← Air events

Regional secondary PM Possible

2001-08-01 to 2001-08-02 Akron, OH, Buffalo-Cheektowaga-Niagara Falls, NY, and 4 other metros regional secondary-particle pollution episode

August 1, 2001 to August 2, 2001

Daily PM2.5 peaked at 57.7 µg/m³ near Akron across 6 covered metros home to 8.1 million people. 4 metros 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 ≈ 2.4 cigarettes. Across everyone living in the affected metros, that is the collective equivalent of ≈ 20 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”

Manual research connected 5 source events to one regional secondary-particle pollution episode using the deterministic grouping rule.

Possible This is a transparent hypothesis supported by limited evidence or an explicit inference, not a definitive attribution.

Journal of the Air & Waste Management Association · May 1, 2005 corroborates

The Steubenville Comprehensive Air Monitoring Program (SCAMP): Analysis of Short-Term and Episodic Variations in PM2.5 Concentrations Using Hourly Air Monitoring Data

SCAMP identifies July 29-August 4 as a regional secondary-PM2.5 episode. Sulfate supplied 47.6% and 46.2% of measured mass on the two composition days, and the authors attribute the episode to secondary formation under warm, sunny, high-pressure stagnation.

Meteorological Service of Canada / American Meteorological Society corroborates

Atmospheric Emission Reduction Scenarios Simulated by Canadian AURAMS Model

The AURAMS study modeled the July 29-August 4, 2001 episode across eastern Canada and the eastern United States. It reports that August 2 brought high ozone and PM2.5 across Quebec mainly from long-range pollutant transport during hot, humid southwesterly flow; the regional pattern involved high-pressure stagnation followed by southwest transport.

U.S. EPA AirData hypothesis

Buffalo-Cheektowaga-Niagara Falls, NY joint pollution fingerprint, 2001-08-02

EPA records show median daily PM2.5 of 46.6 micrograms per cubic meter across 4 monitors, 4.591 times the adjacent-window level. Co-pollutants at least 10% above the adjacent-window comparison were nitrogen dioxide (1.697x), sulfur dioxide (1.697x). Other measured comparisons were carbon monoxide (1.023x).

Inference, not direct attribution

exact_window_regional_secondary_field_study_possible.v1: This inference is recorded in the catalog methodology.

regional_secondary_transboundary_convergence.v1: This inference is recorded in the catalog methodology.

See every retained source and limitation ↓

Sequence: Cincinnati (Aug 1) → Akron (Aug 2) → Columbus (Aug 2) → Buffalo (Aug 2) → Syracuse (Aug 2) → Rochester (Aug 2)

Evidence path

From source to city

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.

Open the evidence ledger ↓
  1. 1

    Source or mechanism

    Regional secondary PM

    SCAMP identifies July 29-August 4 as a regional secondary-PM2.5 episode. Sulfate supplied 47.6% and 46.2% of measured mass on the two composition days, and the authors attribute the episode to secondary formation under warm, sunny, high-pressure…

    View supporting source ↗
    Documented
  2. 2

    Air-mass movement

    The 72-hour air-mass history is reconstructed

    NOAA HYSPLIT modeled 24 backward paths across multiple arrival times and heights. They show where the air traveled, not which source polluted it.

    Explore the modeled paths ↓
    Modeled
  3. 3

    Local response

    57.7 µg/m³ near Akron

    EPA monitors recorded the event across 6 metros. The peak daily concentration is roughly 2.6 cigarette-equivalents at the outdoor daily rate.

    Inspect the pollutant and weather signals ↓
    Documented

Event autopsy

What the instruments saw

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

Akron, OH

Monitor comparison window 2001-07-30 to 2001-08-05 · PM2.5 target: East HS

5 pollutant signals
Fine-particle pulse 56.6 µg/m³

171% above nearby days

PM10 64 µg/m³

142% higher than surrounding days

Pollution fingerprint

Metro-wide median of reporting monitors
PM2.5 56.6 µg/m³

171% higher than surrounding days

Before32.2 µg/m³ Event56.6 µg/m³ After19 µg/m³
3 monitors · 24 HOUR
PM10 64 µg/m³

142% higher than surrounding days

Before40.5 µg/m³ Event64 µg/m³ After23 µg/m³
2 monitors · 24-HR BLK AVG
Carbon monoxide 0.733 ppm

About the same as surrounding days

Before0.746 ppm Event0.733 ppm After0.576 ppm
2 monitors · 1 HOUR
Sulfur dioxide 18.3 ppb

165% higher than surrounding days

Before6.93 ppb Event18.3 ppb After5.87 ppb
2 monitors · 1 HOUR
Ozone 0.060 ppm

20% higher than surrounding days

Before0.062 ppm Event0.060 ppm After0.037 ppm
2 monitors · 8-HR RUN AVG BEGIN HOUR

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 Cincinnati

Peak-date arrivals · 2001-08-02

Broad history Mostly south of the metro
72-hour reach 100–500 km
Sensitivity runs 12 modeled paths
Arrival metro
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.

Views from the selected metro

Camera views near

Browse the camera map →

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.

Affected metros

MetroPeak PM2.5Cigarettes, whole eventPeak dayAll-time standing
Akron, OH 57.7 µg/m³ 2.6 Aug 2, 2001 #6 of its top days
Columbus, OH 57.4 µg/m³ 2.6 Aug 2, 2001 #11 of its top days
Cincinnati, OH-KY-IN 56.1 µg/m³ 4.8 Aug 2, 2001 #9 of its top days
Buffalo-Cheektowaga-Niagara Falls, NY 48.3 µg/m³ 2.2 Aug 2, 2001 #8 of its top days
Syracuse, NY 45.4 µg/m³ 2.1 Aug 2, 2001 #8 of its top days
Rochester, NY 42.5 µg/m³ 1.9 Aug 2, 2001 #11 of its top days

"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.

14 retained sources

Official record

Buffalo-Cheektowaga-Niagara Falls, NY surface conditions, 2001-08-02

National Weather Service surface observations via Iowa Environmental Mesonet

BUFFALO INTL ARPT recorded calm conditions during 0% of event hours and wind at or below three knots during 0%. Observations included 20 haze hours, minimum visibility 4 miles.

What it supports

This source supports a possible mechanism or occurrence; it does not establish the cause by itself.

Limit

A single surface station documents ventilation and obscuration but not the full vertical profile or particle source mix.

Official record

Syracuse, NY surface conditions, August 2, 2001

National Weather Service surface observations via Iowa Environmental Mesonet

SYRACUSE/HANCOCK recorded 15 haze-coded hours, median visibility of 5.5 miles, median wind of 4 knots, and median sea-level pressure of 1020.55 millibars on August 2.

What it supports

This source supports a possible mechanism or occurrence; it does not establish the cause by itself.

Limit

One airport station documents the local air mass and obscuration but not particle composition or the full metropolitan mixing layer.

Official record

Rochester, NY surface conditions, August 2, 2001

National Weather Service surface observations via Iowa Environmental Mesonet

ROCHESTER/MONROE CO recorded 12 haze-coded hours, median visibility of 6.5 miles, median wind of 8 knots, and median sea-level pressure of 1020.8 millibars on August 2.

What it supports

This source supports a possible mechanism or occurrence; it does not establish the cause by itself.

Limit

One airport station documents the local air mass and obscuration but not particle composition or the full metropolitan mixing layer.

Official record

Buffalo-Cheektowaga-Niagara Falls, NY joint pollution fingerprint, 2001-08-02

U.S. EPA AirData

EPA records show median daily PM2.5 of 46.6 micrograms per cubic meter across 4 monitors, 4.591 times the adjacent-window level. Co-pollutants at least 10% above the adjacent-window comparison were nitrogen dioxide (1.697x), sulfur dioxide (1.697x). Other measured comparisons were carbon monoxide (1.023x).

What it supports

This source supports a possible mechanism or occurrence; it does not establish the cause by itself.

Limit

The pollution fingerprint does not uniquely apportion traffic, heating, industry, wood combustion, or secondary aerosol.

Official record

Syracuse, NY joint pollution fingerprint, August 2, 2001

U.S. EPA AirData

EPA records show median daily PM2.5 of 44.5 micrograms per cubic meter across 3 monitors, compared with 7.95 in the adjacent-window comparison. Eight-hour ozone rose to 0.0611 ppm and sulfur dioxide rose to 5.375 ppb.

What it supports

This source supports a possible mechanism or occurrence; it does not establish the cause by itself.

Limit

The pollution fingerprint demonstrates a simultaneous multi-pollutant episode but cannot by itself distinguish transported secondary aerosol from local emissions.

Official record

Rochester, NY joint pollution fingerprint, August 2, 2001

U.S. EPA AirData

EPA records show median daily PM2.5 of 42 micrograms per cubic meter across 2 monitors, compared with 9 in the adjacent-window comparison. Eight-hour ozone rose to 0.0703 ppm and sulfur dioxide rose to 7.0208 ppb.

What it supports

This source supports a possible mechanism or occurrence; it does not establish the cause by itself.

Limit

The pollution fingerprint demonstrates a simultaneous multi-pollutant episode but cannot by itself distinguish transported secondary aerosol from local emissions.

Scientific research

The Steubenville Comprehensive Air Monitoring Program (SCAMP): Analysis of Short-Term and Episodic Variations in PM2.5 Concentrations Using Hourly Air Monitoring Data

Journal of the Air & Waste Management Association

SCAMP identifies July 29-August 4 as a regional secondary-PM2.5 episode. Sulfate supplied 47.6% and 46.2% of measured mass on the two composition days, and the authors attribute the episode to secondary formation under warm, sunny, high-pressure stagnation.

What it supports

A retained source supports the attributed cause for the stated place and dates.

Limit

The intensive monitor was in Steubenville; applying the regional episode to Cincinnati and Columbus is capped at possible.

Scientific research

The Steubenville Comprehensive Air Monitoring Program (SCAMP): Analysis of Short-Term and Episodic Variations in PM2.5 Concentrations Using Hourly Air Monitoring Data

Journal of the Air & Waste Management Association

SCAMP identifies July 29-August 4 as a regional secondary-PM2.5 episode. Sulfate supplied 47.6% and 46.2% of measured mass on the two composition days, and the authors attribute the episode to secondary formation under warm, sunny, high-pressure stagnation.

What it supports

A retained source supports the attributed cause for the stated place and dates.

Limit

The intensive composition monitor was in Steubenville; applicability to Akron and Buffalo is regional and capped at possible.

Show 6 more retained sources

Scientific research

The Steubenville Comprehensive Air Monitoring Program (SCAMP): Analysis of Short-Term and Episodic Variations in PM2.5 Concentrations Using Hourly Air Monitoring Data

Journal of the Air & Waste Management Association

SCAMP identifies July 29-August 4, 2001 as a regional secondary-PM2.5 episode. Sulfate supplied 47.6% and 46.2% of measured mass on the two composition days, and the authors describe secondary formation under warm, sunny, high-pressure conditions; the highest concentrations occurred overnight August 1-2 under reduced mixing heights.

What it supports

A retained source supports the attributed cause for the stated place and dates.

Limit

The composition measurements were made in Steubenville, Ohio, not at the New York metro; they establish the same-window regional episode and mechanism but not a city-specific source fraction.

Scientific research

The Steubenville Comprehensive Air Monitoring Program (SCAMP): Analysis of Short-Term and Episodic Variations in PM2.5 Concentrations Using Hourly Air Monitoring Data

Journal of the Air & Waste Management Association

SCAMP identifies July 29-August 4 as a regional secondary-PM2.5 episode. Sulfate supplied 47.6% and 46.2% of measured mass on the two composition days, and the authors attribute the episode to secondary formation under warm, sunny, high-pressure stagnation.

What it supports

A retained source supports the attributed cause for the stated place and dates.

Limit

The intensive composition monitor was in Steubenville; applicability to Akron and Buffalo is regional and capped at possible.

Scientific research

The Steubenville Comprehensive Air Monitoring Program (SCAMP): Analysis of Short-Term and Episodic Variations in PM2.5 Concentrations Using Hourly Air Monitoring Data

Journal of the Air & Waste Management Association

SCAMP identifies July 29-August 4, 2001 as a regional secondary-PM2.5 episode. Sulfate supplied 47.6% and 46.2% of measured mass on the two composition days, and the authors describe secondary formation under warm, sunny, high-pressure conditions; the highest concentrations occurred overnight August 1-2 under reduced mixing heights.

What it supports

A retained source supports the attributed cause for the stated place and dates.

Limit

The composition measurements were made in Steubenville, Ohio, not at the New York metro; they establish the same-window regional episode and mechanism but not a city-specific source fraction.

Scientific research

Atmospheric Emission Reduction Scenarios Simulated by Canadian AURAMS Model

Meteorological Service of Canada / American Meteorological Society

The AURAMS study modeled the July 29-August 4, 2001 episode across eastern Canada and the eastern United States. It reports that August 2 brought high ozone and PM2.5 across Quebec mainly from long-range pollutant transport during hot, humid southwesterly flow; the regional pattern involved high-pressure stagnation followed by southwest transport.

What it supports

A retained source supports the attributed cause for the stated place and dates.

Limit

The paper validates the episode at Quebec sites and does not directly apportion PM2.5 at Buffalo, Rochester, or Syracuse.

Scientific research

Atmospheric Emission Reduction Scenarios Simulated by Canadian AURAMS Model

Meteorological Service of Canada / American Meteorological Society

The AURAMS study modeled the July 29-August 4, 2001 episode across eastern Canada and the eastern United States. It reports that August 2 brought high ozone and PM2.5 across Quebec mainly from long-range pollutant transport during hot, humid southwesterly flow; the regional pattern involved high-pressure stagnation followed by southwest transport.

What it supports

A retained source supports the attributed cause for the stated place and dates.

Limit

The paper validates the episode at Quebec sites and does not directly apportion PM2.5 at Buffalo, Rochester, or Syracuse.

Scientific research

Atmospheric Emission Reduction Scenarios Simulated by Canadian AURAMS Model

Meteorological Service of Canada / American Meteorological Society

The AURAMS study modeled the July 29-August 4, 2001 episode across eastern Canada and the eastern United States. It reports that August 2 brought high ozone and PM2.5 across Quebec mainly from long-range pollutant transport during hot, humid southwesterly flow; the regional pattern involved high-pressure stagnation followed by southwest transport.

What it supports

A retained source supports the attributed cause for the stated place and dates.

Limit

The paper validates the episode at Quebec sites and does not directly apportion PM2.5 at Buffalo, Rochester, or Syracuse.

What remains uncertain

Status and provenance

Possible This 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.