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Stagnant pollution mixture Possible

2005-07-26 Birmingham-Hoover, AL stagnant mixed-pollution episode

July 26, 2005

Daily PM2.5 peaked at 63 µg/m³ near Birmingham across 1 covered metro home to 1.2 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 ≈ 2.3 cigarettes. Across everyone living in the affected metros, that is the collective equivalent of ≈ 2.7 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 “Stagnant pollution mixture”

A ten-monitor PM2.5 rise occurred with compatible PM10 and carbon monoxide increases. Exact-date NWS products kept Birmingham under the influence of an upper ridge, restored haze to the forecast as visibility struggled above three miles, and described hazy skies into the night; the surface station was calm during two-thirds of event hours. This supports stagnant mixed-pollution accumulation as a possible mechanism.

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

National Weather Service surface observations via Iowa Environmental Mesonet · Jul 26, 2005 hypothesis

Birmingham surface conditions, July 26, 2005

Birmingham's official station recorded 15 hours of haze; 79.2% of event hours had wind at or below three knots and 66.7% were calm.

National Weather Service Birmingham via Iowa Environmental Mesonet · Jul 26, 2005 hypothesis

Area Forecast Discussion: haze with visibility near three miles

The exact-date NWS update restored haze to the forecast because visibility was struggling to rise above three miles at many locations; the broader discussion kept Alabama under the ridge's influence for one more day.

U.S. EPA AirData · Jul 26, 2005 hypothesis

Birmingham joint pollution fingerprint, July 26, 2005

EPA records show median daily PM2.5 of 59.15 micrograms per cubic meter across ten monitors, more than twice the adjacent-window level, with compatible PM10 and carbon monoxide increases.

Inference, not direct attribution

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

See every retained source and limitation ↓

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

    Pattern-based explanation

    official_surface_weak_dispersion_multimonitor_accumulation.v1. This inference is recorded in the catalog methodology.

    Inferred
  2. 2

    Air-mass movement

    The 72-hour air-mass history is reconstructed

    NOAA HYSPLIT modeled 12 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

    63 µg/m³ near Birmingham

    EPA monitors recorded the event across 1 metro. The peak daily concentration is roughly 2.9 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 “Stagnant pollution mixture” explanation; it does not assign the cause by itself.

Observed context · not attribution

Birmingham-Hoover, AL

Monitor comparison window 2005-07-23 to 2005-07-29 · PM2.5 target: North Birmingham

5 pollutant signals
Fine-particle pulse 59.1 µg/m³

71% above nearby days

PM10 89.5 µg/m³

77% higher than surrounding days

Pollution fingerprint

Metro-wide median of reporting monitors
PM2.5 59.1 µg/m³

71% higher than surrounding days

Before34.5 µg/m³ Event59.1 µg/m³ After21.2 µg/m³
10 monitors · 24 HOUR
PM10 89.5 µg/m³

77% higher than surrounding days

Before50.5 µg/m³ Event89.5 µg/m³ After33.5 µg/m³
4 monitors · 24-HR BLK AVG
Carbon monoxide 1.01 ppm

63% higher than surrounding days

Before0.621 ppm Event1.01 ppm After0.592 ppm
3 monitors · 1 HOUR
Sulfur dioxide 2.25 ppb

About the same as surrounding days

Before3.75 ppb Event2.25 ppb After1.38 ppb
1 monitor · 1 HOUR
Ozone 0.035 ppm

About the same as surrounding days

Before0.042 ppm Event0.035 ppm After0.028 ppm
10 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 Birmingham-Hoover

Peak-date arrivals · 2005-07-26

Broad history Mostly northeast of the metro
72-hour reach 100–1,000 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
Birmingham-Hoover, AL 63 µg/m³ 2.9 Jul 26, 2005 #3 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.

4 retained sources

Official record

Birmingham surface conditions, July 26, 2005

National Weather Service surface observations via Iowa Environmental Mesonet

Birmingham's official station recorded 15 hours of haze; 79.2% of event hours had wind at or below three knots and 66.7% were calm.

What it supports

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

Limit

One surface station cannot fully characterize metropolitan ventilation, and haze is not source-specific.

Official record

Area Forecast Discussion: haze with visibility near three miles

National Weather Service Birmingham via Iowa Environmental Mesonet

The exact-date NWS update restored haze to the forecast because visibility was struggling to rise above three miles at many locations; the broader discussion kept Alabama under the ridge's influence for one more day.

What it supports

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

Limit

The discussion documents haze and the synoptic setting but does not identify particle composition or source shares.

Official record

Birmingham joint pollution fingerprint, July 26, 2005

U.S. EPA AirData

EPA records show median daily PM2.5 of 59.15 micrograms per cubic meter across ten monitors, more than twice the adjacent-window level, with compatible PM10 and carbon monoxide increases.

What it supports

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

Limit

The fingerprint supports mixed accumulation but cannot distinguish local from regional source shares.

Scientific research

A Multi-Sensor Analysis of the 2007 Georgia/Florida Fires and Its Impact on Air Quality

Remote Sensing

The regional analysis describes central Alabama summers as frequently hot, humid, and stagnant under the Bermuda High, with inversions that can trap particles near the surface. That mechanism is consistent with the event fingerprint for July 26, 2005.

What it supports

Context for the event; this item does not establish the attributed cause by itself.

Limit

This source describes the regional summer mechanism and a later fire episode; it is not a direct attribution of Birmingham's July 26, 2005 PM2.5 event.

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.