2002-07-01 to 2002-07-02 Rochester, NY, Scranton--Wilkes-Barre--Hazleton, PA, and 1 other metros regional secondary-particle pollution episode
July 1, 2002 to July 2, 2002
Daily PM2.5 peaked at 53.4 µg/m³ near Scranton across
3 covered metros home to 2.3 million people.
1 metro placed a top-ten day in their record.
Counting the extra PM2.5 above each metro's typical day, this event handed the
average affected resident ≈ 2.2 cigarettes.
Across everyone living in the affected metros, that is the collective equivalent of
≈ 5.1 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 “Regional secondary PM”
The Pennsylvania DEP-supported NE-OPS report identifies June 30-July 4 as the first major regional summer pollution episode of 2002, distinguishes it from the Canadian wildfire-smoke episode that began July 6, and attributes the earlier episode to transported pollution typical of summer ozone and PM events.
LikelyApplicable reporting or a supported inference makes this the best current causal explanation.
Pennsylvania Department of Environmental Protection / NE-OPS · Jan 1, 2003corroborates
The report identifies June 30-July 4 as a major summer ozone and PM episode caused by transported pollution from the westward boundary. It separately identifies July 6-8 as the Canadian forest-fire-smoke event, excluding that later smoke episode as the cause of these July 1-2 observations.
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.
The report identifies June 30-July 4 as a major summer ozone and PM episode caused by transported pollution from the westward boundary. It separately identifies July 6-8 as the Canadian forest-fire-smoke event, excluding that later smoke episode as…
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
53.4 µg/m³ near Scranton
EPA monitors recorded the event across 3 metros.
The peak daily concentration is roughly 2.4 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 “Regional secondary PM” explanation; it does
not assign the cause by itself.
Observed context · not attribution
Rochester, NY
Monitor comparison window 2002-06-28 to 2002-07-05
4 pollutant signals
Fine-particle pulse42.4 µg/m³
50% above nearby days
Air movement3.28 kt
8% lower than surrounding days
Carbon monoxide0.472 ppm
14% higher than surrounding days
Pollution fingerprint
Metro-wide median of reporting monitors
PM2.542.4 µg/m³
50% higher than surrounding days
Before— Event42.4 µg/m³ After14.1 µg/m³
Carbon monoxide0.472 ppm
14% higher than surrounding days
Before0.498 ppm Event0.472 ppm After0.335 ppm
Sulfur dioxide5.58 ppb
20% lower than surrounding days
Before7.31 ppb Event5.58 ppb After7.27 ppb
Ozone0.071 ppm
37% higher than surrounding days
Before0.032 ppm Event0.071 ppm After0.049 ppm
Atmospheric conditions
Nearby EPA weather observations
Humidity68.9 %
About the same as surrounding days
Pressure1000 Millibars
About the same as surrounding days
Temperature83.5 °F
5% higher than surrounding days
Wind3.28 kt
8% lower than surrounding days
Scranton--Wilkes-Barre--Hazleton, PA
Monitor comparison window 2002-06-28 to 2002-07-05 · PM2.5 target: Scranton
6 pollutant signals
Fine-particle pulse49.3 µg/m³
121% above nearby days
PM1059.5 µg/m³
76% higher than surrounding days
Pollution fingerprint
Metro-wide median of reporting monitors
PM2.549.3 µg/m³
121% higher than surrounding days
Before13.9 µg/m³ Event49.3 µg/m³ After20.3 µg/m³
PM1059.5 µg/m³
76% higher than surrounding days
Before19.5 µg/m³ Event59.5 µg/m³ After39 µg/m³
Carbon monoxide0.379 ppm
96% higher than surrounding days
Before0.183 ppm Event0.379 ppm After0.135 ppm
Nitrogen dioxide15.6 ppb
58% higher than surrounding days
Before9.21 ppb Event15.6 ppb After7.08 ppb
Sulfur dioxide11.1 ppb
88% higher than surrounding days
Before5.65 ppb Event11.1 ppb After5.81 ppb
Ozone0.050 ppm
64% higher than surrounding days
Before0.024 ppm Event0.050 ppm After0.029 ppm
Syracuse, NY
Monitor comparison window 2002-06-28 to 2002-07-05 · PM2.5 target: EAST SYRACUSE
4 pollutant signals
Fine-particle pulse44.4 µg/m³
183% above nearby days
Air movement4.15 kt
19% lower than surrounding days
Carbon monoxide0.487 ppm
About the same as surrounding days
Pollution fingerprint
Metro-wide median of reporting monitors
PM2.544.4 µg/m³
183% higher than surrounding days
Before9 µg/m³ Event44.4 µg/m³ After15.7 µg/m³
Carbon monoxide0.487 ppm
About the same as surrounding days
Before0.465 ppm Event0.487 ppm After0.412 ppm
Sulfur dioxide2.50 ppb
About the same as surrounding days
Before2.08 ppb Event2.50 ppb After2.54 ppb
Ozone0.058 ppm
36% higher than surrounding days
Before0.026 ppm Event0.058 ppm After0.045 ppm
Atmospheric conditions
Nearby EPA weather observations
Humidity76.4 %
About the same as surrounding days
Pressure980 Millibars
About the same as surrounding days
Temperature78.5 °F
5% higher than surrounding days
Wind4.15 kt
19% 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.
1 retained source
Scientific research
Processes Controlling Urban Air Pollution in the Northeast: Summer 2002
Pennsylvania Department of Environmental Protection / NE-OPS
The report identifies June 30-July 4 as a major summer ozone and PM episode caused by transported pollution from the westward boundary. It separately identifies July 6-8 as the Canadian forest-fire-smoke event, excluding that later smoke episode as the cause of these July 1-2 observations.
What it supports
A retained source supports the attributed cause for the stated place and dates.
Limit
The measurement campaign centered on the Northeast regional episode and does not provide monitor-by-monitor source apportionment for every listed metro.
What remains uncertain
The report resolves the regional mechanism but not a single source facility or emissions inventory.
Status and provenance
LikelyApplicable reporting or a supported inference makes this the best current causal explanation.
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.