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CA Setbacks Map
Kyle Ferrar, MPH

People and Production: Reducing Risk in California Extraction

/by

Executive Summary

New research shows that low-income communities and communities of color that are most impacted by oil and gas extraction (Frontline Communities) in California are at an elevated risk for preterm birth, low birth weight, and other negative birth outcomes. This is in addition to the elevated risks of cancer; risks for respiratory, cardiovascular, and pulmonary disorders; and risks for eyes, ears, nose, throat, and skin irritation that Frontline Communities face, among others. Public health interventions including setback requirements for oil and gas drilling are necessary to address the environmental health endemics documented in Frontline Communities. 

This report focuses on the two immediate stakeholders impacted by oil and gas well drilling setbacks: Frontline Communities and oil and gas operators. First, using U.S. Census data this report helps to define the Frontline Communities most impacted by oil and gas extraction. Then, using GIS techniques and California state data, this report estimates the potential impact of a setback on California’s oil production. Results and conclusions of these analyses are outlined below.

  • Previous statewide and regional analyses on proximity of oil and gas extraction to various demographics, including analyses included in Kern County’s 2020 draft EIR, have inadequately investigated disparate impacts, and have published erroneous results.
  • This analysis shows that approximately 2.17 million Californians live within 2,500’ of an operational oil and gas well, and about 7.37 million Californians live within 1 mile. 
  • California’s Frontline Communities living closest to oil and gas extraction sites with high densities of wells are predominantly low income households with non-white and Latinx demographics.
  • The majority of oil and gas wells are located in environmental justice communities most impacted by contaminated groundwater and air quality degradation resulting from oil and gas extraction, with high risks of low-birth weight pregnancy outcomes.
  • Adequate Setbacks for permitting new oil and gas wells will reduce health risks for Frontline Communities.
  • Setbacks for permitting new oil and gas wells will not decrease existing California oil and gas production.
  • Phasing out wells within setback distances will further decrease health risks for Frontline Communities.
  • Phasing out wells by disallowing rework permits within a 2,500’ setback distance will have a minimal impact on overall statewide oil production, estimated at an annual maximum loss of 1% by volume.
  • Setbacks greater than 2,500’ in combination with other public health interventions are necessary to reduce risk for Frontline Communities.
  • Based on the peer reviewed literature, a setback of at least one mile is recommended.

 

Introduction

The energy focused on instituting policies to protect the health of Frontline Communities in California from the negative impacts of oil and gas extraction is at an all-time high. In August 2020, Assembly Bill 345 was heard in the State Senate’s Natural Resources Committee, but was blocked from reaching the Senate floor for a vote. The bill would have required the Geologic Energy Management Division in the Department of Conservation (CalGEM) to establish a minimum setback distance between oil and gas production and related activities and sensitive receptors like homes, schools, and hospitals. While this strong effort to establish health and safety setbacks through the state legislature may have failed, the movement has paved the way for local actions. Additionally, California is in the midst of a statewide public health rule-making process to address the health impacts of oil and gas extraction currently experienced by Frontline Communities. 

In related advocacy, Frontline Community groups in California recommended a minimum 2500’ setback based on scientific studies, including a 2015 report by the California Council on Science and Technology which identified “significant” health risks at a distance of one-half mile from drill sites. A recent grand jury report from Pennsylvania recommended 5,000’ setbacks, with 2,500’ as a minimum requirement to address the most impacted communities. Additionally, the state of Colorado has recently adopted 2,000’ setbacks for homes and schools, while the existing 2,000’ setback has had minimal impacts on oil and gas production. 

In September 2020, Governor Newsom declared the deadline for the first draft of the pre-regulatory rule-making report will be the first of January 2021. FracTracker Alliance has therefore completed an updated assessment of  the Frontline Communities most impacted by oil and has projected the potential impact on oil and gas extraction operations. An interactive map of oil and gas activity and Frontline Communities is shown below in Figure 1. The map identifies the operational (active, idle, and new) oil and gas wells located within 2,500’ and 1 mile buffer zones from sensitive receptors, defined as homes, schools, licensed daycares and healthcare facilities.

The impacts of oil and gas drilling do not stop at 2,500’, as regional groundwater contamination and air quality degradation of ozone creation and PM2.5 concentrations are widespread hazards of oil and gas extraction. Phasing out wells within 2,500’ of homes will reduce the negative health effects for the Frontline Communities bearing the brunt of the risks associated with living near oil and gas wells, as well as reduce regional environmental hazards. These risks include over 24 categories of health impacts and symptoms associated with 14 bodily systems, including eyes, ears, nose, and throat; mental health; reproduction and pregnancy; endocrine; respiratory; cardiovascular and pulmonary; blood and immune system; kidneys and urinary system; general health; sexual health; and physical health among others. The most regularly documented health outcomes include mortality, asthma and respiratory outcomes, cancer risk including hematological (blood) cancer, preterm birth, low birth weight and other negative birth outcomes.

The interactive map below in Figure 1 shows the operational oil and gas wells located within 2,500’ of sensitive receptors, including homes, schools, healthcare facilities, prisons, and permitted daycares. Overall in the state of California, 16,724 operational (8,618 active, 7,786 idle, and 320 new) wells are located within the 2,500’ setback. Of the total ~105,000 operational (62,000 active, 37,400 idle, and 6,000 new), about 16% are within the setback. These wells accounted for 12.8% of the total oil/condensate produced in California in 2019. Table 1 below shows the counties where these wells are located, by well permit status. It bears noting that these figures on well location and production represent only a snapshot of current industry activity. As discussed below, current setback proposals would provide a phase out period for existing wells that would greatly reduce any immediate impact on production. Further, directional and even horizontal drilling is common in California, meaning operators can relocate their surface drilling equipment to safer distances and still access oil and gas reserves to maintain production.   

 

Table 1. Status of wells within the 2,500’ setback zone, by county. The table shows the counts of wells located within the 2,500’ setback from homes and other sensitive receptors, broken out by the status of the wells.

  Well Count by Status
County Active New Idle
Kern 3,501 234 2,171
Los Angeles 2,580 29 3,006
Orange 914 13 816
Ventura 534 7 600
Santa Barbara 198 17 241
Los Angeles Offshore 168 2 51
Glenn 133   76
San Joaquin 97   71
Monterey 88 9 95
Fresno 86 6 137
Sutter 73   71
Tulare 65 1 30
Colusa 47   80
Tehama 38   34
Solano 30 0 65
Sacramento 22 1 38
San Bernardino 14   29
Humboldt 12   11
Alameda 7   3
Contra Costa 5 1 16
San Benito 3   4
San Luis Obispo 2   14
Yolo 1   13
Grand Total 8,618 320 7,786

 

View map fullscreen

Figure 1. Map of California operational oil and gas wells with 2,500’ and one mile setback distances. One mile setbacks are included as a minimum recommendation of this report based on peer reviewed literature. This report recommends the state of California consider one mile as a minimum setback distance to protect Frontline Communities. As you zoom into the map additional, more detailed layers will appear.

Methods (Quick Overview)

In this article we conducted spatial analyses using both the demographics of Frontline Communities and the amount of oil produced from wells near Frontline Communities. This assessment used CalGEM data (updated 10/1/20) to map the locations of operational oil and gas wells and permits, as shown above in Figure 1. The analyses of oil production data utilized CalGEM’s annual production data reporting barrels of oil/condensate. GIS analyses were completed using ESRI ArcGIs Pro Ver. 2.6.1 with data projected in NAD83 California Teale Albers.

Wells within 2,500’ and 1 mile of sensitive receptors were determined using GIS techniques. This report defines sensitive receptors as residences, schools, licensed child daycare centers, healthcare facilities. Sensitive receptor datasets were downloaded from California Health and Human Services, and the California Department of Education. 

We used block group level “census designated areas” from American Community Survey (2013-2018) demographics to estimate counts of Californians living near oil and gas extraction activity. Census block groups were clipped using the buffered datasets of operational oil and gas wells. A uniform population distribution within the census blocks was assumed in order to determine the population counts of block groups within 2,500’ of an operational oil and gas well, 2,500’ to 1 mile from an operational well, and beyond 1 mile from an operational well. Census demographics and total population counts were scaled using the proportion of the clipped block groups within the setback area (Areal percentage = Area of block group within [2,500’; 2,500’-1 mile; Beyond 1 mile] of an operational well / Total area of block group). 

This conservative approach provided a general overview of the count and demographics of Californians living near extraction operations, but does little to shed light on most impacted Frontline Communities; specifically urban areas with dense populations near large oil fields. More granular analyses at the local level were necessary to address the spatial bias resulting from non-uniform census block group dimensions and population density distributions, as well as the distribution of operational oil and gas wells within the census block groups. Consequently, we conducted further analysis utilizing customized sample areas for each oil field, which were selected manually using remote sensing data. Full census blocks were used to summarize the actual areas and the urban populations constituting the majority of Frontline Communities. 

In the localized, static maps that follow, the census blocks included in the population summaries are shown in pink, while the surrounding census blocks are shown in blue. As seen in Table 2, census data for this initial environmental justice assessment was limited to “Race” (Census Table XO2), “Hispanic or Latino Origin” (Census Table XO3) and several other indicators including “Annual Median Income of Households” (Census Table X19) and “Poverty” (Census Table X17).

Results and Discussion

California Statewide Analysis

Demographics

As a baseline, it is important to provide statewide estimations to track the total number of Californians living near oil and gas extraction operations. This analysis showed that about 2.17 million Californians live within 2,500’ of an operational oil and gas well, and about 7.37 million Californians live within 1 mile. The demographics of these communities at and between these distances is shown below in Table 2, alongside demographic estimates of the California population living beyond 1 mile from an oil and gas well. Census block groups closer to oil and gas wells have higher proportions of Non-white (calculated by subtracting “White Only” from “Total Population”) and Latinx (“Hispanic or Latino Origin”) populations, as well as higher proportions of low-income households, based on both median annual income and poverty thresholds. The analysis show that communities living closer to oil and gas wells have higher percentages of non-white and Latinx populations when compared to the population living beyond 1 mile from an operational oil and gas wells. Communities closer to oil and gas wells are also more likely to be closer to the poverty threshold with lower median annual household incomes.

 

Table 2. The table shows statewide demographics at multiple distances from operational oil and gas wells. Included are estimates of the non-white and Latinx proportions of the populations within set distances from operational oil and gas wells. The percentage of populations within several poverty thresholds were also summarized, along with median annual household income and age.

  Distance from an operational oil and gas well
Indicators of Disparity Within 2,500′ 2,500′ – 1 Mile Beyond 1 Mile (Statewide)
Demographics:  Non-white 44.44% 43.56% 39.16%
Demographics:  Latinx 43.25% 44.97% 37.79%
Poverty:  Under Poverty Threshold 15.01% 14.97% 14.12%
Poverty:  Under 1.5X Poverty Threshold 24.31% 24.85% 23.25%
Poverty:  Under 2X Poverty Threshold 33.59% 34.25% 32.17%
Median Annual Household Income < $40k 30.09% 30.73% 28.72%
Median Annual Household Income <$75k 53.53% 54.36% 51.76%
Age:  0-5 years 6.08% 6.12% 6.37%
Age:  <18 years 21.54% 22.12% 23.39%
Age:   65+ 13.17% 13.11% 13.68%
Demographics: White only 55.56% 56.44% 60.84%

 

CalEnviroScreen

CalGEM operational wells data was also overlaid on CalEnviroScreen 3.0 (CES) indicators of environmental health. CES is provided by the Office of Environmental Health Hazard Assessment (OEHHA), on behalf of the California Environmental Protection Agency (CalEPA).

CalEnviroScreen data, like U.S. Census data, is also aggregated at the census block group level. While this data can also suffer from the same spatial bias as the statewide analysis above, CES is still very useful to visualize and map the regional pollution burden to assess disparate impacts. The results of the analysis are shown below in Table 3. Counts of operational oil and gas wells for ranges of CES percentile scores. Higher percentiles represent increased environmental degradation or negative health impacts as specified. Of note, the majority of operational oil and gas wells are located in census tracts with the worst scores for air quality degradation and high incidence of low birth weight.

The large number of wells located in the 60-80th percentile rather than the worst (80-100th percentile) is a result of spatial bias, and the many factors that are aggregated to generate the CES Total Scores. These factors include relative affluence and other indicators of socio-economic status. The majority of the worst (80th-100 percentile for Total CES Score) census block groups are located in low-income urban census block groups, many in Northern California cities that do not host urban drilling operations.

This spatial bias results from edge effects of census block groups, where communities living near oil and gas extraction operations may not live in the same census block groups as the oil and gas wells, and are therefore not counted. The authors would recommend future analyses be designed that use CES data to assess disparate impacts in the census block groups most impacted by oil and gas extraction. Neighboring census block groups that do not physically contain operational wells still suffer the consequences of proximity.

For the asthma rankings, the majority of wells are located in the best CES 3.0 percentile (0-20th percentile) for Asthma. While there is much urban drilling in Los Angeles, the spatial bias in this type of analysis gives more weight to the majority of oil and gas wells that are located in rural areas, which historically have much lower asthma rates. This is a result of the very high incidence of asthma in cities without urban drilling such as the Bay Area and Sacramento (80-100th percentile).

 

Table 3. Counts of operational oil and gas wells in select CalEnviroScreen 3.0 indicators census tracts.

  Operational Well Counts by CES3.0 Percentile
  0-20%ile 20-40%ile 40-60%ile 60-80%ile 80-100%ile
PM2.5 Air Quality Degradation 5,708 4,237 16,614 7,089 69,987
Ozone Air Quality Degradation 2,238 5,435 6,107 9,898 79,957
Contaminated Drinking Water 1,019 1,675 53,452 6,214 41,206
High Incidence of Low Birth Weight 10,186 13,368 14,995 3,236 58,036
High Incidence of Asthma 40,247 19,827 18,902 4,867 19,792
Total CES 3.0 1,583 5,756 15,671 65,356 12,985

 

Spatial Bias

Using census data to assess the demographics of those communities most affected by oil and gas drilling can produce misleading results both because of how census designated areas (census tracts and block groups) are designed and because of the uneven distribution of residents within tracts. For example, the majority of Californians who live closest to high concentrations of oil and gas extraction, such as the Kern River oil field, do so in residentially zoned cities and urban settings. In most Frontline Communities the urban census designated areas do not actually contain many wellsites. Instead urban census designated areas are located next to the “estate” and “industrial” (including petroleum extraction) zoned census designated areas that contain the well-sites. 

Estate and industrially zoned census designated areas contain the majority of well-sites in Kern County. They are much larger than residentially zoned areas with very low population densities and higher indicators of socioeconomic status. Population centers within the estate zoned areas are often located on the opposite end and farther from well sites than the lower income communities and communities of color living in the neighboring, residentially-zoned census designated areas (e.g., Lost Hills and Shafter). In these cases the statewide demographic summaries above misrepresent the Frontline Communities who are truly closest to extraction operations. Localized environmental justice demographics assessments can also be manipulated in this way.

For instance, The 2020 Kern County draft EIR (chapter 7 PDF pp. 1292-1305) used well counts aggregated by census tracts to conclude that wells in Kern County were not located in disparately impacted communities. Among other requirements for scientific integrity, the draft Kern EIR fails to take into account how the shape, size, and orientation of census designated areas affect the results of an environmental justice assessment. In addition, the EIR uses low-resolution data summarized at the census tract level. Census tracts are much too large to be used to investigate localized health impacts or disparities. Using these blatantly inadequate methods, the draft EIR even claimed Kern County’s oil and gas wells are predominantly located in higher income, white communities, which is outright wrong. For more specific criticisms of the Draft EIR read the FracTracker analysis of the 2020 Kern County EIR.

Results from these types of analyses can be very misleading. Using generalized methods of attributing wells to specific census designated areas does little to identify the communities most impacted by the localized environmental degradation resulting from oil and gas extraction operations, particularly when large census areas such as census tracts are used. 

This report therefore takes a different approach, focusing directly on California’s most heavily drilled communities. To understand who and which communities are most harmed by the large-scale industrial oil and gas extraction operations in California, spatial analyses must be refined to focus individually on the communities closest to the highest density extraction operations. For the analyses below, census block groups within 2,500’ of ten different Frontline Communities, all located near some of California’s largest oil and gas fields, were manually identified. The selected block groups’ major population centers were all located within the 2,500’ buffers. Unlike the statewide analysis above, the localized analyses below do not assume homogenous population distributions. Using these methods, FracTracker has identified and demographically described some of the most vulnerable California communities most at risk to the impacts of oil and gas extraction. In the maps below, the “case” census block groups used to generate descriptive demographic summaries of at risk communities bordering extraction operations are outlined in pink, while surrounding census block groups are outlined in light blue.

Well Density

The analyses above are important to understand some of the public health risks of living near oil and gas drilling in California. Yet the methods above used statewide aggregation of well counts and static buffers that do not not show the spectrum of risk resulting from well density. Numerous Frontline Communities in California are within 1 mile or even 2,500’ of literally thousands of oil and gas wells. Conversely, there are many census areas in California that have been included within the spatial analysis of the full state, as described above, located near a single low producing well. Therefore the above methods conservatively summarize demographics and dilute the signal of disparate impacts for low income communities of color. Those methods are not able to differentiate between such scenarios as living near one low-producing well in the Beverly Hills golf course versus living in the middle of the Wilmington Oil Field. 

As with any toxin, the dosage determines the intensity of the poison. In environmental sciences, increasing exposure to toxins by increasing the number of sources of a toxin can increase the dosage and therefore the severity of the health impact. The impact of well density has been documented in numerous epidemiological studies as a significant indicator of negative health outcomes, including recently published reports from Stanford University and The University of California – Berkeley linking adverse birth outcomes with living near oil and gas wells in California (Tran et. al 2020, Gonzalez et. al 2020). Therefore the rest of this report focuses on the Frontline Communities living near large oil extraction operations–i.e., oil fields with high densities of operational oil and gas wells. 

 

Kern County

Toggle between the sections below by clicking in the upper left corner of the title bar. 

The City of Shafter, California, is located near more than 100 operational wells in the North Shafter oil field, as shown below in the map in Figure 2. Technically, the wells are located within a donut-shaped census block group (outlined in blue) that surrounds the limits of the urban census block groups (outlined in pink). Shafter’s population of nearly 20,000 is over 86% Latinx, but the surrounding “donut” with just 2,000 people is about 70% Latinx, much wealthier, and with very low population density. The other neighboring rural census areas housing the rest of the Shafter oil field wells follow this same trend. 

An uninformed analysis, such as the Kern County EIR, would conclude that the 2,000 individuals who live within the blue “donut” are at the highest risk, because they share the same census designated area as the wells. Notably, the only population center of this census block group (or census tracts, which follow this same trend) is at the opposite end of the block group, farthest from the Shafter oil field. Instead, the most at-risk community is the urban community of Shafter with high population density; the census block groups within the pink hole of the donut contain the communities and homes nearest the North Shafter field.

Figure 2. The City of Shafter, California is located just to the south of the North Shafter oil field. The map shows the 2,500’ setback distance in tan, as well as the census block groups in both pink and blue. Pink block groups show the urban case populations used to generate the demographic summaries. 

The cities of Lost Hills, Arvin, and Taft are all very similar to Shafter. The cities have densely populated urban centers located within or directly next to an oil field. In the maps below in Figures 3 readers can see the community of Lost Hills next to the Lost Hills oil field. Lost Hills, like the densely populated cities of Arvin and Taft, are located very close to large scale extraction operations. Census block groups that include the most impacted area of Lost Hills is outlined in pink, while surrounding low population density census block groups are shown in blue. The majority of the areas outlined in blue are zoned as “estate” and “agriculture” areas. The outlines of the city boundaries are also shown, along with 2,500’ and 1 mile setback distances from currently operational oil and gas wells.

Lost Hills is another situation where a donut-shaped census area distorts the results of low resolution demographics assessments, such as the one conducted by Kern County in their 2020 Draft EIR (PDF pp. 1292-1305). Almost all of the wells within the Lost Hills oil fields are just outside of a 2,500’ setback, but the incredibly high density of extraction operations results in the combined impact of the sum of these wells on degraded air quality. While stringent setback distances from oil and gas wells are a necessary component of environmental justice, a 2,500’ setback on its own is not enough to reduce exposures and risk for the Frontline Community of Lost Hills. For these Frontline Communities, a setback needs to be much larger to reduce exposures. In fact, limiting a public health intervention to a setback requirement alone is not sufficient to address the environmental health inequities in Lost Hills, Shafter, and other similar communities. 

Lost Hill’s nearly 2,000 residents are over 99% Latinx, and over 70% of the households make less than $40,000 in annual income (which is substantially less than the annual median income of Kern County households [at $52,479]). The map in Figure 3 shows that the Lost Hills public elementary school is located within 2,500’ of the Lost Hills oil field and within two miles of more than 2,600 operational wells, in addition to the 6,000 operational wells in the rest of the field. 

The City of Arvin has 8 operational oil and gas wells within the city limits, and another 71 operational wells within 2 miles. Arvin, with nearly 22,000 people, is over 90% Latinx, and over 60% of the households make less than $40,000 in annual income. 

Additionally the City of Taft, located directly between the Buena Vista and Midway Sunset Fields, has a demographic profile with a Latinx population at least 10% higher than the rest of southern Kern County. 

Lost Hills, Arvin, and Taft are among the most impacted densely populated  areas of Kern County and represent the most Kern citizens at risk of exposure to air quality degradation from oil and gas extraction.

In all of these cases, if only census tract well counts are considered, like in the 2020 Kern County draft EIR, these Frontline Communities will be completely disregarded. Census tracts are intentionally drawn to separate urban/residential areas from industrial/estate/agricultural areas. The census areas that contain the oil fields are very large and sparsely populated, while neighboring census areas with dense population centers, such as these small cities, are most impacted by the oil and gas fields.

Figure 3. The Unincorporated City of Lost Hills in Kern County, California is located within 2,500’ of the Lost Hills Oil Field. The map shows the 2,500’ setback distance in tan, as well as the census block groups in both pink and blue. Pink block groups show the urban case populations used to generate the demographic summaries. 

The City of Bakersfield is a unique scenario. It is the largest city in Kern County and as a result suburban developments surround parts of the city. Urban flight has moved much of the wealth into these suburbs. The suburban sprawl has occurred in directions including North toward the Kern River oil field, predominantly on the field’s western flank in Oildale and Seguro. In the map below in Figure 4, these areas are located just to the north of the Kern River.

This is a poignant example of the development of cheap land for housing developments in an area where oil and gas operations already existed; an issue that needs to be considered in the development of setbacks and public health interventions and policies. This small population of predominantly white, middle class neighborhoods shares similar risks as the lower-income Communities of Color who account for the majority of Bakersfield’s urban center. Even though these suburban communities are less vulnerable to the oppressive forces of systemic racism, real estate markets will continue to prioritize cheap land for development, moving communities closer to extraction operations. 

Regardless of the implications of urban sprawl and suburban development, it is important to no disregard the risks to  the demographics of the at-risk areas of the city of Bakersfield are predominantly Non-white (31%) and Latinx (60%), particularly as compared to the city’s suburbs (15% Non-white and 26% Latinx). About 33,000 people live in the city’s northern suburbs, and another 470,000 live in Bakersfield’s urban city center just to the south of the 16,500 operational wells in the Kern River, Front, and Bluff oil fields. The urban population of Bakersfield is a large Frontline Community exposed to the local and regional negative air quality impacts of the Kern River and numerous other surrounding oil fields.

Figure 4. Map of the city of Bakersfield in Kern County, California located between several major oil fields including the Kern Front oil field. The map shows the 2,500’ setback distance in tan, as well as the census block groups in both pink and blue. Pink block groups show the urban case populations used to generate the demographic summaries.  

 

Southern California

The City of Ventura and the proximity of the Ventura oil field is a similar situation to cities in Kern. The urban center of Ventura is bisected by the Ventura oil field’s nearly 1,200 operational wells. While over 70% of the city’s population is Latinx, the very sparsely populated census areas also containing portions of the oil field are 34% Latinx. 

In the map below in Figure 5, take note of the population distribution within the portion of the city closest to the oil field versus the census areas to the east. While a statewide or less granular analysis would assume an evenly distributed population density, in this localized analysis, it is clear that the most vulnerable Frontline Communities are the urban centers closest to the oil fields. Even though the census blocks to the east contain oil and gas wells, the populations are less at risk because the population centers are located farther from the oil field.

Figure 5. Ventura Oil Field in Ventura, California census areas within the 2,500’ setback area. The map shows the 2,500’ setback distance in tan, as well as the census block groups in both pink and blue. Pink block groups show the urban case populations used to generate the demographic summaries. 

Los Angeles

In Los Angeles County, Inglewood, Wilmington, Long Beach, and Los Angeles City are some of the largest oil and gas fields. There are many areas in Los Angeles where a single low-producing well is located in an upper middle class suburb, on a golf course, or next to the Beverly Hills High School. 

While all well sites present sources of exposure to volatile organic compounds (VOCs) and other air toxics, these four oil fields have incredibly high densities of oil and gas wells in urban neighborhoods. The demographics of the Frontline Communities located within 2,500’ of these major fields are presented below in Table 4. These areas are additionally lower income communities; for example, over 50% of annual household incomes in the census areas surrounding the Los Angeles City oil field are below $40,000, while the Los Angeles County median annual income is over $62,000. 

Table 4. Demographics for Frontline Communities living within 2,500’ of Los Angeles’s major oil and gas fields along with counts of operational wells in the fields are shown in the table. The demographic “Latinx” is the count of “Hispanic or Latino Origin” population, and “non-white” was calculated by subtracting “white only” from “total population.”

 

Oil Field Well Count Non-white (%) Latinx (%)
Inglewood 914 62% 11%
Wilmington 2,995 56% 63%
Long Beach 687 50% 30%
Los Angeles City 872 69% 59%
Ventura 1,193 10% 72%

 

Toggle between the sections below by clicking in the upper left corner of the title bar. 

Figure 6. Inglewood Oil Field Frontline Community, Inglewood, California census areas within a 2,500’ setback area. The map shows the 2,500’ setback distance in tan, as well as the census block groups in both pink and blue. Pink block groups show the urban case populations used to generate the demographic summaries.

Figure 7. Wilmington Oil Field Frontline Community, Wilmington, California census areas within a 2,500’ setback area. The map shows the 2,500’ setback distance in tan, as well as the census block groups in both pink and blue. Pink block groups show the urban case populations used to generate the demographic summaries.

Figure 8. Long Beach Oil Field Frontline Community, Long Beach, California census areas within a 2,500’ setback area. The map shows the 2,500’ setback distance in tan, as well as the census block groups in both pink and blue. Pink block groups show the urban case populations used to generate the demographic summaries.

Figure 9. Los Angeles City Oil Field Frontline Community census areas within a 2,500’ setback area. The map shows the 2,500’ setback distance in tan, as well as the census block groups in both pink and blue. Pink block groups show the urban case populations used to generate the demographic summaries.

 

Production

The creation of public health policies such as 2,500’ setbacks to help protect Frontline Communities is controversial in California as many state legislators are still beholden to the oil and gas industry. The industry itself pushes back strongly against any proposal that could affect their bottom line, no matter how insignificant the financial impact may be. When AB345 was proposed, the industry’s lobbying organization Western States Petroleum Association claimed that institution of 2500’ setbacks would immediately shut down at least 30% of California’s total oil production. This number is an outright fabrication. 

As shown in Table 1 above, a 2,500’ setback would impact the less than 9,000 active and new wells; 42% in Kern County and 29% in Los Angeles County. Ventura and Orange Counties are a distant 3rd and 4th, respectively. These counts are further broken down by field in Table 5 below. Statewide these wells accounted for just 12.8% of California’s current oil production by volume (as reported in barrels of oil/condensate by CalGEM), which is much smaller than the wholly unsubstantiated 30% decline claimed by industry.

 

Table 5. Counts of wells by well status for operational (active, idle, and new) oil and gas wells located within a 2,500’ setback.  Fields include the count of wells within the 2,500’ setback and the amount of oil produced from those wells within the setback. The percentage of total oil from that field is also included.

 

Oil Field County Well Count Well Ct % of Total 2019 Oil Prod (BBLS) Oil Prod % of Total
Wilmington Los Angeles 2,514 83% 2,292,669 22%
Kern River Kern 1,338 9% 2,121,071 12%
Inglewood Los Angeles 891 97% 1,806,354 96%
Midway-Sunset Kern 1,892 10% 1,614,081 8%
Ventura Ventura 287 24% 1,202,764 31%
Long Beach Los Angeles 687 100% 1,036,506 100%
Brea-Olinda Los Angeles 695 97% 967,223 95%
Huntington Beach Orange 528 83% 753,494 42%
Placerita Los Angeles 448 100% 508,182 100%
Santa Fe Springs Los Angeles 304 99% 421,719 72%
Cat Canyon Santa Barbara 115 10% 418,697 36%
Beverly Hills Los Angeles 156 100% 351,877 100%
McKittrick Kern 334 18% 346,738 10%
Montebello Los Angeles 227 98% 318,657 97%
Fruitvale Kern 286 80% 316,184 75%
San Ardo Monterey 180 13% 313,339 4%
Torrance Los Angeles 219 100% 307,413 100%
Seal Beach Los Angeles 175 88% 282,790 74%
Shafter, North Kern 70 78% 267,256 66%
Edison Kern 520 41% 261,098 39%
Brentwood Contra Costa 4 100% 230,868 100%
Oxnard Ventura 124 82% 214,884 100%
Sansinena Los Angeles 162 100% 207,474 100%
Poso Creek Kern 320 16% 193,533 4%
Rosecrans Los Angeles 94 100% 174,720 100%
Rio Bravo Kern 80 74% 166,444 82%
Richfield Orange 231 100% 165,426 100%
Coyote, East Orange 81 100% 163,639 100%
San Vicente Los Angeles 48 100% 162,940 100%

 

In the case that setback regulations are crafted both to prohibit new drilling and to phase out existing operations within the setback distance, the industry would have the opportunity to respond with measures that preserve the majority of production volumes, particularly in the Central Valley. For example, in Kern County, the overwhelming majority of new wells drilled in 2020 are directional or horizontal; these drilling technologies would allow operators to access the same below ground resources from surface locations that are further away from and safer for communities. Further, for existing wells within the 2,500’ setback, current proposals would institute a phase out period. Existing wells could be allowed to continue to operate under the terms of their current permits but not allowed to expand or rework their operations to increase or extend production; alternatively (or in addition), well operators could continue for a prescribed timeframe formulated to allow them to recoup their investment (called “amortization”). 

Los Angeles

It is clear that the oil fields of Los Angeles would be the most impacted if setbacks phased out the wells responsible for the highest risk to Frontline Communities. The majority of Los Angeles’s urban oil fields are located entirely within 2,500’ of homes, schools, healthcare facilities and daycares. 

As shown above in Table 5, wells within the setback produce 96% of the oil in the Inglewood fields, 84% in the Long Beach field, and 100% of the oil in several other smaller fields. With the phase out of these wells, oil extraction would cease in these fields. Most of these fields produce very low volumes of oil and already have high counts of idle wells, 28% idle in Wilmington, 25% in Inglewood, and 56% in Long Beach for example. The sole outlier of this trend is the Wilmington field. The majority of production in the Wilmington field comes from wells located in the Long Beach harbor, enough of them located outside of the 2,500’ setback such that while 83% of the Wilmington field wells are within the 2,500’ setback, these wells account for only 22% of the field’s overall production. 

Kern County

The situation in Kern County is quite the opposite of Los Angeles, where the majority of operational wells are located within 2,500’ of homes, residences, and other sensitive receptors like healthcare facilities. In Kern, the overwhelming majority of wells are located beyond 2,500’ and even 1 mile from sensitive receptors. While the Midway-Sunset and Kern River fields have the most wells within the 2,500’ setback area, those wells make up a small percentage of the total operational wells in the fields. As can be seen in the map in Figure 1, wells within the 2,500’ setback zone in the large Kern oil fields are entirely located on the borders of the fields. Overall, a 2,500’ setback in Kern County would only affect 7.1% of active/new wells, accounting for 5.97% of the county’s production.  

The oil and gas industry and operators in states including Texas, Colorado, North Dakota, Pennsylvania, Ohio, West Virginia, New Mexico, and Oklahoma are very vocal of their ability to avoid surface disturbance and target oil and gas pools located under sensitive receptors (homes, schools, healthcare facilities, endangered species habitat etc.) using directional drilling. According to the industry, directional drilling has been used for nearly a century to extract resources from areas where surface disruption would impact sensitive communities and habitats. 

The same is true for California, especially in Kern County and especially recently. An October 2020 draft environmental impact report by the Kern County Planning and Natural Resource Department disclosed that in a dataset of 9,803 wells drilled from 2000 to 2020 by the California Resources Corporation, the majority of wells were drilled directionally (46%) or horizontally (10%), as opposed to vertically. More recent wells in the County have utilized directional and horizontal drilling even more heavily: a 2020 dataset of wells drilled county-wide indicates that 76% were drilled directionally and an additional 7% were drilled horizontally; only 17% were drilled vertically. These statistics indicate that, even if all wells neighboring Frontline Communities in Kern County were to be phased out (itself a small percentage of the total number of wells in the county), there would only be a small impact on Kern County oil production owing to the prevalence of non-vertical techniques that allow operators the flexibility to access reserves from different surface locations. As noted previously, if all oil production from within the 2,500’ setback zone were to be immediately eliminated statewide, it would mean a maximum decrease of just 12.8% of California’s current annual oil production. But the availability of directional and horizontal drilling in Kern County, where the lion’s share of all drilling statewide occurs, means it is more likely that the decrease in production will be significantly less than 12.8% and likely much less than 10%. 

Existing Well Phase Out

Any assertion that a 2,500’ setback would immediately affect oil production is baseless because current setback proposals would institute a phase out period for existing wells. For example, existing permitted wells could be allowed to continue to operate under the terms of their current permits but not allowed to expand or rework their operations to increase or extend production. Alternatively, under a policy approach known as amortization, well operators could continue for a prescribed timeframe formulated to allow them to recoup their investment.   

If wells within the setback distance are phased out pursuant to a “no rework” policy, operators would be afforded some time to maximize production in order to ensure that operators receive a sufficient return on their investment under the terms of their existing permits before they shut down. Under such an approach, older wells with increasing risks of fugitive emissions through leaks at the surface and well casing failures could be sequentially phased out by placing a ban on rework permits not required for maintenance or safety. CalGEM permitted well reworks, including sidetracks and deeper drills, increase production and the lifespan of wells. The catalog of rework permits can be found on the CalGEM website.

Based on CalGEM’s production data from 2018 and 2019, a phase out effectuated by disallowing well reworks would result in an annual reduction of less than 1% of total oil production. Of the 52,997 wells reporting  oil/condensate production volumes in 2018, 338 received a rework permit in the same year. In 2019, of the 48,860 wells reporting oil production volumes, 285 received rework permits. By volume, the wells that received rework permits accounted for 0.87% of oil production in 2018 and just 0.04% in 2019. 

Conclusion

The oil and gas industry in California has consistently pushed back against Frontline Communities who demand public health protections against emissions from oil and gas operations. This occurs even when there will be little to no impact reducing production. It is an industry policy to refuse any concessions and oppose all measures, even to protect public health, by leveraging the industry’s wealth at every level of the political hierarchy. 

Fatefully, 2020 has resulted in multiple wins for public health in California. While the failure of AB345 made it clear that the California state legislature is still beholden to the fossil fuel industry, the momentum has continued. Community grassroots groups in Ventura County successfully passed a 1,500’ setback ordinance for occupied dwellings and 2,500’ setbacks for sensitive receptor sites including healthcare facilities and schools. Just south of Ventura, the County of Los Angeles is also in the midst of a rule-making process that is considering multiple setbacks, including 1,000’ to 2,500’ distances. And a committee of the Los Angeles City Council just voted to develop a proposal that would phase out oil drilling across the city as a non-conforming use. 

While Ventura and Los Angeles are making progress, Kern County is creating a new process to streamline oil and gas well permitting and has even proposed to decrease the existing zone-specific 300’ setbacks from homes to 210’. 

Kern County Frontline Communities and the rest of California also deserve the same consideration as residents of Ventura and Los Angeles Counties. The research is clear that a setback of at least one mile in addition to more site specific public health interventions are necessary to reduce the negative health impacts resulting from these industrial operations within and neighboring Frontline Communities. 

By Kyle Ferrar, Western Program Coordinator, FracTracker Alliance

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Undermined: Voices from the Frontlines of Frac Sand Mining

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FracTracker and Public Lab, with support from Save the Hills Alliance, produced “Undermined,” an audio story featuring interviews with three residents impacted by the Hi-Crush Mine in Augusta, Wisconsin.

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Kyle Ferrar, MPH

Documenting emissions from new oil and gas wells in California

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Working with the environmental nonprofit Earthworks, FracTracker Alliance filmed emissions from oil and gas sites that have been issued permits in California under Governor Gavin Newsom since the beginning of 2019. Using state-of-the-art technology called optical gas imaging (OGI), we documented otherwise invisible toxic pollutants and greenhouse gas emissions (GHGs) being released from oil and gas wells and other infrastructure. This powerful technology provides further evidence of the negative consequences that come from each issued permit. Every single permit approval enabled by decisions made under Newsom can have substantial, visible impacts on local and regional air quality, contributes to climate change, and potentially exposes communities to health-harming pollution.

Despite a stated commitment to transition rapidly off fossil fuels, California has issued 7,625 permits to drill new oil and gas wells and rework existing wells since the beginning of 2019 — that is, on Governor Gavin Newsom’s watch. This expansion of the industry has clear implications for climate change and public health, as this article will demonstrate.

 

Intro

In collaboration with Consumer Watchdog, FracTracker Alliance has been periodically reporting on the number and locations of oil and gas wells permitted by Governor Newsom in California. In July of 2019, we showed how the rate of fracking under Governor Newsom had doubled, as compared to counts under former Governor Brown. Since then we have continued tracking the numbers and updating the California public via multiple news stories, blog reports, and with a map of new permits on NewsomWellWatch.com, where permitting data for the third quarter of 2020 has just been posted.

Now again, the rate of new oil and gas well permits issued by the California Geologic Energy Management division (CALGEM) continues to increase even faster in 2020, with permits issued to drill new oil and gas production wells nearly doubling since 2019. But what exactly does this mean for Frontline Communities and climate change? To answer this question, FracTracker Alliance and Consumer Watchdog teamed up with Earthworks’ Community Empowerment Project (CEP).

CEP’s California team worked with community members and grassroots groups to film emissions of methane and other volatile organic compounds (VOCs) emitted from oil and gas extraction sites, including infrastructure servicing oil and gas production wells such as the well-heads, separators, compressors, crude oil and produced water tanks, and gathering lines. Emissions of GHGs, such as methane, are a violation of the California Air Resources Board’s (CARB) California oil and gas rule (COGR), California Code of Regulations, Title 17, Division 3, Chapter 1, Subchapter 10 Climate Change, Article 4, § 95669, Leak Detection and Repair.

The emissions were filmed by a certified thermographer with a FLIR (Forward Looking Infrared) GF320 camera that uses optical gas imaging (OGI) technology. The OGI technology allows the camera to film and record visualizations of VOC emissions based on the absorption of infrared light. It is the exact same technology required by the U.S. EPA under the rule for new source performance standards and the by California Air Resources Board for Leak Detection and Repair (LDAR) to properly inspect oil and gas infrastructure. The video footage clearly shows the presence of a range of VOCs, methane, and other gases that are otherwise invisible to the naked eye.

The footage shown below is in greyscale and can appear grainy when the camera is being operated in high sensitivity modes, which is sometimes necessary to visualize certain pollution releases. The descriptions preceding each video explain what the trained camera operator saw and documented. A map of these sites is presented at NewsomWellWatch.com.

Newsom Well Watch interactive map

Navigate to the next slide using the arrows at the bottom of the map.

 

Find the story map, and more by clicking the image below.

 

Case Studies on Permitted Sites

Cat Canyon Tunnell Well Pad.

Earthworks’ California CEP thermographer visited this site in December of 2019, and just happened to arrive while the operator (oil and gas company) was conducting activities underground, including drilling new wells and reworking existing wells. In 2019 the operator, Vaquero Energy, was approved to drill 10 new cyclic steam wells and rework 23 existing oil and gas production wells at this site.

The footage shows significant emissions coming from an unknown source near the wellheads on the well pad; most likely these emissions were coming directly from the open boreholes of the wells. The emissions potentially include a cocktail of VOCs and GHGs such as methane, ethane, benzene, and toluene. This footage provides a candid view of what is released during these types of activities. The pollution shown appears to be the result of an uncontrolled source commonly resulting from drilling and reworking wells

Additionally, inspectors are rarely, if ever, present during these types of activities to ensure that they are conducted in accordance with regulations. The CEP camera operator reported the emissions and provided the OGI video to the Santa Barbara County Air Pollution Control District. By the time the inspector arrived, however, the drilling crew had ceased operations. The inspector did not detect any of these emissions, and as a result the operator was not held accountable for this large pollution release.

In the footage below, the emissions can be seen traveling over the fenceline of the well pad, swirling and mixing with the wind. This site is a clear example of what to look for in the following videos, since the emissions are so obvious. Fortunately, there are no homes or buildings in close proximity to this site, which potentially limited direct pollution exposure — although the pollution still degrades air quality and can pose an occupational health risk to oil field workers.

 

South Los Angeles Murphy Drill Site

The Murphy Drill Site in Los Angeles has been a long-standing nuisance and source of harmful pollution for neighbors in Jefferson Park. The site houses 31 individual operational wells, including 9 enhanced oil recovery injection wells and 22 oil and gas production wells, as shown below in the map in Figure 1. The wells are operated by Freeport-McMoran, while the site is owned by the Catholic archdiocese of Los Angeles. The site is within 200 feet of homes, playgrounds and a health clinic. There are over 16,000 residents within 2,500’ of the site, as well as a special needs high school, an elementary school, a hospice facility, and a senior housing complex.

Map of the California Murphy drill site

Figure 1. Map of the Murphy drill site

The neighborhoods near the Murphy Site are plagued with strong chemical odors, including those linked to oil and gas operations (such as the “rotten egg” smell of health-harming hydrogen sulfide), most likely from the toxic waste incinerators on site. Community members have suffered from respiratory problems, chronic nosebleeds, skin and eye irritation, and headaches. The operators have received multiple violations, including for releasing emissions at concentrations 400% over the allowable limit of methane and VOCs. Some of these violations were the direct result of complaints from the community and the Earthworks CEP team, which filmed pollution from the site on multiple occasions. Yet despite receiving “Notices of Violations” and fines, Freeport-McMoran has been allowed to continue operations. In OGI footage, emissions are visible continuously escaping from a vent on the equipment. While this leak has been addressed by regulators, each new visit to this site tends to result in finding new uncontrolled emissions sources.

 

South Los Angeles Jefferson Drill Site

The Jefferson drill site is very similar situation to the Murphy Site. The sites have the same operator, Freeport-McMoran, and surrounding neighborhoods in both locations have suffered from exposure to toxic pollution as well as odors, truck traffic, and noise. The Jefferson site has 49 operational wells, including 15 enhanced oil recovery wells, as shown below in Figure 2. In 2013 the operator reported using over 130,000 pounds of corrosive acids and other toxic chemicals for enhanced oil recovery operations. Regardless, an environmental impact report has never been completed for this site.

Map of the Jefferson drill site in South Los Angeles

Figure 2. Map of the Jefferson drill site in South Los Angeles.

 

The site is located 3 feet from the nearest home, and the surrounding residential buildings are considered “buffers” for the rest of the neighborhood, which also includes an elementary school about 700 feet away. The site was nearly shut down by the City of Los Angeles in 2019, but is currently still operational. In 2019 the site was even issued a permit to rework an existing well in order to increase production from the site. The footage below shows a large, consistent release of pollution from equipment on the well pad. The plume appears above the site and is visible against the background of the sky. The Earthworks CEP team reported the pollution to the South Coast Air Quality Management District (SCAQMD), which conducted an inspection, stopped the leak, and issued a notice of violation and a fine. It is not clear exactly how long this pollution problem had gone unnoticed or unaddressed, and it is not unlikely that another leak will occur without being quickly identified.

 

Wilmington E&B Resources WNF-I Site on Main St

The WNF-I drilling site is located in Carson in the City of Los Angeles. Operated by E&B Natural resources in the Wilmington oil and gas field, the site houses 35 operational oil and gas wells, including 12 enhanced oil recovery wells and a wastewater disposal well. There is also extensive above-ground infrastructure on the well site, including a large, high-volume tank battery used to store oil and wastewater produced from numerous oil and gas wells in the area.

Using OGI, Earthworks identified a large pollution release from the top of the largest tank. In the video footage, the plume or cloud of gases (likely methane and VOCs) can be seen hovering over the site and slowly dispersing over the fence-line into the communities of West Carson and Avalon Village. Despite clear operational problems, CalGEM approved this site for two rework permits in 2019 and then three re-drills (known as sidetracks) of existing wells in 2020 in order to increase production. The SCAQMD reports that they have inspected this facility, but it is not clear whether this major uncontrolled source has been stopped.

 

Long Beach Signal Hill Drill Site

At an urban drilling site in the neighborhood of Signal Hill in Los Angeles County, Earthworks filmed and documented pollution releases from numerous pieces of equipment. The site includes 15 operational oil and gas wells operated by Signal Hill Petroleum and The Termo Company. Emissions of gases (likely methane and VOCs) were documented on infrastructure from both operators. At this site, Signal Hill Petroleum received a permit in April 2019 to rework an operational well to increase production. That well is located less than 70’ from a home.

While this site is located within Los Angeles County, it is outside the jurisdiction of the city itself. Any local protections for drilling sites within the Los Angeles city limits are not afforded to communities such as Signal Hill. This area that includes the Signal Hill oil field and the Signal Hill portion of the Long Beach oil field, where many well sites are unmaintained and oversight is limited — conditions that in turn can result in corrosion and pollution leaks. The SCAQMD inspected this site and reported that these uncontrolled sources of emissions have been addressed by the operator, but it is not clear if the emission have stopped.

Midway-Sunset Crail Tank Farm

This tank farm, located in Kern County, services a number of wells operated by Holmes Western Oil Corporation on the outskirts of the Mid-Way Sunset Field. Of the wells serviced by this site, permits were issued to four active oil and gas production wells in 2019. The permits authorized the operator to rework the wellbores in order to increase production. The site contains nine operational oil and gas wells, including eight production wells pumping oil to the surface and one wastewater disposal well. There are multiple homes near this site, within 400’ to the west and within 300’ to the northeast.

For each gallon of oil produced, another ten gallons of contaminated wastewater are brought to the surface. Using diesel or gas generators this wastewater is pumped back into the ground. California regulators have a bad track record of managing underground injection of wastewater, which is now under the U.S. EPA’s oversight. The groundwater in this area of Kern County is largely contaminated and considered a sacrifice zone.

The emissions from this site are from the pressure release valves on the tops of multiple tanks. The tanks store both crude oil and wastewater. The infrared spectrum allows the camera to film the tank levels, which are nearly full. As the tanks fill with more crude oil and hydrocarbon contaminated wastewater the head space of the tank pressurizes with more VOC’s. This footage was also filmed at night when emissions are typically much lower. During the day heat from the sun (radiative energy) heats the tanks and increases the head space pressure resulting in greater emissions. While the San Joaquin Valley Air Pollution Control District (SJVAPCD) was notified of these uncontrolled sources of emissions, their own inspections of the site did not identify an actionable offense on the part of the operator and these uncontrolled emissions continue to be released.

 

Tank Emissions

Crude oil and wastewater storage tanks are a common source of fugitive emissions and represent the majority of emissions presented in this report. Some tanks and well-sites use best practices that include closed vapor recovery systems to prevent venting tanks from leaking, but the vast majority do not and vent directly to the atmosphere. In all cases, tanks and pipeline infrastructure use pressure release valves to vent emissions when pressure builds too high. This venting is permitted as strictly an emergency activity to prevent hazardous build-up of pressure. Vents are even designed to open and reset themselves automatically. Consequently, tank venting is a common practice and operators seem to often leave these valves open.

While the recently enacted California Oil and Gas Rule (COGR) places limits on GHG emissions from all oil and gas facilities, internal policy of the San Joaquin Air Valley Air Pollution Control District has previously exempted tanks at low-producing well sites from having to be kept in a leak-free condition, creating a regulatory conflict that air districts and CARB need to resolve. This type of emissions source is also difficult for regulators to identify during inspections, for a number of reasons. These valves are typically located on the tops of large tanks where they are difficult to access and view, and inspections and sampling can only occur by chance (i.e., when the valve in open). Further, these valves can be immediately closed by operators during or upon notification of an upcoming inspection.

New Permits: Moving in the Wrong Direction

When Earthworks CEP uses OGI cameras to inspect an oil and gas site in California, finding and documenting pollution releases is so common that it is the default expectation. Because of access and proximity limitations, it is possible that more pollution is being released from sites than CEP can identify. All of these examples of pollution, including releases of methane and VOCs, add up to potentially degrade air quality and expose Frontline Communities to health risks — as well as many others just like them. This summary represents a small collection of leaking well sites visited by Earthworks CEP, which have coincidentally received new permits to operate and rework existing wells since January 1, 2019. CEP has also documented many other hazardous cases, such as the Jewett 1-23 site in Arvin (shown in the footage below), that is persistently exposing elementary school students to VOCs. These sites surely make up only a small proportion of the polluting oil and gas sites in California that harm climate and health.

From the initial drilling of an oil and gas well, during production, and into subsequent reworks, all phases of a well’s lifetime result in unpermitted and undocumented fugitive emissions. Regulating emissions from oil and gas extraction operations has not been effective in California. Regardless of notices of violations and fines, polluting facilities and well sites continue to operate and even receive new permits. Even the COGR rule, lauded as the most stringent GHG emissions regulation in the nation is technically unable to eliminate or even identify these uncontrolled sources. It is clear that the only ways to reduce exposures to these emissions for Frontline Communities is to institute protective setbacks and stop permitting the drilling of new wells and the reworking of aging wells.

By Kyle Ferrar, Western Program Coordinator, FracTracker Alliance

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Incinerators: Dinosaurs in the world of energy generation

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In this article, we’ll take a look at the current trend in “re-branding” incineration as a viable option to deal with the mountains of garbage generated by our society. Incineration can produce energy for electricity, but can the costs—both economically, and ecologically—justify the benefits? What are the alternatives?

Changes in our waste stream

In today’s world of consumerism and production, waste disposal is a chronic problem facing most communities worldwide. Lack of attention to recycling and composting, as well as ubiquitous dependence on plastics, synthetics, and poorly-constructed or single-use goods has created a waste crisis in the United States. So much of the waste that we create could be recycled or composted, however, taking extraordinary levels of pressure off our landfills. According to estimates in 2017 by the US Environmental Protection Agency (EPA), over 30 percent of municipal solid waste is made up of organic matter like food waste, wood, and yard trimmings, almost all of which could be composted. Paper, glass, and metals – also recyclable – make up nearly 40 percent of the residential waste stream. Recycling plastic, a material which comprises 13% of the waste stream, has largely been a failed endeavor thus far.

Why say NO to incinerators?

  • They are bad for the environment, producing toxic chlorinated byproducts like dioxins. Incineration often converts toxic municipal waste into other forms, some of which are even more toxic than their precursors.
  • They often consume more energy than they produce and are not profitable to run.
  • They add CO2 to the atmosphere.
  • They promote the false narrative that we can “get something” from our trash
  • They detract from the conversation about actual renewable energy sources like wind power, solar power, and geothermal energy that will stop the acceleration of climate chaos.

Figure 1: A breakdown of the 267.78 million tons of municipal waste that were generated in the US in 2017. Source: figure developed by FracTracker Alliance, based on 2017 EPA data. Source: https://www.epa.gov/facts-and-figures-about-materials-waste-and-recycling/national-overview-facts-and-figures-materials

Nevertheless, of the approximately 400 million tons of plastic produced annually around the world, only about 10% of it is recycled. The rest winds up in the waste stream or as microfragments (or microplastics) in our oceans, freshwater lakes, and streams.

Figure 2: Increase in global plastics production, 1950-2015, Source: Geyer, R., Jambeck, J. R., & Law, K. L. (2017). Production, use, and fate of all plastics ever made. Science Advances, 3(7), e1700782. Available at: http://advances.sciencemag.org/content/3/7/e1700782 Referenced in https://ourworldindata.org/plastic-pollution

According to an EPA fact sheet, by 2017, municipal solid waste generation increased three-fold compared with 1960. In 1960, that number was 88.1 million tons. By 2017, this number had risen to nearly 267.8 million tons. Over that same period, per-capita waste generation rose from 2.68 pounds per person per day, to 4.38 pounds per person per day, as our culture became more wed to disposable items.

The EPA provides a robust “facts and figures” breakdown of waste generation and disposal here.  In 2017, 42.53 million tons of US waste was shipped to landfills, which are under increasing pressure to expand and receive larger and larger loads from surrounding area, and, in some cases, hundreds of miles away.

How are Americans doing in reducing waste?

On average, in 2017, Americans recycled and composted 35.2% of our individual waste generation rate of 4.51 pounds per person per day.  While this is a notable jump from decades earlier, much of the gain appears to be in the development of municipal yard waste composting programs. Although the benefits of recycling are abundantly clear, in today’s culture, according to a PEW Research Center report published in 2016, just under 30% of Americans live in communities where recycling is strongly encouraged. An EPA estimate for 2014 noted that the recycling rate that year was only 34.6%, nationwide, with the highest compliance rate at 89.5% for corrugated boxes.

Figure 3. Percent of Americans who report recycling and re-use behaviors in their communities, via Pew Research center
Historically, incineration – or burning solid waste – has been one method for disposing of waste. And in 2017, this was the fate of 34 million tons—or nearly 13%– of all municipal waste generated in the United States. Nearly a quarter of this waste consisted of containers and packaging—much of that made from plastic.  The quantity of packaging materials in the combusted waste stream has jumped from only 150,000 tons in 1970 to 7.86 million tons in 2017.  Plastic, in its many forms, made up 16.4% of all incinerated materials, according to the EPA’s estimates in 2017.

Figure 4: A breakdown of the 34.03 tons of municipal waste incinerated for energy in the US in 2017

What is driving the abundance of throw-away plastics in our waste stream?

Sadly, the answer is this: The oil and gas industry produces copious amounts of ethane, which is a byproduct of oil and gas extraction. Plastics are an “added value” component of the cycle of fossil fuel extraction. FracTracker has reported extensively on the controversial development of ethane “cracker” plants, which chemically change this extraction waste product into feedstock for the production of polypropylene plastic nuggets. These nuggets, or “nurdles,” are the building blocks for everything from fleece sportswear, to lumber, to packaging materials. The harmful impacts from plastics manufacturing on air and water quality, as well as on human and environmental health, are nothing short of stunning.

FracTracker has reported extensively on this issue. For further background reading, explore:

A report co-authored by FracTracker Alliance and the Center for Environmental Integrity in 2019 found that plastic production and incineration in 2019 contributed greenhouse gas emissions equivalent to that of 189 new 500-megawatt coal power plants. If plastic production and use grow as currently planned, by 2050, these emissions could rise to the equivalent to the emissions released by more than 615 coal-fired power plants.

Figure 5: Projected carbon dioxide equivalencies in plastics emissions, 2019-2050. Source: Plastic and Climate https://www.ciel.org/plasticandclimate/

Just another way of putting fossil fuels into our atmosphere

Incineration is now strongly critiqued as a dangerous solution to waste disposal as more synthetic and heavily processed materials derived from fossils fuels have entered the waste stream. Filters and other scrubbers that are designed to remove toxins and particulates from incineration smoke are anything but fail-safe. Furthermore, the fly-ash and bottom ash that are produced by incineration only concentrate hazardous compounds even further, posing additional conundrums for disposal.

Incineration as a means of waste disposal, in some states is considered a “renewable energy” source when electricity is generated as a by-product. Opponents of incineration and the so-called “waste-to-energy” process see it as a dangerous route for toxins to get into our lungs, and into the food stream. In fact, Energy Justice Network sees incineration as:

… the most expensive and polluting way to make energy or to manage waste. It produces the fewest jobs compared to reuse, recycling and composting the same materials. It is the dirtiest way to manage waste – far more polluting than landfills. It is also the dirtiest way to produce energy – far more polluting than coal burning.

Municipal waste incineration: bad environmentally, economically, ethically

Waste incineration has been one solution for disposing of trash for millennia. And now, aided by technology, and fueled by a crisis to dispose of ever-increasing trash our society generates, waste-to-energy (WTE) incineration facilities are a component in how we produce electricity.

But what is a common characteristic of the communities in which WTEs are sited? According to a 2019 report by the Tishman Environmental and Design Center at the New School, 79% of all municipal solid waste incinerators are located in communities of color and low-income communities.  Incinerators are not only highly problematic environmentally and economically. They present direct and dire environmental justice threats.

Waste-to-Energy facilities in the US, existing and proposed

Click here to view this map full-screen

Activate the Layers List button to turn on Environmental Justice data on air pollutants and cancer occurrences across the United States.  We have also included real-time air monitoring data in the interactive map because one of the health impacts of incineration includes respiratory illnesses. These air monitoring stations measure ambient particulate matter (PM 2.5) in the atmosphere, which can be a helpful metric.

What are the true costs of incineration?

These trash incinerators capture energy released from the process of burning materials, and turn it into electricity. But what are the costs? Proponents of incineration say it is a sensible way to reclaim or recovery energy that would otherwise be lost to landfill disposal. The US EIA also points out that burning waste reduces the volume of waste products by up to 87%.

The down-side of incineration of municipal waste, however, is proportionally much greater, with a panoply of health effects documented by the National Institutes for Health, and others.

Dioxins (shown in Figures 6-11) are some of the most dangerous byproducts of trash incineration. They make up a group of highly persistent organic pollutants that take a long time to degrade in the environment and are prone to bioaccumulation up the food chain.

Dioxins are known to cause cancer, disrupt the endocrine and immune systems, and lead to reproductive and developmental problems. Dioxins are some of the most dangerous compounds produced from incineration. Compared with the air pollution from coal-burning power plants, dioxin concentrations produced from incineration may be up to 28 times as high.

2,3,7,8-Tetrachlorodibenzo-p-dioxin

2,3,7,8-Tetrachlorodibenzofuran

3,3′,4,4′,5,5′-Hexachlorobiphenyl

Figures 6-11: Dioxin chemical structures via US EPA. Source: https://www.epa.gov/dioxin/learn-about-dioxin
 

Federal EPA regulations between 2000 and 2005 resulted in the closure of nearly 200 high dioxin emitting plants. Currently, there are fewer than 100 waste-to-energy incinerators operating in the United States, all of which are required to operate with high-tech equipment that reduces dioxins to 1% of what used to be emitted. Nevertheless, even with these add-ons, incinerators still produce 28 times the amount of dioxin per BTU when compared with power plants that burn coal.

Even with pollution controls required of trash incinerators since 2005, compared with coal-burning energy generation, incineration still releases 6.4 times as much of the notoriously toxic pollutant mercury to produce the equivalent amount of energy.

Energy Justice Network, furthermore, notes that incineration is the most expensive means of managing waste… as well as making energy. This price tag includes high costs to build incinerators, as well as staff and maintain them — exceeding operation and maintenance costs of coal by a factor of 11, and nuclear by a factor of 4.2.

Figure 12. Costs of incineration per ton are nearly twice that of landfilling. Source: National Solid Waste Management Association 2005 Tip Fee Survey, p. 3.
Energy Justice Network and others have pointed out that the amount of energy recovered and/or saved from recycling or composting is up to five times that which would be provided through incineration.

Figure 13. Estimated power plant capital and operating costs. Source: Energy Justice Network

The myth that incineration is a form of “renewable energy”

Waste is a “renewable” resource only to the extent that humans will continue to generate waste. In general, the definition of “renewable” refers to non-fossil fuel based energy, such as wind, solar, geothermal, wind, hydropower, and biomass. Synthetic materials like plastics, derived from oil and gas, however, are not. Although not created from fossil fuels, biologically-derived products are not technically “renewable” either.

ZeroWasteEurope argues that:

Biogenic materials you find in the residual waste stream, such as food, paper, card and natural textiles, are derived from intensive agriculture – monoculture forests, cotton fields and other “green deserts”. The ecosystems from which these materials are derived could not survive in the absence of human intervention, and of energy inputs from fossil sources. It is, therefore, more than debatable whether such materials should be referred to as renewable.

Although incineration may reduce waste volumes by up to 90%, the resulting waste-products are problematic. “Fly-ash,” which is composed of the light-weight byproducts, may be reused in concrete and wallboard. “Bottom ash” however, the more coarse fraction of incineration—about 10% overall—concentrates toxins like heavy metals. Bottom-ash is disposed of in landfills or sometimes incorporated into structural fill and aggregate road-base material.

How common is the practice of using trash to fuel power plants?

Trash incineration accounts for a fraction of the power produced in the United States. According to the United States Energy Information Administration, just under 13% of electricity generated in the US comes from burning of municipal solid waste, in fewer than 65 waste-to-energy plants nation-wide. Nevertheless, operational waste-to-incineration plants are found throughout the United States, with a concentration east of the Mississippi.

According to EnergyJustice.net’s count of waste incinerators in the US and Canada, currently, there are:

    • 88 operating
    • 41 proposed
    • 0 expanding
    • 207 closed or defeated

Figure 14. Locations of waste incinerators that are already shut down. Source: EnergyJustice.net)
Precise numbers of these incinerators are difficult to ascertain, however. Recent estimates from the federal government put the number of current waste-to-energy facilities at slightly fewer: EPA currently says there are 75 of these incinerators in the United States. And in their database, updated July 2020, the United States Energy Information Administration (EIA), lists 63 power plants that are fueled by municipal solid waste. Of these 63 plants, 40—or 66%—are in the northeast United States.

Regardless, advocates of clean energy, waste reduction, and sustainability argue that trash incinerators, despite improvements in pollution reduction over earlier times and the potential for at least some electric generation, are the least effective option for waste disposal that exists. The trend towards plant closure across the United States would support that assertion.

Let’s take a look at the dirty details on WTE facilities in three states in the Northeastern US.

Review of WTE plants in New York, Pennsylvania, and New Jersey

A. New York State

In NYS, there are currently 11 waste-to-energy facilities that are operational, and two that are proposed. Here’s a look at some of them:

The largest waste-to-energy facility in New York State, Covanta Hempstead Company (Nassau County), was built in 1989. It is a 72 MW generating plant, and considered by Covanta to be the “cornerstone of the town’s integrated waste service plan.”

According to the Environmental Protection Agency’s ECHO database, this plant has no violations listed. Oddly enough, even after drawing public attention in 2009 about the risks associated with particulate fall-out from the plant, the facility has not been inspected in the past 5 years.

Other WTE facilities in New York State include the Wheelabrator plant located in Peekskill (51 MW), Covanta Energy of Niagara in Niagara Falls (32 MW), Convanta Onondaga in Jamesville (39 MW), Huntington Resource Recovery in Suffolk County (24.3 MW), and the Babylon Resource Recovery Facility also in Suffolk County (16.8 MW). Five additional plants scattered throughout the state in Oswego, Dutchess, Suffolk, Tioga, and Washington Counties, are smaller than 15 MW each. Of those, two closed and one proposal was defeated.

B. Pennsylvania

In Pennsylvania, six WTE facilities are currently operating. Two have been closed, and six defeated.

C. New Jersey

And in New Jersey, there are currently four operating WTE facilities. Essex County Resource Recovery Facility, is New Jersey’s largest WTE facility. It opened in 1990, houses three burners, and produces 93 MW total.

Union County Resource Recovery Facility, which opened in 1994, operates three burners, producing 73 MW total. Covanta Camden Energy Recovery Center opened in 1991. It has 13 burners, producing a total of 46 MW. Wheelabrator Gloucester LP (Westville, NJ) opened in 1990. The two burners there produce 21 MW of power. Covanta Warren Energy is the oldest and smallest WTE facility in New Jersey. It produced 14 MW of energy and opened in 1988. Operations are currently shut down, but this closure may not be permanent.

Throw-aways, burn-aways, take-aways

Looming large above the arguments about appropriate siting, environmental justice, financial gain, and energy prices, is a bigger question:

How can we continue to live on this planet at our current rates of consumption, and the resultant waste generation?

The issue here is not so much about the sources of our heat and electricity in the future, but rather “How MUST we change our habits now to ensure a future on a livable planet?”

Professor Paul Connett (emeritus, St. Lawrence University), is a specialist in the build-up of dioxins in food chains, and the problems, dangers, and alternatives to incineration. He is a vocal advocate for a “Zero Waste” approach to consumption, and suggests that every community embrace these principles as ways to guide a reduction of our waste footprint on the planet. The fewer resources that are used, the less waste is produced, mitigating the extensive costs brought on by our consumptive lifestyles. Waste-to-energy incineration facilities are just a symptom of our excessively consumptive society.

Dr. Connett suggests these simple but powerful methods to drastically reduce the amount of materials that we dispose — whether by incineration, landfill, or out the car window on a back-road, anywhere in the world:

    • Source separation
    • Recycling
    • Door-to-door collection
    • Composting
    • Building Reuse, Repair and Community centers
    • Implementing waste reduction Initiatives
    • Building Residual Separation and Research centers
    • Better industrial design
    • Economic incentives
    • Interim landfill for non-recyclables and biological stabilization of other organic materials

Connett’s Zero Waste charge to industry is this: “If we can’t reuse, recycle, or compost it, industry shouldn’t be making it.” Reducing our waste reduces our energy footprint on the planet.

In a similar vein, FracTracker has written about the potential for managing waste through a circular economics model, which has been successfully implemented by the city of Freiburg, Germany. A circular economic model incorporates recycling, reuse, and repair to loop “waste” back into the system. A circular model focuses on designing products that last and can be repaired or re-introduced back into a natural ecosystem.
 

This is an important vision to embrace. Every day. Everywhere.

Recommended resources

Figure 17: Illustration of common waste streams from “The Story of Plastic” (https://www.storyofplastic.org/)

By Karen Edelstein, Eastern Program Coordinator


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Ted Auch, PhD

Energy Security, International Investment, and Democracy in the US Shale Oil & Gas Industry

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FracTracker’s Ted Auch coauthored a recent article in the journal Democracy & Security that considers the US shale oil and gas industry through a national security lens.

This paper was authored by Bryan T. Stinchfield , Ted Auch & Eve Bratman. 

Access the Full Article

Article Abstract

Proponents of the US shale oil and gas industry argued that American citizens’ economic prosperity and national security were at stake if the industry was not rapidly expanded. Following copious amounts of a certain type of “patriotic” rhetoric, the industry grew rapidly. Simultaneously, foreign ownership of US shale industry infrastructure occurred in tandem with calls for new policies and laws to limit US citizens’ democratic rights with regard to the industry’s activities. As a result, we argue that the development of the US shale industry has weakened national security by creating negative security externalities and eroding democratic values. We offer implications for other democratic societies rich in natural resources.

Figure 1. Vicious cycle within the US shale industry.

The intent of some of the industry’s proponents is to criminalize protest, peaceful and otherwise. When peaceful protests are intentionally lumped in with not-peaceful protests, the effect is a weakening of democracy.

Energy Security, International Investment, and Democracy: The Case of the United States Shale Oil and Gas Industry

Bryan T. Stinchfield , Ted Auch & Eve Bratman

To cite this article: Bryan T. Stinchfield , Ted Auch & Eve Bratman (2020): Energy Security, International Investment, and Democracy: The Case of the United States Shale Oil and Gas Industry, Democracy and Security, DOI: 10.1080/17419166.2020.1811969

To link to this article: https://doi.org/10.1080/17419166.2020.1811969

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Shannon Smith

Straight Talk on the Future of Fracking Jobs in Pennsylvania

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Fracking has been raised as an issue that could determine the outcome of the 2020 US presidential election. Republican candidates have cited erroneous figures of how many fracking jobs exist in Pennsylvania, and have falsely claimed that Democratic presidential candidate Joe Biden and running mate Kamala Harris seek to ban fracking. And while the Democratic candidates have made suggestive comments in the past, they have made their position clear. As Senator Harris stated in the vice presidential debate: “I will repeat, and the American people know, that Joe Biden will not ban fracking. That is a fact.”

The debate around this issue is not on whether or not fracking should be banned– something neither party advocates– but rather around the facts. Republican candidates have inflated the extent of fracking jobs by up to 3500 percent. But the natural gas industry and the fracking boom have failed to deliver the job growth and prosperity that was predicted by proponents a decade ago. In reality, the total number of jobs in the natural gas industry in Pennsylvania never reached more than 30,000 over the last five years and is now less with the industry’s economic decline.

The total number of jobs in the natural gas industry in Pennsylvania never reached more than 30,000 over the last five years and is now less with the industry’s economic decline.

The debate should not be around the facts- those are already firmly established. The debate should be around how to best support fossil fuel workers in the inevitable transition to cleaner energy. What does a just transition that supports workers and the climate look like?

FracTracker Alliance and The Breathe Project have compiled a fact sheet to help us answer this question based on where Pennsylvania currently stands.

 

Get the Facts

 

Breathe Project
Energy Innovation Center – Suite 140
1435 Bedford Avenue
Pittsburgh, PA 15219

breathe@breatheproject.org

 

Straight Talk on the Future of Jobs in Pennsylvania (September 2020)

 

The Breathe Project and FracTracker Alliance have crafted the following messaging for refuting the conflated job numbers being touted by pro-fossil fuel organizations and political candidates regarding fracking and jobs in Pennsylvania that, in some cases, has inflated natural gas jobs in the state by 3500 percent.

The natural gas industry and the fracking boom have failed to deliver the job growth and prosperity that was predicted by proponents a decade ago. The total number of jobs in the natural gas industry in Pennsylvania never reached more than 30,000 over the last five years and is now less with the industry’s economic decline.

 

FACT:  The Pa. Dept. of Labor and Industry (DLI) reported that direct employment in natural gas development totaled 19,623 in 2016. This was down from 28,926 total natural gas development jobs in 2015. This includes jobs in drilling, extraction, support operations and pipeline construction and transportation. (StateImpact, 2016)

Pa. DLI  calculated the employment figures using data from six data classifications at the U.S. Bureau of Labor Statistics — specifically, the North American Industry Classification System (NAICS) codes for cured petroleum and natural gas extraction, natural gas liquid extraction, drilling oil and gas wells, support activities for oil and gas operations, oil and gas pipeline and related structures and pipeline transportation of natural gas. (Natural Gas Intel, 2016)

Inflated estimates of fracking-related jobs in Pennsylvania under previous Gov. Tom Corbett included regulators overseeing the industry as gas jobs, truck drivers, and those working in highway construction, steel mills, coal-fired power plants, sewage treatment plants, and others. Pa. Gov. Tom Wolf’s administration revised the way gas industry jobs were calculated to reflect a more accurate depiction of jobs in the sector.

 

FACT: Food & Water Watch calculated that there were 7,633 jobs pre-boom (2001 – 2006), which rose to 25,960 oil and gas industry jobs post-boom (2016 – 2018). (FWW, March 2020)

 Food & Water Watch created a more accurate model using a definition that encompasses only jobs directly involved with domestic oil and gas production, specifically: oil and gas extraction; support activities for oil and gas operations; drilling oil and gas wells; oil and gas pipeline construction; and pipeline transportation.

FACT:  The Food & Water Watch analysis also reports that misleadingly broad definitions in industry-supported job reports overstated the industries’ scope. The industry analysis included broad swaths of manufacturing industries including “fertilizer manufacturing,” convenience store workers, and gas station workers, which accounted for nearly 35 percent of all oil and gas jobs in their analysis. (FWW, PwC at 5 and Table 4 at 9, 2019)

FACT: As a point of comparison, in 2019, close to 1 million state residents were working in healthcare, 222,600 in education, and over 590,000 in local and state government. (Pennsylvania Bureau of Labor Statistics, July, 2020)

FACT: To forecast fracking-related job growth, the American Petroleum Institute used a model with exaggerated multipliers and faulty assumptions, such as the amount of purchases made from in-state suppliers, and it double counted jobs, leading to wildly optimistic estimates. (Ohio River Valley Institute, August 2020)

FACT: In addition, many of the jobs claimed in a 2017 American Chemistry Council Appalachian petrochemical economic impact study would arise in plastics manufacturing, which raises two concerns. First, both the ACC study and subsequent reports by the U.S. Department of Energy assume that 90% of the ethylene and polyethylene produced by imagined Appalachian cracker plants would be shipped out of the region to be used in manufacturing elsewhere in the country and the world. Of the 10% that would presumably stay in the region, much or most of it would serve to replace supplies that the region’s plastics manufacturers currently source from the Gulf Coast. (Ohio River Valley Institute, August 2020)

 

The fracking and petrochemical industries create unsustainable boom and bust cycles that do not holistically improve local economies.

FACT: Economic analyses show that the oil and gas industry is a risky economic proposition due to the current global oversupply of plastics, unpredictable costs to the industry, a lower demand for plastics, and increased competition. The analyses call into question industry’s plans to expand fracking and gas infrastructure in the region. (IEEFA, August 2020)

FACT: Plans to build petrochemical plants in Beaver County, Pennsylvania and Belmont, Ohio, for the sole purpose of manufacturing plastic nurdles will not be as profitable as originally portrayed. (IEEFA Report, June 2020)

 

A clean energy economy is the only way forward.

FACT: The Dept. of Energy’s U.S. Energy and Employment Report (2017) and E2 Clean Jobs Pennsylvania Report (2020) shows that clean energy jobs in Pennsylvania employ twice as many people as the fossil fuel industry prior to the pandemic.

FACT: The 4-state region of Ohio, West Virginia, Kentucky and Pennsylvania has formed a coalition of labor, policy experts and frontline community leaders called Reimagine Appalachia. This coalition is in the process of addressing the vast number of jobs in renewable and clean energy industries in a report that will be published this fall.

Reimagine Appalachia seeks major federal funding packages that will create jobs, rebuild infrastructure and addresses climate change that will ensure that no one is left behind going forward.

 

Sources

O’Leary, Sean. “The Not-So-Natural Gas Boom,” Westvirginiaville.com, Aug. 10, 2020.

O’Leary, Sean. “Lies, damned lies, and economic impact studies,” Ohio River Valley Institute, Aug. 31, 2020.

O’Leary, Sean. “Game Unchanged . . . But, Not Unchangeable,” Ohio River Valley Institute, Aug. 11, 2020.                                                                                                                                                 Food & Water Watch. “Phantom Jobs: Fracking Job Creation Numbers Don’t Add Up,” March 2020.

Natural Gas Intel

Pa. Dept. of Environmental Protection Energy Programs. 2020 Pennsylvania Energy Employment Report,

Institute for Energy Economics and Financial Analysis (IEEFA). “IEEFA report: Financial risks loom for Shell’s Pennsylvania petrochemicals complex,” June 4, 2020.

IEEFA. “Petrochemicals may be another bad bet for the oil industry,” Aug. 19, 2020.

E2. “Clean Jobs Pennsylvania 2020,” April 15, 2020.

Natural Gas Intel. “Direct Employment in Natural Gas Development Declines by One-Third in Pennsylvania,” Dec. 23, 2016.

PennLive. “How many jobs has Marcellus Shale Really Created?” Jan. 5, 2019.

StateImpact, “Pa. oil and gas jobs down 32 percent since last year,” Dec. 23, 2016.

 

The Breathe Project is a coalition of citizens, environmental advocates, public health professionals and academics using the best available science and technology to improve air quality, eliminate climate pollution and make our region a healthy, prosperous place to live.

FracTracker Alliance is a 501(c)3 organization that maps, analyzes, and communicates the risks of oil, gas, and petrochemical development to advance just energy alternatives that protect public health, natural resources, and the climate.

 

Feature image of construction of the Royal Dutch Shell cracker plant in Beaver County, Pennsylvania, October 2019. Ted Auch, FracTracker Alliance.

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Shannon Smith

Paid Data & GIS Internship Positions Available

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This application is closed

Data & GIS Internship | FracTracker Alliance

Job Title: Data & GIS Intern
Internship Period: February 1, 2021 – April 23, 2021, three months
Application Deadline: November 20, 2020
Compensation: $12/hour, 10 hours per week
Locations: Two remote positions available in collaboration with either the Pittsburgh, PA office or the Cleveland, OH office.

FracTracker internships are dedicated to current college and graduate students, as well as recent grads. Applicants should enjoy working with datasets, visualizations, and maps as well as analyzing and writing about oil, gas, and petrochemical issues. FracTracker is offering two paid internships from February 1 through April 23, 2020 in collaboration with the following offices: Pittsburgh, PA and Cleveland, OH. These positions are expected to be 100% remote depending on public health conditions. See where we work.

 

Learn more about FracTracker’s internship program and explore the work past intern projects.

Learn More

 

Responsibilities

The responsibilities of paid interns revolve around the daily work of the other FracTracker staff, time-sensitive projects, and the interns’ own areas of interests. Responsibilities will vary, but may include:

  • Data mining, cleaning, management, and GIS mapping
  • Limited spatial analyses using GIS software
  • Translation of data into blog posts
  • Communications support, including website development, content creation, and other tasks as needed

 

Qualifications

PREFERRED SKILLS:

  • GIS/mapping; Experience with ArcGIS
  • Writing and editing; Experience with Microsoft Word
  • Public speaking
  • Citizen science
  • Research
  • Data management; Experience with Microsoft Excel
  • Website development; Knowledge of WordPress
  • Teamwork and interpersonal skills
  • Ability to work independently
  • Communication and adherence to deadlines

MINIMUM EDUCATION/QUALIFICATIONS:

  • Enrollment in or recent graduation from an accredited college or university is required. Majors can include geography, computer science, environmental science, public health, planning or a related field.
  • Interest in the mission of FracTracker; Familiarity with environmental justice issues
  • Knowledge of environmental and/or public health concerns or other issues of relevance to understanding the implications of oil and gas extraction and climate change

 

Application Process

To apply for one of our spring 2021 paid data & GIS internship positions, please submit the following materials through the online application form below: cover letter, resume, and three references. Applications are not accepted via email, but you may address questions to Shannon Smith at smith@fractracker.org.

Deadline to apply: November 20, 2020 at 5:00pm EST.

Interviews will be conducted during the period of November 30 – December 11, 2020, and a decision made by December 18, 2020. All applicants will be contacted regarding the outcome of their application.

About FracTracker Alliance

Insights Empowering Action

FracTracker Alliance maps, analyzes, and communicates the risks of oil, gas, and petrochemical development to advance just energy alternatives that protect public health, natural resources, and the climate.

Learn more about FracTracker Alliance at www.fractracker.org.

 

This application is closed

 

Questions? Contact Shannon Smith at smith@fractracker.org.

FracTracker Alliance

A New, Extensive Platform for Fracking Imagery

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by Ted Auch, FracTracker Great Lakes Program Coordinator, and Rebecca Johnson, Communications & Administrative Specialist

FracTracker is pleased to release our improved multimedia platform of fracking imagery for your convenient use. You can easily view, download, and share photos and videos of oil, gas, and petrochemical impacts. We’ve made it easy for you to find what you need within over 1,600 photos, GIFs, and videos of the various aspects of fossil fuel industries and activities. All media are free to download and use for all visitors, and the collection will only expand as our work continues!

 

 

Explore Fracking Imagery

 

 “The aeroplane has unveiled for us the true face of the earth.” by French writer and aviator Antoine de Saint-Exupéry author of Le Petit Prince (The Little Prince)

 

Ted Auch, FracTracker Great Lakes Program Coordinator:

It was nearly five years ago on a beautiful Wednesday morning that I met Paul Feezel, a concerned citizen of Carroll County, Ohio, and Cleveland Museum of Natural History’s David Beach at the Carroll County-Tolson Airport (40.5616667, -81.0780833). The occasion was a flight with pilot Mike Stich to see what the Fracking Boom had done to Carroll and neighboring counties.

The aspect of the industry that I came away from that flight most worried about was the hundreds of miles of pipelines we saw connecting well pad to well pad and meandering on downstream to processing facilities. These pipelines took such circuitous routes between pads that everyone in the plane was scratching their heads, wondering how such routes made any financial sense for the operators to get their raw product to market.

Ever since that flight, I have spent a significant chunk of my time at FracTracker mapping the extent of these so-called gas “gathering pipelines” across Ohio, West Virginia, and Pennsylvania. I remain as flummoxed as I was on that day how such a hastily laid and poorly regulated network of pipelines makes sense. More recently, I have been wondering what the cumulative impact of these non-FERC-regulated pipelines has been on forests, wetlands, and the remaining agriculture in the region.

We have flown over this area several more times since that initial flight, with pilots volunteering their time to navigate planes provided by our excellent partners at LightHawk. As I wrote a little over two years ago:

“… you can’t really understand or appreciate the enormity, heterogeneity, and complexity of the unconventional oil and gas industry’s impact unless you look at the landscape from the cockpit of a Cessna 172. This vantage point allows you to see the grandeur and nuance of all things beautiful and humbling. Conversely, and unfortunately more to the point of what I’ve seen in the last year, a Cessna allows one to really absorb the extent, degree, and intensity of all things destructive. I’ve had the opportunity to hop on board the planes of some amazing pilots, like Dave Warner, a forester formerly of Shanks, West Virginia … Tim Jacobson, Esq., out of La Crosse, Wisconsin, northern Illinois retired commodity and tree farmer Doug Harford, and Target corporate jet pilot Fred Muskol, out of the Twin Cities area of Minnesota.”

Frac sand mine impoundment pond in Wedron, IL, 2018. Photo by Ted Auch.

Frac sand mine impoundment pond in Wedron, IL, 2018. Photo by Ted Auch, with aerial assistance from Lighthawk.

I wrote the “Bird’s-Eye-View” piece in August 2018, and since then we’ve made additional flights with our LightHawk partners, including a harrowing flight over Pine Creek State Park in Pennsylvania last May, part of our “Wilderness Lost” digital atlas series that now includes a similar project for the adjoining Loyalsock Creek.

The May 2019 flight was exhilarating to say the least – and thanks to the skills of our pilot Steve Kent, we executed the flight and extracted some powerful imagery that was three months later appended during better flying conditions with pilot Bob Keller. This flight was notable because the cloud ceiling was around 2,400 feet, and some peaks we were flying over and around were in excess of 1,200 feet, which gave us very little room to maneuver, at times forcing us to fly down into valleys to avoid the clouds. This flight also was a great opportunity for me and Steve to practice our communication, given that we were flying so low and slow, which meant that Steve would basically give me a ten-second slot to open my window, lean out, and shoot, while he was banking around the site of interest. Unlike other flights – including the subsequent flight in the Pine Creek – we did not have any opportunities to fly around infrastructure more than once, given how volatile the cloud ceiling was, and that if there was an opening that would allow us to move laterally, we had to take it.

Between our Pine Creek flights and that initial Carroll County aerial tour, we’ve compiled literally thousands of high-quality and illustrative images of the Hydraulic Fracturing Industrial Complex. When we say “hydraulic fracturing” – or “fracking” – we are not simply referring to drill rigs and frack pads, like the industry would limit us to in our analysis, but rather all manner of activities and infrastructure, to include drill rigs and pads – but also pipelines, waste disposal sites, processing plants, and frac sand mining activities, from the aforementioned forests of northeastern Pennsylvania, to Texas’ Gulf Coast. To this point, several authors have used our imagery, such as Paul Bogard and Tom Pearson, the Proceedings of the National Academy of Sciences (PNAS), Yale Environment 360, Oil Change International, the Anthropology Magazine SAPIENS, etc.

Since COVID-19 brought everything to a halt, my colleague Rebecca Johnson and I have been working to organize these images, migrating our older and more cumbersome inventory to the image and video hosting website Flickr, where we could more appropriately catalog, group, and map these images.

Please make use of this resource and keep fighting for a more just energy future.

 

Steel plants in Detroit, MI. Photo by Ted Auch, FracTracker Alliance, with aerial assistance from Lighthawk.

 

Rebecca Johnson, Communications & Administrative Specialist

I began working with FracTracker in May 2019, coming in with a new and relatively limited perspective on the energy landscape, compared to Ted’s, my partner in this undertaking, who has spent years – from the ground and from above – capturing this expansion, its degradation, and the challenges it presents. After seeing the collection of Ted’s and others’ pictures on our website, I knew we needed to amplify our efforts in graphic documentation, in order for more people to see and feel what we are collectively up against.

This task was not taken lightly. FracTracker’s imagery backlog was daunting, to say the least. I scrolled through countless pictures and videos of different aspects of fossil fuel infrastructure and activity until my eyes glazed over. I had no idea the extent of the industry landscape and its effects – and so I had no idea where to even begin. The collection was immense, but the need to get more eyes on these revealing depictions was even bigger.

How was best to expose and illuminate the extensive buildout of and degradation from these resource-intensive, extractive industries?

Cataloguing began with the frac sand industry, and I slowly pieced together the breadth and depth of resource extraction. The aerial snapshots and panoramic captures of enormous mines, immense sand piles, and vast, sandy, slurry ponds connected by looming conveyors and miles of train tracks created a twisting path through my mind, traversing the various stages of extraction to production, through landscapes wrought with reckless human consumption. But frac sand is only one starting point in the onslaught, is only an upstream activity that sets the stage for further ruin downstream, with oil and gas extraction, petrochemical and plastic production, and various types of pollution and erroneous waste disposal from all these activities – not to mention the waste and pollution following human consumption, when we think we are “done” with a material.

As I sifted through images, the dots started connecting, and what started as a simple list of subjects quickly became an outline of what our country’s communities and environment were up against. Navigating through the picture hoard, Ted and I regularly discussed the people he had met while capturing these shots.

He spoke of friends he has made along the way – people in communities that had endured this buildout, seeing their lands chipped away, their natural corridors disconnected, and their waterways depleted or entirely consumed to make room for more industrial sites. It had compelled some of them to leave their homes, and some were even forced to abandon their sacred lands, left only with the lasting, heartbreaking memory of seeing it sullied beyond recognition and repair.

 

Detroit residents stand in front of a Marathon Oil refinery in southwest Detroit, MI, 2020. Photo by Ted Auch.

Detroit residents Doug Wood and Theresa Landrum stand in front of a Marathon Oil refinery in southwest Detroit, MI, 2020. Photo by Ted Auch, FracTracker Alliance.

 

This realization lead to our stepwise sorting of imagery by these industries and activities to include the impacts and hazards to communities, culture, and livelihoods, already endured, happening currently, and looming ominously in the future. It’s easy to see the negative alterations from a bird’s-eye view, with the tainted landscape laid out below, punctured by ugly facilities and marred by indiscriminate ruin. It is another, more emotional thing to connect these scenes to those living in them, to the livelihoods dissolved and the generational homes displaced. Farmers have seen their lands infringed upon, their soils tainted and their waters poisoned. Communities have witnessed their air quality deteriorate, their children and friends fall sick, and their neighborhoods empty, at the expense of these industries. An often-overlooked aspect of extraction is those who bear its initial ramifications in their own communities.

At this point, we’ve winnowed our vast trove of imagery down to over 1,600 images across 46 albums. After weeding through this extensive catalog to identify our most powerful snapshots, we thought it would be appropriate to present the first iteration of this over five-month project to our audience and collaborators, with the hopes of better informing/illustrating your work.

With our migration to Flickr, I hope more eyes find this imagery, explore our collections, and follow the connections from album to album, to better understand the effects of fossil fuel activities. Whether it is the withered landscapes, the depleted environments, or the fragmented lives that speak to the viewer most, it is important to remember what has been endured to procure these resources, and what it will take to move to a cleaner, more just energy landscape.

In the event some of you were not aware of certain aspects of the industry, please take this opportunity to tour these albums and familiarize yourself with the myriad infrastructure and impacts of fracking.

Navigate to the Collections page to see FracTracker’s imagery convey a story through the albums grouped there – such as exploring the buildout through the Infrastructure & Transportation Collection, or the Plastics & Petrochemicals Collection. Visit the Albums page to see snapshots sorted by specific types of facilities, like Frac Sand Mining and Pipelines, or by specific projects, like Endless Effects: the Loyalsock Creek Watershed Project. Once you click on a photo, you can view its location on a map.

 

Explore the Platform

 

A primary source of inspiration for this aerial photography endeavor is the late Bill Hughes out of Wetzel County, West Virginia, who left us in March 2019. Bill was a force of nature in West Virginia’s documentation, with his camera and local know-how, the fracking industry’s negligence, and the fact that they seemed to run roughshod over his beloved state’s beautiful landscape. As our Executive Director Brook Lenker wrote following Bill’s death:

“Just taking pictures was not enough. Context was needed. Bill interpreted each picture – explaining the location, thing or activity, and significance of every image. Did it represent a threat to our water, air, or land? When did it happen? What happened before and after? Did it show a short- or long-term problem? Should state regulatory agencies see it to become better informed? Dissemination followed in many forms: tours of the gas fields; power point presentations to groups in five states; op-ed pieces written for news media; countless responses to questions and inquiries; even blogs and photo essays for various websites. Ceaseless Bill never stopped caring. Maybe Bill Hughes should be an official emblem for Earth Day – a humble, faithful man of modest proportions, spreading the stewardship imperative from a little electric car. Hitch a ride, follow his lead, and, like Bill, always tell it like it is.”

We hope that our work in the air and on the ground photographing industry impacts would make Bill proud. We will continuously update these Flickr albums, and offer as much background and locational data as possible to facilitate an unsurpassed level of depth and breadth for all users.

 

Additional Readings:

Lenker, B. “An Earth Day Tribute to Bill Hughes”, April 22nd, 2019, https://www.fractracker.org/2019/04/earth-day-tribute-bill-hughes/

Auch, T. “Documenting Fracking Impacts: A Yearlong Tour from a Bird’s-Eye-View”, August 8th, 2018, https://www.fractracker.org/2018/08/birds-eye-view-fracking/

FracTracker and Earthworks “Endless Effects: A Digital Atlas Exploring the Environmental Impacts of a Decade of Unconventional Natural Gas Extraction in the Loyalsock Creek Watershed”, August, 2020, https://www.fractracker.org/projects/the-loyalsock-watershed-project/

FracTracker and Earthworks “Wildness Lost: A Digital Atlas Examining Over a Decade of Unconventional Natural Gas Development in Pennsylvania’s Pine Creek Watershed”, August, 2019, https://www.fractracker.org/projects/wildness-lost-pine-creek/

Auch, T. “Fracking Threatens Ohio’s Captina Creek Watershed”, December, 2109, https://www.fractracker.org/2019/12/fracking-in-captina-creek-watershed-story-map/

 

Feature photo of a Toledo Refining Company refinery in Toledo, OH, July, 2019. Photo by Ted Auch, FracTracker Alliance.

 

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Pipeline Map
Erica Jackson

Mariner East 2 Causes Dozens of Spills Since Lockdown Began, Over 300 in Total

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FracTracker Alliance has released a new map of drilling fluid spills along the Mariner East 2 pipeline route, showing 320 spills from its construction since 2017. Of those, a combined 147 incidents have released over 260,000 gallons of drilling fluid into Pennsylvania waterways. 

The unpermitted discharge of drilling fluid, considered “industrial waste,” into waters of the Commonwealth violates The Clean Streams Law.

What you need to know:

  • Sunoco’s installation of the Mariner East 2 pipeline has triggered 320 incidences of drilling mud spills since 2017, releasing between 344,590 – 405,990 gallons of drilling fluid into the environment. View an interactive map and see a timeline of these incidents.
  • Construction has caused between 260,672 – 266,223 gallons of drilling fluid to spill into waterways, threatening the health of ecosystems and negatively affecting the drinking water of many residents.
  • There have been 36 spills since Pennsylvania entered a statewide shutdown on March 16th, 2020, in response to the COVID-19 pandemic. These spills released over 10,000 gallons of drilling fluid — most of which poured into Marsh Creek Lake in Marsh Creek State Park. See a map of this incident.

Pipeline Map

 

View the Interactive Map

While the total reported volume of drilling fluid released into the environment from the pipeline’s construction is between 344,590 – 405,990 gallons, the actual total is larger, as there are 28 spills with unknown volumes. Spills of drilling mud are also referred to as “inadvertent returns,” or “frac-outs.” 

Most of these spills occurred during implementation of horizontal directional drills (HDD). HDDs are used to install a pipeline under a waterway, road, or other sensitive area. This technique requires large quantities of drilling fluid (comprising water, bentonite clay, and chemical additives), which when spilled into the environment, can damage ecosystems and contaminate drinking water sources. 

ME2 Background

The Mariner East 2 pipeline project is part of the Mariner East pipeline system, which carries natural gas liquids (NGLs) extracted by fracked wells in the Ohio River Valley east, to the Marcus Hook Facility in Delaware County, Pennsylvania. The NGLs will then go to Europe to be turned into plastic. Explore FracTracker’s other resources on this project:

Three dozen spills during COVID-19 pandemic

There have been 36 spills since the Commonwealth shutdown statewide on March 16th, 2020, leaks that have jeopardized drinking water sources, putting communities at even higher risk during the COVID-19 pandemic.

The most concerning occurred on August 10th, when pipeline construction released 8,163 gallons of drilling fluids into a wetland and stream system that drains into Marsh Creek Lake in Chester County, a drinking water reservoir (Figure 1). The Department of Environmental Protection (DEP), Pennsylvania Fish and Boat Commission, private contractors, and the Department of Conservation and Natural Resources are responding to the incident and conducting water tests.

On August 11th, construction caused a 15-foot wide and eight-foot deep subsidence event in the wetland (Figure 1). This caused drilling fluid to flow underground and contaminate groundwater, while also “adversely impacting the functions and values of the wetland.” Thirty-three acres of the lake are now closed to boating, fishing, and other uses of the lake — an extra blow, given the solace state parks have provided to many during this pandemic.

Map of Spills at Marsh Creek Lake

Figure 1. This HDD crossing in Upper Uwchlan Township, Chester County, caused over 8,000 gallons of drilling mud to spill into waterways. However, installation of the parallel 16-inch pipeline also caused spills at this same location in 2017.

A plume of drilling mud, captured here on video, entered the Marsh Creek Lake and settled on the lake bottom. 

Upper Uwchlan Reroute

Last week, the PA DEP ordered Sunoco to suspend work on this HDD site and to implement a reroute using a course Sunoco had identified as an alternative in 2017:

“A 1.01 mile reroute to the north of the HDD is technically feasible. This would entail adjusting the project route prior to this HDD’s northwest entry/exit point to proceed north, cross under the Pennsylvania Turnpike, then proceed east for 0.7 miles parallel to the turnpike, cross Little Conestoga Road, then turn south, cross under the turnpike, and then reintersect the existing project route just east of this HDD’s southeast entry/exit point. There is no existing utility corridor here, however; therefore, this route would create a Greenfield utility corridor and would result in encumbering previously unaffected properties. The route would still cross two Waters of the Commonwealth and possible forested wetlands, and would pass in near proximity or immediately adjacent to five residential home sites. Both crossings of the turnpike would require “mini” HDDs or direct pipe bores to achieve the required depth of cover under the highway. Considered against the possibility of additional IRs [inadvertent returns] occurring on the proposed HDD, which are readily contained and cleaned up with minimal affect to natural resources, the permanent taking of the new 4 easement and likely need to use condemnation against previously unaffected landowners results in SPLP’s opinion that managing the proposed HDD is the preferred option.”

Based on that description, the route could follow the general direction of the dashed line in Figure 2:

Map of pipeline

Figure 2. Possible reroute of Mariner East 2 Pipeline shown with dashed line

The DEP’s order also requires Sunoco to restore and remediate “impacted aquatic life, biota, and habitat, including the functions and values of the impacted wetlands resources, and all impacted recreational uses.” Sunoco must submit an Impact Assessment and Restoration Plan for this drill site by October 1, 2020, and the plan must provide for five years of monitoring after its completed restoration. In the meantime, Sunoco must secure the borehole using “grouting or equivalent method,” and continue to monitor the site. 

Sunoco’s continued negligence

The August incident likely surprised no one, as it was not the first spill at this location, and Sunoco’s own assessment acknowledged that this HDD crossing came with “a moderate to high risk of drilling fluid loss and IRs.”

Residents also sounded alarm bells for this drilling site. The proposal for just this location garnered over 200 public comments, all of which called on the DEP to deny Sunoco’s permit for drilling in this area. Many implored the DEP to consider the alternate route Sunoco must now use. 

George Alexander, a Delaware County resident who runs a blog on this pipeline, the Dragonpipe Diary, says, “Sunoco/Energy Transfer continues to demonstrate in real time that they cannot build the Mariner Pipelines without inflicting harm upon our communities … The Marsh Creek situation is reminiscent of the damage to another favorite Pennsylvania lake, Raystown Lake in Huntingdon County.”

In 2017, Sunoco spilled over 200,000 gallons of drilling fluid into Raystown Lake, and released millions more underground. The spill caked acres of the lakebed with a coating of mud, hurting aquatic life and limiting recreational access to the lake. Sunoco failed to report the spills when they occurred, and the DEP fined the company $1.95 million for the incident. The fine is one of many Sunoco has incurred, including a $12.6 million penalty in February 2018 for permit violations, and more recently, a $355,636 penalty for drilling fluid discharges into waterways across eight counties.

Bleak outlook for oil and gas pipelines

On top of the delays, fines, strong public opposition, and even House and Senate members calling for permits to be revoked,  there’s another factor working against Sunoco — the bleak financial outlook of the petrochemical industry.

The fracking boom triggered investment in projects to convert the fracked gas to plastic, leading to an oversupply in the global market. The industry made ambitious plans based on the price of plastic being $1/pound. Now, in 2020, the price is 40 – 60 cents per pound. If the Mariner East 2 pipeline is brought online, it likely will not be as profitable as its operators expected.

The poor finances of the oil and gas industry have led to the demise of several pipeline projects over the last few months. Phillips 66 announced in March it was deferring two pipelines — the Liberty Pipeline, which would transport crude oil from Wyoming to Oklahoma — and the Red Oak Pipeline system, planned to cross from Oklahoma to Texas. Kinder Morgan expressed uncertainty for its proposed Texas Permian Pass pipeline,  and Enterprise Products Partners cancelled its Midland-to-ECHO crude oil pipeline project. The Atlantic Coast Pipeline also was cancelled this past July by Duke Energy and Dominion Energy, following “an unacceptable layer of uncertainty and anticipated delays,” and the Williams Constitution pipeline was also abandoned after years of challenges. In fact, the EIA recently reported that more pipeline capacity has been cancelled in 2020 than new capacity brought in service.

Will the Mariner East 2 be the next to fall?

Before you go

A note from the Safety 7: The Safety 7 are seven residents of Delaware and Chester Counties who are challenging Sunoco before the [Pennsylvania Public Utility Commission]. If you are outraged at the ongoing threat to our communities from this dangerous, destructive pipeline, please consider donating to the Safety 7 Legal fund … Our next hearing begins September 29, and funds from your support are urgently needed. This motion is representative of the kind of legal work we need, if we are to prevail in protecting our communities from this dangerous pipeline project. Please contribute today if you are able, and please share this appeal widely and let your friends and family know why this case matters to you!

Learn more and donate here.

By Erica Jackson, Community Outreach and Communications Specialist, FracTracker Alliance

This map and analysis relied on data provided by the Pennsylvania Department of Environmental Protection.

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