1. General Discussion
1.1 Background
1.1.1 History of
procedure
The OSHA Technical Center
has received many requests for a sampling and analytical procedure for
chloropicrin. Desorption studies using charcoal tubes, and Anasorb 747
showed 2.1% and 25.9% recoveries respectively. The following tubes
showed good desorption efficiencies using 1 mL ethyl acetate: XAD-4
(99.6%), XAD-7 (95.9%), Carbosieve S-III (103%), Porapak S (96.9%),
and Porapak R (98.3%). Many of these tubes showed breakthrough or poor
retention. XAD-4 had good retention and was chosen for this study. Two
XAD-4 tubes in series had no chloropicrin on the backup portion of the
second tube when 5 liters of 90% RH air was drawn through them. The 14
day storage study showed good recoveries for the samples stored under
ambient, dark conditions, but showed an 8.4% loss when stored under
room lights. Chloropicrin is light sensitive, and the samples should
be protected from light after collection as illustrated by the storage
at ambient conditions in room light. 1.1.2 Potential
workplace exposure (Ref. 5.1) Chloropicrin is used as a
larvacide, disinfecting cereals and grains, fumigant, soil
insecticide, grass and weed seed killer, as a war gas, and in
synthesis. The US production for 1982 was 2.91 × 109
grams. 1.1.3 Toxic Effects (This section is for
information purposes and should not be taken as the basis for OSHA
policy.) (Ref. 5.2)
Chloropicrin is a skin and eye irritant and
lacrymator causing irritation at concentrations as low as 0.3 ppm in
humans, depending on individual susceptibility. A concentration of 15
ppm could not be tolerated by any of the test subjects. Chloropicrin
causes irritation of upper respiratory passages followed by edema and
pneumonia. Gastrointestinal effects are nausea, vomiting, colic, and
diarrhea. Lethal rat doses were 340 ppm for 1 minute, or 110 ppm for
20 minutes. Reported human oral lethal dose ranges from 5 to 50
mg/kg.
1.1.4 Physical properties (Ref.
5.1):
Compound:
Synonyms: |
trichloronitromethane;
acquinite; nitrochloroform; Larvacide 100; Picfume; chlor-o-pic;
dojyopicrin; dolochlor; microlysin; pic-chlor; picride |
Molecular weight: |
164.39 |
Density: |
1.6558 |
Freezing point: |
-64°C |
Boiling point: |
112°C |
Odor: |
pungent (threshold is 1.1
ppm) |
Color: |
white to pale yellow oily
liquid |
Molecular formula: |
CCl3NO2 |
CAS: |
76-06-2 |
IMIS: |
0675 |
RTECS: |
48193 (PB6300000) |
DOT: |
UN 1580: NA
1583 | 1.2 Limit defining
parameters
1.2.1 The detection limit of the
analytical procedure is 0.01 ng, with a 1-µL injection volume. This is
the smallest amount which could be detected under normal operating
conditions.
1.2.2 The overall detection limit is 0.298 ppb
based on a 5 liter air volume. (All ppm amounts in this study are
based on a 5-L air volume.) 1.3
Advantages
1.3.1 The sampling procedure is
convenient. 1.3.2 The analytical method is reproducible
and sensitive.
1.3.3 Reanalysis of samples is
possible. 1.3.4 It may be possible to analyze other
compounds at the same time. 1.3.5 Interferences may be
avoided by proper selection of column and GC parameters.
1.4 Disadvantages
Samples and analytical standards must be protected from
the light. 2. Sampling
procedure
2.1 Apparatus
2.1.1 A calibrated personal sampling
pump, the flow of which can be determined within ±5% at the
recommended flow.
2.1.2 Sampling tubes containing XAD-4 resin.
A sampling tube consists of two sections of XAD-4 resin separated by a
glass wool plug or polyurethane plug. The front section contains 80 mg
and the backup section 40 mg. The sections are held in place with
glass wool plugs in a glass tube 4 mm ID × 70 mm. length, SKC or
equivalent. 2.2 Sampling
technique
2.2.1 Open the ends of the XAD-4 tubes
immediately before sampling.
2.2.2 Connect two tubes together
and connect them to the sampling pump with flexible
tubing. 2.2.3 Place the tubes in a vertical position to
minimize channeling, with the smaller section towards the
pump. 2.2.4 Air being sampled should not pass through
any hose or tubing before entering the XAD-4 tubes.
2.2.5
Separate the XAD-4 tubes and seal with plastic caps immediately after
sampling. Seal each sample lengthwise with OSHA Form-21 sealing
tape. 2.2.6 With each batch of samples, submit at least
one blank tube from the same lot used for samples. This tube should be
subjected to exactly the same handling as the samples (break ends,
seal, & transport) except that no air is drawn through
it. 2.2.7 Transport the samples (and corresponding
paperwork) to the lab for analysis. 2.2.8 Bulks submitted
for analysis must be shipped in a separate container from other
samples. 2.3 Desorption
efficiency Six tubes were liquid
spiked at loadings of 0.338 µg (0.0101 ppm), 1.69 µg (0.0503 ppm), 3.48
µg (0.104 ppm), and 6.95 µg (0.207 ppm) chloropicrin. They were allowed
to equilibrate overnight at room temperature. They were opened, each
section placed into a separate 2 mL vial, desorbed with 1 mL of the
desorbing solution for 30 minutes with occasional shaking, and analyzed
by GC-ECD. The overall average was 99.8%.(Table 2.3)
Table
2.3 Desorption Efficiency
|
Tube # |
0.338 µg |
1.69 µg |
3.48 µg |
6.95 µg |
|
1 |
101 |
100 |
99.7 |
98.9 |
2 |
96.4 |
103 |
99.9 |
98.7 |
3 |
102 |
100 |
100 |
99.2 |
4 |
101 |
97.9 |
99.9 |
98.8 |
5 |
99.2 |
99.3 |
99.6 |
98.9 |
6 |
101 |
102 |
98.6 |
99.0 |
average |
100 |
100 |
99.6 |
99.0 |
overall ave |
|
99.8 |
|
|
standard deviation |
±1.42 |
|
|
| 2.4 Retention
efficiency
2.4.1 Six tubes were liquid spiked
with 6.95 µg (0.207 ppm) chloropicrin and allowed to equilibrate
overnight. The next day a second XAD-4 tube was attached, and 5 liters
humid air (90% RH) was pulled through them at 0.1 L/min. The tubes
were opened, desorbed with ethyl acetate, and analyzed by GC-ECD. The
retention efficiency averaged 98.9%. There was no chloropicrin found
on the backup portions of the second tubes. (Table 2.4.1)
Table
2.4.1 Retention Study with 5 L
|
% Recovered |
Tube # |
Front tube |
Back tube |
|
|
'A' |
'B' |
'A' |
'B' |
Total |
|
1 |
76.5 |
16.3 |
7.1 |
0.0 |
99.9 |
2 |
89.7 |
8.9 |
2.4 |
0.0 |
101 |
3 |
74.6 |
15.8 |
7.6 |
0.0 |
98.0 |
4 |
90.7 |
5.5 |
1.8 |
0.0 |
98.0 |
5 |
77.1 |
14.8 |
6.2 |
0.0 |
98.1 |
6 |
83.9 |
10.4 |
4.0 |
0.0 |
98.3 |
|
|
|
average |
98.9 |
| 2.4.2 Six tubes were
liquid spiked with 5.96 µg (0.177 ppm) chloropicrin and allowed to
equilibrate overnight. The next day a second XAD-4 tube was attached,
and 10 liters humid air (89% RH) was pulled through them at 0.2 L/min.
The tubes were opened, desorbed with ethyl acetate, and analyzed by
GC-ECD. The retention efficiency averaged 97.5%. There was little
chloropicrin found on the backup portions of the second tubes. (Table
2.4.2)
Table
2.4.2 Retention Efficiency with 10 L
|
|
%
Recovered |
|
Tube # |
Front tube |
Back tube |
|
|
'A' |
'B' |
'A' |
'B' |
Total |
|
1 |
86.1 |
9.6 |
3.3 |
0.2 |
99.2 |
2 |
76.9 |
13.8 |
6.4 |
0.5 |
97.6 |
3 |
82.9 |
10.5 |
3.2 |
0.2 |
96.8 |
4 |
77.4 |
12.7 |
5.8 |
0.5 |
96.4 |
|
|
|
average |
97.5 |
| 2.5
Storage Twelve tubes were spiked
with 6.64 µg (0.198 ppm) chloropicrin and stored at room temperature
until opened and analyzed. Six tubes were stored in the dark, and six
tubes were stored under room lights. The recoveries averaged 98.3% for
the dark samples stored for 14 days. The samples stored under room
lights decreased to a 91.6% recovery when stored for 14 days. (Table
2.5)
Table 2.5 Storage
Study
|
Day |
%
Recovered |
|
Light |
Dark |
|
7 |
94.8 |
96.8 |
7 |
95.9 |
96.8 |
7 |
94.6 |
102 |
average |
95.1 |
98.5 |
14 |
91.5 |
99.8 |
14 |
93.4 |
98.4 |
14 |
89.9 |
96.4 |
average |
91.6 |
98.2 |
|
overall average |
93.4 |
| 2.6
Precision
The precision was calculated using the area
counts from six injections of each standard at concentrations
of 0.332, 1.66, 3.32, and 6.64 µg/mL chloropicrin in ethyl acetate
with 0.04 µL/mL methylene chloride internal standard. The pooled
coefficient of variation was 0.0134. (Table 2.6)
Table 2.6 Precision
Study
|
Injection Number |
0.322 µg/mL |
1.66 µg/mL |
3.32 µg/mL |
6.64 µg/mL |
|
1 |
80597 |
360994 |
693030 |
1355453 |
2 |
82315 |
358426 |
695874 |
1347293 |
3 |
79872 |
358399 |
696123 |
1351383 |
4 |
79852 |
358267 |
702018 |
1366389 |
5 |
84808 |
359793 |
700711 |
1379674 |
6 |
83235 |
359322 |
699542 |
1365029 |
Average |
81779 |
359200 |
697883 |
1360870 |
Standard
Deviation |
±2016 |
±1067 |
±3422 |
±11875 |
CV |
0.0247 |
0.00297 |
0.00503 |
0.00873 |
Pooled CV |
0.0134 |
|
|
|
| where:
2.7 Air
volume and sampling rate studied
2.7.1 The air volume studied is 5
liters. 2.7.2 The sampling rate studied is 0.1 liters
per minute. A maximum flow of 0.2 liters per minute may be
used. 2.8
Interferences
Suspected interferences
should be listed on sample data sheets.
2.9 Safety
precautions
2.9.1 Sampling equipment should be
placed on an employee in a manner that does not interfere with
work performance or safety.
2.9.2 Safety glasses
should be worn at all times.
2.9.3 Follow all
safety practices that apply to the workplace being
sampled.
3.
Analytical method
3.1 Apparatus
3.1.1 Gas chromatograph equipped with
an electron capture detector. A HP 5890 series II gas
chromatograph was used in this study.
3.1.2 GC column
capable of separating the analyte and an internal standard from
any interferences. The column used in this study was a 60 meter RTX-5
capillary column 1.0 µm d.f., 0.32 mm ID.
3.1.3 An
electronic integrator or some other suitable method of measuring peak
areas.
3.1.4 Two-milliliter vials with Teflon-lined
caps.
3.1.5 A 10-µL syringe or other convenient
size for sample injection.
3.1.6 Pipets for dispensing
the desorbing solution.
3.1.7 Volumetric flasks - 5
mL and other convenient sizes for preparing standards.
3.2 Reagents
3.2.1 Purified GC grade nitrogen,
hydrogen, and air.
3.2.2 Chloropicrin Reagent
grade
3.2.3 Ethyl acetate, Reagent
grade
3.2.4 Methylene chloride, Reagent grade 3.2.5
Desorbing solution of 0.04 µL/mL methylene chloride in ethyl
acetate. If methylene chloride is present in the workplace do not use
an internal standard. 3.3 Sample
preparation
3.3.1 Sample tubes are opened and the
front and back section of each tube are placed in separate 2-mL
vials.
3.3.2 Each section is desorbed with 1 mL of the
desorbing solution.
3.3.3 The vials are sealed
immediately and allowed to desorb for 30 minutes with occasional
shaking. 3.4 Standard
preparation
3.4.1 Standards are prepared by
diluting a known quantity of chloropicrin with the desorbing
solution.
3.4.2 At least two separate stock standards
should be made.
3.4.3 Dilutions of the stock standards
are made to cover the range of the samples.
3.4.4 A stock
solution of 1.0 µL/mL is 1.66 mg/mL, or 1.66 µg/µL. A dilution of 20
µL stock in 5 mL desorbing solution is 6.64 pg/mL. The range of
standards used in this study was 0.166 to 6.64 µg/mL.
3.5 Analysis
3.5.1 Gas chromatograph
conditions.
Flow rates (mL/min) |
Temperature (°C) |
Nitrogen
(make-up): 30 |
Injector:
140 |
Hydrogen
(carrier): 1.5 |
Detector: 300 |
Hydrogen
(detector): 30 |
Column:
100 |
Figure 1.
An analytical standard of 6.64 µg/mL chloropicrin in ethyl acetate
with 0.04 µL/mL methylene chloride internal
standard.
3.5.2 Peak areas are
measured by an integrator or other suitable means.
3.6 Interferences
(analytical)
3.6.1 Any compound having the general
retention time of the analyte or the internal standard used is an
interference. Possible interferences should be listed on the sample
data sheet. GC parameters should be adjusted if necessary so these
interferences will pose no problems.
3.6.2 Retention time
data on a single column is not considered proof of chemical identity.
Samples over the target concentration should be confirmed by GC/Mass
Spec or other suitable means. 3.7 Calculations
3.7.1 A curve with area counts versus
concentration is calculated from the calibration
standards.
3.7.2 The area counts for the samples
are plotted with the calibration curve to obtain the concentration of
chloropicrin in solution.
3.7.3 To calculate the
concentration of analyte in the air sample the following formulas are
used:
3.7.4 The above equations can be
consolidated to form the following formula. To calculate the ppm
of analyte in the sample based on a 5-liter air
sample:
µ/mL |
= concentration of
analyte in sample or standard |
24.46 |
=Molar
volume(liters/mole)at 25°C and 760 mmHg. |
MW |
=Molecular weight
(g/mole) |
DV |
=Desorption volume |
5 L |
=5 liter air sample |
DE |
=Desorption
efficiency |
3.7.5 This calculation is done for
each section of the sampling tube and the results added
together. 3.8 Safety
precautions
3.8.1 All handling of solvents should
be done in a hood.
3.8.2 Avoid skin contact with all
chemicals.
3.8.3 Wear safety glasses, gloves and a
lab coat at all times. 4. Recommendations for further study
A collection study should be
performed. 5.
References
5.1 Windholz, M., "The Merck Index",
Tenth Edition, Merck & Co., Rahway N.J., 1983, p.
333.
5.2 "Documentation of the Threshold Limit Values and
Biological Exposure Indices", Fifth Edition, American Conference of
Governmental |