New York State Department of Environmental Conservation (DEC) Oil and Gas Database includes records for nearly 45,000 wells in the state, nearly all of which are related to the oil and gas industry. Of these records, only 19,600 include drilling dates; some records simply reflect drilling permits that were applied for and expired, or were cancelled for other reasons. Of the records listed, 99% of those drilled are vertical, “conventional” wells.
Research by Bishop (2013) indicates that there could be more than 30,000 additional oil and gas wells that are not documented in the DEC’s database, and potentially not adequately plugged.
Over the past half-century, drilling activity in New York State has ebbed and flowed. In that period of time, drilling interest in oil and gas saw two main peaks: between 1975 and 1985, and — especially for gas — between 2004 and 2010. Gas drilling activity has currently tailed off to practically nothing since the ban on high-volume hydraulic fracturing was passed in late 2014.
In 2018 and 2019, there was a brief flurry of oil drilling, but that too has dropped off. The causes for the decline in new wells are complicated, but likely reflect a combination of reduced consumption of fossil fuels, as well as steady decreases in the price of oil and gas. Prices in the past several years are up to half what they were previously. In addition, the impact of COVID on the industry has also contributed to this decline, although other sources assert that the fossil fuel industry has benefited from the global pandemic.
In this blog we’ll look specifically at spatial and temporal patterns in oil and gas drilling across New York State.
Mapping analysis
Every year, FracTracker updates the full state-wide dataset of oil, gas, and other assorted (non-drinking water) wells. To see the entire “big picture,” you can explore our interactive map below, which shows all wells in the New York State database, from prior to 1900 through late February 2021.
New York State Oil and Gas Wells
This map shows that, despite New York State banning high volume hydraulic, nearly 45,000 wells have been drilled, according to the Department of Environmental Conservation (DEC). Not all the wells in the DEC’s database were actually drilled; some were sites that were permitted, but never explored. Many have been plugged and abandoned. There may be nearly as many undocumented wells as there are in the database, given that record keeping in earlier years was nowhere near as comprehensive as it is today.
In order to turn layers on and off in the map, use the Layers dropdown menu. This tool is only available in Full Screen view. Data sources can be found in the Details section of the map as well as listed the end of this article.
FracTracker has also taken a more fine-grained approach to consider the patterns in drilling in New York State both spatially and temporally. Using the DEC wells database, we first filtered out well data for records that had actual spud (drilling) dates between 1970 and the present. Then, using pivot tables in Microsoft Excel, we graphed the data, and also looked for patterns around where the drilling was taking place.
Emergent from this process, we see the following.
Spatial distributions
Oil and gas hotspots are directly related to the underlying geology of a region. In New York State, the majority of oil wells have been drilled in the Chipmunk and Bradford Formations, followed by the Fulmer Valley, Glade, and Richburg Formations.
Oil Wells in NYS and Their Associated Geological Formations
Updated February 2021
Figure 1. Oil Wells in NYS and Their Associated Geological Formations. Gas wells have historically been most productive in the Medina Formation, followed by the Queenston, and also Trenton-Black River Formations. Data source: New York State DEC Oil and Gas Database.
Gas Wells in NYS and Their Associated Geological Formations
Updated February 2021
Figure 2. Gas wells in NYS and their associated geological formations. Data source: NYS DEC Oil and Gas Database.
Temporal distributions
Activity in drilling has exhibited distinct patterns over time, as well.
In 1982 and 1983, gas drilling in New York State surged, with 774 and 667 new wells drilled over those two years, respectively. The hot spot was in the Medina Group, which over the years, continued to be a primary focus. Well depths in this section of bedrock average around 3,400 feet at that time, although wells were exploited at a more shallow depth in subsequent years. Starting in 1995, gas was discovered in the Black River shale formation, with reservoirs more than 10,000 feet deep in some places. All of these wells were vertically oriented, but still were exploited using hydraulic fracturing technologies.
Oil
The early to mid-1980s marked a relatively high level in oil well drilling in New York State, with a peak occurring in 1984, with 153 wells drilled. After a lull of about 20 years, activity picked up again in 2005, hitting a high point in 2006 when 188 oil wells were drilled. In 2010, there was another peak with 188 wells, followed by a waning period of 4 years. Then, in 2019, interest exploded in a small area of the Bradford oil fields in Cattaraugus County, with 156 wells drilled, and an average production of 319 barrels per well over the course of that year.
Economic implications
According to EIA estimate from 2014, the cost of drilling an onshore oil well is between $4.9 – 8.3 million, however smaller vertical wells like those common in New York State are likely to cost more in the range of $150,000. With the price of oil at $64 a barrel in 2019, in its first year in production, the gross profit of any of these wells in New York, based on reported production, would have been between $0 and $120,000, with an average year around $20,400 per well. It’s hard to imagine how drilling for oil in recent years in New York State could have possibly been profitable, in particular with the steep drop-off in production typically seen after the first year or two.
These simple examples of a localized “oil boom” in New York State provide a stark example of exactly how unsustainable these endeavors are, particularly for small drilling operators. So, despite the enthusiastic rush to oil drilling in 2019, activity after that has been followed by a quick decline, with only 41 oil wells drilled in New York State in 2020, and only 4, so far, in 2021.
Patterns in other types of wells
The increase in dry wells seems to track with the general patterns of oil and gas exploration. Hence, in periods when a lot of oil and gas wells are being drilled, there will be a higher number of wells that are dry, or nonproductive. During the 1970s, there was also a strong peak in disposal wells drilled. We are not certain whether this is, or is not, related to the high number of gas wells drilled during this period.
New York State moving towards better stewardship of legacy wells
Some of the oil and gas wells drilled in the 19th and early 20th century were particularly poorly documented (or not documented at all), and improperly plugged. This creates a public and environmental safety hazard, with more than 30,000 of these undocumented oil and gas wells spread across the state potentially leaking methane into the air and water. Finding the abandoned and orphan wells has been a long term problem because they are often located in rough terrain across central and western New York. Fortunately, the New York State Department of Environmental Conservation has taken new measures to locate and plug these legacy wells, using drone technology. FracTracker reported on a pilot initiative a few years ago that was testing this technique, but the new program is backed by $400,000 in funding from NYSERDA, the New York State Energy Research and Development Authority, in support of New York States ambitious goals to reduce greenhouse gas emissions through the Climate Leadership and Community Protection Act.
The Takeaway
One hundred years ago, few people expressed concerns about the environmental hazards associated with oil and gas drilling. Record-keeping was spotty, which has left us with a legacy of wells whose locations are lost to memory, or simply improperly plugged. After several periods of vigorous mineral extraction activity in the 1980s and early 2000s, oil and gas drilling has declined in its profitability, and formerly easily-accessed reserves have been depleted. Today, with unprecedented interest in clean energy sources like wind, geothermal, and solar, society can become less dependent on fossil fuels, and focus on responsibly stewarding the remnants of these “dinosaurs,” using new technologies to help clean up the damages left by them.
https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/New-York-State-wells-feature.jpg8331875Karen Edelsteinhttps://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/2021-FracTracker-logo-horizontal.pngKaren Edelstein2021-04-01 11:10:062021-04-13 10:39:49New York State Oil & Gas Well Drilling: Patterns Over Time
This article focuses on the city of Arvin as an example to show how some Frontline Communities in California are completely surrounded by an unrelenting barrage of carcinogenic and toxic air pollutants from oil and gas wells. Kern County’s proposed environmental impact report (EIR) would streamline the approval of an additional 67,000 new oil and gas wells in the County and thus further degrade air quality. We provide several recommendations for how local and state decision-makers can better protect public health from these serious threats.
Upstream greenhouse-gas and volatile organic compound (VOC) emissions from oil and gas extraction have been drastically under-reported throughout the United States, and California’s emissions regulations for oil and gas production wells are not comprehensive enough to protect Frontline Communities. The contribution of VOCs from the oil and gas extraction sector is responsible for California’s central valley and Kern County communities being exposed to the worst air quality in the country. As carcinogens, air toxics, and precursors to ozone, VOC’s present a myriad of health threats.
The contribution of VOCs from the well-sites in Kern, in addition to the cumulative burden of the Central Valley’s degraded air quality, puts Kern residents at considerable risk. Obvious loopholes in the California Air Resources Board’s oil and gas rule must be addressed immediately, and revised to prevent the cumulative impact of multiple exposure sources from causing additional documented negative health impacts. Additionally Kern County’s proposed environmental impact report (EIR) would streamline the approval of an additional 67,000 new oil and gas wells in the County and thus further degrade air quality. It is crucial that the EIR is instead revised to eliminate extraction near sensitive populations. (For more details on this proposal, see our more in depth environmental justice analysis of Kern County and our article on the proposed EIR.)
In support of establishing new public health rules that protect Frontline Communities, Earthwork’s Community Empowerment Project, in collaboration with the Central California Environmental Justice Network and FracTracker Alliance, has focused on documenting the uncontrolled emissions from extraction sites within and surrounding the small city of Arvin, California. Using infrared cameras with state of the art optical gas imaging (OGI) technology, the team documented major leaks at multiple well-sites. Footage from Arvin spans the years from 2016-2020. A collection of this footage has been compiled into the interactive story map that follows.
Toxic Emissions Filmed at Oil and Gas Wells in Arvin, CA
This StoryMap explores how current California regulations fail to stop emissions from tanks on oil and gas well-sites by looking at examples of emissions from well-sites in Arvin, California. Place your cursor over the image and scroll down to advance the StoryMap and explore a series of maps charting the fracking-for-plastic system. Click on the icon in the bottom left to view the legend.
The cases of uncontrolled emissions in the story map provides just an example of the inventory of uncontrolled emissions sources in Kern County, and California at large. Finding and filming emissions sources while using OGI cameras in California is not at all uncommon, otherwise there would not be seven prime examples just in the City of Arvin. Prior to 2018, emissions from these well-sites went completely unregulated. While the California oil and gas rule (COGR) was developed to address greenhouse gas emissions from small sources, certain aspects of the rule are not being enforced by the local air districts. Rather than requiring tanks to have closed evaporation systems the air districts allow operators to set pressure/vacuum hatches to open and emit toxic and carcinogenic vapors when pressure builds inside tanks. While this is a safety mechanism on tanks, in practice it allows tanks to be consistent sources of exposure that put neighboring communities at risk. Specifically, California Code of Regulations, Title 17, Division 3, Chapter 1, Subchapter 10 Climate Change, Article 4, § 95669, Leak Detection and Repair, Paragraph I states that “Hatches shall remain closed at all times except during sampling, adding process material, or attended maintenance operations.”
While the COGR rule is a step in the right direction to reduce emissions, oil and gas’s legacy of degradation to ambient air quality has placed the Central Valley in the worst categories for these pollutants in the country. This puts Kern residents at considerable risk. The local health department continues to report improved conditions and increased numbers of healthy air days, but the truth is the mean, median and maximum values of ozone concentrations at US EPA monitoring locations in Kern County have remained relatively constant at harmful levels from 2015-2019. Expanding the data to 2020 shows a two sharp decreases in ambient levels of pollutants that correspond to decreases in reported production volumes for the county. The first decrease in 2016 corresponds to a drop in production following the institution of State Bill requirements for fracking permits. The decrease in 2020 is a result of the slowed production and burning of fossil fuels related to the Covid-19 Pandemic, as shown below in Figure 1.
Figure 1. Plot of annual Maximum 1 hour Ozone concentrations at all monitoring locations in western Kern County. Ozone concentrations are presented in parts per million. Annual trends in ambient concentrations of ozone. Note the decrease in concentrations in 2016 and in 2020. Both events correlate to decreases in production.
Using the U.S. EPA’s AirData mapping portal, air quality data for Kern County was exported, compiled and plotted to show trends over time. Above in Figure 1, annual ambient concentrations of ozone are shown. The trends of ambient concentrations follow similar trends in the spatial and temporal distribution of CalGEM reported production volumes. FracTracker Alliance is conducting more thorough analyses of these correlations, so stay tuned for future reports.
The locations of these monitoring locations are shown below in the map in Figure 2. Note that there are not any monitors in northwestern Kern, near large oil fields including North Belridge and Lost Hills. The communities near these fields, such as the City of Lost Hills are predominantly Latinx with elevated levels of linguistic isolation and poverty.
Figure 2. Map of Air Quality Monitors in Kern County.
Conclusion
Permitting new oil and gas wells in Kern County is certain to degrade the already harmful local and regional ambient air quality of the Central Valley. Kern County’s proposed EIR, as it stands will streamline an additional 67,000 sources of VOCs to the inventory of emissions already impacting communities. The health impacts from concentrations of ozone are well established, and the release of VOCs are major risk driver for communities living closest to oil and gas extraction operations as well as for regional public health. Together, these primary and secondary pollutants create a major risk driver for Kern County communities. Globally, these emissions are responsible for upwards of 8 million premature deaths annually. The burden on Frontline Communities in Kern County is likely much higher, and will only grow if the currently drafted EIR is passed. Additional air quality monitoring stations in northwestern Kern County should be installed immediately to help track air quality impacts.
To reduce this harm to Frontline Communities, California Senator Scott Weiner has submitted a new senate bill. Senate Bill 467 would stop the issuance of hydraulic fracturing permits and create a public health setback distance of 2,500 feet from homes, schools and other health care facilities for all new drilling permits. The bill would also create a program to provide new training and job opportunities for workers who would be negatively impacted by the bill. Senate Bill 467 provides the first step for a green transition away from the health impacts resulting from fossil fuel industries.
The Take Away
Built on sound data and ample research, FracTracker recommends the following measures be taken to protect the health of California’s overburdened Frontline Communities: Kern County should revise its environmental impact report to address the onslaught of harmful oil and gas emissions (EIR), California Air Resources Board’s oil and gas rule should close its loophole allowing emissions from the pressure/vacuum hatch on the tank to be exempt from regulation, and legislators should educate themselves on the importance of 2,500 foot setbacks requirements for oil and gas wells.
References & Where to Learn More
FracTracker’s public comments regarding recommendations to modify the Kern County Draft Environmental Impact Report (EIR): https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/03/Kern.EIR_.comments_FracTrackerAlliance_3.8.21_compressed.pdf
Access to reliable data is crucial to our understanding of risky fracking waste disposal, and in turn, our ability to protect public health. But when it comes to oil and gas liquid waste disposal wells in Pennsylvania, despite monitoring by two separate agencies, we are left with an incomplete and inaccurate account.
If we were to emulate the Charles Dickens classic, this article might begin, “It was the best of datasets, it was the worst of datasets.” Unfortunately, even that would be too generous when it comes to describing available data around oil and gas liquid waste disposal wells in Pennsylvania. To fully understand the legacy and current state of these wells, it is necessary to query the two agencies that have a role in overseeing them, the United States Environmental Protection Agency (EPA) and the Pennsylvania Department of Environmental Protection (DEP).
Given the relatively small inventory of these wells compared to other oil and gas producing states, the problems with the two datasets are enormous. Before jumping into these issues, however, it would be useful to review the nature of these wells, why there are two regulatory agencies involved, and why there are so few of them in Pennsylvania in the first place, relatively speaking.
Disposal Wells Categories
To further our industrial exploits of the planet, humans have found it useful to inject all kinds of things into the earth. In the United States, this ultimately falls under the jurisdiction of EPA’s Underground Injection Control (UIC) program, and the point of injection is known as an injection well. Altogether, there are six classes of injection wells, with those related to oil and gas operations falling into Class II.
There are three categories of Class II injection wells, including waste disposal, enhanced recovery, and hydrocarbon storage. There is also an infamous exemption known as the “Haliburton Loophole,” which has allowed oil and gas companies to inject millions of gallons of hydraulic fracturing fluid into oil and gas wells in order to stimulate production without any federal oversight at all.
When most people speak of “injection wells” in an oil and gas context, they are usually referring to waste disposal wells, and this is our focus here. This well type is also referred to as Class II-D (disposal) and salt water disposal wells (SWD). This latter term is used by a majority of state regulators, so we will use that abbreviation here, even though considering this type of toxic and radioactive fluid “salt water” is surely one of the industry’s most egregious euphemisms.
Dealing with Dangerous Fluids
There are two main types of liquid waste that are disposed of at SWD injection wells. As always, these waste types have a number of different names to keep everyone on their toes but for the sake of simplicity will call them “flowback” and “brine,” and both are problematic materials to handle. Additionally, the very act of industrial-scale fluid injection presents problems in its own right.
As mentioned above, when operators pump a toxic stew of water, sand, and chemicals into a well to stimulate oil and gas production, that mixture is known as hydraulic fracturing fluid, or fracking fluid. Some of these chemicals are so secretive that even the operators of the well don’t know what is included in the mix, let alone nearby residents or first responders in the event of an incident.
Between 10% and 100% of this fluid will return to the surface, and is then known as flowback fluid, becoming a waste stream. In Pennsylvania, the average amount of fracking fluid injected into production wells exceeds 10 million gallons in recent years according to data from the industry’s self-reporting registry known as FracFocus. With more than 12,000 of these wells drilled statewide, disposing of this waste stream becomes an enormous concern.
In addition to flowback fluid, there are pockets of ancient fluids encountered by the drilling and fracking processes that return to surface as well. These solutions are commonly referred to as brine due to their extremely high salt content, although this is not the type of fluid that you’d want to baste a Thanksgiving turkey with. Total salt concentrations can reach up to 343 grams per liter, roughly ten times the salt concentration of sea water. These brines include but are not limited to the familiar sodium chloride that we use to season our food, but include other components as well, including significant bromide and radium concentrations.
When Pennsylvania experimented with our public health by authorizing disposal of these fracking brines in municipal plants designed to treat sewer sludge, the bromides in that drilling waste stream became problematic as they interacted with disinfectants to cause a cancerous class of chemicals known as trihalomethanes. This ended the practice of surface “treatment” from these sites into streams in 2011, and along the way caused many water authorities to switch from chlorine to chloramine disinfectant processes. This, in turn, may have exacerbated lead exposure issues in the region, as the water disinfected with chloramine often eats away at the calcium scale deposits covering lead pipes and solder in the region’s older homes.
Marcellus and Utica wastewater are also very high in a radioactive isotope of radium known as Ra-226, which has a half-life of 1600 years. After that amount of time, half of the present radium will have emitted an alpha particle, which can cause mutations in strands of DNA when introduced inside the body, through contaminated drinking water, for example. After the hazardous expulsion of the alpha particle, the result become radon gas, which is estimated to cause 20,000 lung cancer deaths per year in the United States. Further down the decay chain is Polonium 210, which was infamously used in the assassination of Russian spy Alexander Litvinenko in London in 2006.
None of this should be injected into formations beneath people’s homes, near drinking water supplies, streams, or really anywhere that we aren’t comfortable sacrificing for the next few thousand years.
On top of all the problems with the water chemistry of both produced water and brine, the very act of injecting these fluids into the ground has triggered a large number of earthquakes in areas with frequent or large volumes of waste injection. This human-caused phenomenon is known as induced seismicity. The most well-known example of this is the previously stable state of Oklahoma which surged to have more magnitude 3.0+ earthquakes than California for a number of years during a drilling boom in that region. The largest of these was the magnitude 5.8 Pawnee earthquake in 2016.
Figure 3. PA Earthquakes and Potential Causes: 1/2000 – 2/2021, Magnitude 2.0 or Greater. Most earthquakes in the eastern portion of the state are associated with Quaternary faults. In the western portion, the causes are less straightforward, and include zipper fracking, mine blasting or collapse, and faults that are more ancient and deeper than the Quaternary faults, many of which remain unmapped. As the use of SWD wells increases, seismic activity may increase as well.
Manmade earthquakes are not limited to Oklahoma. For example, there were approximately 130 seismic events in one year period in the Youngstown, Ohio area due to SWD activity, including one measuring 4.0 on the last day of 2011. Over the years, the regulatory reaction to induced earthquakes seems to walking along the slippery slope from “that can’t happen” to “that can’t happen here” to “they’re all small earthquakes” to “we can mitigate the impact,” despite all evidence to the contrary.
Two Regulators
So who gets to be in charge of this dumpster fire? As mentioned above, this is ultimately under the umbrella of EPA’s Underground Injection Control program. However, they have a complicated arrangement with the various states defining who has primary enforcement authority for this type of well.
In Pennsylvania, such wells must obtain a permit from EPA before obtaining a second permit from DEP. In a 2017 hearing in Plum Borough, Allegheny County, furious residents concerned with a variety of issues with a proposed SWD well were told that in Pennsylvania, EPA could only consider whether or not the well would violate the 1972 Clean Water Act when considering the permit, and that the correct audience for everything else would be DEP. Both permits for this well that is near and undear to me were ultimately issued, and operations are expected to begin in the next month if Governor Wolf does not instruct the DEP to reconsider their permit.
There is some precedent for overturning such a permit. In March of 2020, DEP yanked a permit for a SWD well in Grant Township, Indiana County, suddenly respecting a home-rule charter law that the agency had previously sued the Township over.
Without the prospect of royalties or impact fees, no community wants these wells and regulators know that they are nothing but problems. However, the reality is that the regulators oversee an industry that produces a tsunami of this toxic waste – more than 61.8 million barrels of it from unconventional wells in Pennsylvania in 2020 according to self-reported data, which is almost 2.6 billion gallons of the stuff, or slightly more than the capacity of Beaverdam Run Reservoir in Cambria County, a 382 acre lake with an average depth of 20 feet.
Unsuitable Geography
Nationally, injection wells are quite common, with over 740,000 such wells in the EPA inventory for 2018 and Class II (O&G) wells represent about a quarter of this figure. Of these Class II injection wells, roughly 20% are for fluid disposal, giving us an estimated 37,000 SWD wells nationwide. This number is expected to go up, as more than three-quarters of the 8,600 permits issued in 2018 were for oil and gas purposes.
However, in Pennsylvania, there have been quite few of these, compared to other states. The primary reason for this is its geology, which has largely been considered unsuitable for this type of activity. For example, a 2009 industry analysis states:
“The disposal of flowback and produced water is an evolving process in the Appalachians. The volumes of water that are being produced as flowback water are likely to require a number of options for disposal that may include municipal or industrial water treatment facilities (primarily in Pennsylvania), Class II injection wells [SWDs], and on-site recycling for use in subsequent fracturing jobs. In most shale gas plays, underground injection has historically been preferred. In the Marcellus play, this option is expected to be limited, as there are few areas where suitable injection zones are available.”
I discussed this topic in a phone call with an official from EPA, who largely confirmed this point of view, but preferred the phrase, “the geology is complicated” instead of the word “unsuitable.” When the UIC program was established from the 1974 Safe Drinking Water Act, there were only seven such wells in operation, and according to EPA’s data, there were still just 11 active SWD wells in the Commonwealth but with more on the way. I was cautioned that the geology wasn’t the only reason, however. Neighboring Ohio had hundreds of these wells, many of which are clustered close to the border with Pennsylvania. The two states have different primacy and permitting arrangements, which is a factor as well.
I have not come across sources mentioning why Pennsylvania’s geology was so unsuitable – or complicated, if we are being generous. However, there are numerous widespread issues that could be a factor, including voids created by karst and legacy coal mines, and formations that might have otherwise trapped gasses and fluids being punctured with up to 760,000 mostly unplugged oil and gas wells and more than one million drinking water wells.
Even when these fluids have been pumped deep underground, they are not necessarily out of sight and out of mind. For example, an abandoned well in Noble County Ohio suddenly began spewing gas field brine just a few weeks ago, resulting in a fish kill in a nearby stream. The incident is believed to be related to SWD wells in the general vicinity even though the closest of these is miles away from the toxic geyser. The waste fluids injected beneath the surface will exploit any pathway available through crumbling or porous rocks to alleviate the pressure built up from the injection process. These fluids don’t care whether the target is an old gas well, mine void, or drinking water aquifer.
Of course, we could ask the question in reverse, and ask what makes the injection of oil and gas fluids suitable in other locations, and the aggregated evidence would lead us to “nothing” as our answer. Nothing, other than the fact that drilling and fracking produces billions of gallons of liquid waste, and that it has to go somewhere.
Although EPA play a major role in permitting and regulating SWD wells in Pennsylvania, they do not publish data related to these wells on their website. FracTracker started hearing rumors about a spate of new SWD permits all over the state that were not accounted for in DEP data. As it turns out, many of these turned out to be other oil and gas wastewater processing facilities, and the public’s confusion about these is completely understandable because these facilities lacked the proper public notice process. These facilities are concerning in their own right – and residents of Pennsylvania should look here to see if one of these 49 facilities are in their neighborhoods – but these are not disposal wells.
To clear up the confusion, I submitted a Freedom of Information Act request to EPA for a spreadsheet of their Class II injection wells in Pennsylvania. This was apparently an onerous task that would require more than ten hours of labor on their behalf. When I mentioned that I was mostly interested in disposal wells, that sped the process up considerably.
Ultimately, I received a portion of the data fields that I had asked for.
Asked For
Received
Well Name
Yes
Well API Number
Yes
Class II Category (disposal, recovery, storage)
No
Date application received
No
Application status (e.g., pending, complete)
Yes
Application result (e.g., approved, rejected)
No
Application result date (date of EPA’s decision)
No
Well status (e.g., active, plugged)
Yes
Well county name
Yes
Well municipality name
No
Well latitude
Yes
Well longitude
Yes
Table 1 – Summary of fields requested and received in FracTracker’s FOIA submission with EPA.
I started to compare the EPA dataset to DEP’s SWD well dataset, which is a part of its conventional well inventory. Each source had 23 records. We were off to a good start, but this data victory turned out to be limited in scope as the discrepancies between the two datasets continued to grow. Inconsistencies between the two datasets are as follows:
County
DEP API
DEP Well Name
EPA API Match
EPA Name Match
Notes
Allegheny
003-21223
SEDAT 3A
Y
Y
Armstrong
005-21675
HARRY L DANDO 1
Y
Y
Beaver
007-20027
COLUMBIA GAS OF PENNA INC CGPA5
Y
Y
Bedford
009-20039
KENNETH A DIEHL D1
N
N
Not on EPA List
Cambria
021-20018
THE PEOPLES NATURAL GAS CO 4627X
N
N
Not on EPA list
Clearfield
033-27255
FRANK & SUSAN ZELMAN 1
N
Y
DEP / EPA API Number mismatch
033-27257
POVLIK 1
N
Y
No EPA API No.
033-00053
IRVIN A-19 FMLY FEE A 19
Y
Y
033-22059
SPENCER LAND CO 2
Y
Y
Elk
047-23835
FEE SENECA RESOURCES WARRANT 3771 38268
Y
Y
047-23885
FEE SENECA RESOURCES WARRANT 3771 38282
N
Y
DEP / EPA API Number mismatch
Erie
049-24388
NORBERT CROSS 2
Y
Y
049-20109
HAMMERMILL PLT 1
N
N
Not on EPA List
049-00013
HAMMERMILL 3
N
N
Not on EPA List
049-00012
HAMMERMILL 1
N
N
Not on EPA List
Greene
N
N
Not on DEP list. EPA Permit PAS2D210BGRE – no API to match
Indiana
063-31807
MARJORIE C YANITY 1025
Y
Y
063-20246
T H YUCKENBERG 1
Y
Y
Somerset
111-20059
W SHANKSVILLE SALT WATER DISP 1
Y
N
111-20006
MORRIS H CRITCHFIELD 1
Y
N
Potter
105-20473
H A HEINRICK RW-55
CA
Y
Category Anomaly – Not on DEP SWD list – does appear as Plugged OG Well (consistent w/ EPA status notes)
Venango
121-44484
LATSHAW 9
Y
Y
Warren
123-39874
BITTINGER 4
N
Y
API Mismatch (But does match Bittinger #1) Lat/Long match site name
123-33914
JOSEPH BITTINGER 1
N
Y
API Mismatch (But does match Bittinger #4) Lat matches site name, Long slightly off
123-33944
JOSEPH BITTINGER 2
Y
Y
123-33945
JOSEPH BITTINGER 3
CA
Y
Category Anomaly – Not on DEP SWD list – does appear as “Injection”
123-34843
SMITH/RAS UNIT 1
CA
Y
Category Anomaly – Not on DEP SWD list – does appear as “Observation”
123-22665
LEROY STODDARD & FRANK COFFA 1 WELL
N
N
Not on DEP list of all wells. Does appear on eFACTS. No location data
Table 2 – Discrepancies between EPA and DEP data for SWD wells in PA.
Altogether, there was at least one data discrepancy on 17 out of 28 wells (61%) on the combined inventories, and this is allowing for significantly different formatting of the well’s name. The DEP list contained five records that were not on the EPA dataset at all, four records where the well’s API number did not match, three instances where the DEP well type was different from EPA’s listing, two wells with matching API numbers but different well names, two wells that were missing the API number on the EPA list, and one well that was on the EPA list that I have not been able to find in any of DEP’s inventories. These last two wells could not be mapped due to the lack of location data.
It isn’t always possible to know which dataset is erroneous, but the EPA list has several obvious omissions and one instance where the API number and well name are in the wrong columns. The quality of DEP data has improved over the years and appear to have some data controls in place to avoid some of these basic errors. For that reason, I suspect that most of the problems stem from the EPA dataset, and I have used DEP coordinates to map these wells.
Waste Disposal Wells in Pennsylvania
This map contains numerous layers that explore the current state of Class II-D Salt Water Disposal (SWD) injection wells for oil and gas waste in Pennsylvania. View the map “Details” tab below in the top left corner to learn more and access the data, or click on the map to explore the dynamic version of this data.
In the early 1970s, it was recognized that industrial injection of oil and gas waste underground could lead to risks to human health and the environment, so several major protective laws were put in place, including the Clean Water Act of 1972, the Safe Drinking Water Act of 1974, and the Pennsylvania’s 1971 Environmental Rights Amendment. Decades later, it feels like the Pennsylvania Department of Environmental Protection and the United States Environmental Protection Agency don’t take their regulatory responsibilities very seriously when it comes to oil and gas liquid waste disposal wells. While the state does have fewer of this type of well than other states, there are five that are currently under construction, according to the EPA dataset. Many of these, like the Sedat 3A well in Allegheny County, have come after significant community opposition, and many of the residents’ concerns have not been addressed by either agency.
There will undoubtedly be more of these disposal wells proposed in the near future. Residents would do well to hassle their municipalities to update their ordinances for this type of well if they happen to live in a place where such ordinances are possible. Solicitors should be instructed to regularly scour the Pennsylvania Bulletin and be in contact with EPA for the earliest possible notification of a proposed site, so that there is time to respond within the comment periods.
Additionally, the sloppiness of the datasets calls all sorts of questions into play regarding the co-regulation of these wells. In the case of an incident, it’s not even clear that both agencies have the information on hand to even locate the site in the field. Meanwhile, a 61% error rate between the sites name, API number, and status does not inspire confidence that agencies are keeping a close eye on these facilities, to say the least.
Above all, we must all realize that it isn’t safe to assume that someone will let us know when these types of facilities are proposed. Regulators have shown us through their actions that they are thinking far more about the billions of gallons of waste that needs to be disposed of than of the well-being of dozens or even hundreds of neighbors near each toxic dump site.
References & Where to Learn More
Data supporting this article, as well as the static map in Figure 3, can be found here.
FracTracker Pennsylvania articles, maps, and imagery: https://www.fractracker.org/map/us/pennsylvania/
https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/02/Waste-Disposal-Wells-in-Pennsylvania-feature.jpg16673750Matt Kelso, BAhttps://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/2021-FracTracker-logo-horizontal.pngMatt Kelso, BA2021-02-26 12:23:392021-03-12 14:58:33Pennsylvania’s Waste Disposal Wells – A Tale of Two Datasets
Kyle Ferrar, Western Program Coordinator for FracTracker Alliance, contributed to the December 2020 memo, “Recommendations to CalGEM for Assessing the Economic Value of Social Benefits from a 2,500’ Buffer Zone Between Oil & Gas Extraction Activities and Nearby Communities.”
The purpose of this memo is to recommend guidelines to CalGEM for evaluating the economic value of the social benefits and costs to people and the environment in requiring a 2,500 foot setback for oil and gas drilling (OGD) activities. The 2,500’ setback distance should be considered a minimum required setback. The extensive technical literature, which we reference below, analyzes health benefits to populations when they live much farther away than 2,500’, such as 1km to 5km, but 2,500’ is a minimal setback in much of the literature. Economic analyses of the benefits and costs of setbacks should follow the technical literature and consider setbacks beyond 2,500’ also.
The social benefits and costs derive primarily from reducing the negative impacts of OGD pollution of soil, water, and air on the well-being of nearby communities. The impacts include a long list of health conditions that are known to result from hazardous exposures in the vulnerable populations living nearby. The benefits and costs to the OGD industry of implementing a setback are more limited under the assumption that the proposed setback will not impact total production of oil and gas.
The comment letter submitted by Voices in Solidarity against Oil in Neighborhoods (VISIÓN) on November 30, 2020 lays out an inclusive approach to assessing the health and safety consequences to the communities living near oil and gas extraction activities. This memo addresses how CalGEM might analyze the economic value of the net social benefits from reducing the pollution suffered by nearby communities. In doing so, this memo provides detailed recommendations on one part of the broader holistic evaluation that CalGEM must use in deciding the setback rule.
This memo consists of two parts. The first part documents factors that CalGEM should take into account when evaluating the economic benefits and costs of the forthcoming proposed rule. These include factors like the adverse health impacts of pollution from OGD, the hazards causing them and their sources, and the way they manifest into social and economic costs. It also describes populations that are particularly vulnerable to pollution and its effects as well as geographic factors that impact outcomes.
The second part of this memo documents the direct and indirect economic benefits of the proposed rule. Here, the memo discusses the methods and data that should be leveraged to analyze economic benefits of reducing exposure to OGD pollution through setbacks. This includes the health benefits, impacts on worker productivity, opportunity costs of OGD activity within the proposed setback, and the fact that impacted communities are paying the external costs of OGD.
The fossil fuel industry has historically taken advantage of the nation’s mineral estate for private profit, while outsourcing the public health debts of degraded environmental quality to Frontline Communities. While President Biden has recently ordered the Department of Interior to put a 60-day halt on permitting new oil and gas drilling permits on federal lands, no such policy exists for state lands in California. Governor Newsom’s administration has allowed the California Geological Energy Management Division to issue rework and new drilling permits on California state lands, bringing the total number of operational oil and gas wells on state lands up to a total of 178, almost half of which are “idle.” This number pales in comparison to the number of California oil and gas wells on federal lands; a total of 6,997 operational wells.
FracTracker Alliance has mapped out the operational oil and gas wells located on state lands in California, using the California Protected Areas Database. The areas containing the highest concentrations of oil and gas wells on state lands include two sensitive ecosystem environments. Figure 1 shows the 102 operational oil and gas wells located in Southern California’s Bolsa Chica Ecological Preserve. The wells are part of the Huntington Beach oil field. The preserve shares marine habitat with a marine protected area (MPA) and is habitat for numerous rare and several endangered species. More sensitive habitat also threatened by oil and gas extraction; Figure 2 shows the oil and gas production wells on the Sacramento River Delta, just upriver of the Bay Area. It is habitat for several threatened and endangered species such as the Delta Smelt and Giant Garter Snake.
California needs Governor Newsom to take a stand against the further exploitation of California’s public lands. A ban on permitting new wells on state land and a commitment to plug existing wells would set an example for Biden’s administration to make the current 60-day freeze a permanent policy.
Figure 1. The Bolsa Chica Ecological Preserve hosts over 100 operational oil and gas wells that put the preserve’s ecological habitat at risk.
Figure 2. There are 50 operational oil and gas wells permitted on California state lands in the Sacramento River Delta.
https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/02/Figure-2.-There-are-50-operational-oil-and-gas-wells-permitted-on-California-state-lands-in-the-Sacramento-River-Delta-feature.jpg16673750Kyle Ferrar, MPHhttps://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/2021-FracTracker-logo-horizontal.pngKyle Ferrar, MPH2021-02-12 17:42:002021-02-12 17:42:00Oil and Gas Wells on California State Lands
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.
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.
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.
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.
Shafter
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.
Lost Hills, Arvin, & Taft
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.
Bakersfield
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
Ventura
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.
Inglewood
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.
Wilmington
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.
Long Beach
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.
Los Angeles City
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.
https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2020/12/CASetbacksMappic.jpg7731887Kyle Ferrar, MPHhttps://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/2021-FracTracker-logo-horizontal.pngKyle Ferrar, MPH2020-12-17 13:45:242021-01-04 13:28:04People and Production: Reducing Risk in California Extraction
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.
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.
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.
https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2019/08/EQT-Tioga-Wide-7.gif300800Kyle Ferrar, MPHhttps://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/2021-FracTracker-logo-horizontal.pngKyle Ferrar, MPH2020-11-18 12:40:132020-11-25 14:08:38Documenting emissions from new oil and gas wells in California
We updated the FracTracker North Dakota Shale Viewer with current data and additional details on the astronomical levels of water used and waste produced throughout the process of fracking for oil and gas in North Dakota.
As folks who visit the FracTracker website may know, the fracking industry is predicated on cheap sources of water and waste disposal. The water they use to bust open shale seams becomes part of the waste stream that they refer to by the benign term “brine,” equating it to nothing more than the salt water we swim in when we hit the beaches.
Some oil and gas operators like SWEPI and Enervest in Michigan, however, have taken to calling their waste “SLOP” (Figure 1), which from my standpoint is actually refreshingly honest.
Fracking Energy Return on Investment 2012 – 2020
Since we created our North Dakota Shale Viewer on October 5th, 2012, much has changed across the fracking landscape, while other songs have remained the same. Both of these truths exist with respect to fracking’s impact on water and the industry’s inability to get its collective head around the billions of barrels of oftentimes radioactive waste it produces by its very nature. From the outset, fracking was on dubious footing when it came to the water and waste associated with its operations, and we have seen a nearly universal and exponential increase in water demand and waste production on a per well basis since fracking became the highly divisive topic it remains to this day.
Figure 1. Oil & Gas waste tank operated by SWEPI and Enervest at the Hayes pad, Otsego County, Michigan May 21st, 2016 (44.892933, -84.786530). Photo by Ted Auch, FracTracker Alliance.
Environmental economists like to look at energy sources from a more holistic standpoint vis a vis engineers, traditional economists, and the divide-and-conquer rhetoric from Bismarck to the White House. They do this by placing all manner of energy sources along a spectrum of Energy Return On Energy Invested (EROEI).
It stands to reason that if natural gas from fracking were a real “bridge fuel” in the transition away from coal, it would at least approach or exceed the EROEI of the latter, but at 46:1 coal is still four times more efficient than natural gas. However, it must be said that coal’s days are numbered as well. Witness the recent bankruptcy of coal giant Murray Energy, and the only reason its EROEI has increased or remained steady is because the mining industry has transitioned to almost exclusively mountaintop removal and/or strip mining and the associated efficiencies resulting from mechanization/automation.
The North Dakota Shale Viewer
We enhanced our North Dakota Shale Viewer nearly eight years since it debuted. This exercise included the addition of several data layers that speak to the above issues and how they have changed since we first launched the North Dakota Shale Viewer.
It is worth noting that oil production in total across North Dakota has not even doubled since 2012, and gas production has only managed to increase 3.5-fold. However, the numbers look even worse when you look at these totals on a per well basis, which as I have mentioned seems to me to be the only way reasonable people should be looking at production. Using this lens, we see that production of oil in North Dakota on a per well basis oil is 1% less than it was in 2012 and gas production has not even doubled per well. This is a stunning contrast to the upticks in water and waste we have documented and are now including in our North Dakota Shale Viewer.
Water Demand Rises for Fracking
We’ve incorporated individual horizontal well freshwater demand for nearly 12,000 wells up to and including Q1-2020. The numbers are jaw dropping when you consider that at the time we debuted this map North Dakota, unconventional wells were using roughly 2.1 million gallons per well compared to an average of 8.3 million gallons per well so far this year. This per well increase is something we have been documenting for years now in states like Pennsylvania, Ohio, and West Virginia.
This is concerning for multiple reasons, the first being that if fracking ever were to rebound to its halcyon days of the early teens, it would mean some of our country’s most prized and fragile watersheds would be pushed to an irreversible hydrological tipping point. Hoekstra et al. (2012) have come to call this the “blue water” precautionary principle whereby “depletion beyond 20% of a river’s natural flow increases risks to ecological health and ecosystem services.”
Another concern is that while permitting in North Dakota has slowed like it has nationwide, the aforementioned quarterly water usage totals per well are now 5.25 times what they were in October 2012 and the total water used by the industry in North Dakota now amounts to 60.43 billion gallons– that we know of — which is nearly 50 times what the industry had used when we created our North Dakota Shale Viewer (Figure 2).[1]
With respect to the points made earlier about the value of EROEI, this increase in water demand has not been reflected in the productivity of North Dakota’s oil and gas wells, which means the EROEI continues to fall at rate that should make the industry blush. Furthermore, this trend should prompt regulators and elected officials in Bismarck and elsewhere to begin to ask if the long-term and permanent environmental and/or hydrological risk is worth the short-term rewards vis à vis the “blue water” precautionary principle, in this case of the Missouri River, outlined by Hoekstra et al. (2012). It is my opinion that it most assuredly is not and never was worth the risk!
The most stunning aspect of the above divergence in production and water demand is that on a per well basis, water only costs the industry roughly 0.46-0.76% of total well pad costs. This narrow range is a function of the water pricing schemes shared with me by the North Dakota Western Area Water Supply Authority (WAWSA). This speaks to an average price of water between $3.68 and $4.07 per 1,000 gallons for “industrial” use (aka, fracking industry) by way of eight depots and “several hundred miles of transmission and distribution lines” spread across the state’s four northwest counties of Mountrail, Divide, Williams, and McKenzie.
Figure 2. Average Freshwater Demand Per Well and Cumulative Freshwater Demand by North Dakota fracking industry from 2011 to Q1-2020.
Increasing Fracking Waste Production
On the fracking waste front, the monthly trend is quite volatile relative to what we’ve documented in states like Oklahoma, Kansas, and Ohio. Nonetheless, the amount of waste produced is increasing per well and in total. How you quantify this increase is quite sensitive to the models you fit to the data. The exponential and polynomial (Plotted in Figure 3) fits yield 4.76 to 9.81 million barrel per month increases, while linear and power functions yield the opposite resulting in 1.82 to 10.91 million-barrel declines per month. If we assume the real answer is somewhere in between we see that fracking waste is increasingly slightly at a rate of 1.51% per year or 460,194 barrels per month.
Figure 3. Average Per Well and Monthly Total Fracking Waste Disposal across 675 North Dakota Class II Salt Water Disposal (SWD) wells from 2010 to Q1-2020.
North Dakota has concerning legislation related to oil and gas waste disposal. Senate Bill 2344 claims that landowners do not actually own the “subsurface pore space” beneath their property. The bill was passed into law by Legislature last Spring but there are numerous lawsuits working against it. We will have further analysis of this bill published on FracTracker.org soon.
FracTracker collaborated with Earthworks to create an interactive map that allows North Dakota residents to determine if oil and gas waste is disposed of or has spilled near them in addition to a list of recommendations for state and local policymakers, including the closing of the state’s harmful oil and gas hazardous waste loophole. Read the report for detailed information about oil and gas waste in North Dakota.
This data is critical to understanding the environmental and/or hydrological impact(s) of fracking, whether it is Central Appalachia’s Ohio River Valley, or in this case North Dakota’s Missouri River Basin. We will continue to periodically update this data.
Without supply-side price signaling or adequate regulation, it appears that the industry is uninterested and insufficiently incentivized to develop efficiencies in water use. It is my opinion that the only way the industry will be incentivized to do so is if states put a more prohibitive and environmentally responsible price on water and waste. In the absence of outright bans on fracking, we must demand the industry is held accountable for pushing watersheds to the brink of their capacity, and in the process, compromising the water needs of so many communities, flora, and fauna.
[1] Here in Ohio where I have been looking most closely at water supply and demand across the fracking landscape it is clear that we aren’t accounting for some 10-12% of water demand when we compare documented water withdrawals in the numerator with water usage in the denominator.
https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2020/06/Oil-Gas-waste-tank-in-Michigan-feature.jpg8963125Ted Auch, PhDhttps://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/2021-FracTracker-logo-horizontal.pngTed Auch, PhD2020-06-18 10:24:572020-08-24 14:49:53The North Dakota Shale Viewer Reimagined: Mapping the Water and Waste Impact
Kern County, California has approved at least 18,356 illegal permits to drill new and rework existing oil and gas wells from 2015 – 2019 (data downloaded May 18, 2020). In a monumental decision in February of 2020, a California court ruled that a Kern County oil and gas ordinance paid for and drafted by the oil industry violated the state’s foundational environmental law. Kern County has failed to consider the environmental harms resulting from oil and gas drilling, such as water supply and air quality problems, farmland degradation, and increased noise, and communities have had enough.
Starting in 2015, Kern County used a local ordinance to fast-track the drilling of up to 72,000 new oil and gas wells over the next 25 years. The court’s recent decision allows the existing 18,356 permits to remain valid, but blocked the county from issuing any more permits after the end of April, 2020. This is an important victory for Kern County communities, but the existing permits present a public health threat that regulators have never adequately addressed.
To better understand the impacts of these illegal permits, and identify the communities most impacted, FracTracker Alliance has conducted an environmental justice spatial analysis based on the location of the permits. A map of the permits is found below in Figure 1. shows that there are 18,356 “Drilling” and “Rework” permits issued in Kern County since 2015, as well as the 1,304 permits located within 2,500’ of a sensitive receptor, including hospitals, schools, daycares, and homes.
Figure 1. Map of California Geologic Energy Management Division (CalGEM), formerly the California Division of Oil, Gas, and Geothermal Resources (DOGGR), approved drilling and rework permits, 2015-2019.
The ordinance, written by oil industry consultants, sidestepped state requirements for environmental reviews or public notices, as required by the California Environmental Quality Act (CEQA). It was used as a blanket environmental impact report (EIR), so that the threats of specific projects need not be considered.
To pass the ordinance, the county used a flawed study to hide the immense harm caused by oil and gas drilling and extraction. The appellate court that ruled against the ordinance stated it was passed “despite its significant, adverse environmental impacts.” As a result, the county allowed wells to be constructed next to people’s homes, schools, daycares, and healthcare facilities.
Permitting Summary
FracTracker aggregated, cleaned, and compiled California Geologic Energy Management Division’s (CalGEM) datasets of well permits. A breakdown of the statewide counts of permit types is shown below in Table 1. The table shows that in 2019, permits to drill new oil and gas wells made up about 34% of total permits. Over the course of the last five years, statewide permits have been distributed pretty equally between drilling wells, reworking wells to increase production (including re-drilling activities like deepening and sidetracking wells), and plugging and abandoning wells.
Table 1. Breakdown of permit types issued by California Geologic Energy Management Division (CalGEM), formerly the California Division of Oil, Gas, and Geothermal Resources (DOGGR), 2015-2019.
The illegal Kern County ordinance took effect in 2015, and permit counts for Kern County are shown in Table 2 and Figure 2 below. Note the permit count increase from 2014 to 2015 in the graph in Figure 2. The data shows that Kern County permitting counts increased in 2015 with the passage of the illegal ordinance. In 2016, a new statewide rule (State Bill 4) took effect regulating hydraulic fracturing. Since most oil and gas drilling in California was using hydraulic fracturing, permit numbers statewide, including in Kern, fell drastically. Since 2016, permitting rates have been climbing back up to pre-2016 levels. As of May 18, 2020, Kern County has already approved 1,310 new drilling permits, putting Kern County on track to meet or exceed 2015 permit numbers.
Table 2. Breakdown of permit types issued by California Geologic Energy Management Division (CalGEM) in Kern County alone, 2015-2019.
Figure 2. Time Series of drilling permits issued by Kern County, California, 2014 to present.
2015
New Kern ordinance to fast-track permits. Kern permits increase disproportionately.
2016
New SB4 statewide fracking permit requirements. Kern permits decrease as a result.
2016
2017 - 2020
Proportion of Kern permits begin to increase once again
2020
California court ruled that a Kern County oil and gas ordinance paid for and drafted by the oil industry violated the state’s foundational environmental law. State permitting continues under CalGEM.
2020
Kern County is the most heavily drilled county in the United States, and from 2015 to 2019 well permits were issued in Kern at elevated numbers as compared to the rest of the state. From the implementation of the ordinance (2014 to 2015), the proportion of drilling permits issued by Kern County increased from 82% to 94% of the state total. In Figure 3 below, the time series shows that Kern County makes up the majority of permits issued to drill new wells in California, and the proportion of wells drilled in Kern County has been higher from 2015 to 2019 than it had been prior. Not only did the ordinance allow permits to be drilled without any consideration for the community and public health impacts of Frontline Communities, but the actual numbers and proportions of wells drilled in Kern County increased as well. We have mapped these permits in Figure 3 below to show exactly where they are located.
Figure 3. Time series of permits issued to drill new wells in California from 1998 to 2019. The contribution of individual counties is shown with different colors, the area under the trend line representing the cumulative total.
Environmental Justice Mapping
The locations of well permits were mapped using GIS software and overlaid with indicators of social and environmental justice. The layers of Environmental Justice (EJ) mapping data were derived from CalEnviroScreen 3.0 census tract data, assigned to the block level, and 2015 American Community Survey demographical data, also summarized at the census block data.
Demographics
One of the major failings of the Kern County ordinance was the lack of risk communication with Frontline Communities. Not only were communities not informed of proposed drilling projects, all communications from Kern County and CalGem have been posted solely in English. Any attempts at communication of impacts and notices have excluded non-English speakers. Providing notices and information in non-English languages, at the very least in Spanish, needs to be a top priority for any regulatory body in California. The current permitting policy leverages systematic racism to preclude communities from participating in the decision-making processes that directly affect their families’ health.
As shown below in map in Figure 4, the majority of Kern County ranks high in “linguistic isolation” according to CalEnviroScreen 3.0. Our analysis shows that 11,244 permits were issued in block groups that CalEnviroscreen 3.0 has ranked in the top 60th percentile for linguistic isolation. A total 16,143 permits were issued in block groups that are 40% or more Hispanic, and that number increases to 18,000 (98.1%) permits if you include the permits issued in the Midway-Sunset Field, located on the border of one of Kern’s largest, and predominantly “Hispanic,” census block groups.
Figure 4. Map of Oil and Gas Permits with Kern County “Hispanic” Demographics and Language Disparities. The shades of yellow to red census blocks represent the 60th percentile and above linguistic isolation. Hatched census tracts are census blocks with demographical profiles over 40% Hispanic.
Within Kern County, these permits were approved mostly in low income areas, and areas with pre-existing environmental degradation. In the map in Figure 5, below, permit locations were overlaid with CalEnviroScreen 3.0 rankings for existing environmental degradation and median income data from the American Community Survey (2015) to visually show the disparity.
Our analysis shows that 17,978 0f the 18,356 total drilling and reworking permits were issued in census block groups where the median income was at least 20% lower than that of Kern County (Kern median income = $51,579). Additionally, these areas are more impacted by existing sources of pollution. In fact, 18,298 (99.7%) permits were issued in census blocks designated as the above the 60th percentile of those suffering from existing pollution burden by CalEnviroScreen 3.0.
Figure 5. Map of oil and gas permits with Kern County environmental justice areas. Shown in shades of blue are the block groups with median incomes less than 80% of that of the Kern County ($51,579). The hatched areas are above the 60th percentile for CalEnviroScreen pollution burden.
Conclusion
Our results find that from 2015-2019, very few well permits were issued in census blocks that are predominantly white, with median incomes above the median, and low rankings of linguistic isolation. The policies enacted by Kern County to fast track permits were instituted in predominantly poor, linguistically isolated, Hispanic communities already suffering from existing environmental degradation. Through systematic racism, these areas have become Kern County’s “sacrifice zones.” Moving forward, we are pressuring Kern County to adopt a permitting approach that considers the health of Frontline Communities.
Unfortunately, since the court’s decision, well permitting in Kern County has not only continued, but actually accelerated. While the appellate court ordered permitting to stop for one month, the gap was quickly filled. Between March 28 and May 18, 2020; CalGEM approved 733 permits to drill new wells and rework existing wells in Kern County. In addition, CalGEM approved 38 new fracking permits in 2020 since March 28th, all in Kern County (regulated separately under State Bill 4), increasing the environmental burden on Kern communities further. Like Kern County, CalGEM’s permitting process also deserves scrutiny, as state permitting requirements are lax.
These irresponsible policies have had a direct impact on the health of Central Valley communities. Environmental monitoring has shown time and again that emissions from oil and gas wells include a cocktail of air toxics and carcinogens, and that living near oil and gas activity has been shown to be associated with numerous health impacts such as low birth weight, cancer, skin problems, asthma, and depression, The exclusion of Spanish-speaking residents from notifications and information on decisions that affect their health is an even further condemnation of the systematic and outright racism of Kern County’s permitting approach.
There is more work to be done, but the elimination of Kern County’s fast-tracking ordinance is a major win for public health and democracy.
FracTracker Alliance would like to congratulate the organizations responsible for this legislative victory and thank them for all their hard work. They include Committee for a Better Arvin, Committee for a Better Shafter, and Greenfield Walking Group, represented by the Center on Race, Poverty & the Environment, together with the Center for Biological Diversity, and Sierra Club, who was represented by Earthjustice.
By Kyle Ferrar, MPH, Western Program Coordinator, FracTracker Alliance
https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2020/06/CalGEM-Drilling-and-Rework-Permits-2015-2020-feature.jpg8331875Kyle Ferrar, MPHhttps://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/2021-FracTracker-logo-horizontal.pngKyle Ferrar, MPH2020-06-08 08:44:542021-02-02 15:53:05Systematic Racism in Kern County Oil and Gas Permitting Ordinance
Unconventional wells in Pennsylvania were always resource-intensive, but the maps below show how the amount of water used per well has grown significantly in recent years. In 2013, these wells used an average of 5.8 million gallons per well. By 2019, that figure had increased 145%, consuming more than 14.3 million gallons per well. This is a glimpse into the unsustainable resource demands of this industry and the decreasing energy returned on investment.
As fracking proponents will eagerly remind you, hydraulic fracturing was invented decades ago – back in 1947 – so the practice has been in use for quite a while. What really separates modern unconventional shale gas wells from the supposedly traditional, conventional wells is more a matter of scale than anything else. While conventional wells are typically fracked with tens of thousands of gallons of fluid, their unconventional counterparts are far thirstier, consuming millions of gallons per well.
And of course, more inputs translate into more outputs — not necessarily in the form of gas, but in the form of toxic, radioactive waste. This creates a slew of problems ranging from health impacts, to increased transportation, to disposal.
However, this increase in consumption has continued to grow on a per-well basis, so that wells drilled in recent years aren’t really in the same category as wells drilled a decade ago at the beginning of Pennsylvania’s unconventional boom.
In Pennsylvania, unconventional wells are primarily drilled into two deep shale layers, the Devonian-aged Marcellus Shale, which is about 390 million years old, and the Utica Shale from the Late Ordovician period, which was deposited about 60 million years before the Marcellus. These formations have been known about for decades, but did not yield enough gas justify the expense of drilling until the 21st century, when horizontal drilling allowed for a much greater surface area of exposure to the shale formations. However, stimulating this increased distance also requires significantly more fracking fluid – a mixture of water, sand, and chemicals – which increased the consumptive use of water by several orders of magnitude. And in the end, all of this extra work that is required to extract the gas from the ground has made the industry unprofitable, as high production numbers have outpaced demand.
FracFocus Data
As residents in shale fields around the country started to see impacts to their drinking water, they began to demand to know more about what was injected into the ground around them. The industry’s response was FracFocus, a national registry to address the water component of this question, if not the issue of fracking chemicals. In the early days, visitors to the site could only access data one well at a time, so systematic analyses by third parties were precluded. Additionally, record keeping was sloppy, with widespread data entry issues, incorrect locations, duplicate entries, and so forth.
Many of these issues were addressed with the rollout of FracFocus 2.0 in May of 2013. This fixed many of the data entry issues, such as the six different spellings of “Susquehanna” that were used, and enabled downloads of the entire data set. For that reason, when we wanted to look at changes over time, our analysis started in 2013, where only minimal obvious corrections were required at the county level.
Unconventional wells in Pennsylvania were always resource-intensive, but this GIF shows that the amount of water used per well has grown significantly in recent years. In 2013, these wells used an average of 5.8 million gallons per well. By 2019, that figure had increased 145%, consuming more than 14.3 million gallons per well. This is a glimpse into the unsustainable resource demands of this industry and the decreasing energy returned on investment.
However, statewide data is available since 2008, and as long as we keep in mind the data quality issues from the earlier years, the results are even more stark.
Year
FracFocus Reports
Total Water (gal)
Average Water per Well (gal)
Maximum Water (gal)
2008
2
4,117,827
4,117,827
4,117,827
2009
19
37,415,216
4,157,246
6,176,104
2010
57
123,747,550
4,267,157
7,595,793
2011
1,174
786,513,944
4,345,381
12,146,478
2012
1,375
2,721,696,367
4,676,454
14,247,085
2013
1,272
7,431,752,338
5,842,573
19,422,270
2014
1,277
10,359,150,398
8,112,099
26,927,838
2015
904
8,216,787,382
9,089,367
32,049,750
2016
589
5,933,622,817
10,074,063
32,701,940
2017
710
8,547,034,675
12,038,077
38,681,496
2018
805
10,901,333,749
13,542,030
36,812,580
2019
686
9,811,475,207
14,302,442
39,329,556
2020
76
986,425,600
12,979,284
29,177,980
Grand Total
8,946
65,861,073,069
9,248,852
39,329,556
Figure 1: While the total number of frack jobs reported to FracFocus has declined over the years, the amount of water per well has increased substantially.
In terms of the total number of unconventional wells drilled, the boom years in Pennsylvania were around 2010 to 2014, with more than 1,000 wells drilled each of those years, a total that has not been achieved again since. It is important to note that in this FracFocus data, we are not counting the wells, per se, but the reported instances of well stimulation through hydraulic fracturing, commonly called frack jobs. In the earliest portion of the date range, submitting data to FracFocus was voluntary, and therefore the total activity from 2008 through 2010 is vastly undercounted, but we have included what data was available.
It should be noted that the average consumption for frack jobs started in 2020 are down from the 2019 totals, however, the sample size is considerably smaller. This smaller sample due, in part, to reduced drilling activity due to oversupply of gas in the Northeast, but also due to the fact that the year is still in progress. This analysis is based on data downloaded from FracFocus in April 2020.
Changes Over Time
As we examine changes in the average water consumption over time from Figure 1, we can see that operators in Pennsylvania averaged between 4-5 million gallons of water per well from 2008 to 2012. The numbers take off from there, tripling to more than 14 million gallons for 2019, the last full year available. At the same time, drilling operators began experimenting with truly monstrous quantities of water. In 2008, the only well with water data available used just over 4.1 million gallons. By 2019, there was a well that used 39.3 million gallons of water, almost a tenfold increase.
From late 2008 through early 2020, the industry recorded the use of 65.8 billion gallons of water in unconventional wells. Since we know that many wells during the early boom years did not report to FracFocus, the actual usage must be substantially higher. For the years with the most reliable and complete data – 2013 to 2019 – total water consumption ranged from 5.9 to 10.9 billion gallons per year. For context, the average Pennsylvanian uses about 100 gallons per day, or 36,500 gallons per year.
That means that the 10.9 billion gallons that were pumped into fracked wells in 2018 equals the total usage of 298,667 residents for an entire year. Alternatively, that water could have filled 16,517 Olympic-sized swimming pools. It is equivalent to 33,455 acre-feet, meaning it could fill an acre-sized column of water that stretches more than six miles high.
Surely, there must be a better way to make use of our precious resources than to turn millions upon millions of gallons of water into toxic waste.
By Matt Kelso, Manager of Data & Technology, FracTracker Alliance
https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2020/05/waterfall-1806956_1920.jpg9271920Matt Kelso, BAhttps://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/2021-FracTracker-logo-horizontal.pngMatt Kelso, BA2020-05-29 16:22:102020-06-01 10:54:09Fracking Water Use in Pennsylvania Increases Dramatically
Figure 1. Oil Wells in NYS and Their Associated Geological Formations. Gas wells have historically been most productive in the Medina Formation, followed by the Queenston, and also Trenton-Black River Formations. Data source: New York State DEC Oil and Gas Database.
FracTracker Alliance, 2021
