Initial Ozone Exceedance Analysis for July 29, 2026

9 monitor site(s) exceeded the ozone standard of 70 ppb on 2026-07-29.

Prescribed fires within 50 miles:
Today: 0 | 1 Day Before: 0 | 2 Days Before: 0

Wildfires within 100 miles:
Total: 4

Monitors Exceeding Ozone Concentration of 70 ppb

Monitor AQS ID Site Name Location (Lat, Long) Ozone Value AQI Category
060658001 Riverside - Rubidoux 34.00, -117.42 75.0 Sensitive Group
060658005 Mira Loma - Van Buren 34.00, -117.49 74.0 Sensitive Group
060370016 Glendora - Laurel 34.14, -117.85 82.0 Sensitive Group
060372005 Pasadena 34.13, -118.13 72.0 Sensitive Group
060710005 Crestline - Lake Gregory 34.24, -117.27 94.0 Unhealthy
060710306 Victorville - Park Avenue 34.51, -117.33 79.0 Sensitive Group
060714001 Hesperia - Olive Street 34.42, -117.29 83.0 Sensitive Group
060719004 San Bernadino - 4th Street 34.11, -117.27 84.0 Sensitive Group
060714003 Redlands - Dearborn 34.06, -117.15 90.0 Unhealthy

Air Quality Analysis

Monitor AQS ID Air Quality Analysis
060658001

Hourly Ozone Analysis

At Riverside - Rubidoux, hourly ozone concentrations showed an increasing trend on July 29 and July 30. O3 levels exceeded 70 ppb on 5 occasions, occurring at: July 29, 11:00 AM, July 29, 12:00 PM, July 29, 01:00 PM, July 29, 02:00 PM, July 29, 03:00 PM. Among these exceedances, 1 were significant pollution spikes (peaks), recorded at: July 29, 01:00 PM. Hourly ozone levels showed a distinct day-night pattern. The highest recorded ozone concentration was 86.0 ppb at July 29, 01:00 PM, while the lowest was 15.0 ppb at July 29, 04:00 AM. Unusual ozone spikes detected at: July 29, 01:00 PM.


Daily ozone Analysis of the Year

Throughout 2026, ozone levels at Riverside - Rubidoux exceeded 70 ppb on 43 days, which accounts for 11.8% of the year. On July 29, 2026, the ozone concentration reached 74.0 ppb, ranking #25 among exceedance events this year. The highest ozone exceedance this year was 101.0 ppb on March 20, 2026, which was 27.0 ppb higher than this event. The majority of exceedance events occurred in July, with 15 occurrences. The season with the highest exceedance frequency was Summer, accounting for 23 exceedance days.


Historical daily Ozone Analysis

Between 2022 and 2026, ozone levels at Riverside - Rubidoux exceeded the 70 ppb daily standard most frequently during Spring, accounting for 27.7% of all exceedances. The month with the highest number of exceedances was July, making up 9.5% of the total. The exceedance recorded on July 29, 2026 at Riverside - Rubidoux reached 74.0 ppb, which is 18.9 ppb higher than the average Spring ozone level of 55.1 ppb. This exceedance is notable but does not rank in the top 10 highest exceedances recorded from 2022 to 2026. These exceedances are often influenced by seasonal factors such as wildfires, prescribed burns, stagnant air, temperature inversions, or increased local emissions.


060658005

Hourly Ozone Analysis

At Mira Loma - Van Buren, hourly ozone concentrations showed an increasing trend on July 29 and July 30. O3 levels exceeded 70 ppb on 5 occasions, occurring at: July 29, 10:00 AM, July 29, 11:00 AM, July 29, 12:00 PM, July 29, 01:00 PM, July 29, 02:00 PM. Among these exceedances, 1 were significant pollution spikes (peaks), recorded at: July 29, 01:00 PM. Hourly ozone levels showed a distinct day-night pattern. The highest recorded ozone concentration was 88.0 ppb at July 29, 01:00 PM, while the lowest was 20.0 ppb at July 29, 02:00 AM. Unusual ozone spikes detected at: July 29, 01:00 PM.


Daily ozone Analysis of the Year

Throughout 2026, ozone levels at Mira Loma - Van Buren exceeded 70 ppb on 38 days, which accounts for 10.4% of the year. On July 29, 2026, the ozone concentration reached 75.0 ppb, ranking #19 among exceedance events this year. The highest ozone exceedance this year was 99.0 ppb on March 20, 2026, which was 24.0 ppb higher than this event. The majority of exceedance events occurred in July, with 14 occurrences. The season with the highest exceedance frequency was Summer, accounting for 19 exceedance days.


Historical daily Ozone Analysis

Between 2022 and 2026, ozone levels at Mira Loma - Van Buren exceeded the 70 ppb daily standard most frequently during Spring, accounting for 27.4% of all exceedances. The month with the highest number of exceedances was July, making up 9.5% of the total. The exceedance recorded on July 29, 2026 at Mira Loma - Van Buren reached 75.0 ppb, which is 20.4 ppb higher than the average Spring ozone level of 54.6 ppb. This exceedance is notable but does not rank in the top 10 highest exceedances recorded from 2022 to 2026. These exceedances are often influenced by seasonal factors such as wildfires, prescribed burns, stagnant air, temperature inversions, or increased local emissions.


060370016

Hourly Ozone Analysis

At Glendora - Laurel, hourly ozone concentrations showed an increasing trend on July 29 and July 30. O3 levels exceeded 70 ppb on 5 occasions, occurring at: July 29, 11:00 AM, July 29, 12:00 PM, July 29, 01:00 PM, July 29, 02:00 PM, July 29, 03:00 PM. No significant pollution spikes were observed during this period. Hourly ozone levels showed a distinct day-night pattern. The highest recorded ozone concentration was 95.0 ppb at July 29, 03:00 PM, while the lowest was 15.0 ppb at July 29, 01:00 AM. Unusual ozone spikes detected at: July 29, 03:00 PM.


Daily ozone Analysis of the Year

Throughout 2026, ozone levels at Glendora - Laurel exceeded 70 ppb on 53 days, which accounts for 14.5% of the year. On July 29, 2026, the ozone concentration reached 77.0 ppb, ranking #25 among exceedance events this year. The highest ozone exceedance this year was 109.0 ppb on March 20, 2026, which was 32.0 ppb higher than this event. The majority of exceedance events occurred in July, with 16 occurrences. The season with the highest exceedance frequency was Spring, accounting for 26 exceedance days.


Historical daily Ozone Analysis

Between 2022 and 2026, ozone levels at Glendora - Laurel exceeded the 70 ppb daily standard most frequently during Spring, accounting for 26.6% of all exceedances. The month with the highest number of exceedances was July, making up 9.5% of the total. The exceedance recorded on July 29, 2026 at Glendora - Laurel reached 77.0 ppb, which is 22.6 ppb higher than the average Spring ozone level of 54.4 ppb. This exceedance is notable but does not rank in the top 10 highest exceedances recorded from 2022 to 2026. These exceedances are often influenced by seasonal factors such as wildfires, prescribed burns, stagnant air, temperature inversions, or increased local emissions.


060372005

Hourly Ozone Analysis

At Pasadena, hourly ozone concentrations showed an increasing trend on July 29 and July 30. O3 levels exceeded 70 ppb on 5 occasions, occurring at: July 29, 11:00 AM, July 29, 12:00 PM, July 29, 01:00 PM, July 29, 02:00 PM, July 29, 03:00 PM. Among these exceedances, 1 were significant pollution spikes (peaks), recorded at: July 29, 01:00 PM. Hourly ozone levels showed a distinct day-night pattern. The highest recorded ozone concentration was 88.0 ppb at July 29, 01:00 PM, while the lowest was 6.0 ppb at July 29, 12:00 AM. Unusual ozone spikes detected at: July 29, 01:00 PM.


Daily ozone Analysis of the Year

Throughout 2026, ozone levels at Pasadena exceeded 70 ppb on 27 days, which accounts for 7.4% of the year. On July 29, 2026, the ozone concentration reached 72.0 ppb, ranking #20 among exceedance events this year. The highest ozone exceedance this year was 101.0 ppb on March 19, 2026, which was 29.0 ppb higher than this event. The majority of exceedance events occurred in March, with 10 occurrences. The season with the highest exceedance frequency was Spring, accounting for 15 exceedance days.


Historical daily Ozone Analysis

Between 2022 and 2026, ozone levels at Pasadena exceeded the 70 ppb daily standard most frequently during Spring, accounting for 27.8% of all exceedances. The month with the highest number of exceedances was May, making up 9.4% of the total. The exceedance recorded on July 29, 2026 at Pasadena reached 72.0 ppb, which is 21.8 ppb higher than the average Spring ozone level of 50.2 ppb. This exceedance is notable but does not rank in the top 10 highest exceedances recorded from 2022 to 2026. These exceedances are often influenced by seasonal factors such as wildfires, prescribed burns, stagnant air, temperature inversions, or increased local emissions.


060710005

Hourly Ozone Analysis

At Crestline - Lake Gregory, hourly ozone concentrations showed an increasing trend on July 29 and July 30. O3 levels exceeded 70 ppb on 5 occasions, occurring at: July 29, 11:00 AM, July 29, 12:00 PM, July 29, 01:00 PM, July 29, 02:00 PM, July 29, 03:00 PM. Among these exceedances, 1 were significant pollution spikes (peaks), recorded at: July 29, 01:00 PM. Hourly ozone levels showed a distinct day-night pattern. The highest recorded ozone concentration was 98.0 ppb at July 29, 03:00 PM, while the lowest was 51.0 ppb at July 29, 05:00 AM. Unusual ozone spikes detected at: July 29, 03:00 PM.


Daily ozone Analysis of the Year

Throughout 2026, ozone levels at Crestline - Lake Gregory exceeded 70 ppb on 65 days, which accounts for 17.8% of the year. On July 29, 2026, the ozone concentration reached 80.0 ppb, ranking #32 among exceedance events this year. The highest ozone exceedance this year was 98.0 ppb on July 15, 2026, which was 18.0 ppb higher than this event. The majority of exceedance events occurred in July, with 21 occurrences. The season with the highest exceedance frequency was Summer, accounting for 38 exceedance days.


Historical daily Ozone Analysis

Between 2022 and 2026, ozone levels at Crestline - Lake Gregory exceeded the 70 ppb daily standard most frequently during Spring, accounting for 27.8% of all exceedances. The month with the highest number of exceedances was May, making up 9.4% of the total. The exceedance recorded on July 29, 2026 at Crestline - Lake Gregory reached 80.0 ppb, which is 21.8 ppb higher than the average Spring ozone level of 58.2 ppb. This exceedance is notable but does not rank in the top 10 highest exceedances recorded from 2022 to 2026. These exceedances are often influenced by seasonal factors such as wildfires, prescribed burns, stagnant air, temperature inversions, or increased local emissions.


060710306

Hourly Ozone Analysis

At Victorville - Park Avenue, hourly ozone concentrations showed an increasing trend on July 29 and July 30. O3 levels exceeded 70 ppb on 4 occasions, occurring at: July 29, 12:00 PM, July 29, 01:00 PM, July 29, 02:00 PM, July 29, 03:00 PM. Among these exceedances, 1 were significant pollution spikes (peaks), recorded at: July 29, 01:00 PM. Hourly ozone levels showed a distinct day-night pattern. The highest recorded ozone concentration was 84.0 ppb at July 29, 03:00 PM, while the lowest was 23.0 ppb at July 29, 05:00 AM. Unusual ozone spikes detected at: July 29, 03:00 PM.


Daily ozone Analysis of the Year

Throughout 2026, ozone levels at Victorville - Park Avenue exceeded 70 ppb on 23 days, which accounts for 6.3% of the year. On July 29, 2026, the ozone concentration reached 71.0 ppb, ranking #21 among exceedance events this year. The highest ozone exceedance this year was 83.0 ppb on July 27, 2026, which was 12.0 ppb higher than this event. The majority of exceedance events occurred in May, with 7 occurrences. The season with the highest exceedance frequency was Summer, accounting for 13 exceedance days.


Historical daily Ozone Analysis

Between 2022 and 2026, ozone levels at Victorville - Park Avenue exceeded the 70 ppb daily standard most frequently during Spring, accounting for 27.5% of all exceedances. The month with the highest number of exceedances was May, making up 9.4% of the total. The exceedance recorded on July 29, 2026 at Victorville - Park Avenue reached 71.0 ppb, which is 14.8 ppb higher than the average Spring ozone level of 56.2 ppb. This exceedance is notable but does not rank in the top 10 highest exceedances recorded from 2022 to 2026. These exceedances are often influenced by seasonal factors such as wildfires, prescribed burns, stagnant air, temperature inversions, or increased local emissions.


060714001

Hourly Ozone Analysis

At Hesperia - Olive Street, hourly ozone concentrations showed an increasing trend on July 29 and July 30. O3 levels exceeded 70 ppb on 5 occasions, occurring at: July 29, 11:00 AM, July 29, 12:00 PM, July 29, 01:00 PM, July 29, 02:00 PM, July 29, 03:00 PM. No significant pollution spikes were observed during this period. Hourly ozone levels showed a distinct day-night pattern. The highest recorded ozone concentration was 84.0 ppb at July 29, 03:00 PM, while the lowest was 36.0 ppb at July 29, 05:00 AM. Unusual ozone spikes detected at: July 29, 03:00 PM.


Daily ozone Analysis of the Year

Throughout 2026, ozone levels at Hesperia - Olive Street exceeded 70 ppb on 33 days, which accounts for 9.0% of the year. On July 29, 2026, the ozone concentration reached 72.0 ppb, ranking #23 among exceedance events this year. The highest ozone exceedance this year was 84.0 ppb on June 05, 2026, which was 12.0 ppb higher than this event. The majority of exceedance events occurred in June, with 12 occurrences. The season with the highest exceedance frequency was Summer, accounting for 23 exceedance days.


Historical daily Ozone Analysis

Between 2022 and 2026, ozone levels at Hesperia - Olive Street exceeded the 70 ppb daily standard most frequently during Spring, accounting for 27.4% of all exceedances. The month with the highest number of exceedances was May, making up 9.4% of the total. The exceedance recorded on July 29, 2026 at Hesperia - Olive Street reached 72.0 ppb, which is 16.8 ppb higher than the average Spring ozone level of 55.2 ppb. This exceedance is notable but does not rank in the top 10 highest exceedances recorded from 2022 to 2026. These exceedances are often influenced by seasonal factors such as wildfires, prescribed burns, stagnant air, temperature inversions, or increased local emissions.


060719004

Hourly Ozone Analysis

At San Bernadino - 4th Street, hourly ozone concentrations showed an increasing trend on July 29 and July 30. O3 levels exceeded 70 ppb on 5 occasions, occurring at: July 29, 11:00 AM, July 29, 12:00 PM, July 29, 01:00 PM, July 29, 02:00 PM, July 29, 03:00 PM. Among these exceedances, 1 were significant pollution spikes (peaks), recorded at: July 29, 12:00 PM. Hourly ozone levels showed a distinct day-night pattern. The highest recorded ozone concentration was 97.0 ppb at July 29, 03:00 PM, while the lowest was 10.0 ppb at July 29, 02:00 AM. Unusual ozone spikes detected at: July 29, 03:00 PM.


Daily ozone Analysis of the Year

Throughout 2026, ozone levels at San Bernadino - 4th Street exceeded 70 ppb on 52 days, which accounts for 14.2% of the year. On July 29, 2026, the ozone concentration reached 74.0 ppb, ranking #42 among exceedance events this year. The highest ozone exceedance this year was 106.0 ppb on March 20, 2026, which was 32.0 ppb higher than this event. The majority of exceedance events occurred in July, with 19 occurrences. The season with the highest exceedance frequency was Summer, accounting for 32 exceedance days.


Historical daily Ozone Analysis

Between 2022 and 2026, ozone levels at San Bernadino - 4th Street exceeded the 70 ppb daily standard most frequently during Spring, accounting for 28.2% of all exceedances. The month with the highest number of exceedances was July, making up 9.7% of the total. The exceedance recorded on July 29, 2026 at San Bernadino - 4th Street reached 74.0 ppb, which is 17.6 ppb higher than the average Spring ozone level of 56.4 ppb. This exceedance is notable but does not rank in the top 10 highest exceedances recorded from 2022 to 2026. These exceedances are often influenced by seasonal factors such as wildfires, prescribed burns, stagnant air, temperature inversions, or increased local emissions.


060714003

Hourly Ozone Analysis

At Redlands - Dearborn, hourly ozone concentrations showed an increasing trend on July 29 and July 30. O3 levels exceeded 70 ppb on 6 occasions, occurring at: July 29, 10:00 AM, July 29, 11:00 AM, July 29, 12:00 PM, July 29, 01:00 PM, July 29, 02:00 PM, July 29, 03:00 PM. Among these exceedances, 1 were significant pollution spikes (peaks), recorded at: July 29, 12:00 PM. Hourly ozone levels showed a distinct day-night pattern. The highest recorded ozone concentration was 100.0 ppb at July 29, 12:00 PM, while the lowest was 9.0 ppb at July 29, 05:00 AM. Unusual ozone spikes detected at: July 29, 12:00 PM.


Daily ozone Analysis of the Year

Throughout 2026, ozone levels at Redlands - Dearborn exceeded 70 ppb on 57 days, which accounts for 15.6% of the year. On July 29, 2026, the ozone concentration reached 84.0 ppb, ranking #23 among exceedance events this year. The highest ozone exceedance this year was 99.0 ppb on July 09, 2026, which was 15.0 ppb higher than this event. The majority of exceedance events occurred in July, with 20 occurrences. The season with the highest exceedance frequency was Summer, accounting for 34 exceedance days.


Historical daily Ozone Analysis

Between 2022 and 2026, ozone levels at Redlands - Dearborn exceeded the 70 ppb daily standard most frequently during Spring, accounting for 27.6% of all exceedances. The month with the highest number of exceedances was January, making up 9.4% of the total. The exceedance recorded on July 29, 2026 at Redlands - Dearborn reached 84.0 ppb, which is 27.0 ppb higher than the average Spring ozone level of 57.0 ppb. This exceedance is notable but does not rank in the top 10 highest exceedances recorded from 2022 to 2026. These exceedances are often influenced by seasonal factors such as wildfires, prescribed burns, stagnant air, temperature inversions, or increased local emissions.



Average Hourly Ozone for Days Around Event



Historical Daily Maximum 8-Hour Ozone Concentration

Timeseries for 060658001

Time series plot of daily maximum 8-Hour ozone concentrations at Riverside - Rubidoux for each year between 2022 and 2026. The colored dots represent the daily maximum 8-Hour ozone concentrations on July 29, 2026. The black line indicates the 5-year average daily maximum 8-Hour ozone concentration, and the grey dashed line represents the 70 ppb daily ozone standard.

Timeseries for 060658005

Time series plot of daily maximum 8-Hour ozone concentrations at Mira Loma - Van Buren for each year between 2022 and 2026. The colored dots represent the daily maximum 8-Hour ozone concentrations on July 29, 2026. The black line indicates the 5-year average daily maximum 8-Hour ozone concentration, and the grey dashed line represents the 70 ppb daily ozone standard.

Timeseries for 060370016

Time series plot of daily maximum 8-Hour ozone concentrations at Glendora - Laurel for each year between 2022 and 2026. The colored dots represent the daily maximum 8-Hour ozone concentrations on July 29, 2026. The black line indicates the 5-year average daily maximum 8-Hour ozone concentration, and the grey dashed line represents the 70 ppb daily ozone standard.

Timeseries for 060372005

Time series plot of daily maximum 8-Hour ozone concentrations at Pasadena for each year between 2022 and 2026. The colored dots represent the daily maximum 8-Hour ozone concentrations on July 29, 2026. The black line indicates the 5-year average daily maximum 8-Hour ozone concentration, and the grey dashed line represents the 70 ppb daily ozone standard.

Timeseries for 060710005

Time series plot of daily maximum 8-Hour ozone concentrations at Crestline - Lake Gregory for each year between 2022 and 2026. The colored dots represent the daily maximum 8-Hour ozone concentrations on July 29, 2026. The black line indicates the 5-year average daily maximum 8-Hour ozone concentration, and the grey dashed line represents the 70 ppb daily ozone standard.

Timeseries for 060710306

Time series plot of daily maximum 8-Hour ozone concentrations at Victorville - Park Avenue for each year between 2022 and 2026. The colored dots represent the daily maximum 8-Hour ozone concentrations on July 29, 2026. The black line indicates the 5-year average daily maximum 8-Hour ozone concentration, and the grey dashed line represents the 70 ppb daily ozone standard.

Timeseries for 060714001

Time series plot of daily maximum 8-Hour ozone concentrations at Hesperia - Olive Street for each year between 2022 and 2026. The colored dots represent the daily maximum 8-Hour ozone concentrations on July 29, 2026. The black line indicates the 5-year average daily maximum 8-Hour ozone concentration, and the grey dashed line represents the 70 ppb daily ozone standard.

Timeseries for 060719004

Time series plot of daily maximum 8-Hour ozone concentrations at San Bernadino - 4th Street for each year between 2022 and 2026. The colored dots represent the daily maximum 8-Hour ozone concentrations on July 29, 2026. The black line indicates the 5-year average daily maximum 8-Hour ozone concentration, and the grey dashed line represents the 70 ppb daily ozone standard.

Timeseries for 060714003

Time series plot of daily maximum 8-Hour ozone concentrations at Redlands - Dearborn for each year between 2022 and 2026. The colored dots represent the daily maximum 8-Hour ozone concentrations on July 29, 2026. The black line indicates the 5-year average daily maximum 8-Hour ozone concentration, and the grey dashed line represents the 70 ppb daily ozone standard.


Prescribed Fires within 50 Miles

Monitor AQS ID On the Day One Day Before Two Days Before
060658001
  • No fires
  • No fires
  • No fires
060658005
  • No fires
  • No fires
  • No fires
060370016
  • No fires
  • No fires
  • No fires
060372005
  • No fires
  • No fires
  • No fires
060710005
  • No fires
  • No fires
  • No fires
060710306
  • No fires
  • No fires
  • No fires
060714001
  • No fires
  • No fires
  • No fires
060719004
  • No fires
  • No fires
  • No fires
060714003
  • No fires
  • No fires
  • No fires

Wildfires within 100 Miles

Monitor AQS ID 2-Day Range to Exceedance Date
060658001
  • Wildfire: Keller Fire
    Acres Burned: 10.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 1:22 p.m.
  • Wildfire: Fish Fire
    Acres Burned: 4201.00
    Date Created: July 27, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 5:40 p.m.
  • Wildfire: Tin Fire
    Acres Burned: 37.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 12:45 a.m.
  • Wildfire: Green Fire
    Acres Burned: 55.00
    Date Created: July 28, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 8:58 p.m.
060658005
  • Wildfire: Keller Fire
    Acres Burned: 10.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 1:22 p.m.
  • Wildfire: Fish Fire
    Acres Burned: 4201.00
    Date Created: July 27, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 5:40 p.m.
  • Wildfire: Tin Fire
    Acres Burned: 37.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 12:45 a.m.
  • Wildfire: Green Fire
    Acres Burned: 55.00
    Date Created: July 28, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 8:58 p.m.
060370016
  • Wildfire: Keller Fire
    Acres Burned: 10.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 1:22 p.m.
  • Wildfire: Fish Fire
    Acres Burned: 4201.00
    Date Created: July 27, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 5:40 p.m.
  • Wildfire: Tin Fire
    Acres Burned: 37.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 12:45 a.m.
  • Wildfire: Green Fire
    Acres Burned: 55.00
    Date Created: July 28, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 8:58 p.m.
060372005
  • Wildfire: Keller Fire
    Acres Burned: 10.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 1:22 p.m.
  • Wildfire: Fish Fire
    Acres Burned: 4201.00
    Date Created: July 27, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 5:40 p.m.
  • Wildfire: Tin Fire
    Acres Burned: 37.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 12:45 a.m.
  • Wildfire: Green Fire
    Acres Burned: 55.00
    Date Created: July 28, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 8:58 p.m.
060710005
  • Wildfire: Keller Fire
    Acres Burned: 10.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 1:22 p.m.
  • Wildfire: Fish Fire
    Acres Burned: 4201.00
    Date Created: July 27, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 5:40 p.m.
  • Wildfire: Tin Fire
    Acres Burned: 37.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 12:45 a.m.
  • Wildfire: Green Fire
    Acres Burned: 55.00
    Date Created: July 28, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 8:58 p.m.
060710306
  • Wildfire: Keller Fire
    Acres Burned: 10.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 1:22 p.m.
  • Wildfire: Fish Fire
    Acres Burned: 4201.00
    Date Created: July 27, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 5:40 p.m.
  • Wildfire: Tin Fire
    Acres Burned: 37.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 12:45 a.m.
  • Wildfire: Green Fire
    Acres Burned: 55.00
    Date Created: July 28, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 8:58 p.m.
060714001
  • Wildfire: Keller Fire
    Acres Burned: 10.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 1:22 p.m.
  • Wildfire: Fish Fire
    Acres Burned: 4201.00
    Date Created: July 27, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 5:40 p.m.
  • Wildfire: Tin Fire
    Acres Burned: 37.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 12:45 a.m.
  • Wildfire: Green Fire
    Acres Burned: 55.00
    Date Created: July 28, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 8:58 p.m.
060719004
  • Wildfire: Keller Fire
    Acres Burned: 10.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 1:22 p.m.
  • Wildfire: Fish Fire
    Acres Burned: 4201.00
    Date Created: July 27, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 5:40 p.m.
  • Wildfire: Tin Fire
    Acres Burned: 37.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 12:45 a.m.
  • Wildfire: Green Fire
    Acres Burned: 55.00
    Date Created: July 28, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 8:58 p.m.
060714003
  • Wildfire: Keller Fire
    Acres Burned: 10.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 1:22 p.m.
  • Wildfire: Fish Fire
    Acres Burned: 4201.00
    Date Created: July 27, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 5:40 p.m.
  • Wildfire: Tin Fire
    Acres Burned: 37.00
    Date Created: July 26, 2026
    Date extinguished: July 27, 2026
    Date Last Updated: July 27, 2026, 12:45 a.m.
  • Wildfire: Green Fire
    Acres Burned: 55.00
    Date Created: July 28, 2026
    Date extinguished: None
    Date Last Updated: July 30, 2026, 8:58 p.m.

Fire Emission Analysis

Monitor AQS ID Emission Analysis
060658001

On July 29, 2026, an analysis was conducted to assess the potential impact of nearby fire activity on ozone levels at Riverside - Rubidoux. 3 wildfires were detected within 100 miles of the site from two days before the event to the event day. The proximity of these fires to the site suggests they may have contributed to elevated ozone levels on this date. The following wildfires were identified: Tin Fire, which burned 37.00, started on July 26, 2026, and ended on July 27, 2026. It was located 11.0 miles away. Keller Fire, which burned 10.00, started on July 26, 2026, and ended on July 27, 2026. It was located 29.3 miles away. Green Fire, which burned 55.00, started on July 28, 2026, and last updated on July 29, 2026. It was located 23.4 miles away. No prescribed fires were identified within 50 miles of Riverside - Rubidoux.

In addition to reported prescribed fire and wildfire records from CAL FIRE and the Prescribed Fire Reporting System (PFIRS), satellite imagery detected 173 fire hotspots over the past two days (from two days before the event to the current day) within 100 miles of the site. This indicates ongoing fire activity in the region, which may have contributed to the observed air quality conditions. Satellite data confirms the presence of smoke plumes over the monitoring site, suggesting that emissions from nearby fires were transported into the area, potentially impacting ozone levels.

060658005

On July 29, 2026, an analysis was conducted to assess the potential impact of nearby fire activity on ozone levels at Mira Loma - Van Buren. 3 wildfires were detected within 100 miles of the site from two days before the event to the event day. The proximity of these fires to the site suggests they may have contributed to elevated ozone levels on this date. The following wildfires were identified: Tin Fire, which burned 37.00, started on July 26, 2026, and ended on July 27, 2026. It was located 10.6 miles away. Keller Fire, which burned 10.00, started on July 26, 2026, and ended on July 27, 2026. It was located 31.5 miles away. Green Fire, which burned 55.00, started on July 28, 2026, and last updated on July 29, 2026. It was located 27.7 miles away. No prescribed fires were identified within 50 miles of Mira Loma - Van Buren.

In addition to reported prescribed fire and wildfire records from CAL FIRE and the Prescribed Fire Reporting System (PFIRS), satellite imagery detected 173 fire hotspots over the past two days (from two days before the event to the current day) within 100 miles of the site. This indicates ongoing fire activity in the region, which may have contributed to the observed air quality conditions. Satellite data confirms the presence of smoke plumes over the monitoring site, suggesting that emissions from nearby fires were transported into the area, potentially impacting ozone levels.

060370016

On July 29, 2026, an analysis was conducted to assess the potential impact of nearby fire activity on ozone levels at Glendora - Laurel. 4 wildfires were detected within 100 miles of the site from two days before the event to the event day. The proximity of these fires to the site suggests they may have contributed to elevated ozone levels on this date. The following wildfires were identified: Tin Fire, which burned 37.00, started on July 26, 2026, and ended on July 27, 2026. It was located 30.3 miles away. Keller Fire, which burned 10.00, started on July 26, 2026, and ended on July 27, 2026. It was located 52.8 miles away. Fish Fire, which burned 4201.00, started on July 27, 2026, and last updated on July 29, 2026. It was located 92.6 miles away. Green Fire, which burned 55.00, started on July 28, 2026, and last updated on July 29, 2026. It was located 47.4 miles away. No prescribed fires were identified within 50 miles of Glendora - Laurel.

In addition to reported prescribed fire and wildfire records from CAL FIRE and the Prescribed Fire Reporting System (PFIRS), satellite imagery detected 3799 fire hotspots over the past two days (from two days before the event to the current day) within 100 miles of the site. This indicates ongoing fire activity in the region, which may have contributed to the observed air quality conditions. Satellite data confirms the presence of smoke plumes over the monitoring site, suggesting that emissions from nearby fires were transported into the area, potentially impacting ozone levels.

060372005

On July 29, 2026, an analysis was conducted to assess the potential impact of nearby fire activity on ozone levels at Pasadena. 4 wildfires were detected within 100 miles of the site from two days before the event to the event day. The proximity of these fires to the site suggests they may have contributed to elevated ozone levels on this date. The following wildfires were identified: Tin Fire, which burned 37.00, started on July 26, 2026, and ended on July 27, 2026. It was located 42.9 miles away. Keller Fire, which burned 10.00, started on July 26, 2026, and ended on July 27, 2026. It was located 65.0 miles away. Fish Fire, which burned 4201.00, started on July 27, 2026, and last updated on July 29, 2026. It was located 86.5 miles away. Green Fire, which burned 55.00, started on July 28, 2026, and last updated on July 29, 2026. It was located 63.1 miles away. No prescribed fires were identified within 50 miles of Pasadena.

In addition to reported prescribed fire and wildfire records from CAL FIRE and the Prescribed Fire Reporting System (PFIRS), satellite imagery detected 3799 fire hotspots over the past two days (from two days before the event to the current day) within 100 miles of the site. This indicates ongoing fire activity in the region, which may have contributed to the observed air quality conditions. Satellite data confirms the presence of smoke plumes over the monitoring site, suggesting that emissions from nearby fires were transported into the area, potentially impacting ozone levels.

060710005

On July 29, 2026, an analysis was conducted to assess the potential impact of nearby fire activity on ozone levels at Crestline - Lake Gregory. 3 wildfires were detected within 100 miles of the site from two days before the event to the event day. The proximity of these fires to the site suggests they may have contributed to elevated ozone levels on this date. The following wildfires were identified: Tin Fire, which burned 37.00, started on July 26, 2026, and ended on July 27, 2026. It was located 29.6 miles away. Keller Fire, which burned 10.00, started on July 26, 2026, and ended on July 27, 2026. It was located 43.0 miles away. Green Fire, which burned 55.00, started on July 28, 2026, and last updated on July 29, 2026. It was located 17.3 miles away. No prescribed fires were identified within 50 miles of Crestline - Lake Gregory.

In addition to reported prescribed fire and wildfire records from CAL FIRE and the Prescribed Fire Reporting System (PFIRS), satellite imagery detected 192 fire hotspots over the past two days (from two days before the event to the current day) within 100 miles of the site. This indicates ongoing fire activity in the region, which may have contributed to the observed air quality conditions. Satellite data confirms the presence of smoke plumes over the monitoring site, suggesting that emissions from nearby fires were transported into the area, potentially impacting ozone levels.

060710306

On July 29, 2026, an analysis was conducted to assess the potential impact of nearby fire activity on ozone levels at Victorville - Park Avenue. 4 wildfires were detected within 100 miles of the site from two days before the event to the event day. The proximity of these fires to the site suggests they may have contributed to elevated ozone levels on this date. The following wildfires were identified: Tin Fire, which burned 37.00, started on July 26, 2026, and ended on July 27, 2026. It was located 46.7 miles away. Keller Fire, which burned 10.00, started on July 26, 2026, and ended on July 27, 2026. It was located 61.7 miles away. Fish Fire, which burned 4201.00, started on July 27, 2026, and last updated on July 29, 2026. It was located 93.7 miles away. Green Fire, which burned 55.00, started on July 28, 2026, and last updated on July 29, 2026. It was located 33.2 miles away. No prescribed fires were identified within 50 miles of Victorville - Park Avenue.

In addition to reported prescribed fire and wildfire records from CAL FIRE and the Prescribed Fire Reporting System (PFIRS), satellite imagery detected 3795 fire hotspots over the past two days (from two days before the event to the current day) within 100 miles of the site. This indicates ongoing fire activity in the region, which may have contributed to the observed air quality conditions. Satellite data confirms the presence of smoke plumes over the monitoring site, suggesting that emissions from nearby fires were transported into the area, potentially impacting ozone levels.

060714001

On July 29, 2026, an analysis was conducted to assess the potential impact of nearby fire activity on ozone levels at Hesperia - Olive Street. 4 wildfires were detected within 100 miles of the site from two days before the event to the event day. The proximity of these fires to the site suggests they may have contributed to elevated ozone levels on this date. The following wildfires were identified: Tin Fire, which burned 37.00, started on July 26, 2026, and ended on July 27, 2026. It was located 40.8 miles away. Keller Fire, which burned 10.00, started on July 26, 2026, and ended on July 27, 2026. It was located 54.9 miles away. Fish Fire, which burned 4201.00, started on July 27, 2026, and last updated on July 29, 2026. It was located 99.5 miles away. Green Fire, which burned 55.00, started on July 28, 2026, and last updated on July 29, 2026. It was located 26.5 miles away. No prescribed fires were identified within 50 miles of Hesperia - Olive Street.

In addition to reported prescribed fire and wildfire records from CAL FIRE and the Prescribed Fire Reporting System (PFIRS), satellite imagery detected 2656 fire hotspots over the past two days (from two days before the event to the current day) within 100 miles of the site. This indicates ongoing fire activity in the region, which may have contributed to the observed air quality conditions. Satellite data confirms the presence of smoke plumes over the monitoring site, suggesting that emissions from nearby fires were transported into the area, potentially impacting ozone levels.

060719004

On July 29, 2026, an analysis was conducted to assess the potential impact of nearby fire activity on ozone levels at San Bernadino - 4th Street. 3 wildfires were detected within 100 miles of the site from two days before the event to the event day. The proximity of these fires to the site suggests they may have contributed to elevated ozone levels on this date. The following wildfires were identified: Tin Fire, which burned 37.00, started on July 26, 2026, and ended on July 27, 2026. It was located 21.1 miles away. Keller Fire, which burned 10.00, started on July 26, 2026, and ended on July 27, 2026. It was located 33.7 miles away. Green Fire, which burned 55.00, started on July 28, 2026, and last updated on July 29, 2026. It was located 14.3 miles away. No prescribed fires were identified within 50 miles of San Bernadino - 4th Street.

In addition to reported prescribed fire and wildfire records from CAL FIRE and the Prescribed Fire Reporting System (PFIRS), satellite imagery detected 192 fire hotspots over the past two days (from two days before the event to the current day) within 100 miles of the site. This indicates ongoing fire activity in the region, which may have contributed to the observed air quality conditions. Satellite data confirms the presence of smoke plumes over the monitoring site, suggesting that emissions from nearby fires were transported into the area, potentially impacting ozone levels.

060714003

On July 29, 2026, an analysis was conducted to assess the potential impact of nearby fire activity on ozone levels at Redlands - Dearborn. 3 wildfires were detected within 100 miles of the site from two days before the event to the event day. The proximity of these fires to the site suggests they may have contributed to elevated ozone levels on this date. The following wildfires were identified: Tin Fire, which burned 37.00, started on July 26, 2026, and ended on July 27, 2026. It was located 23.4 miles away. Keller Fire, which burned 10.00, started on July 26, 2026, and ended on July 27, 2026. It was located 29.9 miles away. Green Fire, which burned 55.00, started on July 28, 2026, and last updated on July 29, 2026. It was located 7.5 miles away. No prescribed fires were identified within 50 miles of Redlands - Dearborn.

In addition to reported prescribed fire and wildfire records from CAL FIRE and the Prescribed Fire Reporting System (PFIRS), satellite imagery detected 211 fire hotspots over the past two days (from two days before the event to the current day) within 100 miles of the site. This indicates ongoing fire activity in the region, which may have contributed to the observed air quality conditions. Satellite data confirms the presence of smoke plumes over the monitoring site, suggesting that emissions from nearby fires were transported into the area, potentially impacting ozone levels.



High-Split Trajectory for Ozone Exceedance Monitor Site