Tag Archive for: California

Air Pollution in the Bay Area’s Refinery Corridor

Emissions from Refineries and other Sources
By
Kyle Ferrar, Western Program Coordinator &
Kirk Jalbert, Manager of Community Based Research & Engagement

Key Takeaways

  • Refineries and petrochemical industry in the Bay Area’s refinery corridor are responsible for the majority of the risk-driving point source emissions in this region.
  • The Chevron Richmond refinery has the largest refining capacity and emits the most hazardous air pollutants (HAPs).
  • The Tesoro refinery in Martinez and the Shell refinery in Martinez emit the most HAPs per barrel of oil (based on refining capacity).
  • The Valero refinery in Benicia, the Tesoro refinery in Martinez, and the Shell refinery in Martinez emit the most criteria air pollutants (CAPs).
  • If refineries increase their capacity and process more crude, the emissions of these various pollutants will invariably increase.
  • New emissions rules need to prioritize ambient air quality and hold the Air District and elected officials accountable for policies that increase risk.

Overview of the Bay Area’s Refinery Corridor

The Bay Area Air Quality Management District is revising the rules for facilities that emit a variety of hazardous pollutants into the air. The current draft of the new rules could actually increase the amount polluters are allowed to emit. The communities at risk are speaking out to support policies that would reduce the amount of air pollutants rather than increase the limits. In support of these communities, the FracTracker Alliance has focused on analyzing the sources of air pollutants in the region. The East Bay Oil Refinery Corridor is located along the North Shore of the East Bay, stretching from Richmond, CA east to Antioch, CA. The region has been named a “sacrifice zone” for the heavy concentration of petrochemical industrial sites. In addition to the five refineries along the north coast, these communities host a variety of other heavy industries and waste sites. The locations of these facilities have been mapped previously by the FracTracker Alliance, here. In the report we found that people of color, specifically African Americans, are disproportionately represented in the community demographics. Novel results indicate that Hispanic students may be disproportionately impacted by the presence of the petrochemical industry. In this post, we continue the analysis of risk in the region by providing an analysis of the contributions to air pollution from these facilities.

Regulations

Refineries and other sources of air pollution are regulated by the U.S. EPA’s Clean Air Act (CAA). The CAA regulates two classes of pollutants:

  1. Criteria air pollutants (CAPs) – including sulfur dioxide, oxides of nitrogen, carbon monoxide, and particulate matter; and
  2. Hazardous air pollutants (HAPs), which includes a list of 594 carcinogenic and non-carcinogenic chemicals that pose a risk to those exposed.

In addition, California regulates green-house-gas (GHG) emissions, and refineries are the second largest industrial source of GHGs. These regulations get applied when facilities need to obtain a permit for a new source of air pollution, or if a facility is making a structural change that could significantly affect emissions. Facilities are required to use “Maximum Available Control Technology” as it relates to industry best practices to control emissions. With these existing engineering controls, refinery emissions are released into the air from the multiple sources/processes shown below in Figure 1. Notice that a large amount of emissions are simply from “Leaks.”

Sources of Refinery HAPs

Figure 1. Breakdown of emissions from petroleum refineries (US EPA, 2011)

The new rules drafted by the BAAQMD to regulate emissions from the East Bay Oil Refinery Corridor would not cap emissions at any level. The current proposal outlines limits on emissions per barrel, promoting efficiency rather than focusing on emissions reductions. Air quality in the refinery corridor could be improved only if this approach was proposed in conjunction with emission limits or reductions. But as the currently proposed rules stand, emissions could actually increase. Enforcement procedures for infractions are also limited. If a refinery’s emissions violate the per barrel standards, the refinery has a whole 3 years to address the violation. Also, these new rules come at a time when refineries are moving to increase the volume of crude coming in from other regions, such as Canada’s tar sands and the Bakken Shale. These regions produce much lower “quality” crude oil, with much higher emissions. This all amounts to more air pollution rather than less.

Community and environmental activist groups such as the Communities for a Better Environment (CBE) and the Bay Area Refinery Corridor Coalition have raised specific issues with the proposed rules as they stand. First, they allow for increase emissions when Air District data forecasts increasing refinery emissions, despite declining local and domestic fuels demand. Refining the lower quality crude is more energy intensive, which also results in increased emissions. In order to offset the increased emissions, CBE reports that refineries can just increase total refining production to decrease per barrel averages. This would in affect increase emissions to meet regulatory requirements. In addition, transporting the crude via new shipping routes would put additional communities at elevated risk of railway accidents (CBE, 2015).

Ambient Air Quality

Air quality in the Bay Area has been continuously improving over the last few decades, but these refinery communities are still at a significantly higher risk of dying from heart disease and strokes. The largest disparity is felt by the African-American populations. Data for Richmond, CA shows they are 1.5 times more likely to die from these diseases than the Contra Costa county average (Casanova, Diemoz, Lifshay, McKetney, 2010). Emissions reductions not only favor the local communities such as the refinery corridor that are most impacted, but also all of the downwind communities, specifically the Central Valley. The Air District’s 2012 report of PM provides a summary of these trends. PM is an important because it is “the air pollutant that causes by far the greatest harm to public health in the bay area. It is a useful indices because there is a linear correlation between increasing ambient concentrations and mortality. Figure 2 shows the progress the Bay Area has made, overall. This graph is based on regional monitors and not those in the refinery communities, where improvements have not been as drastic. In Figure 3 below, the graph shows major pollutant drivers of seven health risks and how health impacts have been reduced over this time period. What we see from the bar graph, is that non-diesel anthropogenic point sources of PM contribute the most to risk for the majority of health endpoints considered. Across the entire bay area, refineries account for 6% of all PM (BAAQMD, 2012).

An overview of other chemicals associated with the petrochemical industry in ambient air and their resulting health effects are outlined in tables 1-3 below. This is by no means a comprehensive list, but these are chemicals of primary concern, specific to petroleum refinery emissions, and are known risk drivers for the region.

Fig 2 PM

Figure 2. Measurements of PM, averaged across the entire bay area, over time – showing an overall improvement in air quality.

Fig 3 health impacts

Figure 3. Contribution of different species of air pollution to health impacts. The analysis is specific to the bay area and compares health risks estimates from the past (1980s) to estimates in 2012.

Table 1. Health impacts from criteria air pollutants

Criteria Air Pollutants
Compound Health Effect
Sulfur Dioxide (SO2) and Oxides of Nitrogen (NOx) Array of adverse respiratory effects, airway inflammation in healthy people, increased respiratory symptoms in people with asthma
Carbon Monoxide (CO) Harmful health effects associated with the reduction of oxygen delivery to the body’s organs (heart and brain) and tissues
Particulate Matter Increased respiratory symptoms, irritation of the airways, coughing, or difficulty breathing, decreased lung function; aggravated asthma; development of chronic bronchitis; irregular heartbeat; nonfatal heart attacks; and premature death in people with heart or lung disease

Table 2. Health impacts from hazardous air pollutants known to be emitted from petroleum refineries

Hazardous Air Pollutants
Compound Acute Chronic
Benzene, Toluene, Ethylbenzene, Xylenes Neurological effects, Irritation of the eye, skin and respiratory tract Blood disorders (reduced number of red blood cells and aplastic anemia), cancer.
1,3-Butadiene Irritation of the eyes, throat and respiratory tract Cardiovascular effects, leukemia, cancer
Naphthalene Hemolytic anemia, damage to the liver, neurological effects Cataracts, damage to the retina, hemolytic anemia, cancer
PAHs Skin disorders, depression of the immune system Skin disorders (dermatitis, photosensitization), depression of the immune system, damage to the respiratory tract, cataracts, cancer

Table 3. Health impacts from other pollutants emitted from petroleum refineries

Other Pollutants
Compound Mechanism Health Effect
Volatile Organic Compounds (VOC) Combine with NOx in sunlight to create ozone Significantly reduce lung function and induce respiratory inflammation in normal. Healthy people during periods of moderate exercise, symptoms include chest pain, coughing, nausea, and pulmonary congestion
Greenhouse Gases (GHG), including Methane (CH4), Carbon Dioxide (CO2), Nitrous Oxide (N2O) Compounds with high global warming potential contribute to climate change Increase in average temperatures, higher levels of ground-level ozone, increased drought, harm to water resources, ecosystems and wildlife, health risk to sensitive populations

North Coast Emissions

With these gains in ambient air quality it is hard to fathom why regulators would consider allowing refineries to increase emissions inventories. For this analysis, the focus was to map and compare emissions inventories from numerous industrial sites, with a particular focus on the petroleum refineries.

Current refinery capacities as of 2014 are shown in Figure 4, below. The Richmond Chevron has the largest refining capacity in the region, by far. Refining capacity is the maximum amount of crude oil the refinery is allowed to refine, according to their permit. Refining capacity numbers are used in place of actual refined crude volumes for this analysis, because actual crude volumes are considered proprietary information and are not published by the California Energy Commission (CEC).

The Richmond refinery has a raw crude (atmospheric crude is the technical term) refinement capacity over twice as large as the Phillips 66 San Francisco Refinery, and almost 40% larger than the Tesoro (Golden Eagle) refinery, which is the second largest in the region. According to the newly proposed rules, this would allow the Richmond refinery to emit the most pollutants.

The raw total emissions data is shown in Figure 5. The Phillips 66 refinery in Rodeo contributes the least to ambient air quality degradation. The Chevron Richmond refinery processes 40 – 100% more than the four other refineries, and emits 10 – 570% more than the other refiners. This large difference in capacity and emissions means that Chevron Richmond is more efficient than some, but much less efficient than others. To understand the efficiency differences between the refineries, the total HAPs emissions were adjusted by the refining capacity, shown below in Figure 6. With this data we can rank the refining efficiency specifically for HAPs emissions, based on facility capacity. The Tesoro refinery in Martinez and the Shell refinery in Martinez emit the most HAPs per barrel oil (based on refining capacity). From highest emitter to lowest emitter per barrel of crude, the facilities can be ranked:

  1. Tesoro Refining & Marketing Co LLC (Golden Eagle Refinery in Martinez)
  2. Shell Oil Products (Martinez Refinery)
  3. Chevron Products Co Richmond Refinery
  4. Valero Refining Co – California Benicia Refinery
  5. Phillips 66 San Francisco Refinery (Rodeo Refinery)
fig 4 capacity

Figure 4. Operating capacity of refineries. The bars show the maximum amount of crude the refineries are allowed to process daily, in barrels (1 barrel = 42 gallons).

fig 5 total

Figure 5. Total amount of HAPs emissions from East Bay refineries

These refineries along with the other industrial sites in the region have been mapped below in Figure 7. The data has been displayed to show the HAPs emissions from these facilities. The amounts of emissions are shown with graduated circles. The larger the circle, the higher the emissions. The cumulative summation of HAPs is a good value for comparing between facilities with diverse emission inventories (the list of all species of emitted pollutants), but different HAP chemicals have very different effects, both in magnitude and in health impacts. Different chemicals will affect different body systems, as described above in Tables 1-3 above. We have therefore incorporated individual chemical data into the map as well (Figure 7, below). The data displayed shows the total sum of HAPs emitted (in lbs/year) from petrochemical industrial facilities in the region. Explore the map to see emission sources for a selection of important pollutants. Smaller industrial sites/sources have been left out of the map.

Figure 7. Map of the East Bay’s Refinery Corridor with emissions data

California East Bay refinery emissions

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If you open the map into its own page, you can toggle between individual chemical emissions from these facilities. Use the layers tab to change the chemicals displayed. For more information on the individual chemicals, continue reading below.

This unique selection of pollutants was chosen by identifying the highest health risk drivers in the region. They are known to increase both cancer and non-cancer risk for residents in the bay area. The graphs that follow show the emissions inventories reported by each refinery. The refineries are organized on the X –axis according to increasing refining capacity, as they are in Figure 4, above.

Analysis of the graphs show that the Richmond Chevron facility is a largely responsible for 1,2,4-trimethylbenzene, naphthalene, hydrogen cyanide, PAH’s, vanadium, lead and nickel compounds. The Tesoro refinery is mostly responsible for almost all of the 1,3-butadiene, and most responsible for hydrogen sulfide and VOCs. Shell is mostly responsible for the ethylbenzene, much of the mercury and sulfur dioxide emissions, and the most VOCs. Valero in Benicia is responsible for much of the 1,2,4-trimethylbenzene, all BTEX compounds, the most nickel compounds, and the most oxides of nitrogen. And finally, the Phillips 66 refinery in Rodeo with the lowest operating capacity also had the lowest emissions in almost every case except lead, which was very large compared to all refineries except Chevron Richmond. The Valero refinery in Benicia, the Tesoro refinery in Martinez, and the Shell refinery in Martinez emit the most criteria air pollutants (CAPs), including PM2.5 (particulate matter with a diameter less than 2.5 um), sulfur dioxide, and oxides of nitrogen.

Figure 8 – 22. Emissions totals of various air pollutants from East Bay refineries

Marine Terminals

Emissions from marine terminals are also a significant source of HAPs and particulate matter. In the map in Figure 7, the marine terminals are shown with yellow markers. Their relative contributions of total hazardous pollutants are much less than the refineries and other sources, but when we look at specific risk drivers, such as 1,3-butadiene and benzene, we find that their contributions are quite sizable. Marine terminals are also a key component for the refineries looking to access more low-grade crude. Increasing the refining capacity of the refinery will also increase the emissions from the terminals.

The Tesoro Golden Eagle Refinery in Martinez, CA was recently approved for a 30-year lease on a new marine terminal. The new terminal will allow Tesoro to switch to processing lower-cost, lower-quality crude oil from California, Bakken crude, and Canadian tar sands. When crude is transported via ocean liner, besides the issue of air pollution there is the additional risk of an ocean spill. Tom Griffith, Martinez resident and co-founder of the Martinez Environmental Group and founding member of the Bay Area Refinery Corridor Coalition recently summed up the threat, saying:

When you take a close look at what is going on in the marine oil terminals along the refinery corridor from Richmond to Stockton, it’s chilling to imagine what could happen if a huge oil tanker carrying tar sands crude crashed in the Bay! (Earthjustice, 2015)

Incidents

Chevron Fire 2012

Figure 23. Fires at Chevron Richmond Refinery 2012. Photo by John Sebastian Russo for the SF Chronicle

Like oil spills from tankers, there are other risks of industrial accidents for refineries that need to be considered. Accidents or incidents may occur that result in a sudden, large release of air pollution. Looking at the emissions data, the Richmond Chevron refinery with the largest production capacity may seem to be an efficient station compared to the other refineries. However, an explosion and large fire in 2012 there sent 15,000 community members to local hospitals with respiratory distress. The SF Chronicle’s coverage of the story can be found here. (Fire shown in photo right.) The incident resulted from pipes corroding and failing, and the facility failing to make the decision to shut down the process. The resulting plume of smoke is shown in the cover photo of this article. Other major explosions and fires have occurred in the recent past, as well, including a flaring incident in 2014, a fire in 2007, and two other explosion and fire events in 1999 and 1989.

Of course these events are not unique to the Chevron refinery. The Tesoro Golden Eagle refinery has a reputation of being the most dangerous refinery in the country for occupational hazards, and has one of the worst track records of violations.

Conclusions

If refineries increase their capacity and process more crude, the emissions of these various pollutants will invariably increase. Increased emissions elevate risk for surrounding communities, and in the bay area these communities already bare a disparate burden. Additionally, many of the pollutants will be transported with the prevailing wind that blows from the coast up the river delta and into the central valley. In FracTracker’s recent analysis of impacted communities in the refinery corridor, maps of air quality showed that the refinery communities are some of the most impacted in the entire bay area.

In addition, California’s Central Valley has some of the worst air quality in the U.S. Click here to view maps of state air quality of disproportionate impacts by us using CalEnviroScreen 2.0. While many of the HAPs have a greater local impact, others such as ozone have regional impacts, while others like mercury are transported globally.

What we find in this report is that the refineries and petrochemical industry in the refinery corridor are responsible for the majority of the risk-driving emissions in this region. When the risk and total emissions are averaged for the entire Bay Area, the risk outcomes are much less than for those living in the communities hosting the industries. New emissions rules should prioritize contributions of emissions to ambient air pollution loads. The biggest issue with using a “per barrel” emissions limit is that it prioritizes the refining capacity rather than mitigating the existing health impacts. These types of policy decisions deal directly with risk management. The Air Management District must decide what amount of cancer and disease are acceptable to keep the refineries in the communities. An upper limit on emissions makes it easier to set a risk limit, an upper bound for health impacts. The upper limit also holds the Air Management District and elected officials accountable for their policy decisions.

References

  1. U.S.EPA. 2011. Addressing Air Emissions from the Petroleum Refinery Sector U.S. EPA. Accessed 3/15/16.
  2. CBE. 2015. Playing It Safe: Supplemental comment on air district staff proposal, rules 12-15 and 12-16; Evidence of increasing bay area refinery GHG and pm2.5 emissions.. Communities for a Better Environment
  3. Casanova, D. Diemoz, L. Lifshay, J. McKetney, C. 2010. Community Heath Indicators for Contra Costa County. Community Health Assessment, Planning and Evaluation (CHAPE) Unit of Contra Costa Health Services’ Public Health division. Accessed 4/15/16.
  4. BAAQMD. 2012. Summary of PM Report. Bay Area Air Quality Management District. Accessed 4/15/16.

** Feature image of the Richmond Chevron Refinery courtesy of D.H. Parks

** Feature image of the Richmond Chevron Refinery courtesy of Paul Chinn | The Chronicle

Petrochemical Industry Presence in East Bay CA’s North Coast Refinery Corridor

Who Lives Near the Refineries?
By

Kyle Ferrar, Western Program Coordinator &
Kirk Jalbert, Manager of Community-Based Research & Engagement

Key Takeaways

  • Communities living along the North Coast of the East Bay region in California are the most impacted by the presence of the petrochemical industry in their communities.
  • Emissions from these facilities disproportionately degrade air quality in this corridor region putting residents at an elevated risk of cancer and other health impacts.
  • People of color are more likely to live near the refineries and are therefore disproportionately affected.

Refinery Corridor Introduction

The North Coast of California’s East Bay region hosts a variety of heavy industries, including petroleum refineries, multiple power plants and stations, chemical manufacturing plants, and hazardous waste treatment and disposal facilities. Nationwide, the majority of petroleum refineries are located in heavily industrialized areas or near crude oil sources. The north coast region is unique. Access to shipping channels and the location being central to the raw crude product from North Dakota and Canada to the North, and California’s central valley oil fields to the south has resulted in the development of a concentrated petrochemical infrastructure within the largely residential Bay Area. The region’s petrochemical development includes seven fossil fuel utility power stations that produce a total of 4,283 MW, five major oil refineries operated by Chevron, Phillips 66, Shell Martinez, Tesoro, and Valero, and 4 major chemical manufacturers operated by Shell, General Chemical, DOW, and Hasa Inc. This unequal presence has earned the region the title, “refinery corridor” as well as “sacrifice zone” as described by the Bay Area Refinery Corridor Coalition.

The hazardous emissions from refineries and other industrial sites are known to degrade local air quality. It is therefore important to identify and characterize the communities that are affected, as well as identify where sensitive populations are located. The communities living near these facilities are therefore at an elevated risk of exposure to a variety of chemical emissions. In this particular North Coast region, the high density of these industrial point sources of air pollution drives the risk of resultant health impacts. According to the U.S.EPA, people of color are twice as likely to live near refineries throughout the U.S. This analysis by FracTracker will consider the community demographics and other sensitive receptors near refineries along the north coast corridor.

In the map below (Figure 1) U.S. EPA risk data in CalEnviroscreen is mapped for the region of concern. The map shows the risk resulting specifically from industrial point sources. Risk along the North Coast is elevated significantly. Risk factors calculated for the region show that these communities are elevated above the average. The locations of industrial sites are also mapped, with specific focus on the boundaries or fencelines of petrochemical sites. Additional hazardous sites that represent the industrial footprint in the region have been added to the map including sites registered with Toxic Release Inventory (TRI) permits as well as Superfund and other Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) sites. The Toxmap TRI sites are facilities that require a permit to emit hazardous air pollutants. The superfund and other CERCLA sites are locations where a historical footprint of industry has resulted in contamination. The sites are typically abandoned or uncontrolled hazardous waste sites that are part of register for tax-funded clean-ups.

Figure 1. Interactive map of risk in the East Bay’s North Coast refinery corridor

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Oil refineries in particular are unique sources of air emissions. There are 150 large domestic refineries throughout the United States. They are shown in the map in Figure 2 below. The majority (90%) of the refined products from these refineries are fuels; motor vehicle gasoline accounts for 40%. The refinery sites have hundreds of stacks, or point sources, and they emit a wide variety of pollutants, as outlined by the U.S. EPA:

  • Criteria Air Pollutants (CAPs)
    • Sulfur Dioxide (SO2)
    • Nitrogen Oxides (NOx)
    • Carbon Monoxide (CO)
    • Particulate Matter (PM)
  • Volatile Organic Compounds (VOCs)
  • Hazardous Air Pollutants (HAPs)
    • Carcinogens, including benzene, naphthalene, 1,3-butadiene, PAH
    • Non-carcinogenic HAP, including HF and HCN
    • Persistent bioaccumulative HAP, including mercury and nickel
  • Greenhouse Gases (GHG)
  • Hydrogen Sulfide (H2S)

Figure 2. Map of North American Petroleum Refineries


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BAAQMD Emissions Index

Figure 3. BAAQMD emissions index visualization

Disparate health impacts are therefore a known burden for these Bay Area communities. The region includes the cities of Richmond, Pinole, Hercules, Rodeo, Crockett, Port Costa, Benicia, Martinez, Mt. View, Pacheco, Vine Hill, Clyde, Concord, Bay Point, Antioch, and Oakley. In addition to preserving the ecological system health of this intercostal region is also important for both the ecological biodiversity of the marsh as well as commercial and recreational purposes. These wetlands provide a buffer, able to absorb rising waters and abate flooding.

The Bay Area Air Quality Management District’s (BAAQMD) Cumulative Impacts report identified areas where air pollution’s health impacts are relatively high in the San Francisco Bay Area. The report is does not limit their analysis to the North Coast, but shows that these regions with the most impacts are also the most vulnerable due to income, education level, and race and ethnicity. The report shows that there is a clear correlation between socio-economic disadvantages and racial minorities and the impacted communities. Figure 3 shows the regions identified by the BAAQMD as having the highest pollution indices.

Analysis

This analysis by FracTracker focuses specifically on the north shore of the East Bay region. Like the BAAQMD report, National Air toxic Assessment (NATA) data to identify census tracts with elevated risk. Specifically, elevated cancer and non-cancer risk from point sources emitting hazardous air pollutants (HAPs) as regulated by the U.S. EPA were used. CalEnviroScreen 2.0 data layers were also incorporated, specifically the U.S. EPA’s Risk Screening Environmental Indicators (RSEI) data. RSEI uses toxic release inventory (TRI) data, emission locations and weather to model how chemicals spread in the air (in 810m-square grid units), and combines air concentrations with toxicity factors.

The census tracts that were identified as disproportionately impacted by air quality are shown in the map below (Figure 4). The demographics data for these census tracts are presented in the tables below. Demographics were taken from the U.S. census bureau’s 2010 Census Summary File 1 Demographic Profile (DP1). The census tracts shapefiles were downloaded from here.

Figure 4. Interactive Map of Petrochemical Sites and Neighboring Communities in the East Bays North Coast Industrial Corridor

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Buffers were created at 1,000 ft; 2,000 ft; and 3,000 ft buffers from petrochemical sites. These distances were developed as part of a hazard screening protocol by researchers at the California Air Resources Board (ARB) to assess environmental justice impacts. The distances are based on environmental justice literature, ARB land use guidelines, and state data on environmental disamenities (Sadd et al. 2011). A demographical profile was summarized for the population living within a distance of 3,000 feet, and for the census tracts identified as impacted by local point sources in this region. The analysis is summarized in Table 1 below. Additional data on the socioeconomic status of the census tracts is found in Table 2.

Based on the increased percentage of minorities and indicators of economic hardship shows that the region within the buffers and the impacted census tracts host a disproportionate percentage of vulnerable populations. Of particular note is 30% increase in Non-white individuals compared to the rest of the state. We see in Table 2 that this is disparity is specifically for Black or African American communities, with an over 150% increase compared to the total state population. The number of households reported to be in poverty in the last 12 months of 2014 and those households receiving economic support via EBT are also elevated in this region. Additional GIS analysis shows that 7 healthcare facilities, 7 residential elderly care facilities, 32 licensed daycares, and 17 schools where a total of 10,474 students attended class in 2014. Of those students, 54.5% were Hispanic and over 84% identified as “Non-white.”

Table 1. Demographic Summaries of Race. Data within the 3,000 ft buffer of petrochemical sites was aggregated at the census block level.

Total Population Non-White Non-White (%ile)  Hispanic or Latino  Hispanic or Latino (%ile)
Impacted Census Tracts 387,446 212,307 0.548 138,660 0.358
3,000 ft. Buffer 77,345 41,696 0.539 30,335 0.392
State Total 37,253,956 0.424 0.376

Table 2. Additional Status Indicators taken from the 2010 census at the census tract level

Indicators (Census Tract data) Impacted Count Impacted Percentile State Percentile
Children, Age under 5 27,854 0.072 0.068
Black or African American 60,624 0.156 0.062
Food Stamps (households) 0.1103 0.0874
Poverty (households) 0.1523 0.1453

Conclusion

The results of the refinery corridor analysis show that the communities living along the North Coast of the East Bay region are the most impacted by the presence of the petrochemical industry in their communities. Emissions from these facilities disproportionately degrade air quality in this corridor region putting residents at an elevated risk of cancer and other health impacts. The communities in this region are a mix of urban and single family homes with residential land zoning bordering directly on heavy industry zoning and land use. The concentration of industry in this regions places an unfair burden on these communities. While all of California benefits from the use of fossil fuels for transportation and hydrocarbon products such as plastics, the residents in this region bear the burden of elevated cancer and non-cancer health impacts.

Additionally, the community profile is such that residents have a slightly elevated sensitivity when compared to the rest of the state. The proportion of the population that is made up of more sensitive receptors is slightly increased. The region has suburban population densities and more children under the age of 5 than average. The number of people of color living in these communities is elevated compared to background (all of California). The largest disparity is for Black or African American residents. There are also a large number of schools located within 3,000 ft of at least one petrochemical site, where over half the students are Hispanic and the vast majority are students of color. Overall, people of color are disproportionately affected by the presence of the petrochemical industry in this region. Continued operation and any increases in production of the refineries in the East Bay disproportionately impact the disadvantaged and disenfranchised.

With this information, FracTracker will be elaborating on the work within these communities with additional analyses. Future work includes a more in depth look at emissions and drivers of risk on the region, mapping crude by rail terminals, and working with the community to investigate specific health endpoints. Check back soon.

References

  1. U.S.EPA. 2011. Addressing Air Emissions from the Petroleum REfinery Sector U.S. EPA. Accessed 3/15/16.
  2. Sadd et al. 2011. Playing It Safe: Assessing Cumulative Impact and Social Vulnerability through an Environmental Justice Screening Method in the South Coast Air Basin, California. International Journal of Environmental Research and Public Health. 2011;8(5):1441-1459. doi:10.3390/ijerph8051441.

** Feature image of the Richmond Chevron Refinery courtesy of Paul Chinn | The Chronicle

Photo courtesy of Brian van der Brug | LA Times

More Oil Field Wastewater Pits Found in California!

Who’s in charge here?
By Kyle Ferrar, Western Program Coordinator

FracTracker Alliance recently worked with Clean Water Action to map an update to last year’s report* on the use of unlined, above ground oil and gas waste disposal pits, also known as sumps.

The new report identifies additional oil field wastewater pits and details how California regulators continue to allow these facilities to degrade groundwater, surface waters, and air quality. Other oil and gas production states do not permit or allow these type of operations due to the many documented cases of water contamination. A report published in 2011 identified unlined pits and other surface spills as the largest threat to groundwater quality. The sites are ultimately sacrifice zones, where the contamination from produced water and drilling mud solid wastes leaves a lasting fingerprint.

Central Coast & New Central Valley Pit Data

Ca Central Coast oil field wastewater pits

Figure 1. Central Coast wastewater pits

New data has been released by the Central Coast Regional Water Quality Control Board, identifying the locations of 44 active wastewater facilities and 5 inactive facilities in the California counties of Monterey, Santa Barbara, and San Luis Obispo. The number of pits at each facility is not disclosed, but satellite imagery shows multiple pits at some facilities. The locations of the majority of central coast pits are shown in the map in Figure 1, to the right.

In the web map below (Figure 2), the most updated data shows the number of pits at “active” facilities (those currently operating), shown in red and green, and inactive pits, shown in yellow and orange. The number of pits at each facility in the central valley are shown by the size of the graduated circles. Pit count data for the central coast facilities was not reported, therefore all facilities are shown with a small marker.

Figure 2. Interactive map of California oil field wastewater pits

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Exploring the new central coast data shows that the operators with the most facilities include Greka Oil & Gas Inc. (14), E & B Natural Resources (10), ERG Operating Company, LLC (6), and Chevron (5). As shown in the table below, the majority of central coast pits are located in Santa Barbara County.

Table 1. Summaries by County

Site Counts by Activity and County
Facility Counts Pit Counts
County Active Inactive Active Inactive
Santa Barbara 35 2 Unknown Unknown
Monterey 9 0 Unknown 0
San Luis Obispo 0 3 0 Unknown
Kern 161 191 673 347
Fresno 8 5 31 14
Tulare 6 1 28 1
Kings 5 0 14 0
San Benito 0 4 0 5
Grand Total 224 206 746 367

Wastewater Pit Regulations

Way back in 1988, the U.S. EPA recognized that the federal regulations governing disposal practices of wastewater are inadequate to protect public health, but has yet to take action (NRDC 2015). There is little chance the U.S. EPA will enact regulations focused on pits. In certain cases, if wastewaters spill or are discharged to surface waters the operations will fall under the jurisdiction of the Clean Water Act and will require a National Pollutant Discharge Elimination System (NPDES) permit. Since the objective of the pit is to contain the wastewater to keep it away from surface waters, pits and the wastewater facilities in California that manage them do not require federal oversight. For now the responsibility to protect health and environment has been left to the states.

Most states have responded and have strict regulations for wastewater management. For the few states that allow unlined pits, the main use is storage of wastewater rather than as an dedicated method of disposal. The majority of high production states have banned or ended the use of unlined pits, including Texas, North Dakota, Pennsylvania, Ohio, and New Mexico, Texas (Heberger & Donnelly 2015). An effective liner will prevent percolation of wastewaters into groundwater. The goal of California oil field wastewater pits is quite the opposite.

For California, percolation is the goal and a viable disposal option.

Therefore other regulations that require monitoring of liquid levels in the pits are moot. In fact there is no evidence of regulation requiring spill reporting in California whatsoever (Kuwayama et al. 2015).

Numerous other extraction states throughout the country have phased out the use of open pits entirely, including those with liners due to the common occurrence of liner failures. The list includes those new players in the shale boom using hydraulic fracturing techniques such as North Dakota, Ohio, Pennsylvania, Wyoming, and Colorado. Rather than using the pits as storage, these states’ regulatory agencies favor instead the protections of closed systems of liquid storage. Wastewaters are stored in large tanks, often the same tanks used to store the fresh water used in the hydraulic fracturing process.

Because hydraulic fracturing in California uses much less water, it should be much easier to manage the flowback fluids and other wastewaters. According to the CCST report, 60% of the produced water from hydraulic fracturing operations was disposed to these unlined pits. Regardless of extraction technique, oil extraction in California produces 15 times the amount of wastewater. In total, an estimated 40% of all produced water was discharged to unlined “percolation” pits. As the 3rd largest oil producing state in the country, this equates to a massive waste stream of about 130 billion gallons/year (Grinberg 2014).

Regulatory Action

The facilities’ permits identify waste discharge requirements (WDRs) that allow for the discharge of oil field wastewater to the “ground surface, into natural drainage channels, or into unlined surface impoundments.” Using the Race Track Hill and Fee 34 Facilities as an example, the WDRS place criteria limits on total dissolved solids (TDS), chlorides, and boron. If you disregard all the other toxic constituents not monitored, the allowable concentration limits set for these three wastewater constituents would be reasonable for a discharge permit on the east coast, where a receiving body of water could provide the volume necessary for dilution. When the wastewater is applied directly to the ground or into a pit, the evaporative loss of water results in elevated concentrations of these contaminants.

Even with these very lax regulations, a number of facilities are in violation of the few restrictions required in their permits. Cease and desist orders have been several operators, most notably to Valley Water Management’s Race Track Hill and Fee 34 Facilities. According to the Regional Water Board documents, the Fee 34 disregarded salinity limitations and other regulations. As a result the Regional Water Board found soil and groundwater contamination that “threatens or creates a condition of pollution in surface and groundwater, and may result in the degradation of water quality.” Reports show that 6 domestic supply and 12 agricultural supply wells are located within 1 mile of the Fee 34 facility. At the Race Track Hill Facility the wastewater is continuously sprayed over several acre fields in a small watershed of the Cottonwood Creek. During a rain, the salt and boron loadings that have accumulated in the soil over the past 60 years of spraying can create increased salt and boron loading in the Kern River and groundwater. This would be a violation of the Clean Water Act (CVRWQCB 2015).

As shown in Table 2, below, the majority of facilities are currently operating without a permit whatsoever (61.2%). Of the 72 facilities that bothered to get permits, 32 (44.4%) received the permit prior to 1975, before the Tulare Basin Plan was implemented to preserve water quality. Of the 183 active facilities in the Central Valley, only 15 facilities have received Cease and Desist (11% of permitted) or Cleanup and Abatement Orders (6% of unpermitted). Only 3 of the 41 active Central Coast facilities operate with a permit (7.3%).

These types of WDR permits that allow pollutants to concentrate in the soil and the groundwater and degrade air quality. Chemicals that pose a public health risk are not being monitored. But at this point, these facilities are not only sites of legacy contamination, but growing threats to groundwater security. Operators say that closing the pits will mean certain doom for oil extraction in California, and recent letters from operators make pleas to DOGGR, that their very livelihood depends on using the pits as dumping grounds. The pits are the cheapest and least regulated mode of disposal.

Table 2. Facility Status Summaries

Facility Status
Activity Permitted Permitted; Cease & Desist Order Unpermitted Unpermitted; Cleanup & Abatement Order Grand Total
Active 75 9 137 6 227
Inactive 20 2 184 3 209
Grand Total 92 11 321 9 433

New Mexico Case Study

Much like the groundwater impacts documented by California’s Central Valley Regional Water Quality Control Board, other states have been forced to deal with this issue. The difference is that other states have actually shut down the polluting facilities. In California, cease and desist orders have been met with criticism and pleas by operators, stating that the very livelihood of the oil and gas industry in California depends on wastewater disposal in pits. The same was said in other states such as New Mexico when these crude and antiquated practices were ended. Figure 3 below shows the locations of wastewater pits in New Mexico and the areas where groundwater was contaminated as a result of the pits.
The New Mexico oil and gas industry predicted in August 2008 that fewer drillers would sink wells in New Mexico, at least in part because of the new pit rule. Pro-industry (oil and gas) state representatives were concerned that new drilling techniques coupled with the pit rules could lead to an industry exodus from New Mexico, hoping that the Governor “would step in to help protect an important state revenue source.” But the state’s average rig count from June — when the pit rule took effect — through December 2008 was 7% higher than it was over the same period in the previous year. Development of oil and gas reserves is independent of such regulation. Read the FracTracker coverage of groundwater contamination in New Mexico, here!

Figure 3. Legacy map of cases where pits contaminated groundwater in New Mexico

View Map Fullscreen | How Our Maps Work

References & Resources

* In case you missed it, the 2014 report on wastewater pits can be found here (Grinberg, A. 2014). FracTracker’s previous coverage of the issue can be found here.

** Feature image of Central Valley oil field wastewater pits courtesy of Brian van der Brug | LA Times

  1. Grindberg, A. 2016. UPDATE ON OIL AND GAS WASTEWATER DISPOSAL IN CALIFORNIA: California Still Allowing Illegal Oil Industry Wastewater Dumping Clean Water Action. Accessed 2/15/16.
  2. Grinberg, A. 2014. In the Pits, Oil and Gas Wastewater Disposal into Open Unlined Pits and the Threat to California’s Water and Air. Clean Water Action. Accessed 12/5/14.
  3. NRDC. 2015. Groups File Notice of Intent to Sue EPA Over Dangerous Drilling and Fracking Waste. NRDC. Accessed 10/1/15.
  4. Heberger, M. Donnelly, K. 2015. Oil, Food, and Water: Challenges and Opportunities for California Agriculture. Pacific Institute. Accessed 2/1/16.
  5. Kuwayama et al. 2015. Pits versus Tanks: Risks and Mitigation Options for On-site Storage of Wastewater from Shale Gas and Tight Oil Development. Resources for the Future. Accessed 2/1/16.
  6. CVRWQCB. 2015. Cease and Desist Order R5-2015-0093. CVRWQCB. Accessed 2/1/16.
Aliso Canyon natural gas leak - Photo by Environmental Defense Fund

A Climate Disaster – California in state of emergency as a result of massive natural gas leak

By Kyle Ferrar, Western Program Coordinator, FracTracker Alliance

A natural gas well equipment failure in southern California has resulted in the largest point release of methane to the atmosphere in U.S. history. California Governor Jerry Brown has declared a California state of emergency for the incident, and the California Air Resources Board (CARB) has identified the site as the single largest source point of global warming.1 Since October 23, 2015 the failure has been reported to be releasing 62 million cubic feet of methane per day – 110,000 pounds per hour – for a total of about 80 million metric tons thus far. (A running counter for the natural gas leak can be found here, on Mother Jones).2,3 This quantity amounts to a quarter of California’s total methane emissions, and the impact to the climate is calculated to be the equivalent of the operation of 7 million cars.

SoCalGas (a subsidiary of Sempra Energy) reports that nothing can be done to stop or reduce the leak until February or March of 2016. As a result, the nearby community of Porter Ranch has been largely evacuated (30,000 people) due to health complaints and the rotten egg smell of tertbutyl mercaptan and tetradydrothiophen. Air quality sampling, being assessed by the Office of Environmental Health Hazard and Assessment (OEHHA), measured volatile organic compounds, specifically the carcinogen benzene, at concentrations below acute toxicity health standards.4 Exposure to benzene even at low levels presents a risk of cancer and other health hazards. Locals have complained of headaches, sore throats, nosebleeds and nausea. The LA County Department of Public Health has ordered SoCalGas to offer free temporary relocation to any area residents affected. About 1,000 people are suing the company.5 A fly over of the site has been posted to youtube by the Environmental Defense Fund, and can be seen here. The video uses a FLIR camera to take infrared video that shows the leak.

Site Description

CA gas storage and Aliso Canyon natural gas leak

Figure 1. California active natural gas storage fields most active in 2014

The source of the leak is a natural gas storage well operated by SoCalGas in the Aliso Canyon oil field – a drained oil field now used to store natural gas. SoCalGas is the largest natural gas utility in the U.S., distributing natural gas to 20.9 million.4 Aliso Canyon is the largest gas storage field in the state, but there are numerous other gas storage fields in the state that could present similar risks. In Figure 1, to the right, California’s other currently active gas storage fields are shown. Injection volumes of natural gas are summed and averaged over the area of the field, and the Aliso Canyon is shown to have injected over 1,000,000 cubic feet per km2 of natural gas since the beginning of 2014. Other high volume fields include Honor Rancho, McDonald Island Gas, and Wild Goose Gas.

The failed well, known as Standard Sesnon 25, is marked with a red star in the map of gas storage wells shown below (Figure 2). The well was drilled in October of 1953. Reports show that pressures in the well bored reached 2,516 PSI in 2015. If you use the map to navigate around the state of California, it is clear that there are numerous other natural gas storage facilities in California, with wellbore pressures similar to or higher than the reported pressure of Standard Sesnon 25 and other wells in the Aliso Canyon Field. Beyond California, the state of Michigan is reported to have the most natural gas storage by volume, at 1.1 trillion cubic feet.6 The incident that caused the leak was a well casing failure, although the cause of the well casing failure has not yet been identified. There have been numerous editorials written that have painted SoCalGas as a model for contemporary corporate greed and corruption for several reasons, including the removal of safety valves, reports of corrosion, and lack of resources for inspections and repairs.7 Rather than this being a unique case of criminal neglect, casing failures are a statistical likelihood for wells of this age. Well casing failures are a systemic issue of all oil and gas development. Every well casing has a shelf life and will fail eventually.8 Additionally, leaks from gas storage wells have occurred at other SoCalGas natural gas storage facilities in California, such as Montebello and Playa Del Rey.

Figure 2. California’s gas storage wells. The size of orange markers indicates wellhead pressure, as reported in 2015. Blue markers show the volume of gas injected in 2014/2015. The Aliso Canyon leak at ‘Standard Sesnon 25’ natural gas storage well is marked with a red star. Click here to manipulate the map. After expanded, use the “Layers” menu to visualize the data with colored markers rather than size. 

Response

Fixing the problem is therefore much more complicated, overall, in this specific case. Since the well casing has ruptured deep underground, natural gas is leaking in the annular space outside the borehole and spewing from the topsoil surrounding the well head. To stop the leak the production pipe must be plugged below the rupture. All attempts to plug the well from the surface have failed due to the high pressure within the borehole, a 7” inner diameter of the production pipe. Therefore, a relief well is being drilled to intersect the well casing, to inject a mud-chemical cocktail intended to plug the well far below the casing failure. Updates on the response, claims information, and the location of the Community Resource Center can be found here. Additionally, Governor Jerry Brown has declared a state of emergency, which means federal support and a requirement of the state of California to cover the costs.9

The state response to the natural gas leak has included numerous agencies. According to documents from California Public Utilities Commission (CPUC), the agencies leading the response are the California Department of Conservation, Division of Oil, Gas, and Geothermal Resources (DOGGR), the Office of Emergency Services (CalOES), California Air Resources Board (ARB), California Division of Occupational Safety and Health (CalOSHA), the California Energy Commission (CEC), and the CPUC. DOGGR is conducting an independent investigation of the incident. The investigation will include a third party analysis for root-cause issues. CARB is monitoring total methane emissions while the Office of Environmental Health Hazard Assessment with CalEPA are collecting and reviewing air quality data. Coordinated response information can be found on the CalOES site. SoCalGas has submitted a proposal to regulators to raise customer rates in order to raise $30 million for a more proactive approach to inspections and repairs.10

This event is the largest, but is not the first major methane/natural gas leak to occur at a wellsite. Leaks can result from a number of natural and anthropogenic (man made) causes. Besides the natural degradation of well integrity with age, acute events can also cause casing failures. There are documented cases where seismic activity has caused casing failures.

As a result of an earthquake natural fractures in the region can grow and disrupt well bores. In areas of dense drilling, fracture stimulations that propagate improperly or intersect unknown faults. When two wells become interconnected, known as “downhole communication” or a “frack hit” when it occurs due to hydraulic fracturing, spills and leaks can occur due to over-pressurization. In many states, these risks are mitigated by having setbacks between wells. California, the most seismically active state, has minimal setbacks for drilling or fracking oil and gas wells. In previous research, FracTracker found that over 96% of new hydraulic fractures in 2013 were drilled within 1,200 feet of another well, which would even violate setback rules in Texas!

Climate Impacts

Natural gas is hailed by the fossil fuel industry as the bridge fuel that will allow the world to transition to renewables. The main argument claims natural gas is necessary to replace coal as our main source of generating electricity. Burning both coal and natural gas produce carbon dioxide, but natural gas is more efficient. For the same amount of energy production, natural gas produces half as much carbon dioxide emissions. The legitimate threat of climate impacts comes from fugitive (leaked) emissions of methane, before the natural gas can be burned. Since methane is a gas, it is much harder to contain than oil or coal. Methane is also more insulating than carbon dioxide in the atmosphere (34-86 times more insulating), making it a more potent greenhouse gas. The leaked natural gas from the Aliso Canyon well is currently equivalent to 7,000,000 tons of CO2 (Updated here, on Mother Jones).

Current estimates show methane is responsible for 25% of the world’s anthropogenic warming to date. Proponents of the bridge fuel theorize that if methane leakage can be kept under 4% of total production, natural gas power generation will provide a climate-positive alternative to coal. EPA estimates set the leakage rate at 2.4%, but independent research estimates actual rates up to 7.9%.11 The EDF has been conducting an $18 million project focused on quantifying methane leaks from the natural gas industry. A team of 20 researchers from 13 institutions conducted the 2 year study measuring emissions from the Barnett Shale. Details can be found on the Environmental Defense Fund’s Page.12

Natural Gas Leak References

  1. Goldenberg, S. (2016). A single gas well leak is California’s biggest contributor to climate change. The Guardian. Accessed 1/6/16.
  2. Environmental Defense Fund. (2015). Aerial Footage of Aliso Canyon Natural Gas Leak. via YouTube. Accessed 1/5/16.
  3. Lurie, J. (2016). Thousands of Californians are Fleeing an Enormous Methane Leak. Here are 8 Things You Need to Know. Mother Jones. Accessed 1/6/16.
  4. CalOES. (2015). Aliso Canyon Natural Gas Leak. Accessed 1/8/15.
  5. BBC. (2015). California state of emergency over methane leak. Accessed 1/8/15
  6. Ellison, G. (2015). Michigan has most underground natural gas storage in U.S. MLive. Accessed 1/8/15.
  7. Reicher, M. (2015). SocalGas knew of corrosion at Porter Ranch gas facility, doc shows. LA Daily News. Accessed 1/5/16.
  8. Ingraffea et al. (2013). Assessment and risk analysis of casing and cement impairment in oil and gas wells in Pennsylvania, 2000-2012. PNAS. Vol.111 no.30.
  9. Cronin, M. (2015). Why Engineers Can’t Stop Los Angeles’ Enormous Methane Leak. Accessed 1/4/16.
  10. CUUC. (2015). Appendix A. Accessed 1/5/15. [please note that some CPUC files are being taken offline for unknown reasons]
  11. Howarth et al. (2011). Methane and the greenhouse-gas footprint of natural gas from shale formations. Climatic Change. 106:679-690.
  12. Song, L. (2015). Texas Fracking Zone Emits 90% More Methane Than EPA Estimated. InsideClimate News.

Feature Image: Aliso Canyon natural gas leak – Photo by Environmental Defense Fund

Oil wastewater pit

Wastewater Pits Still Allowed in California

By Kyle Ferrar, Western Program Coordinator

Above-ground, unlined, open-air sumps/ponds

It is hard to believe, but disposing of hazardous oil and gas wastewaters in unlined, open-air pits – also known as sumps or ponds – is still a common practice in California. It is also permitted in other states such as Texas and West Virginia. Because these ponds are unlined and not enclosed, they contribute to degraded air quality, are a hazard for terrestrial animals and birds, and threaten groundwater quality. A 2014 report by Clean Water Action, entitled In the Pits provides a thorough summary of the issue in California. Since the report was released, new data has been made available by the Central Valley Regional Water Quality Review Board identifying additional locations of wastewater pits.

With the increase of oil and gas development in unconventional reservoirs, such as the Monterey Shale Play in California, the size of the resultant waste stream of drill cuttings, produced brines, and wastewater has skyrocketed. Operators now drill larger, deeper wells, requiring larger volumes of liquid required for enhanced oil recovery methods, such as steam injection, and stimulations such as hydraulic fracturing and acidizing. While California is the 4th largest oil-producing state, it is 2nd only to Texas in wastewater production. This boom of unconventional development, which may still in its infancy in California, has resulted in an annual waste stream of over 130 billion gallons across the state, 80 billion (62%) from Kern County alone.1

Results of the state mandated California Council on Science and Technology Report found that more than half of the California oil industries waste water is “disposed” in pits.2 As outlined by Clean Water Action, the massive waste-stream resulting from drilling, stimulation, and production is one of the most significant and threatening aspects of oil and gas operations in terms of potential impacts to public health and environmental resources.

Wastewater Facility Details

Last February, the LA Times reported on the pits, identifying a total of 933 in California.3 The most recent data from the Regional Water Quality Control Board of the Central Valley shows:

  • A total of 1,088 pits at 381 different facilities
  • 719 pits are listed as “Active.” 369 are “Idle.”
  • 444/939 (47.3%) ponds do not list a permit.
  • 462 pits are operated by Valley Water Management Corporation.

In Table 1, below, the counts of Active and Idle facilities and pits are broken down further to show the numbers of sites that are operating with or without permits. The same has been done for the operator with the most pits in Table 2, because Valley Wastewater operates nearly 9 times as many pits as the second largest operator, E & B Natural Resources Management Corporation. These two operators, along with California Resources Elk Hills LLC, all operate the same number of facilities (28). The other top 20 operators in Kern County are listed in Table 3, below.

Table 1. Wastewater Pit and Facility Counts by Category
Counts Active Idle
Facilities 180 201
Unpermitted Facilities 102 179
Facility Permitted prior to 1985 37 11
Individual Pits 719 369
Unpermitted Individual Pits 187 257
Pit Permitted prior to 1985 252 63

 

Table 2. Valley Water Wastewater Pit and Facility Counts by Category
Counts Active Inactive
Facilities 21 7
Unpermitted Facilities 2 2
Facility Permitted prior to 1985 9 1
Individual Pits 356 78
Unpermitted Individual Pits 5 9
Pit Permitted prior to 1985 166 35

 

Table 3. Top 20 Operators by Facility Count, with Pond Counts.
Rank Operator Pond Count Facility Count
1 Valley Water Management Company 462 28
2 E & B Natural Resources Management Corporation 53 28
3 California Resources Elk Hills, LLC 31 28
4 Aera Energy LLC 67 25
5 California Resources Corporation 31 23
6 Chevron U.S.A. Inc. 40 14
7 Pyramid Oil Company 21 12
8 Macpherson Oil Company 14 9
9 Schafer, Jim & Peggy 8 8
10 Crimson Resource Management 20 6
11 Bellaire Oil Company 11 6
12 Howard Caywood 11 6
13 LINN Energy 10 6
14 Seneca Resources Corporation 9 6
15 Holmes Western Oil Corporation 6 6
16 Hathaway, LLC 22 5
17 Central Resources, Inc. 15 5
18 Griffin Resources, LLC 13 5
19 KB Oil & Gas 8 5
20 Petro Resources, Inc. 6 5

Maps of the Pit Locations and Details

 

The following maps use the Water Authority data to show the locations details of the wastewater pits. The first map shows the number of pits housed at each facility. Larger markers represent more pits. Zoom in closer using the [+] to see the activity status of the facilities. Click the link below the map to open a new webpage. View the names of the facility operators by turning on the layer in the “Layers” menu at the top of the page. The second and third maps show the activity and permit status of each facility. The fourth map allows you to view both activity status and permit status simultaneously by toggling the layers on and off (Open the map in its own webpage, then use the layers menu at the top of the screen to change views).

Map 1. Facility Pit Counts with the top 10 operators identified as well as facility status

Map 1. To view the legend and map full screen, click here.

Map 2. Facility Activity Status

Map 2. To view the legend and map full screen, click here.

Map 3. Facility Permit Status

Map 3. To view the legend and map full screen, click here.

Map 4. Facilityhttps://maps.fractracker.org/lembed/?appid=7385605f018e437691731c94bb589f0a” width=”800″ height=”500″>
Map 4. To view the legend and map full screen, click here.

References

  1. USGS. 2014. Oil, Gas, and Groundwater Quality in California – a discussion of issues relevant to monitoring the effects of well stimulation at regional scales.. California Water Science Center. Accessed 10/1/15.
  2. CCST. 2015. Well Stimulation in California. California Council on Science and Technology. Accessed 9/1/15.
  3. Cart, Julie. 2/26/15. Hundreds of illicit oil wastewater pits found in Kern County . Los Angeles Times. Accessed 9/1/15.
FracTracker map of the density of wells by U.S. state as of 2015

1.7 Million Wells in the U.S. – A 2015 Update

Please Note

Click here to view an update on this topic


 

Updated National Well Data

By Matt Kelso, Manager of Data & Technology

In February 2014, the FracTracker Alliance produced our first version of a national well data file and map, showing over 1.1 million active oil and gas wells in the United States. We have now updated that data, with the total of wells up to 1,666,715 active wells accounted for.

Density by state of active oil and gas wells in the United States. Click here to access the legend, details, and full map controls. Zoom in to see summaries by county, and zoom in further to see individual well data. Texas contains state and county totals only, and North Carolina is not included in this map. 

While 1.7 million wells is a substantial increase over last year’s total of 1.1 million, it is mostly attributable to differences in how we counted wells this time around, and should not be interpreted as a huge increase in activity over the past 15 months or so. Last year, we attempted to capture those wells that seemed to be producing oil and gas, or about ready to produce. This year, we took a more inclusive definition. Primarily, the additional half-million wells can be accounted for by including wells listed as dry holes, and the inclusion of more types of injection wells. Basically anything with an API number that was not described as permanently plugged was included this time around.

Data for North Carolina are not included, because they did not respond to three email inquiries about their oil and gas data. However, in last year’s national map aggregation, we were told that there were only two active wells in the state. Similarly, we do not have individual well data for Texas, and we use a published list of well counts by county in its place. Last year, we assumed that because there was a charge for the dataset, we would be unable to republish well data. In discussions with the Railroad Commission, we have learned that the data can in fact be republished. However, technical difficulties with their datasets persist, and data that we have purchased lacked location values, despite metadata suggesting that it would be included. So in short, we still don’t have Texas well data, even though it is technically available.

Wells by Type and Status

Each state is responsible for what their oil and gas data looks like, so a simple analysis of something as ostensibly straightforward as what type of well has been drilled can be surprisingly complicated when looking across state lines. Additionally, some states combine the well type and well status into a single data field, making comparisons even more opaque.

Top 10 of 371 published well types for wells in the United States.

Top 10 of 371 published well types for wells in the United States.

Among all of the oil producing states, there are 371 different published well types. This data is “raw,” meaning that no effort has been made to combine similar entries, so “gas, oil” is counted separately from “GAS OIL,” and “Bad Data” has not been combined with “N/A,” either. Conforming data from different sources is an exercise that gets out of hand rather quickly, and utility over using the original published data is questionable, as well. We share this information, primarily to demonstrate the messy state of the data. Many states combine their well type and well status data into a single column, while others keep them separate. Unfortunately, the most frequent well type was blank, either because states did not publish well types, or they did not publish them for all of their wells.

There are no national standards for publishing oil and gas data – a serious barrier to data transparency and the most important takeaway from this exercise… 

Wells by Location

Active oil and gas wells in 2015 by state. Except for Texas, all data were aggregated published well coordinates.

Active oil and gas wells in 2015 by state. Except for Texas, all data were aggregated published well coordinates.

There are oil and gas wells in 35 of the 50 states (70%) in the United States, and 1,673 out of 3,144 (53%) of all county and county equivalent areas. The number of wells per state ranges from 57 in Maryland to 291,996 in Texas. There are 135 counties with a single well, while the highest count is in Kern County, California, host to 77,497 active wells.

With the exception of Texas, where the data are based on published lists of well county by county, the state and county well counts were determined by the location of the well coordinates. Because of this, any errors in the original well’s location data could lead to mistakes in the state and county summary files. Any wells that are offshore are not included, either. Altogether, there are about 6,000 wells (0.4%) are missing from the state and county files.

Wells by Operator

There are a staggering number of oil and gas operators in the United States. In a recent project with the National Resources Defense Council, we looked at violations across the few states that publish such data, and only for the 68 operators that were identified previously as having the largest lease acreage nationwide. Even for this task, we had to follow a spreadsheet of which companies were subsidiaries of others, and sometimes the inclusion of an entity like “Williams” on the list came down to a judgement call as to whether we had the correct company or not.

No such effort was undertaken for this analysis. So in Pennsylvania, wells drilled by the operator Exco Resources PA, Inc. are not included with those drilled by Exco Resources PA, Llc., even though they are presumably the same entity. It just isn’t feasible to systematically go through thousands of operators to determine which operators are owned by whom, so we left the data as is. Results, therefore, should be taken with a brine truck’s worth of salt.

Top 10 wells by operator in the US, excluding Texas. Unknown operators are highlighted in red.

Top 10 wells by operator in the US, excluding Texas. Unknown operators are highlighted in red.

Texas does publish wells by operator, but as with so much of their data, it’s just not worth the effort that it takes to process it. First, they process it into thirteen different files, then publish it in PDF format, requiring special software to convert the data to spreadsheet format. Suffice to say, there are thousands of operators of active oil and gas wells in the Lone Star State.

Not counting Texas, there are 39,693 different operators listed in the United States. However, many of those listed are some version of “we don’t know whose well this is.” Sorting the operators by the number of wells that they are listed as having, we see four of the top ten operators are in fact unknown, including the top three positions.

Summary

The state of oil and gas data in the United States is clearly in shambles. As long as there are no national standards for data transparency, we can expect this trend to continue. The data that we looked for in this file is what we consider to be bare bones: well name, well type, well status, slant (directional, vertical, or horizontal), operator, and location. In none of these categories can we say that we have a satisfactory sense of what is going on nationally.

2015 Data Download

Click to download zip file

Click on the above button to download the three sets of data we used to make the dynamic map (once you are zoomed in to a state level). The full dataset was broken into three parts due to the large file sizes.

Largest Coastal Spill in 25 years [in California]

By Kyle Ferrar, Western Program Coordinator

The Santa Barbara Pipeline Spill

On May 19, 2015, just 20 miles north of Santa Barbara, a heavily corroded section of pipeline ruptured spilling upwards of 101,000 gallons. The pipeline was operated by Plains All American LLC, based out of Houston Texas, and was used to move crude oil from offshore rigs to inland refineries. The spill occurred on a section of pipe running parallel to the coastline at a distance of only a tenth of a mile to the ocean. As a result, the ruptured oil traveled through a drainage culvert and onto the beach where 21,000 gallons spilled into the ocean. The oil spread into a slick that covered 4 miles of coastline, and has since spread to southern California beaches more than 100 miles to the south. Santa Barbara county officials immediately closed two beaches, Refugio and El Capitan, and southern California beaches were also closed June 3rd through June 5th. Commercial fishing has been prohibited near the spill, and nearly 300 dead marine mammals and birds have been found, as well as dead cephalopods (octopi).1

Mapping the Impacts


Santa Barbara 2015 Oil Spill at Refugio Beach. To view the legend and map full screen, click here.

The map above shows details of the oil spill, including the location on the coastline, the extent that the spill traveled south, and the Exxon offshore platforms forced to suspend operations due to their inability to transport crude to onshore refineries.

The dynamic map also shows the wildlife habitats that are impacted by this oil spill, putting these species at risk. This area of Central California coastline is incredibly unique. The Santa Barbara Channel Islands are formed and molded as colder northern swells meet warmer southern swells, generating many temperature gradients and microhabitats able to support an incredible amount of biodiversity. Many species are endemic to only this region of the California coastline, and therefore are very sensitive to the impacts of pollution. In addition to the many bird species, including the endangered Western Snow Plover and Golden Eagle, this area of coastline is home to a number of whale and porpoise species, and, as seen in the map, the Leatherback Sea Turtle and the Black Abolone Sea Snail, both threatened.

Santa Barbara Channel_10.7.13

Figure 1. Offshore Drilling Near Santa Barbara from 2013

For California’s harbor seal populations, this kill event reinforces existing environmental pressures that have been shrinking the seal and sea lion (pinniped) communities, increasing the threat of shark attacks on humans. For the potential impact that this could have on California’s sensitive sea otter population, see FracTracker’s recent story on the West Coast Sea Otter.

In 2013, The FracTracker Alliance collaborated with the Environmental Defense Center on the report Dirty Water: Fracking Offshore California. The report showed that much of the offshore oil is extracted by hydraulic fracturing (Fig 1.), and outlined the environmental impacts that would result from a spill of this magnitude.

Clean Up Efforts

Workers are currently cleaning the spill by hand using buckets and shovels. These old fashioned techniques may be painstaking, but they are the least invasive and they are necessary to ensure that there is not additional damage to the sensitive ecosystems. Even scraping the coastline with wire brushes and putty knives cannot remove the stain of oil that has been absorbed by porous rocks. The oil will only wear away with time as it is diluted back into the ocean. Costs of the clean-up response alone have already reached $92 million, which is being paid by Texas-based Plains All American Pipeline. There have not been any reports yet on the financial impacts to the recreational and fishing industries.2

Prevention Opportunities

By comparison, the Santa Barbara oil spill in 1969 was estimated at 200 million gallons. After over 45 years, nearly a half decade, one would think that advancements in pipeline engineering and technology would prevent these types of accidents. Plains All American, the pipeline operator states that their pressure monitors can detect leaks the size of pinholes. Why, then, did the ruptured pipe continue to spill crude for three hours after the public was notified of the incident?

This section of pipeline (falsely reported by the media to be abandoned) was built in 1987. At capacity the pipeline could transport 50,400 gallons of oil per hour, but during the time of the spill the pipeline was running under capacity. Pipeline inspections had occurred in 2012 and in April of 2014, just weeks prior. The Pipeline and Hazardous Material Safety Administration said testing conducted in May had identified extensive corrosion of the pipeline that required maintenance. It is possible that this incident is an isolated case of mismanagement, but the data tell a different story as this is not an isolated event.

Plains released a statement that a spill of this magnitude was “highly unlikely,” although this section of the pipeline has experienced multiple other spills, the largest of which being 1,200 gallons. Just a year prior, May 2014, the same company, Plains, was responsible for a 19,000 gallon spill of crude in Atwater Village in Los Angeles County. According to a joint hearing of two legislative committees, the operators, Plains did not meet state guidelines for reporting the spill. According to the county, the operator should have been able to shut down the pipeline much faster.3 It is not clear how long the pipeline was actually leaking.

NASA Spill Visualizations

As a result of the spill and to assist with the clean-up and recovery, NASA’s Jet Propulsion Laboratory (JPL) in Pasadena, CA has developed new technology to track the oil slick and locate contamination of beaches along the coastline. The JPL deployed a De Havilland Twin Otter aircraft carrying a unique airborne instrument developed to study the spill and test the ability of imaging spectroscopy to map tar on area beaches. What this means is that from aircraft special cameras can take pictures of the beach. Based on the nature of the light waves reflecting off the beach in the pictures, tar balls and oil contamination can be identified. Clean-up crews can then be dispatched to these areas. On their website, NASA states “The work is advancing our nation’s ability to respond to future oil spills.”4 A picture generated using this technology, and showing oil contamination in water and on the beach, is shown below.

SBOilSpill_NASA

References

  1.  Maza, C. 2015. California oil spill: Regulators, lawmakers scrutinize company response. Christian Science Monitor. Accessed 7/1/15.
  2. Chang, A. 2015. Workers clean up oil spill on California beaches by hand. The Washington Times. Accessed 7/5/15.
  3. Panzar, J. 2015. Official says pipeline firm violated state guidelines for reporting Santa Barbara spill. Los Angeles Times. Accessed 7/6/15.
  4. NASA. 2015. NASA Maps Beach Tar from California Oil Pipeline Spill. NASA Jet Propulsion Laboratory California Institute of Technology. Accessed 7/7/17.

Offshore Oil and Gas Drilling: Risks to the Sea Otter

By Emily Watson, FracTracker Summer Intern

Sea otters, an endangered keystone species, are at risk due to offshore oil and gas drilling spills. Along the west coast of the U.S., this marine mammal’s habitat is commonly near offshore drilling sites, specifically in California and Alaska.

Sea Otters – a Keystone Species

Sea otter numbers used to range from several hundred thousand to more than a million. Today, there are estimated to be just over 106,000 in existence worldwide, with fewer than 3,000 living in California. Their habitats range from Canada, Russia, Japan, California and Washington, but the majority of all wild sea otters are found in Alaskan waters.

Sea otters play a significant role in their local environments, and a much greater ecosystem role than any other species in their habitat area. Sea otters are predators, critical to maintaining the balance of the near-shore kelp ecosystems, and are referred to as keystone species. Without this balancing act, coastal kelp forests in California would be devoured by other aquatic life.  Sea otter predation helps to ensure that the kelp community continues to provide cover and food for many of the marine animals. Additionally, kelp plays a tremendous role in capturing carbon in the coastal ecosystems. In that sense, sea otters also inadvertently help to reduce levels of atmospheric carbon dioxide.

Oil Spills and their Health Implications

Recently, Alaska and California, home to a wide variety of marine life, have been popular areas for offshore oil and gas drilling, which may include the use of fracking to extract hydrocarbons. Oil spills are a great concern for the sea otter; unlike other marine animals that may be able to eventually rid themselves of the oil, contact with the oil causes the sea otters fur to mat, preventing insulation, which can lead to hypothermia. Additionally, the ingestion of toxic oil chemicals while cleansing their fur can cause liver and kidney failure, as well as severe damage to their lungs and eyes.

Because their numbers are low and their geographic location area is rather small compared to other sea otter populations, the California sea otter is especially vulnerable, and could be devastated by oil contamination.

Prince William Sound, Alaska

Exxon Valdez cleanup. Photograph by Natalie Fobes, National Geographic

Exxon Valdez cleanup. Photograph by Natalie Fobes, National Geographic

On March 24, 1989, the tanker vessel Exxon Valdez ran aground on Bligh Reef in Prince William Sound, Alaska, spilling an estimated 42 million liters of Prudhoe Bay crude oil. This incident affected marine life throughout western Prince William Sound, the Gulf of Alaska, and lower Cook Inlet. An estimated 3500–5500 otters from a total population of about 30,000 may have died as a direct result of the oil spill. Oiling and ingestion of oil-contaminated shellfish may have affected reproduction and caused a variety of long-term sublethal effects. Necropsies of sea otter carcasses indicated that most deaths of sea otters were attributed to the oil, and pathologic and histologic changes were associated with oil exposure in the lung, liver, and kidney. Studies of long-term effects indicate that the sea otter population in the Prince William Sound area suffered from chronic effects of oil exposure at least through 1991. While some populations may recover after a spill, it would seem that the threat of oil pollution impacts is intensified for populations in deteriorating habitats and to those that are in decline.

Santa Barbara Coast, California

LA Santa Barbara Oil Spill Cleanup - Photo by: Brian van der Brug / Los Angeles Times

LA Santa Barbara Oil Spill Cleanup – Photo by: Brian van der Brug / Los Angeles Times

On Tuesday, May 19, 2015, a pipeline was found to be leaking into the Santa Barbara Coast in California. This broken pipeline, owned by Plains All American, spilled approximately 105,000 gallons of crude oil into the ocean, according to various news reports, stretching out into a 4-mile radius along the central California coastline.

These waters are home to an array of shore birds, seals, sea lions, otters and whales. Numerous amounts of marine life have been found washed up on the shore, including crabs, octopuses, fish, birds, and dolphins. Elephant seals, sea lions, and other marine wildlife have been taken to Seaworld in San Diego for treatment and recovery.

The Santa Barbara accident occurred on the same stretch of coastline as spill in 1969 that – at the time – was the largest ever incident in U.S. waters and contributed to the rise of the American environmental movement. Several hundred-thousand gallons spilled from a blowout on an oil platform, and thousands of seabirds were killed and numerous ocean wildlife, including sea lions, elephant seals, and fish perished.

Conclusion

Overall, the ocean is home to a great diversity of marine wildlife, all of which are vulnerable to oil contamination. Offshore gas drilling is a significant threat to the survival of sea otters and other marine life, wherein spills and accidents could cause health problems, toxicity, and even death. Oil spills are exceptionally problematic for sea otters, due to the vulnerable state of this animal and its endangered species state. Keeping keystone species healthy is instrumental to maintaining a well flourished ecosystem, while protecting habitats for a large array of marine and wildlife. The potential impacts on CA sea otters and other marine life due to events such as the 2015 oil spill in California should not be taken lightly.

CA Crude Oil by Rail Shipments and Railway Accidents

CA Crude Oil by Rail Shipments and Railway Accidents

By Kyle Ferrar, Western Program Coordinator, FracTracker Alliance

Incidents in California involving oil-by-rail cars increased from 3 in 2011 to 25 in 2013. There were 24 incidents within the first 6 months of 2014, and oil spills from rail cars increased from 98 in 2010 to 182 in 2013.1 With such an increase in oil train incidents, we have to ask what the state is doing to protect public safety.

CA Crude Oil by Rail – The Status Quo

California is currently far behind states like New Hampshire and Minnesota that have taken more control over in-state hazards, and have passed laws aimed at forcing rail and pipeline companies to abide by more rigorous emergency response measures instead of relying on the federal government and undertaking state-level spill response plans. These state movements are in response to the existing federal oversight, which critics cite as inadequate.2

State environmental health officials have acknowledged the dangers of a derailment, but have downplayed the risk – comparing the hazard of an incident to be similar to ethanol or gasoline, based on volatility. They do not believe oil train derailments are as hazardous as other materials transported by rail such as chlorine or ammonia. The bigger concern, though, is the huge volume of Bakken crude oil that is being shipped by rail. A recent report by the State of California Interagency Rail Safety Working group acknowledged this and identified key vulnerabilities along CA rail lines; Destinations of the crude trains in CA are the Bay Area via the Feather River or Donner Pass, Bakersfield via the Tehachapi Pass, and Los Angeles via the same route. These routes pass through the state’s most densely populated areas, as well as through some of the state’s most sensitive ecological areas, and each route has at least one high hazard area for derailments. Other issues identified include the impact of earthquakes on trains and rail lines and a shortage of emergency response capacity.

At-Risk Populations

A recent report by the Natural Resources Defense Council used census data to identify at risk-populations for communities living near the rail lines that can be used for transporting shipments. The analysis identified a total of nearly four million people in the Bay Area and the Central Valley alone that live within 1 mile (the U.S. DOT isolation zone for a crude tanker fire) of a crude shipment rail line. The authors go on to provide the following recommendations to prevent crude oil train accidents:

  1. Remove Defective, Dangerous Tankers from Crude by Rail Service
  2. Impose Safer Speed Limits
  3. Reroute Around Sensitive Areas
  4. Provide Emergency Responder Resources
  5. Make Additional operational Safety and Oversight Improvements
  6. Exercise Local Government Powers4

Crude Oil Shipment Trends

Support of these recommendations is most important as more crude shipments in CA are on the horizon. A recent permit application by the Phillips 66 oil company included a proposal to use Amtrak passenger lines to transport Bakken crude through the San Francisco Bay Area. A review of the proposal by Hinman Consulting Engineers found that over the next 30 years, there is an approximate 28% risk of derailment in the heavily populated stretches of Berkeley, Emeryville, Oakland, Santa Clara, San Jose and others. This estimate is assuming there is no increase in shipping volumes. The damage of an accident was estimated by the researchers, and the analysis showed that approximately 47,000 households and $22 billion in improved property value lay within the projected blast zone, 1000 feet from the railway. A projection of the damage from a single accident estimated that an average of 117 households along with $244 million in property value could be destroyed. Hinman also stated that “this figure does not include loss of revenue, environmental cleanup costs, loss of human life, or other societal costs.”5 A proposal by Valero Refining Co. plans to ship 100 crude oil tank cars a day through downtown Sacramento and downtown Davis to Benicia.

Responses by CA Regulators and Railroads

To plan for this increase in rail traffic, Sacramento passed a shipping charge to prevent and manage spills that will result in $11 million in 2015. Another bill has been introduced to impose a second shipping fee on oil companies to train and equip first responders to deal with major spills and fires on railroad lines. An additional bill was also authored requiring rail carriers to communicate more closely with state emergency officials about crude oil rail movements.6

The map below shows where spills and train accidents have occurred in CA since 2011. When zoomed out the map shows areas with higher incidence rates of accidents, but when zoomed to a higher resolution the map differentiates the accidents by year.7

CA Crude Oil by Rail and Railroad Accidents

View Full Screen

In the map above, a hot spot analysis shows the frequency of railroad accidents, such as derailments. Areas with the highest incidence rates are shown in yellow. The actual locations and descriptions with dates of these accidents can be seen by zooming in using the plus (+) button in the top left corner of the map, and clicking on a diamond symbol. Shown in red and green are the BNSF and other railroad lines used for the transportation of crude by rail.

BNSF Route

Figure taken from BNSF’s U.S. DOT disclosure to the state of California for emergency preparedness.9

From what little data has been released, it is clear that BNSF railway intends to ship two Bakken crude trains per week carrying more than one million gallons of crude through the CA counties of Butte, Contra Costa, Lassen, Modoc, Placer, Plumas, Sacramento, San Joaquin, and Yuba.8 The same information from Union Pacific Railroad has not been made public by the state of CA. The route shown in the figure to the right has been mapped in the FracTracker Alliance’s California Crude Shipment Routes and Railroad Accidents map above. From the map, you can see that there have been numerous accidents already on this BNSF rail line, particularly near Stockton and in the heavily populated North Bay Area.

References

  1. California Office of Emergency Services. 5/6/14. Historical HazMat Spill Notifications. Accessed 3/8/15.
  2. Douglas E. 6/16/14. 2 States Beef Up Oil-by-Rail and Pipeline Safety After String of Accidents. Inside Climate News. Accessed 3/9/15.
  3. Interagency Rail Safety Working Group. 6/10/14. Oil by Rail Safety in California. California Office of Emergency Services.
  4. Bailey D. 6/2014. It Could Happen Here: The Exploding Threat of Crude by Rail in California. Natural Resources Defense Council. Accessed 3/10/15.
  5. Reis E & Coughlin A. 6/6/2014. New Proposed Oil Transportation Calls for Rational, Risk-Based Mitigation Approach. Hinman Consulting Engineers. Accessed 3/11/15
  6. Bizjak T. 6/16/14. California to impose fee on crude oil rail shipments; funds to be used for spill prevention, cleanup. The Sacramento Bee. Accessed 3/10/15.
  7. U.S. DOT. 5/7/2014. Emergency Order. Docket No. DOT-OST-2014-0067. Accessed 3/10/15.
  8. California Public Utilities Commission. 2015. Railroad Safety and Operations. Accessed 3/8/15.
  9. U.S. DOT. 9/30/14. Re: U.S. Department of Transportation Emergency Order Docket Number DOT-OST-2014-0067 (Issued May 7, 2014). Accessed 3/10/15.

Hydraulic fracturing, stimulations, & oil & gas drilling unjustly burden Hispanic & non-white students

By Kyle Ferrar, CA Program Coordinator, FracTracker Alliance

As my first year in The Bay Area of California comes to a conclusion and the summer once again turns into fall I realize how much more this time of year meant for me living on the east coast. For us lucky ducks living in the Bay Area, fall is perpetual. With the California drought seasons blur together, but back home in Pennsylvania and New York, fall marks a much appreciated relief from 90°F+ days. Regardless of where you live certain fall activities are universal, including hockey, postseason baseball, football, and most importantly for kids – going back to school.

In California alone, almost 6.24 million students from kindergarten to 12th grade are enrolled and attend classes at one of the 10,366 state “campuses.” State-recognized schools range in size from under a dozen students to a maximum 2013/2014 enrollment of 5,229. When so many children are together in one space, they share much more than just the scholarship, social development, and the occasional but inevitable flu virus. They share the same environmental media (air, water, soil) and are therefore exposed to the same environmental contaminants.

To understand who among this vulnerable population is subject to potential health impacts, the FracTracker Alliance has put together a report analyzing the demographic characteristics of schools located near oil and gas extraction activity. An interactive map of the data that was analyzed is shown below, as are the points of the report. The full report can be found here:

 Disproportionate Burdens for Hispanic and Non-White Students in California

and here in Spanish:

Las Estimulaciones por Fracturación Hidráulica y la Perforación Petrolífera Cerca de las Escuelas y dentro de los Distritos Escolares de California son una Carga Desproporcionada para los Estudiantes Hispanos y Estudiantes No Blancos.

Fracked well near elementary school

Sequoia Elementary School located in Shafter, CA.

In the background, less than 1,200 feet from the school is
an oil well (API 403043765) that was hydraulically fractured.

Key Findings of School Analysis:

  • There are 485 active/new oil and gas wells within 1 mile of a school and 177 active/new oil and gas wells within 0.5 miles of a school.
  • There are 352,784 students who attend school within 1 mile of an oil or gas well, and 121,903 student who attend school within 0.5 miles of an oil or gas well.
  • There are 78 stimulated wells drilled within 1 mile of a school and 14 stimulated wells drilled within 0.5 miles of a school.
  • There are 61,612 students who attend school within 1 mile of a stimulated oil or gas well, and 12,362 students who attend school within 0.5 miles of a stimulated oil or gas well.
  • School Districts with greater Hispanic and non-white student enrollment are more likely to contain more oil and gas drilling and stimulation.
  • Schools campuses with greater Hispanic and non-white student enrollment are more likely to be closer to more oil and gas drilling and stimulation.
  • Students attending school within 1 mile of oil and gas wells are predominantly non-white (79.6%), and 60.3% are Hispanic.
  • The top 11 school districts with the highest well counts are located the San Joaquin Valley with 10 districts in Kern County and the other just north of Kern in Fresno County.
  • The two districts with the highest well counts are in Kern County; Taft Union High School District, host to 33,155 oil and gas wells, and Kern Union High School District, host to 19,800 oil and gas wells.
  • Of the schools with the most wells within a 1 mile radius, 8/10 are located in Los Angeles County.

Report Map

The interactive map below allows the user to compare the demographical profiles of school districts with oil and gas drilling and stimulation activity. Non-white enrollment percentages of school districts are displayed in shades of blue. Overlaid with red are the relative counts of stimulated and/or non-stimulated oil and gas wells. The highest counts of wells are hosted in school districts located in the Central (San Joaquin) Valley and along California’s south coast. Geologically, these areas lay above the Monterey Shale – the 50 million year sedimentary basin producing California’s oil reserves.