AristaTek has received a request from
a PEAC customer that military Levels of Concern (LOCs)
for toxic chemicals be incorporated into the PEAC tool.
AristaTek listened, and the next PEAC revision will
contain this information.
The military Levels of Concern comes
from a Technical Guide document called “TG 230 Chemical
Exposure Guidelines for Deployed Military Personnel”.
The reference document was published in January 2002,
but updated addendums are also available. The document
is published by the U.S. Army Center for Health
Promotion and Preventive Medicine (USACHPPM).
Let us look at these military
chemical exposure guidelines and compare these numbers
with LOCs from other data sources. TG 230 Chemical
Exposure Guidelines for Deployed Military Personnel
A copy of this document and related
documents including the May 2003 addendum can be
obtained from the Internet at the USACHPPM site:
http://chppm-www.apgea.army.mil/desp/pages/samp_doc.htm
This document presents many
categories of LOCs, for short term exposures, long term
exposures, and for each category LOC by inhalation,
drinking water, and soil contamination. The LOCs
selected for incorporation into the PEAC tool are
inhalation values. Even within the short-term exposure
category are 1-hour, 8-hour, and 14-day military
exposure guidelines; also 10-minute and 24-hour exposure
guidelines for selected chemical warfare agents.
Long-term inhalation exposure numbers are for continuous
exposure for up to one year. For these different
categories, LOC values are presented for three health
levels, minimal, significant, and severe. Approximately
70 chemicals (about 20 more in the May 2003 addendum)
are considered in the short-term category; several more
chemicals are in the long-term (1-year exposure)
category. Exposure symptoms and odor detection limits
are listed for some of the chemicals.
All these different LOCs developed by
the U.S. Army for various categories may seem confusing.
Other organizations have stated LOC values intended for
different purposes, and have used different language to
describe the numbers. These numbers were developed by
Occupational Safety and Health Administration (OSHA),
U.S. National Institute for Occupational Safety and
Health (NIOSH), American Council of Governmental
Industrial Hygienists (ACGIH), U.S. Environmental
Protection Agency, American Industrial Hygiene
Association (AIHA), U.S. Department of Energy
Subcommittee on Consequence Assessment and Protective
Actions (SCAPA), and the National Research Council
(NRC)/Committee on Toxicology (COT). Before we look at
the numbers developed by the other organizations, let us
examine the military exposure guidelines (MEGs) for
Deployed Military Personnel.
As the name implies, the
LOC numbers are for deployed military personnel, e.g.
healthy young adults. Infants, children, the elderly, or
people whose health is already impaired, or sensitive
people are at additional risk. Some definitions for air
LOCs are as follow:
Military Exposure
Guidelines (MEGs)
|
1-hour duration, severe |
The airborne concentration
above which continuous exposure for 1 hour could
begin to produce life-threatening or lethal
effects in a small portion of individuals.
Increasing concentrations and/or duration of
exposure will increase incidence of lethality and
severity of non-lethal severe effects. |
|
1-hour duration, significant
|
The airborne concentration
above which continuous exposure for 1 hour could
begin to produce irreversible, permanent, or
serious health effects that may result in
performance degradation or incapacitate a small
portion of individuals. Increasing concentrations
and/or duration of exposure will increase
incidence and severity of effects. |
|
1-hour duration, minimal
|
The airborne concentration
above which continuous exposure for 1 hour could
begin to produce mild, non-disabling, transient,
reversible effects, if any. Such effects should
not impair performance. Increasing concentrations
and/or duration of exposure could result in
performance degradation, especially for tasks
requiring specific mental/visual acuity or
physical dexterity/strength. |
|
8-hour and 24 hour |
The airborne concentration
above which continuous exposure for 8 or 24 hours
could begin to produce mild, non-disabling,
transient, reversible effects, if any. Such
effects should not impair performance. Increasing
concentrations and/or duration of exposure could
result in performance degradation, especially for
tasks requiring specific mental/visual acuity or
physical dexterity/strength. |
|
14-day |
The airborne concentration for
a continuous exposure for up to 14 days (24
hour/day basis) that should not impair performance
and is considered protective against significant,
non-cancer effects. Increasing concentrations
and/or duration could result in performance
degradation or increase the potential for inducing
delayed/permanent disease (e.g. kidney disease or
cancer). |
|
1 year |
The airborne concentration for
a continuous exposure for up to 1 year (365 days,
24 hour/day basis) that is considered protective
against health effects including chronic disease
and increased risk to cancer (i.e., cancer risk
greater than 1 x 10-4). No performance
degradation or long-term health consequences are
expected with exposure at or below this level.
Increasing concentrations and/or duration could
result in performance degradation or increase the
potential for delayed/permanent disease (e.g.
kidney disease or cancer).
|
Deployed military personnel are
assumed to consist of relatively healthy and fit male
and non-pregnant female adults between the ages of 18 to
55 years, and an average weight of 70 kilograms (154
pounds). Predisposing factors such as illness (e.g.
asthma) or stress or life-style choices (e.g. smoking or
alcohol use) may alter susceptibility to the toxicant.
Comparison of 1-hour MEGs with ERPGs
The American Industrial Hygiene
Association has published Emergency Response Planning
Guidelines (ERPGs) representing airborne concentrations
of toxic chemicals for use by emergency responders in
case of a chemical spill. Three LOCs are published for
1-hour exposure, designated ERPG-1, ERPG-2, and ERPG-3.
These LOCs have been published for 110 chemicals as of
2004, and about 7 new chemicals are added each year. A
list of chemicals current as of 2002 is at http://www.bnl.gov/scapa/scapawl.htm.
The 2004 edition can be ordered from the American
Industrial Hygiene Association at a cost of $20 at https://www.aiha.org/webapps/commerce/product.aspx?id=AEAH04-559&cat=Books&subcat=NewTitles.
Definitions of ERPG-1, ERPG-2, and ERPG-3 are as
follows:
ERPG-1: The maximum airborne
concentration below which it is believed that nearly all
individuals could be exposed for up to one hour without
experiencing other than mild transient adverse health
effects or perceiving a clearly defined, objectionable
odor.
ERPG-2: The maximum airborne
concentration below which it is believed that nearly all
individuals could be exposed for up to one hour without
experiencing or developing irreversible or other serious
health effects or symptoms which could impair an
individual’s ability to take protective action.
ERPG-3: The maximum airborne
concentration below which it is believed that nearly all
individuals could be exposed for up to one hour without
experiencing or developing life-threatening health
effects.
Table 1. Comparison of ERPG and MEG
for 1-hour Exposure, Units: mg/m3.
|
Chemical |
ERPG-1 |
ERPG-2 |
ERPG-3 |
MEG-minimal |
MEG-significant |
MEG-severe |
|
Acrolein |
0.23 |
1.145 |
6.87 |
ND |
ND |
25 |
|
Ammonia |
17 |
105 |
525 |
17 |
77 |
766 |
|
Arsine |
NA |
1.6 |
4.8 |
NA |
0.54 |
1.6 |
|
Boron trifluoride |
2 |
30 |
100 |
0.6 |
16 |
39 |
|
Bromine |
0.65 |
3.27 |
32.7 |
0.16 |
1.6 |
56 |
|
Carbon disulfide |
3 |
156 |
1557 |
3 |
156 |
1557 |
|
Carbon monoxide |
230 |
403 |
575 |
NA |
95 |
330 |
|
Carbon tetrachloride |
126 |
629 |
4718 |
75 |
352 |
1070 |
|
Diborane |
NA |
1.13 |
3.4 |
0.34 |
1.13 |
4.2 |
|
Ethylene oxide |
NA |
90 |
900 |
14 |
81 |
360 |
|
Fluorine |
0.775 |
7.8 |
31 |
2.6 |
7.8 |
20.2 |
|
Formaldehyde |
1.2 |
12.3 |
31 |
1.2 |
12.3 |
31 |
|
Hexachlorobutadiene |
32 |
107 |
320 |
32 |
107 |
320 |
|
Hydrazine |
0.66 |
6.55 |
39.3 |
0.13 |
17 |
46 |
|
Hydrogen chloride |
NA |
30 |
234 |
2.7 |
33 |
149 |
|
Hydrogen cyanide |
NA |
11 |
27.5 |
2.2 |
7.8 |
16.6 |
|
Hydrogen fluoride |
1.64 |
16.4 |
41 |
0.82 |
19.7 |
36 |
|
Hydrogen sulfide |
0.14 |
58.8 |
140 |
0.71 |
38 |
70 |
|
Methyl bromide |
NA |
195 |
778 |
58.3 |
195 |
777 |
|
Methylene chloride |
695 |
2600 |
13880 |
695 |
2600 |
13880 |
|
Methyl mercaptan |
0.01 |
49 |
197 |
1 |
9.7 |
45 |
|
Nitric acid |
2.6 |
15.5 |
201 |
1.3 |
10 |
57 |
|
Phosgene |
NA
|
0.8 |
4 |
0.4 |
1.2 |
3 |
|
Phosphine |
NA |
0.7 |
7 |
NA |
0.42 |
1.5 |
|
Sulfur dioxide |
0.8 |
8 |
39 |
ND |
8 |
39 |
|
Sulfuric acid |
2 |
10 |
30 |
2 |
10 |
30 |
|
Toluene |
189 |
1131 |
3770 |
754 |
1923 |
10933 |
ND = not determined
NA = not available, data
insignificant
If the LOC numbers are compared,
sometimes the MEGs are the same as ERPGs as in the case
of methylene chloride and sometimes they are different.
The ERPG numbers for many chemicals had been published
when the military put together their MEG document in
2002 (revised May 2003) so it is not surprising that
they adopted the same numbers for some of the chemicals.
If the numbers are different, sometimes the MEGs are
higher and sometimes they are lower than the
corresponding ERPGs.
The U.S. Army (USACHPPM) used many of
the LOC numbers developed by the U.S. Environmental
Protection Agency (EPA), called Acute Exposure Guideline
Levels (AEGL), when forming the MEG list. The EPA AEGL
list is not the same as the AIHA ERPG list. Therefore
some of the MEG numbers are different.
Usually the LOC estimates are good to
roughly only one significant figure or even only one
order of magnitude. Calculations and conversion factors
artificially increase the apparent number of significant
figures. For example, the ERPG-1, ERPG-2, and ERPG-3 for
methylene chloride are 200, 750, and 4000 parts per
million (ppm) respectively. The conversion factor for
ppm to mg/m3 is 3.47. This converts to 695,
3600, and 13880 mg/m3 respectively, which are
the numbers published by the U.S. Army. For toluene, the
corresponding ERPG numbers are 50, 300, and 1000 ppm
which convert to 189, 1131, and 3770 mg/m3.
Why not express everything in parts
per million (ppm)? The units of ppm do not apply to
solid particulates, dusts, and some acid gases; airborne
concentrations must be expressed in “mass per unit
volume”, e.g. mg/m3 [milligrams per cubic
meter of air under standard conditions]. Gases and
liquid vapors in air can be expressed in units of ppm or
mg/m3 .
Acute Exposure Guideline Levels
(U.S. Environmental Protection Agency) and Temporary
Emergency Exposure Limits (U.S. Department of Energy).
Two additional lists that were
consulted when USACHPPM developed their MEGs were (1)
the Acute Exposure Guideline Levels (AEGLs) developed by
the Environmental Protection Agency (EPA) and (2)
Temporary Emergency Exposure Limits (TEELs) developed by
the Department of Energy Subcommittee on Consequence
Assessment and Protective Actions (SCAPA). The AEGLs
were developed for 10-minute, 30-minute, 1-hour, 4-hour,
and 8-hour exposures. The EPA defines three exposure
levels, as follows:
AEGL-1: The airborne concentration of
a substance at or above which it is predicted that the
general population, including “susceptible” individuals,
could experience notable discomfort, irritation, or
certain asymptomatic, non-sensory effects. However, the
effects are not disabling and are transient and
reversible upon cessation of exposure.
AEGL-2: The airborne concentration of
a substance above which it is predicted that the general
population, including “susceptible” individuals could
experience irreversible or other serious, long-lasting
health effects or impaired ability to escape.
AEGL-3: The airborne concentration of
a substance at or above which it is predicted that the
general population including “susceptible” individuals
could experience life-threatening health effects or
death.
“Susceptible” individuals may include
persons in the 40 to 65 age bracket, smokers, or people
who use alcohol; but not hyper-susceptible or
hypersensitive individuals.
The AEGL-1 and AEGL-2 levels are also
evaluated to ensure that the chemicals do not pose a
greater than 0.0001 increased risk for cancer.
The AEGL numbers are peer-reviewed
and published in the U.S. Federal Register. They
are also available at the EPA website at
http://www.epa.gov/opptintr/aegl/chemlist.htm.
The DOE SCAPA list of TEELs are a
temporary list designed to serve as interim ERPGs until
the final, peer-reviewed numbers are developed by AIHA.
As of 2004, AIHA has developed ERPGs for 110 chemicals
but the DOE SCAPA has developed numbers for
approximately 2000 chemicals. The DOE SCAPA list can be
obtained at the website,
http://www.bnl.gov/scapa/teels.htm.
Table 2. Comparison of AEGL and MEG
for 1-hour Exposure, Units: mg/m3.
|
Chemical |
AEGL-1 |
AEGL-2 |
AEGL-3 |
MEG-minimal |
MEG-significant |
MEG-severe |
|
Acrolein |
0.069 |
0.23 |
3.2 |
ND |
ND |
25 |
|
Ammonia |
21 |
77 |
770 |
17 |
77 |
766 |
|
Agent GB (sarin) |
0.0028 |
0.035 |
0.13 |
0.0028 |
0.035 |
0.13 |
|
Agent VX |
0.00017 |
0.0029 |
0.010 |
0.0017 |
0.0029 |
0.010 |
|
Arsine |
NR |
0.54 |
1.6 |
NA |
0.54 |
1.6 |
|
Boron trifluoride |
0.33 |
8.6 |
39 |
0.6 |
16 |
39 |
|
Bromine |
0.16 |
1.6 |
56 |
0.16 |
1.6 |
56 |
|
Carbon disulfide |
12.4 |
498 |
1493 |
3 |
156 |
1557 |
|
Carbon monoxide |
NR |
95 |
380 |
NA |
95 |
330 |
|
Carbon tetrachloride |
75 |
352 |
1070 |
75 |
352 |
1070 |
|
Diborane |
NR |
1.13 |
4.2 |
0.34 |
1.13 |
4.2 |
|
Ethylene oxide |
NR |
81 |
360 |
14 |
81 |
360 |
|
Fluorine |
2.6 |
7.8 |
20.2 |
2.6 |
7.8 |
20.2 |
|
Formaldehyde |
1.1 |
17.2 |
69 |
1.2 |
12.3 |
31 |
|
Hydrazine |
0.13 |
17 |
46 |
0.13 |
17 |
46 |
|
Hydrogen chloride |
2.7 |
33 |
131 |
2.7 |
33 |
149 |
|
Hydrogen cyanide |
2.2 |
7.8 |
16.5 |
2.2 |
7.8 |
16.6 |
|
Hydrogen fluoride |
0.82 |
19.7 |
36 |
0.82 |
19.7 |
36 |
|
Hydrogen sulfide |
0.71 |
38 |
70 |
0.71 |
38 |
70 |
|
Methyl mercaptan |
NR |
92.6 |
134 |
1 |
9.7 |
45 |
|
Nitric acid |
1.4 |
62 |
237 |
1.3 |
10 |
57 |
|
Phosgene |
NR |
1.2 |
3 |
0.4 |
1.2 |
3 |
|
Phosphine |
NR |
2.8 |
5 |
NA |
0.42 |
1.5 |
|
Sulfur dioxide |
0.66 |
2.6 |
71 |
ND |
8 |
39 |
|
Toluene |
754 |
1923 |
10933 |
754 |
1923 |
10933 |
NR = Not Recommended (EPA note)
As seen in table 2, the U.S. Army
adopted EPA’s AEGL Levels Of Concern for many chemicals
when formulating the MEGs. But there are also many
differences. In Event of a Chemical Release Airborne
Concentrations Vary
In the real world of a chemical
release, concentrations in the air will vary by orders
of magnitude as time progresses because of the chemical
mixing with air. Emergency Responders should use these
numbers (MEGs or ERPGs or AEGLs) as rough guidelines and
not as a sharp cutoff for “safe” and “dangerous”
conditions.
Even if a toxic chemical is released
at a constant rate, a sensor measuring the concentration
at a point downwind will see the concentrations vary
with time, typically as shown above. AristaTek, Inc.,
has performed many tests at the HazMat Spill Center near
Mercury, Nevada, where a toxic chemical surrogate was
released under different conditions, and concentrations
measured using sensors at various locations downwind. As
the chemical cloud passed over the sensors, data similar
to that plotted in the above graph was recorded.
Responders to releases must keep in mind that real-world
conditions do not produce constant concentrations out in
the field. Differences between listed MEG and ERPG or
AEGL Levels of Concern even by a factor of 2 do not have
a great deal of practical significance in an outdoor
situation.