2001-04-30 Riverside-San Bernardino-Ontario, CA stagnant mixed-pollution episode
April 30, 2001
Daily PM2.5 peaked at 82.7 µg/m³ near Riverside across
1 covered metro home to 4.7 million people.
Counting the extra PM2.5 above each metro's typical day, this event handed the
average affected resident ≈ 3.0 cigarettes.
Across everyone living in the affected metros, that is the collective equivalent of
≈ 14 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”
Riverside's April 30 PM2.5 peak coincided with increases in carbon monoxide, nitrogen dioxide, and sulfur dioxide while block-average PM10 stayed near its surrounding-day level. The exact NWS discussion documents a strong, shallow inversion under high pressure and subsidence. A peer-reviewed Riverside study from February-May 2001 identifies the area's recurring mixture of aged basin aerosol, traffic emissions, and secondary ammonium nitrate. Together these support stagnant anthropogenic mixture at possible confidence, without assigning exact source shares or excluding every undocumented episodic source.
PossibleThis is a transparent hypothesis supported by limited evidence or an explicit inference, not a definitive attribution.
National Weather Service San Diego Area Forecast Discussion via Iowa Environmental Mesonet · Apr 30, 2001hypothesis
The exact-date NWS discussion reported high pressure aloft, warming and subsidence, a marine inversion lowered to about 1,500 feet, and an inversion strength near 10 degrees Celsius. A later discussion said the strong inversion remained intact and prevented significant mixing.
EPA's certified daily record shows 82.7 micrograms per cubic meter of PM2.5 at Rubidoux on April 30 after 64.15 on the preceding sampled day and before 33.85 on the following sampled day. Across the metro's reporting monitors, median carbon monoxide rose to 0.6022 ppm, nitrogen dioxide to 26.0652 ppb, and sulfur dioxide to 1.2391 ppb, while same-day block-average PM10 remained 27 micrograms per cubic meter. The joint pattern is more compatible with accumulated fine combustion and secondary pollution than a coarse-dust event.
Inference, not direct attribution
exact_inversion_plus_fine_combustion_fingerprint_and_same_period_source_context_possible.v1: This inference is recorded in the catalog methodology.
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.
exact_inversion_plus_fine_combustion_fingerprint_and_same_period_source_context_possible.v1. This inference is recorded in the catalog methodology.
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
82.7 µg/m³ near Riverside
EPA monitors recorded the event across 1 metro.
The peak daily concentration is roughly 3.8 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 “Stagnant pollution mixture” explanation; it does
not assign the cause by itself.
Observed context · not attribution
Riverside-San Bernardino-Ontario, CA
Monitor comparison window 2001-04-27 to 2001-05-03 · PM2.5 target: Rubidoux
6 pollutant signals
Fine-particle pulse82.7 µg/m³
64% above nearby days
Air movement8.5 kt median wind
11 kt maximum
What observers saw7 mi minimum visibility
0 hours at or below 3 miles
Pollution fingerprint
Metro-wide median of reporting monitors
PM2.582.7 µg/m³
64% higher than surrounding days
Before64.2 µg/m³ Event82.7 µg/m³ After33.9 µg/m³
PM1027 µg/m³
About the same as surrounding days
Before27.5 µg/m³ Event27 µg/m³ After33 µg/m³
Carbon monoxide0.602 ppm
26% higher than surrounding days
Before0.463 ppm Event0.602 ppm After0.478 ppm
Nitrogen dioxide26.1 ppb
55% higher than surrounding days
Before13 ppb Event26.1 ppb After16.8 ppb
Sulfur dioxide1.24 ppb
97% higher than surrounding days
Before0.630 ppb Event1.24 ppb After0.609 ppb
Ozone0.044 ppm
About the same as surrounding days
Before0.043 ppm Event0.044 ppm After0.042 ppm
Atmospheric conditions
BEAUMONT, 42.1 km from the PM2.5 target
Wind8.5 kt median
11 kt maximum · No calm observed hours
Visibility7 mi minimum
0 observed hours at or below 3 miles
Temperature83.3°F median
46.4°F to 91.4°F
Humidity26% median
76% maximum
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
Strong shallow inversion over Southern California, April 30, 2001
National Weather Service San Diego Area Forecast Discussion via Iowa Environmental Mesonet
The exact-date NWS discussion reported high pressure aloft, warming and subsidence, a marine inversion lowered to about 1,500 feet, and an inversion strength near 10 degrees Celsius. A later discussion said the strong inversion remained intact and prevented significant mixing.
What it supports
This source supports a possible mechanism or occurrence; it does not establish the cause by itself.
Limit
The NWS discussion documents the trapping conditions but does not attribute the measured PM2.5 to a source sector.
Official record
Riverside pollution fingerprint, April 30, 2001
U.S. EPA AirData
EPA's certified daily record shows 82.7 micrograms per cubic meter of PM2.5 at Rubidoux on April 30 after 64.15 on the preceding sampled day and before 33.85 on the following sampled day. Across the metro's reporting monitors, median carbon monoxide rose to 0.6022 ppm, nitrogen dioxide to 26.0652 ppb, and sulfur dioxide to 1.2391 ppb, while same-day block-average PM10 remained 27 micrograms per cubic meter. The joint pattern is more compatible with accumulated fine combustion and secondary pollution than a coarse-dust event.
What it supports
This source supports a possible mechanism or occurrence; it does not establish the cause by itself.
Limit
Only one FRM PM2.5 monitor sampled on the event date, and the co-pollutant comparison is descriptive rather than source apportionment.
Scientific research
Inferring the Sources of Fine and Ultrafine Particulate Matter at Downwind Receptor Sites in the Los Angeles Basin
Fine et al., Aerosol Science and Technology
A peer-reviewed mobile supersite study sampled Riverside from February through May 2001. It describes Riverside and Rubidoux as downwind receptors for aged Los Angeles Basin aerosol, identifies morning traffic emissions and low mixing heights, and notes secondary ammonium-nitrate formation associated with downwind ammonia sources. This establishes the plausible recurring anthropogenic mixture during the exact season, not the composition of April 30 itself.
What it supports
Context for the event; this item does not establish the attributed cause by itself.
Limit
The study covers the same place and measurement period but does not publish an exact April 30 source apportionment.
What remains uncertain
No exact-date chemical-speciation or receptor-model result was recovered.
The result is a broad source-mixture estimate and does not name a unique emitter or quantify source shares.
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.