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RADIOACTIVITY IN SHALE
NORM & TENORM

Radioactivity is a very important topic, on multiple levels, when considering all the environmental impacts of fracking for oil and natural gas. While most media attention is focused on the chemicals going downhole in the fracking process, it is just as important to realize that 'Mother Nature' sends her own group of toxics back out of these Marcellus Shale wells in the flowback right away, and the produced water over time.

 
Two of these toxics are water soluble Radium 226 (Ra226) and Radium 228 (Ra228). An investigation by the New York Times in 2010 was very effective in demonstrating the presence of radioactivity in these fluids from Marcellus Shale wells. As an example of one fracked Marcellus well they researched, well #6H in Cross Creek County Park, Washington County, Pennsylvania, had alarming levels of Ra 226, Ra 228 along with Uranium 238 in the flowback liquids.
 
VIDEO: Shale Gas & Oil Radioactive Wastes from the Marcellus and Utica Shales

What are they, how are they managed, and should we be concerned? (1:09:24)

 


REJECTED WASTE TAKEN TO IDAHO
By Tara Kinsell, Observer-Reporter

July 11, 2013 - “Rice Energy has informed us that they have removed the roll-off boxes containing the TENORM material,” said John Poister, spokesperson for the Pennsylvania Department of Environmental Protection. “They have provided us documentation that the material was sent to a U.S. Ecology site in Idaho for proper disposal.” TENORM is an acronym for technologically enhanced naturally occurring radioactive material. It occurs when the levels of radioactivity that are present naturally are increased by human activities. The Rice Energy truck carrying the drill cuttings from a Center Township (Greene County, PA) well site set off the radiation warning system on April 19 while entering Max Environmental. The truck was immediately quarantined and tested to determine what type of radiation it contained, according to Poister. It was determined that the drill cuttings contained Radium 226 at a level of 96 microrem (mrem).

 

Source:
Pennsylvania DEP WASTE REPORT
2nd Half of 2013

This unconventional well waste was sent to:

US ECOLOGY IDAHO, INC.
GRAND VIEW, ID

Website: "The Company addresses the complex waste management needs of its customers, offering treatment, disposal and recycling of hazardous and radioactive waste, as well as a wide range of complementary field and industrial services. Services include: Hazardous waste, PCB, NORM, TENORM"

Wells listed in the waste report for
July 1 - December 31, 2013:

HARTLEY UNIT 6H - 12/26/2011
FLOWBACK FRACTURING SAND 
32.44 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, GERMAN TOWNSHIP
GPS: 39.914019 -79.883219

HARTLEY UNIT 7H - 12/26/2011
FLOWBACK FRACTURING SAND
32.44 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, GERMAN TOWNSHIP
GPS: 39.914017 -79.883272

HARTLEY UNIT 8H - 12/27/2011
FLOWBACK FRACTURING SAND
32.45 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, GERMAN TOWNSHIP
39.914017         -79.883325

HARTLEY UNIT 9H - 12/27/2011
FLOWBACK FRACTURING SAND
32.45 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, GERMAN TOWNSHIP
39.914017 -79.883378

HARTLEY UNIT 10H - 12/28/2011
FLOWBACK FRACTURING SAND
32.45 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, GERMAN TOWNSHIP
39.914014 -79.883433

HARTLEY UNIT 11H - 12/28/2011 
FLOWBACK FRACTURING SAND
32.45 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, GERMAN TOWNSHIP
39.914014 -79.883486

FRANKHOUSER UNIT 3H-A  3H - 1/12/2012
FLOWBACK FRACTURING SAND
48.61 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, LUZERNE TOWNSHIP
39.944019 -79.901514

FRANKHOUSER UNIT 4H - 9/29/2011
FLOWBACK FRACTURING SAND
48.61 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, LUZERNE TOWNSHIP
39.9441 -79.901528

FRANKHOUSER UNIT 5H - 9/29/2011
FLOWBACK FRACTURING SAND
48.61 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, LUZERNE TOWNSHIP
39.944142 -79.901536

FRANKHOUSER UNIT 6H - 9/29/2011
FLOWBACK FRACTURING SAND
48.62 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, LUZERNE TOWNSHIP
39.944183 -79.901542

CHICO UNIT 2H - 10/5/2011 
FLOWBACK FRACTURING SAND
23.57 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE  COUNTY, SPRINGHILL TOWNSHIP
39.746967 -79.858528

CHICO UNIT 3H - 10/5/2011
FLOWBACK FRACTURING SAND
23.57 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, SPRINGHILL TOWNSHIP
39.746978 -79.858478

KIKTA UNIT 1H - 10/19/2011 
FLOWBACK FRACTURING SAND
54.86 Tons - LANDFILL 
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, NORTH UNION TOWNSHIP
39.947036 -79.743575

KIKTA UNIT 2H - 10/21/2011
FLOWBACK FRACTURING SAND
54.87 Tons - LANDFILL 
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, NORTH UNION TOWNSHIP
39.947014 -79.743531

KIKTA UNIT 3H - 10/19/2011
FLOWBACK FRACTURING SAND
54.87 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, NORTH UNION TOWNSHIP
39.946989 -79.743486

KIKTA UNIT 4H - 10/23/2011
FLOWBACK FRACTURING SAND
54.87 Tons - LANDFILL 
CHEVRON APPALACHIA LLC OGO-39307 
FAYETTE COUNTY, NORTH UNION TOWNSHIP
39.946967 -79.743442

JACKSON FARMS UNIT 41H - 2/7/2012
FLOWBACK FRACTURING SAND
79.69 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, MENALLEN TOWNSHIP
39.967181 -79.809758

JACKSON FARMS UNIT 42H - 2/7/2012
FLOWBACK FRACTURING SAND
79.69 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, MENALLEN TOWNSHIP
39.967158 -79.809711

JACKSON FARMS UNIT 43H - 2/8/2012
FLOWBACK FRACTURING SAND
79.69 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307 
FAYETTE COUNTY, MENALLEN TOWNSHIP
39.967136 -79.809667

CHICO UNIT 1H - 10/5/2011 
FLOWBACK FRACTURING SAND 
23.56 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
FAYETTE COUNTY, SPRINGHILL TOWNSHIP
39.746956 -79.858581

GROOMS UNIT 5H - 8/29/2011 
FLOWBACK FRACTURING SAND 
27.71 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
GREENE  COUNTY, FRANKLIN TOWNSHIP
39.922006 -80.218442

GROOMS UNIT 6H - 8/29/2011
FLOWBACK FRACTURING SAND 
27.71 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
GREENE COUNTY, FRANKLIN TOWNSHIP
39.921994 -80.218392

GROOMS UNIT 7H - 8/28/2011
FLOWBACK FRACTURING SAND
27.71 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307 
GREENE COUNTY, FRANKLIN TOWNSHIP
39.921983 -80.218339

GROOMS UNIT 8H - 8/28/2011
FLOWBACK FRACTURING SAND
27.71 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
GREENE COUNTY, FRANKLIN TOWNSHIP
39.921972         -80.218289

GROOMS UNIT 12H - 8/27/2011
FLOWBACK FRACTURING SAND
27.71 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
GREENE COUNTY, FRANKLIN TOWNSHIP
39.921928 -80.218083

GROOMS UNIT 9H - 8/28/2011
FLOWBACK FRACTURING SAND
27.71 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
GREENE COUNTY, FRANKLIN TOWNSHIP
39.921961 -80.218236

GROOMS UNIT 10H - 8/28/2011
FLOWBACK FRACTURING SAND
27.71 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
GREENE COUNTY, FRANKLIN TOWNSHIP
39.92195 -80.218186

GROOMS UNIT 11H - 8/27/2011
FLOWBACK FRACTURING SAND 
27.72 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
GREENE COUNTY, FRANKLIN TOWNSHIP
39.921939 -80.218133

VRONA UNIT 1H-A 1H - 7/9/2011 
FLOWBACK FRACTURING SAND
42.51 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
GREENE COUNTY, CUMBERLAND TOWNSHIP
39.948139 -79.956894

FRYE UNIT 13H - 1/19/2012
FLOWBACK FRACTURING SAND 
72.42 Tons - LANDFILL 
CHEVRON APPALACHIA LLC OGO-39307
WESTMORELAND COUNTY, SALEM TOWNSHIP
40.365386 -79.480575

FRYE UNIT 14H - 1/19/2012
FLOWBACK FRACTURING SAND
72.43 Tons - LANDFILL 
CHEVRON APPALACHIA LLC OGO-39307 
WESTMORELAND  COUNTY, SALEM TOWNSHIP
40.365425 -79.480564

FRYE UNIT 15H - 1/20/2012
FLOWBACK FRACTURING SAND
72.43 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
WESTMORELAND COUNTY, SALEM TOWNSHIP
40.365467 -79.48055

MATTY-MOMYER UNIT - 5/9/2012 
FLOWBACK FRACTURING SAND
30.03 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
WESTMORELAND COUNTY, SOUTH HUNTINGDON TWP
40.184806 -79.721361

MATTY-MOMYER UNIT - 5/9/2012
FLOWBACK FRACTURING SAND
30.04 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
WESTMORELAND COUNTY, SOUTH HUNTINGDON TWP
40.184828 -79.721317

DERMOTTA UNIT 2H-A  2H - 4/26/2012
FLOWBACK FRACTURING SAND
11.8 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
WESTMORELAND COUNTY, SEWICKLEY TOWNSHIP
40.275631 -79.765122

DERMOTTA UNIT 3H - 2/21/2012 
FLOWBACK FRACTURING SAND
11.81 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
WESTMORELAND COUNTY, SEWICKLEY TOWNSHIP
40.275692 -79.76505

DERMOTTA UNIT 4H - 2/22/2012 
FLOWBACK FRACTURING SAND 
11.81 Tons - LANDFILL
CHEVRON APPALACHIA LLC OGO-39307
WESTMORELAND COUNTY, SEWICKLEY TOWNSHIP
40.275722 -79.765017
  


New York Times article
February 26, 2011

We learn from this New York Times article that radiation levels in the wastewater from Cross Creek Park 6H OG Well were off the chart! Some of the locations for dumping that brine (wastewater) were listed, but the largest amount of brine was disposed of at a location NOT LISTED.

Below is part of a table from a DEP Production Report.
The largest quantity of this highly radioactive brine
went to an unknown location:

 

CROSS CREEK COUNTY PARK

6H

Drilling

510

ADVANCED WASTE - NEW CASTLE

CROSS CREEK COUNTY PARK

6H

Brine

65

PA BRINE TRT - FRANKLIN PLT

CROSS CREEK COUNTY PARK

6H

Drilling

595

TUNNELTON LIQUIDS COMPANY

CROSS CREEK COUNTY PARK

6H

Brine

4008

NOT LISTED

NYT Story: http://www.nytimes.com/2011/02/27/us/27gas.html
Map: http://www.nytimes.com/interactive/2011/02/27/us/natural-gas-map.html


 
USGS - Published September 7, 2011
Online Document       PDF - 1.08MB

Radium Content of Oil- and Gas-Field Produced Waters in the Northern Appalachian Basin (USA)

Excerpts below: Cross Creek 6H is Well/Sample ID 11.1 and 11.2
 

 
 
 
 
 

Flowback & Produced Water (Brine)
from Cross Creek County Park 6H
PA DEP Permit #125-22830

Date of Samples: 4-9-2009 & 6-29-2009

Radium 226 in Brine (pCi/L) 951
Radium 226 in Brine (pCi/L) 1,280

Radium 228 in Brine (pCi/L) 703
Radium 228 in Brine (pCi/L) 1,110

Total Radium in Brine (pCi/L) 1,654
Total Radium in Brine (pCi/L) 2,390

TDS (mg/L) 157,000
TDS (mg/L) 200,000

Uranium 238 in Brine (pCi/L) 90

Benzene 880 ppb

(For comparison's sake, the Federal
drinking water limit is 5 pC/iL)


RADIUM  Source: EPA webpage on Radium
Radium forms when isotopes of uranium or thorium decay in the environment. Most radium (radium-226) originates from the decay of the plentiful uranium-238. Radium is a naturally radioactive, silvery-white metal when freshly cut. It blackens on exposure to air.

The various isotopes of radium originate from the radioactive decay of uranium or thorium. Radium-226 is found in the uranium-238 decay series, and radium-228 and -224 are found in the thorium-232 decay series.

Radium-226, the most common isotope, is an alpha emitter, with accompanying gamma radiation, and has a half-life of about 1600 years. Radium-228, is principally a beta emitter and has a half-life of 5.76 years. Radium-224, an alpha emitter, has a half life of 3.66 days. Radium decays to form isotopes of the radioactive gas radon.


Study says Pennsylvania drilling
water high in radium

September 4, 2012 - The Marcellus shale absorbs uranium from ancient saltwater trapped within the rock layer. The decaying uranium then leaks radium into the water. As the wells continue to produce oil and gas, Engle said the brine becomes saltier and more radioactive.

For its study, the Geological Survey examined 52 samples of Marcellus shale brine collected from wells in New York and Pennsylvania from 2009 through 2011. In 37 of the samples, radioactivity from radium-226 and radium-228 was at least 242 times higher than the drinking-water standard and at least 20 times higher than the industrial standard. That included a sample collected Dec. 21, 2009, in Tioga County, Pa., that was 3,609 times higher than the drinking water standard and 300 times higher than the industrial.

Story

Where was this liquid waste (*brine*) disposed of?

Someone's glass of water?

Pennsylvania DEP reports indicate that the fate of the majority of that radioactive wastewater (168,336 gallons) is unknown, most of the wastewater at that time was being taken to sewage treatment plants, diluted with processed sewage, and dumped into the rivers around Pittsburgh; the drinking water source for hundreds of thousands of local residents.

Who says that fracking has never contaminated water? Indeed, it has contaminated drinking water for hundreds of thousands, if not millions of people living near shale drilling. This page will provide further evidence linked to the radioactivity, and solubility, of that threat to the safety, health and welfare of those living close to, or downstream from shale fracking.


 

 
The Railroad Commission of Texas (RRC) provides this summary on Naturally Occurring Radioactive Materials (NORM)

 

 
NORM in the Oil and Gas Field
Source: RRC

NORM encountered in oil and gas exploration, development and production operations originates in subsurface formations, which may contain radioactive materials such as uranium and thorium and their daughter products, radium 226 and radium 228. NORM can be brought to the surface in the formation water that is produced in conjunction with oil and gas. NORM in these produced waters typically consists of the radionuclides, radium 226 and 228. In addition, radon gas, a radium daughter, may be found in produced natural gas.

Because the levels are typically so low, NORM in produced waters and natural gas is not a problem in Texas unless it becomes concentrated in some manner. Through temperature and pressure changes that occur in the course of oil and gas production operations, radium 226 and 228 found in produced waters may co-precipitate with barium sulfate scale in well tubulars and surface equipment. Concentrations of radium 226 and 228 may also occur in sludge that accumulates in oilfield pits and tanks. These solids become sources of oil and gas NORM waste.

In gas processing activities, NORM generally occurs as radon gas in the natural gas stream. Radon decays to Lead-210, then to Bismuth-210, Polonium-210, and finally to stable Lead-206. Radon decay elements occur as a film on the inner surface of inlet lines, treating units, pumps, and valves principally associated with propylene, ethane, and propane processing streams.

Workers employed in the area of cutting and reaming oilfield pipe, removing solids from tanks and pits, and refurbishing gas processing equipment may be exposed to particles containing levels of alpha-emitting radionuclides that could pose health risks if inhaled or ingested.
 

 
NORM AND TENORM
Source: U.S. Environmental Protection Agency
[Webpage]

 

 
TENORM
Source: EPA

The geologic formations that contain oil and gas deposits also contain naturally-occurring radionuclides, which are referred to as "NORM" (Naturally-Occurring Radioactive Materials). Geologists have recognized their presence since the early 1930s and use it as a method for finding deposits (Ma87).

Much of the petroleum in the earth's crust was created at the site of ancients seas by the decay of sea life. As a result, petroleum deposits often occur in aquifers containing brine (salt water). Radionuclides, along with other minerals that are dissolved in the brine, precipitate (separate and settle) out forming various wastes at the surface.

Because the extraction process concentrates the naturally occurring radionuclides and exposes them to the surface environment and human contact, these wastes are classified as TENORM.

TENORM contamination levels in equipment varied widely among types of equipment and geographic region. The geographic areas with the highest equipment readings were northern Texas and the gulf coast crescent from southern Louisiana and Mississippi to the Florida panhandle. Very low levels of TENORM were found in California, Utah, Wyoming, Colorado, and northern Kansas.

According to an API industry-wide survey, approximately 64 percent of the gas producing equipment and 57 percent of the oil production equipment showed radioactivity at or near background levels. TENORM radioactivity levels tend to be highest in water handling equipment. Average exposure levels for this equipment were between 30 to 40 micro Roentgens per hour (μR/hr), which is about 5 times background. Gas processing equipment with the highest levels include the reflux pumps, propane pumps and tanks, other pumps, and product lines. Average radiation levels for this equipment as between 30 to 70 μR/hr. Exposures from some oil production and gas processing equipment exceeded 1 mR/hr.

Gas plant processing equipment is generally contaminated on the surface by lead-210 (Pb-210). However, TENORM may also accumulate in gas plant equipment from radon (Rn-222) gas decay. Radon gas is highly mobile. It originates in underground formations and dissolves in the organic petroleum areas of the gas plant. It concentrates mainly in the more volatile propane and ethane fractions of the gas.

Gas plant scales differ from oil production scales, typically consisting of radon decay products which accumulate on the interior surfaces of plant equipment. Radon itself decays quickly, (its half-life is 3.8 days). As a result, the only radionuclides that affect disposal are the radon decay products polonium-210 (Po-210) and lead-210. Polonium-210 is an alpha emitter with a half-life of 140 days. Pb-210 is a weak beta and gamma emitter with a half-life of 22 years.
 

 
Q: What other ways can radiation leave the gas patch?
A: In the propane you burn.
[Complete PDF document]

 

 
Potential for elevated Radiation levels in Propane
Source: National Energy Board of Canada

In November of 1992 the National Energy Board received an incident report from Petroleum Transmission Company Ltd. with respect to elevated, but not unsafe, levels of radiation detected in propane. The origin of this radiation was determined to be natural occurring radioactive materials ("NORM") which occur as a result of radon, a radioactive gas, selectively dissolving in the propane fraction of natural gas liquids. Upon radioactive decay, radon gas is converted into radon progeny particulates.

These particulates can accumulate along internal surfaces of tubulars, filters and other equipment surfaces such as those found within extraction facilities or along the propane transmission pipelines. The particular radioactive species identified were radon 222 and radon progeny which are part of the natural uranium (U-238) decay series.

Alberta Occupational Health and Safety ("AOHS"), Radiation Health Branch conducted a further investigation and has since issued a report on its findings. Although the AOHS report indicates that no significant public health risk due to radon or radon progeny in propane product was found, AOHS recommends that the petroleum industry develop a quality assurance program to qualitatively measure the concentration of radon in propane prior to release to the open market. *

The report also indicates that workers are only receiving radiation exposures approaching the safe maximum annual limit when they come in direct contact with equipment and when contact is maintained for a complete work day. Survey measurements indicate that radon progeny are accumulating in various equipment.

Although worker proximity at this time does not currently pose a significant health risk, the continued build-up of radon progeny in on-line equipment could change the status quo when equipment is taken off-line for servicing or disposal. Removal of metal housings or machining of contaminated internal surfaces could present an unacceptable level of worker exposure either externally due to radiation emission from radon progeny or internally due to the possible inhalation of these particulates by workers not following acceptable contamination control procedures. Therefore, the report indicates that an on-going radiation monitoring program is a prudent option to consider by all companies with facilities having similar equipment in propane service.
 

 
Q: What other ways can radiation leave the gas patch?
A: In the natural gas you burn.
[Complete PDF document]
 

 
Radon in Natural Gas from Marcellus Shale
By Marvin Resnikoff, Ph.D.
Report submitted to the New York DEC

A significant public health hazard associated with drilling for natural gas in the Marcellus Shale formation must be seriously investigated by the New York State Department of Environmental Conservation (DEC).  This hazard is from radioactive radon gas and the potential for large numbers of lung cancer among natural gas customers.  This issue, which has been ignored in the DEC’s Draft Supplemental Environmental Impact Statement, must be addressed in a revised Impact Statement and before DEC issues any drilling permits. 

Unlike present sources for natural gas, located in Texas and Louisiana, the Marcellus Shale is considerably closer to New York consumers.  In addition, the radioactive levels at the wellheads in New York are higher than the national average for natural gas wells throughout the US.

 In this paper Radioactive Waste Management Associates calculates the wellhead concentrations of radon in natural gas from Marcellus Shale, the time to transit to consumers, particularly New York City residents, and the potential health effects of releasing radon, especially in the smaller living quarters found in urban areas.

 It is well known that radon (radon-222) is present in natural gas. Published reports by R H Johnson of the US Environmental Protection Agency and C V Gogolak of the US Department of Energy also address this issue.  Radon is present in natural gas from Marcellus Shale at much higher concentrations than natural gas from wells in Louisiana and Texas. 

Since radon is a decay product of radium-226, to calculate radon levels it is necessary to know the concentrations of radium-226,  Based on a USGS study and gamma ray logs (also known as GAPI logs) that we have examined, the radium concentrations in the Marcellus Shale is 8 to 32 times background. This compares to an average radium-226 in surface soil in New York State of 0.81 picoCuries per gram (pCi/g)

Using this range of radium concentrations and a simple Fortran program that simulates the production of radon in the well bore, and transit to the wellhead, we calculate a range of radon concentrations at the wellhead between 36.9 picoCuries per liter (pCi/L) to 2576 pCi/L. 

These wellhead concentrations in Marcellus shale are up to 70 times the average in natural gas wells throughout the U.S. The average was calculated by R.H.Johnson of the US Environmental Protection Agency in 1973 (pre-fracking) to be 37 pCi/L to a maximum of 1450 pCi/L.

In addition, the distance to New York State apartments and homes from the Marcellus formation is 400 miles and sometimes less.  This contrasts with the distance from the Gulf Coast and other formations which is 1800 miles.  At 10 mph movement in the pipeline, natural gas containing the radioactive gas, radon, which has a half-life of 3.8 days, will have three times the radon concentrations than natural gas originating at the Gulf Coast., everything else being equal, which it is not.

Being an inert gas, radon will not be destroyed when natural gas is burned in a kitchen stove. 

We calculate the number of excess lung cancer deaths for New York State.  Our results: the potential number of fatal lung cancer deaths due to radon in natural gas from the Marcellus shale range from 1,182 to 30,448.

This is an additional number of lung cancer deaths due to radon from Marcellus Shale over deaths from natural radon already impacting New York State homes and their residents.


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