As a spring 2020 intern with FracTracker, my work mostly involved mapping gathering lines in West Virginia and Ohio. Gathering lines are pipelines that transport oil and gas from the wellhead to either compressor stations or storage/processing facilities. The transmission pipelines (which are often larger in diameter than gathering lines) take the oil and gas from the processing facilities to other storage facilities/compressor stations, or to distribution pipelines which go to end users and consumers. As you can see from Figure 2 in the map of Doddridge County, WV, many gathering lines eventually converge at a compressor station. You can think of gathering lines like small brooks and streams that feed transmission pipelines. The transmission lines are the main arteries, like a river, moving larger quantities of gas and oil over longer distances.
PROJECT DESCRIPTION
The main project and goal of my internship was to record as many gathering pipelines as I could find in Ohio and West Virginia, since gathering lines are not generally mapped and therefore not easily available for the public to view. For example, the National Pipeline Mapping System’s public map viewer (created by the Department of Transportation Pipeline and Hazardous Materials Safety Administration) has a note stating, “It does not contain gas gathering or distribution pipelines.” Mapping gathering lines makes this data accessible to the public and will allow us to see the bigger picture when it comes to assessing the environmental impact of pipelines.
After collecting gathering line location data, I performed GIS analysis to determine the amount of acreage of land that has been clearcut due to gathering pipeline installations.
Another analysis we could perform using this data is to count the total number of waterways that the gathering lines cross/interact with and assess the quality of water and wildlife in areas with higher concentrations of gathering pipelines.
Figure 1. This map shows an overview of gathering line pipelines in the Powhatan Point, Ohio and Moundsville, West Virginia of the Ohio River Valley.
PIPELINE GATHERING LINE MAPPING PROCESS
I worked with an aerial imagery BaseMap layer (a BaseMap is the bottommost layer when viewing a map), a county boundaries layer, production well location points, and compressor station location points. I then traced lines on the earth that appeared to be gathering lines by creating polygon shapefiles in the GIS application ArcMap.
My methodology and process of finding the actual routes of the gathering lines included examining locations at various map scale ranges to find emerging line patterns of barren land that connect different production well points on the map. I would either concentrate on looking for patterns along well pad location points and look for paths that may connect those points, or I would begin at the nearest gathering line I had recorded to try to find off-shoot paths off of those pipelines that may connect to a well pad, compressor station or previously recorded gathering line.
I did run into a few problems during my search for gathering lines. Sometimes, I would begin to trace a gathering line path, only to either loose the path entirely, or on further inspection, find that it was a power line path. Other times when using the aerial imagery basemap, the gathering line would flow into an aerial photo from a year prior to the pipeline installation and I would again lose the path. To work around these issues, I would first follow the gathering line trail to its end point before I started tracing the path. I would also view the path very closely in various scale ranges to ensure I wasn’t tracing a road, waterway, or powerline pathway.
ACREAGE ANALYSIS
In the three months that I was working on recording gathering pipeline paths in Ohio and West Virginia, I found approximately 29,103 acres (3,494 miles) of barren land clearcut by gathering pipelines. These total amounts are not exact since not all gathering lines can be confirmed. There are still more gathering lines to be recorded in both Ohio and West Virginia, but these figures give the reader an idea of the land disturbance caused by gathering lines, as shown in Figures 1 and 2.
In Ohio, I recorded approximately 10,083 acres (641 miles) with the average individual gathering pipeline taking up about 45 acres of land. With my gathering line data and data previously recorded by FracTracker, I found that there are 28,490 acres (1,690 miles) of land spanning 9 counties in southeastern Ohio that have been cleared and used by gathering lines.
For West Virginia, I was able to record approximately 19,020 acres (1,547 miles) of gathering lines, with the average gathering line taking up about 48 acres of space each. With previous data recorded in West Virginia by FracTracker, the total we have so far for the state is 22,897 acres (1,804 miles), although that is only accounting for the 9 counties in northern West Virginia that are recorded.
Figure 2. This aerial view map shows connecting gathering line pipelines that cover a small portion of Doddridge County, WV.
CONCLUSION
I was shocked to see how many gathering lines there are in these rural areas. Not only are they very prevalent in these less populated communities, but it was surprising to see how concentrated and close together they tend to be. When most people think of pipelines, they think of the big transmission pipeline paths that cross multiple states and are unaware of how much land that the infrastructure of these gathering pipelines also take up.
It was also very eye-opening to find that there are at least 29,000 acres of land in Ohio and West Virginia that were clearcut for the installation of gathering lines. It is even more shocking that these gathering pipelines are not being recorded or mapped and that this data is not publicly available from the National Pipeline Mapping System. While driving through these areas you may only see one or two pipelines briefly from your car, but by viewing the land from a bird’s eye perspective, you get a sense of the scale of this massive network. While the transmission pipeline arteries tend to be bigger, the veins of gathering lines displace a large amount of land as well.
I was also surprised by the sheer number of gathering lines I found that crossed waterways, rivers, and streams. During this project, it wasn’t unusual at all to follow a gathering line path that would cross water multiple times. In the future, I would be interested to look at the number of times these gathering pipelines cross paths with a stream or river, and the impact that this has on water quality and surrounding environment. I hope to continue to record gathering lines in Ohio and West Virginia, as well as Pennsylvania, so that we may learn more about this infrastructure and the impact it may have on the environment.
About Me
I first heard of FracTracker three years ago when I was volunteering with an environmental group called Keep Wayne Wild in Ohio. Since learning about FracTracker, I have been impressed with their eye-opening projects and their ability to make the gas and oil industry more transparent. A few years after first hearing about FracTracker, and as my interest in the GIS field continued to grow, I began taking GIS classes and reached out to them for this internship opportunity.
By Trevor Oatts, FracTracker Spring 2020 Data & GIS Intern
https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2020/07/Mapping-gathering-lines-in-OH-and-WV-feature.jpg8331875Intern FracTrackerhttps://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/2021-FracTracker-logo-horizontal.pngIntern FracTracker2020-07-02 12:09:192021-04-15 14:16:43Mapping Gathering Lines in Ohio and West Virginia
Challenges have plagued Shell’s construction of the Falcon Pipeline System through Pennsylvania, Ohio, and West Virginia, according to documents from the Pennsylvania Department of Environmental Protection (DEP) and the Ohio Environmental Protection Agency (EPA).
Records show that at least 70 spills have occurred since construction began in early 2019, releasing over a quarter million gallons of drilling fluid. Yet the true number and volume of spills is uncertain due to inaccuracies in reporting by Shell and discrepancies in regulation by state agencies.
A drilling fluid spill from Falcon Pipeline construction near Moffett Mill Road in Beaver County, PA. Source: Pennsylvania DEP
Releases of drilling fluid during Falcon’s construction include inadvertent returns and losses of circulation – two technical words used to describe spills of drilling fluid that occur during pipeline construction.
Drilling fluid, which consists of water, bentonite clay, and chemical additives, is used when workers drill a borehole horizontally underground to pull a pipeline underneath a water body, road, or other sensitive location. This type of installation is called a HDD (horizontal directional drill), and is pictured in Figure 1.
Figure 1. An HDD operation – Thousands of gallons of drilling fluid are used in this process, creating the potential for spills. Click to expand. Source: Enbridge Pipeline
Here’s a breakdown of what these types of spills are and how often they’ve occurred during Falcon pipeline construction, as of March, 2020:
Loss of circulation
Definition: A loss of circulation occurs when there is a decrease in the volume of drilling fluid returning to the entry or exit point of a borehole. A loss can occur when drilling fluid is blocked and therefore prevented from leaving a borehole, or when fluid is lost underground.
Cause: Losses of circulation occur frequently during HDD construction and can be caused by misdirected drilling, underground voids, equipment blockages or failures, overburdened soils, and weathered bedrock.
Construction of the Falcon has caused at least 49 losses of circulation releasing at least 245,530 gallons of drilling fluid. Incidents include:
15 losses in Ohio – totaling 73,414 gallons
34 losses in Pennsylvania – totaling 172,116 gallons
Inadvertent return
Definition: An inadvertent return occurs when drilling fluid used in pipeline installation is accidentally released and migrates to Earth’s surface. Oftentimes, a loss of circulation becomes an inadvertent return when underground formations create pathways for fluid to surface. Additionally, Shell’s records indicate that if a loss of circulation is large enough, (releasing over 50% percent of drilling fluids over 24-hours, 25% of fluids over 48-hours, or a daily max not to exceed 50,000 gallons) it qualifies as an inadvertent return even if fluid doesn’t surface.
Cause: Inadvertent returns are also frequent during HDD construction and are caused by many of the same factors as losses of circulation.
Construction of the Falcon has caused at least 20 inadvertent returns, releasing at least 5,581 gallons of drilling fluid. These incidents include:
18 inadvertent returns in Pennsylvania – totaling 5,546 gallons
2,639 gallons into water resources (streams and wetlands)
2 inadvertent returns Ohio – totaling 35 gallons
35 gallons into water resources (streams and wetlands)
However, according to the Ohio EPA, Shell is not required to submit reports for losses of circulation that are less than the definition of an inadvertent return, so many losses may not be captured in the list above. Additionally, documents reveal inconsistent volumes of drilling mud reported and discrepancies in the way releases are regulated by the Pennsylvania DEP and the Ohio EPA.
Very few of these incidents were published online for the public to see; FracTracker obtained information on them through a public records request. The map below shows the location of all known drilling fluid releases from that request, along with features relevant to the pipeline’s construction. Click here to view full screen, and add features to the map by checking the box next to them in the legend. For definitions and additional details, click on the information icon.
Our investigation into these incidents began early this year when we received an anonymous tip about a release of drilling fluids in the range of millions of gallons at the SCIO-06 HDD over Wolf Run Road in Jefferson County, Ohio. The source stated that the release could be contaminating drinking water for residents and livestock.
Working with Clean Air Council, Fair Shake Environmental Legal Services, and DeSmog Blog, we quickly discovered that this spill was just the beginning of the Falcon’s construction issues.
Documents from the Ohio EPA confirm that there were at least eight losses of circulation at this location between August 2019 and January 2020, including losses of unknown volume. The SCIO-06 HDD location is of particular concern because it crosses beneath two streams (Wolf Run and a stream connected to Wolf Run) and a wetland, is near groundwater wells, and runs over an inactive coal mine (Figure 2).
Figure 2. Losses of circulation that occurred at the SCIO-06 horizontal directional drill (HDD) site along the Falcon Pipeline in Jefferson County Ohio. Data Sources: OH EPA, AECOM
According to Shell’s survey, the coal mine (shown in Figure 2 in blue) is 290 feet below the HDD crossing. A hazardous scenario could arise if an HDD site interacts with mine voids, releasing drilling fluid into the void and creating a new mine void discharge.
A similar situation occurred in 2018, when EQT Corp. was fined $294,000 after the pipeline it was installing under a road in Forward Township, Pennsylvania hit an old mine, releasing four million gallons of mine drainage into the Monongahela River.
The Ohio EPA’s Division of Drinking and Ground Waters looked into the issues around this site and reported, “GIS analysis of the pipeline location in Jefferson Co. does not appear to risk any vulnerable ground water resources in the area, except local private water supply wells. However, the incident location is above a known abandoned (pre-1977) coal mine complex, mapped by ODNR.”
While we cannot confirm if there was a spill in the range of millions of gallons as the source claimed, the reported losses of circulation at the SCIO-06 site total over 60,000 gallons of drilling fluid. Additionally, on December 10th, 2019, the Ohio EPA asked AECOM (the engineering company contracted by Shell for this project) to estimate what the total fluid loss would be if workers were to continue drilling to complete the SCIO-06 crossing. AECOM reported that, in a “very conservative scenario based on the current level of fluid loss…Overall mud loss to the formation could exceed 3,000,000 gallons.”
Despite this possibility of a 3 million+ gallon spill, Shell resumed construction in January, 2020. The company experienced another loss of circulation of 4,583 gallons, reportedly caused by a change in formation. However, in correspondence with a resident, Shell stated that the volume lost was 3,200 gallons.
Whatever the amount, this January loss of circulation appears to have convinced Shell that an HDD crossing at this location was too difficult to complete, and in February 2020, Shell decided to change the type of crossing at the SCIO-06 site to a guided bore underneath Wolf Run Rd and open cut trench through the stream crossings (Figure 3).
Figure 3. The SCIO-06 HDD site, which may be changed from an HDD crossing to an open cut trench and conventional bore to cross Wolf Run Rd, Wolf Run stream (darker blue), an intermittent stream (light blue) and a wetland (teal). Click to expand.
An investigation by DeSmog Blog revealed that Shell applied for the route change under Nationwide Permit 12, a permit required for water crossings. While the Army Corps of Engineers authorized the route change on March 17th, one month later, a Montana federal court overseeing a case on the Keystone XL pipeline determined that the Nationwide Permit 12 did not meet standards set by federal environmental laws – a decision which may nullify the Falcon’s permit status. At this time, the ramifications of this decision on the Falcon remain unclear.
Inconsistencies in Reporting
In looking through Shell’s loss of circulation reports, we noted several discrepancies about the volume of drilling fluid released for different spills, including those that occurred at the SCIO-06 site. As one example, the Ohio EPA stated an email about the SCIO-06 HDD, “The reported loss of fluid from August 1, 2019 to August 14, 2019 in the memo does not appear to agree with the 21,950 gallons of fluid loss reported to me during my site visit on August 14, 2019 or the fluid loss reported in the conference call on August 13, 2019.”
In addition to errors on Shell’s end, our review of documents revealed significant confusion around the regulation of drilling fluid spills. In an email from September 26, 2019, months after construction began, Shell raised the following questions with the Ohio EPA:
when a loss of circulation becomes an inadvertent return – the Ohio EPA clarifies: “For purposes of HDD activities in Ohio, an inadvertent return is defined as the unintended return of any fluid to the surface, as well as losses of fluids to underground formations which exceed 50-percent over a 24-hour period and/or 25-percent loss of fluids or annular pressure sustained over a 48-hour period;”
when the clock starts for the aforementioned time periods – the Ohio EPA says the time starts when “the drill commences drilling;”
whether Shell needs to submit loss of circulation reports for losses that are less than the aforementioned definition of an inadvertent return – the Ohio EPA responds, “No. This is not required in the permit.”
How are these spills measured?
A possible explanation for why Shell reported inconsistent volumes of spills is because they were not using the proper technology to measure them.
Shell’s “Inadvertent Returns from HDD: Assessment, Preparedness, Prevention and Response Plan” states that drilling rigs must be equipped with “instruments which can measure and record in real time, the following information: borehole annular pressure during the pilot hole operation; drilling fluid discharge rate; the spatial position of the drilling bit or reamer bit; and the drill string axial and torsional loads.”
In other words, Shell should be using monitoring equipment to measure and report volumes of drilling fluid released.
Despite that requirement, Shell was initially monitoring releases manually by measuring the remaining fluid levels in tanks. After inspectors with the Pennsylvania DEP realized this in October, 2019, the Department issued a Notice of Violation to Shell, asking the company to immediately cease all Pennsylvania HDD operations and implement recording instruments. The violation also cited Shell for not filing weekly inadvertent return reports and not reporting where recovered drilling fluids were disposed.
In Ohio, there is no record of a similar request from the Ohio EPA. The anonymous source that originally informed us of issues at the SCIO-6 HDD stated that local officials and regulatory agencies in Ohio were likely not informed of the full volumes of the industrial waste releases based on actual meter readings, but rather estimates that minimize the perceived impact.
While we cannot confirm this claim, we know a few things for sure: 1) there are conflicting reports about the volume of drilling fluids spilled in Ohio, 2) according to Shell’s engineers, there is the potential for a 3 million+ gallon spill at the SCIO-06 site, and 3) there are instances of Shell not following its permits with regard to measuring and reporting fluid losses.
The inconsistent ways that fluid losses (particularly those that occur underground) are defined, reported, and measured leave too many opportunities for Shell to impact sensitive ecosystems and drinking water sources without being held accountable.
What are the impacts of drilling fluid spills?
Drilling fluid is primarily composed of water and bentonite clay (sodium montmorillonite), which is nontoxic. If a fluid loss occurs, workers often use additives to try and create a seal to prevent drilling fluid from escaping into underground voids. According to Shell’s “Inadvertent Returns From HDD” plan, it only uses additives that meet food standards, are not petroleum based, and are consistent with materials used in drinking water operations.
However, large inadvertent returns into waterways cause heavy sedimentation and can have harmful effects on aquatic life. They can also ruin drinking water sources. Inadvertent returns caused by HDD construction along the Mariner East 2 pipeline have contaminated many water wells.
Losses of circulation can impact drinking water too. This past April in Texas, construction of the Permian Highway Pipeline caused a loss that left residents with muddy well water. A 3 million gallon loss of circulation along the Mariner East route led to 208,000 gallons of drilling mud entering a lake, and a $2 million fine for Sunoco, the pipeline’s operator.
Our Falcon Public EIA Project found 240 groundwater wells within 1/4 mile of the pipeline and 24 within 1,000 ft of an HDD site. The pipeline also crosses near surface water reservoirs. Drilling mud spills could put these drinking water sources at risk.
But when it comes to understanding the true impact of the more than 245,000+ gallons of drilling fluid lost beneath Pennsylvania and Ohio, there are a lot of remaining questions. The Falcon route crosses over roughly 20 miles of under-mined land (including 5.6 miles of active coal mines) and 25 miles of porous karst limestone formations (learn more about karst). Add in to the mix the thousands of abandoned, conventional, and fracked wells in the region – and you start to get a picture of how holey the land is. Where or how drilling fluid interacts with these voids underground is largely unknown.
Other Drilling Fluid Losses
In addition to the SCIO-04 HDD, there are other drilling fluid losses that occurred in sensitive locations.
In Robinson Township, Pennsylvania, over a dozen losses of circulation (many of which occurred over the span of several days) released a reported 90,067 gallons of drilling fluid into the ground at the HOU-04 HDD. This HDD is above inactive surface and underground mines.
The Falcon passes through and near surface drinking water sources. In Beaver County, Pennsylvania, the pipeline crosses the headwaters of the Ambridge Reservoir and the water line that carries out its water for residents in Beaver County townships (Ambridge, Baden, Economy, Harmony, and New Sewickley) and Allegheny County townships (Leet, Leetsdale, Bell Acres, and Edgeworth). The group Citizens to Protect the Ambridge Reservoir, which formed in 2012 to protect the reservoir from unconventional oil and gas infrastructure, led efforts to stop Falcon Construction, and the Ambridge Water Authority itself called the path of the pipeline “not acceptable.”In response to public pressure, Shell did agree to build a back up line to the West View Water Authority in case issues arose from the Falcon’s construction.
Unfortunately, a 50-gallon inadvertent return was reported at the HDD that crosses the waterline (Figure 4), and a 160 gallon inadvertent return occurred in Raccoon Municipal Park within the watershed and near its protected headwaters (Figure 5). Both of these releases are reported to have occurred within the pipeline’s construction area and not into waterways.
Figure 4) HOU-10 HDD location on the Falcon Pipeline, where 50 gallons were released on the drill pad on 7/9/2019
Figure 5) SCIO-05 HDD location on the Falcon Pipeline, where 160 gallons were released on 6/10/19, within the pipeline’s LOD (limit of disturbance)
Farther west, the pipeline crosses through the watershed of the Tappan Reservoir, which provides water for residents in Scio, Ohio and the Ohio River, which serves over 5 million people.
A 35- gallon inadvertent return occurred at a conventional bore within the Tappan Lake Protection Area, impacting a wetland and stream. We are not aware of any spills impacting the Ohio River.
Pipelines in a Pandemic
This investigation makes it clear that weak laws and enforcement around drilling fluid spills allows pipeline construction to harm sensitive ecosystems and put drinking water sources at risk. Furthermore, regulations don’t require state agencies or Shell to notify communities when many of these drilling mud spills occur.
The problem continues where the 97-mile pipeline ends – at the Shell ethane cracker. In March, workers raised concerns about the unsanitary conditions of the site, and stated that crowded workspaces made social distancing impossible. While Shell did halt construction temporarily, state officials gave the company the OK to continue work – even without the waiver many businesses had to obtain.
The state’s decision was based on the fact it considered the ethane cracker to “support electrical power generation, transmission and distribution.” The ethane cracker – which is still months and likely years away from operation – does not currently produce electrical power and will only provide power generation to support plastic manufacturing.
This claim continues a long pattern of the industry attempting to trick the public into believing that we must continue expanding oil and gas operations to meet our country’s energy needs. In reality, Shell and other oil and gas companies are attempting to line their own pockets by turning the country’s massive oversupply of fracked gas into plastic. And just as Shell and state governments have put the health of residents and workers on the line by continuing construction during a global pandemic, they are sacrificing the health of communities on the frontlines of the plastic industry and climate change by pushing forward the build-out of the petrochemical industry during a global climate crisis.
This election year, while public officials are pushing forward major action to respond to the economic collapse, let’s push for policies and candidates that align with the people’s needs, not Big Oil’s.
By Erica Jackson, Community Outreach & Communications Specialist, FracTracker Alliance
https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2020/06/FalconPipelineFrontPage-scaled.jpg4301500Erica Jacksonhttps://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/2021-FracTracker-logo-horizontal.pngErica Jackson2020-06-16 11:47:062021-04-15 14:16:44Falcon Pipeline Construction Releases over 250,000 Gallons of Drilling Fluid in Pennsylvania and Ohio
FracTracker Alliance has released a new national map, filled with energy and petrochemical data. Explore the map, continue reading to learn more, and see how your state measures up!
This map has been updated since this blog post was originally published, and therefore statistics and figures below may no longer correspond with the map
The items on the map (followed by facility count in parenthesis) include:
For oil and gas wells, view FracTracker’s state maps.
Transportation & Storage
Natural gas compressor stations (1,367) – Facilities built along a pipeline route that pressurize natural gas to keep it flowing through the pipeline.
Crude oil rail terminals (94) – Rail terminals that load and unload crude oil (liquid hydrocarbons that have yet to be processed into higher-value petroleum products).
Liquefied natural gas import/export terminals (8) – Facilities that can a) liquefy natural gas so it can be exported as LNG (liquefied natural gas) and/or b) re-gasify LNG so it can be used as natural gas. Natural gas is transported in a liquid state because it takes up less space as a liquid than as a gas.
Natural Gas Underground Storage (486) – Locations where natural gas is stored underground in aquifers, depleted gas fields, and salt formations.
Petroleum Product Terminals (1,484) – Terminals with a storage capacity of 50,000 barrels or more and/or the ability to receive volumes from tanker, barge, or pipeline. Petroleum products include products “produced from the processing of crude oil and other liquids at petroleum refineries, from extraction of liquid hydrocarbons at natural gas processing plants, and from production of finished petroleum products at blending facilities.”
Petroleum Ports (242) – A port that can import and/or export 200,000 or more short tons of petroleum products a year.
Natural gas import/export pipeline facility (54) – A facility where natural gas crosses the border of the continental United States.
Pipelines
Crude oil pipelines – major crude oil pipelines, including interstate truck lines and selected intrastate lines, but not including gathering lines.
Natural gas liquid pipelines – Also referred to as hydrocarbon gas liquid pipelines, they carry the heavier components of the natural gas stream which are liquid under intense pressure and extreme cold, but gas in normal conditions.
Natural gas pipelines– Interstate and intrastate natural gas pipelines. Due to the immensity of this pipeline network and lack of available data, this pipeline layer in particular varies in degree of accuracy.
Petroleum Product Pipelines – Major petroleum product pipelines.
Recent Pipeline Projects – Pipeline projects that have been announced since 2017. This includes projects in various stages, including under construction, complete, planned or canceled. Click on the pipeline for the status.
Processing & Downstream
Natural Gas Processing Plants (478) – Plants that separate impurities and components of the natural gas stream.
Chemical plants (36) – Includes two types of chemical plants – petrochemical production and ammonia manufacturing – that report to EPA’s Greenhouse Gas Reporting Program.
Ethylene Crackers (30) – Also referred to as ethane crackers, these petrochemical complexes that converts ethane (a natural gas liquid) into ethylene. Ethylene is used to make products like polyethylene plastic.
Petroleum Refineries (135) – A plant that processes crude oil into products like petroleum naphtha, diesel fuel, and gasoline.
Power Plants (9,414) – Electric generating plants with a capacity of at least one megawatt, sorted by energy source.
Wind Turbines (63,003) – Zoom in on wind power plants to see this legend item appear.
Natural Resources
Shale Plays (45) – Tight oil and gas shale plays, which are formations where oil and gas can be extracted.
Major Rivers
Solar Energy Potential – Potential solar energy generation, in kilowatt-hours per square meter per day – averaged annually.
This map is by no means exhaustive, but is exhausting. It takes a lot of infrastructure to meet the energy demands from industries, transportation, residents, and businesses – and the vast majority of these facilities are powered by fossil fuels. What can we learn about the state of our national energy ecosystem from visualizing this infrastructure? And with increasing urgency to decarbonize within the next one to three decades, how close are we to completely reengineering the way we make energy?
Key Takeaways
Natural gas accounts for 44% of electricity generation in the United States – more than any other source. Despite that, the cost per megawatt hour of electricity for renewable energy power plants is now cheaper than that of natural gas power plants.
The state generating the largest amount of solar energy is California, while wind energy is Texas. The state with the greatest relative solar energy is not technically a state – it’s D.C., where 18% of electricity generation is from solar, closely followed by Nevada at 17%. Iowa leads the country in relative wind energy production, at 45%.
The state generating the most amount of energy from both natural gas and coal is Texas. Relatively, West Virginia has the greatest reliance on coal for electricity (85%), and Rhode Island has the greatest percentage of natural gas (92%).
With 28% of total U.S. energy consumption for transportation, many of the refineries, crude oil and petroleum product pipelines, and terminals on this map are dedicated towards gasoline, diesel, and other fuel production.
Petrochemical production, which is expected to account for over a third of global oil demand growth by 2030, takes the form of chemical plants, ethylene crackers, and natural gas liquid pipelines on this map, largely concentrated in the Gulf Coast.
Electricity generation
The “power plant” legend item on this map contains facilities with an electric generating capacity of at least one megawatt, and includes independent power producers, electric utilities, commercial plants, and industrial plants. What does this data reveal?
In terms of the raw number of power plants – solar plants tops the list, with 2,916 facilities, followed by natural gas at 1,747.
In terms of megawatts of electricity generated, the picture is much different – with natural gas supplying the highest percentage of electricity (44%), much more than the second place source, which is coal at 21%, and far more than solar, which generates only 3% (Figure 1).
Figure 1. Electricity generation by source in the United States, 2019. Data from EIA.
This difference speaks to the decentralized nature of the solar industry, with more facilities producing less energy. At a glance, this may seem less efficient and more costly than the natural gas alternative, which has fewer plants producing more energy. But in reality, each of these natural gas plants depend on thousands of fracked wells – and they’re anything but efficient.
The cost per megawatt hour of electricity for a renewable energy power plants is now cheaper than that of fracked gas power plants. A report by the Rocky Mountain Institute, found “even as clean energy costs continue to fall, utilities and other investors have announced plans for over $70 billion in new gas-fired power plant construction through 2025. RMI research finds that 90% of this proposed capacity is more costly than equivalent [clean energy portfolios, which consist of wind, solar, and energy storage technologies] and, if those plants are built anyway, they would be uneconomic to continue operating in 2035.”
The economics side with renewables – but with solar, wind, geothermal comprising only 12% of the energy pie, and hydropower at 7%, do renewables have the capacity to meet the nation’s energy needs? Yes! Even the Energy Information Administration, a notorious skeptic of renewable energy’s potential, forecasted renewables would beat out natural gas in terms of electricity generation by 2050 in their 2020 Annual Energy Outlook.
This prediction doesn’t take into account any future legislation limiting fossil fuel infrastructure. A ban on fracking or policies under a Green New Deal could push renewables into the lead much sooner than 2050.
In a void of national leadership on the transition to cleaner energy, a few states have bolstered their renewable portfolio.
Figure 2. Electricity generation state-wide by source, 2019. Data from EIA.
One final factor to consider – the pie pieces on these state charts aren’t weighted equally, with some states’ capacity to generate electricity far greater than others. The top five electricity producers are Texas, California, Florida, Pennsylvania, and Illinois.
Transportation
In 2018, approximately 28% of total U.S. energy consumption was for transportation. To understand the scale of infrastructure that serves this sector, it’s helpful to click on the petroleum refineries, crude oil rail terminals, and crude oil pipelines on the map.
Transportation Fuel Infrastructure. Data from EIA.
The majority of gasoline we use in our cars in the US is produced domestically. Crude oil from wells goes to refineries to be processed into products like diesel fuel and gasoline. Gasoline is taken by pipelines, tanker, rail, or barge to storage terminals (add the “petroleum product terminal” and “petroleum product pipelines” legend items), and then by truck to be further processed and delivered to gas stations.
China leads the world in this movement. In 2018, just over half of the world’s electric vehicles sales occurred in China. Analysts predict that the country’s oil demand will peak in the next five years thanks to battery-powered vehicles and high-speed rail.
In the United States, the percentage of electric vehicles on the road is small but growing quickly. Tax credits and incentives will be important for encouraging this transition. Almost half of the country’s electric vehicle sales are in California, where incentives are added to the federal tax credit. California also has a “Zero Emission Vehicle” program, requiring electric vehicles to comprise a certain percentage of sales.
We can’t ignore where electric vehicles are sourcing their power – and for that we must go back up to the electricity generation section. If you’re charging your car in a state powered mainly by fossil fuels (as many are), then the electricity is still tied to fossil fuels.
Petrochemicals
Many of the oil and gas infrastructure on the map doesn’t go towards energy at all, but rather aids in manufacturing petrochemicals – the basis of products like plastic, fertilizer, solvents, detergents, and resins.
Natural gas processing plants separate components of the natural gas stream to extract natural gas liquids like ethane and propane – which are transported through the natural gas liquid pipelines. These natural gas liquids are key building blocks of the petrochemical industry.
Ethane crackers process natural gas liquids into polyethylene – the most common type of plastic.
The chemical plants on this map include petrochemical production plants and ammonia manufacturing. Ammonia, which is used in fertilizer production, is one of the top synthetic chemicals produced in the world, and most of it comes from steam reforming natural gas.
As we discuss ways to decarbonize the country, petrochemicals must be a major focus of our efforts. That’s because petrochemicals are expected to account for over a third of global oil demand growth by 2030 and nearly half of demand growth by 2050 – thanks largely to an increase in plastic production. The International Energy Agency calls petrochemicals a “blind spot” in the global energy debate.
Petrochemical development off the coast of Texas, November 2019. Photo by Ted Auch, aerial support provided by LightHawk.
Investing in plastic manufacturing is the fossil fuel industry’s strategy to remain relevant in a renewable energy world. As such, we can’t break up with fossil fuels without also giving up our reliance on plastic. Legislation like the Break Free From Plastic Pollution Act get to the heart of this issue, by pausing construction of new ethane crackers, ensuring the power of local governments to enact plastic bans, and phasing out certain single-use products.
“The greatest industrial challenge the world has ever faced”
Mapped out, this web of fossil fuel infrastructure seems like a permanent grid locking us into a carbon-intensive future. But even more overwhelming than the ubiquity of fossil fuels in the US is how quickly this infrastructure has all been built. Everything on this map was constructed since Industrial Revolution, and the vast majority in the last century (Figure 3) – an inch on the mile-long timeline of human civilization.
Figure 3. Global Fossil Fuel Consumption. Data from Vaclav Smil (2017)
In fact, over half of the carbon from burning fossil fuels has been released in the last 30 years. As David Wallace Wells writes in The Uninhabitable Earth, “we have done as much damage to the fate of the planet and its ability to sustain human life and civilization since Al Gore published his first book on climate than in all the centuries—all the millennia—that came before.”
What will this map look like in the next 30 years?
A recent report on the global economics of the oil industry states, “To phase out petroleum products (and fossil fuels in general), the entire global industrial ecosystem will need to be reengineered, retooled and fundamentally rebuilt…This will be perhaps the greatest industrial challenge the world has ever faced historically.”
Is it possible to build a decentralized energy grid, generated by a diverse array of renewable, local, natural resources and backed up by battery power? Could all communities have the opportunity to control their energy through member-owned cooperatives instead of profit-thirsty corporations? Could microgrids improve the resiliency of our system in the face of increasingly intense natural disasters and ensure power in remote regions? Could hydrogen provide power for energy-intensive industries like steel and iron production? Could high speed rail, electric vehicles, a robust public transportation network and bike-able cities negate the need for gasoline and diesel? Could traditional methods of farming reduce our dependency on oil and gas-based fertilizers? Could zero waste cities stop our reliance on single-use plastic?
Of course! Technology evolves at lightning speed. Thirty years ago we didn’t know what fracking was and we didn’t have smart phones. The greater challenge lies in breaking the fossil fuel industry’s hold on our political system and convincing our leaders that human health and the environment shouldn’t be externalized costs of economic growth.
https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2020/02/National-map-feature-3.png400900Erica Jacksonhttps://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/2021-FracTracker-logo-horizontal.pngErica Jackson2020-02-28 17:35:142022-05-02 15:21:42National Energy and Petrochemical Map
Map: Ohio Quarterly Utica Oil and Gas Production along with Quarterly Wastewater Disposal
Well Volumes
A little under a year ago, FracTracker released a map and associated analysis, “A Disturbing Tale of Diminishing Returns in Ohio,” with respect to Utica oil and gas production, highlighting the increasing volume of waste injected in wastewater disposal wells, and trends in lateral length in fracked wells from 2010 to 2018. In this article, I’ll provide an update on Ohio’s Utica oil and gas production in 2018 and 2019, the demands on freshwater, and waste disposal. After looking at the data, I recommend that we holistically price our water resources and the ways in which we dispose of the industry’s radioactive waste in order to minimize negative externalities.
Recently, I’ve been inspired by the works of Colin Woodward[1] and Marvin Harris, who outline the struggle between liberty and the common good. They relate this to the role that commodities and increasing resource intensity play in maintaining or enhancing living standards. This quote from Harris’s “Cannibals and Kings” struck me as the 122 words that most effectively illustrate the impacts of the fracking boom that started more than a decade ago in Central Appalachia:
“Regardless of its immediate cause, intensification is always counterproductive. In the absence of technological change, it leads inevitably to the depletion of the environment and the lowering of the efficiency of production since the increased effort sooner or later must be applied to more remote, less reliable, and less bountiful animals, plants, soils, minerals, and sources of energy. Declining efficiency in turn leads to low living standards – precisely the opposite of the desired result. But this process does not simply end with everybody getting less food, shelter, and other necessities in return for more work. As living standards decline, successful cultures invent new and more efficient means of production which sooner or later again lead to the depletion of the natural environment.” From Chapter 1, page 5 of Marvin Harris’ “Cannibals and Kings: The Origins of Cultures, 1977
In reflecting on Harris’s quote as it pertains to fracking, I thought it was high time I updated several of our most critical data sets. The maps and data I present here speak to intensification and the fact that the industry is increasingly leaning on cheap water withdrawals, landscape impacts, and waste disposal methods to avoid addressing their increasingly gluttonous ways. To this point, the relationship between intensification and resource utilization is not just the purview of activists, academics, and journalists anymore; industry collaborators like IHS Markit admitting as much in their latest analysis pointing to the fact that oil and gas operators “will have to drill substantially more wells just to maintain current production levels and even more to grow production”. Insert Red Queen Hypothesis analogy here!
Oil and Gas Production in Ohio
The four updated data sets presented here are: 1) oil, gas, and wastewater production, 2) surface and groundwater withdrawal rates for the fracking industry, 3) freshwater usage by individual Ohio fracked wells, and 3) wastewater disposal well (also referred to as Class II injection wells) rates.
Below are the most important developments from these data updates as it pertains to intensification and what we can expect to see in the future, with or without the ethane cracker plants being trumpeted throughout Appalachia.
From a production standpoint, total oil production has increased by 30%, while natural gas production has increased by 50% year over year between the last time we updated this data and Q2-2019 (Table 1).
According to the data we’ve compiled, the rate of growth for wastewater production has exceeded oil and is nearly equal to natural gas at 48% from 2017 to 2018. On average the 2,398 fracked wells we have compiled data for are producing 27% more wastewater per well now than they did at the end of 2017.
————–2017————–
————–2019————–
Oil (million barrels)
Gas (million Mcf)
Brine (million barrels)
Oil (million barrels)
Gas (million Mcf)
Brine (million barrels)
Max
0.51
12.92
0.23
0.62
17.57
0.32
Total
83.14
5,768.47
76.01
108.15
8,679.12
112.28
Mean
0.40
2.79
0.37
0.45
3.62
0.47
Table 1. Summary statistics for 2,398 fracked wells in Ohio from a production perspective from 2017 to Q2 2019.
Figure 1. Total fracked gas produced per quarter and average fracked gas produced per well in Ohio from 2013 to Q2-2019.
The increasing amount of resources and number of wells necessary to achieve marginal increases in oil and gas production is a critical factor to considered when assessing industry viability and other long-term implications. As an example, in Ohio’s Utica Shale, we see that total production is increasing, but as IHS Markit admits, this is only possibly by increasing the total number of producing wells at a faster rate. As is evidenced in Figure 1, somewhere around the Winter of 2017-2018, the production rate per well began to flatline and since then it has begun to decrease.
Water demands for oil and gas production in Ohio
Since last we updated the industry’s water withdrawal rates, the Ohio Department of Natural Resources (ODNR) has begun to report groundwater rates in addition to surface water. The former now account for nine sites in seven counties, but amount to a fraction of reported withdrawals to date (around 00.01% per year in 2017 and 2018). The more disturbing developments with respect to intensification are:
1) Since we last updated this data, 59 new withdrawal sites have come online. There are currently 569 sites in total in ODNR’s database. This amounts to a nearly 12% increase in the total number of sites since 2017. With this additional inventory, the average withdrawal rate across all sites has increased by 13% (Table 2).
2) Since 2010, the demand for freshwater to be used in fracking has increased by 15.6% or 693 million gallons per year (Figure 2).
3) We expect to see an inflection point when water production will increase to accommodate the petrochemical buildout with cracker plants in Dilles Bottom, OH; Beaver County, PA; and elsewhere. In 2018 alone, the oil and gas industry pulled 4.69 billion gallons of water from the Ohio River Valley. Since 2010, the industry has permanently removed 22.96 billion gallons of freshwater from the Ohio River Valley. It would take the entire population of Ohio five years to use the 2018 rate in their homes.[2]
As we and others have mentioned in the past, this trend is largely due to the bargain basement price at which we sell water to the oil and gas sector throughout Appalachia.[3] To increase their nominal production returns, companies construct longer laterals with orders of magnitude more water, sand, and chemicals. At this rate, the fracking industry’s freshwater demand will have doubled to around 8.8-.9.5 billion gallons per year by around 2023. Figure 3 demonstrates that average fracked lateral length continues to increase to the tune of +15.7-21.2% (+1,564-2,107 feet) per quarter per lateral. This trend alone is more than 2.5 times the rate of growth in oil production and roughly 24% greater than the rate of growth in natural gas production (See Table 1).
4. The verdict is even more concerning than it was a couple years ago with respect to water demand increasing by 30% per quarter per well or an average of 4.73 million gallons (Figure 4). The last time we did this analysis >1.5 years ago demand was rising by 25% per quarter or 3.84 million gallons. At that point I wouldn’t have guessed that this exponential rate of water demand would have increased but that is exactly what has happened. Very immediate conversations must start taking place in Columbus and at the region’s primary distributor of freshwater, The Muskingum Watershed Conservancy District (MWCD), as to why this is happening and how to push back against the unsustainable trend.
2017
2018
Sites
510
569
Maximum (billion gallons)
1.059
1.661
Sum (billion gallons)
18.267
22.957
Mean (billion gallons)
0.358
0.404
Table 2. Summary of fracking water demands throughout Ohio in 2017 when we last updated this data as well as how those rates changed in 2018.
Figure 2. Hydraulic fracturing freshwater demand in total across 560+ sites in Ohio from 2010 to 2018 (million gallons per year).
Figure 3. Average lateral length for all of Ohio’s permitted hydraulically fractured laterals from from Q3-2010 to Q4-2019, along with average rates of growth from a linear and exponential standpoint (feet).
Figure 4. Average Freshwater Demand Per Unconventional Well in Ohio from Q3-2011 to Q3-2019 (million gallons).
Waste Disposal
When it comes to fracking wastewater disposal, the picture is equally disturbing. Average disposal rates across Ohio’s 220+ wastewater disposal wells increased by 12.1% between Q3-2018 and Q3-2019 (Table 3). Interestingly, this change nearly identically mirrors the change in water withdrawals during the same period. What goes down– freshwater – eventually comes back up.
Across all of Ohio’s wastewater disposal wells, total volumes increased by nearly 22% between 2018 and the second half of 2019. However, the more disturbing trend is the increasing focus on the top 20 most active wastewater disposal wells, which saw an annual increase of 17-18%. These wells account for nearly 50% of all waste and the concern here is that many of the pending wastewater disposal well permits are located on these sites, within close proximity, and/or are proposed by the same operators that operate the top 20.
When we plot cumulative and average disposal rates per well, we see a continued exponential increase. If we look back at the last time, we conducted this analysis, the only positive we see in the data is that at that time, average rates of disposal per well were set to double by the Fall of 2020. However, that trend has tapered off slightly — rates are now set to double by 2022.
Each wastewater disposal well is seeing demand for its services increase by 2.42 to 2.94 million gallons of wastewater per quarter (Figure 5). Put another way, Ohio’s wastewater disposal wells are rapidly approaching their capacity, if they haven’t already. Hence why the oil and gas industry has been frantically submitting proposals for additional waste disposal wells. If these wells materialize, it means that Ohio will continue to be relied on as the primary waste receptacle for the fracking industry throughout Appalachia.
Variable
——————-All Wells——————-
——————-Top 20——————-
To Q3-2018
To Q3-2019
% Change
To Q3-2018
To Q3-2019
% Change
Number of Wells
223
243
+9.0
——-
——-
——-
Max (MMbbl)
1.12
1.20
+7.1
——-
——-
——-
Sum (MMbbl)
203.19
247.05
+21.6
101.43
119.31
+17.6
Average (MMbbl)
0.91
1.02
+12.1
5.07
5.97
+17.8
Table 3. Summary Statistics for Ohio’s Wastewater Disposal Wells (millions of barrels (MMbbl)).
Figure 5. Average Fracking Waste Disposal across all of Ohio’s Wastewater Disposal Wells and the cumulative amount of fracking waste disposed of in these wells from Q3-2010 to Q2-2019 (million barrels).
Using the Pennsylvania natural gas data merged with the Ohio wastewater data, we were able to put a finer point on how much wastewater would be produced with a 100,000 barrel ethane cracker like the one PTT Global Chemical has proposed for Dilles Bottom, Ohio. The following are our best estimate calculations assuming 1 barrel of condensate is 20-40% ethane. These calculations required that we take some liberties with the merge of the ratio of gas to wastewater in Ohio with the ratio of gas to condensate in Pennsylvania:
For 2,064 producing Ohio fracked wells, the ratio of gas to wastewater is 64.76 thousand cubic feet (Mcf) of gas produced per barrel of wastewater.
Assuming 40% ethane, the ratio of gas to condensate in Washington County, PA wells for the first half of 2019 was 320.08 Mcf of gas per barrel of ethane condensate. For 100,000 barrels of ethane needed per cracker per day, that would result in 494,285 barrels (20.76 million gallons) of brine per day.
Assuming 20% ethane, the ratio of gas to condensate in Washington County, PA wells for the first half of 2019 was 640.15 Mcf per barrel of ethane condensate = For 100,000 barrels of ethane needed per cracker per day that would result in 988,571 barrels/41.52 million gallons of wastewater per day.
But wait, here is the real stunner:
The 40% assumption result is 3.81 times the daily rates of wastewater taken in by our current inventory of wastewater disposal wells and 5.37 times the daily rates of brine taken in by the top 20 wells (Note: the top 20 wastewater disposal wells account for 71% of all wastewater waste taken in by all of the state’s disposal wells).
The 20% assumption result is 7.62 times the daily rates of wastewater taken in by our current inventory of wastewater disposal wells and 10.74 times the daily rates of wastewater taken in by the top 20 wells.
Therefore, we estimate the fracked wells supplying the proposed PTTGC ethane cracker will generate between 20.76 million and 41.52 million gallons of wastewater per day. That is 3.8 to 7.6 times the amount of wastewater currently received by Ohio’s wastewater disposal wells.
What does this means in terms of truck traffic? We can assume that at least 80% of the trucks that transport wastewater are the short/baby bottle trucks which haul 110 barrels per trip. This means that our wastewater estimates would require between 4,493 and 8,987 truck trips per day, respectively. The pressures this amount of traffic will put on Appalachian roads and communities will be hard to measure and given the current state of state and federal politics and/or oversight it will be even harder to measure the impact inevitable spills and accidents will have on the region’s waterways.
Conclusion
There is no reason to believe these trends will not persist and become more intractable as the industry increasingly leans on cheap waste disposal and water as a crutch. The fracking industry will continue to present shareholders with the illusion of a robust business model, even in the face of rapid resource depletion and precipitous production declines on a per well basis.
I am going to go out on a limb and guess that unless we more holistically price our water resources and the ways in which we dispose of the industry’s radioactive waste, there will be no other supply-side signal that we could send that would cause the oil and gas industry to change its ways. Until we reach that point, we will continue to compile data sets like the ones described above and included in the map below, because as Supreme Court Justice Louis Brandeis once said, “Sunlight is the best disinfectant!”
By Ted Auch, Great Lakes Program Coordinator, FracTracker Alliance with invaluable data compilation assistance from Gary Allison
[1] Colin Woodward’s “American Character: A history of the epic struggle between individual liberty and the common good” is a must read on the topic of resource utilization and expropriation.
[3] In Ohio the major purveyor of water for the fracking industry is the Muskingum Watershed Conservancy District (MCWD) and as we’ve pointed out in the past they sell water for roughly $4.50 to $6.50 per thousand gallons. Meanwhile across The Ohio River the average price of water for fracking industry in West Virginia in the nine primary counties where fracking occurs is roughly $8.38 per thousand gallons.
Data Downloads
Quarterly oil, gas, brine, and days in production for 2,390+ Unconventional Utica/Point Pleasant Wells in Ohio from 2010 to Q2-2019
The Captina Creek Watershed straddles the counties of Belmont and Monroe in Southeastern Ohio and feeds into the Ohio River. It is the highest quality watershed in all of Ohio and a great examples of what the Ohio River Valley’s tributaries once looked, smelled, and sounded like. Sadly, today it is caught in the cross-hairs of the oil and gas industry by way of drilling, massive amounts of water demands, pipeline construction, and fracking waste production, transport, and disposal. The images and footage presented in the story map below are testament to the risks and damage inherent to fracking in the Captina Creek watershed and to this industry at large. Data included herein includes gas gathering and interstate transmission pipelines like the Rover, NEXUS, and Utopia (Figure 1), along with Class II wastewater injection wells, compressor stations, unconventional laterals, and freshwater withdrawal sites and volumes.
The image at the top of the page captures my motivation for taking a deeper dive into this watershed. Having spent 13+ years living in Vermont and hiking throughout The Green and Adirondack Mountains, I fell in love with the two most prominent tree species in this photo: Yellow Birch (Betula alleghaniensis) and Northern Hemlock (Tsuga candadensis). This feeling of being at home was reason enough to be thankful for Captina Creek in my eyes. Seeing this region under pressure from the oil and gas industry really hit me in my botanical soul. We remain positive with regards to the area’s future, but protective action against fracking in the Captina Creek Watershed is needed immediately!
Fracking in the Captina Creek Watershed: A Story Map
Pennsylvania’s fracking industry is producing record amounts of toxic waste — where does it all go?
Drilling for methane and other fossil fuels is an energy-intensive process with many associated environmental costs. In addition to the gas that is produced through high volume hydraulic fracturing (“unconventional drilling,” or “fracking”), the process generates a great deal of waste at the drill site. These waste products may include several dozen tons of drill cutting at every well that is directionally drilled, in addition to liner materials, contaminated soil, fracking fluid, and other substances that must be removed from the site.
In 2018, Pennsylvania’s oil and gas industry (including both unconventional and conventional wells) produced over 2.9 billion gallons (nearly 69 million barrels) of liquid waste, and 1,442,465 tons of solid waste. In this article, we take a look at where this waste (and its toxic components) end up and how waste values have changed in recent years. We also explore how New York State, despite its reputation for being anti-fracking, isn’t exempt from the toxic legacy of this industry.
Waste that comes back to haunt us
According to a study by Physicians, Scientists and Engineers, over 80% of all waste from oil and gas drilling stays within the state of Pennsylvania. But once drilling wastes are sent to landfills, is that the end of them? Absolutely not!
Drilling waste also gets into the environment through secondary means. According to a recent report by investigative journalists at Public Herald, on average, 800,000 tons of fracking waste from Pennsylvania is sent to Pennsylvania landfills. When this waste is sent to landfills, radioactivity and other chemicals can percolate through the landfill, and are collected as leachate, which is then shipped to treatment plants.
Public Herald documented how fourteen sewage treatment plants in Pennsylvania have been permitted by Pennsylvania’s Department of Environmental Protection (PA DEP) to process and discharge radioactive wastes into more than a dozen Pennsylvania waterways.
Public Herald’s article includes an in-depth analysis of the issue. Their work is supported by a map of the discharge sites, created by FracTracker.
Trends over time
Pennsylvania Department of Environmental Protection maintains a rich database of oil and gas waste and production records associated with their Oil and Gas Reporting Website. The changes in waste disposal from Pennsylvania’s unconventional drilling reveal a number of interesting stories.
Let’s look first at overall unconventional drilling waste.
According to data from the federal Energy Information Administration, gas production in Pennsylvania began a steep increase around 2010, with the implementation of high volume hydraulic fracturing in the Marcellus Shale (see Figure 1). The long lateral drilling techniques allowed industry to exploit exponentially more of the tight shale via single well than was ever before possible with conventional, vertical drilling.
Figure 1. Data summary from FracTracker.org, based on EIA data.
The more recently an individual well is drilled, the more robust the production. We see an overall increase in gas production over time in Pennsylvania over the past decade. Paradoxically, the actual number of new wells drilled each year in the past 4-5 years are less than half of the number drilled in 2011 (see Figure 2).
Figure 2: Data summary from FracTracker.org, based on PA DEP data
Why is this? The longer laterals —some approaching 3 miles or more—associated with new wells allow for more gas to be extracted per site.
With this uptick in gas production values from the Marcellus and Utica Formations come more waste products, including copious amounts drilling waste, “produced water,” and other byproducts of intensive industrial operations across PA’s Northern Tier and southwestern counties.
Comparing apples and oranges?
When we look at the available gas production data compared with data on waste products from the extraction process, some trends emerge. First of all, it’s readily apparent that waste production does not track directly with gas production in a way one would expect.
Recall that dry gas production has increased annually since 2006 (see Figure 1). However, the reported waste quantities from industry have not followed that same trend.
In the following charts, we’ve split out waste from unconventional drilling by solid waste in tons (Figure 3) and liquid waste, in barrels (Figure 4).
Figure 3: Annual tonnage of solid waste from the unconventional oil and gas industry, organized by the state it is disposed in. Data source: PA DEP, processed by FracTracker Alliance
Figure 4: Annual volume of liquid waste from the unconventional oil and gas development, organized by state it is disposed in. One barrel is equivalent to 42 gallons. Data source: PA DEP, processed by FracTracker Alliance
Note the striking difference in disposal information for solid waste, compared with liquid waste, coming from Pennsylvania.
“Disposal Location Unknown”
Until just the last year, often more than 50% of the known liquid waste generated in PA was disposed of at unknown locations. The PA DEP waste report lists waste quantity and method for these unknown sites,depending on the year: “Reuse without processing at a permitted facility,” “Reuse for hydraulic fracturing,” “Reuse for diagnostic purposes,” “Reuse for drilling or recovery,” “Reuse for enhanced recovery,” and exclusively in more recent years (2014-2016), “Reuse other than road-spreading.”
In 2011, of the 20.5 million barrels of liquid waste generated from unconventional drilling, about 56% was allegedly reused on other drilling sites. However, over 9 million barrels—or 44% of all liquid waste—were not identified with a final destination or disposal method. Identified liquid waste disposal locations included “Centralized treatment plant for recycle,” which received about a third of the non-solid waste products.
In 2012, the quantity of the unaccounted-for fracking fluid waste dropped to about 40%. By 2013, the percentage of unaccounted waste coming from fracking fluid dropped to just over 21%, with nearly 75% coming from produced fluid, which is briny, but containing fewer “proprietary”—typically undisclosed—chemicals.
By 2017, accounting had tightened up further. PA DEP data show that 99% of all waste delivered to undisclosed locations was produced fluid shipped to locations outside of Pennsylvania. By 2018, all waste disposal was fully accounted for, according to DEP’s records.
In looking more closely at the data, we see that:
Prior to 2018, well drillers did not consistently report the locations at which produced water was disposed of or reused. Between 2012 and 2016, a greater volume of unconventional liquid waste went unaccounted for than was listed for disposal in all other locations, combined.
In Ohio, injection wells, where liquid waste is injected into underground porous rock formations, accounted for the majority of the increase in waste accepted there: 2.9 million barrels in 2017, and 5.7 million barrels in 2018 (a jump of 97%).
West Virginia’s acceptance of liquid waste increased significantly in 2018 over 2017 levels, a jump of over a million barrels, up from only 55,000. This was almost entirely due to unreported reuse at well pads.
In 2018, reporting, in general, appears to be more thorough than it was in previous years. For example, in 2017, nearly 692,000 barrels of waste were reused at well pads outside PA, but those locations were not disclosed. Almost 7000 more barrels were also disposed of at unknown locations. In 2018, there were no such ambiguities.
A closer look at Pennsylvania’s fracking waste shipped to New York State
Despite a reputation for being resistant to the fracking industry, for most of this decade, the state of New York has been accepting considerable amounts of fracking waste from Pennsylvania. The greatest percentage shipped to New York State is in the form of drilling waste solids that go to a variety of landfills throughout Central and Western New York.
Looking closely at the bar charts above, it’s easy to notice that the biggest recipients of Pennsylvania’s unconventional liquid drilling waste are Pennsylvania itself, Ohio, as well as a significant quantity of unaccounted-for barrels between 2011 and 2016 (“Disposal location unknown”). The data for disposal of solid waste in New York tells a different story, however. In this case, Pennsylvania, Ohio, and New York State all play a role. We’ll take a look specifically at the story of New York, and illustrate the data in the interactive map that follows.
In this map, source locations in Pennsylvania are symbolized with the same color marker as the facility in New York that received the waste from the originating well pad. In the “Full Screen” view, use the “Layers” drop down menu to turn on and off data from separate years.
From the early days of unconventional drilling in Pennsylvania, New York State’s landfills provided convenient disposal sites due to their proximity to the unconventional drilling occurring in Pennsylvania’s Northern tier of counties. Pennsylvania and Ohio took the majority of solid wastes from unconventional drilling waste from Pennsylvania. New York State, particularly between 2011-2015, was impacted far more heavily than all other states, combined (Figure 5, below).
Figure 5: Known disposal locations (excluding PA and OH) of Pennsylvania’s solid waste. Data source: PA DEP, processed by FracTracker Alliance
Here’s the breakdown of locations in New York to where waste was sent. Solid waste disposal into New York’s landfills also dropped by half, following the state’s ban on unconventional drilling in 2014. Most of the waste after 2012 went to the Chemung County Landfill in Lowman, New York, 10 miles southeast of Elmira.
Figure 6: Solid waste from unconventional drilling, sent to facilities in NYS. Data source: PA DEP, processed by FracTracker Alliance
Is waste immobilized once it’s landfilled?
The fate of New York State’s landfill leachate that originates from unconventional drilling waste is a core concern, since landfill waste is not inert. If drilling waste contains radioactivity, fracking chemicals, and heavy metals that percolate through the landfill, and the resulting leachate is sent to municipal wastewater treatment plants, will traditional water treatment methods remove those wastes? If not, what will be the impact on public and environmental health in the water body that receives the “treated” wastewater? In Pennsylvania, for example, a case is currently under investigation relating to pollution discharges into the Monongahela River near Pittsburgh. “That water was contaminated with diesel fuels, it’s alleged, carcinogens and other pollutants,” said Rich Bower, Fayette County District Attorney.
Currently, a controversial expansion of the Hakes Landfill in Painted Post, New York is in the news. Sierra Club and others were concerned about oversight of radium and radon in the landfill’s leachate and air emissions, presumably stemming from years of receiving drill cuttings. The leachate from the landfill is sent to the Bath Wastewater Treatment plant, which is not equipped to remove radioactivity. “Treated” wastewater from the plant is then discharged into the Cohocton River, a tributary of the Chesapeake Bay. In April 2019, these environmental groups filed a law suit against Hakes C&D Landfill and the Town of Campbell, New York, in an effort to block the expansion.
Similar levels of radioactivity in leachate have also been noted in leachate produced at the Chemung County Landfill, according to Gary McCaslin, President of People for a Healthy Environment, Inc.
In recent years, much of the solid unconventional waste arriving in New York State has gone to the Chemung County Landfill (see Figure 6, above). Over the course of several years, this site requested permission to expand significantly from 180,000 tons per year to 417,000 tons per year. However, by 2016, the expansion was deemed unnecessary, and according, the plans were put on hold, in part “…because of a decline in the amount of waste being generated due to a slower economy and more recycling than when the expansion was first planned years ago.” The data in Figure 5 above also parallel this story, with unconventional drilling waste disposed in New York State dropping from over 200,000 tons in 2011 to just over 20,000 tons in 2018.
Liquid waste transported to New York State
The story about liquid unconventional drilling waste exported from Pennsylvania to states other than Ohio is not completely clear (see Figure 7, below). Note that the data indicate more than a 2000% increase in waste liquids going from Pennsylvania to West Virginia after 2017. While it has not been officially documented, FracTracker has been anecdotally informed that a great deal of waste was already going to West Virginia, but that the record-keeping prior to 2018 was simply not strongly enforced.
Figure 7: Known disposal locations (excluding Pennsylvania and Ohio) of Pennsylvania’s liquid waste. Data source: PA DEP, processed by FracTracker Alliance
Beginning in the very early years of the Pennsylvania unconventional fracking boom, a variety of landfills in New York State have also accepted liquid wastes originating in Pennsylvania, including produced water and flowback fluids (see Figure 8, below).
Figure 8: Liquid waste from unconventional drilling, sent to facilities in New York State. Data source: PA DEP, processed by FracTracker Alliance
In addition, while this information doesn’t even appear in the PA DEP records (which are publicly available back to 2010), numerous wastewater treatment plants did accept some quantity, despite being fully unequipped to process the highly saline waste before it was discharged back into the environment.
One such facility was the wastewater treatment plant in Cayuga Heights, Tompkins County, which accepted more than 3 million gallons in 2008. Another was the wastewater treatment plant in Auburn, Cayuga County, where the practice of accepting drilling wastewater was initially banned in July 2011, but the decision was reversed in March 2012 to accept vertical drilling waste, despite strong public dissent. Another wastewater treatment plant in Watertown, Jefferson County, accepted 35,000 gallons in 2009.
Fortunately, most New York State wastewater treatment plant operators were wise enough to not even consider adding a brew of unknown and/or proprietary chemicals to their wastewater treatment stream. Numerous municipalities and several counties banned fracking waste, and once the ban on fracking in New York State was instituted in 2014, nearly all importation of liquid unconventional drilling waste into the state ceased.
Nevertheless, conventional, or vertical well drilling also generates briny produced water, which the New York State Department of Environmental Conservation (DEC) permits communities in New York to accept for ice and dust control on largely rural roads. These so-called “beneficial use determinations” (BUDs) of liquid drilling waste have changed significantly over the past several years. During the height of the Marcellus drilling in around 2011, all sorts of liquid waste was permitted into New York State (see FracTracker’s map of affected areas) and was spread on roads. As a result, the chemicals—many of them proprietary, of unknown constituents, or radioactive—were indirectly discharged into surface waters via roadspreading.
Overall, in the years after the ban in 2014 on high volume hydraulic fracturing was implemented, restrictions on Marcellus waste coming into New York have strengthened. Very little liquid waste entered New York’s landfills after 2013, and what did come in was sent to a holding facility owned by Environmental Services of Vermont. This facility is located outside Syracuse, New York.
New York State says “no” to this toxic legacy
Fortunately, not long after these issues of fracking fluid disposal at wastewater treatment facilities in New York State came to light, the practice was terminated on a local level. The 2014 ban on fracking in New York State officially prevented the disposal of Marcellus fluids in municipal wastewater treatment facilities and required extra permits if it were to be road-spread.
In New York State, the State Senate—after 8 years of deadlock—in early May 2019, passed key legislation that would close a loophole that had previously allowed dangerous oil and gas waste to bypass hazardous waste regulation. Read the press release from Senator Rachel May’s office here. However, despite strong support from both the Senate, and the Assembly, as well as many key environmental groups, the Legislature adjourned for the 2019 session without bringing the law to a final vote. Said Elizabeth Moran, of the New York Public Interest Research Group (NYPIRG), “I want to believe it was primarily a question of timing… Sadly, a dangerous practice is now going to continue for at least another year.”
See Earthworks’ recent three part in-depth reporting on national, New York, and Pennsylvania oil and gas waste, with mapping support by FracTracker Alliance.
All part of the big picture
As long as hydrocarbon extraction continues, the issues of waste disposal—in addition to carbon increases in the atmosphere from combustion and leakage—will result in impacts on human and environmental health. Communities downstream and downwind will bear the brunt of landfill expansions, water contamination, and air pollution. Impacts of climate chaos will be felt globally, with the greatest impacts at low latitudes and in the Arctic.
Transitioning to net-zero carbon emissions cannot be a gradual endeavor. Science has shown that in order to stay under the 1.5 °C warming targets, it must happen now, and it requires the governmental buy-in to the Paris Climate Agreement by every economic power in the world.
No exceptions. Life on our planet requires it.
We have, at most, 12 years to make a difference for generations to come.
FracTracker is closely mapping and following the petrochemical build-out in Appalachia, as the oil and gas industry invests in petrochemical manufacturing. Much of the national attention on the build-out revolves around the Appalachian Storage Hub (ASH), a venture spearheaded by Appalachian Development Group.
The ASH involves a network of infrastructure to store and transport natural gas liquids and finds support across the political spectrum. Elected officials are collaborating with the private sector and foreign investors to further development of the ASH, citing benefits such as national security, increased revenue, job creation, and energy independence.
Left out of the discussion are the increased environmental and public health burdens the ASH would place on the region, and the fact that natural gas liquids are the feedstock of products such as plastic and resins, not energy.
The “Shale Revolution” brought on by high-volume hydraulic fracturing (fracking) in this region encompasses thousands of wells drilled into the Marcellus and Utica-Point Pleasant shale plays across much of the Allegheny Plateau. This area spans from north of Scranton-Wilkes Barre, Pennsylvania, just outside the Catskills Mountains to the East in Susquehanna County, Pennsylvania, and down to the West Virginia counties of Logan, Boone, and Lincoln. The westernmost extent of the fracking experiment in the Marcellus and Utica shale plays is in Noble and Guernsey Counties in Ohio.
Along the way, producing wells have exhibited steeper and steeper declines during the first five years of production, leading the industry to develop what they refer to as “super laterals.” These laterals (the horizontal portion of a well) exceed 3 miles in length and require in excess of 15 million gallons of freshwater and 15,000 tons of silica sand (aka, “proppant”)[1].
The resource-intense super laterals are one way the industry is dealing with growing pressure from investors, lenders, the media, state governments, and the public to reduce supply costs and turn a profit, while also maintaining production. (Note: unfortunately these sources of pressures are listed from most to least concerning to industry itself!)
Another way the fracking industry is hoping to make a profit is by investing in the region’s natural gas liquids (NGLs), such as ethane, propane, and butane, to support the petrochemical industry.
The Appalachian Storage Hub
Continued oil and gas development are part of a nascent effort to establish a mega-infrastructure petrochemical complex, the Appalachian Storage Hub (ASH). For those that aren’t familiar with the ASH it could be framed as the fracking industry’s last best attempt to lock in their necessity across Appalachia and nationwide. The ASH was defined in the West Virginia Executive as a way to revitalize the Mountain State and would consist of the following:
“a proposed underground storage facility that would be used to store and transport natural gas liquids (NGLs) extracted from the Marcellus, Utica and Rogersville shales across Kentucky, Ohio, Pennsylvania and West Virginia. Construction of this hub would not only lead to revenue and job creation in the natural gas industry but would also further enable manufacturing companies to come to the Mountain State, as the petrochemicals produced by shale are necessary materials in most manufacturing supply chains…[with] the raw materials available in the region’s Marcellus Shale alone…estimated to be worth more than $2 trillion, and an estimated 20 percent of this shale is composed largely of ethane, propane and butane NGLs that can be utilized by the petrochemical industry in the manufacturing of consumer goods.”
This is yet another example of fracking rhetoric that appeals to American’s sense of patriotism and need for cheaper consumer goods (in this case, plastics), given that they are seeing little to no growth in wages.
While a specific location for underground storage has not been announced, the infrastructure associated with the ASH (such as pipelines, compressor stations, and processing stations) would stretch from outside Pittsburgh down to Catlettsburg, Kentucky, with the latter currently the home of a sizeable Marathon Oil refinery. The ASH “would act like an interstate highway, with on-ramps and off-ramps feeding manufacturing hubs along its length and drawing from the available ethane storage fields. The piping would sit above-ground and follow the Ohio and Kanawha river valley.”
The politics of the ASH – from Columbus and Charleston to Washington DC
Elected officials across the quad-state region are supporting this effort invoking, not surprisingly, its importance for national security and energy independence.
State-level support
West Virginia Senator Joe Manchin (D) went so far as to introduce “Senate Bill 1064 – Appalachian Energy for National Security Act.” This bill would require Secretary of Energy Rick Perry and his staff to “to conduct a study on the national security implications of building ethane and other natural-gas-liquids-related petrochemical infrastructure in the United States, and for other purposes.”
Interestingly, the West Virginia Senator told the West Virginia Roundtable Inc’s membership meeting that the study would not examine the “national security implications” but rather the “additional security benefits” of an Appalachian Storage Hub and cited the following to pave the way for the national security study he is proposing: “the shale resource endowment of the Appalachian Basin is so bountiful that, if the Appalachian Basin were an independent country, the Appalachian Basin would be the third largest producer of natural gas in the world.”
Senator Manchin is not the only politician of either party to unabashedly holler from the Appalachian Mountaintops the benefits of the ASH. Former Ohio Governor, and 2016 POTUS primary participant, John Kasich (R) has been a fervent supporter of such a regional planning scheme. He is particularly outspoken in favor of the joint proposal by Thailand-based PTT Global Chemical and Daelim to build an ethane cracker in Dilles Bottom, Ohio, across the Ohio River from Moundsville, West Virginia. The ethane cracker would convert the region’s fracked ethane into ethylene to make polyethylene plastic. This proposed project could be connected to the underground storage component of the ASH.
Dilles Bottom, OH ethane cracker site. Photo by Ted Auch, aerial assistance provided by LightHawk.
Not to be outdone in the ASH cheerleading department, West Virginia Governor Jim Justice (R), who can’t seem to find any common ground with Democrats in general nor Senator Manchin specifically, is collaborating with quad-state governors on the benefits of the ASH. All the while, these players ignore or dismiss the environmental, social, and economic costs of such an “all in” bet on petrochemicals and plastics.
Even the region’s land-grant universities have gotten in on the act, with West Virginia University’s Appalachian Oil and Natural Gas Research Consortium and Energy Institute leading the way. WVU’s Energy Institute Director Brian Anderson pointed out that, “Appalachia is poised for a renaissance of the petrochemical industry due to the availability of natural gas liquids. A critical path for this rebirth is through the development of infrastructure to support the industry. The Appalachian Storage Hub study is a first step for realizing that necessary infrastructure.”
utilize a new or significantly improved technology;
avoid, reduce or sequester greenhouse gases;
be located in the United States; and,
have a reasonable prospect of repayment.
This type of Public-Private Investment Program is central planning at its finest, in spite of the likelihood that the prospects of the ASH meeting the second and fourth conditions above are dubious at best (even if the project utilizes carbon capture and storage technologies).
Public-Private Investment Programs have a dubious past. In her book “Water Wars,” Vandana Shiva discusses the role of these programs globally and the involvement of institutions like the World Bank and International Monetary Fund:
“public-private partnerships”…implies public participation, democracy, and accountability. But it disguises the fact that the public-private partnership arrangements usually entail public funds being available for the privatization of public goods…[and] have mushroomed under the guise of attracting private capital and curbing public-sector employment.”
In response to the Department of Energy’s Title XVII largesse, Congresswoman Pramila Jayapal and Ilhan Omar introduced Amendment 105 in Rule II on HR 2740. According to Food and Water Watch, this amendment would restrict “the types of projects the Department of Energy could financially back. It would block the funding for ALL projects that wouldn’t mitigate climate change.”
The only condition of Department of Energy’s Title XVII loan program ASH is guaranteed to meet is the third (be located in the United States), but as we’ve already mentioned, the level of foreign money involved complicates the domestic facade.
Foreign involvement in the ASH lends credence to Senator Manchin’s and others’ concerns about where profits from the ASH will go, and who will be reaping the benefits of cheap natural gas. The fact that the ASH is being heavily backed by foreign money is the reason Senator Manchin raised an issue with the outsized role of state actors like Saudi Arabia and China as well as likely state-backed private investments like PTT Global Chemical’s. The Senator even cited how a potential $83.7 billion investment in West Virginia from China’s state-owned energy company, China Energy, would compromise “domestic manufacturing and national security opportunities.”
“Critical” infrastructure
With all of the discussion and legislation focused on energy and national security, many don’t realize the output of the ASH would be the production of petroleum-based products: mainly plastic, but also fertilizers, paints, resins, and other chemical products.
Bills like this and the not unrelated “critical infrastructure” bills being shopped around by the American Legislative Exchange Council will amplify the rural vs urban and local vs state oversight divisions running rampant throughout the United States. The reason for this is that yet another natural resource boom/bust will be foisted on Central Appalachia to fuel urban growth and, in this instance, the growth and prosperity of foreign states like China.
Instead of working night and day to advocate for Appalachia and Americans more broadly, we have legislation in statehouses around the country that would make it harder to demonstrate or voice concerns about proposals associated with the ASH and similar regional planning projects stretching down into the Gulf of Mexico.
Producing wells mapped
Impacts from the ASH and associated ethane cracker proposals will include but are not limited to: an increase in the permitting of natural gas wells, an increase in associated gas gathering pipelines across the Allegheny Plateau, and an exponential increase in the production of plastics, all of which are harmful to the region’s environment and the planet.
The production of the region’s fracked wells will determine the long-term viability of the ASH. From our reading of things, the permitting trend we see in Ohio will have to hit another exponential inflection point to “feed the beast” as it were. Figure 1 shows an overall decline in the number of wells drilled monthly in Ohio.
Figure 2, below it, shows the relationship between the number of wells that are permitted verse those that are actually drilled.
Figures 1. Monthly (in blue) and cumulative (in orange) unconventional oil and gas wells drilled in Ohio, January, 2013 to November, 2018
Figure 2. Permitted Vs Drilled Wells in Ohio, January, 2013 to November, 2018
That supply-demand on steroids interaction will likely result in an increased reliance on “super laterals” by the high-volume hydraulic fracturing industry. These laterals require 5-8 times more water, chemicals, and proppant than unconventional laterals did between 2010 and 2012.
Given this, we felt it critical to map not just the environmental impacts of this model of fracking but also the nuts and bolts of production over time. The map below shows the supply-demand links between the fracking industry and the ASH, not as discrete pieces or groupings of infrastructure, but rather a continuum of up and downstream patterns.
The current iteration of the map shows production values for oil, natural gas, and natural gas liquids, how production for any given well changes over time, and production declines in newer wells relative to those that were fracked at the outset of the region’s “Shale Revolution.” Working with volunteer Gary Allison, we have compiled and mapped monthly (Pennsylvania and West Virginia) and quarterly (Ohio)[2] natural gas, condensate, and natural gas liquids from 2002 to 2018.
This map includes 15,682 producing wells in Pennsylvania, 3,689 in West Virginia, and 2,064 in Ohio. We’ve also included and will be updating petrochemical projects associated with the ASH, either existing or proposed, across the quad-states including the proposed ethane cracker in Dilles Bottom, Ohio and the ethane cracker under construction in Beaver County, Pennsylvania, along with two rumored projects in West Virginia.
We will continue to update this map on a quarterly basis, will be adding Kentucky data in the coming months, and will be sure to update rumored/proposed petrochemical infrastructure as they cross our radar. However, we can’t be everywhere at once so if anyone reading this hears of legitimate rumors or conversations taking place at the county or township level that cite tapping into the ASH’s infrastructural network, please be sure to contact us directly at info@fractracker.org.
By Ted Auch, Great Lakes Program Coordinator, FracTracker Alliance with invaluable data compilation assistance from Gary Allison
Feature Photo: Ethane cracker plant under construction in Beaver County, PA. Photo by Ted Auch, aerial assistance provided by LightHawk.
[1] For a detailed analysis of the HVHF’s increasing resource demand and how lateral length has increased in the last decade the reader is referred to our analysis titled “A Disturbing Tale of Diminishing Returns in Ohio” Figures 12 and 13.
[2] Note: For those Bluegrass State residents or interested parties, Kentucky data is on its way!
https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2019/07/Cracker-Plant-2-scaled.jpg6831500Ted Auch, PhDhttps://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/2021-FracTracker-logo-horizontal.pngTed Auch, PhD2019-07-23 14:37:052021-04-15 14:56:27The Underlying Politics and Unconventional Well Fundamentals of an Appalachian Storage Hub
New maps show the build-out of oil and gas infrastructure that converts the upper Ohio River Valley’s fracked gas into petrochemical products
In 2004, Range Resources purchased land in Washington County, Pennsylvania and “fracked” the first well in the Marcellus Shale, opening the flood gates to a wave of natural gas development.
Since then, oil and gas companies have fracked thousands of wells in the upper Ohio River Valley, from the river’s headwaters in Pennsylvania, through Ohio and West Virginia, and into Kentucky.
Industry sold natural gas as a “bridge fuel” to renewable energy, but 15 years since the first fracked Marcellus well, it’s clear that natural gas is more of a barrier than a bridge. In fact, oil and gas companies are not bridging towards clean energy at all, but rather investing in the petrochemical industry- which converts fracked gas into plastic.
This article dives into the expanding oil, gas, and petrochemical industry in the Ohio River Valley, with six maps and over 16,000 data points detailing the build-out of polluting infrastructure required to make plastic and other petrochemical products from fossil fuels.
The petrochemical industry is expanding rapidly, with $164 billion planned for new infrastructure in the United States alone. Much of the build-out involves expanding the nation’s current petrochemical hub in the Gulf Coast, yet industry is also eager to build a second petrochemical hub in the Ohio River Valley.
The shale rock below the Ohio River Valley releases more than methane gas used for energy. Fracked wells also extract natural gas liquids (NGLs) which the petrochemical industry manufactures into products such as plastic and resins. Investing in the petrochemical industry is one way to capitalize on gases that would otherwise be released to the atmosphere via venting and flaring. As companies continue to spend billions more on drilling than they’re bringing in, many are looking towards NGLs as their saving grace.
These maps look at a two-county radius along the upper Ohio River where industry is most heavily concentrated.
Step 1. Extraction
The petrochemical lifecycle begins at the well, and there are a lot of wells in the Ohio River Valley. The majority of the natural gas produced here is extracted from the Marcellus and Utica Shale plays, which also contain “wet gas,” or NGLs, such as ethane, propane, and butane.
Rig in Greene County, PA. Photo by Ted Auch.
12,507
active, unconventional wells in the upper Ohio River Valley
Of particular interest to the petrochemical industry is the ethane in the region, which can be “cracked” into ethylene at high temperatures and converted into polyethylene, the most common type of plastic. The Department of Energy predicts that production of ethylene from ethane in the Appalachian Basin will reach 640,000 barrels a day by 2025 – that’s 20 times the amount produced in 2013.
In our first map, we attempted to show only active and unconventional (fracked) wells, a difficult task as states do not have a uniform definition for “unconventional” or “active.” As such, we used different criteria for each state, detailed below.
This map shows 12,660 wells, including:
12,507 shale oil and gas wells:
5,033 wells designated as “active” and “unconventional” in Pennsylvania
2,971 wells designated as “drilled,” “permitted,” or “producing,” and are drilled in the Utica-Point Pleasant and Marcellus Shale in Ohio
4,269 wells designated as “active” or “drilled” in the Marcellus Shale in West Virginia
234 wells designated as “horizontal” and are not listed as abandoned or plugged in Kentucky
153 Class II injection wells, which are used for the disposal of fracking wastewater
2 in Pennsylvania
101 in Ohio
42 in West Virginia
8 in Kentucky
The map also shows the Marcellus and Utica Shale plays, and a line demarcating the portions of these plays that contain higher quantities of wet gas. These wet gas regions are of particular interest to the petrochemical industry. Finally, the Devonian-Ohio Shale play is visible as you zoom in.
A vast network of pipelines transports the oil and gas from these wells to processing stations, refineries, power plants, businesses, and homes. Some are interstate pipelines passing through the region on their way to domestic and international markets.
A number of controversial pipeline projects cross the Ohio River Valley. Construction of the Mariner East II Pipeline is under criminal investigation, the Revolution Pipeline exploded six days after it came on line, protesters are blocking the construction of the Mountain Valley Pipeline, and the Atlantic Coast Pipeline is in the Supreme Court over permits to cross the Appalachian Trail.
Accurate pipeline data is not typically provided to the public, ostensibly for national security reasons. The result of this lack of transparency is that residents along the route are often unaware of the infrastructure, or whether or not they might live in harm’s way. While pipeline data has improved in recent years, much of the pipeline data that exists remains inaccurate. In general, if a route is composed of very straight segments throughout the rolling hills of the Upper Ohio River Valley, it is likely to be highly generalized.
The pipeline map below includes:
natural gas interstate and intrastate pipelines
8 natural gas liquid pipelines
7 petroleum product pipelines
3 crude oil pipelines
18 pipeline projects that are planned or under construction for the region, including 15 natural gas pipelines and 3 natural gas liquids pipelines. To view a spreadsheet of these pipelines, click here.
Pipelines transport oil and the natural gas stream to an array of facilities. Compressor stations and pumping stations aid the movement of the products through pipelines, while processing stations separate out the natural gas stream into its different components, including NGLs, methane, and various impurities.
At this step, a portion of the extracted fossil fuels are converted into sources of energy: power plants can use the methane from the natural gas stream to produce electricity and heat, and oil refineries transform crude oil into products such as gasoline, diesel fuel, or jet fuel.
A separate portion of the fuels will continue down the petrochemical path to be converted into products such as plastics and resins. Additionally, a significant portion of extracted natural gas leaks unintentionally as “fugitive emissions” (an estimated 2-3%) or is intentionally vented into the atmosphere when production exceeds demand.
This map shows 756 facilities, including:
29 petroleum and natural gas power plants
3 electric utilities
24 independent power producers
1 industrial combined heat and power (CHP) plant
1 industrial power producer (non CHP)
10 pumping stations, which assist in the transmission of petroleum products in pipelines
645 compressor stations to push natural gas through pipelines
21 gas processing plants which separate out NGLs, methane, and various impurities from the natural gas stream
46 petroleum terminals, which are storage facilities for crude and refined petroleum products, often adjacent to intermodal transit networks
3 oil refineries, which convert crude oil into a variety of petroleum-based products, ranging from gasoline to fertilizer to plastics
2 petroleum ports, which are maritime ports that process more than 200 short tons (400,000 pounds) of petroleum products per year
*A small portion of these facilities are proposed or in construction, but not yet built. Click on the facilities for more information.
After natural gas is extracted from underground, transported via pipeline, and separated into dry gas (methane) and wet gas (NGLs), its components are often pumped back underground for storage. With the expansion of the petrochemical industry, companies are eager to find opportunities for NGL storage.
Underground storage offers a steady supply for petrochemical manufacturers and allows industry to adapt to fluctuations in demand. A study out of West Virginia University identified three different types of NGL storage opportunities along the Ohio and Kanawha River valleys:
Mined-rock cavern: Companies can mine caverns in formations of limestone, dolomite, or sandstone. This study focused on caverns in formations of Greenbrier Limestone.
Salt cavern: Developing caverns in salt formations involves injecting water underground to create a void, and then pumping NGLs into the cavern.
Gas field: NGLs can also be stored in natural gas fields or depleted gas fields in underground sandstone reservoirs.
Above-ground tanks offer a fourth storage option.
Natural gas and NGL storage contains many risks. These substances are highly flammable, and accidents or leaks can be fatal. A historically industrialized region, the Ohio River Valley is full of coal mines, pipelines, and wells (including abandoned wells with unknown locations). All of this infrastructure creates passages for NGLs to leak and can cause the land above them to collapse. As many of these storage options are beneath the Ohio River, a drinking water supply for over 5 million people, any leak could have catastrophic consequences.
Furthermore, there are natural characteristics that make the geology unsuitable for underground storage, such as karst geological formations, prone to sinkholes and caves.
Notable Storage Projects
Appalachia Development Group LLC is heading the development of the Appalachia Storage & Trading Hub initiative, “a regional network of transportation, storage and trading of Natural Gas Liquids and chemical intermediates.” The company has not announced the specific location for the project’s storage component. Funding for this project is the subject of national debate; the company applied for a loan guarantee through a federal clean energy program, in a move that may be blocked by Congress.
Energy Storage Ventures LLC plans to construct the Mountaineer NGL Storage facility near Clarington, Ohio along the Ohio River. This facility involves salt cavern storage for propane, ethane, and butane. To supply the facility, the company plans to build three pipelines beneath the Ohio River: two pipelines (one for ethane and one for propane and butane) would deliver NGLs to the site from Blue Racer Natrium processing plant. A third pipeline would take salt brine water from the caverns to the Marshall County chlorine plant (currently owned by Westlake Chemical Corp).
The storage map below shows potential NGL storage sites to feed petrochemical infrastructure as well as natural gas storage for energy production:
Existing natural gas storage facilities:
3,012 natural gas storage wells
46 natural gas storage facilities, including 1 aquifer and 45 depleted gas fields
While conventional oil and gas extraction has occurred in the region for decades, and fracking for 15 years, the recent petrochemical build-out adds an additional environmental and health burdens to the Ohio River Valley. Our final map represents the facilities located “downstream” in the petrochemical process which convert fossil fuels into petrochemical products.
Polyethylene pellets, also called nurdles, manufactured by ethane crackers. Image source.
Ethane Crackers
Much of the petrochemical build-out revolves around ethane crackers, which convert ethane from fracked wells into small, polyethylene plastic pellets. They rely on a regional network of fracking, pipelines, compressor stations, processing stations, and storage to operate.
In 2017, Royal Dutch Shell began construction on the first ethane cracker to be built outside of the Gulf Coast in 20 years. Located in Beaver County, Pennsylvania, this plant is expected to produce 1.6 million tons of polyethylene plastic pellets per year. In the process, it will release an annual 2.2 million tons of carbon dioxide (CO2).
A second ethane cracker has been permitted in Belmont County, Ohio. Several organizations, including the Sierra Club, Center for Biological Diversity, FreshWater Accountability Project, and Earthworks have filed an appeal against Ohio EPA’s issuance of the air permit for the PTTGC Ethane Cracker.
The Shell Ethane Cracker, under construction in Beaver County, is expected to produce 1.6 million tons of plastic per year. Photo by Ted Auch, aerial assistance provided by LightHawk.
Methanol plants also convert part of the natural gas stream (methane) into feedstock for a petrochemical product (methanol). Methanol is commonly used to make formaldehyde, a component of adhesives, coatings, building materials, and many other products. In addition to methanol plants and ethane crackers, the map below also shows the facilities that make products from feedstocks, such as fertilizer (made from combining natural gas with nitrogen to form ammonia, the basis of nitrogen fertilizer), paints, and of course, plastic.
These facilities were determined by searching the EPA’s database of industrial sites using the North American Industry Classification System (NAICS).
In total, we mapped 61 such facilities:
2 methanol plants (both in construction)
3 ethane crackers (one in construction, one under appeal, and one uncertain project)
How are these facilities all connected? Our final map combines the data above to show the connections between the fossil fuel infrastructure. To avoid data overload, not all of the map’s features appear automatically on the map. To add features, view the map full screen and click the “Layers” tab in the top right tool bar.
The expansion of oil and gas infrastructure, in addition to the downstream facilities listed above, has rapidly increased in the last few years. According to the Environmental Integrity Project, regulatory agencies in these four states have authorized an additional 15,516,958 tons of carbon dioxide equivalents to be emitted from oil and gas infrastructure since 2012. That’s in addition to emissions from older oil and gas infrastructure, wells, and the region’s many coal, steel, and other industrial sites.
View the Environmental Integrity Project’s national map of emission increases here, which also includes permit documents for these new and expanding facilities.
The petrochemical build-out will lock in greenhouse gas emissions and plastic production for decades to come, ignoring increasingly dire warnings about plastic pollution and climate change. A recent report co-authored by FracTracker Alliance found that the greenhouse gas emissions across the plastic lifecycle were equivalent to emissions from 189 coal power plants in 2019 – a number that’s predicted to rise in coming years.
What does the petrochemical build out look like in the Ohio River Valley?
But it doesn’t have to be this way. The oil and gas industry’s plan to increase plastic manufacturing capacity is a desperate attempt to stay relevant as fracking companies “hemorrhage cash” and renewable energy operating costs beat out those of fossil fuels. Investing instead in clean energy, a less mechanized and more labor intensive industry, will offer more jobs and economic opportunities that will remain relevant as the world transitions away from fossil fuels.
In fact, the United States already has more jobs in clean energy, energy efficiency, and alternative vehicles than jobs in fossil fuels. It’s time to bring these opportunities to the Ohio River Valley and bust the myth that Appalachian communities must sacrifice their health and natural resources for economic growth.
People gather at the headwaters of the Ohio River to advocate for the sustainable development of the region. Add your voice to the movement advocating for People Over Petro by signing up for the coalition’s email updates today!
This data in this article are not exhaustive. FracTracker will be updating these maps as data becomes available.
By Erica Jackson, Community Outreach and Communications Specialist, FracTracker Alliance
https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2019/07/Beaver-Cracker-Plant-Feature-scaled.jpg6671500Erica Jacksonhttps://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/2021-FracTracker-logo-horizontal.pngErica Jackson2019-07-10 09:33:552022-02-15 10:54:51Mapping the Petrochemical Build-Out Along the Ohio River
The FracTracker Alliance tends to look mostly at the impacts of drilling, from violations affecting surface and ground water to forest fragmentation to neighbors breathing diesel exhaust near disposal wells. We also try to give residents tools to help predict where future activity will occur, but as this article details, such predictive tools can do little more than trail moving targets. To that end, we have taken a look into areas where gas production is high for unconventional wells in the state, which are likely sites of future development.
The Pennsylvania Department of Environmental Protection’s (DEP) Production Report is self-reported by the various operators active in the state. Unconventional wells generate a large quantity of natural gas, measured in thousands of cubic feet (Mcf), as well as limited amounts of oil and condensate, both of which are measured in 42 gallon barrels. In this analysis, we are only considering the gas production.
In the map above, you can click on any well to learn more about the production values, along with a variety of other information including the well’s formation and age. The age was calculated by counting days from the spud date to the end of the report cycle, March 31, 2019.
Top Average Gas Production by County – April 2018 to March 2019
County
Producing Wells
Avg. Production (Mcf)
Production Rank
Avg. Age of Producing Wells
Age Rank
Wyoming
251
1,269,156
1
5 Yr / 10 Mo / 4 Days
12
Sullivan
128
1,087,868
2
5 Yr / 2 Mo/ 24 Days
8
Allegheny
117
1,075,018
3
4 yr/ 2 Mo / 7 Days
2
Susquehanna
1,429
1,066,734
4
5 Yr / 6 Mo / 22 Days
10
Greene
1,131
796,755
5
5 yr / 10 Mo / 28 Days
13
Figure 1 – This table shows the top five counties in Pennsylvania for per-well unconventional gas production. The final column shows the county ranking for the average age of wells, from youngest to oldest
We can also see this data summarized by county, where average production and age values are available on a county by county basis (see Figure 1). Hydrocarbon wells are known to decrease production steeply over time, a phenomenon known as the decline curve, so it is not surprising to see a relatively young inventory of wells represented in the list of top five counties with per-well gas production. Age is not the only factor in production values, however, as certain geographies simply contain more accessible gas resources than others.
Figure 2 – 12 month gas production and age of well. Production is usually much higher during the earliest phases of the well’s production life. This does not include wells that have been plugged or taken out of production. Click on image for full-sized view.
In Figure 2, we look at the production of all unconventional wells in the state, expecting to see the highest production in younger wells. This mostly appears to be the case, but as mentioned above, there are also hot and cold spots with respect to production. A notable variable in this consideration is producing formation.
Since 93% (8,730 out of 9,404) of unconventional wells reporting gas production are in the Marcellus Shale Formation, the traditional hot spots in the northeastern and southwestern portions of the state heavily skew the overall totals in terms of both production and number of wells. Other formations of note include the Onodaga Limestone (137 wells, 1.5% of total), Burket Member (117 wells, 1.2%), Genesee Formation (104 wells, 1.1%), and the Utica Shale (99 wells, 1.1%) (Figure 3).
Figure 3 – Unconventional gas production over 12 months, showing formation. Click on image for full-sized view.
Drillers have been exploring some of these formations for decades. In fact, the oldest producing well that is currently classified as unconventional was 13,435 days old as of March 31, which works out to 36 years, 9 months, and 12 days.
However, this is fairly rare – only 384 (4%) of the 9,404 producing wells were more than 10 years old. 5,981 wells (64%) are between 5 and 10 years old, with the remaining 3,039 wells (32%) younger than 5 years old.
This does not take into account wells of any age that have been plugged or otherwise taken out of production.
Age of Pennsylvania’s active wells
< 5 years old
5-10 years old
> 10 years old
Utica Shale
The Utica Shale is worth a special mention here for a couple of reasons. First, we must acknowledge its prominence in neighboring Ohio, which has 2,160 permitted Utica wells to go with just 40 permitted Marcellus wells, the prevalence of the two plays seems to invert just as one passes over the state line. And yet, the most productive Utica wells are near the border with New York, not Ohio.
In fact, each of the top 11 producing Utica wells during the 12 month period were located in Tioga County. It’s worth noting that these are all between one and two years old, which would have given the wells time to be drilled, fracked, and brought into production, while still being in the prime of their production life. Compared to the Marcellus, sample size quickly becomes an issue when analyzing the Utica in Pennsylvania (Figure 4).
Figure 4 – Producing Utica wells in Pennsylvania. Note that the cluster of heavily producing wells in Tioga and Potter Counties near the New York border are mostly young wells where higher production would be expected. Click on image for full sized view.
Second, portions of the Utica are known for their wet gas content, meaning that the gas has significant quantities of natural gas liquids (NGLs) including ethane, propane, and butane, which are gaseous at ambient temperatures but typically condensed into liquid form by oil and gas companies. These are used for specialized fuels and petrochemical feedstocks, and are therefore more valuable than the methane in natural gas.
The production report does not capture the amount of NGLs in the gas, but a map from the Energy Information Administration shows the entire play, noting that the composition is dryer on the eastern portions of the play. In fact, a wet gas composition along the Ohio border might help to explain continued interest in what are otherwise well below average gas production results for Pennsylvania.
A Moving Target
It is difficult to predict where the industry will focus its attention in the coming months and years, but taking a look at production and formation data can give us a few clues. Obviously, operators who found a particularly productive pocket of hydrocarbons are likely to keep drilling more holes in the ground in those areas until production is no longer profitable. Therefore, impacts to water, air, and nearby residents can be expected to continue in heavily drilled areas largely because the production level makes it attractive for drillers.
On the other hand, we should not assume that areas that are currently not productive are off the table for future consideration, either. Different formations are productive in different geographies, so a sweet spot for the Marcellus might be a dud in the Utica, or vice versa.
Finally, when comparing production, we must always take the age of the well into consideration, as all oil and gas wells can be expected to start off with a short period of very high production, followed by years of ever-diminishing returns throughout the expected 10 to 11 year lifecycle of the well. Because of this, what seems like a hotspot now may look below average in a similar analysis in three to four years, particularly in formations with relatively light drilling activity. This means that the top list of production by well could change over time, so be sure to check back in with FracTracker to see how events unfold.
By Matt Kelso, Manager of Data and Technology, FracTracker Alliance
https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2019/06/Washington-County-Rig-2-scaled.jpg6671500Matt Kelso, BAhttps://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/2021-FracTracker-logo-horizontal.pngMatt Kelso, BA2019-06-10 12:07:422021-04-15 14:56:30Production and Location Trends in PA: A Moving Target
In March of 2019, two and a half years after Shell Pipeline Co. announced plans for the Falcon Ethane Pipeline System, the imported pipes arrived at the Port of Philadelphia. As tree clearing and construction begins, we share frustration with residents that the project is underway while many of our concerns remain unaddressed.
Between 2010 and 2018, over 280 pipeline incidents were reported in Ohio, West Virginia, and Pennsylvania (the three states the Falcon crosses). Of those incidents, 70 were fires and/or explosions. As regulatory agencies and operators fail to protect the public, communities are taking the reins.
Residents of southwest PA gather along the Falcon route
These grassroots efforts are contributing to a shift in public perception about the safety and need of pipelines. In some cases, including with the Northeast Energy Direct Pipeline and the Constitution Pipeline, organizing efforts are helping stop projects before they begin.
We invite all residents along the Falcon route to get involved in ongoing efforts to monitor construction. Below, you’ll find a guide to reporting violations as well as high-risk areas along the Falcon route that require close monitoring.
Be a citizen watchdog
Taking photos of pipeline development and recording your observations is a great way to monitor impacts. One tool to use while monitoring is the FracTracker mobile app (search “FracTracker” in the App Store or Google Play to download for free). The app allows the public to submit geolocated photos and descriptions of development, such as pipelines and wells, and concerns, such as spills and noise pollution. These reports help FracTracker crowdsource data and alert us to concerns that need follow up action. The app also contains a map of wells, pipelines, and compressor stations, including the Falcon pipeline route for reference in the field.
Click on the images below to view app reports of Falcon construction.
Documenting violations
During the construction phase, incidents often occur when companies cause erosion of the ground and release sediment, equipment, or discharge into waterways. Mountain Watershed Association and Clean Air Council have provided the following information on the process of looking for and documenting violations.
Step 1) Document baseline conditions. Documenting the pre-construction status of an area is crucial for understanding how it’s been impacted down the road. Document baseline conditions by taking photos, videos, and notes at different sites, and include the location and date on these materials (the Fractracker app does this for you automatically). Observing sites at different times and in different weather (such as during or after a storm) will give you the best data.
Step 2) Know what to look for. Below are images and descriptions of common construction violations.
4) Contact support organizations. There are several organizations ready to take action once violations have been confirmed. For confirmed violations in Beaver County, PA, contact Alex Bomstein, at the Clean Air Council (215-567-4004 x118) and for confirmed violations in Allegheny or Washington Counties, PA, contact Melissa Marshall at the Mountain Watershed Association (724-455-4200 x7#). For violations in Ohio or West Virginia, reach out to FracTracker (412-802-0273).
Reports made on the FracTracker App are shared with any app user and the FracTracker team, who look through the reports and contact users for any required follow up. App reports can also be submitted to regulatory agencies electronically. Simply visit the web version of the app, click on your report, and copy the URL (web address) of your report. Then “paste” it into the body of an email or online complaint form. The receiver will see the exact location, date, and any notes or photos you included in the report.
Where should you be monitoring?
Monitoring efforts must be limited to publicly accessible land. In general, areas that are most at-risk for environmental impact include stream and wetland crossings, steep slopes (particularly those near water crossings), flood-prone zones, and areas where storm water runoff will reach waterways. View a map of the Falcon’s water crossings here, and continue reading for more vulnerable locations to monitor.
The information below identifies high-risk areas along the pipeline route where monitoring efforts are extra necessary due to their impacts on drinking water, wetlands, undermined areas, and vulnerable species.
Drinking Water
We found 240 private water wells within 1/4 mile of the Falcon.
While all of these wells should be assessed for their level of risk with pipeline construction, the subset of wells nearest to horizontal directional drilling (HDD) sites deserve particular attention. HDD is a way of constructing a pipeline that doesn’t involve digging a trench. Instead, a directional drilling machine is used to drill horizontally underground and the pipe is pulled through.
While an HDD is designed to avoid surface impacts, if rushed or poorly executed, it can damage surface water, groundwater, and private property. The Mariner East 2 pipeline construction left several families without water after construction crews punctured an aquifer at an HDD site.
Shell’s data highlights 24 wells that are within 1,000 feet of a proposed HDD site.
We’ve isolated the groundwater wells and HDDs in a standalone map for closer inspection below. The 24 most at-risk wells are circled in blue.
Testing your groundwater quality before construction begins is crucial for determining impacts later on. Two upcoming workshops in Washington County, PA and another in Beaver County, PA will discuss how to protect your water and property.
The Falcon’s HDD locations offer disturbing similarities to what caused the Mariner East pipeline spills. Many of Sunoco’s failures were due to inadequately conducted (or absent) geophysical surveys that failed to identify shallow groundwater tables, which then led to drilling mud entering streams and groundwater.
Figure 1 below shows Greene Township, Beaver County, just south of Hookstown, where the “water table depth” is shown. The groundwater at this HDD site averages 20ft on its western side and only 8ft deep on the eastern side.
Figure 1. Water table depth in Greene Township
Water Reservoirs
The Falcon also crosses the headwaters of two drinking water reservoirs: the Tappan Reservoir in Harrison County, OH (Figure 2) and the Ambridge Reservoir in Beaver County, PA (Figure 3). The Falcon will also cross the raw water line leading out of the Ambridge Reservoir.
The Ambridge Reservoir supplies water to five townships in Beaver County (Ambridge, Baden, Economy, Harmony, and New Sewickley) and four townships in Allegheny County (Leet, Leetsdale, Bell Acres & Edgeworth). The Tappan Reservoir is the primary drinking water source for residents in Scio.
Figure 2. Tappan Reservoir and the Falcon route in Harrison County, Ohio
Figure 3. Ambridge Reservoir and the Falcon route in Beaver County, Pennsylvania
Wetlands
Wetlands that drain into Raccoon Creek in Beaver County, PA will be particularly vulnerable in 2 locations. The first is in Potter Township, off of Raccoon Creek Rd just south of Frankfort Rd, where the Falcon will run along a wooded ridge populated by half a dozen perennial and intermittent streams that lead directly to a wetland, seen in Figure 4. Complicating erosion control further, Shell’s survey data shows that this ridge is susceptible to landslides. This area is also characterized by the USGS as having a “high hazard” area for soil erosion.
Figure 4. Wetlands and streams in Potter Township, PA
The other wetland area of concern along Raccoon Creek is found in Independence Township at the Beaver County Conservation District (Figure 5). Here, the Falcon will go under the Creek using HDD (highlighted in bright green). Nevertheless, the workspace needed to execute the crossing is within the designated wetland itself. An additional 15 acres of wetland lie only 300ft east of the crossing but are not accounted for in Shell’s data. This unidentified wetland is called Independence Marsh, considered the crown jewel of the Independence Conservancy’s watershed stewardship program.
Figure 5. Wetlands and Raccoon Creek in Independence Township, PA
Subsurface concerns
Shell’s analysis shows that 16.8 miles of the Falcon pipeline travel through land that historically has or currently contains coal mines. Our analysis using the same dataset suggests the figure is closer to 20 miles. Construction through undermined areas poses a risk for ground and surface water contamination and subsidence.
Of these 20 miles of undermined pipeline, 5.6 miles run through active coal mines and are located in Cadiz Township, OH (Harrison Mining Co. Nelms Mine, seen in Figure 6); Ross Township, OH (Rosebud Mining Co. Deep Mine 10); and in Greene Township, PA (Rosebud Mining Co. Beaver Valley Mine).
Figure 6. Coal mines and are located in Cadiz Township, OH
More than 25 of the Falcon’s 97 pipeline miles will be laid within karst landscapes, including 9 HDD sites. Karst is characterized by soluble rocks such as limestone prone to sinkholes and underground caves. A cluster of these are located in Allegheny and Washington counties, PA, with extensive historical surface mining operations.
The combination of karst and coal mines along Potato Garden Run, in Figure 7, make this portion of the pipeline route particularly risky. At this HDD site, the Falcon will cross a coal waste site identified in the permits as “Imperial Land Coal Slurry” along with a large wetland.
Figure 7. Coal mines in Imperial, Pennsylvania
Vulnerable species
Southern Redbelly Dace
The Southern Redbelly Dace, a threatened species, is especially vulnerable to physical and chemical (turbidity, temperature) changes to their environment. PA Fish and Boat Commission explicitly notes in their correspondence with Shell that “we are concerned about potential impacts to the fish, eggs and the hatching fry from any in-stream work.” Of note is that these sites of concern are located in designated “High Quality/Cold Water Fishes” streams of the Service Creek watershed (Figure 8). PFBC stated that that no in-stream work in these locations should be done between May 1 and July 31.
Figure 8. “High Quality/Cold Water Fishes” streams identified as habitat for the Southern Redbelly Dace
Northern Harriers & Short-Eared Owls
Portions of the Falcon’s workspace are located near 6 areas with known occurrences of Short-eared Owls (PA endangered species) and Northern Harriers (PA threatened species). Pennsylvania Game Commission requested a study of these areas to identify breeding and nesting locations, which were executed from April-July 2016 within a 1,000-foot buffer of the pipeline’s workspace (limited to land cover areas consisting of meadows and pasture). One Short-eared Owl observation and 67 Northern Harrier observations were recorded during the study. PGC’s determined that, “based on the unusually high number of observations at these locations” work should not be done in these areas during harrier breeding season, April 15 through August 31.
Figure 9. Surveyed areas for Short-eared Owls (PA endangered species) and Northern Harriers (PA threatened species)
Bald Eagles
A known Bald Eagle nest is located in Beaver County. Two potential “alternate nests” are located where the Falcon crosses the Ohio River. National Bald Eagle Management Guidelines bar habitat disturbances that may interfere with the ability of eagles to breed, nest, roost, and forage. The 1 active nest in close proximity to the Falcon, called the Montgomery Dam Nest, is located just west of the pipeline’s terminus at Shell’s ethane cracker facility.
U.S. Fish and Wildlife Service requested that Shell only implement setback buffers for the one active nest at Montgomery Dam (Figure 10). These include no tree clearing within 330 feet, no visible disturbances with 660 feet, and no excessive noise with 1,000 feet of an active nest. Furthermore, Shell must avoid all activities within 660ft of the nest from January 1st to July 31st that may disturb the eagles, including but not limited to “construction, excavation, use of heavy equipment, use of loud equipment or machinery, vegetation clearing, earth disturbance, planting, and landscaping.
Figure 10. Bald Eagle nest in Potter Township, Pennsylvania
Bats
The Falcon is located within the range of federally protected Indiana Bats and Northern Long-eared Bats in Pennsylvania and West Virginia. In pre-construction surveys, 17 Northern Long-eared Bats were found at 13 of the survey sites, but no Indiana Bats were captured.
A total of 9 Northern Long-eared Bat roost trees were located, with the nearest roost tree located 318 feet from the pipeline’s workspace. Figure 11 below shows a cluster of roost trees in Raccoon Township, PA. For a map of all the roost trees, click here. The U.S. Fish and Wildlife Service stated that “Due to the presence of several Northern Long-eared Bat roost trees within the vicinity of the project footprint (although outside of the 150-foot buffer), we recommend the following voluntary conservation measure: No tree removal between June 1 and July 31.”
The Pennsylvania Game Commission noted in early correspondences that Silver-haired Bats may be in the region (a PA species of special concern). PGC did not require a further study for the species, but did request a more restrictive conservation of no tree clearing between April 1 and October 31.
Figure 11. Northern long-eared bat roost trees in Raccoon Township, Pennsylvania
For more information on the wildlife impacts of the Falcon Pipeline, click here.
By documenting the impacts of the Falcon Pipeline, you’re contributing to a growing body of work that shows the risks of fossil fuel pipelines. Not only does this evidence protect drinking water and vulnerable species, it serves as evidence against an inherently dangerous project that will contribute to climate change and the global plastics crisis.
We hope you’re inspired to take action and add your voice to a growing team in the region committed to safer and healthier environments. Thank YOU for your dedication to the cause!
By Erica Jackson, Community Outreach and Communications Specialist, FracTracker Alliance.
Portions of this article were adapted from previous posts in the Falcon Public EIA Project, written by Kirk Jalbert.
https://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2019/05/PipelineConstructionFeature.png6671500Erica Jacksonhttps://www.fractracker.org/a5ej20sjfwe/wp-content/uploads/2021/04/2021-FracTracker-logo-horizontal.pngErica Jackson2019-05-08 08:27:302021-04-15 14:56:31The Falcon Public Monitoring Project
Photo by Ted Auch, FracTracker Alliance
What does the petrochemical build out look like in the Ohio River Valley?
Taking photos of pipeline development and recording your observations is a great way to monitor impacts. One tool to use while monitoring is the 
We found 240 private water wells within 1/4 mile of the Falcon.
