Your pre-sampling and post-sampling pump calibrations using a primary standard are both 0.05 L/min. You collect personal samples on two employees working in the operation. The samples are collected for 430 minutes (Sample 1) and 440 minutes (Sample 2).
Calculate the sample volumes for each of the samples.
The laboratory reports that the front section of Sample 1 contains 5.000 pg of methyl n-amyl ketone and the back section contains 200 pg of methyl n-amyl ketone. The front section of Sample 2 contains 4.000 pg of methyl n-amyl ketone and the back section contains 50 pg of methyl n-amyl ketone. Neither the front nor back sections of the field blank you supplied contain any detectable levels of methyl n-amyl ketone.
1. Calculate the concentrations of the two personal samples in pg/L and mg/m'.
2. Convert the result to ppm (MN for methyl n-amyl ketone = 114.2).
3. Show all the steps for your calculations.
You then reference OSHA's Table Z-1 and find that the 8-hour TWA PEL for methyl n-amyl ketone is 100 ppm
Discuss how the results of the two personal samples you collected compare to the OSHA PEL. and describe the sampling method you implemented.
You also look up the ACGH TLV for methyl n-amyl ketone and find that the TLV is 50 ppm as an 8-hour TWA exposure.
Discuss how the results for the two personal samples compare to the ACCH TLV.
Discuss whether you would recommend comparing the results of your sampling to the OSHA PEL or the ACGIH TLV. Include your rationale for the choice. and explain how you would rationalize your choice to your employer.
Welding fumes are a common occupational exposure. Several different welding fumes can cause similar adverse health effects. Personal sampling of a welding operation at a manufacturing facility produced the following 8-hour Time-weighted average (TWA) results for individual metal fumes.
(R) Respirable fraction (I) hhalable fraction
Briefly summarize the primary health effects associated with overexposure to each type of metal fume. including both acute and chronic health effects. Explain what analytical methods you would use for evaluating health hazards in the workplace.
Identify the types of metal fumes that would produce similar health effects on an exposed worker. Calculate the equivalent exposure (in relation to OSHA PELS) for the metal fumes with similar health effects based on the -Result" column in the table above. Discuss whether you believe any of the individual metal fume exposures or the combined exposure exceeds an OSHA PEL or an ACGIH TLV.
1.Compound: Methyl-n-amyl ketone (2-Heptanone)
Sample Volumes;
Flow Rate; 0.05 L/min
Sample 1; (430/1)*0.05L=21.5L
Sample 2; (440/1)*0.05L=22L
Concentrations of personal samples in mg/L and mg/m3
C = (Wf + Wb - Bf – Bb) / V where Wf: analyte found in sample front
Wb: analyte found in sample back
Bf: average media blank front
Bf: average media blank back
In mg/L
Sample 1; (5000+200-0-0) / 21.5= 241.86046512mg/L
Sample 2; (4000+50-0-0) / 22= 184.09090941mg/L
In mg/L
Since mg/L=mg/L,
Sample 1=241.86046512mg/L
Sample 2=184.09090941 mg/L
In ppm
X ppm= (Y mg/L * 24.45) / M.W
M.W of C7H14O = 114.19
Sample 1; (241.86046512*24.45) / 114.19= 51.79 ppm
Sample 2; (184.0909091*24.45) / 114.19= 39.42 ppm
c.Comparison of NIOSH REL to OSHA PEL methods in concentration (in pm) results
Maximum Exposure Limit; NIOSH REL=100ppm
OSHA PEL= 100ppm
Both samples where within the range of the two methods.
Sampling method implemented; Calibration of each personal sampling pump with sampler in line, breaking the ends of the sampler immediately prior to sampling, attaching the sampler to personal sampling pump with flexible tubing and sampling at a known flow rate (0.05 L/min) (Bloomfield, Exner, Signorelli, & Scott, 2013).
Concentration (in pm) results of samples using ACGIH TLV method
Maximum Exposure Limit for ACGIH TLV; 50ppm
Thus, Sample 1 (51.79ppm) exceeded the maximum limit while Sample 2 (39.42ppm) was within range.
NIOSH 2553 method: This method was developed as part of an update of NIOSH Method 130 which combined the NIOSH Methods: the 2nd edition of the NIOSH Manual of Analytical Methods.
Major improvements over ACGIH TLV includes: lower LOD/LOQ values, improved DE recovery results (at lower levels) by using Anasorb CMS and 2% IPA in CS2, a 30 day storage stability study, and the replacement of the packed column with a Rtx-200 fused silica capillary column (Bloomfield, Stanwell-Smith, Crevel, & Pickup, 2006)
2: Homework AssignmentPrimary Health Effects of Metal Fumes
Metal Fume |
Similar metal |
Health Effect |
|
Acute |
Chronic |
||
Sb |
Cd |
Irritation to eyes, skin & lungs |
Potentiate pneumoconiosis |
Be |
Cu, Al |
“Metal fume Fever” |
Damage of respiratory tract |
Cd |
Cd, Zn alloys |
Irritation of respiratory System |
Kidney damages and emphysema |
Cr(VI) |
Steel |
Respiratory tract infections |
Dermatitis and |
Cu |
Brass |
Irritation to eyes, skin & lungs |
Prolonged fever |
Fe(oxides) |
Steel |
Irritation to eyes, skin & lungs |
Siderosis |
Mg(oxides) |
Nausea and vomiting |
Prolonged fever |
|
Mo |
Ni alloys |
Irritation to eyes, skin & lungs |
Shortness of breath |
Ni |
Inconel |
Irritation to eyes, skin & lungs |
Increased cancer risk |
Zn(oxides) |
Galvanized metal |
“Metal fume Fever” |
Alteration of zinc metabolism and bio distribution |
Analytical Methods for evaluation of health hazards in workplace; Atomic Absorption (AAS/AES) & Inductive Coupled Plasma (ICP) (Luby, et al., 2005).
E= C/OSHA PEL
Metal fume |
Equivalent Exposure (E) |
Sb |
(0.05/0.5)=0.1 |
Be |
(0.00001/0.002)=0.005 |
Cd |
(0.025/0.1)=0.25 |
Cr(VI) |
(0.02/1) =0.02 |
Cu |
(0.03/0.1) =0.3 |
Fe (oxides) |
(0.5/10) =0.05 |
Mg (oxides) |
(0.02/15) =0.0013 |
Mo |
(0.003/15) =0.0002 |
Ni |
(0.25/1) =0.25 |
Zn (oxides) |
(0.3/5) =0.006 |
References
Bloomfield, S. F., Stanwell-Smith, R., Crevel, R. W., & Pickup, J. (2006). Too clean, or not too clean: the Hygiene Hypothesis and home hygiene. Clinical and Experimental Allergy, 402–425.
Bloomfield, S., Exner, M., Signorelli, C., & Scott, E. A. (2013). Effectiveness of laundering processes used in domestic (home) settings. US: International Scientific Forum on Home Hygiene.
Luby, S., Agboatalla, M., Feikin, D., Painter, J., Billhimmer, W., Atref, A., & Hoekstra, R. M. (2005). Effect of hand-washing on child health: a randomized control trial. Lancet, 225–33.
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