Starved Rock State Park by Michelle McCray

How Frac Sand Mining is Altering an Economy Dependent on Starved Rock State Park, IL

An Ottawa, IL resident’s letter to U.S. Silica regarding how the firm’s “frac” sand mines adjacent to Starved Rock State Park will alter the local economy.

Starved Rock State Park

As is so often the case, we find that those things we have taken most for granted are usually the things we miss most when they are gone. The list of what our nation has lost to industrial and commercial concerns couldn’t possibly be compiled in a single article. The short-sighted habits of economic progress have often led to long-term loss and ecologic disaster. That is why it took a man like Abraham Lincoln, a man of long-term vision and wisdom, to sign into existence our first national park, preserving for antiquity what surely would have been lost to our American penchant for development and overuse.

With that in mind, I have always found it amazing how the gears of our own local and state governments have continually chosen the economic path of least resistance and allowed the areas surrounding Starved Rock State Park to be ravaged and destroyed for what is, ultimately, minimal gain. I am no expert but I suspect it could be argued that a full 1/3 of LaSalle County’s economic engine is funded by the simple existence of Starved Rock State Park. Beyond the 2 million plus visitors to the park each year, it cannot be forgotten that nearly every municipality in LaSalle County has directly or indirectly benefited from the countless number of businesses that prosper from the magnetism of the park’s tranquil canyons.

Photos by Michelle McCray of McCray Photography.

Preservation Not Development

As the 4-year battle with Mississippi Sand over development of the Ernat property has proved, there are many rational souls who truly acknowledge the importance of maintaining a healthy and productive park environment. With the recent sale of the Ernat property to U.S. Silica, we are again confronted with the prospect of irrational development of the eastern boundaries of Starved Rock State Park.

Given the gravity of these decisions, I would like to share a letter recently sent on behalf of many of those who have fought so hard and so long for preservation of that same eastern boundary. This letter was sent to Brian Shinn, CEO of U.S. Silica Holdings, INC. (SLCA) in Frederick, Maryland nearly a month ago, and we have yet to receive a response. In sharing this information on FracTracker’s website, I hope this letter will contribute to further discussion among our local representatives over a far more long-term vision of what LaSalle County wishes to be and what qualities, both environmental and economic, that it wishes to maintain and protect:

Letter to US Silica

Dear Mr. Shinn,

I am writing this letter on behalf of dozens of LaSalle County, Illinois residents who have, for the past several years, been intimately involved in the active pursuit of rational use and conservation of our local natural environment. As I am sure you are aware, the debate over use of the Ernat property as a functional sand mining operation has been a long and hard-fought battle. Years of litigation by the Sierra Club and other local environmental groups helped stall it’s development by Mississippi Sand, and have now led to the sale of the Ernat acreage to U.S. Silica. As irrational as the previous proposals were, the sale putting that acreage under your control has not lessened our concerns over the damaging use of that property as it relates to historic Highway 71 and the entire Starved Rock State Park area.

Obviously, sand mining operations have been a long-standing component of LaSalle County economics. Decades of mining under U.S. Silica supervision have not substantially reduced the quality of life for county residents or the natural environment as a whole. However, as can be specified by many local experts, the development and spoilage of the Ernat property will most certainly have longstanding and drastic impacts on both the ecology of Starved Rock State Park and the economic engine that it sustains. Starved Rock State Park attracts over 2 million visitors each year, with an estimated half million visitors using the Hwy. 71 entrance paralleling the Ernat farm as their main gateway into the park. The Ernat property’s river frontage has long been the tranquil eastern entry into the Illinois Canyon area, as well as an active nesting site for countless birds amidst bountiful wetlands and flat, open prairies. The Ernat property’s shared access to Horseshoe Creek has also made it essential to the entire Illinois Canyon ecosystem within the park. In short, any development of this property will most certainly have long-term negative impacts on both the economics and ecology of the Illinois River Basin.

In writing this letter, we are hoping that U.S. Silica, under your guidance, may consider the opportunity to preserve this indispensable parcel of land and examine ways in which U.S. Silica might make this land available as a gift or negotiated property to the state of Illinois. It would certainly be an important addition to the entire Starved Rock State Park area. I have included the signatures of many of our own local coalition. We hope you will consider the long-term impacts that this development would have to one of Illinois premier natural areas. Thank you.

Inspiring Action

I hope those who have signed this letter will be inspired to further action, and those who have not will reconsider their years of inaction. The natural heritage and local economies of our entire Illinois River Basin are depending on it.

Sincerely,

Paul Wheeler

Only when the last tree has died…
and the last river been poisoned…
and the last fish been caught…
will we realize we cannot eat money.

Sand Mining Photos

For additional photos from Illinois, explore our online photo album.


Mr. Wheeler grew up in Oak Lawn, IL and now lives with his wife and daughter in the Ottawa, IL area and is a para-educator.

Feature image by Michelle McCray of McCray Photography.

Karen Edelstein and her partner in Hawaii

Staff Spotlight: Karen Edelstein

As part of our staff spotlight series, learn more about Karen Edelstein and how her work through FracTracker has changed the course of drilling in New York State.

Time with FracTracker: I started with FracTracker in 2010 as a contract employee and then in 2012 started working 25 hours a week as a regular part-time staffer.

Education: M.P.S. in Environmental Management, and B.S. in Natural Resources, both from Cornell University

Office Location: Ithaca, NY

Title: Eastern Program Coordinator

What do you actually do in that role?

My job has changed a lot since I started working for FracTracker. I came to FracTracker when many New Yorkers were frantically learning as much as they could about unconventional drilling for natural gas, which at the time, appeared likely to start happening in the near future. Over a period of years, using credible public data, I have created dozens of maps on topics about geology, water withdrawals, waste transportation, hydrocarbon storage, and documenting the surging movements of public opposition to high-volume hydraulic fracturing for gas. The maps were informative to a wide range of decision-makers, environmental advocates, educators, and citizens.

Now, I’m working more broadly on projects up and down the East Coast. These projects include documenting controversies surrounding pipelines and other oil and gas infrastructure, and the public opposition to this development. I also support FracTracker’s mission to educate and report on the alternatives to fossil fuel infrastructure, and have been looking at renewable energy issues, as well.

Previous Positions and Organizations

Over the past 16 years, I’ve used geographic information systems in positions at numerous environmental and educational organizations, working for land trusts and other nonprofit agencies, secondary school teacher development programs, and county government agencies. Prior to that, I worked as a naturalist and environmental educator for ten years.

How did you first get involved working on oil and gas issues / fracking?

Karen Edelstein, August 2016

Karen Edelstein, FracTracker’s Eastern Program Coordinator

I live in a rural area of New York State that was in the cross-hairs of the oil and gas industry about 9 years ago. Landsmen were at the door asking me to lease my land, “thumper trucks” were pounding the roads trying to get seismic readings, and helicopters were overhead dropping bundles of equipment to conduct testing. Few people, including me, understood the enormity of what was going on. I joined a few community groups that wanted to know more.

Shortly after a multi-year work contract I had at a local college ended, in 2010, I met the (then small) staff of FracTracker at a public training event in Central New York. The organization had just been formed, and the presentation was all about mapping in Pennsylvania. I went right up to the director and told him how much we needed similar work in New York State, and I could be the person to do it! I started working part-time for FracTracker within the month.

What is one of the most impactful projects that you have been involved in with FracTracker?

Our map of New York State bans and moratoria on high volume hydraulic fracturing received a great deal of attention in the years leading up to the eventual statewide ban on the process. Over time, close to 200 municipalities enacted legislation. It was rewarding to document this visually through a progression of dozens of maps during that period. These maps of how municipality after municipality invoked New York State home rule provided important touchstones for community activists, too. In late 2014, in their announcement about the decision to ban HVHF in NYS, New York’s Health and Environment commissioners cited FracTracker’s map as an indication of patterns of strong ambivalence towards the process among state residents:

Together DEC’s proposed restrictions and local bans and moratoria total approximately 7.5 million acres, or about 63% of the resource. Here’s a summary of the local government restrictions and prohibitions. And the picture even gets cloudier. The practical impact of the Dryden decision I mentioned earlier is that even more acreage may be off-limits to HVHF drilling. Within the 4.5 million acres NOT excluded by the state or local restrictions, approximately 253 towns have zoning and 145 have no zoning. Each town with zoning would have to determine whether its current law restricts or even allows HVHF. So those towns without zoning would still have to decide whether to allow HVHF virtually anywhere or to prescribe where drilling could occur. The uncertainty about whether HVHF is an authorized use would undoubtedly result in additional litigation. It would also result in a patchwork of local land use rules which industry has claimed would utterly frustrate the rational development of the shale resource. Clearly the court’s decision shifted the battleground to town boards, to as evidenced by the conflicting claims of the opposing stakeholder groups. According to the Joint Landowners Coalition, many towns in the Southern Tier have passed resolutions favoring HVHF, while the online map from FracTracker.org indicates that many of the same towns are moving toward a ban. Indeed, our own informal outreach to towns in the Southern Tier confirms that even towns that support HVHF decisions are still up in the air. I’d say that the prospects for HVHF development in NY are uncertain, at best.

The BP Whiting, IN Oil Refinery

US Oil Refineries and Economic Justice

How annual incomes in the shadow of oil refineries compare to state and regional prosperity

North American Oil Refinery Capacity (Barrels Per Day (BPD))

Figure 1. North American Oil Refinery Capacity

Typically, we analyze the potential economic impacts of oil refineries by simply quantifying potential and/or actual capacity on an annual or daily basis. Using this method, we find that the 126 refineries operating in the U.S. produce an average of 100,000-133,645 barrels per day (BPD) of oil – or 258 billion gallons per year.

In all of North America, there are 158 refineries. When you include the 21 and 27 billion gallons per year produced by our neighbors to the south and north, respectively, North American refineries account for 23-24% of the global refining capacity. That is, of course, if you believe the $113 dollar International Energy Agency’s 2016 “Medium-Term Oil Market Report” 4.03 billion gallon annual estimates (Table 1 and Figure 1).

Table 1. Oil Refinery Capacity in the United States and Canada (Barrels Per Day (BPD))

United States Canada Mexico Total
Refinery Count 126 17 6 158
Average Capacity 133,645 BPD 104,471 BPD 228,417 BPD 139,619 BPD
Low Foreland & Silver Eagle Refining in NV & WY, 2-3K BPD Prince George & Moose Jaw Refining in BC and SK, 12-15K BPD Pemex’s Ciudad Madero Refinery, 152K BPD
High Exxon Mobil in TX & LA, 502-560K BPD Valero and Irving Oil Refining in QC & NS, 265-300K BPD Pemex’s Tula Refinery, 340K BPD
Median 100,000 BPD 85,000 BPD 226,500 109,000
Total Capacity 16.8 MBPD 1.8 MBPD 1.4 MBPD 22.1 MBPD

Census Tract Income Disparities

However, we would propose that an alternative measure of a given oil refinery’s impact would be neighborhood prosperity in the census tract(s) where the refinery is located. We believe this figure serves as a proxy for economic justice. As such, we recently used the above refinery location and capacity data in combination with US Census Bureau Cartographic Boundaries (i.e., Census Tracts) and the Census’ American FactFinder clearinghouse to estimate neighborhood prosperity near refineries.

Methods

Our analysis involved merging oil refineries to their respective census tracts in ArcMAP 10.2, along with all census tracts that touch the actual census tract where the refineries are located, and calling that collection the oil refinery’s sphere of influence, for lack of a better term. We then assigned Mean Income in the Past 12 Months (In 2014 Inflation-Adjusted Dollars) values for each census tract to the aforementioned refinery tracts – as well as surrounding regional, city, and state tracts – to allow for a comparison of income disparities. We chose to analyze mean income instead of other variables such as educational attainment, unemployment, or poverty percentages because it largely encapsulates these economic indicators.

As the authors of the UN’s International Forum of Social Development paper Social Justice in an Open World wrote:

In today’s world, the enormous gap in the distribution of wealth, income and public benefits is growing ever wider, reflecting a general trend that is morally unfair, politically unwise and economically unsound… excessive income inequality restricts social mobility and leads to social segmentation and eventually social breakdown…In the modern context, those concerned with social justice see the general  increase  in  income  inequality  as  unjust,  deplorable  and  alarming.  It is argued that poverty reduction and overall improvements in the standard of living are attainable goals that would bring the world closer to social justice.

Environmental regulatory agencies like to separate air pollution sources into point and non-point sources. Point sources are “single, identifiable” sources, whereas non-point are more ‘diffuse’ resulting in impacts spread out over a larger geographical area. We would equate oil refineries to point sources of socioeconomic and/or environmental injustice. The non-point analysis would be far more difficult to model given the difficulties associated with converting perceived quality of life disturbance(s) associated with infrastructure like compressor stations from the anecdotal to the empirical.

Results

Primarily, residents living in the shadow of 80% of our refineries earn nearly $16,000 less than those in the surrounding region – or, in the case of urban refineries, the surrounding Metropolitan Statistical Areas (MSAs). Only residents living in census tracts within the shadow of 25 of our 126 oil refineries earn around $10,000 more annually than those in the region.

On average, residents of census tracts that contain oil refineries earn 13-16% less than those in the greater region and/or MSAs (Figure 2). Similarly, in comparing oil refinery census tract incomes to state averages we see a slightly larger 17-21% disparity (Figure 3).

Digging Deeper

United States Oil Refinery Income Disparities (Note: Larger points indicate oil refinery census tracts that earn less than the surrounding region or city)

Figure 4. United States Oil Refinery Income Disparities (Note: Larger points indicate oil refinery census tracts that earn less than the surrounding region or city.)

Oil refinery income disparities seem to occur not just in one region, but across the U.S. (Figure 4).

The biggest regional/MSA disparities occur in northeastern Denver neighborhoods around the Suncor Refinery complex (103,000 BPD), where the refinery’s census tracts earn roughly $42,000 less than Greater Denver residents1. California, too, has some issues near its Los Angeles’ Valero and Tesoro Refineries and Chevron’s Bay Area Refinery, with a combined daily capacity of nearly 600 BPD. There, two California census associations in the shadow of those refineries earn roughly $38,000 less than Contra Costa and Los Angeles Counties, respectively. In the Lone Star state Marathon’s Texas City, Galveston County refinery resides among census tracts where annual incomes nearly $33,000 less than the Galveston-Houston metroplex. Linden, NJ and St. Paul, MN, residents near Conoco Phillips and Flint Hills Resources refineries aren’t fairing much better, with annual incomes that are roughly $35,000 and nearly $33,000 less than the surrounding regions, respectively.

Click on the images below to explore each of the top disparate areas near oil refineries in the U.S. in more detail. Lighter shades indicate census tracks with a lower mean annual income ($).

Conclusion

Clearly, certain communities throughout the United States have been essentially sacrificed in the name of Energy Independence and overly-course measures of economic productivity such as Gross Domestic Product (GDP). The presence and/or construction of mid- and downstream oil and gas infrastructure appears to accelerate an already insidious positive feedback loop in low-income neighborhoods throughout the United States. Only a few places like Southeast Chicago and Detroit, however, have even begun to discuss where these disadvantaged communities should live, let alone how to remediate the environmental costs.

Internally Displaced People

There exists a robust history of journalists and academics focusing on Internally Displaced People (IDP) throughout war-torn regions of Africa, the Middle East, and Southeast Asia – to name a few – and most of these 38 million people have “become displaced within their own country as a result of violence.” However, there is a growing body of literature and media coverage associated with current and potential IDP resulting from rising sea levels, drought, chronic wildfire, etc.

The issues associated with oil and gas infrastructure expansion and IDPs are only going to grow in the coming years as the Shale Revolution results in a greater need for pipelines, compressor stations, cracker facilities, etc. We would propose there is the potential for IDP resulting from the rapid, ubiquitous, and intense expansion of the Hydrocarbon Industrial Complex here in the United States.

N. American Hydrocarbon Industrial Complex Map


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Footnotes and Additional Reading

  1. The Suncor refinery was implicated in a significant leak of tar sands crude associated benzene into the South Platte River as recently as 2013. According to Suncor’s website this refinery “supplies about 35% of Colorado’s gasoline and diesel fuel demand and is a major supplier of jet fuel to the Denver International Airport. The refinery is also the largest supplier of paving-grade asphalt in Colorado.”
  2. New York Times story on the growing footprint of BP’s Whiting Refinery: Surrounded by Industry, a Historic Community Fights for Its Future

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

Mariner East 2 Pipeline Route

Mariner East 2 and Watershed Risks

Mariner East 2 (ME 2) is a $2.5 billion, 350 mile-long pipeline that, if built, would be one of the largest pipeline construction projects in Pennsylvania’s history—carving a fifty-foot wide path through 17 counties. A project of Sunoco Logistics, ME 2 would have the capacity to transport 275,000 barrels a day of propane, ethane, butane, and other hydrocarbons from the shale fields of Western Pennsylvania and neighboring states to an international export terminal in Marcus Hook, located on the Delaware River.

ME 2 has sparked a range of responses from residents in Pennsylvania, however, including concerns about recent pipeline accidents, the ethics of taking land by eminent domain, and the unknown risks to sensitive ecosystems. Below we explore the watersheds that could be impacted by this proposed pipeline.

Watershed Impacts

While some components of Sunoco’s ME 2 proposal are approved, the project requires more permits from the Pennsylvania Department of Environmental Protection (DEP) before construction can begin. Among those are permits to build through and under stream and wetlands. Many of the waters threatened by ME 2 are designated by the Commonwealth as “exceptional value” (EV) or “high quality” (HQ) and are supposed to be given greater protections from harm. Water Obstruction and Encroachment Permits, also known as “Chapter 105” permits, are required for any building activities that would disrupt any body of water, including wetlands and streams. Sunoco applied for these so-called “Chapter 105” permits in the summer of 2015, but its applications were rejected as incomplete several times.

The below map shows the ME 2 route as of May 2016 relative to the watersheds and streams it will cross. Zoom into the map to see additional layers. Note that this is the most accurate representations of ME 2’s route we have seen to date. MWA provided the shapefiles for ME 2’s route to FracTracker Alliance and continues its investigations into potential watershed impacts.

Proposed ME 2 Route

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In total, ME 2’s path will include 1,227 stream crossings, 570 wetland crossings, and 11 pond crossings. Of the 1,227 stream crossings, 19 are EV and 318 are HQ, meaning that 337 crossings will disturb what DEP refers to as “special protection” waters. In addition, there are 129 exceptional value wetlands being crossed. These numbers were compiled by Mountain Watershed Association (MWA) from Sunoco’s permitting applications. MWA also identified 2 HQ streams in Washington County, and 3 HQ streams in Blair County, that are proposed to be crossed that are not acknowledged as being HQ in Sunoco’s permits.

Public Comment Period Open

People living along the proposed route are sometimes in the best position to see what the route looks like from the ground, where wetlands and streams are, and what kinds of wetlands and streams they are. The DEP is accepting public comments on Sunoco’s ME 2 Ch. 105 permit application through Wednesday, August 24. Each DEP regional office receives separate Ch. 105 applications depending on where the pipeline routes through different counties. Those wishing to comment on the project can do so through the DEP regional office websites: DEP Southwest RegionDEP South-central Region, DEP Southeast Region. For guidance on how to write comments on permits, see MWA’s Pipeline Project Information & Talking Points.


We wish to thank Mountain Watershed Association and the Clean Air Council for helping us compile data and analysis for this article.

Written by Kirk Jalbert, PhD, MFA – Manager of Community-Based Research & Engagement, FracTracker Alliance

Launch of the FracTracker Fund

Launch of the FracTracker Fund

New York: A Sunshine State!

Photovoltaic solar resources of the US (NREL)

Photovoltaic solar resources of the US (NREL)

It’s difficult to talk about the risks of oil and gas extraction without providing data on energy alternatives in the conversation. Let’s look at New York State, as an example. There, solar power is taking a leadership position in the renewable energy revolution in the United States. Although New York State receives far less sunshine than many states to the west and south, the trends are bright! Currently, New York State ranks seventh in the nation in installed solar capacity, with over 700 MW of power generated by the sun, enough to power 121,000 homes.

Despite common assumptions that solar power only makes sense where the sun shines 360 days a year, we’ve been seeing successful adoption of solar in Europe for years. For example, in Germany, where even the most southern part of the country is further north of the Adirondack Mountains in New York State, close to 7% of all the power used comes from combined residential and commercial scale photovoltaic sources–35.2 TWh in all. Munich, one of the sunniest places in all of Germany, has a lower average solar irradiation rate of 3.1 kWh/m2/day than most cities in New York State; compare it with locations in New York like Rochester (3.7 kWh/m2/day), New York City (4.0 kWh/m2/day), and Albany (3.8 kWh/m2/day). At present, Germany still leads New York State by more than double the electrical output from solar for equivalent areas.

cumulative_capacity

Cumulative Solar Capacity in New York

The cumulative capacity for completed photovoltaic systems in New York State has risen steeply in the past three years, with ground-mounted and roof-top residential capacity outpacing commercial capacity by a wide margin.

Nonetheless, commercial and industrial scale installations in New York account for over 100 MW of power capacity in the state.

Large-Scale Solar Installations Map

This map shows the location of those large-scale solar installations in the US (zoom out to see full extent of US), as of March 2016. Here is our interactive map:

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In the past fifteen years, the increase in small to medium-sized solar installations in New York State has been significant, and growth is projected to continue.  The following animation, based on data from the New York State Energy Research and Development Authority (NYSERDA), shows that increase in capacity (by zip code) since 2000:

solar_animation_cumulative_2000-15

Solar Installations by Zip Code

NYSERDA also provides maps that show distributions of residential, governmental/NGO, and commercial solar energy projects (images shown below). For example, Suffolk County leads the way in the residential arena, with nearly 8200 photovoltaic (PV) systems on roofs and in yards, with an average size of 8.3 kW each.

Erie County has 128 PV systems run by governmental and not-for-profit groups, with an average size of about 27 kW each. Albany County has over 320 commercial installations, with an average size each of about 117 kW.

New York State’s Future Solar Contribution

pricing

Price of Completed Solar Systems 2003-2016

The prices of solar panels is steeply declining, and is coupled with generous tax incentives. The good news, according to the Solar Energy Industries Association (SEIA), is that over the next five years, New York State’s solar capacity is expected to quadruple its current output, adding over 2900 MW of power. This change would elevate New York State from seventh to fourth place in output in the US.


By Karen Edelstein, Eastern Program Coordinator, FracTracker Alliance

Bill Hughes giving tour to students in shale fields, WV

A Cross-Country Ride to Support Oil and Gas Tours in West Virginia

Bill Hughes giving tours of gas fields in West Virginia. Photo by Joe Solomon. https://flic.kr/s/aHskkXZj3z

Bill Hughes giving a tour of gas fields in West Virginia. Photo by Joe Solomon.

As many of you know, educating the public is a FracTracker Alliance core value – a passion, in fact. In addition to our maps and resources, we help to provide hands-on education, as well. The extraordinary Bill Hughes is a FracTracker partner who has spent decades “in the trenches” in West Virginia documenting fracking, well pad construction, water withdrawals, pipeline construction, accidents, spills, leaks, and various practices of the oil and gas industry. He regularly leads tours for college students, reporters, and other interested parties, showing them first-hand what these sites look, smell, and sound like.

While most of us have heard of fracking, few of us have seen it in action or how it has changed communities. The tours that Bill provides allow students and the like to experience in person what this kind of extraction means for the environment and for the residents who live near it.

Biking to Support FracTracker and Bill Hughes

Dave Weyant at the start of his cross-country bike trip in support of WV tours

Dave Weyant at the start of his cross-country Pedal for the Planet bike trip

In the classic spirit of non-profit organizations, we work in partnership with others whenever possible. Right now, as you read this posting, another extraordinary Friend of FracTracker, Dave Weyant (a high school teacher in San Mateo, CA), is finishing his cross-country cycling tour – from Virginia to Oregon in 70 days.

Dave believes strongly in the power of teaching to reach the hearts of students and shape their thinking about complicated issues. As such, he has dedicated his journey to raising money for FracTracker. He set up a GoFundMe campaign in conjunction with his epic adventure, and he will donate whatever he raises toward Bill’s educational tours.

Help us celebrate Dave Weyant’s courage, vision, and generosity – and support Bill Hughes’s tireless efforts to open eyes, evoke awareness, and foster communication about fracking – by visiting Dave’s GoFundMe page and making a donation. Every gift of any size is most welcome and deeply appreciated.

100% of the funds raised from this campaign will go to support Bill’s oil and gas tours in West Virginia. FracTracker Alliance is a registered 501(c)3 organization. Your contribution is tax deductible.

And to those of you who have already donated, thank you very much for your support!

South Belridge field by Sarah Leen, National Geographic

Trends in California’s Oil and Gas Development

By Kyle Ferrar, Western Program Coordinator

Over 38,000 oil and gas wells have likely been hydraulically fractured in California. The last permitted hydraulic fracturing operation in CA was approved in June 2015. Additionally, new aquifer exemption proposals will make it easier for operators to obtain hydraulic fracturing permits. One of the most interesting and troubling issues we found when analyzing the data on violations is that operators with the highest number of new well permits are also responsible for the majority of violations. In this article, we provide a look at these and other the trends of unconventional drilling in CA.

Updated CA Shale Viewer

First of all, the CA Shale Viewer has been updated! New data has been uploaded into the map about unconventional drilling in California, and new data resources have been used to identify shale gas activity (Fig. 1). Recent reports in CA have exposed what many researchers expected – hydraulic fracturing has been occurring in the state without any oversight or documentation for a long time.

In this presentation of the Updated CA Shale Viewer we showcase an analysis of these new data sources that better describe unconventional drilling in CA. We then look to new well permitting data to see what current spatial trends may mean for future oil and gas development. We also look at a sample of operator violations issued by the state regulatory agency to tell us a bit about who the bad actors may be.

Figure 1. CA Shale Viewer – Location of well stimulation & other unconventional oil & gas activity


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Current Fracking Activity

Fracking in California has been put on hold at the moment as a result of low oil prices combined with the new permitting requirements for groundwater monitoring. In 2015, the CA Council on Science and Technology (CCST) released a report on hydraulic fracturing, as required by State Bill 4, proposed by Senator Pavley. The legislation required the Division of Oil, Gas and Geothermal Resources to create regulations for hydraulic fracturing and other stimulation activities such as acidizing. The report highlighted the necessity of protecting California’s groundwater resources. As another requirement of SB4, the state water resources control board adopted Model Criteria for Groundwater Monitoring in areas of Oil and Gas Well Stimulation, which includes three main components:

  1. Area-specific required groundwater monitoring near stimulation wells by operators
  2. Requirements for designated contractor sampling and testing
  3. Regional scale groundwater monitoring to be implemented by the State Water Board

With these requirements in place to protect groundwater, using hydraulic fracturing and other “extreme” high energy input techniques to extract oil is not currently economical in California. Operators have not submitted a permit application for hydraulic fracturing in CA since June 2015.

This status may change in the near future, though, as DOGGR has proposed groundwater monitoring exemptions for 3 large aquifer systems in Kern and Arroyo Grande counties. Such a proposal would mean that operators would not have to monitor for groundwater contamination in these areas when using hydraulic fracturing or other stimulation technologies like acidizing.

Previous Fracking Activity

One outcome of the aforementioned CCST report on hydraulic fracturing was a review of stimulation activity that has occurred in CA but went undocumented. Researchers at Lawrence Berkeley National Laboratory (LBNL) screened thousands of oil and gas well logs and records to calculate the extent to which hydraulic fracturing was actually being used in California’s oil fields. LBNL derived “Well Stimulation Treatment” probabilities based on the number of well records that reported utilizing hydraulic fracturing.

Probabilities were then derived for each pool, which is a geographically isolated formation within an oil field. Using these probabilities, FracTracker calculated a conservative estimate for the number of stimulated wells in the state at over 38,000. There are 228,010 unique Well ID’s listed in the DOGGR database. This puts the proportion of hydraulically fractured wells in California at 16.7% of the total 228,090 wells known.

New Wells

Whereas many other states break down their oil and gas data to show in what phase of development a well may be, CA identifies all wells between the permitted and producing/injecting phase as “new.” In Figure 2 below you can see the wells identified in 2016 as “new.” The DOGGR dataset shows there are currently 6,561 new wells in California as of July 2016. Counts of new well permits were calculated for individual operators and are listed below in Table 1.

Table 1. Top 10 operators according to new well permit counts in California, along with the number of new well permits currently active, the percent those permits represent of total new well permits in the state, and the percentage of violations the operator is responsible in the DOGGR dataset provided to FracTracker Alliance.

Order Operator Permit Count Permit % Violations %
1 Aera Energy LLC 2012 30.67% 22.34%
2 Chevron U.S.A. Inc. 968 14.75% 20.35%
3 California Resources Production Corporation 768 11.70% 5.89%
4 Linn Operating, Inc. 574 8.75% 12.04%
5 E & B Natural Resources Management Corporation 572 8.71% 1%
6 California Resources Elk Hills, LLC 374 5.70% 5.52%
7 Seneca Resources Corporation 185 2.82% 2.83%
8 Freeport-McMoRan Oil & Gas LLC 164 2.50% 15.22%
9 Vaquero Energy, Inc. 154 2.35% 0.22%
10 Macpherson Oil Company 116 1.77% 2.09%

There are 68 fields in CA that have added new wells in the new DOGGR dataset published in July 2016. The top 10 fields are listed in Table 2 below.

Table 2. Top 10 Oil Fields by Permit (New Well) Count

Order Oil Field Well Count
1 Belridge, South 1518
2 Midway-Sunset 903
3 Poso Creek 553
4 Lost Hills 488
5 Cymric 336
6 Kern River 294
7 Elk Hills 276
8 Kern Front 233
9 McKittrick 186
10 Belridge, North 174

In Figure 2 below, the counts of new wells in fields are shown in shades of yellow/red. The fields with the highest number of new wells are located in the Central Valley. The top 10 operators’ wells are also identified. The majority of new well permits are located in the South Belridge oil field, and the majority of those wells are operated by Aera Energy. As can be seen in the map, most new wells are located in fields in Kern county, but Santa Barbara and Fresno, and even Salinas counties have fields with 40 or more new well permits.

Figure 2. New Well Permitting Map of Unconventional Drilling in California


View map fullscreen | How FracTracker maps work

Violations

Who collects violations data?

In most states with heavy oil and gas drilling, data on violations is collected by the state regulatory agency, aggregated in datasets and spreadsheets, and made available to the public. FracTracker has done analyses with such data in the past.

In Pennsylvania for instance, a 2011 look at the data showed us that as the number of inspectors on the ground in the Marcellus Shale fields increases, the number of violations/well actually decrease. This was important information that challenged the cynical hypothesis: that more inspectors mean additional eyes on the ground to identify more violations during inspections. In reality, more inspectors actually mean that operators are held to higher standards, and further best management practices (BMPs) are employed. This trend at least seemed to be the case in Pennsylvania. As a regulatory agency, such knowledge is incredibly important, and even validates increased spending and budgets for more personnel.

In California, the issue of publishing violations data is again met with a similar response from the Division of Oil Gas and Geothermal Resources (DOGGR), specifically the “Oh, is that my job?” question.

How is it shared?

At FracTracker, we spent time working with regulatory officials at DOGGR to get some data on violations. We were informed that at some point in the future, the data may be aggregated and available digitally. Until then, however, a request for the data would have to be made to each of the six district offices individually and would take approximately a year to pull together scanned copies of violations notices in PDF format. Unfortunately, we at FracTracker do not have the capacity to process such files. Instead we asked for anything DOGGR had digitally available, and we were provided with a sample subset of 2,825 violations dating mostly from 2013 and 2014 and only in District 2, the Los Angeles Basin.

What does CA violations data look like?

Looking at the sample of data in Table 2, we see that the majority of violations are caused by the operators that also have the most new well permits. Aera Energy, in particular, is responsible for over 1/5 of all violations in our sample set. Limiting factors and sampling bias of the sample set of violations may impact this analysis, though, as all violations are limited to Los Angeles County.  Operators that mostly operate in the Central Valley will be under represented in the violations count. When more violations data becomes available we will be sure to expand this analysis.

Bans and Regulations on Unconventional Drilling in California

Although every state regulatory agency lambasts that they have the most comprehensive and conservative set of oil and gas extraction regulations, California regulators may actually be right. That is, save for New York which has banned hydraulic fracturing outright.

Regardless of the policy decisions made at the state-level, multiple local municipalities in CA have attempted to or succeeded in passing local bans. Six counties have passed outright bans on unconventional drilling in California, as can be seen in the FracTracker Local Actions map below (Fig. 3). Most recently the county of Alameda, home to the cities of Berkeley and Oakland, has passed a ban. The county of Monterey is also considering a ban on all oil and gas extraction, which has been approved as a local ballot initiative for November 2016.

Figure 3. Local Actions, Bans and Regulations Map


View map fullscreen | How FracTracker maps work

As the price of oil rebounds closer to $100/barrel, there will be more interest by operators to increase unconventional drilling in California. The addition of new aquifer exemptions will make it all the more appealing. These local movements are therefore incredibly important to ensure that “extreme” extraction methods like fracking don’t expand in the future.

Feature Photo: South Belridge field by Sarah Leen, National Geographic

Air emissions from drilling rig

A Review of Oil and Gas Emissions Data in Pennsylvania

By Wendy Fan, 2016 Intern, FracTracker Alliance

From 2011-2013, the PA Department of Environmental Protection (DEP) required air emission data to be conducted and reported by oil and gas drillers in Pennsylvania. We have tried to look at this data in aggregate to give you a sense of the types and quantities of different pollutants. Corresponding to their degree of oil and gas drilling activity, Washington, Susquehanna, Bradford, Greene, and Lycoming counties are the highest emitters of overall pollutants between the specified years. Despite the department’s attempt to increase transparency, the data submitted by the operators severely underestimates the actual amount of pollutants released, especially with regard to methane emissions. Furthermore, gaps such as inconsistent monitoring systems, missing data, and a lack of a verification process of the self-reported data weaken the integrity and reliability of the submitted data. This article explores the data submitted and its implications in further detail.

Why Emissions Are Reported

The U.S. Energy Information Administration (EIA) estimates that U.S. natural gas production will increase from 23 trillion cubic feet in 2011 to over 33 trillion cubic feet in 2040. Pennsylvania, in particular, is one of the states with the highest amount of drilling activity at present. This statistic can be attributed to resource-rich geologic formations such as the Marcellus Shale, which extends throughout much of Appalachia. While New York has banned drilling using high-volume hydraulic fracturing (fracking), Pennsylvania continues to expand its operations with 9,775 active unconventional wells as of June 10, 2016.

Between 2000-2016, drillers in Pennsylvania incurred 5,773 violations and $47.2 million in fines. The PA DEP, which oversees drilling permits and citations, has undergone criticism for their lack of action with complaints related to oil and gas drilling, as well as poor communication to the public*. In order to increase transparency and to monitor air emissions from wells, the DEP now requires unconventional natural gas operators to submit air emission data each year. The data submitted by operators are intended to be publicly accessible and downloadable by county, emission, or well operator.

* Interestingly, PA scored the highest when we rated states on a variety of data transparency metrics in a study published in 2015.

Importance of Data Collected

PA’s continual growth in oil and gas drilling activity is concerning for the environment and public health. Pollutants such as methane, carbon dioxide (CO2), and nitrous oxides (NOx) are all major contributors to climate change, and these are among the more common emissions found near oil and gas activities. Long-term exposure to benzene, also commonly associated with drilling sites, can result in harmful effects on the bone marrow and the decrease in red blood cells. Vomiting, convulsions, dizziness, and even death can occur within minutes to several hours with high levels of benzene.

With such risks, it is crucial for residents to understand how many wells are within their vicinity, and the levels of these pollutants emitted.

Air Monitoring Data Findings & Gaps

Although the DEP collects emission data on other important pollutants such as sulfur oxides (SOx), particulate matter (PM10 and PM2.5), and toluene, this article focuses only on a few select pollutants that have shown the highest emission levels from natural gas activity. The following graphs illustrate emissions of methane, carbon dioxide (CO2), carbon monoxide (CO), nitrogen oxides (NOx), benzene, and volatile organic compounds (VOCs) for the top 10 counties with the highest amounts of natural gas activity. PA wells drilled data (often called SPUD data) will also be referenced throughout the article. Data source: PA SPUD Data.

CMC

PA DEP’s Calculation Methods Codes for Emissions

Well operators self-report an estimate of total emissions in tons per year through either an online or paper reporting system. They must also indicate the method they used to generate this estimate with the Calculation Methods Codes for Emissions (table shown right).

For more information on how the data is prepared and what are the reporting requirements, refer to PA DEP’s Instruction for Completing the Annual Emissions Statement Reporting Forms

Total Amount of Unconventional Wells 2000-2016

AmountofWells

Figure 1

Overall, Washington, Susquehanna, Bradford, Greene, and Lycoming counties were the main emitters of all selected pollutants (methane, CO2, CO, NOx, VOCs, and benzene) throughout Pennsylvania based on tons per year (Fig 1). This trend may be correlated to the amount of natural gas activity that exists within each state as shown in the graph above. The top three Pennsylvania counties with the highest amount of oil and gas activity since 2000 are Washington, Susquehanna, and Bradford with 1,347; 1,187; and 1,091 unconventional active wells, respectively.

Methane Emissions

PA_Methane

Figure 2

In 2012, Susquehanna, Bradford, and Lycoming counties reported the highest amount of methane released with levels at 36,607, 23,350, and 14,648 tons, respectively (Fig 2). In 2013, Bradford, Lycoming, and Greene counties reported the highest amount of methane released with levels at 17,805, 17,265, and 15,296 tons, respectively.

Although the overall trend of methane emission declines from 2012 to 2013, there is an unusual drop in Susquehanna County’s methane emissions from 2012 to 2013. Susquehanna’s levels went from 36,607 tons to 12,269 tons in that timeframe. However, the DEP SPUD data recorded an increase of 190 active wells to 214 active wells from 2012 to 2013 in that same county. Though the well operators did not provide details for this shift, possible reasons may be because of improved methods of preventing methane leaks over the year, well equipment may be less robust as it once was, operators may have had less of a reason to monitor for leaky wells, or operators themselves could have changed.

Lackawanna and Luzerne counties reported zero tons of methane released during the year of 2012 (not shown on graph). There are two possible reasons for this: both counties did not have any unconventional wells recorded in the 2012 SPUD data, which may explain why the two counties reported zero tons for methane emissions, or the levels submitted are a significant underestimation of the actual methane level in the counties. (While there were no new wells, there are existing wells in production in those counties.)

Considering that methane is the primary component of natural gas activity, the non-existent level of methane reported seem highly implausible even with inactive wells on site. Typically, an old or inactive gas well can either be abandoned, orphaned, or plugged. By definition, abandoned wells have been inactive for more than a year, and orphaned wells were abandoned prior to 1985. (Because of this distinction, however, no unconventional wells can be considered “orphaned.”) To plug a well, cement plugs are used to cover up wellbores in order to cease all flow of gas. The act of physically plugging up the wells paints an illusion that it is no longer functioning and has ceased all emissions.

Because of this flawed impression, systematic monitoring of air emissions is often not conducted and the wells are often ignored. Several studies have shown even abandoned and plugged wells are still spewing out small and at times large quantities of methane and CO2. One study published in 2014 in particular measured 19 abandoned wells throughout Pennsylvania, and concluded that abandoned wells were significant contributors to methane emissions – contributing 4-7% of total anthropogenic (man-made) methane emissions in PA.

View methane emissions map full screen: 2012-2013

Carbon Dioxide Emissions

PA_CO2

Figure 3

In 2012, Bradford County reported 682,302 tons of CO2 emitted; Washington County reported 680,979 tons; and Susquehanna reported 560,881 tons (Fig. 3). In 2013, Washington continued to lead with 730,674 tons, Bradford at 721,274 tons, and Lycoming with 537,585 tons of COemitted.

What’s intriguing is according to SPUD data, Armstrong, Westmoreland, and Fayette also had considerable natural gas activity between the two years as shown on the map. Yet, their levels of CO2 emission are significantly lower compared to Lycoming or Susquehanna Counties. Greene County, in particular, had lower levels of CO2 reported. Yet, they had 106 active wells in 2012 and 117 in 2013. What is even more unusual is that Bradford County had 9 more wells than Greene County in 2013, yet, Greene County still had significantly higher CO2 levels reported.

Reasons for this difference may be that Greene County lacked the staff or resources to accurately monitor for CO2, the county may have forgotten to record emissions from compressor stations or other fugitive emission sources, or the method of monitoring may have differed between counties. Whatever the reason is, it is evident that the levels reported by Greene County may not actually be an accurate depiction of the true level of COemitted.

View CO2 emissions map full screen: 2012-2013

Carbon Monoxide Emissions

Spudded wells in PA with reported CO emissions by county 2011-13

Spudded wells in PA with reported CO emissions by county 2011-13

PA_CO

Figure 4

According to the PA SPUD data, the number of new wells drilled in Bradford County dropped from 389 in 2011 to 163 in 2012 to 108 to 2013. The diminishing number of newly drilled wells in this particular county may explain the noticeable outlier in CO emission as seen on the graph (Fig 4).

View CO emissions map full screen: 2011-2013

NOx and VOCs

Compressor stations are also known to emit VOC, NOx, and various greenhouse gases; they run 24/7 and serve multiple wells. Compressor stations are necessary to move the natural gas along the pipelines, and thus, may still be required to function even after some wells have ceased operation. Furthermore, there can be multiple compressor stations in a region because they are installed at intervals of about 40 to 100 miles. This suggests that in addition to drilled wells, compressor stations provide additional avenues for NOx or VOC to leak into the air.

View NOx and VOC emissions maps full screen: VOC 2011-2013 | NOx 2011-2013

Benzene Emissions

Spudded wells in PA with reported benzene emissions by county 2011-13

Spudded wells in PA with reported benzene emissions by county 2011-13

Chart of PA benzene emissions data county to county

Figure 7

The levels of benzene emitted varied the most when compared to the other pollutants presented previously. Generally, the high levels of methane, CO2, and NOx emitted correlate with the high amount of natural gas activity recorded for each county’s number of drilled unconventional wells. However, it is interesting that both Westmoreland and Fayette counties had fewer active wells than Bradford County, yet, still reported higher levels of benzene (Fig 1, Fig 7).

An explanation for this may be the different monitoring techniques, the equipment used on each site which may vary by contractor or well access, or that there are other external sources of benzene captured in the monitoring process.

View benzene emissions map full screen: 2011-2013

Questions Remain

Although the collection and monitoring of air emission from wells is a step in the right direction, the data itself reveals several gaps that render the information questionable.

  • The DEP did not require operators to report methane, carbon dioxide, and nitrous oxide in 2011. Considering that all three components are potent greenhouse gases and that methane is the primary component in natural gas production, the data could have been more reliable and robust if the amount of the highest pollutants were provided from the start.
  • Systematic air monitoring around abandoned, orphaned, and plugged wells should still be conducted and data reported because of their significant impact to air quality. The DEP estimates there are approximately 200,000 wells that have been abandoned and unaccounted for. This figure includes older, abandoned wells that had outdated methods of plugging, such as wood plugs, wood well casings, or no plug at all. Without a consistent monitoring system for fugitive air emissions, the public’s true risk of the exposure to air pollutants will remain ambiguous.
  • All emissions submitted to the DEP are self-reported data from the operators. The DEP lacks a proper verification process to confirm whether the submitted data from operators are accurate.
  • The finalized data for 2014 has yet to be released despite the DEP’s April 2016 deadline. The DEP inadvertently posted the reports in March 2016, but quickly removed them without any notification or explanation as to why this information was removed. When we inquired about the release date, a DEP representative stated the data should be uploaded within the next couple of weeks. We will provide updates to this post when that data is posted but the DEP.

Overall, PA DEP’s valiant attempt to collect air data from operators and to increase transparency is constrained by the inconsistency and inaccuracy of the dataset. The gaps in the data strongly suggest that the department’s collection process and/or the industry’s reporting protocol still require major improvements in order to better monitor and communicate this information to the public.