41.7 µg/m³ near Raleigh across
1 covered metro home to 1.6 million people.
Counting the extra PM2.5 above each metro's typical day, this event handed the
average affected resident ≈ 1.4 cigarettes.
Across everyone living in the affected metros, that is the collective equivalent of
≈ 2.2 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 “Temperature inversion”
An exact-date NWS discussion documents a capped inversion over the central North Carolina air mass during a short, certified Raleigh particle episode. The evidence supports a possible accumulation mechanism, not a specific emissions source.
PossibleThis is a transparent hypothesis supported by limited evidence or an explicit inference, not a definitive attribution.
National Weather Service Raleigh via Iowa Environmental Mesonet · Aug 6, 2004hypothesis
On August 6, NWS Raleigh reported lingering low-level moisture beneath a capped inversion shown by the Greensboro sounding, with clouds expected to limit daytime heating across central North Carolina.
EPA monitor records show a short Raleigh particle episode: continuous PM2.5 reached 38.2 µg/m³ on August 4, the Millbrook FRM sample reached 41.7 µg/m³ on August 6, and continuous PM2.5 fell to 12.8 µg/m³ on August 7. PM10 also fell from 44 µg/m³ on August 4 to 12 µg/m³ on August 6, while event-day ozone, CO, and SO2 were not similarly elevated.
North Carolina Division of Air Quality · Jan 1, 2005hypothesis
North Carolina's annual monitoring report lists 41.7 µg/m³ as the highest of 330 valid 24-hour PM2.5 samples at Raleigh's Millbrook monitor in 2004, corroborating that the August 6 value was a real local annual maximum.
Inference, not direct attribution
Documented inversion overlap: The event overlaps a documented inversion period, but the retained material does not directly attribute the measured PM2.5 episode.
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.
Documented inversion overlap. The event overlaps a documented inversion period, but the retained material does not directly attribute the measured PM2.5 episode.
Inferred
2
Air-mass movement
The transport path has not been reconstructed
The retained record does not yet show how air traveled from the proposed source to
these metros. A trajectory replay or dated plume analysis belongs here.
Research gap
3
Local response
41.7 µg/m³ near Raleigh
EPA monitors recorded the event across 1 metro.
The peak daily concentration is roughly 1.9 cigarette-equivalents at the outdoor daily rate.
Before, during, and after the episode: nearby pollutant monitors and surface-weather
stations show what changed. This context tests the “Temperature inversion” explanation; it does
not assign the cause by itself.
Observed context · not attribution
Raleigh, NC
Monitor comparison window 2004-08-03 to 2004-08-09 · PM2.5 target: Millbrook School
5 pollutant signals
Fine-particle pulse41.7 µg/m³
83% above nearby days
PM1012 µg/m³
43% lower than surrounding days
Pollution fingerprint
Metro-wide median of reporting monitors
PM2.541.7 µg/m³
83% higher than surrounding days
Before3.90 µg/m³ Event41.7 µg/m³ After—
PM1012 µg/m³
43% lower than surrounding days
Before29 µg/m³ Event12 µg/m³ After21 µg/m³
Carbon monoxide0.270 ppm
22% lower than surrounding days
Before0.348 ppm Event0.270 ppm After0.409 ppm
Sulfur dioxide1.26 ppb
52% lower than surrounding days
Before3 ppb Event1.26 ppb After2.61 ppb
Ozone0.023 ppm
34% lower than surrounding days
Before0.040 ppm Event0.023 ppm After0.035 ppm
Atmospheric conditions
Nearby EPA weather observations
Humidity67.7 %
About the same as surrounding days
Temperature67.9 °F
8% lower 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.
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.
3 retained sources
Official record
2004 Ambient Air Quality Report
North Carolina Division of Air Quality
North Carolina's annual monitoring report lists 41.7 µg/m³ as the highest of 330 valid 24-hour PM2.5 samples at Raleigh's Millbrook monitor in 2004, corroborating that the August 6 value was a real local annual maximum.
What it supports
This source supports a possible mechanism or occurrence; it does not establish the cause by itself.
Limit
The report validates the monitored value but does not attribute the episode to an emissions source or meteorological mechanism.
Official record
Area Forecast Discussion: lingering low-level moisture beneath a capped inversion
National Weather Service Raleigh via Iowa Environmental Mesonet
On August 6, NWS Raleigh reported lingering low-level moisture beneath a capped inversion shown by the Greensboro sounding, with clouds expected to limit daytime heating across central North Carolina.
What it supports
This source supports a possible mechanism or occurrence; it does not establish the cause by itself.
Limit
The discussion documents an atmospheric trapping layer, not a particular emitting source.
Official record
Raleigh particle episode fingerprint, August 4–7, 2004
U.S. EPA AirData
EPA monitor records show a short Raleigh particle episode: continuous PM2.5 reached 38.2 µg/m³ on August 4, the Millbrook FRM sample reached 41.7 µg/m³ on August 6, and continuous PM2.5 fell to 12.8 µg/m³ on August 7. PM10 also fell from 44 µg/m³ on August 4 to 12 µg/m³ on August 6, while event-day ozone, CO, and SO2 were not similarly elevated.
What it supports
This source supports a possible mechanism or occurrence; it does not establish the cause by itself.
Limit
The scheduled FRM and continuous measurements are not interchangeable and were not available on every date; together they establish episode timing, not a daily chemical composition series.
What remains uncertain
The classification therefore describes a possible trapping mechanism and is capped at possible confidence.
The event-day inversion and monitored episode are documented, but no exact-date chemical source apportionment or dominant emitting source was recovered.
Status and provenance
PossibleThis is a transparent hypothesis supported by limited evidence or an explicit inference, not a definitive attribution.
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.