1) Gas well drilling produces large volumes of wastewater that can potentially contaminate nearby private water supplies if not properly managed. The wastewater contains high levels of salts like sodium and chloride as well as metals and organic compounds.
2) Contamination of private water supplies from gas drilling has occurred but is relatively uncommon, with over 95% of complaints found to be unrelated to drilling activities. A study in Pennsylvania found around 3-5% of private wells near gas drilling operations exceeded standards for certain contaminants.
3) Regulations require gas well operators to obtain permits addressing drilling, construction, and abandonment practices to protect water resources. Strict adherence to regulations has likely reduced contamination risks compared to older drilling methods
Flow-Assurance Challenges in Gas-Storage Schemes in Depleted Reservoirs
This article, written by Senior Technology Editor Dennis Denney, contains highlights of paper SPE 146239, "Flow-Assurance Challenges in Gas-Storage Schemes in Depleted Reservoirs," by Alireza Kazemi, SPE, and Bahman Tohidi, SPE, Hydrafact Ltd., and Emile Bakala Nyounary, Heriot-Watt University, prepared for the 2011 SPE Offshore Europe Oil and Gas Conference and Exhibition, Aberdeen, 6–8 September.
Duke Study: Methane contamination of drinking water accompanying gas-well dri...Marcellus Drilling News
Study of 68 water wells in Pennsylvania and New York showing a link between shale gas drilling and higher levels of methane in nearby well water supplies.
The document summarizes the Air Force's efforts to expand its groundwater treatment system at the former McClellan Air Force Base to contain and clean up contaminated groundwater. Key points:
1) The Air Force is completing installation of six new groundwater extraction wells as part of the Phase III expansion program to fully capture and contain contaminated groundwater within base boundaries.
2) The expanded system will include over 100 extraction wells and be able to treat 2,000 gallons of water per minute when complete.
3) Low-flow pumps are being installed in monitoring wells to improve groundwater sampling, saving both time and money compared to prior methods.
4) The Air Force signed an agreement to transfer nearly 97 acres
Update on Hydraulic Fracturing:Preparing for Gasland 2Now Dentons
In this presentation, FMC Law's Alex MacWilliam discusses hydraulic fracturing. The presentation covers the hydraulic fracturing process; the legislative and regulatory management of key issues related to hydraulic fracturing; liability issues in fracturing litigation; finally, lessons and trends related to hydraulic fracturing.
Revised and new drilling regulations, what is known as Chapter 78 of the 1984 Oil and Gas Act, in Pennsylvania. The revision process started in 2011. It separates drilling rules into conventional and unconventional. The drilling industry says the rules will cost drillers billions each year without a corresponding benefit for the environment or safety. The new rules will be adopted in mid-2016 if they are not challenged in court.
A proposed "final" version of changes to PA's Chapter 78 (Conventional) and Chapter 78a (unconvetional/shale) drilling rules and regulations, made by the Dept. of Environmental Protection. Newly elected Gov. Tom Wolf and his Sec. of the DEP John Quigley have reworked what was a final version of the rules to put their own stamp on the drilling industry in the state. The newly revised rules are opposed by the Marcellus industry as unnecessary and overly burdensome.
Independent Review of Hydrological Issues: Deloro Mine SiteLOWaterkeeper
This document provides a 3-page summary of an independent hydrogeological review of the Deloro Mine Site remediation activities:
- It describes the site location, geology, hydrogeology, and history of mining and contamination by arsenic and low-level radioactive waste.
- It outlines the remediation completed in the Industrial and Mine Area (IMA) and Tailings Area (TA), including waste consolidation and capping. It describes ongoing remediation in the Young's Creek Area (YCA).
- It evaluates the containment of radiological wastes, groundwater monitoring, and the merits of the MOECC's application to amend its nuclear license for ongoing oversight of remediation
Swim Drink Fish Canada submission for relicensing written hearing for the Del...LOWaterkeeper
The Ministry of Environment and Climate Change (MOECC) is currently applying to renew its Waste Nuclear Substance Licence for the Deloro site until 2022. The current licence will expire on October 31, 2017. Here's are findings and recommendations on the matter.
Flow-Assurance Challenges in Gas-Storage Schemes in Depleted Reservoirs
This article, written by Senior Technology Editor Dennis Denney, contains highlights of paper SPE 146239, "Flow-Assurance Challenges in Gas-Storage Schemes in Depleted Reservoirs," by Alireza Kazemi, SPE, and Bahman Tohidi, SPE, Hydrafact Ltd., and Emile Bakala Nyounary, Heriot-Watt University, prepared for the 2011 SPE Offshore Europe Oil and Gas Conference and Exhibition, Aberdeen, 6–8 September.
Duke Study: Methane contamination of drinking water accompanying gas-well dri...Marcellus Drilling News
Study of 68 water wells in Pennsylvania and New York showing a link between shale gas drilling and higher levels of methane in nearby well water supplies.
The document summarizes the Air Force's efforts to expand its groundwater treatment system at the former McClellan Air Force Base to contain and clean up contaminated groundwater. Key points:
1) The Air Force is completing installation of six new groundwater extraction wells as part of the Phase III expansion program to fully capture and contain contaminated groundwater within base boundaries.
2) The expanded system will include over 100 extraction wells and be able to treat 2,000 gallons of water per minute when complete.
3) Low-flow pumps are being installed in monitoring wells to improve groundwater sampling, saving both time and money compared to prior methods.
4) The Air Force signed an agreement to transfer nearly 97 acres
Update on Hydraulic Fracturing:Preparing for Gasland 2Now Dentons
In this presentation, FMC Law's Alex MacWilliam discusses hydraulic fracturing. The presentation covers the hydraulic fracturing process; the legislative and regulatory management of key issues related to hydraulic fracturing; liability issues in fracturing litigation; finally, lessons and trends related to hydraulic fracturing.
Revised and new drilling regulations, what is known as Chapter 78 of the 1984 Oil and Gas Act, in Pennsylvania. The revision process started in 2011. It separates drilling rules into conventional and unconventional. The drilling industry says the rules will cost drillers billions each year without a corresponding benefit for the environment or safety. The new rules will be adopted in mid-2016 if they are not challenged in court.
A proposed "final" version of changes to PA's Chapter 78 (Conventional) and Chapter 78a (unconvetional/shale) drilling rules and regulations, made by the Dept. of Environmental Protection. Newly elected Gov. Tom Wolf and his Sec. of the DEP John Quigley have reworked what was a final version of the rules to put their own stamp on the drilling industry in the state. The newly revised rules are opposed by the Marcellus industry as unnecessary and overly burdensome.
Independent Review of Hydrological Issues: Deloro Mine SiteLOWaterkeeper
This document provides a 3-page summary of an independent hydrogeological review of the Deloro Mine Site remediation activities:
- It describes the site location, geology, hydrogeology, and history of mining and contamination by arsenic and low-level radioactive waste.
- It outlines the remediation completed in the Industrial and Mine Area (IMA) and Tailings Area (TA), including waste consolidation and capping. It describes ongoing remediation in the Young's Creek Area (YCA).
- It evaluates the containment of radiological wastes, groundwater monitoring, and the merits of the MOECC's application to amend its nuclear license for ongoing oversight of remediation
Swim Drink Fish Canada submission for relicensing written hearing for the Del...LOWaterkeeper
The Ministry of Environment and Climate Change (MOECC) is currently applying to renew its Waste Nuclear Substance Licence for the Deloro site until 2022. The current licence will expire on October 31, 2017. Here's are findings and recommendations on the matter.
This document summarizes a study that evaluated water quality in 100 private drinking water wells located near natural gas extraction sites in the Barnett Shale Formation in North Texas. The study found that some wells located within 3 km of active gas wells contained levels of arsenic, selenium, strontium and total dissolved solids that exceeded EPA limits. Lower levels of these constituents were found in wells further than 3 km from gas sites and in areas without gas extraction. Methanol and ethanol were also detected in 29% of samples. Contaminant levels did not show a clear spatial pattern and could be due to various factors like mobilizing of natural materials, changes to the water table, or industrial accidents.
The Balangero asbestos open pit mine, located 35km NW of Torino (Italy), was the largest operation of this kind in Western Europe. The dry tailings were lifted by a conveyor belt from the mill and dumped over a natural slope with an approximate angle of 25 degrees, progressively reaching a maximum thickness estimated at 80 m.
By the '80s the dump was deeply scarred by various local and large scale instabilities, to the point that houses located at the toe, on the opposite side of the valley, were evacuated.
The award winning restoration project used a multidisciplinary approach including hydraulics, geotechnical, pedological and risk engineering to yield a well balanced and sustainable solution. This paper illustrates the Risk Based Decision Making (RBDM) process used through the feasibility, design and construction follow-up of the environmental restoration of the 60 Mm3 dry Balangero asbestos tailings dump.
The slopes were hit by storm Quinn and Medicane Rolf and came out unscathed. That was after surviving heavy summer storms in 2010 and 2011.
Testing and Implementation of AMD Mitigation, Alum Gulch-Flux Canyon, Cox Gul...Daniel Eyde
The document summarizes a plan to mitigate acid mine drainage (AMD) and heavy metals in several tributaries in southeastern Arizona that flow into Sonoita Creek and Patagonia Lake. The plan involves installing gabion retaining wall structures and stream bed footers containing zeolite materials downstream of mine discharge points to raise pH and reduce metals like zinc, cadmium, lead, and copper. Water quality and biological monitoring will occur before and after installation to evaluate effectiveness. Zeolites are effective at absorbing metals and raising pH, as shown in previous studies. The structures are intended to last 5-10 years before material replacement depending on runoff conditions.
Hydrogeochemistry and Microbiology of Wadi Al Bih Limestone Aquifer in Northe...QUESTJOURNAL
ABSTRACT: This study investigated the hydrogeochemical characteristics and microbiological pollution of groundwater in Wadi Al Bih limestone aquifer, Ras Al Khaimah area, northern United Arab Emirates (UAE). Results indicate that the decrease of groundwater exploitation in Wadi Al Bih basin from 58 million cubic meter (MCM) during the period 1991-1995 to 22 MCM during the period 2011-2015, has increased groundwater storage, raised hydraulic heads by 1 m in Al Burayrat area and 16 m near Wadi Al Bih main dam, and decreased the average groundwater salinity by 30% in Wadi Al Bih well field and 45% in Al Burayrat well field. Results of chemical analyses showed noticeable fluctuations in groundwater temperature, EC, and TDS contents, rather than concentrations of all ions. The November 2014 and June 2015 isosalinity contour maps indicate that the groundwater salinity increases from east to west, in the direction of groundwater flow. The groundwater in the eastern part of Wadi Al Bih is good for domestic purposes and irrigation. However, the water hardness is high because the aquifer is predominantly composed of limestone. Wadi Al Bih limestone aquifer is highly sensitive to urban and agricultural activities, and several well were recorded to have Coliform bacteria in Wadi Al Bih and Al Burayrat areas
The waterway and erosion management plan at the Arlington Agricultural Research Station organic fields requires improvements. Significant erosion is occurring due to steep slopes and intensive tillage. Some fields exceed the tolerable soil loss rate of 5 tons/acre/year. A HydroCAD model showed the existing waterway can convey 10-year storm flows. Recommendations include strip cropping, terracing problem fields, and diverting flows around a gullying area. Terraces will be installed in two fields to reduce slopes and soil loss to under 5 tons/acre/year.
This document outlines the guidelines for constructing check dams in order to provide drinking water facilities and groundwater recharge. It discusses the objectives of check dams, selection criteria for areas to implement check dams, types of check dams, design aspects, implementation arrangements, operation and maintenance responsibilities, funding arrangements, institutional arrangements for management, and monitoring mechanisms. Check dams are constructed across small rivers and streams to reduce water flow during monsoons and allow water to seep into the soil.
Lake Manzala Engineered Wetland, Port Said, Egypt [IWC4 Presentation]Iwl Pcu
Presentation during the focused learning discussion on Constructed Wetlands at the 4th GEF Biennial International Waters Conference.
Dr. Dia El Din El-Quosy
Project Manager
E-mail: lmewp@menanet.net
Lake Manzala Engineered Wetland Project
This document summarizes a study that measured 222Rn activity levels in 198 groundwater wells in southern Quebec, Canada. The goals were to examine the relationship between 222Rn levels and local geology/hydrogeology and to estimate potential health risks. Most wells showed low 222Rn activities below 100 Bq/L, the WHO limit for groundwater. Higher levels up to 310 Bq/L were found in wells tapping the Appalachian Mountains and Mont-Saint-Hilaire intrusion, known U-rich areas. 222Rn levels seemed related to lithological differences between more U-rich metasediments and magmatic intrusions versus carbonaceous silty shales. Radon was slightly enriched
Case Studies: Treatment of Acid Mine and Metal Contaminated Waters Using Zeol...Daniel Eyde
The Presentation presents case studies using zeolites in the treatment of acid mine and metal contaminated waters at Coal Operations in WV, & Legacy Mine Water Discharges at Uranium, Gold and Silver Operations in NM, MT and AZ
This document summarizes a study conducted by undergraduate geology students at Fort Lewis College analyzing water quality data from the Gold King Mine spill. The students:
1) Compared water quality data from EPA samples to their own samples collected along the Animas River after the spill.
2) Created a 3D model of the Gold King Mine underground workings to investigate possible connections explaining high discharge volumes.
3) Presented their comparative analysis and findings to the public to provide a more complete understanding of the mine and varying metal concentrations in streams.
This document summarizes a study on stormwater impacts to McVicar Creek. The study aimed to: identify impacts; characterize them through a stream assessment; identify 3 representative sites; pursue further research; and develop remediation recommendations. The initial assessment identified 3 sites - Court Street, Castlegreen, and County Fair - for further study. Additional data collection and stakeholder workshops were held. The workshops developed stormwater management objectives and site-specific recommendations. For Court Street, increased enforcement and education were recommended. For Castlegreen, investigating infrastructure and partnering with local groups. For County Fair, educating landowners and considering end-of-pipe solutions were recommended. The final recommendations emphasized objectives and further stakeholder
The "Findings Statement" issued by the New York State Dept. of Environmental Conservation that supplies the faulty thinking and irrational rationale for banning fracking in the Empire State. The ban is temporary--until a new governor and head of DEC are in place (hopefully at the next election). The Findings Statement is a pathetic attempt to paper over political motivations for a frack ban. It contains broad, sweeping and unsubstantiated by any evidence statements that denigrate the miracle of fracking. It is, in a word, pathetic.
International Journal of Engineering Research and Development (IJERD)IJERD Editor
journal publishing, how to publish research paper, Call For research paper, international journal, publishing a paper, IJERD, journal of science and technology, how to get a research paper published, publishing a paper, publishing of journal, publishing of research paper, reserach and review articles, IJERD Journal, How to publish your research paper, publish research paper, open access engineering journal, Engineering journal, Mathemetics journal, Physics journal, Chemistry journal, Computer Engineering, Computer Science journal, how to submit your paper, peer reviw journal, indexed journal, reserach and review articles, engineering journal, www.ijerd.com, research journals,
yahoo journals, bing journals, International Journal of Engineering Research and Development, google journals, hard copy of journal
IRJET- Index And Engineering Properties of Residual Tropical Soils of Sou...IRJET Journal
This document summarizes a study that investigated the engineering properties of soils in Konso town, Ethiopia. Eight test pits were dug and soil samples were collected and tested in the lab to determine their physical, index, shear strength, and consolidation properties. The dominant soil type was found to be silty clay (MH) based on grain size analysis and Atterberg limits tests. Properties tested included moisture content, plasticity index, clay fraction, free swell, specific gravity, shear strength parameters, and unconfined compression strength. The results showed that the soils generally had moderate to high expansiveness based on free swell tests. Proper handling and testing methods are needed when evaluating properties of residual tropical soils.
This document investigates co-locating a desalination plant with the Joslin Steam Electric Station in Point Comfort, Texas to provide a drought-proof water supply for regions L and N. A reverse osmosis desalination plant is proposed that would treat 180 million gallons per day of seawater to produce 90 million gallons per day of drinking water and reject hypersaline water. Reject water and solids from pretreatment would be returned through the existing plant discharge. Environmental impacts were found to be minimal. The estimated cost of the desalinated water is $1.75 per 1000 gallons. Combining this supply with 100,000 acre-feet of existing surface water supply would provide 200,000 acre-feet
Ben Barton has over 9 years of experience in environmental consulting, specializing in contaminated site assessment and remediation, spill response, and environmental monitoring. He has managed over 60 Phase I environmental site assessments, 50 Phase II and III assessments of sites such as gas stations, industrial operations, and First Nation lands. Mr. Barton has also directed the remediation of numerous contaminated sites using methods like excavation, in-situ injection, and pump and treat systems. He is the team lead for Tetra Tech's GeoEnvironmental group in Whitehorse, Yukon Territory.
Identification of possible migration of contaminants in groundwater at a land...Alexander Decker
This document summarizes a study on identifying possible groundwater contamination at a landfill site in Barka, Oman. Borehole drilling, soil sampling, and groundwater sampling and analysis were conducted. Results showed elevated levels of contaminants like TDS, sodium, calcium, magnesium, chloride, and coliform bacteria in groundwater below the landfill compared to background levels, indicating contamination from leachate and liquid waste disposal. A pump test also found decreasing contaminant concentrations with pumping time, suggesting contaminant migration from the landfill area.
DNAPL Remediation with ClO2_UV-published paperDarcy Bye
This study investigated the sorption of PAHs, PCBs, phenols, and BTEX hydrocarbons from groundwater onto a subsoil core sample. It also examined the destruction of these contaminants in ClO2/UV solution systems using methanol as the carrier solvent. Sorption experiments showed the contaminants formed S-type isotherms and could be modeled using the Freundlich equation. Off-site travel times for the contaminants in groundwater ranged from 145 to 80,817 years based on sorption. Treatment with ClO2/UV destroyed 76-98% of the contaminants and produced no dioxins or furans as byproducts, demonstrating this method's potential for remediating recal
A Review of Zeolite Based Treatment Water Systems and Thier Applicability in ...Daniel Eyde
The revisions to the Clean Water Act, ever lower NPDES water discharge standards and competition for scarce water resources have increased the need for cost-effective water treatment products and applications. Many water treatment sites are remote and lack infrastructure, others are passive or semi-passisve wetlands and bioreactors whose effluent, while meeting discharge standards, still require additional treatment for turbidity, COD, BOD and pH adjustment. The use of natural zeolites, alone or in conjunction with other treatment technologies, have had success in mitigating amD/amR discharges, as well as heavy metals, turbidity, NH4+, Al, Mn and silica in coal and hard rock mining impacted effluents. In uranium mining areas and NURE impacted waters, treatment systems initially designed more for problems like for Three Mile Island and Fukushima have been effective in capturing radionuclides in both passive and active treatment systems, most recently at the Homestake Uranium Tailings at Grants, NM. The applicability of the ion exchange and filtration capabilities of zeolites, their ability to be used in passive treatment systems and their limitations are reviewed.
Hydraulic Fracturing and Marcellus Shale Gas 11 22 2011Michael Klein
The drilling technique of Hydraulic Fracturing has allowed natural gas producers to extract natural gas economically from deep shale formations. This innovative drilling technique has made enormous quantities of natural gas available in wide areas of the United States from Texas, Louisiana, Pennsylvania, New York, Wyoming, North Carolina, and Colorado. The drilling technique of hydraulic fracturing accounts for roughly a quarter of total natural gas production in the United States as cited by the Energy Information Administration. With the increased emphasis on the use of natural gas in our federal energy policy, there will be new regulations, processes, and resources that will be required to mitigate the risks to human health and the environment from this new drilling technique. The presentation discusses the process of hydraulic fracturing; the threats that are posed to human health and the environment, areas in the USA where the process is used with an emphasis on the Marcellus Shale formation, current and new regulations being put into place, and plaintiff challenges to the process.
The Impact of Marcellus Gas Drilling on Rural Drinking Water SuppliesMarcellus Drilling News
A multi-year study by the bipartisan Center for Rural Pennsylvania on the effects of Marcellus Shale gas drilling on rural water supplies. The study concludes that fracking does not lead to chemical contamination of water supplies, and likely does not affect methane migration into water supplies (although the authors recommend more study of the methane migration issue).
This document summarizes a study that evaluated water quality in 100 private drinking water wells located near natural gas extraction sites in the Barnett Shale Formation in North Texas. The study found that some wells located within 3 km of active gas wells contained levels of arsenic, selenium, strontium and total dissolved solids that exceeded EPA limits. Lower levels of these constituents were found in wells further than 3 km from gas sites and in areas without gas extraction. Methanol and ethanol were also detected in 29% of samples. Contaminant levels did not show a clear spatial pattern and could be due to various factors like mobilizing of natural materials, changes to the water table, or industrial accidents.
The Balangero asbestos open pit mine, located 35km NW of Torino (Italy), was the largest operation of this kind in Western Europe. The dry tailings were lifted by a conveyor belt from the mill and dumped over a natural slope with an approximate angle of 25 degrees, progressively reaching a maximum thickness estimated at 80 m.
By the '80s the dump was deeply scarred by various local and large scale instabilities, to the point that houses located at the toe, on the opposite side of the valley, were evacuated.
The award winning restoration project used a multidisciplinary approach including hydraulics, geotechnical, pedological and risk engineering to yield a well balanced and sustainable solution. This paper illustrates the Risk Based Decision Making (RBDM) process used through the feasibility, design and construction follow-up of the environmental restoration of the 60 Mm3 dry Balangero asbestos tailings dump.
The slopes were hit by storm Quinn and Medicane Rolf and came out unscathed. That was after surviving heavy summer storms in 2010 and 2011.
Testing and Implementation of AMD Mitigation, Alum Gulch-Flux Canyon, Cox Gul...Daniel Eyde
The document summarizes a plan to mitigate acid mine drainage (AMD) and heavy metals in several tributaries in southeastern Arizona that flow into Sonoita Creek and Patagonia Lake. The plan involves installing gabion retaining wall structures and stream bed footers containing zeolite materials downstream of mine discharge points to raise pH and reduce metals like zinc, cadmium, lead, and copper. Water quality and biological monitoring will occur before and after installation to evaluate effectiveness. Zeolites are effective at absorbing metals and raising pH, as shown in previous studies. The structures are intended to last 5-10 years before material replacement depending on runoff conditions.
Hydrogeochemistry and Microbiology of Wadi Al Bih Limestone Aquifer in Northe...QUESTJOURNAL
ABSTRACT: This study investigated the hydrogeochemical characteristics and microbiological pollution of groundwater in Wadi Al Bih limestone aquifer, Ras Al Khaimah area, northern United Arab Emirates (UAE). Results indicate that the decrease of groundwater exploitation in Wadi Al Bih basin from 58 million cubic meter (MCM) during the period 1991-1995 to 22 MCM during the period 2011-2015, has increased groundwater storage, raised hydraulic heads by 1 m in Al Burayrat area and 16 m near Wadi Al Bih main dam, and decreased the average groundwater salinity by 30% in Wadi Al Bih well field and 45% in Al Burayrat well field. Results of chemical analyses showed noticeable fluctuations in groundwater temperature, EC, and TDS contents, rather than concentrations of all ions. The November 2014 and June 2015 isosalinity contour maps indicate that the groundwater salinity increases from east to west, in the direction of groundwater flow. The groundwater in the eastern part of Wadi Al Bih is good for domestic purposes and irrigation. However, the water hardness is high because the aquifer is predominantly composed of limestone. Wadi Al Bih limestone aquifer is highly sensitive to urban and agricultural activities, and several well were recorded to have Coliform bacteria in Wadi Al Bih and Al Burayrat areas
The waterway and erosion management plan at the Arlington Agricultural Research Station organic fields requires improvements. Significant erosion is occurring due to steep slopes and intensive tillage. Some fields exceed the tolerable soil loss rate of 5 tons/acre/year. A HydroCAD model showed the existing waterway can convey 10-year storm flows. Recommendations include strip cropping, terracing problem fields, and diverting flows around a gullying area. Terraces will be installed in two fields to reduce slopes and soil loss to under 5 tons/acre/year.
This document outlines the guidelines for constructing check dams in order to provide drinking water facilities and groundwater recharge. It discusses the objectives of check dams, selection criteria for areas to implement check dams, types of check dams, design aspects, implementation arrangements, operation and maintenance responsibilities, funding arrangements, institutional arrangements for management, and monitoring mechanisms. Check dams are constructed across small rivers and streams to reduce water flow during monsoons and allow water to seep into the soil.
Lake Manzala Engineered Wetland, Port Said, Egypt [IWC4 Presentation]Iwl Pcu
Presentation during the focused learning discussion on Constructed Wetlands at the 4th GEF Biennial International Waters Conference.
Dr. Dia El Din El-Quosy
Project Manager
E-mail: lmewp@menanet.net
Lake Manzala Engineered Wetland Project
This document summarizes a study that measured 222Rn activity levels in 198 groundwater wells in southern Quebec, Canada. The goals were to examine the relationship between 222Rn levels and local geology/hydrogeology and to estimate potential health risks. Most wells showed low 222Rn activities below 100 Bq/L, the WHO limit for groundwater. Higher levels up to 310 Bq/L were found in wells tapping the Appalachian Mountains and Mont-Saint-Hilaire intrusion, known U-rich areas. 222Rn levels seemed related to lithological differences between more U-rich metasediments and magmatic intrusions versus carbonaceous silty shales. Radon was slightly enriched
Case Studies: Treatment of Acid Mine and Metal Contaminated Waters Using Zeol...Daniel Eyde
The Presentation presents case studies using zeolites in the treatment of acid mine and metal contaminated waters at Coal Operations in WV, & Legacy Mine Water Discharges at Uranium, Gold and Silver Operations in NM, MT and AZ
This document summarizes a study conducted by undergraduate geology students at Fort Lewis College analyzing water quality data from the Gold King Mine spill. The students:
1) Compared water quality data from EPA samples to their own samples collected along the Animas River after the spill.
2) Created a 3D model of the Gold King Mine underground workings to investigate possible connections explaining high discharge volumes.
3) Presented their comparative analysis and findings to the public to provide a more complete understanding of the mine and varying metal concentrations in streams.
This document summarizes a study on stormwater impacts to McVicar Creek. The study aimed to: identify impacts; characterize them through a stream assessment; identify 3 representative sites; pursue further research; and develop remediation recommendations. The initial assessment identified 3 sites - Court Street, Castlegreen, and County Fair - for further study. Additional data collection and stakeholder workshops were held. The workshops developed stormwater management objectives and site-specific recommendations. For Court Street, increased enforcement and education were recommended. For Castlegreen, investigating infrastructure and partnering with local groups. For County Fair, educating landowners and considering end-of-pipe solutions were recommended. The final recommendations emphasized objectives and further stakeholder
The "Findings Statement" issued by the New York State Dept. of Environmental Conservation that supplies the faulty thinking and irrational rationale for banning fracking in the Empire State. The ban is temporary--until a new governor and head of DEC are in place (hopefully at the next election). The Findings Statement is a pathetic attempt to paper over political motivations for a frack ban. It contains broad, sweeping and unsubstantiated by any evidence statements that denigrate the miracle of fracking. It is, in a word, pathetic.
International Journal of Engineering Research and Development (IJERD)IJERD Editor
journal publishing, how to publish research paper, Call For research paper, international journal, publishing a paper, IJERD, journal of science and technology, how to get a research paper published, publishing a paper, publishing of journal, publishing of research paper, reserach and review articles, IJERD Journal, How to publish your research paper, publish research paper, open access engineering journal, Engineering journal, Mathemetics journal, Physics journal, Chemistry journal, Computer Engineering, Computer Science journal, how to submit your paper, peer reviw journal, indexed journal, reserach and review articles, engineering journal, www.ijerd.com, research journals,
yahoo journals, bing journals, International Journal of Engineering Research and Development, google journals, hard copy of journal
IRJET- Index And Engineering Properties of Residual Tropical Soils of Sou...IRJET Journal
This document summarizes a study that investigated the engineering properties of soils in Konso town, Ethiopia. Eight test pits were dug and soil samples were collected and tested in the lab to determine their physical, index, shear strength, and consolidation properties. The dominant soil type was found to be silty clay (MH) based on grain size analysis and Atterberg limits tests. Properties tested included moisture content, plasticity index, clay fraction, free swell, specific gravity, shear strength parameters, and unconfined compression strength. The results showed that the soils generally had moderate to high expansiveness based on free swell tests. Proper handling and testing methods are needed when evaluating properties of residual tropical soils.
This document investigates co-locating a desalination plant with the Joslin Steam Electric Station in Point Comfort, Texas to provide a drought-proof water supply for regions L and N. A reverse osmosis desalination plant is proposed that would treat 180 million gallons per day of seawater to produce 90 million gallons per day of drinking water and reject hypersaline water. Reject water and solids from pretreatment would be returned through the existing plant discharge. Environmental impacts were found to be minimal. The estimated cost of the desalinated water is $1.75 per 1000 gallons. Combining this supply with 100,000 acre-feet of existing surface water supply would provide 200,000 acre-feet
Ben Barton has over 9 years of experience in environmental consulting, specializing in contaminated site assessment and remediation, spill response, and environmental monitoring. He has managed over 60 Phase I environmental site assessments, 50 Phase II and III assessments of sites such as gas stations, industrial operations, and First Nation lands. Mr. Barton has also directed the remediation of numerous contaminated sites using methods like excavation, in-situ injection, and pump and treat systems. He is the team lead for Tetra Tech's GeoEnvironmental group in Whitehorse, Yukon Territory.
Identification of possible migration of contaminants in groundwater at a land...Alexander Decker
This document summarizes a study on identifying possible groundwater contamination at a landfill site in Barka, Oman. Borehole drilling, soil sampling, and groundwater sampling and analysis were conducted. Results showed elevated levels of contaminants like TDS, sodium, calcium, magnesium, chloride, and coliform bacteria in groundwater below the landfill compared to background levels, indicating contamination from leachate and liquid waste disposal. A pump test also found decreasing contaminant concentrations with pumping time, suggesting contaminant migration from the landfill area.
DNAPL Remediation with ClO2_UV-published paperDarcy Bye
This study investigated the sorption of PAHs, PCBs, phenols, and BTEX hydrocarbons from groundwater onto a subsoil core sample. It also examined the destruction of these contaminants in ClO2/UV solution systems using methanol as the carrier solvent. Sorption experiments showed the contaminants formed S-type isotherms and could be modeled using the Freundlich equation. Off-site travel times for the contaminants in groundwater ranged from 145 to 80,817 years based on sorption. Treatment with ClO2/UV destroyed 76-98% of the contaminants and produced no dioxins or furans as byproducts, demonstrating this method's potential for remediating recal
A Review of Zeolite Based Treatment Water Systems and Thier Applicability in ...Daniel Eyde
The revisions to the Clean Water Act, ever lower NPDES water discharge standards and competition for scarce water resources have increased the need for cost-effective water treatment products and applications. Many water treatment sites are remote and lack infrastructure, others are passive or semi-passisve wetlands and bioreactors whose effluent, while meeting discharge standards, still require additional treatment for turbidity, COD, BOD and pH adjustment. The use of natural zeolites, alone or in conjunction with other treatment technologies, have had success in mitigating amD/amR discharges, as well as heavy metals, turbidity, NH4+, Al, Mn and silica in coal and hard rock mining impacted effluents. In uranium mining areas and NURE impacted waters, treatment systems initially designed more for problems like for Three Mile Island and Fukushima have been effective in capturing radionuclides in both passive and active treatment systems, most recently at the Homestake Uranium Tailings at Grants, NM. The applicability of the ion exchange and filtration capabilities of zeolites, their ability to be used in passive treatment systems and their limitations are reviewed.
Hydraulic Fracturing and Marcellus Shale Gas 11 22 2011Michael Klein
The drilling technique of Hydraulic Fracturing has allowed natural gas producers to extract natural gas economically from deep shale formations. This innovative drilling technique has made enormous quantities of natural gas available in wide areas of the United States from Texas, Louisiana, Pennsylvania, New York, Wyoming, North Carolina, and Colorado. The drilling technique of hydraulic fracturing accounts for roughly a quarter of total natural gas production in the United States as cited by the Energy Information Administration. With the increased emphasis on the use of natural gas in our federal energy policy, there will be new regulations, processes, and resources that will be required to mitigate the risks to human health and the environment from this new drilling technique. The presentation discusses the process of hydraulic fracturing; the threats that are posed to human health and the environment, areas in the USA where the process is used with an emphasis on the Marcellus Shale formation, current and new regulations being put into place, and plaintiff challenges to the process.
The Impact of Marcellus Gas Drilling on Rural Drinking Water SuppliesMarcellus Drilling News
A multi-year study by the bipartisan Center for Rural Pennsylvania on the effects of Marcellus Shale gas drilling on rural water supplies. The study concludes that fracking does not lead to chemical contamination of water supplies, and likely does not affect methane migration into water supplies (although the authors recommend more study of the methane migration issue).
1.5 "Environmental Concern and QA/QC in Shale Gas Drilling and Fracturing" - ...Pomcert
The document discusses environmental concerns and quality assurance/quality control practices regarding shale gas drilling and hydraulic fracturing. It covers topics such as well construction, cementing, casing, mud selection, fracturing, water sourcing and management, and monitoring. It emphasizes the importance of best practices like baseline water testing, closed-loop systems, secondary containment, inspection, and optimization to safely develop shale gas resources while protecting water and the environment.
This document discusses hydraulic fracturing and proposes potential economic solutions to address its environmental and social costs. It summarizes that while hydraulic fracturing is touted as an economic necessity, it poses risks to groundwater and emissions. It lacks oversight and does not account for all costs. The document proposes repealing the 2005 law exempting fracking from Clean Water Act oversight, implementing performance standards to limit water impacts, and requiring performance bonds to cover cleanup costs from spills. Passing the proposed 2012 FRAC Act could bring fracking under a single federal authority to oversee risks.
Coal use in India contributes significantly to water pollution in several ways: (1) Coal ash contains toxic heavy metals that pollute water sources; (2) Coal mining contaminates water with acid mine drainage and heavy metals; (3) Coal-fired power plants place stress on water resources for steam generation and emit pollutants that cause acid rain. A CPCB study found that untreated wastewater from coal mines increases turbidity in rivers and toxic element levels in groundwater. Strict regulations on wastewater treatment and zero discharge are needed to reduce coal's pollution of water resources.
- Produced water from oil and gas extraction poses high costs for transportation and disposal, but also presents an opportunity for beneficial use if desalinated.
- Advances in desalination technology, particularly reverse osmosis, have the potential to make treatment of lower-salinity produced waters cost-effective by allowing deep-well injection of concentrate without an EPA permit.
- A study in Texas found that about 1/3 of produced waters have salinities below 10,000 mg/L, making them candidates for desalination, with potential annual cost savings of millions for operators if treatment and beneficial use were implemented on a large scale.
Water’s Journey Through the Shale Gas Drilling and Production ProcessesMarcellus Drilling News
The paper "Water’s Journey Through the Shale Gas Drilling and Production Processes in the Mid-Atlantic Region" was published by Penn State Cooperative Extension in May 2012. It traces the various paths for a water droplet used by the Marcellus Shale natural-gas industry in the mid-Atlantic region, also dealing with the issue of wastewater.
PA Forest Fragmentation from Marcellus Shale, Wind Turbines & Transmission LinesPaul Zeph
This document discusses potential impacts on Pennsylvania's environment from increased Marcellus Shale drilling, wind turbine development, and new transmission lines. It notes that these industrial activities can fragment forests and sensitive habitats, increasing edge effects. This raises concerns for interior forest bird species and other wildlife through direct habitat loss and disturbance. Specific cases of water contamination from gas drilling operations in Dimock are also examined.
The document discusses U.S. shale gas resources and the challenges of developing them. It notes that shale gas reserves are conservatively estimated at 500-1000 trillion cubic feet and that hydraulic fracturing and horizontal drilling first made shale gas production economically viable. However, each shale play has unique characteristics that require tailored solutions. The document summarizes characteristics of major shale plays like the Barnett, Woodford, Haynesville, Bakken and Fayetteville and notes that best practices must evolve locally to address specific challenges in each play. Unconventional resources like shale gas require unconventional solutions to optimize production and costs.
The document discusses the science behind coal flotation and fines dewatering processes. It explains that as coal particle size decreases, surface chemistry dominates over density. Flotation and dewatering are affected by process water chemistry resulting from coal oxidation and weathering reactions. Humic acids, slimes, and dissolved minerals in recycled water impact plant performance over time. An improved understanding of these complex interactions could help optimize recovery and dewatering of fine coal.
Latest Advances in the Development of Ecological Drilling Fluids John Downs
This document summarizes a presentation given by John Downs of Hydro Formates at the IBC Asia Conference on June 25-26, 2002 regarding advances in ecological drilling fluids. It discusses how traditional drilling practices and conventional drilling fluids can damage the environment by increasing waste volumes and toxicity. Specifically, it notes how the use of barite as a weighting agent in drilling fluids increases waste toxicity levels through solubilization of barium into chloride-containing drilling fluids and discharges, despite barite having low solubility in fresh water. The document argues that formate brine drilling fluids best match the profile of an ideal ecological drilling fluid by minimizing waste volumes and toxicity.
This document discusses shale gas, an unconventional source of natural gas found in shale rock formations hundreds of meters underground. It can be extracted through hydraulic fracturing and horizontal drilling. While shale gas can increase energy supply and reduce dependence on foreign oil, there are environmental concerns about potential groundwater contamination and impacts on wildlife habitats and communities. The document also outlines the global distribution of shale gas resources and debates around the pros and cons of developing this energy source.
This document discusses shale gas, an unconventional source of natural gas found in shale rock formations hundreds of meters underground. It can be extracted through hydraulic fracturing and horizontal drilling. While shale gas can increase energy supply and reduce dependence on foreign oil, there are environmental concerns about potential groundwater contamination and impacts on wildlife habitats and communities. The document also outlines the global distribution of shale gas resources and debates around the pros and cons of developing this energy source.
Hydraulic fracturing, also known as fracking, involves injecting fluid into shale rock formations to force open cracks and allow natural gas and oil to flow out. While fracking has increased US energy independence and reduced coal use, it also poses risks to the environment and public health. Fracking requires large amounts of water and chemicals and has been linked to groundwater contamination, air pollution, increased seismic activity, and health issues in humans and animals. However, replacing coal plants with natural gas could significantly reduce greenhouse gas emissions while more renewable technologies are developed. The dangers of fracking must be weighed against its current role in transitioning from coal to cleaner energy sources over the long run.
A new study by a pair of researchers from Rice University (Houston, TX). The study looks in detail at the chemical compounds found in frack wastewater from shale plays in PA, TX and NM and finds, according to the researchers, that frack water "was not quite as bad as we thought."
The document discusses natural gas drilling and its potential impacts on drinking water. It outlines the goals of an internship related to researching hydraulic fracturing and its public health implications. It then provides details on the drilling process, including horizontal drilling and hydraulic fracturing techniques. It discusses the usage of water in these processes and potential risks to water quality from chemical additives and produced water. It recommends best practices like baseline water testing, closed-loop drilling systems to contain waste, and increased setbacks from drinking water sources to protect public health.
This document discusses shale gas exploration and production. It begins by defining unconventional gas formations like shale gas, which form within organic-rich shale source rock rather than migrating to discrete traps like conventional gas. It then discusses properties of shale like total organic content and thermal maturity that determine gas potential. Key techniques for shale gas production include horizontal drilling and hydraulic fracturing. Fracturing fluid consists mainly of water and sand but also chemical additives. Produced water from drilling and fracturing requires management and often treatment due to high total dissolved solids.
This document provides an overview of Marcellus Shale drilling in Pennsylvania and discusses environmental and public health concerns associated with the process. It notes that 64% of PA underlies the Marcellus Shale formation and outlines concerns such as chemical and wastewater leaks threatening drinking water, air pollution, excessive water use, and impacts to public lands. It proposes actions citizens can take to strengthen regulations around water use, chemical disclosure, buffer zones, and ensuring industry pays for damages.
Last Updated October 31, 2011Hydrofracking Is hydraulic fractu.docxsmile790243
Last Updated: October 31, 2011
Hydrofracking: Is hydraulic fracturing, or hydrofracking, a safe way to extract natural gas?
Pro/Con Article Media Editorials News
Page Tools Highlighting
FULL ARTICLE
Introduction
Background
Supporters Argue
Opponents Argue
Conclusion
Chronology
By the Numbers
Spotlights
Discussion Questions
Bibliography
Further Resources
Introduction
SUPPORTERS ARGUE
There is no proven case of hydrofracking contaminating drinking water, and the process is perfectly safe. Natural gas can revive local economies, reduce U.S. dependence on foreign oil, and provide a cleaner-burning fossil fuel. Further regulation is unnecessary and will only prevent an opportunity for the United States to develop an alternative energy source and create jobs.
OPPONENTS ARGUE
The chemicals used in fracking fluid are toxic and pose a danger to public health if they contaminate drinking water reserves or leak out of wells. Oil and gas companies are not being honest with the public about the dangers of hydrofracking, and the federal government should apply much stricter, nationwide regulations to ensure that hydrofracking does not cause widespread health problems that could plague the public for generations.
Issues and Controversies: Hydrofracking Workers
Workers at a natural gas well site in Burlington, Pennsylvania, in April 2010 prepare a drill to begin the process of hydraulic fracturing, or hydrofracking.
AP Photo/Ralph Wilson
Many observers have hailed natural gas as a solution to several energy problems facing the U.S. Utilizing the country's ample domestic supply of the resource, many have said, could greatly decrease U.S. dependence on foreign oil and possibly drive energy prices down. Furthermore, natural gas produces much less carbon dioxide than other fossil fuels, about half as much as coal, making it the cleanest burning fossil fuel available. Energy experts have also touted natural gas as a cheap alternative to renewable energy sources, such as wind or solar energy, until engineers devise a way to make renewable energy more cost efficient. According to the Department of Energy, natural gas already produces about one-fifth of the nation's electricity, a proportion that may increase as energy firms tap more domestic reserves of natural gas.
The Marcellus Shale, a 95,000-square-mile geologic formation deep underground that stretches from West Virginia through Pennsylvania to upstate New York, is estimated to contain as much as 500 trillion cubic feet of natural gas. In order to access the natural gas in the Marcellus Shale and other shale formations, however, energy companies have to employ a controversial procedure called hydraulic fracturing—also known as "hydrofracking" or simply "fracking." Hydrofracking is a technique that releases natural gas by pumping millions of gallons of water, laced with sand and chemicals, thousands of feet underground to blast open, or fracture, shale formations, freeing the gas. [See Today's Science: Nat ...
V.P. Wright (2020) – Burial corrosion and porosity formation in carbonate res...GiovannaDellaPorta2
Burial corrosion and porosity formation can take place at depths of several kilometers in carbonate reservoirs through dissolution processes termed burial corrosion or mesogenetic dissolution. There is debate around the terminology but it is useful to take a hydrological approach and see the key processes as due to burial fluids derived from below the reservoir, known as hypogene fluids. Some consistent relationships seen in hypogene diagenetic systems that may prove useful for exploration include the common association with faults, especially transtensional faults, and platform slopes and margins forming major pathways, especially if fractured and near kitchens or compacting shale basins. Identifying the fluid source and mechanism is difficult but can provide predictive insight for exploration.
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Chapter wise All Notes of First year Basic Civil Engineering
Syllabus
Chapter-1
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Chapter 2
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Chapter 3
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Gas Drilling Water Quality and Private Drinking Supplies
1. College of Agricultural Sciences • Cooperative Extension
School of Forest Resources
Water Facts #28
Gas Well Drilling and Your Private Water Supply
Gas well drilling has occurred for decades in much of below the fresh water aquifers. These fluids are
western and northern Pennsylvania with tens of commonly referred to as “brines”.
thousands of active gas wells in the state and over
5,000 new wells drilled each year. Most of these wells Stimulation or flow back fluids are fluids that are
tap gas reserves a few thousand feet below the used to improve gas recovery from the rock and
earth’s surface. With discoveries of new gas reserves are returned to the ground surface. An example is
in the Marcellus shale and new drilling technologies “hydrofracturing” which uses high pressure fluids
to reach previously untapped gas reserves, both the to break the gas-producing rock to improve the
number and depth of gas wells are expected to rise flow of gas. Along with large amounts of water,
dramatically over the next several decades. various other materials may be used or mixed
with the water for the fracturing process including
sand, oils, gels, acids, alcohols and various man-
made organic chemicals. The exact additives
have traditionally been difficult to determine
because they were considered proprietary.
Recent changes to the state gas well drilling
permit along with action by River Basin
Commissions now requires disclosure of
additives used in hydrofracturing as part of the
gas drilling permit application and approval.
Production fluids are produced along with the
natural gas after the well is in production.
Production fluids usually have a similar chemistry
to the bottom hole fluids.
A typical Marcellus gas well site (Tom Murphy, The volume of fluids produced during gas well drilling
Lycoming County Cooperative Extension). and operation can vary considerably depending on
the depth and location of the gas well. One study in
Potential Water Quality Impacts from Drilling Pennsylvania found average volumes of water
Gas well drilling can occasionally impact groundwater produced during shallow gas well drilling in western
resources that are the source of water for household Pennsylvania was 25,000 gallons during drilling,
water wells and springs. A single gas well can 50,000 gallons during stimulation and 150 gallons per
produce hundreds of thousands of gallons of waste day during production. Drilling of deeper gas wells in
fluids during drilling and during years of gas the Marcellus formation relies more on
production. The wastes fluids generated from a gas hydrofracturing which requires several million gallons
well can be classified into several categories of freshwater. On average, about 10 to 30 percent of
including: the water used for hydrofracturing Marcellus wells
Top hole fluids are the fresh water aquifers that returns to the ground surface as a “flow back” waste
are encountered usually within the first few fluid.
hundred feet of the drilling process.
Bottom hole fluids are very old salt water deposits While top hole fluid is usually representative of
encountered deep underground during drilling groundwater used for local water wells and springs,
1
2. the remaining water encountered during gas well How Common are Problems?
drilling (bottom hole, stimulation and production Contamination of private wells and springs can occur
fluids) may be contaminated with various pollutants. from gas well drilling but it has not been common
over the past few decades. Data from various
Groundwater Pollutants from Gas Wells regulatory agencies responsible for enforcement of
Pollution of private water supplies from gas well gas well drilling regulations indicate that more than
activity has occurred in Pennsylvania. This 95% of complaints received by homeowners
contamination may occur from absent or corroded suspecting problems from nearby gas well drilling are,
gas well casings (on older or abandoned gas wells) or instead, due to pre-existing problems or other nearby
it may originate from flooded or leaking waste fluid land use activities.
holding pits or spills at the drilling site.
A study by McKean County Cooperative Extension
Gas well waste fluids usually contain levels of some and Penn State University in 2007 looked at water
pollutants that are far above levels considered safe quality in 200 private water wells in an area that has
for drinking water supplies. As a result, even small undergone extensive oil and gas well drilling for
amounts of pollution from waste fluids can result in several decades. About three percent of these private
significant impacts to nearby drinking water supplies. water wells exceeded drinking water standards for
The broad categories of pollutants in gas drilling total dissolved solids, barium or chloride (three of the
waste fluids includes: most likely water pollutants from gas well drilling).
Another five percent of these private wells had
Salts—most notably sodium and chloride. Gas elevated levels of at least one of these pollutants that
well waste fluids can have over 100,000 mg/L of could be tied to gas well drilling. A similar study of
these compounds. Other pollutants that can 200 water wells in the northeast region of the state in
occur as various salts include magnesium, early 2008 did not detect any water wells with these
calcium and potassium. These salts cause the same pollutants prior to intensive Marcellus shale
“total dissolved solids” in the wastes to be very drilling activity.
high.
It is important to note that the McKean County study
Metals—including iron, manganese, barium, did not attempt to differentiate between effects from
arsenic and trace amounts of other heavy metals. past versus current gas well drilling. Given the
changes and strengthening of regulations on gas well
Organics—these include both natural and man- drilling that occurred in the mid 1980’s, it is likely that
made materials that are used during the drilling most of the groundwater contamination found in
process such surfactants, detergents, oil, grease, McKean County occurred from past drilling practices.
benzene and toluene. Dozens of other man- Still, these results point to the importance of
made organics may be used in small remaining vigilant in properly testing and monitoring
concentrations during hydrofracturing. private water supplies near gas wells using the
strategies outlined later in this publication.
Another problem that can occur from gas well drilling Regulations to Protect Water Supplies
is methane gas migration from gas wells into nearby Gas well drilling is regulated by the Oil and Gas Act of
water wells. The methane gas will rapidly escape 1984. This Act regulates the permitting, construction
from the groundwater and may pose an explosion and abandonment of gas wells drilled throughout the
hazard in confined spaces. Methane gas testing in state. A summary of the various relevant components
water is difficult but it usually creates obvious of the Oil and Gas Act are provided here.
symptoms in the home including effervescence and
spurting faucets due to gas build-up. To learn more 1) Permits
about methane gas problems in private wells, consult Before drilling a gas well in Pennsylvania, the
the Penn State Extension publication entitled Water operator must submit an extensive permit application
Facts #24—Methane Gas and Its Removal from for approval from the Pennsylvania Department of
Wells in Pennsylvania available from your local Environmental Protection (DEP). Among other
Cooperative Extension office or online at: things, the permit application must include a map
showing the location of the gas well, proximity of the
http://pubs.cas.psu.edu/FreePubs/pdfs/XH0010.pdf gas well to coal seams, and distances to nearby
surface water and water supplies. The map must also
2
3. include the projected horizontal boreholes, property -drilling survey water samples and samples collected
lines and acreage which will be disturbed during by DEP during investigations are analyzed for the
drilling. A bond ranging from $2,500 to $25,000 must salts and metals listed on page two. Individual gas
be posted with the permit to ensure compliance with well companies and DEP may choose additional
environmental regulations related to the well drilling. water tests such as coliform bacteria, methane, and
The permit also requires notification of surface land various organic compounds depending on the
owners and coal mineral right owners at the well site circumstances.
along with all drinking water supply owners within
1,000 feet of the well. Notification of these various As part of any pre-drilling survey water sample, the
stakeholders is done by certified mail. As a result, gas well company is required to hire an independent
homeowners with private water wells or springs state-certified water testing laboratory to conduct the
which are located within 1,000 feet of the proposed water testing. You can find local, state-certified water
gas well site should receive notification by certified testing labs by contacting your local Penn State
mail during the permit process. Cooperative Extension. An up-to-date listing of state
certified water testing labs from the DEP Bureau of
2) Setback Distances Labs is also linked on the Penn State Water
Gas wells must be at least 200 feet from any drinking Resources Extension site at:
water supplies. This setback may be waived by the
water supply owner in a lease agreement. Gas wells http://water.cas.psu.edu/WS_Testing.htm
must also be 100 feet from any stream, spring or
body of water identified on the most current 7.5
minute USGS topographic map. A 100 foot setback
is also required from any wetland greater than one
acre in size. These setbacks may also be relaxed if
additional protection is put in place to protect these
natural resources.
3) Protection of Drinking Water Quality
Section 208 of the Oil and Gas Act specifically
includes language to protect nearby drinking water
supplies. This includes a requirement that gas well
drilling operators restore or replace any water supply
determined by the DEP to be polluted as a result of
nearby gas well drilling. The gas well operator is
presumed to be responsible for pollution of any
drinking water supply within 1,000 feet of the gas Gas well drilling companies will contract with
well IF it occurs within six months after completion of independent state-certified water testing labs to
the gas well. The operator can use any one of five conduct pre-drilling water testing at nearby
defenses to prove the are not responsible for water homes using drinking water wells and springs.
contamination including:
An employee or subcontractor from the certified
The pollution existed prior to the drilling laboratory will visit homes within 1,000 feet of the
The landowner or water purveyor refused to allow proposed gas well site to collect the water samples.
the operator access to conduct a pre-drilling This ensures that the samples are collected correctly
water test using proper methods and materials. To ensure data
The water supply is not within 1,000 ft of the well quality, documentation must be completed for each
The pollution occurred more than six months sample showing proper sample collection,
after completion of drilling preservation, handling procedures and chain of
The pollution occurred as the result of some custody (people who handled the sample).
cause other than the gas drilling
Here are some important things to remember if you
To preserve their defense, most gas well operators are visited by someone wanting to test your water as
will collect the necessary pre-drilling water quality part of a pre-gas drilling survey:
information from all drinking water supplies within Do not deny access to the water testing
1,000 feet of their drilling operation. Although there is laboratory personnel. It is important to note that
no list of required water quality parameters, most pre gas well operators are NOT presumed
3
4. responsible for pollution of water supplies that sedimentation due to these disturbances. Erosion and
they were denied access to prior to the drilling. Sediment Plans may be required that include the use
Get the name and company affiliation of any of filter fence, sediment traps, vegetation, hay bales,
person asking to sample your water supply and culverts and rocked road entrances. These plans also
ask for proof of identification. include a requirement to restore vegetation to the drill
Tell the person testing your water as much as you site within nine months of well completion.
know about your water supply including Enforcement of erosion and sediment problems
approximate depth, yield, age, and treatment related to gas well operations is overseen by
devices. This information will help them to personnel from the DEP, Bureau of Oil and Gas
determine proper sampling locations. It may also Management.
help the gas drilling company choose proper
drilling techniques to avoid causing problems to 6) Groundwater Protection During Drilling
your water supply. New protections were included in the 1984 Oil and
Ask what water quality tests will be performed by Gas Act to ensure that groundwater aquifers are not
the laboratory on your water sample. This list may contaminated by drilling fluids, brines and wastes. A
help you decide if you want to have your own, thick, steel casing is cemented into place from the
more extensive test done at your own cost (see ground surface to below the deepest freshwater
discussion in the Homeowner Strategies to aquifer (typically several hundred feet below the
Protect Water Supplies section). ground surface). This freshwater protection string
The owner of the water supply has a right to segregates the fresh groundwater from the drilling
receive a copy of any pre-drilling water test process and prevents waste fluids from entering
results collected by a lab representing the energy freshwater aquifers. Changes to these regulations are
company. You can request a copy of these water proposed in 2010 to provide even greater protection
test reports from the water laboratory or the for groundwater aquifers.
energy company. If they are unwilling to provide
a copy, contact one of the Pennsylvania DEP, 7) Disposal of Drilling Fluids
Bureau of Oil and Gas Management offices below Disposal of the various fluids used and generated
and they will obtain a copy for you. during and after the drilling process are also
Central Office 717-772-2199 regulated to protect surface and groundwater
Southwest Office 412-442-4024 resources. All waste fluids produced during drilling
Northcentral Office 570-321-6550 are collected in metals tanks or pits. All pits must
Northwest Office 814-332-6860 have an acceptable liner with at least two feet of
freeboard to protect both groundwater and nearby
4) Protection of Water Flows from Wells and Springs surface water. Final use or disposal of waste fluids
Gas well drilling can occasionally change the flow of depends on the source of the water. The relatively
water from a water well or spring, although these clean freshwater or top hole water encountered in the
changes are often temporary. Unlike water quality first several hundred feet of drilling is sometimes re-
impacts, gas well operators are NOT presumed used later in the drilling process or land applied and
responsible for water quantity impacts to nearby allowed to infiltrate back into local groundwater if it
water supplies. For this reason, water flow data is meets certain water quality criteria. Top-hole water
often not measured during pre-drilling surveys may also be trucked to an off-site treatment facility.
conducted during the permitting process. Instead, Some of the remaining drilling fluids (brines,
impacts to water quantity would need to be fracturing wastes, etc.) may be recycled and reused
investigated by DEP inspectors and/or proven by the during the drilling and hydrofracturing process but
water supply owner. Concerned water supply owners most is eventually trucked to dedicated treatment
may wish to hire a well driller or water consultant to sites where it is treated and discharged to a surface
document the flow of water from their well or spring stream. Another less common method to dispose of
prior to the gas drilling activity (see Homeowner waste fluids is through pumping into very deep
Strategies section for more detail). disposal wells regulated by the Pennsylvania
Department of Environmental Protection and the U.S.
5) Land Disturbance Environmental Protection Agency. These wells
Gas well construction involves extensive disturbance access a confined, deep permeable formation where
including roads, drilling pads and pipelines. Drilling the wastes can be segregated from shallow,
pads alone may be four to six acres in size for deeper groundwater aquifers. Some brine may also be
gas wells. Various regulations are in place to protect trucked to municipal or industrial treatment plants or
surface water and groundwater from erosion and applied to rural gravel and dirt roads for dust control.
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5. Municipal or industrial treatment facilities can only other sites. The freshwater protection casing is left in
accept gas well waste fluids if they have a permit place and the hole is filled to the ground surface with
demonstrating adequate capacity and technology to non-porous material.
properly treat the waste fluids. Waste fluids from
below the fresh water casing must meet limits for Prior to current regulations, gas wells were often left
iron, oil/grease, total suspended solids and pH in place even after they were taken out of production.
before they can be discharged. Alkalinity, acidity, Thousands of these wells are located throughout
total dissolved solids and chlorides are also much of western and north-central Pennsylvania.
monitored in these treated waters. Proposed These abandoned gas wells, often referred to as
changes to regulations may require treatment plants “orphan wells” should be properly decommissioned
to further treat these waste fluids to meet a standard to prevent future groundwater contamination. The
of less than 500 mg/L of total dissolved solids by state has a fund to properly decommission orphan
January of 2011. Other recent changes to gas wells. Contact one of the regional Pennsylvania
regulations now require the gas well drilling Department of Environmental Protection (DEP),
operators to specifically identify the location of Bureau of Oil and Gas Management offices listed on
treatment facilities where drilling and hydrofracturing the previous page to report an orphan gas or oil well
fluids will be taken for treatment and ultimate in your area.
disposal.
Homeowner Strategies to Protect Water Supplies
8) Water Withdrawals 1) Maintain Your Water Supply
A major concern with newer and deeper gas well Most homeowner complaints related to gas well
drilling technologies has been the withdrawal of large drilling and drinking water supplies are determined to
volumes (millions of gallons) of water used mostly in be problems that existed before gas drilling or were
the hydrofracturing process. These large water caused by other activities. Periodic maintenance and
withdrawals may come from many sources (streams, testing of private water supplies can help to identify
ponds, lakes, etc.) and can have significant effects if and avoid these problems. Penn State Cooperative
not done carefully. Water withdrawals generally Extension has many resources and publications
exceeding 10,000 gallons per day require permits or dedicated to proper management of private water
registration with DEP under authority of the Water systems. They are available at your local county
Resources Planning Act. Withdrawals occurring in Extension office or online at:
the Susquehanna or Delaware River watersheds http://water.cas.psu.edu
may also require permits from the Susquehanna
River Basin Commission or the Delaware River 2) Learn When and Where Drilling Will Occur
Basin Commission. The Clean Streams Law also Some homeowners will learn of nearby gas well
limits the amount of water that can be withdrawn drilling plans through lease agreements or through
from streams to maintain sufficient stream flows to required notification by certified mail if their water
protect aquatic life. These various regulations have supply is within 1,000 feet of the proposed well. But,
all been used to shut down gas well drilling anyone can be kept abreast of gas well drilling plans
operations that failed to acquire the proper permits or through several online features available through the
exceeded allowable withdrawals from streams. Pennsylvania DEP including:
Concerns over water use during gas well drilling PA DEP Marcellus web site: Includes spreadsheets,
prompted changes to the state permit in 2008. The graphs and maps of Marcellus drilling activity. (http://
permit now must include information on the sources www.depweb.state.pa.us/ then enter Marcellus as a
and locations of water to be used in the drilling keyword).
process, the impacts of drilling on water resources
and proof that the water withdrawals have been eNotice: once registered on this web site you can
approved by the appropriate river basin commission. choose to receive notice of gas well permits in your
area. (www.dep.state.pa.us/enotice/)
9) Well Plugging
Once a well is no longer in production (a period of a eMap: a web-based geographic information system
few years to several decades for most wells), it must that allows mapping of proposed gas well locations
be decommissioned and plugged. In some cases, by permit number.
the production well casing (below the freshwater (www.emappa.dep.state.pa.us/emappa/viewer.htm)
protection string) may be removed and re-used at
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6. eFacts: after drilling begins, monitor inspection Local state-certified water testing labs can assist with
reports, violations, etc. on this web site. selection of water quality parameters and many offer
(http://www.dep.state.pa.us/dep/efacts/ standard packages of tests that correspond to gas
well drilling activities. Keep in mind that testing for all
3) Control Seismic Testing of the possible contaminants will be costly (several
Prior to drilling wells in an area, gas companies will hundred dollars for the tests alone). Listed below are
often seek permission from land owners to do three general categories of pollutants that are
seismic testing to determine the thickness of gas increasingly comprehensive of all possible pollutants
bearing rocks and other geologic information. A but also increasingly costly:
certain type of seismic testing commonly called “3D” Tier 1—are basic parameters that are likely to
uses two to three-inch diameter holes that are change if gas drilling affects groundwater. These
usually about 20 feet deep. Explosive charges are include total dissolved solids (TDS), pH, barium,
detonated in each hole and the resulting shock chloride, and methane. These tests are available
waves are recorded by instruments. from most certified labs and can be tested for a
reasonable cost.
There are no regulations to protect water supplies Tier 2—are good additions to the Tier 1 pollutants
from seismic testing. If 3D seismic testing with small that include total suspended solids (turbidity), iron
explosives is going to occur on your property, make manganese, hardness (calcium and magnesium),
sure to stipulate that each shot hole is immediately sodium, total organic carbon, strontium,
filled to prevent groundwater contamination by oil&grease, detergents, lead, arsenic, alkalinity,
surface water. If seismic testing is to be done close coliform bacteria, sulfate and nitrate.
to your water supply, you may want to stipulate that Tier 3– are pollutants that are more costly and
water quantity conditions be documented in your well include volatile organic compounds (VOC’s) or a
or spring by a professional water well contractor or subgroup of VOC’s called BTEX (benzene etc.)
hydrogeologist before allowing the seismic along with radionuclides like gross alpha, radium
exploration. and radon.
4) Collect Water Quality Data Prior to Drilling 5) Document Well and Spring Flow Before Drilling
Prior to gas well drilling occurring, drinking water Diminished or lost water supplies resulting from gas
supplies within 1,000 feet of the proposed gas well well drilling have occurred but are rare. When this
will likely be tested at no charge to the homeowner does occur, it is usually an obvious, complete loss of
by a certified testing laboratory hired by the gas water rather than a subtle decrease in water yield.
company. Make sure to arrange to receive results Well and spring owners that wish to document water
from this water testing. supply conditions before and after gas well activities
would need to hire a professional water well
If your water supply is more than 1,000 feet from a contractor or hydrogeologist to independently
proposed gas well site OR if you simply want to measure and document these conditions. You can
confirm the results collected during the pre-drill find a list of local water well contractors certified by
survey, you would need to arrange to have your the National Ground Water Association (NGWA) at
water tested at your expense. This test should also www.wellowner.org.
be arranged through a state-certified water testing
laboratory. 6) Continuously Monitor Water Quality
In addition to water samples analyzed by labs, some
It is important to remember that water samples water supply owners are interested in methods to
collected to document impacts from gas well drilling continuously monitor their water quality. Inexpensive
generally should be collected by an unbiased total dissolved solids (TDS) or conductivity meters
professional. Most often this is an employee of the can be purchased from many online suppliers for $50
water testing laboratory. This adds significantly to the to $100. These meters allow the water supply owner
cost of water testing but will be vital to the to quickly and easily measure the total amount of
admissibility of the results in any legal action related dissolved contaminants in their water. Large
to pollution of a private water supply. You can expect increases in the TDS or conductivity of water in
to pay $200 to $800 or more to have a pre-drilling conjunction with nearby gas drilling activity would
water sample collected and analyzed by a certified warrant follow-up testing by a state accredited water
water testing laboratory depending on the complexity lab.
of the test package.
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7. 7) Test Water After Drilling homeowners should be utilized only for educational
There are no requirements for gas well companies to purposes including:
test private water supplies, even those within 1,000
feet of an active gas well, after the gas well drilling General water system education: about half of
has concluded. Therefore, any post-drilling water the private water systems in Pennsylvania have
sampling is a voluntary decision that must be never been tested. Penn State recommends that
arranged by the homeowner unless the testing is all private wells and springs should be routinely
previously stipulated in a lease agreement or part of tested for coliform bacteria, pH, total dissolved
a complaint to DEP. Obvious changes to your water solids, and any other pollutants associated with
supply that would warrant a complaint to DEP can land use activities occurring within sight of the
include: water supply.
Rapid increases in the TDS or conductivity of the
water supply based on readings from a meter. Comparison to pre-drilling test results: water test
Occurrence of increased severity of sediment in results collected by the homeowner could be
local surface water (streams, ponds, etc.). used to confirm pre-drilling results collected by
Changes in the appearance of drinking water certified labs contracted by the gas company. In
from a well or spring such as sediment, foaming, this case, homeowners should collect and submit
bubbling or spurting faucets a duplicate sample within a few days of samples
Changes in drinking water taste including salty or collected by the gas company. If the homeowner
metallic tastes collected sample shows lower levels of
Changes in water odor such as a rotten egg odor, contaminants than the sample collected by the
fuel or oily smell laboratory, it would then be advisable to hire a
Reduction or loss of water quantity certified water testing lab to visit your home and
collect an additional sample that would be
Should you notice any obvious changes in your admissible in any future legal action.
water supply in conjunction with nearby gas well
drilling, you can file a complaint with the regional Post-drilling decisions: homeowner-collected
DEP, Bureau of Oil and Gas offices listed earlier in samples after drilling could be used to look for
this publication. They will investigate the claim within any changes in water quality. If concentrations of
ten days and make a determination of the cause contaminants are present at higher levels than
within 45 days. Water pollution complaints filed the pre-drilling concentrations, further testing is
during gas well drilling operations or within six again warranted by an independent
months after drilling was completed place the burden representative of a certified lab. Keep in mind
of proof on the gas well operator. Water pollution that samples collected after drilling should be
complaints filed more than six months after drilling scheduled soon after drilling is completed to
has ended and all water quantity complaints place allow time to receive the results and take action
the burden of proof on the homeowner. During the before six months has passed. This will maintain
investigation, DEP will obtain results from all pre- the burden of proof on the gas company rather
drilling water testing. They may also decide to collect than the homeowner.
additional water samples as part of the investigation.
While many of the pollutants associated with gas well If you choose to sample your water supply yourself,
drilling will have obvious stains, odors or tastes in make sure to obtain proper sample containers from
your water, others have no obvious symptoms. For the laboratory and follow their sample collection
this reason, some homeowners may wish to hire an instruction very carefully. For more details on how to
independent water laboratory to collect a post-drilling collect water samples, consult the Penn State
water sample. Cooperative Extension publication entitled Water
Facts #10—Testing Your Drinking Water available
Many homeowners question whether they can collect from your Extension office or online at:
their own water samples and deliver them to an http://pubs.cas.psu.edu/FreePubs/pdfs/XH0023.pdf
independent laboratory to save on testing costs.
While this method will save money, it is important to 8) Include Water Resource Protection in Your Lease
realize that test results from water samples collected Many of the aforementioned ideas for protecting a
by the homeowner are generally not recognized in water supply can be stipulated in a gas leasing
legal proceedings because they are not independent. agreement (if a lease is offered by the gas
As a result, samples collected and submitted by company). The lease agreement provides an
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