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https://www.kvpr.org/post/dormant-risky-new-state-law-aims-prevent-problems-idle-oil-and-gas-wells

Idle Wells are a Major Risk

Designating a well as “idle” is a temporary solution for operators, but comes at a great economic and environmental cost to Californians 

Idle wells are oil and gas wells which are not in use for production, injection, or other purposes, but also have not been permanently sealed. During a well’s productive phase, it is pumping and producing oil and/or natural gas which profit its operators, such as Exxon, Shell, or California Resources Corporation. When the formations of underground oil pools have been drained, production of oil and gas decreases. Certain techniques such as hydraulic fracturing may be used to stimulate additional production, but at some point operators decide a well is no longer economically sound to produce oil or gas. Operators are supposed to retire the wells by filling the well-bores with cement to permanently seal the well, a process called “plugging.”

A second, impermanent option is for operators to forego plugging the well to a later date and designate the well as idle. Instead of plugging a well, operators cap the well. Capping a well is much cheaper than plugging a well and wells can be capped and left “idle” for indefinite amounts of time.

Well plugging

Unplugged wells can leak explosive gases into neighborhoods and leach toxic fluids into drinking waters. Plugging a well helps protect groundwater and air quality, and prevents greenhouse gasses from escaping and expediting climate change. Therefore it’s important that idle wells are plugged.

While plugging a well does not entirely eliminate all risk of groundwater contamination or leaking greenhouse gases, (read more on FracTracker’s coverage of plugged wells) it does reduce these risks. The longer wells are left idle, the higher the risk of well casing failure. Over half of California’s idle wells have been idle for more than 10 years, and about 4,700 have been idle for over 25 years. A report by the U.S. EPA noted that California does not provide the necessary regulatory oversite of idle wells to protect California’s underground sources of drinking water.

Wells are left idle for two main reasons: either the cost of plugging is prohibitive, or there may be potential for future extraction when oil and gas prices will fetch a higher profit margin.  While idle wells are touted by industry as assets, they are in fact liabilities. Idle wells are often dumped to smaller or questionable operators.

Orphaned wells

Wells that have passed their production phase can also be “orphaned.” In some cases, it is possible that the owner and operator may be dead! Or, as often happens, the smaller operators go out of business with no money left over to plug their wells or resume pumping. When idle wells are orphaned from their operators, the state becomes responsible for the proper plugging and abandonment.

The cost to plug a well can be prohibitively high for small operators. If the operators (who profited from the well) don’t plug it, the costs are externalized to states, and therefore, the public. For example, the state of California plugged two wells in the Echo Park neighborhood of Los Angeles at a cost of over $1 million. The costs are much higher in urban areas than, say, the farmland and oilfields of the Central Valley.

Since 1977, California has permanently sealed about 1,400 orphan wells at a cost of $29.5 million, according to reports by the Division of Oil, Gas, and Geothermal Resources (DOGGR). That’s an average cost of about $21,000 per well, not accounting for inflation. From 2002-2018, DOGGR plugged about 600 wells at a cost of $18.6 million; an average cost of about $31,000.

Where are they?

Map of California’s Idle Wells


View map fullscreen | How FracTracker maps work

The map above shows the locations of idle wells in California.  There are 29,515 wells listed as idle and 122,467 plugged or buried wells as of the most recent DOGGR data, downloaded 3/20/19. There are a total of 245,116 oil and gas wells in the state, including active, idle, new (permitted) or plugged.

Of the over 29,000 wells are listed as idle, only 3,088 (10.4%) reported production in 2018. Operators recovered 338,201 barrels of oil and 178,871 cubic feet of gas from them in 2018. Operators injected 1,550,436,085 gallons of water/steam into idle injection wells in 2018, and 137,908,884 cubic feet of gas.

The tables below (Tables 1-3) provide the rankings for idle well counts by operator, oil field, and county (respectively).  Chevron, Aera, Shell, and California Resources Corporation have the most idle wells. The majority of the Chevron idle wells are located in the Midway Sunset Field. Well over half of all idle wells are located in Kern County.

Table 1. Idle Well Counts by Operator
Operator Name Idle Well Count
1 Chevron U.S.A. Inc. 6,292
2 Aera Energy LLC 5,811
3 California Resources Production Corporation 3,708
4 California Resources Elk Hills, LLC 2,016
5 Berry Petroleum Company, LLC 1,129
6 E & B Natural Resources Management Corporation 991
7 Sentinel Peak Resources California LLC 842
8 HVI Cat Canyon, Inc. 534
9 Seneca Resources Company, LLC 349
10 Crimson Resource Management Corp. 333

 

Table 2. Idle Well Counts by Oil Field
Oil Field Count by Field
1 Midway-Sunset 5,333
2 Unspecified 2,385
3 Kern River 2,217
4 Belridge, South 2,075
5 Coalinga 1,729
6 Elk Hills 958
7 Buena Vista 887
8 Lost Hills 731
9 Cymric 721
10 Cat Canyon 661

 

Table 3. Idle Well Counts by County
County Count by County
1 Kern 17,276
2 Los Angeles 3,217
3 Fresno 2,296
4 Ventura 2,022
5 Santa Barbara 1,336
6 Orange 752
7 Monterey 399
8 Kings 212
9 San Luis Obispo 202
10 Sutter 191

 

Risks

According to the Western States Petroleum Association (WSPA) the count of idle wells in California has increased from just over 20,000 idle wells in 2015 to nearly 30,000 wells in 2018! That’s an increase of nearly 50% in just 3 years!

Nobody knows how many orphaned wells are actually out there, beneath homes, in forests, or in the fields of farmers. The U.S. EPA estimates that there are more than 1 million of them across the country, most of them undocumented. In California, DOGGR officially reports that there are 885 orphaned wells in the state.

A U.S. EPA report on idle wells published in 2011 warned that existing monitoring requirements of idle wells in California was “not consistent with adequate protection” of underground sources of drinking water. Idle wells may have leaks and damage that go unnoticed for years, according to an assessment by the state Department of Conservation (DOC). The California Council on Science and Technology is actively researching this and many other issues associated with idle and orphaned wells. The published report will include policy recommendations considering the determined risks. The report will determine the following:

  • State liability for the plugging and abandoning of deserted and orphaned wells and decommissioning facilities attendant to such wells
  • Assessment of costs associated with plugging and abandoning deserted and orphaned wells and decommissioning facilities attendant to such wells
  • Exploration of mechanisms to ameliorate plugging, abandoning, and decommissioning burdens on the state, including examples from other regions and questions for policy makers to consider based on state policies

Current regulation

As of 2018, new CA legislation is in effect to incentivize operators to properly plug and abandon their stocks of idle wells. In California, idle wells are defined as wells that have not had a 6-month continuous period of production over a 2-year period (previously a 5-year period). The new regulations require operators to pay idle well fees.  The fees also contribute towards the plugging and proper abandonment of California’s existing stock of orphaned wells. The new fees are meant to act as bonds to cover the cost of plugging wells, but the fees are far too low:

  • $150 for each well that has been idle for 3 years or longer, but less than 8 years
  • $300 for each well that has been idle for 8 years or longer, but less than 15 years
  • $750 for each well that has been idle for 15 years or longer, but less than 20 years
  • $1,500 for each well that has been idle for 20 years or longer

Operators are also allowed to forego idle well fees if they institute long-term idle well management and elimination plans. These management plans require operators to plug a certain number of idle wells each year.

In February 2019, State Assembly member Chris Holden introduced an idle oil well emissions reporting bill. Assembly bill 1328 requires operators to monitor idle and abandoned wells for leaks. Operators are also required to report hydrocarbon emission leaks discovered during the well plugging process. The collected results will then be reported publicly by the CA Department of Conservation. According to Holden, “Assembly Bill 1328 will help solve a critical knowledge gap associated with aging oil and gas infrastructure in California.”

While the majority of idle wells are located in Kern County, many are also located in California’s South Coast region. Due to the long history and high density of wells in the Los Angeles, the city has additional regulations. City rules indicate that oil wells left idle for over one year must be shut down or reactivated within a month after the city fire chief tells them to do so.

Who is responsible?

All of California’s wells, from Kern County to three miles offshore, on private and public lands, are managed by DOGGR, a division of the state’s Department of Conservation. Responsibilities include establishing and enforcing the requirements and procedures for permitting wells, managing drilling and production, and at the end of a well’s lifecycle, plugging and “abandoning” it.

To help ensure operator liability for the entire lifetime of a well, bonds or well fees are required in most states. In 2018, California updated the bonding requirements for newly permitted oil and gas wells. These fees are in addition to the aforementioned idle well fees. Operators have the option of paying a blanket bond or a bond amount per well. In 2018, these fees raised $4.3 million.

Individual well fees:

  • Wells less than 10,000 feet deep: $10,000
  • Wells more than 10,000 feet deep: $25,000

Blanket fees:

  • Less than 50 wells: $200,000
  • 50 to 500 wells: $400,000
  • 500 to 10,000 wells: $2,000,000
  • Over 10,000 wells: $3,000,000

With an average cost of at least $31,000 to plug a well, California’s new bonding requirements are still insufficient. Neither the updated individual nor blanket fees provide even half the cost required to plug a typical well.

Conclusions

Strategies for the managed decline of the fossil fuel industry are necessary to make the proposal a reality. Requiring the industry operators to shut down, plug and properly abandon wells is a step in the right direction, but California’s new bonding and idle well fees are far too low to cover the cost of orphan wells or to encourage the plugging of idle wells. Additionally, it must be stated that even properly abandoned wells have a legacy of causing groundwater contamination and leaking greenhouse gases such as methane and other toxic VOCs into the atmosphere.

By Kyle Ferrar, Western Program Coordinator, FracTracker Alliance

Cover photo: Kerry Klein, Valley Public Radio

DOGGR

Literally Millions of Failing, Abandoned Wells

By Kyle Ferrar, Western Program Coordinator, FracTracker Alliance

In California’s Central Valley and along the South Coast, there are many communities littered with abandoned oil and gas wells, buried underground.

Many have had homes, buildings, or public parks built over top of them. Some of them were never plugged, and many of those that were plugged have since failed and are leaking oil, natural gas, and toxic formation waters (water from the geologic layer being tapped for oil and gas). Yet this issue has been largely ignored. Oil and gas wells continue to be permitted without consideration for failing and failed plugged wells. When leaking wells are found, often nothing is done to fix the issue.

As a result, greenhouse gases escape into the atmosphere and present an explosion risk for homes built over top of them. Groundwater, including sources of drinking water, is known to be impacted by abandoned wells in California, yet resources are not being used to track groundwater contamination.

Abandoned wells: plugged and orphaned

The term “abandoned” typically refers to wells that have been taken out of production. At the end of their lifetime, wells may be properly abandoned by operators such as Chevron and Shell or they may be orphaned.

When operators properly abandon wells, they plug them with cement to prevent oil, natural gas, and salty, toxic formation brine from escaping the geological formation that was tapped for production. Properly plugging a well helps prevent groundwater contamination and further air quality degradation from the well. The well-site at the surface may also be regraded to an ecological environment similar to its original state.

Wells that are improperly abandoned are either plugged incorrectly or are “orphaned” by their operators. When wells are orphaned, the financial liability for plugging the well and the environmental cleanup falls on the state, and therefore, the taxpayers.

You don’t see them?

In California’s Central Valley and South Coast abandoned wells are everywhere. Below churches, schools, homes, they even under the sidewalks in downtown Los Angeles!

FracTracker Alliance and Earthworks recently spent time in Los Angeles with an infrared camera that shows methane and volatile organic compound (VOC) emissions. We visited several active neighborhood drilling sites and filmed plumes of toxic and carcinogenic VOCs floating over the walls of well-pads and into the surrounding neighborhoods. We also visited sites where abandoned, plugged wells had failed.

In the video below, we are standing on Wilshire Blvd in LA’s Miracle Mile District. An undocumented abandoned well under the sidewalk leaks toxic and carcinogenic VOCs through the cracks in the pavement as mothers push their children in walkers through the plume. This is just one case of many that the state is not able to address.

California regulatory data shows that there are 122,466 plugged wells in the state, as shown below in the map below. Determining how many of them are orphaned or improperly plugged is difficult, but we can come up with an estimate based on the wells’ ages.

While there are no available data on the dates that wells were plugged, there are data on “spud dates,” the date when operators begin drilling into the ground. Of the 18,000 wells listing spud dates, about 70% were drilled prior to 1980. Wells drilled before 1980 have a higher risk of well casing failures and are more likely to be sources of groundwater contamination.

Additionally, wells plugged prior to 1953 are not considered effective, even by industry standards. Prior to 1950, wells either were orphaned or plugged and abandoned with very little cement. Plugging was focused on protecting the oil reservoirs from rain infiltration rather than to “confine oil, gas and water in the strata in which they are found and prevent them from escaping into other strata.” Of the wells with drilling dates in the regulatory data, 30% are listed as having been drilled prior to the use of cement in well plugging.

With a total of over 245,000 wells in the state database, and considering the lack of monitoring prior to 1950, it’s reasonable to assume there are over 80,000 improperly plugged and unplugged wells in California.

Map of California’s Plugged Wells

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The regions with the highest counts of plugged wells are the Central Valley and the South Coast. The top 10 county ranks are listed below in Table 1. Kern County has more than half of the total plugged wells in the entire state.

Table 1. Ranks of Counties by Plugged Well Counts
  • Rank
  • 1
  • 2
  • 3
  • 4
  • 5
  • 6
  • 7
  • 8
  • 9
  • 10
  • County
  • Kern
  • Los Angeles
  • Orange
  • Fresno
  • Ventura
  • Santa Barbara
  • Monterey
  • San Luis Obispo
  • Solano
  • Yolo
  • Plugged Well Count
  • 65,733
  • 17,139
  • 7,259
  • 6,970
  • 4,302
  • 4,192
  • 2,266
  • 1,463
  • 1,456
  • 1,383

The issue is not unique to California. Nationally, an estimated 2.56 million oil and gas wells have been drilled and 1.93 million wells had been abandoned by 1975. Using interpolated data, the EPA estimates that as of 2016 there were 3.12 million abandoned wells in the U.S. and 69% of them were left unplugged.

In 2017, FracTracker Alliance organized an exercise to track down the locations of Pennsylvania’s abandoned wells that are not included in the PA Department of Environmental Protection’s digital records. Using paper maps and the FracTracker Mobile App, volunteers explored Pennsylvania woodlands in search of these hidden greenhouse gas emitters.

What are the risks?

Emissions

Studies by Kang et al. 2014, Kang et al 2016, Boothroyd et al 2016, and Townsend-Small et al. 2016 have all measured methane emissions from abandoned wells. Both properly plugged and improperly abandoned wells have been shown to leak methane and other VOCs to the atmosphere as well as into the surrounding groundwater, soil, and surface waters. Leaks were shown to begin just 10 years after operators plugged the wells.

Well density

The high density of aging and improperly plugged wells is a major risk factor for the current and future development of California’s oil and gas fields. When fields with old wells are reworked using new technology, such as hydraulic fracturing, CO2 flooding, or solvent flooding (including acidizing, water flooding, or steam flooding), the injection of additional fluid and gas increases pressure in a reservoir. Poorly plugged or aging wells often lack the integrity to avoid a blowout (the uncontrolled release of oil and/or gas from a well). There is a consistent risk that formation fluids will be forced to migrate up the plugged wellbores and bypass the existing plugs.

Groundwater

In a 2014 report, the U.S. Geological Service warned the California State Water Resources Control Board that the integrity of abandoned wells is a serious threat to groundwater sources, stating, “Even a small percentage of compromised well bores could correspond to a large number of transport pathways.”

The California Council on Science and Technology (CCST) has also suggested the need for additional research on existing aquifer contamination. In 2014, they called for widespread testing of groundwater near oil and gas fields, which has still not occurred.

Leaks

In addition to the contamination of underground sources of drinking water, abandoned well failures can even create a pathway for methane and fluids to escape to Earth’s surface. In many cases, such as in Pennsylvania, Texas, and California, where drilling began prior to the turn of the 20th century, many wells have been left unplugged. Of the abandoned wells that were plugged, the plugging process was much less adequate than it is today.

If plugged wells are allowed to leak, surface expressions can form. These leaks can travel to the Earth’s crust where oil, gas, and formation waters saturate the topsoil. A construction supervisor for Chevron named David Taylor was killed by such an event in the Midway-Sunset oil field near Bakersfield, CA. According to the LA Times, Chevron had been trying to control the pressure at the well-site. The company had stopped injections near the well, but neighboring operators continued high-pressure injections into the pool. As a result, migration pathways along old wells allowed formation fluids to saturate the Earth just under the well-site. Tragically, Taylor fell into a 10-foot diameter crater of 190° fluid and hydrogen sulfide.

California regulations

Following David Taylor’s death in 2011, California regulators vowed to make urgent reforms to the management of underground injection, and new rules finally went into effect on April 1, 2018. These regulations require more consistent monitoring of pressure and set maximum pressure standards. While this will help with the management of enhanced oil recovery operations, such as steam and water flooding and wastewater disposal, the issue of abandoned wells is not being addressed.

New requirements incentivizing operators to plug and abandon idle wells will help to reduce the number of orphan wells left to the state, but nothing has been done or is proposed to manage the risk of existing orphaned wells.

Conclusion

Why would the state of California allow new oil and gas drilling when the industry refuses to address the existing messes? Why are these messes the responsibility of private landholders and the state when operators declare bankruptcy?

New bonding rules in some states have incentivized larger operators to plug their own wells, but old low-producing or idle wells are often sold off to smaller operators or shell (not Shell) companies prior to plugging. This practice has been the main source of orphaned wells. And regardless of whether wells are plugged or not, research shows that even plugged wells release fugitive emissions that increase with the age of the plug.

If the fossil fuel industry were to plug the existing 1.666 million currently active wells, there would be nearly 5 million plugged wells that require regular inspections, maintenance, and for the majority, re-plugging, to prevent the flow of greenhouse gases. This is already unattainable, and drilling more wells adds to this climate disaster.

By Kyle Ferrar, Western Program Coordinator, FracTracker Alliance

Thomas Fire Photo by Marcus Yam, LA Times

California’s Oil Fields Add Fuel to the Fire

Never has the saying “adding fuel to the fire” been so literal.

California wildfires have been growing at unheard of rates over the last five years, causing record breaking destruction and loss of life. Now that we’ve had a little rain and perhaps a reprieve from this nightmare wildfire season, it is important to consider the factors influencing the risk and severity of fires across the state.

Oil and gas extraction and consumption are major contributors to climate change, the underlying factor in the recent frequent and intense wildfires. A lesser-known fact, however, is that many wildfires have actually burned in oil fields in California – a dangerous circumstance that also accelerates greenhouse gas emissions. Our analysis shows where this situation has occurred, as well as the oil fields most likely to be burned in the future.

First, we looked at where wildfires are currently burning across the state, shown below in Map 1. This map is from CAL FIRE and is continuously updated.

Map 1. The CAL FIRE 2018 Statewide Incidents Map

CAL FIRE map showing the locations and perimeters of California wildfires

California’s recent fire seasons

The two largest wildfires in California recorded history occurred last year. The Mendocino Complex Fire burned almost a half million acres (1,857 square kilometers) in Mendocino National Forest. The Thomas Fire in the southern California counties of Ventura and Santa Barbara burned nearly 282,000 acres (1,140 square kilometers). A brutal 2017 fire season, however is now overshadowed by the ravages of 2018’s fires.

With the effects of climate change increasing the severity of California’s multi-year drought, each fire season seems to get worse. The Woolsey Fire in Southern California caused a record amount of property damage in the hills of Santa Monica and Ventura County. The Camp Fire in the historical mining town of Paradise resulted in a death toll that, as of early December, has more than tripled any other wildfire. And many people are still missing.

The Thomas Fire

A most precarious situation erupts when a wildfire spreads to an oil field. Besides having a surplus of their super flammable namesake liquid, oil fields are also storage sites for various other hazardous and volatile chemicals. The Thomas Fire was such a scenario.

The Thomas fire burned through the steep foothills of the coastal Los Padres mountains into the oil fields. When in the oil fields, the oil pumped to the surface for production and the stores of flammable chemicals provided explosive fuel to the wildfire. While firefighters were able to get the majority of the fire “contained,” the oil fields were too dangerous to access. According to the community, oil fires remained burning for weeks before they were able to be extinguished.

The Ventura office of the Division of Oil Gas and Geothermal Resources (DOGGR) reported that the Thomas Fire burned through the Taylor Ranch oil fields and a half dozen other oil fields including the Ventura, San Miguelito, Rincon, Ojai, Timbe Canyon, Newhall-Portrero, Honor Rancho and Wayside Canyon. DOGGR Ventura officials said Newhall-Potrero was “half burned over.” Thomas also burned within a 1/3 mile of the Sespe oil field. Schools and other institutions closed down throughout the Los Angeles Basin, but DOGGR said there was no impact on oil and gas operations that far south. The fire spurred an evacuation of the Las Flores Canyon Exxon oil storage facility but thankfully was contained before reaching the facility.

Wildfire threat for oil fields

Map 2. California Wildfires in Oil Fields


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The Thomas Fire was not the first time or the last time an oil field burned in a California wildfire. Map 2 above shows state wildfires from the last 20 years overlaid with maps of California oil fields, oil wells, and high threat wildfire zones. The map shows just the oil fields and oil and gas wells in California that have been burned by a wildfire.

We found that 160 of California’s 517 oil fields (31%) have been burned by encroaching wildfires, affecting more than 10,000 oil and gas well heads.

An ominous finding: the state’s highest threat zones for wildfires are located close to and within oil and gas fields.

The map shows that wildfire risk is greatest in Southern California in Ventura and Los Angeles counties due to the arid environment and high population density. Over half the oil fields that have burned in California are in this small region.

Who is at fault?

Reports show that climate change has become the greatest factor in creating the types of conditions conducive to uncontrollable wildfires in California. Climate scientists explain that climate change has altered the natural path of the Pacific jet stream, the high-altitude winds that bring precipitation from the South Pacific to North America.

In a recent study, researchers from the University of Idaho and Columbia University found that the impact of global warming is growing exponentially. Their analysis shows that since 2000, human-caused climate change prompted 75% more aridity — causing peak fire season to expand every year by an average of nine days. The Fourth National Climate Assessment details the relationship between climate change and wildfire prevalence, and comes to the same conclusion: impacts are increasing.

On the cause of wildfires, the report explains:

Compound extremes can include simultaneous heat and drought such as during the 2011–2017 California drought, when 2014, 2015, and 2016 were also the warmest years on record for the state; conditions conducive to the very large wildfires, that have already increased in frequency across the western United States and Alaska since the 1980s.

Both 2017 and 2018 have continued the trend of warmest years on record, and so California’s drought has only gotten worse. The report goes on to discuss the threat climate change poses to the degradation of utilities’ infrastructure. Stress from climate change-induced heat and drought will require more resources dedicated to maintaining utility infrastructure.

The role of public utilities

The timing of this report could not be more ironic considering the role that utilities have played in starting wildfires in California. Incidents such as transformer explosions and the degradation of power line infrastructure have been implicated as the causes of multiple recent wildfires, including the Thomas Fire and the most recent Woolsey and Camp wildfires – three of the most devastating wildfires in state history. As public traded corporations, these utilities have investors that profit from their contribution to climate change which, in turn, has created the current conditions that allow these massive wildfires to spread. On the other hand, utilities in California may be the least reliant on fossil fuels. Southern California Edison allows customers to pay a surcharge for 100% renewable service, and Pacific Gas and Electric sources just 20% of their electricity from natural gas.

As a result of the fire cases, each of which might be attributed to negligence, stock prices for the two utilities plummeted but eventually rebounded after the California Public Utilities Commission (CPUC) assured investors that the utilities would be “bailed out” in the case of a possible financial failure to the reproach of the general public. The CPUC assured that the state could bail out utilities if they were forced to finance recovery for the fires they may have caused.

CPUC President, Michael Picker, stated:

The CPUC is one of the government agencies tasked with ensuring that investor-owned utilities operate a safe and reliable grid… An essential component of providing safe electrical service is the financial wherewithal to carry out safety measures.

Along with regulation and oversight, part of the agency’s work involves ensuring utilities are financially solvent enough to carry out safety measures.

Conclusion

January 1, 2019 will mark the seventh year of drought in California. Each fall brings anxiety and dread for state residents, particularly those that live in the driest, most arid forests and chaparral zones. Data show that the wildfires continue to increase in terms of intensity and frequency as the state goes deeper into drought induced by climate change.

While California firefighters have been incredibly resourceful, over 70% of California forest land is managed by the federal government whose 2019 USDA Forest Service budget reduces overall funding for the National Forest System by more than $170 million. Moving forward, more resources must be invested in supporting the health of forests to prevent fires with an ecological approach, rather than the current strategy which has focused predominantly on the unsustainable practice of fuel reduction and the risky tactics of “fire borrowing”. And of course, the most important piece of the puzzle will be addressing climate change.

By Kyle Ferrar, Western Program Coordinator, FracTracker Alliance

Feature image by Marcus Yam, LA Times

High Impact Areas and Donut Holes - Variability in PA's Unconventional O&G Industry map

High Impact Areas and Donut Holes – A Look at Unconventional O&G Activity in PA

FracTracker Alliance has been mapping the impacts of unconventional oil and gas (O&G) drilling activity in Pennsylvania since 2010, and the Pennsylvania Shale Viewer is our most complete map to show the impacts of the industry.

While it can rightly be said that the development of the Marcellus Shale and other unconventional formations have affected half the state since 2005, this analysis takes a look at high impact areas, as well as a closer look at areas that have been avoided so far.


By Matt Kelso, Manager of Data and Technology, FracTracker Alliance

http://www.bakersfield.com/news/arvin-looks-to-impose-more-regulations-on-oil-gas-operators/article_2beb26d6-cbdc-11e7-ba1a-4b0ac35a0fa8.html

Arvin, CA – a City in the Most Drilled County in the Country – files for a Setback Ordinance

The City of Arvin, with a population of about 20,000, is located in Kern County, California just 15 miles southeast of Bakersfield. Nicknamed ‘The Garden in the Sun,’ Arvin is moving forward with establishing new regulations that would limit oil and gas development within the city limits.

Setback Map

The new ordinance proposes setback distances for sensitive sites including hospitals and schools, as well as residentially and commercially zoned parcels. The proposal establishes a 300-foot buffer for new development and 600’ for new operations.

In the map below, FracTracker Alliance has mapped out the zoning districts in Arvin and mapped the reach of the buffers around those districts. The areas where oil and gas well permits will be blocked by the ordinance are shown in green, labeled “Buffered Protected Zones.” The “Unprotected Zones” will still allow oil and gas permits for new development.

There are currently 13 producing oil and gas wells within the city limits of Arvin, 11 of them are located in the protected zones. Those within the protected zones are operated by Sun Mountain Oil and Gas and Petro Capital Resources. They were all drilled prior to 1980, and are shown in the map below.

Map 1. Arvin, CA Proposed setback ordinance

View map fullscreen | How FracTracker maps work

Information on the public hearings and proposals can be found in the Arvin city website, where the city posts public notices. As of January 24, 2018, these are the current documents related to the proposed ordinance that you will find on the webpage:

Earlier Proposals in Arvin

The proposed 2017 setback ordinance is in response to a previously proposed 2016 ordinance that would allow Kern County to fast track permits for oil and gas activities without environmental review or any public notice for the next 20 years. This could mean 72,000 new wells without review, in an area that already possesses the worst air quality in the country. Communities of color would of course be disproportionately impacted by such policy. In Kern County, the large percentage of Latinx residents suffer the impacts of oil drilling and fracking operations near their homes schools and public spaces.

In December of 2016, Committee for a Better Arvin, Committee for a Better Shafter, and Greenfield Walking Group, represented by Center for Race, Poverty and the Environment, sued Kern County. The lawsuit was filed in coordination with EarthJustice, Sierra Club, Natural Resources Defense Council, and the Center for Biological Diversity.

The Importance of Local Rule

Self-determination by local rule is fundamental of United States democracy, but is often derailed by corporate industry interests by the way of state pre-emption. There is a general understanding that local governments are able to institute policies that protect the interests of their constituents, as long as they do not conflict with the laws of the state or federal government. Typically, local municipalities are able to pass laws that are more constrictive than regional, state, and the federal government.

Unfortunately, when it comes to environmental health regulations, states commonly institute policies that preserve the rights of extractive industries to access mineral resources. In such cases, the state law “pre-empts” the ability of local municipalities to regulate. Local laws can be considered the mandate of the people, rather than the influence of outside interest on representatives. Therefore, when it comes to land use and issues of environmental health, local self-determination must be preserved so that communities are empowered in their decision making to best protect the health of their citizens.

For more on local policies that regulate oil and gas operations in California, see FracTracker’s pieces, Local Actions in California, as well as What Does Los Angeles Mean for Local Bans?


By Kyle Ferrar, Western Program Coordinator, FracTracker Alliance

Feature image by: Henry A. Barrios / The Californian

Changes to PA Maps feature image

Recent Changes to Pennsylvania Maps

Recently, the Pennsylvania Department of Environmental Protection (DEP) started to offer additional data resources with the introduction of the Open Data Portal. This development, along with the continued evolution of the ArcGIS Online mapping platform that we utilize has enabled some recent enhancements in our mapping of Pennsylvania oil and gas infrastructure. We’ve made changes to the existing Pennsylvania Shale Viewer for unconventional wells, and created a Conventional and Historical Wells in Pennsylvania map.

Unconventional Wells

Rather than defining the newer, industrial-scaled oil and gas wells by specific geological formations, configuration of the well, or the amount of fluid injected into the ground during the hydraulic fracturing process, Pennsylvania’s primary classification is based on whether or not they are considered to be unconventional.

Unconventional Wells – An unconventional gas well is a bore hole drilled or being drilled for the purpose of or to be used for the production of natural gas from an unconventional formation. An unconventional formation is defined as a geologic shale formation below the base of the Elk Sandstone or its geologic equivalent where natural gas generally cannot be produced except by horizontal or vertical well bores stimulated by hydraulic fracturing.

PA Shale Viewer (Unconventional Drilling)

View map fullscreen | How FracTracker maps work

The previous structure of the PA Shale Viewer had separate layers for permits, drilled wells, and violations. This version replaces the first two layers with a single layer of unconventional locations, which we have called “Unconventional Wells and Permits” for the sake of clarity. The violations layer appears in the same format as before. When users are zoomed out, they will see generalized layers showing the overall location of O&G infrastructure and violations in the state, which were formed by creating a one mile buffer around these features. As users zoom in, the generalized layers are then replaced with point data showing the specific wells and violations. At this point, users can click on individual points and learn more about the features they see on the map.

PA Shale Viewer Zoomed In

Figure 1. PA Shale Viewer zoomed in to see individual wells by status

O&G locations are displayed by their well status, as of the time that FracTracker processed the data, including: Abandoned, Active, Operator Reported Not Drilled, Plugged OG Well, Proposed but Never Materialized, and Regulatory Inactive Status. Note that just because a well is classified as Active does not mean that it has been drilled, or even necessarily permitted. These milestones, along with whether or not it has been plugged, can be determined by looking for entries in the permit issue date, spud date, and plug date entries in the well’s popup box.

Conventional and Historical Wells

The map below shows known conventional wells in Pennsylvania along with additional well locations that were digitized from historical mining maps.

Conventional Oil and Gas Wells Map

View map fullscreen | How FracTracker maps work

Although there are over 19,000 unconventional oil and gas locations in Pennsylvania, this figure amounts to just 11% of the total number of wells in the state that the DEP has location data for, the rest being classified as conventional wells. Furthermore, in a state that has been drilling for oil and gas since before the Civil War, there could be up to 750,000 abandoned wells statewide.

The DEP has been able to find the location of over 30,000 of these historical wells by digitizing records from old paper mining maps. This layer has records for 16 different counties, but well over half of these wells are in just three counties – Allegheny, Butler, and Washington. It looks like it would take a lot more work to digitize these historical wells throughout the rest of the state, but even when that happens, we will probably still not know where the majority of the old oil and gas wells in the state are located.


By Matt Kelso, Manager of Data & Technology

Healthy Homes article in PA

Healthy Homes: Re-Framing Fracking Impacts

An Ohio family took joy in raising their kids and cattle at their farmhouse, built in 1853 with crooked walls and no indoor bathrooms. When they leased land to fracking activity, however, the “beep, beep, beep” of heavy truck traffic kept them up all night, and a cow died after drinking a strange fluid flowing on the land during the cold of winter. They dedicated their retirement savings to moving and building a new home, only to soon after receive a compressor station as their neighbor – close enough to hear the engines at all hours and loud enough to make them dread even walking out to their mailbox.

During the upswing of a boom-and-bust cycle of the gas industry in Greene County, the influx of outside workers and the high demand on rental housing resulted in one particular family being unable to secure an apartment. Without adequate housing, their children were temporarily taken from their custody.

In Huntingdon, a young woman resisted a pipeline being forced through her property by stationing herself in a tree, while workers with chainsaws felled those around her. Eminent domain enabled the gas company to claim this privately-owned land under a weak guise of “public good.”

These unsettling but true stories hint at the countless ways fracking plays out in individual households. A healthy home environment – with clean air, potable drinking water, and safety from outside elements – is essential to human life and functioning. Yet, the industrial processes involved in unconventional oil and gas development (UOGD), often summed up with the term “fracking,” may interfere with or even take away the ability to maintain a healthy home.

This article aims to put these household impacts, and the right to a healthy home, at the center of the fracking debate.

Framing the issue

definition-of-a-frame

The way we understand just about anything depends on our frame of reference. A frame, like the frame around a picture, brings its contents into focus. At the same time, it excludes the information outside its borders. A frame declares that what’s inside is what matters. When it comes to the human effects of fracking, various conflicting frames exist, each dictating their own picture of what fracking actually does and means.

health-frame

The frame we use to look at the fracking debate is so important, because it dictates how we talk about and think about the problem. Likewise, if we can identify the frame others are using when they talk about fracking, we can see more clearly what they have prioritized and what they are leaving out of the conversation.

Two researchers who conducted surveys, interviews, and focus groups in five Pennsylvania counties in 2014 and 2015 argue for the need for a new frame.1 Some of the common ways of talking about fracking not only favor shale gas development for reasons like those included in the frame on the left above, they also work against those trying to make a stand against the negative effects fracking. These researchers suggest that, rather than arguing within the existing, dominant frames, activists should consider proactively “reframing the debate around other core values.” The right to a healthy home is a widely-shared value. I propose we adopt a frame that puts that right at the center of the picture.

What is a “healthy home”?

The term healthy home isn’t new. The federal agencies Housing and Urban Development (HUD) and the Centers for Disease Control (CDC) both use this phrase in defining the importance of a home environment free from hazards and contaminants, like lead and radon. Simply put, a healthy home is one that supports health.

Why Now?

We sit poised at a unique moment to take on the task of reframing fracking. While new drilling in some places appears to be on the decline, countless large-scale petrochemical projects, like a growing crop of plastic-producing ethane crackers in the northeast US, are ramping up. These facilities will demand massive supplies of natural gas and byproducts, perpetuating and likely increasing drilling.

The renewed demand on wells and their associated infrastructure increase the burden on those households in its wake, living amid stimulated wells, near odorous compressor stations, next to pipelines with pig launchers spewing emissions.

Continued demand on natural gas – for energy or cheap plastics – also requires less-discussed but equally-invasive infrastructure, such as the massive underground gas storage underlying communities in growing numbers in states like Ohio and Pennsylvania. Such infrastructure exposes residents to the possibility of leaks, like the one that forced the evacuation of thousands of families in Porter Ranch, California. It burdens other communities with the disposal of toxic waste fluids, including underground injection and the associated earthquakes, like the hundreds pockmarking Ohio and now encroaching on Pennsylvania. Keeping the fracking going means communities, like some dairy farming regions in Wisconsin, continue to see the environmental and quality-of-life impacts of frac sand mining.

Engagement is urgent and timely,2 and the entire country has a role to play. This moment in our energy history is a chance for all of us – those affected by, in favor of, concerned about, eager to welcome, or otherwise learning about UOGD – to get clear on our frame of understanding fracking.

pipeline-route-runs-behind-home-and-swingset

A pipeline right-of-way, about 200 yards behind this house and children’s swingset, shows how close fracking infrastructure comes to homes. Photo credit: Leann Leiter

Why a “Healthy Homes” Frame?

Proponents of frames that endorse fracking often live at a considerable distance from the processes involved,3 buffering them and their families from its impacts. According to researchers4 who listened to the testimonies of residents at a community hearing, the distance they lived from the industrial activities shows up in how they talk about fracking. Those in favor tend to use a depersonalized, “birds-eye view” in describing the impacts. People for whom the negative impacts are or will be a part of their lives rely on more descriptive, specific, and place-based language.

Similarly, a frame that focuses on household impacts emphasizes the on-the-ground, lived experience of living near fracking infrastructure. This frame approaches the debate on fracking by continually asking, what is this like for the people who live with the process? What are the impacts to their home environment? Such a frame does not ignore large-scale issues of jobs and energy supply, but grounds these bigger questions with the real and urgent consequences to the people who are suffering.

oval-healthy-homes-frame

Household impacts

Despite rulings that define UOGD as an industrial process, drilling companies locate all manner of infrastructure – wells, pipelines, compressor stations, among others – in areas formerly residential or agricultural. Rules dictating distances from UOGD facilities to structures like houses vary by municipality and state. Yet, these new and often imposing facilities repeatedly occupy the immediate view of homes, or are within close proximity that defy medical and safety warnings.


Video: Glaring light of burning flares and noises both droning and sudden, along with major truck traffic and other changes to the immediate landscape around the household, produce high levels of stress, leading to its own health problems, creating an environment where water may become unsafe to drink and breathing the air becomes a hazard.

The Oil & Gas Threat Map (by Earthworks and FracTracker) shows the populations within a half-mile “threat radius” of infrastructure that includes fracking – close enough for residents to be exposed to contaminated air emissions, and possibly smell disturbing odors, hear loud sounds and feel vibrations, and see bright lights and the fire of emergency flares. As confirmed by the EPA, in some cases, UOGD results in contamination of drinking water, as well.

Researchers at The Environmental Health Project (EHP) offer individual health assessments to residents living in the shadow of fracking operations. In a physician’s thorough review of over 61 assessments, they identified the following symptoms to be temporally related to gas activity:

Table 1. Symptoms temporally related to UOGD

SYMPTOM CATEGORY n Symptom %
UPPER RESPIRATORY SYMPTOMS 39 64% Nose or throat irritation 25 41%
 Sinus pain or infections 17 28%
Nose bleeds 8 13%
CONSTITUTIONAL SYMPTOMS 33 54% Sleep disruption 26 43%
Fatigue 13 21%
 Weak or Drowsy 9 15%
NEUROLOGICAL SYMPTOMS 32 52% Headache 25 41%
Dizziness 11 18%
Numbness 9 15%
Memory loss 8 13%
PSYCHOLOGICAL SYMPTOMS 32 52% Stress or anxiety 23 38%
Irritable or moody 12 20%
Worry 6 10%
LOWER RESPIRATORY SYMPTOMS 30 49% Cough 21 34%
Shortness of breath 19 31%
Weezing 14 23%
GASTRO-INTESTINAL SYMPTOMS 27 44% Nausea 13 21%
Abdominal pain 12 20%
EYE SYMPTOMS 23 38% Itchy eyes 11 18%
Painful or dry 10 16%
DERMATOLOGICAL SYMPTOMS 19 31% Rash 10 16%
Itching 7 11%
Lesions or blisters 6 10%
CARDIAC SYMPTOMS 17 28% Palpitations 9 15%
Chest pain 6 10%
Other cardiac symptoms 6 10%
HEARING CHANGES OR TINNITUS 10 16% Hearing loss 3 5%
Tinnitus (ringing in the ear) 10 16%
 MUSCULOSKELETAL 10 16% Painful joints 9 15%
Aches 7 11%
ENDOCRINE 7 11% Hair loss 7 11%
n =  Number of patients reporting symptom, out of 61 patients assessed
% = Percentage of patients reporting symptom, out of 61 patients assessed
Table adapted from EHP – Click to download Excel spreadsheet

Mental and emotional stress can exacerbate and create physical health symptoms. For households close to fracking, the fear of a disaster, like a well pad fire, or concern for the long term health effects of exposures through air and water can create serious stress. These developments change communities, sometimes in divisive, negative ways, potentially adding to the stress.

Fracking, a disruptive, landscape-altering process can also produce what’s called solastalgia, whereby negatively-perceived changes to the land alter a person’s sense of belonging. In the case of fracking in residential areas, people may lose not only their relationship to the land, but their homes as they once knew them.5 Solastalgia, considered by some researchers to be a new psycho-social condition, is “the lived experience of the physical desolation of home.”6

When Home is Unsafe, Where to Get Help

EHP Trifold Cover

Click to expand and explore the tri-fold. Click here to access and print this free resource, and many others by EHP.

EHP offers a new resource for protecting your health at a household level, called: “Protecting Your Health from Unconventional Oil and Gas Development.” We created this free informational resource in collaboration with residents and health care providers in four different shale gas counties.

The final product is the direct result of input and knowledge from 15 focus groups and project meetings in these affected communities with over 100 participants, including residents and healthcare providers. EHP has packed this resource with practical steps for households amid shale gas development to limit their exposure to air and water contamination that may be associated with fracking.

For follow-up questions, or for free personalized health services for those experiencing fracking-related exposures, you can contact EHP directly at 724-260-5504 or by email at info@environmentalhealthproject.org.

Re-Centering Home in the Fracking Debate

Putting affected households at the center of the fracking debate better reflects the experiences of people on the front lines. This powerful frame could help counter the power of those who speak positively about fracking, but lack direct experience of the process.

For those at the frontlines of fracking, the intent is that these resources and tools will help you protect your health and your homes.

For those not yet directly affected by fracking, you can lend a hand. Show support for health protective measures by signing up at EHP for updates on events, education, and opportunities to make your voice heard. And, whenever and wherever you can weigh in on the debate, put a frame around fracking that puts impacted households at the center.

References

  1. Cooley, R., & Casagrande, D. (2017). Marcellus Shale as Golden Goose. ExtrACTION: Impacts, Engagements, and Alternative Futures.
  2. Short, D., Elliot, J., Norder, K., Lloyd-Davies, E., & Morley, J. (2015). Extreme energy, ‘fracking’ and human rights: a new field for human rights impact assessments?, The International Journal of Human Rights, 19:6, 697-736, DOI:10.1080/13642987.2015.1019219
  3. Cooley, R., & Casagrande, D. (2017). Marcellus Shale as Golden Goose. ExtrACTION: Impacts, Engagements, and Alternative Futures.
  4. Mando, J. (2016). Constructing the vicarious experience of proximity in a Marcellus Shale public hearing. Environmental Communication, 10(3), 352-364.
  5. Resick, L. K. (2016). Gender, protest, and the health impacts of unconventional natural gas development. In Y. Beebeejaum (Ed.), The participatory city (pp. 167-175). Berlin: Jovis Verlag GmgH.
  6. Albrecht et al (2007). Solastalgia: the distress caused by environmental change, Australasian Psychiatry . Vol 15 Supplement.

By Leann Leiter, Environmental Health Fellow for the SW-PA Environmental Health Project and FracTracker Alliance

Feature photograph: A compressor station sits above a beautiful farm in Washington County, Pennsylvania. Photo credit: Leann Leiter

Ethanol and fracking

North American Ethanol’s Land, Water, Nutrient, and Waste Impact

Corn Ethanol and Fracking – Similarities Abound

Even though it is a biofuel and not a fossil fuel, in this post we discuss the ways in which the corn ethanol production industry is similar to the fracking industry. For those who may not be familiar, biofuel refers to a category of fuels derived directly from living matter. These may include:

  1. Direct combustion of woody biomass and crop residues, which we recently mapped and outlined,
  2. Ethanol1 produced directly from the fermentation of sugarcanes or indirectly by way of the intermediate step of producing sugars from corn or switchgrass cellulose,
  3. Biodiesel from oil crops such as soybeans, oil palm, jatropha, and canola or cooking oil waste,2 and
  4. Anaerobic methane digestion of natural gas from manures or human waste.

Speaking about biofuels in 2006, J. Hill et al. said:

To be a viable substitute for a fossil fuel, an alternative fuel should not only have superior environmental benefits over the fossil fuel it displaces, be economically competitive with it, and be producible in sufficient quantities to make a meaningful impact on energy demands, but it should also provide a net energy gain over the energy sources used to produce it.

Out of all available biofuels it is ethanol that accounts for a lion’s share of North American biofuel production (See US Renewables Map Below). This trend is largely because most Americans put the E-10 blends in their tanks (10% ethanol).3 Additionally, the Energy Independence and Security Act of 2007 calls for ethanol production to reach 36 billion gallons by 2022, which would essentially double the current capacity (17.9 billion gallons) and require the equivalent of an additional 260 refineries to come online by then (Table 1, bottom).

US Facilities Generating Energy from Biomass and Waste along with Ethanol Refineries and Wind Farms


View map fullscreen | How FracTracker maps work

But more to the point… the language, tax regimes, and potential costs of both ethanol production and fracking are remarkably similar. (As evidenced by the quotes scattered throughout this piece.) Interestingly, some of the similarities are due to the fact that “Big Ag” and “Big Oil” are coupled, growing more so every year:

The shale revolution has resulted in declining natural gas and oil prices, which benefit farms with the greatest diesel, gasoline, and natural gas shares of total expenses, such as rice, cotton, and wheat farms. However, domestic fertilizer prices have not substantially fallen despite the large decrease in the U.S. natural gas price (natural gas accounts for about 75-85 percent of fertilizer production costs). This is due to the relatively high cost of shipping natural gas, which has resulted in regionalized natural gas markets, as compared with the more globalized fertilizer market. (USDA, 2016)

Ethanol’s Recent History

For background, below is a timeline of important events and publications related to ethanol regulation in the U.S. in the last four decades: 

Benefits of Biofuels

[Bill] Clinton justified the ethanol mandate by declaring that it would provide “thousands of new jobs for the future” and that “this policy is good for our environment, our public health, and our nation’s farmers—and that’s good for America.” EPA administrator Carol Browner claimed that “it is important to our efforts to diversify energy resources and promote energy independence.” – James Bovard citing Peter Stone’s “The Big Harvest,” National Journal, July 30, 1994.

Of the 270 ethanol refineries we had sufficient data for, we estimate these facilities employ 235,624 people or 873 per facility and payout roughly $6.18-6.80 billion in wages each year, at an average of $22.9-25.2 million per refinery. These employees spend roughly 423,000 hours at the plant or at associated operations earning between $14.63 and $16.10 per hour including benefits. Those figures amount to 74-83% of the average US income. In all fairness, these wages are 13-26% times higher than the farming, fishing, and forestry sectors in states like Minnesota, Nebraska, and Iowa, which alone account for 33% of US ethanol refining.

Additional benefits of ethanol refineries include the nearly 179 million tons of CO2 left in the field as stover each year, which amounts to 654,532 tons per refinery. Put another way – these amounts are equivalent to the annual emissions of 10.7 million and 39,194 Americans, respectively.

Finally, what would a discussion of ethanol refineries be without an estimate of how much gasoline is produced? It turns out that the 280 refineries (for which we have accurate estimates of capacity) produce an average of 71.93 million gallons per year and 20.1 billion gallons in total. That figure represents 14.3% of US gasoline demand.

Costs of Biofuels

Direct Costs

Biofuel expansions such as those listed in the timeline above and those eluded to by the likes of the IPCC have several issues associated with them. One of which is what Pimentel et al. considered an insufficient – and to those of us in the fracking NGO community, familiar sounding – “breadth of relevant expertise and perspectives… to pronounce fairly and roundely on this many-sided issue.”

The above acts and reports in the timeline prompted many American farmers to double down on corn at the expense of soybeans, which caused Indirect Land Use Change (ILUC); the global soy market skyrocketed. This, in turn, prompted the clearing and/or burning of large swaths of the Amazonian rainforests and tropical savannas in Brazil, the world’s second-leading soy producer. More recently, large swaths of Indonesia and Malaysia’s equally biodiverse peatland forests have been replaced by palm oil plantations (Table 2 and Figure 3, bottom). In the latter countries, forest displacement is increasing by 2.7-5.3% per year, which is roughly equal to the the rate of land-use change associated with hydraulic fracturing here in the US4 (Figure 1).


Figures 1A and 1B. Palm Oil Production in A) Indonesia and B) Malaysia between 1960 and 2016.

There is an increasing amount of connectivity between disparate regions of the world with respect to energy consumption, extraction, and generation. These connections also affect how we define renewable or sustainable:

In a globalized world, the impacts of local decisions about crop preferences can have far reaching implications. As illustrated by an apparent “corn connection” to Amazonian deforestation, the environmental benefits of corn-based biofuel might be considerably reduced when its full and indirect costs are considered. (Science, 2007)

These authors pointed to the fact that biofuel expectations and/or mandates fail to account for costs associated with atmospheric – and leaching – emissions of carbon, nitrogen, phophorus, etc. during the conversion of lands, including diverse rainforests, peatlands, savannas, and grasslands, to monocultures. Also overlooked were:

  • The ethical concerns associated with growing malnourishment from India to the United States,
  • The fact that 10-60%5 more fossil fuel derived energy is required to produce a unit of corn ethanol than is actually contained within this very biofuel, and
  • The tremendous “Global land and water grabbing” occuring in the name of natural resource security, commodification, and biofuel generation.

Sacrificing long-term ecological/food security in the name of short-term energy security has caused individuals and governments to focus on taking land out of food production and putting it into biofuels.

The rationale for ethanol subsidies has continually changed to meet shifting political winds. In the late 1970s ethanol was championed as a way to achieve energy independence. In the early 1980s ethanol was portrayed as salvation for struggling corn farmers. From the mid and late 1980s onward, ethanol has been justified as saving the environment. However, none of those claims can withstand serious examination. (James Bovard, 1995)

This is instead of going the more environmentally friendly route of growing biofuel feedstocks on degraded or abandoned lands. An example of such an endeavor is the voluntary US Conservation Reserve Program (CRP), which has stabilized at roughly 45-57 thousand square miles of enrolled land since 1990, even though the average payout per acre has continued to climb (Figure 2).

The Average Subsidy to Farmers Per Acre of Conservation Reserve Program (CRP) between 1986 and 2015.

Figure 2. The Average Subsidy to Farmers Per Acre of Conservation Reserve Program (CRP) between 1986 and 2015.

The primary goals of the CRP program are to provide an acceptable “floor” for commodity prices, reduce soil erosion, enhance wildlife habitat, ecosystem services, biodiversity, and improve water quality on highly erodible, degraded, or flood proned croplands. Interestingly CRP acreage has declined by 27% since a high of 56 thousand square miles prior to the Energy Independence and Security Act of 2007 being passed. Researchers have pointed to the fact that corn ethanol production on CRP lands would create a carbon debt that would take 48 years to repay vs. a 93 year payback period for ethanol on Central US Grasslands.

To quote Fred Magdoff in The Political Economy and Ecology of Biofuels:

Alternative fuel sources are attractive because they can be developed and used without questioning the very workings of the economic system — just substitute a more “sustainable,” “ecologically sound,” and “renewable” energy for the more polluting, expensive, and finite amounts of oil. People are hoping for magic bullets to “solve” the problem so that capitalist societies can continue along their wasteful growth and consumption patterns with the least disruption. Although prices of fuels may come down somewhat — with dips in the business cycle, higher rates of production, or a burst in the speculative bubble in the futures market for oil — they will most likely remain at historically high levels as the reserves of easily recovered fuel relative to annual usage continues to decline.

Indirect Costs: Ethanol, Fertilizers, and the Gulf of Mexico Dead Zone

This is the Midwest vs. the Middle East. It’s corn farmers vs. the oil companies. – Dwaney Andreas in Big Stink on the Farm by David Greising

Sixty-nine percent6 of North America’s ethanol refineries are within the Mississippi River Basin (MRB). These refineries collectively rely on corn that receives 1.9-5.1 million tons of nitrogen each year, with a current value of $1.06-2.91 billion dollars or 9,570-26,161 tons of nitrogen per refinery per year (i.e. $5.42-14.81 million per refinery per year). These figures account for 27-73% of all nitrogen fertilizer used in the MRB each year. More importantly, the corn acreage receiving this nitrogen leaches roughly 0.81-657 thousand tons of it directly into the MRB. Such a process amounts to 5-44% of all nitrogen discharged into the Gulf of Mexico each year and 1.7-13.8 million tons of algae responsible for the Gulf’s growing Dead Zone.

Midwest/Great Plains US Ethanol Refineries and Crop Residue Production

Leaching of this nitrogen is analogous to flushing $45.7-371.6 million dollars worth of precious capital down the drain. Put another way, these dollar figures translate into anywhere between 55% and an astonishing 4.53 times Direct Costs to the Gulf’s seafood and tourism industries of the Dead Zone itself.

These same refineries rely on corn acreage that also receives 0.53-2.61 million tons of phosphorus each year with a current value of 0.34-1.66 billion dollars. Each refinery has a phosphrous footprint in the range of 2,700 to 13,334 tons per year (i.e., $1.72-8.47 million). We estimate that 25,399-185,201 tons of this fertilizer phosphorus is leached into the the MRB, which is equivalent to 19% or as much as 1.42 times all the phosphorous dischared into the Gulf of Mexico per year. Such a process means $16.13-117.60 million is lost per year.

Together, the nitrogen and phosphorus leached from acreage allocated to corn ethanol have a current value that is between 75% and nearly 6 times the value lost every year to the Gulf’s seafood and tourism industries.

Indirect Costs: Fertilizer and Herbicide Costs and Leaching

The 270 ethanol refineries we have quality production data for are relying on corn that receives 367,772 tons of herbicide and insecticide each year, with a current value of $6.67 billion dollars or 1,362 tons of chemical preventitive per refinery per year (i.e. $24.7 million per refinery per year). More importantly the corn acreage receiving these inputs leaches roughly 15.8-128.7 thousand tons of it directly into surrounding watersheds and underlying aquifers. Leaching of these inputs is analogous to flushing $287 million to $2.3 billion dollars down the drain.

What’s Next?

During the recent Trump administration EPA, USDA, DOE administrator hearings, the Renewable Fuel Standard (RFS) was cited as critical to American energy independence by a bipartisan group of 23 senators. Among these were Democratic senator Amy Klobuchar and Republican Chuck Grassley, who co-wrote a letter to new EPA administrator Scott Pruitt demanding that the RFS remains robust and expands when possible. In the words of Democratic Senator Heidi Heitkamp – and long-time ethanol supporter – straight from the heart of the Bakken Shale Revolution in North Dakota:

The RFS has worked well for North Dakota farmers, and I’m fighting to defend it. As we’re doing today in this letter, I’ll keep pushing in the U.S. Senate for the robust RFS [and Renewable Volume Obligations (RVOs)] we need to support a thriving biofuels industry and stand up for biofuels workers. Biofuels create good-paying jobs in North Dakota and help support our state’s farmers, who rely on this important market – particularly when commodity prices are challenging.

Furthermore, the entire Iowa congressional delegation including the aforementioned Sen. Grassley joined newly minted USDA Secretary Sonny Perdue when he told the Iowa Renewable Fuels Association:

You have nothing to worry about. Did you hear what he said during the campaign? Renewable energy, ethanol, is here to stay, and we’re going to work for new technologies to be more efficient.

How this advocacy will play out and how the ethanol industry will respond (i.e., increase productivity per refinery or expand the number of refineries) is anybody’s guess. However, it sounds like the same language, lobbying, and advertising will continue to be used by the Ethanol and Unconventional Oil and Gas industries. Additional parallels are sure to follow with specific respect to water, waste, and land-use.

Furthermore, as both industries continue their ramp up in research and development, we can expect to see productivity per laborer to continue on an exponential path. The response in DC – and statehouses across the upper Midwest and Great Plains – will likely be further deregulation, as well.

From a societal perspective, an increase in ethanol production/grain diversion away from people’s plates has lead to a chicken-and-egg positive feedback loop, whereby our farmers continue to increase total and per-acre corn production with less and less people. In rural areas, mining and agriculture have been the primary employment sectors. A further mechanization of both will likely amplify issues related to education, drug dependence, and flight to urban centers (Figures 4A and B).

We still don’t know exactly how efficient ethanol refineries are relative to Greenhouse Gas Emissions per barrel of oil. By merging the above data with facility-level CO2 emissions from the EPA Facility Level Information on Greenhouse gases Tool (FLIGHT) database we were able to match nearly 200 of the US ethanol refineries with their respective GHG emissions levels back to 2010. These facilities emit roughly:

  • 195,116 tons of CO2 per year, per facility,
  • A total of 36.97 million tons per year (i.e., 2.11 million Americans worth of emissions), and
  • 22,265 tons of CO2 per barrel of ethanol produced.

Emissions from ethanol will increase to 74.35 million tons in 2022 if the Energy Independence and Security Act of 2007’s prescriptions run their course. Such an upward trend would be equivalent to the GHG emissions of somewhere between that of Seattle and Detroit.

What was once a singles match between Frackers and Sheikhs may turn into an Australian Doubles match with the Ethanol Lobby and Farm Bureau joining the fray. This ‘game’ will only further stress the food, energy, and water (FEW) nexus from California to the Great Lakes and northern Appalachia.

We are on a thinner margin of food security, just as we are on a thinner margin of oil security… The [World] Bank implicitly questions whether it is wise to divert half of the world’s increased output of maize and wheat over the next decade into biofuels to meet government “mandates.” – Ambrose Evans-Pritchard in The Telegraph

Will long-term agricultural security be sacrificed in the name of short-term energy independence?

US and Global Corn Production and Acreage between 1866 and 2015.

Figure 3. US and Global Corn Production and Acreage between 1866 and 2015.

Figures 4A and 4B. A) Number of Laborers in the US Mining, Oil and Gas, Agriculture, Forestry, Fishing, and Hunting sector and B) US Corn Production Metrics Per Farm Laborer between 1947 and 2015.

Ethanol Tables

Table 1. Summary of our Corn Ethanol Production, Land-Use, and Water Demand analysis

Gallons of Corn Ethanol Produced Per Year 17,847,616,000
Bushels of Corn Needed 6,374,148,571
Percent of US Production 44.73%
Land Needed 104,372,023 acres
“” 163,081 square miles
Percent of Contiguous US Land 5.51%
Percent of US Agricultural Land 11.28%
Gallons of Water Needed 49.76 trillion (i.e. 3.55 million swimming pools)
Gallons of Water Per Gallon of Oil 2,788
Average and Total Site/Industry Capacity
Average Corn Ethanol Production Per Existing or Under Construction Facility (n = 257) 69,717,250
Gallons of Corn Ethanol Produced Per Year 17,847,616,000
Difference Between 2022 Energy Independence and Security Act of 2007 36 Billion Gallon Mandate 18,152,384,000
# of New Refineries Necessary to Get to 2022 Levels 260
Percent Increase Over Current Facility Inventory 1.7
IEA 2009 World Energy Outlook 250-620% Increase Predictions for 2030
250% 44,619,040,000
# of New Refineries Necessary 640
Percent Increase Over Current Facility Inventory 150.00
620% 110,655,219,200
# of New Refineries Necessary 1,587
Percent Increase Over Current Facility Inventory 520.00

Table 2. Global Population Growth and Corn and Soybean Productivity Trends.

Percent Change Metric
+1.13% Global Population Growth Trend
Corn (Bushels Per Acre)
+1.15% Per Year United States
+1.20% Per Year Global
Soybean (Tons Per Acre)
+0.9% Per Year United States
+1.5% Per Year Brazil
Palm Oil (Tons)
+5.1% Per Year Indonesia
+2.7% Per Year Malaysia

References and Footnotes

  1. Ethanol as defined in the Ohio Revised Code (ORC) Corporation Franchise Tax 5733.46 means “fermentation ethyl alcohol derived from agricultural products, including potatoes, cereal, grains, cheese whey, and sugar beets; forest products; or other renewable resources, including residue and waste generated from the production, processing, and marketing of agricultural products, forest products, and other renewable resources that meet all of the specifications in the American society for testing and materials (ASTM) specification D 4806-88 and is denatured as specified in Parts 20 and 21 of Title 27 of the Code of Federal Regulations.”
  2. A) Pyrolysis is included in the biofuel category and involves the anaerobic decay of cellulose rich feedstocks such as switchgrass at high temperatures producing synthetic diesel or syngas, and
    B) According to many researchers biofuels made from waste biomass or crops grown on degraded and abandoned lands with warm-season prairie grasses and legumes incur little or no carbon debt and provide “immediate and sustained Greenhouse Gas (GHG) advantages” by rehabilitating soil health and capturing, rather than emitting by way of increased fertilizer use, various forms of nitrogen including N2O, NO3, and NO2.
  3. According to Fred Magdoff, the ethanol complex is lobbying for “more automobile engines capable of using E-85 (85 percent ethanol, 15 percent gasoline) for which there are currently 2,710 fueling stations across the country although 56% of them are in just nine states: 1) Wisconsin (117), 2) Missouri (107), 3) Minnesota (335), 4) Michigan (174), 5) Indiana (172), 6) Illinois (221),  7) Iowa (193), 8) Texas (99), and 9) Ohio (97). Some states are mandating a mixture greater than 10 percent. Ethanol can’t be shipped together with gasoline in pipelines because it separates from the mixture when moisture is present, so it must be trucked to where it will be mixed with gasoline.” The E-85 blend comes with its own costs including higher emissions of CO, VOC, PM10, SOx, and NOx than gasoline.
  4. McClaugherty, C., Auch, W. Genshock, E. and H. Buzulencia. (2017). Landscape impacts of infrastructure associated with Utica shale oil and gas extraction in eastern Ohio, Ecological Society of America, 100th Annual Meeting, Baltimore, MD, August, 2015.
  5. Hill et al. recently indicated “Ethanol yields 25% more energy than the energy invested in its production, whereas biodiesel yields 93% more.”
  6. An additional 9-10 refineries or 73% of all ethanol refineries are within 25 miles of the Mississippi River Basin.

By Ted Auch, PhD, Great Lakes Program Coordinator, FracTracker Alliance

Cover photo, left: Oil and gas well pad, Ohio. Photo by Ted Auch.
Cover photo, right: A typical ethanol plant in West Burlington, Iowa. Photo by Steven Vaughn.


Data Downloads

Click on the links below to download the datasets used to create the maps in this article.

  1. Detailed US Ethanol water, land, chemical fertilizer, and herbicide demand
  2. Estimates of North American Ethanol Refinery’s water and land-use demand
Mobile app update release feature image

FracTracker Mobile App Now Includes Activity Feed and Mapped Pipelines

Explore and Document Drilling Activity Near You with the FracTracker App

The oil and gas industry – from its wells to pipelines to refineries – has a variety of ways of impacting the communities and environment that surround its infrastructure. Given the scope of the industry, it’s almost impossible to see how oil and gas affects people and for them to share their experiences with others. Until today. FracTracker is excited to announce that we have completely rebuilt and significantly improved our frack-tracking mobile app. This app can serve as a documenting and tracking tool for reporters, residents, researchers, and groups concerned about oil and gas and its impacts.

Screenshots

Updated App Features

The free app, available for iPhone and Android users, still offers the ability to see drilling near you in the U.S. and add reports and photos about this activity onto a shared map. Based on feedback from many of our partners and readers, we have added and updated several features, as well.

  • Profile – Sign in to the app with an email address and password, with the option to add other information to your profile. This area is also where you can privately view your previous and pending reports.
  • Activity Feed – Shows the most recent submissions by app users. Scroll down to view older reports.
  • Save As Draft – Not ready to submit your report? Save it as a draft and return to submit it later.
  • Real-Time Submissions – We will no longer be curating incoming reports before they go live – so the activity feed and map show real-time submissions.
  • Flagging Tool – Mark a submission as inappropriate. A FracTracker moderator will review the report and take the appropriate action.
  • Indicate Senses Affected – Classify a report by the sense(s) impacted – e.g. Nearby drilling activity is loud, or an impoundment is causing noxious odors.
  • Pipelines Mapped – In addition to active wells and user reports, we have added national pipelines to the map. Please note that many of the pipeline locations are approximate because detailed, public pipeline data is lacking. Help us make this information more accurate by posting photos of pipelines near you.

Feedback Loops

Several organizations and community groups helped to test and improve the app during its redesign, including residents living amongst the oil and gas fields on the Front Range of Colorado and Southwest Pennsylvania, as well as with students at Drexel University.

When we redesigned our mobile app, we felt it was important to go into communities that are living amongst the oil and gas industry. Together, we identified what they needed most when reporting their concerns and potential impacts. The results are a very versatile app. People living around urban refinery hubs, as well as those living in rural extraction regions, will find this tool incredibly useful.

We’d love to hear your feedback about these changes once you have had a chance to explore the app’s updated features.

The app was developed by FracTracker Alliance in collaboration with Viable Industries, L.L.C.

Mobile App Contact

Kirk Jalbert, PhD, MFA
Manager of Community-Based Research and Engagement
FracTracker Alliance
jalbert@fractracker.org

PA Oil & Gas Fines feature image

Pennsylvania Oil & Gas Fines Analysis

In March 2017, FracTracker Alliance conducted a review of the available Pennsylvania oil and gas fine data released publicly by the PA Department of Environmental Protection (DEP) to identify trends in industry-related fines over time and by particular operators. In total, the DEP has assessed nearly $36 million in fines to oil and gas extraction and pipeline operators since January 1, 2000. Such fines are associated with over 42,000 violations issued1 by DEP in that time frame, covering 204,000 known oil and gas locations,2 as well as 91,000 miles of pipelines3 within the Commonwealth.

Understanding the Data Structure

The amount of money that the Pennsylvania Department of Environmental Protection (DEP) fines oil and gas (O&G) operations is included in the DEP’s compliance report published on their website. Even though fines data are made available, they are not necessarily straight-forward, and caution must be taken not to over-estimate the total number of assessed fines.

Records of fines are associated with enforcement identification codes on the compliance report. A single fine is often applied to numerous violations, and the full amount of the fine is listed on every record in this subset. Therefore, the total dollar amount of fines assessed to O&G companies appears overstated. For example, if a $400,000 fine were assessed to settle a group of 10 violations, that figure will appear on the report 10 times, for an apparent aggregate of $4,000,000 in fines. To get an accurate representation of fines assessed, we need to isolate fines associated with particular enforcement ID numbers, which are used administratively to resolve the fines.

This process is further complicated by the fact that, on occasion, such enforcement ID numbers are associated with more than one operator. This issue could result from a change in the well’s operator (or a change of the operator’s name), a group of wells in close proximity that are run by different operators, or it might point to an energy extraction company and a midstream company sharing responsibility for an incident. Sometimes, the second operator listed under an enforcement ID is in fact “not assigned.” The result is that we cannot first summarize by operator and then aggregate those subtotals without overstating the total amount of the assessed fines. In all, 62 of the enforcement ID numbers apply to more than one operator, but this figure amounts to less than one percent of the nearly 15,000 distinct enforcement ID numbers issued by DEP.

Conventional & Unconventional Violations & Fines

Oil and gas wells in Pennsylvania are categorized as either conventional or unconventional, with the latter category intended to represent the modern, industrial-scaled operations that are commonly referred to as “fracking wells.” Contrastingly, conventional wells are supposed to be the more traditional O&G wells that have been present in Pennsylvania since 1859. The actual definition of these wells leaves some blurring of this distinction, however, as almost all O&G wells now drilled in Pennsylvania are stimulated with hydraulic fracturing to some degree, and some of the conventional wells are even drilled horizontally – just not into formations that are technically defined as unconventional. For the most part, however, unconventional remains a useful distinction indicating the significant scale of operations.

Table 1. Summary of oil and gas wells, violations, and fines in Pennsylvania

Category Conventional Unconventional (blank) Total
Wells 193,655 10,291 0 203,946
Violations 27,223 6,126 9,026 42,375
Fines $7,000,203 $13,689,032 $21,563,722 $35,949,495*
Fines per Violation 257 2,235 2,389 848
Fines per Well 36 1330  – 176.27
Violations per Well 0.14 0.60  – 0.21
Wells per Violation 7.11 1.68  – 4.81
* The total fine amount issued is not a summary of the three preceding categories, as some of the fines appear in multiple categories

Ninety-five (95)% of the state’s 204,000 O&G wells are classified as conventional, so it should not be surprising to see that this category of wells accounts for a majority of violations issued by the department. However, fines associated with these violations are less frequent, and often less harsh; the $7 million in fines for this category accounts for only 19% of the total assessed penalties. In contrast, the total penalties that have been assessed to unconventional wells in the state are nearly twice that of conventional wells, despite accounting for just 5% of the state’s well inventory

On the 54,412 records on the compliance report, 10,518 (19%) do not indicate whether or not it is an unconventional well. The list of operators includes some well-known conventional and unconventional drilling operators, and hundreds of names of individuals or organizations where O&G drilling is not their primary mode of business (such as municipal authorities and funeral homes). This category also contains violations for midstream operations, such as pipelines and compressor stations. Altogether, 3,795 operators have entries that were not categorized as either conventional or unconventional on the compliance report, and 124 of these operators were issued fines. One additional complication is that some of the violations and fines that fall into this category are cross-referenced in the conventional and unconventional categories, as well.

The resulting impact of these factors is that the blank category obscures the trends for violations and fines in the other two categories. While tempting to reclassify well data in this category as either conventional or unconventional, this would be a tall task due to the sheer number of records involved, and would likely result in a significant amount of errors. Therefore, the FracTracker Alliance has decided to present the data as is, along with an understanding of the complexities involved.

Most Heavily Fined Operators

Despite the numerous caveats listed above, we can get a clear look at the aggregated fines issued to the various O&G operators in the state by constructing our queries carefully. Table 2 shows the top 12 recipients of O&G-related fines assessed by DEP since 2000. Ten of these companies are on the extraction side of the business, and the total number of well permits issued4 to these companies since 2000 are included on the table. By looking at the permits instead of the drilled wells, we discover the operator that was originally associated with the drilling location, whereas the report of drilled wells associates the current operator associated with the site, or most recent operator in the event that the location is plugged and abandoned.

Stonehenge Appalachia and Williams Field Services operate in the midstream sector. Combining the various business name iterations and subsidiaries would be an enormous task, which we did not undertake here, with the exception of those near the top of the list. This includes Vantage Energy Appalachia, which was combined with records from Vantage Energy Appalachia II, and the compliance history of Rice Energy is the sum of three subsidiaries, the drilling company Rice Drilling B, and two pipeline companies, Rice Midstream Holdings and Rice Poseidon Midstream.

Table 2. Top 12 operators that have been assessed oil and gas-related fines by DEP since 2000

Operator Total Fines Conventional Permits Unconventional Permits Violations Fines / Violation Fines / Permit
Range Resources Appalachia LLC $5,717,994 2,104 2,206 819 $6,982 $1,327
Chesapeake Appalachia LLC $3,120,123 18 3,072 754 $4,138 $1,010
Rice Energy* $2,336,552 442 165 $14,161 $5,286
Alpha Shale Res LP $1,681,725 3 62 31 $54,249 $25,873
Stonehenge Appalachia LLC $1,500,000  – 294 $5,102
Cabot Oil & Gas Corp $1,407,275 19 902 726 $1,938 $1,528
CNX Gas Co LLC $1,274,330 1,613 677 387 $3,293 $556
WPX Energy Appalachia LLC $1,232,500 347 159 $7,752 $3,552
Chevron Appalachia LLC $1,077,553 2 604 113 $9,536 $1,778
Vantage Energy Appalachia LLC** $1,059,766 3 300 35 $30,279 $3,498
Williams Field Services Co, LLC $872,404  – 158 $5,522
XTO Energy Inc $739,712 1,962 461 383 $1,931 305
* Fines for Rice Energy here represent the sum of three subsidiaries, the drilling company Rice Drilling B, and two pipeline companies, Rice Midstream Holdings and Rice Poseidon Midstream.

** Fines for Vantage Energy Appalachia were combined with records from Vantage Energy Appalachia II.

Predictably, many of the entries on this list are among the most active drillers in the state, including Range Resources and Chesapeake Appalachia. However, Alpha Shale Resources has the dubious distinction of leading the pack with the highest amount of fines per violation, as well as the highest amount of fines per permit. Fitting in with the theme, the story here is complicated by the fact that Alpha had a joint venture with Rice, before selling them their stake in a group of wells and midstream operations that were fined $3.5 million by DEP.5 On this compliance report, the fines from this incident are split between the two companies.

Fines Issued Over Time

It is worth taking a look at how O&G related fines have varied over time, as well (Figure 1, shown in millions of dollars). Numerous factors could contribute to changes in trends, such as the number of available DEP inspectors,6 the amount of attention being paid to the industry in the media, differing compliance strategies employed by various political administrations, or changes in practices in the field, which could in turn be impacted by significant fines issued in the past.

PA Oil & Gas Fines Analysis chart

Figure 1. O&G Fines Issued by DEP, 2000 through 2016

The notable spike in fines issued from 2010 to 2012 corresponds with the peak of unconventional drilling in the state – 4,908 of these industrial scaled wells were drilled during those three years, amounting to 48% of all unconventional wells in PA. In contrast, only 504 unconventional wells were drilled in 2016, or around a quarter of the total for 2011. In this context, the reduction in fines since the early part of the decade seems reasonable.

The association with the number of unconventional wells falls apart a bit in the years 2013 to 2014, however. These two years saw an average of 1,293 unconventional wells drilled, but the fines issued amounted to only 35% of the 2011 total.

Considerable strides have been made in the public accessibility of oil and gas data available from the PA DEP since FracTracker started requesting and reviewing this information in 2009. Still, there are many gaps in the datasets, such as geolocation details for 10 of the 20 largest fines issued by the department. FracTracker hopes external analyses like this one will help to close such gaps and identify operators who, too, need to improve their compliance records.

References & Footnotes

  1. Pennsylvania Department of Environmental Protection (PA DEP) Oil and Gas (O&G) Compliance Database.
  2. PA DEP O&G Spud Database. Note: Starting date 1/1/1800 captures unknown spud (wells drilled) dates.
  3. Pipeline Hazardous Materials and Safety Administration (PHMSA) Pipeline Data Mart Reports.
  4. PA DEP Permits Issued Database.
  5. State Impact PA. (2016). Rice Energy fined $3.5 million for wellsite and pipeline violations.
  6. PennEnvironment Research & Policy Center. (2017). Fracking Failures 2017, Oil and Gas Industry Environmental Violations in Pennsylvania.

Oil & Gas Fines White Paper

This analysis is also available for download in a printer-friendly, white paper format:


Cover Photo by Pete Stern, Loyalsock, PA

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