Samples will be collected to characterize all work operations involved in the
Oil Spill remediation effort. Currently, all job categories have been identified
and will be separated into 3 general zones of activities. These zones are
identified as:
- Work activities in the off-shore remediation operations;
- Work activities in the near-shore remediation operations and;
- Work activities
in the on-shore remediation operations.
These activities are listed in the
attached spread sheet with a notation about the personal protective equipment (PPE)
requirements identified for each task. Sampling will be identified as Personal
Samples, Area Samples, Bulk Sample, Direct Reading Sample or Noise sampling. If
Possible bulk samples will be taken at each location sampled. Bulk samples will
be taken with a glass vile. The range with the number of results and the
appropriate mean value for each category will be listed in the column labeled as
results next to the appropriate sample type. GPS coordinates of samples taken
will be identified, including state if possible. Results will be compared to the lowest known Occupational Exposure Limit for the listed contaminant for purposes of risk assessment and PPE recommendations.
| Summary of
Air Sampling |
| Oil |
| Media |
Analyte(s) |
Sampling time and flow rate |
Method |
| SKC 575-002 Passive Sampler or charcoal tube |
Benzene, cyclohexane, toluene, ethyl benzene,
xylene, trimethylbenzes |
4 hour for SKC 575-002,
4 hour at 0.05 L/min for charcoal tube
|
OSHA Method 7
OSHA Method 111
OSHA Method 1002
OSHA Method 1005
|
| Charcoal tube |
Petroleum distillates |
4 hour at 0.05 L/min |
OSHA Method 48 |
| ULTRA I Passive Sampler containing Tenax TA |
Heavy aliphatics and aromatics |
Minimum of 4 hours, maximum of 16 hours |
OSHA Maries Project Study |
| Assay Technology ChemDisk Aldehyde Monitor |
Formaldehyde |
4 hour (TWA) |
OSHA Method 1007 |
|
Dispersants |
| Media |
Analyte(s) |
Sampling time and flow rate |
Method |
| SKC 575-002 Passive Sampler or charcoal tube |
2-butoxyethanol |
4 hour for SKC 575-002,
4 hour at 0.05 L/min for charcoal tube
|
OSHA Method 83 (must be separate sample from
other analytes due to different extracting solvent) |
| OVS-7 tube |
Propylene glycol |
2 hour at 1 L/min |
OSHA Method PV2051 |
| Acid
Gases/Mist |
| Media |
Analyte(s) |
Sampling time and flow rate |
Method |
| Silica Gel Tube with pre-filter |
Acid Gases and Mists |
0.2 L/Min for eight hours |
OSHA Method ID-165SG |
Sampling for Aromatics
Sample side by side with charcoal tubes and SKC 575-002 badges to establish the
correspondence in exposure levels between the two samplers and the levels of
exposure to the following chemicals:
- Cyclohexane
- Benzene
- Toluene
- Ethyl benzene
- Xylene
- Petroleum Distillates
- SKC 575-002 Diffusive Sampler collect for 4 hours, and request analysis
for cyclohexane, benzene, ethyl benzene, xylene and Q115 (Q115 is a
qualitative/quantitative analysis of any chemicals found on the sampler which
were not requested by the industrial hygienist).
- Charcoal tubes collect at 0.05 L/min for 4 hours and request cyclohexane,
benzene, toluene, ethyl benzene, xylene, petroleum distillates, and Q115 (Q115
is a qualitative/quantitative analysis of any chemicals found on the sampler
which were not requested by the industrial hygienist). (If there is
correspondence between the charcoal tubes and the 575-002 Passive Samplers,
then the charcoal tube sampling will be discontinued).
Sampling for Dispersants
- In areas where the dispersant has been sprayed collect with SKC 575-002
Passive Sampler for 4 hours and request analysis for 2-butoxyethanol
- In areas where the dispersant has been sprayed collect with OVS-7 tubes at
1 L/min for 2 hours and request analysis for propylene glycol
Sampling for Heavy Aliphatics and Aromatics
- To characterize the low levels of less volatile chemicals and heavy
aliphatics in the exposures collect with ULTRA I Tenax TA Passive Sampler for
up to 16 hours (minimum time of 4 hours) and request analysis for Mass spec (IMIS
code M125). Once the chemicals are characterized the less volatile chemicals,
sampling with this sampler will be discontinued.
Sampling for Formaldehyde
- In areas where there is potential exposure to combustion products of
burning of oil, collect with ChemDisk Aldehyde Passive Sampler for 4 hours.
Submit at least one blank for each set of samples. Keep samplers cool before
and after sampling. Follow manufacturer’s instructions.
Sampling for Acid Gases
In areas where there is potential exposure to combustion products of burning of
oil and other contaminants collect representative samples with pre-filtered
silica gel tubes for acid gases . Submit at least one blank for each set of
samples. Keep samplers cool before and after sampling. Follow manufacturer’s
instructions.
Since the method analyte is the acid ion, any other sources for the ion will be
a positive interference. The main concern along the Gulf coast and on the water
would be salt spray interfering with the hydrogen chloride analysis. A large
part of this could be mitigated through the use of a pre-filter which would
capture any spray before the air enters the sampling tube.
The sampling strategy may change due to the results found.
OSHA Salt Lake Technical Center is getting the Reporting IDs for this emergency
response.
Special sample handling:
- Store samples in a cooler with plastic ice packet after sampling.
- Try to avoid sprays of water on samplers during sampling
- Use the Reporting ID of this emergency response on Form 91a so the results
can be tracked.
Emergency Response to Oil Spill
Additional Direct Reading Sampling:
Noise dosimeter measurements will be collected on job tasks where noise
screening indicates levels greater than 85 dba.
Direct reading instruments will be utilized as required to screen and or sample
for Ozone, Hydrogen Sulfide, Carbon Monoxide and VOC’s as indicated by job
characteristics.
Characteristics and OELs for Oil
In characterizing worker exposure we are relying on new recommended protective limits set by organizations such as the ACGIH, NIOSH and AIHA , and not on the older, less protective PELS. Results will be compared to the lowest known Occupational Exposure Limit for the listed contaminant for purposes of risk assessment and PPE recommendations.
| Oil Components
and Dispersants |
| Analyte |
OSHA PEL |
ACGIH TLV |
NIOSH REL |
AIHA
WEEL |
Vapor Pressure |
Odor Threshold |
CAS # |
IMIS |
| anthracene |
|
|
|
|
|
|
120-12-7 |
0227 |
| benzene |
1 ppm TWA
5 ppm STEL
0.5 ppm Action Level |
0.5 ppm TWA
2.5 ppm STEL
|
0.1 ppm TWA
1 ppm STEL |
|
10 kPa @ 20°C |
4.68 ppm |
71-43-2 |
0320 |
| benzo-alpha-pyrene |
|
|
|
|
|
|
50-32-8 |
0726 |
| butoxyethanol, 2- |
50 ppm TWA |
20 ppm TWA |
5 ppm TWA |
|
|
0.001 ppm |
111-76-2 |
0435 |
| chrysene |
|
|
|
|
|
|
218-01-9 |
0629 |
| Cyclohexane |
300 ppm TWA |
100 ppm TWA |
300 ppm TWA |
|
12.9 kPa @ 20°C |
25 ppm |
110-82-7 |
0810 |
| cyclohexane, methyl- |
500 ppm TWA |
400 ppm TW
500 ppm TLV |
400 ppm TWA |
|
37 mm Hg @ 20°C |
498 ppm |
108-87-2 |
1740 |
| decane |
|
|
|
|
0.17 kPa @ 25°C |
|
124-18-5 |
D166 |
| ethanol |
1000 ppm TWA |
1000 ppm TWA |
1000 ppm TWA |
|
59.3 mm Hg @ 20°C |
0.136 ppm |
64-17-5 |
1060 |
| ethyl acetate |
400 ppm TWA |
400 ppm TWA |
400 ppm |
|
76 mm Hg @ 20°C |
0.61 ppm |
141-78-6 |
1040 |
| Ethyl Benzene |
100 ppm TWA |
100 ppm TWA
125 ppm STEL |
100 ppm TWA
125 ppm STEL |
|
0.9 kPa @ 20° |
140 ppm |
100-41-4 |
1080 |
| naphthalene |
10 ppm TWA |
10 ppm TWA
15 ppm STEL |
10 ppm TWA
15 ppm STEL |
|
|
0.038 ppm |
91-20-3 |
1810 |
| n-hexane |
500 ppm TWA |
50 ppm TWA |
50 ppm TWA |
|
160 mbar @ 20°C |
|
110-54-3 |
1380 |
| octane |
500 ppm TWA |
300 ppm TWA |
75 ppm TWA
385 ppm C |
|
14 mm Hg @ 25°C |
5.75 ppm |
111-65-9 |
1957 |
| pentane |
1000 ppm TWA |
600 ppm TWA |
120 ppm TWA
610 ppm C |
|
|
31.6 ppm |
109-66-0 |
1990 |
| Petroleum Distillates |
2000 mg/m3 TWA |
|
350 mg/m3 TWA
1800 mg/m3 Ceiling
|
|
|
|
8002-05-9 |
2037 |
| phenanthrene |
|
|
|
|
|
|
85-01-8 |
2038 |
| Propylene Glycol |
|
|
|
50 ppm |
0.08 mm Hg @ 20°C |
|
57-55-6 |
P108 |
| pyrene |
|
|
|
|
|
|
129-00-0 |
2217 |
| Toluene |
200 ppm TWA
300 ppm Ceiling
500 ppm Peak |
20 ppm TWA |
100 ppm TWA
150 ppm STEL
|
|
3.8 kPA @ 25°C |
1.6 ppm |
108-88-3 |
2460 |
| undecane |
|
|
|
|
0.1 kPa @ 20°C |
|
1120-21-4 |
U106 |
| Xylene |
100 ppm TWA |
100 ppm TWA
150 ppm STEL |
100 ppm TWA
150 ppm STEL |
|
9 mm Hg @ 20°C |
0.62 ppm |
1330-20-7 |
2590 |
|