Showing posts with label Benzene. Show all posts
Showing posts with label Benzene. Show all posts

Monday, January 28, 2013

Fracking failures Colorado and the oil and gas Industry fear being published



Below are some of the most relevant talking points (COGCC facts) about OG/Frack Mining in Colorado.

Please feel free at any time to reach out to me with any questions. Stay tuned for new data/research coming as well.


Colorado Oil & Gas Conservation Commission Data and Failures

ü 43% of all operator spills result in groundwater contamination.

ü 3.1% of all operator spills result in surface water contamination.

ü 57% of all protective berms fail to prevent secondary industrial liquid waste migration.

ü 2003-2012 Weld County, CO - 1.7 million gallons of produced water and oil never recovered from the ground after operator spills. It's still in the environment.

ü 2.4 billion square feet of surface has been contaminated by 1,000 O&G surface spills. Study:1,000 spills in Weld County, CO

ü Laramie-Fox Hills Aquifer was contaminated with toluene and thermogenic gas by an O&G operation in 2009 - Weld County, CO

ü Colorado has 129,073 Completed O&G wells. ~48,000 are active and ~81,000 are inactive.

ü Early statistics show that ~55% of all abandoned wells are being re-entered/re-drilled.

ü Colorado has over 5,000 reported industrial waste spills on record.

ü There have been 3,552 oil and gas related public complaints filed with the COGCC.

ü The burden of expense has been shifted to the local emergency response departments to battle any fires or mishaps. This expense has been shifted by the oil and gas industry to citizen tax payers, meaning 'you.'

ü There have been 3,964 'Notice of Alleged Violations' filed by the COGCC.

ü There are 825 unique oil and gas operators listed at COGCC.

ü There are 693 'UIC SIMULTANEOUS DISPOSAL', 'UIC ENHANCED RECOVERY', 'UIC DISPOSAL' sites in Colorado. Approximately 300 are active.

ü There are over 5,000 pits in Colorado of all statuses.
ü There are 11 gas storage facilities in Colorado.
ü There are 168 gas processing plants in Colorado.
ü There are 183 gas compressor stations in Colorado.
ü There are 108 gas gathering systems in Colorado.

ü There are more than 4,000 active oil and gas wells closer to homes than the COGCC 350' setback mandates, thus denying the state to prevent or mitigate adverse impacts to human health... EPIC FAILURE BY THE STATE?

ü COGCC has failed to prevent or mitigate adverse environmental and human health impacts in accordance with their mission statement.



LARAMIE FOX-HILLS AQUIFER CONTAMINATION (EPA know frack fluid Toluene and thermogenic 'frack gas' contaminates private well water and Colorado's largest aquifer)



Home Explodes, Resident Transported to Burn Center - Cause: Orphaned Natural Gas Well 




KERR-MCGEE OIL & GAS BENZENE SPILL CONTAMINATES GROUNDWATER 17 UG/L 




GROUNDBREAKING - Air Pollution and Natural Gas Operations Air Study Report

http:www.fractivist.blogspot.com/2012/11/groundbreaking-air-pollution-and.html




SouthWestern Energy Sends Letter to COGCC - Recognizing Setback Loophole




*FOR IMMEDIATE RELEASE* SIERRA CLUB AND 12 OTHER ORGANIZATIONS DEMAND IMMEDIATE CLOSURE OF THE COGCC SETBACK LOOPHOLE




Hidden Climate Threat - Not so Hidden Really?




Research Published and sent to the Gov et al - The Gov clearly needs to admit the State of Colorado has failed to prevent adverse impacts to the environment and its citizens. Governor, you are grossly negligent!



O&G EXEMPTIONS





Much more in the blog have a look around...


Shane


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Wednesday, November 21, 2012

KERR-MCGEE OIL & GAS BENZENE SPILL CONTAMINATES GROUNDWATER 17 UG/L

THE BATTERY WAS SHUT IN. THE PETROLEUM HYDROCARBON IMPACTED SOIL IS BEING EXCAVATED. GROUNDWATER WAS ENCOUNTERED IN THE EXCAVATION AT ~4` BGS. LAB ANALYTICAL RESULTS CONFIRMED BENZENE IMPACTS TO GROUNDWATER ABOVE THE CGWQS AT A CONCENTRATION OF 17 UG/L.

OFFICIAL COGCC DOCX LINK


........................................................................................................

Date Rec'd:11/20/2012Report taken by:  BOB CHESSON
DocNum:2231131API number:  05-123 -18271Facility ID:  250468


Operator Information
Operator:KERR-MCGEE OIL & GAS ONSHORE LPOper. No.47120
Address:P O BOX 173779 ATTN: ASHLEY COCCIOLONE  DENVER , CO 80217-3779
Phone:(720 )929-6000Fax:(720 )929-7461
Operator Contact:PAUL  SCHNEIDER


Description of Spill:
Date of Incident:11/13/2012
Type of Facility:WELL


Well Name/No.
HSR-BARCLAY  2-28Fac. Name/No. 
County Name:WELD
qtrqtr: NWNEsection: 28township: 3Nrange: 66Wmeridian: 6



Volumes spilled and recovered (bbls)
Oil spilled:   Recvrd:   
Water spilled:   Recvrd:   
Other spilled:   0Recved:  0 

GW Impact?
 Y

Surface water impact?
 N

Contained within berm?
 N

Area and vertical extent of spill:
  - X   -

Current land use:
  AGRICULTURE

Weather conditions:
  60 DEG F, CLEAR
Soil/Geology description  UNKNOWN
Distance in feet to nearest surface water:  535
Depth to shallowest GW:  4
Wetlands:  2700Buildings:  1900
Livestock:  Water Wells:  320
Cause of spill:

HISTORICAL IMPACTS

Immediate Response:
THE BATTERY WAS SHUT IN. THE PETROLEUM HYDROCARBON IMPACTED SOIL IS BEING EXCAVATED. GROUNDWATER WAS ENCOUNTERED IN THE EXCAVATION AT ~4` BGS. LAB ANALYTICAL RESULTS CONFIRMED BENZENE IMPACTS TO GROUNDWATER ABOVE THE CGWQS AT A CONCENTRATION OF 17 UG/L.

Emergency Pits:
NA

How extent determined:
SOIL AND GROUNDWATER SAMPLES WILL BE COLLECTED FROM THE EXCAVATION. THE ANALYTICAL RESULTS AND EXCAVATION DETAILS WILL BE PROVIDED ON A FORM 27.

Further Remediation
WILL BE PROVIDED ON A FORM 27.

Prevent Problem:
A NEW TANK BATTERY WILL BE CONSTRUCTED.

Detailed Description:
FIELD CREWS DISCOVERED HISTORICAL PETROLEUM HYDROCARBON IMPACTED SOIL WHILE REMOVING THE OLD TANK BATTERY. THERE WAS NO INDICATION OF LEAKING DUMPLINES, TANKS OR FITTINGS. THE VOLUME OF THE RELEASE IS UNKNOWN.

Saturday, September 15, 2012

KERR-MCGEE OIL & GAS - INCIDENT CAUSED GROUNDWATER CONTAMINATION - BENZENE



WHILE HYDRO-VACING TO LOCATE UNTRACEABLE UNDERGROUND LINES, PETROLEUM HYDROCARBON-IMPACTED SOIL WAS DISCOVERED. A HOLE IN THE WATER DUMP LINE WAS DISCOVERED WHILE EXCAVATING THE IMPACTED SOIL. THE VOLUME OF THE RELEASE IS UNKNOWN.

Click image and docx to enlarge







Sunday, July 22, 2012

Biomonitoring Summary on Benzene - Oil and Gas



Biomonitoring Summaries are intended to provide a brief general overview about the chemical or chemical group, including usage, environmental pathways, sources of exposure, toxicology, health effects, and human exposure information.

Benzene
CAS No. 71-43-2

General Information
Benzene is a volatile chemical that is produced commercially from coal and petroleum sources. It is among the most abundantly produced chemicals in the U.S. and is used extensively as an industrial solvent, in the synthesis of numerous chemicals, and as an additive in unleaded gasoline (ATSDR, 2007).

Human exposure occurs primarily by inhaling benzene in ambient air (Hattemer-Frey et al., 1990; Wallace, 1996). Sources of benzene in the air may result from either natural (e.g., forest fires) or industrial sources. Among industrial sources, automobile emissions and vapor around gasoline filling stations contribute to benzene in air (ATSDR, 2007). Tobacco smoke contributes to benzene in indoor air (Duarte-Davidson, et al., 2001), and tobacco smoke is estimated to account for about half of the total estimated exposure to benzene (ATSDR, 2007). Indoor sources for benzene, which include the offgassing of building materials, account for a significant portion of a non-smoker's benzene exposure (Wallace, 1996; Wallace et al., 1987). The consumption of food, drinking water, and beverages are considered negligible sources of exposure unless benzene contamination has occurred, such as from leaking underground fuel storage tanks (ATSDR, 2007; Wallace, 1996). In recent years, less than five percent of domestic wells used for drinking water in the U.S. have been found to contain detectable amounts of benzene (Rowe et al., 2007). Workplace exposure to benzene may result from production, use, or transportation of petroleum products.

Benzene is well absorbed after inhalational, oral, or dermal exposure. In the blood, benzene is distributed rapidly throughout the body, especially into the brain and fatty tissues, and can cross the placenta. Benzene is metabolized in the liver, and some metabolites may be distributed to the bone marrow, where additional metabolism may result in toxic effects on hematopoietic cells (ATSDR, 2007; Ross, 2000). The primary benzene metabolites are phenol, catechol, hydroquinone, 1,2,4-benzenetriol, and to a lesser extent, trans, trans-muconic acid, which are eliminated in urine as glucuronide and sulfate conjugates (Ross, 2000). Urinary S-phenylmercapturic and t,t-muconic acids are used for monitoring workplace exposure. A very small amount of unchanged benzene is eliminated in the breath.

Accidental and intentional exposures to high concentrations of benzene vapor can lead rapidly to euphoria, central nervous system depression, cardiac arrhythmias, followed by unconsciousness and death (ATSDR, 2007). Workers have developed skin irritation following repeated dermal exposure and mucous membrane irritation following repeated vapor inhalation (ATSDR, 2007). Epidemiologic studies of workers in industries involving benzene have found that benzene exposure can cause bone marrow suppression and increases the risk of various leukemias (Savitz and Andrews, 1997). Supportive evidence for benzene carcinogenicity comes from animal studies and from in vitro studies demonstrating the clastogenic properties of benzene on blood forming cells (NTP, 1986; Ross, 2000). The background exposure levels for the general population have been estimated to be much lower than the estimated lowest effect level for benzene at which leukemia risk is increased (Duarte-Davidson, et al., 2001).

Workplace standards and guidelines for benzene have been established by OSHA and ACGIH, respectively. The U.S. EPA has established environmental and drinking water standards for benzene, and the FDA has established a bottled water standard. Benzene is classified as a known human carcinogen by IARC and by NTP. Information about external exposure (ie., environmental levels) and health effects is available from ATSDR at: http://www.atsdr.cdc.gov/toxprofiles/.

Biomonitoring Information
Levels of blood benzene reflect recent exposure. The median level of blood benzene observed in the NHANES 2003–2004 subsample appear slightly lower than the median level in a nonrepresentative subsample of adults in NHANES III (1988–1994) (Ashley et al., 1994), as well for other previous studies of the U.S. general population (Bonanno et al., 2001; Buckley et al., 1997; Sexton et al., 2005 and 2006; Lin et al., 2008), and studies from other countries (Brugnone et al., 1994; Navasumrit et al., 2005).

Smoking, residing, or working in urban areas and exposure to gasoline and petroleum products can result in blood benzene levels that are higher than those in the nonsmoking general population (Ashley et al., 1995; Carrer et al., 2000; Backer et al., 1997). The amount and duration of cigarette smoking increases the likelihood of higher blood benzene levels (Bonanno et al., 2001; Churchill et al., 2001; Lin et al., 2008). Workers exposed to gasoline fumes, such as garage mechanics, drivers, and street vendors, and workers exposed to solvent fumes have been found to have blood benzene levels as much as tenfold higher than levels in the general population (Brugnone, et al., 1994 and 1999; Moolenaar et al., 1997; Perbellini et al., 2002; Romieu et al., 1999).

Finding a measurable amount of benzene in blood does not mean that the level of benzene causes an adverse health effect. Biomonitoring studies of blood benzene can provide physicians and public health officials with reference values so that they can determine whether or not people have been exposed to higher levels of benzene than levels found in the general population. Biomonitoring data can also help scientists plan and conduct research on exposure and health effects.

Source: Centers for Disease Control and Prevention



Benzene belongs to a class of chemicals called volatile organic compounds, so called because they evaporate in the air. Benzene is made from coal and petroleum sources and is present in gasoline. As one of the most commonly-made chemicals in the United States, benzene is often used to make many other chemicals. Benzene is also present in cigarette smoke.

How People Are Exposed to Benzene

People are exposed to benzene by breathing it in the air. Benzene gets into the air from forest fires, car emissions, gasoline vapors, and tobacco smoke. People who work with petroleum products, including gasoline, are exposed to benzene by touching or breathing in the chemical.
Benzene also can be absorbed into the body by eating food or drinking water or other beverages contaminated with benzene. These exposures are less common than breathing in the chemical.

How Benzene Affects People's Health

Breathing in unusually high doses of benzene can cause difficulty in thinking, changes in heart function, unconsciousness, or death. In smaller amounts over longer periods of time, benzene can also decrease the formation of blood cells. Benzene is considered to be a cancer-causing chemical.

Levels of Benzene in the U.S. Population

In the Fourth National Report on Human Exposure to Environmental Chemicals (Fourth Report), CDC scientists measured benzene in the blood of 1,345 participants aged twenty years and older who took part in the National Health and Nutrition Examination Survey (NHANES) during 2003–2004. The prior survey period of 2001–2002 is also included in the Fourth Report. By measuring benzene in blood, scientists can estimate the amount of benzene that has entered people's bodies.
  • CDC researchers found benzene present in the blood of the majority of participants.
  • Prior research has shown that people who smoke have more benzene in their blood.
Finding a measurable amount of benzene in the blood does not mean that levels of benzene cause an adverse health effect. Biomonitoring studies on levels of benzene provide physicians and public health officials with reference values so that they can determine whether people have been exposed to higher levels of benzene than are found in the general population. Biomonitoring data can also help health scientists plan and conduct research on exposure and health effects.

For More Information




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MY TAKE
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What are the effects of Benzene exposure from the living within the heavy industry called; 'oil and gas?'  Does anyone truly know? Why not? Would it make sense for communities in Colorado to start their own biomonitoring?  All citizens must get this test done and keep the information as a baseline when future development occurs, you'll have a greater chance demonstrating the causal link of affects to your health from oil and gas development and fugitive emissions. 


I think that in Weld County, Colorado, the results from biomonitoring would be shocking. I will personally get the blood, urine summary done and publish the results when it is complete. I've lived far too long in Weld County and its time for me to go! I believe the oil and gas industry should not operate with federal and state exemptions that harm the environment or humans. Somehow, the 'cost factor' was sadly overlooked. We are all victims of the industry's greed.


Shane




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Saturday, July 21, 2012

Noble Energy & Petro-Canada Notice of Alleged Violation - Dumping Drilling Wastes Migrating into River


Click image to enlarge

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BEFORE THE OIL AND GAS CONSERVATION COMMISSION
OF THE STATE OF COLORADO
IN THE MATTER OF ALLEGED VIOLATIONS OF THE RULES AND REGULATIONS OF THE COLORADO OIL AND GAS CONSERVATION COMMISSION BY NOBLE ENERGY PRODUCTION, INC., WELD COUNTY, COLORADO
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)
)
)
CAUSE NO. 1V
ORDER NO. 1V-355
ADMINISTRATIVE ORDER BY CONSENT
(Pursuant to Rule 522.b.(3) of the Rules and Regulations of the
Colorado Oil and Gas Conservation Commission, 2 CCR 404-1)
FINDINGS
1. On January 22, 2007, the Colorado Oil and Gas Conservation Commission (“COGCC” or “Commission”) approved an Application for Permit-to-Drill (“APD”) submitted by Noble Energy Production, Inc. (“Noble”) for the Buxman I #26-6 Well (API No. 05-123-23401) (the “Well”), located in the SE¼ NW¼ of Section 26, Township 6 North, Range 66 West, 6th P.M.
2. On April 11, 2007, Weld County Environmental Health Services received a complaint regarding trucks dumping drilling wastes at a location in the SW¼ NE¼ of Section 33, Township 6 North, Range 66 West, 6th P.M., which at the time was owned by Mr. Buxman. The location is adjacent to the Cache la Poudre River.
3. On April 12, 2007, Weld County Staff conducted a site inspection and observed an area of approximately 300,000 ft2 adjacent to the river where water-based bentonitic drilling mud had been disposed. Weld County Staff referred the matter to COGCC Staff (the “Staff”) for investigation (COGCC Complaint No. 1175595).
4. On April 13, 2007, Staff inspected the mud disposal site. Staff identified Noble as one of two parties responsible for the drilling mud disposal. Staff directed Noble and Petro-Canada Resources (USA) Inc. (“Petro-Canada”), the other responsible operator, to cease drilling mud disposal at the site and take immediate steps to prevent drilling mud from migrating into the Cache la Poudre River. At Staff’s direction, Noble and the other responsible operator constructed earthen berms along portions of the river to prevent additional drilling mud from entering the river.
5. During the April 13, 2007 inspection, Staff collected a representative sample of the drilling mud for organic analysis. The sample had a total petroleum hydrocarbon (“TPH”) concentration of 115 mg/kg, which is below the concentration level found in Table 910-1 in effect at the time of 1,000 mg/kg for soil in sensitive areas, and a benzene concentration of 88 µg/kg, which is below the benzene concentration level of 0.17 mg/kg2 found in Table 910-1.
6. The landowners at the disposal site told Staff they had agreed to the disposal but did not have a written disposal agreement with any party. The landowners also told the Staff they did not intend to till the mud into their land, in that trees and brush piles made much of the disposal area unsuitable for tilling.
7. On April 20, 2007, Staff conducted a second site inspection. During this inspection, the Staff observed an area where it appeared that drilling mud may have previously entered the river. Staff estimated that less than five gallons of waste mud had migrated to the river. Corrective actions taken by Noble and Petro-Canada prevented more mud from reaching the river. A surface water sample taken at the point where the mud entered the river contained concentrations of benzene, toluene, ethylbenzene, and xylenes (“BTEX”) below the laboratory detection limit. Concentrations of BTEX compounds were trace or non-detect in a drilling fluid sample taken near the point of entry had trace amounts. Acting upon the assessment that site remediation had not yet begun, Staff instructed Noble and Petro-Canada to immediately remove all free liquids from the disposal site for off-site disposal.
8. On April 23, 2007, Noble notified the National Response Center of a release of drilling fluids.
9. On April 26, 2007, Staff issued a Notice of Alleged Violation (“NOAV”) #1175598 to Noble, which included alleged violations of the following COGCC rules:
a. Rule 324A.a., which requires operators to take precautions to prevent significant adverse environmental impacts to air, water, soil, or biological resources to the extent necessary to protect public health, safety and welfare;
b. Rule 907.a.(1), which provided at the time of the discharge that operators ensure that exploration and production (“E&P”) waste is properly stored, handled, transported, treated, recycled, or disposed to prevent threatened or actual significant adverse environmental impacts to air, water, soil or biological resources or to the extent necessary to ensure compliance with allowable concentration levels in Table 910-1, with consideration to WQCC ground water standards and classifications;
c. Rule 907.d.(3).B., which requires operators to dispose of water-based bentonitic drilling fluids by acceptable methods of land application, such as production facility construction and maintenance and lease road maintenance. Additionally, operators are required to obtain written authorization from the surface owner prior to land application of water-based bentonitic drilling fluids and to retain records about the disposal.
The NOAV required certain abatement or corrective actions to be taken by the operator by May 10, 2007. The actions required Noble to submit a Spill/Release Report Form 19 and a Site Investigation and Remediation Workplan, Form 27 to: describe the corrective actions previously taken by Petro-Canada, the other responsible operator; remove the remaining drilling mud; determine the approximate thickness of the mud; determine if shallow ground water at the disposal site was impacted; and provide COGCC copies of the written landowner disposal authorizations.
10. On April 30, 2007, Noble submitted a Form 19 (COGCC Document No. 2057592) to the COGCC. Noble determined that approximately 4,900 barrels of waste mud from the Well were disposed of by third-party contractors at the site. The disposed mud covered an area approximately 300,000 ft2 in a layer 3-to-5 inches deep. Noble and the other responsible operator removed approximately 1,540 barrels of free liquid from the disposal area after April 20, 2007 and before April 27, 2007.
11. On April 30, 3007, Noble submitted a Form 27 to the COGCC. Staff approved the Form 27 (COGCC Document No. 2057593) work plan with additional conditions on May 17, 2007. Pursuant to the approved Form 27 work plan, Noble and Petro-Canada removed the remaining drilling mud for disposal at their respective land farms. Noble also sampled soil and groundwater in the disposal area. Concentrations of BTEX, total volatile hydrocarbons including gasoline range organics, total extractable hydrocarbons and diesel range organics were all below regulatory standards in the soil. BTEX compounds were not detected in the sampled groundwater.
12. On May 8, 2007, Noble provided Staff with copies of Authorization Forms for Land Treatment of Water Based Betonitic Drilling Fluids between Rocky Mountain Energy Solutions and the landowners dated April 9, 2007.
13. Rule 523. specifies a base fine of One Thousand dollars ($1,000) for each day of violation of Rules 324A.a., 907.a.(1), and 907.d.(3)B. Rule 523.a.(3) specifies that “the maximum penalty for any single violation shall not exceed Ten Thousand dollars ($10,000) regardless of the number of days of such violation,” unless the violation results in significant waste of oil and gas resources, damage to correlative rights, or a significant adverse impact on public health, safety or welfare or the environment.
14. For purposes of this Administrative Order by Consent (“AOC”) only, Staff considers each violation to have occurred for a minimum of ten days, April 11, 2007 through April 20, 2007, inclusive. Further, Staff reserves the right to present evidence that any and all violations resulted in significant waste of oil and gas resources, damage to correlative rights, or a significant adverse impact on public health, safety or welfare or the environment, and, that as result of that impact, the maximum penalty of Ten Thousand dollars ($10,000), under Rule 523.a.(3), should not apply.
15. Noble violated Rule 324A.a. because it failed to take precautions to prevent significant adverse environmental impacts to air, water, soil, or biological resources to the extent necessary to protect public health, safety and welfare by allowing water based bentonitic drilling mud to be improperly disposed of. A base fine of Ten Thousand dollars ($10,000) has been calculated for the violation of Rule 324A.a.
16. Noble violated Rule 907.a.(1) because it failed to ensure that E&P waste, including water based bentonitic drilling mud, was properly stored, handled, transported, treated, recycled, or disposed to prevent threatened or actual significant adverse environmental impacts to air, water, soil or biological resources or to the extent necessary to ensure compliance with allowable concentration levels in Table 910-1, with consideration to WQCC ground water standards and classifications. A base fine of Ten Thousand dollars ($10,000) has been calculated for the violation of Rule 907.a.(1).
17. Noble violated Rule 907.d.(3)B. because it failed to dispose of water-based bentonitic drilling fluids by acceptable methods of land application, such as production facility construction and maintenance or lease road maintenance. Additionally, it failed to obtain written authorization from the surface owner prior to land application of water-based bentonitic drilling fluids and failed to retain records about the disposal. A base fine of Ten Thousand dollars ($10,000) has been calculated for the violation of Rule 907.d.(3)B.
18. Staff have calculated a base fine of Thirty Thousand ($30,000) dollars for those violations brought under this AOC.
19. Staff may reduce the fine amount if it finds mitigating circumstances as is provided for by Rule 523.d. Based on Noble’s cooperation with COGCC, its prompt response and thorough remediation efforts, evidence that the landowners had consented to the disposal operation, and Noble’s post-NOAV compliance history regarding waste drilling mud handling and disposal practices, Staff have reduced the fine amount from Fifty Thousand ($30,000) dollars to an adjusted fine of Twenty Thousand dollars ($20,000) for purposes of this AOC only. If the NOAV is not resolved by consent, Staff reserve the right seek the full amount of the base fine for each day for each violation without reduction for the factors described above or any other facts or circumstances.
20. Payment of the fine pursuant to this AOC does not relieve Noble from its obligations to complete abatement or corrective actions set forth in the NOAV, as may be amended or modified by Staff, or the approved Form 27.
21. Noble should execute this AOC no later than fourteen (14) days after the date it is executed by Staff for recommendation to the Commission for expedited approval. Fines may increase if this matter is not recommended for expedited approval.
22. Noble, or its successors or assigns, should be required to remain responsible for complying with this AOC, in the event of any subsequent sale of property.
23. Pursuant to Article IX, of the “Memorandum of Agreement” between the Water Quality Control Division (“WQCD”) and the COGCC, adopted February 15, 2000, Staff has conferred with WQCD enforcement staff in determining the monetary penalty against Noble for violations of WQCC standards for surface waters.
24. Noble agrees to the findings of this AOC only for the purpose of expeditiously resolving the matter without a contested hearing. Notwithstanding the above, Noble does not admit to any of the factual or legal determinations made by the Commission herein, and fully reserves its right to contest same in any future action or proceeding other than a proceeding to enforce this AOC.
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NO INSPECTIONS FOUND ON COGCC'S WEBSITE PER THIS UNIQUE API AND NO RECORD OF AN NOAV FILED.


You requested :Inspection Information
API Number:05-123-23401
New Inspection Search Results - No Records Found
Inspection
Date
Doc #Location IDInsp.
API #
Insp.
Status
Overall
Inspection Status
Overall I.R.
Pass/Fail
Overall F.R.
Pass/Fail
Violation
(Y/N)

Search Results - No Records Found
Inspection
Date
Doc #Insp.
Type
Insp.
Status
PA
P/F/I
Pass/Fail
P/F
Violation
Y/N




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There are no supporting documents indicating any formal rule violations and or associated fines. Was the Poudre River contaminated? Was the soil and or water tested for BTEX? What about downstream recipients of the water? I request the COGCC to provide all data regarding this alleged violation.Contact the COGCC's acting Director, Tom Kerr and ask him to respond: EMAIL LINK


Data compiled by: Shane Davis 
Source: COGCC 



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Monday, July 16, 2012

KERR-MCGEE O&G: Groundwater Impacted – REPORT CONFIRMED BENZENE GROUNDWATER IMPACTS

Date received 5/18/2012 


WELD COUNTY, COLORADO 


Operator: KERR-MCGEE OIL & GAS ONSHORE LP Oper. No. 47120 Address: P O BOX 173779 ATTN: ASHLEY COCCIOLONE DENVER , CO 80217-3779 Phone: (720 )929-6000 Fax: (720 )929-7461 Operator Contact: PAUL SCHNEIDER


Current land use: PASTURE
Ground water impacted: YES
Cause of spill: 'Historical Impacts - There was no indication that dump lines of tank fittings were leaking'



LINK

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Immediate Response:
THE WELLS WERE SHUT IN AND PETROLEUM HYDROCARBON IMPACTED SOIL IS BEING EXCAVATED. GROUNDWATER WAS ENCOUNTERED IN THE EXCAVATION AT ~7` BGS. THE LABORATORY ANALYTICAL REPORT CONFIRMED BENZENE GROUNDWATER IMPACTS (19 UG/L) ABOVE THE CGWQS.

Emergency Pits:
NA

How extent determined:
SOIL AND GROUNDWATER SAMPLES WILL BE COLLECTED FROM THE EXCAVATION. THE ANALYTICAL RESULTS AND EXCAVATION DETAILS WILL BE PROVIDED ON A FORM 27.

Further Remediation
WILL BE PROVIDED ON A FORM 27.

Prevent Problem:
HISTORICAL IMPACTS. THERE WAS NO INDICATION THAT DUMP LINES, TANKS OR FITTINGS WERE LEAKING.

Detailed Description:
DURING NEW TANK BATTERY CONSTRUCTION, FIELD CREWS ENCOUNTERED HISTORICAL PETROLEUM HYDROCARBON IMPACTED SOIL ASSOCIATED WITH AN ABANDONED CEMENT WATER TANK.


click image to enlarge






















Data Compiled by: Shane Davis
Source: COGCC

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