niosh oil & gas extraction safety & health program
TRANSCRIPT
NIOSH Oil & Gas Extraction Safety &
Health Program
Exposure Assessment and Research Gaps
John Snawder, NIOSH, Cincinnati OHJohn Snawder, NIOSH, Cincinnati OH
Disclaimer: The findings and conclusions in this presentation have not been formally
disseminated by NIOSH and should not be construed to represent any agency determination
or policy.
NIOSH Oil & Gas Extraction Sector Program
The goal of the NIOSH Oil and Gas Extraction Safety and Health Program is to reduce the rate of injury and disease among workers in the oil and gas and disease among workers in the oil and gas extraction industry.
www.cdc.gov/niosh/programs/oilgas/goals
The program seeks to fulfill its goals through the
following:
• High Quality Research and Prevention Activities
NIOSH Oil & Gas Extraction Sector Program
• High Quality Research and Prevention Activities
• Practical Workplace Solutions
• Partnerships
• Research to Practices (r2p)
Spokane, WA
Oil and Gas Program Staff and Field
Research Locations
Denver, COCincinnati, OH
Anchorage, AK
http://www.cdc.gov/niosh/docs/2010-130/pdfs/2010-130.pdf
Web search: NIOSH, oil and gas field effort
1° Objectives (Health)
• Develop partnerships with oil and gas industry
• Review the work processes
• Identify potential chemical hazards• Identify potential chemical hazards
• Characterize risks for exposure (Exposure
assessment work)
• Evaluate significance of risks (> Occupational
Exposure Limits [OEL’s])
• Communicate findings
2° Objectives (if necessary)
• Identify potential / possible controls for
exposures
• Evaluate possible controls for exposure
• Trial proposed controls, reevaluate
Pumper trucks Blender and Sand trucks
Well head
Volatile Organic Compounds (VOC)
Real-time VOC Flow-back Pond
VOCs Detected above Flowback Pond• Air/CO2*
• Sulfur dioxide*, formaldehyde
• Butane
• Isopentane
• Pentane
• Propanol
• C6 aliphatic hydrocarbons
• Heptane
• Methyl cyclohexane
• C8 aliphatic hydrocarbons
• Toluene
• Octane
• Ethyl cyclohexane
• Ethyl benzene/xylene isomers
• Decahydronaphthalene
• Undecane
• Decamethylcyclopentasiloxane*
• Naphthalene
• Dodecane
• Methyl naphthalenes
• Diethyl phthalate*
• Butanal
• Hexane
• Isobutanol
• C7 aliphatic hydrocarbons
• 2-methyl hexane, 3-methyl
hexane
• Methyl cyclopentane
• Benzene
• Cyclohexane
• Ethyl pentane
• C9 aliphatic hydrocarbons
• C9-C12 aliphatic hydrocarbons
• including branched alkanes,
• alkenes, plus decahydro alkyl
• naphthalenes
• C9 & C10 alkyl benzenes
• Nonane
• Propyl benzene
• Octamethylcyclotetrasiloxane*
• Decane
VOCs Collected above Flow Back Pond
Respirable Silica
Respirable Silica Results by Location
Site > ACGIH TLV* > NIOSH REL* > OSHA PEL* Total # samples
A 24 (92.3%) 19 (73.1%) 14 (53.9%) 26
B 16 (84.2%) 14 (73.7%) 12 (63.2%) 19
C 5 (62.5%) 5 (62.5%) 4 (50.0%) 8
D 19 (90.5%) 14 (66.7%) 9 (42.9%) 21
E 25 (92.6%) 23 (85.2%) 18 (66.7%) 27
F 4 (40%) 1 (10%) 0 10
Total 93 (83.8%) 76 (68.5%) 57 (51.4%) 111
* Number of samples/%
Respirable Silica Results by Job Title
Job Title >ACGIH TLV* >NIOSH REL* >OSHA PEL* Total # samples
Blender Operator 15 (93.8%) 13 (81.3%) 8 (50%) 16
Chemical Truck Operator 3 (100%) 2 (66.7%) 2 (66.7%) 3
Fueler 2(100%) 0 0 2
Hydration Unit Operator 4 (80%) 2 (40%) 2 (40%) 5
Mechanic 2 (66.7%) 2 (66.7%) 0 3Mechanic 2 (66.7%) 2 (66.7%) 0 3
Operator, Data Van 1 (100%) 0 (0%) 0 1
Pump Truck Operator 0 (0%) 0 (0%) 0 1
Q.C. Tech 0 (0%) 0 (0%) 0 1
Roving Operator 2 (50%) 1 (25%) 0 4
Sand Coordinator 7 (70%) 5 (50%) 1 (10%) 10
Sand Truck Driver 1 (100%) 0 (0%) 0 1
Sand Mover Operator 46 (92%) 42 (84%) 37 (74%) 50
T-belt Operator 5 (83.3%) 5 (83.3%) 5 (83.3%) 6
Water Tank Operator 5 (71.7%) 4 (57.1%) 2 (28.6%) 7
Wireline Operator 0 (0%) 0 0 1
Total 93 (83.8%) 76 (68.5%) 57 (51.4%) 111
* Number of samples/%
Real-time Respirable Silicag
/m3
mg
/m
Diesel Particulate
Midday: Early a.m.
Diesel Particulate Exposure
• Exposures are episodic. Ultrafine particulates were
found to increase during periods of heavy pumping;
i.e., during hydraulic fracturing operations.
• Traffic and idling equipment are not major • Traffic and idling equipment are not major
contributors to exposure.
• Ambient wind and location in relation to the source
are major determinants of exposure.
mg
/m3
Diesel Particulate (ultrafine)m
g/m
Diesel Particulate as Elemental Carbon
Typical Sampling Week: 3/13 PBZ Samples Exceeded 20 µg/m3 EC
• Day 1: Samples collected = 4, 2 PBZ samples Exceeded 20 µg/m3; 26 and
41 µg/m3 (Sandmover operator and chemical hand)
• Day 2: Samples collected = 4, no PBZ samples Exceeded 20 µg/m3.• Day 2: Samples collected = 4, no PBZ samples Exceeded 20 µg/m3.
• Day 3: Samples collected = 4, 1 PBZ sample Exceeded 20 µg/m3; 52 µg/m3
water transfer operator downwind of pump.
• 2 Area Samples were taken in cab/operator area of a blender and water
unit. Both samples exceeded 20µg/m3; 40 and 42 µg/m3.
Chemicals
1,2,4-Trimethylbenzene Boric Acid Heptahydrate Polyethoxylated Alkanol (1)
1,3,5 Trimethylbenzene Boric Oxide Glutaraldehyde Polyethoxylated Alkanol (2)
2,2-Dibromo-3-Nitrilopropionamide Butan-1-01 Guar gum Polyethylene Glycol Mixture
2.2-Dibromo-3-Nitrilopropionamide Citric Acid Hemicellulase Enzyme Polysaccharide
2-butoxyethanol Crystalline Silica: Cristobalite Hydrochloric Acid Potassium Carbonate
2-Ethylhexanol Crystalline Silica: Quartz Hydrotreated light
distillate
Potassium Chloride
2-methyl-4-isothiazolin-3-one Dazomet Hydrotreated Light
Distilled
Potassium Hydroxide
5-chloro-2-methyl-4-isothiazotin-3-one Diatomaceus Earth Iron Oxide Prop-2-yn-1-01
Acetic Acid Diesel (use discontinued) Isopropanol Propan-2-01
Acetic Anhydride Diethylbenzene Isopropyl Alcohol Propargyl AlcoholAcetic Anhydride Diethylbenzene Isopropyl Alcohol Propargyl Alcohol
Acie Pensurf Doclecylbenzene Sulfonic Acid Kerosine Propylene
Alchohol Ethoxylated E B Butyl Cellosolve Magnesium Nitrate Sodium Ash
Alphatic Acid Ethane-1,2-diol Mesh Sand (Crystalline
Silica)
Sodium Bicarbonate
Alphatic Alcohol Polyglycol Ether Ethoxlated Alcohol Methanol Sodium Chloride
Aluminum Oxide Ethoxylated Alcohol Mineral Spirits Sodium Hydroxide
Ammonia Bifluoride Ethoxylated Octylphenol Monoethanolamine Sucrose
Ammonia Bisulfite Ethylbenzene Naphthalene Tetramethylammonium
Chloride
Ammonium chloride Ethylene Glycol Nitrilotriacetamide Titaniaum Oxide
Ammonium Salt Ethylhexanol Oil Mist Toluene
Ammonia Ferrous Sulfate Petroleum Distallate
Blend
Xylene
Aromatic Hydrocarbon Formaldehyde Persulfate Petroleum
Distillates
Aromatic Ketones Glycol Ethers (includes 2BE) Petroleum Naphtha
Real-time Exposures in Chemical Trailer
Airborne Aldehydes
• At ground level near “frac” tank: < 0.2 ppm (<0.82 mg/m3)
• At top of “frac” tank near opening: 0.21 ppm (0.85 mg/m3)**
• “Frac” tank head space: 0.44 ppm (1.76 mg/m3)
• ** NIOSH Ceiling 0.2 ppm (0.8 mg/m3)
Challenges • Large numbers of sub-contractors
• Constantly changing workforce
– hard to reach/track
– transient
• Rapidly evolving technology • Rapidly evolving technology
– drilling and completions
• Small companies
– little OH&S expertise
• Lack of baseline exposure data e.g., DPM, VOC’s, lead,
NORM, noise, thermal stress, biological monitoring, multiple exposure routes
DPM = diesel particulate matter, NORM = naturally occurring
radioactive materials VOCs = volatile organic compounds
Data Gaps (injuries, illness)
• Lack of specific injury or illness surveillance data
– Currently rely on BLS/CFOI/SOII data
• Does not include injury or illness rates specific to oil and gas
activities such as hydraulic fracturing
– young, transient workforce
– evolving technology
• Incomplete reporting of non-fatal injuries
– No mechanism for consistent and systematic collection
– Disincentives to reporting
Data Gaps (health hazards )
• Degree of physical hazard risks?
– noise, thermal stress, naturally occurring radioactive
materials (NORM) multiple exposure routes
• Biological monitoring?
• Extended work shift implications (fatigue)?• Extended work shift implications (fatigue)?
• Extent of chemical hazard exposure risks?
– mixed exposures (silica, DPM, VOCs, etc.)
– multiple exposure routes (inhalation, ingestion)
– dermal exposures (Pb, Solvents, PAH’s)
– take home exposure/transfer risks
PAHs = Polynuclear Aromatic Hydrocarbons
Thank You. Questions?
John Snawder513.533.8496 /[email protected]
Michael Breitenstein
Eric Esswein303.236.5946 / [email protected]
Michael Breitenstein513.533.8290/[email protected]