R 336.1232
R 336.1232 Methodology for determining initial threshold screening level.
Cite as Mich. Admin. Code R 336.1232
Rule 232. (1) The initial threshold screening level (ITSL) for each toxic air contaminant
shall be determined as follows:
(a) If an inhalation reference concentration (RfC) can be determined from best available
information sources, then the ITSL equals the inhalation RfC.
(b) If an ITSL cannot be determined under the provisions of subdivision (a) of this subrule
and an oral reference dose (RfD) can be determined through best available information and
data are not available to indicate that oral route to inhalation route extrapolation is
inappropriate, then the ITSL is determined as follows:
3
20
70
m
kg
x
RfD
Oral
ITSL
(c) If an ITSL cannot be determined under the provisions of subdivision (a) or (b) of this
subrule and an occupational exposure level (OEL) exists for the toxic air contaminant, then
the ITSL is determined as follows:
ITSL = OEL divided by 100
Where the OEL is the lowest value of either the national institute of occupational safety
and health (NIOSH) recommended exposure level listed in the NIOSH pocket guide to
chemical hazards or the time-weighted average or ceiling threshold limit value listed in the
TLVs and BEIs. The NIOSH Pocket Guide to Chemical Hazards is adopted by reference
in R 336.1902. TLVs and BEIs. Threshold Limit Values for Chemical Substances and
Physical Agents, and Biological Exposure Indices, is adopted by reference in R 336.1902.
(d) If an ITSL cannot be determined under the provisions of subdivision (a), (b), or (c) of
this subrule, then the ITSL may be determined from a 7-day, inhalation, no observed
adverse effect level (NOAEL) or lowest observable adverse effect level (LOAEL) as
follows:
ITSL
NOAEL
x
x hours
perday
hoursperday
35 100
24
exposed
ITSL
LOAEL
x
xUF x hours
perday
hoursperday
35 100
24
exposed
Where:
UF = A value from 1 to 10 determined on a case-by-case basis, considering type and severity
of effect.
The ITSL may be determined on a case-by-case basis using NOAELs or LOAELs from
repeated dose studies other than 7-day studies.
(e) If an ITSL cannot be determined under the provisions of subdivision (a), (b), (c), or
(d) of this subrule, then the ITSL may be determined from a 7-day, oral, NOAEL or
LOAEL as follows:
ITSL = NOAEL (mg / kg / day)
35 x 100
x W
I
x b
a
A
A
ITSL =
LOAEL
35 x 100 xUF x W
I
x b
a
A
A
Where:
WA = Body weight of experimental animal in kilograms (kg).
IA = Daily inhalation rate of experimental animal in cubic meters/day.
b = Absorption efficiency by the oral route of exposure.
a = Absorption efficiency by the inhalation route of exposure.
UF = A value from 1 to 10 determined on a case-by-case basis, considering type and severity
of effect.
The ITSL may be determined on a case-by-case basis using NOAELs or LOAELs from
repeated dose studies other than 7-day studies.
(f) If an ITSL cannot be determined under the provisions of subdivision (a), (b), (c), (d),
or (e) of this subrule, then the ITSL may be determined from an inhalation LC50 that is 4
or more hours in duration as follows:
ITSL
LC
x
50
500 100
Where:
LC50 = A calculated concentration of a chemical in air to which exposure for a
specific length of time is expected to cause death in 50% of a defined experimental animal
population.
(g) If an ITSL cannot be determined under the provisions of subdivision (a), (b), (c), (d),
(e), or (f) of this subrule, then the ITSL may be determined from a 1-hour inhalation LC50
as follows:
ITSL
LC
x
x
50
500 100 40
(h) If an ITSL cannot be determined under the provisions of subdivision (a), (b), (c), (d),
(e), (f), or (g) of this subrule, then the ITSL may be determined from an animal oral LD50
as follows:
ITSL = 1
500 x 1
40 x 1
100 x LD50 (mg / kg) x W
0.167 x I
A
A
Where:
LD50 = The dose of a chemical that has been calculated to cause death in 50% of
a defined animal population.
WA = Body weight of experimental animal in kilograms (kg).
IA =
Daily inhalation rate of experimental animal in cubic meters/day.
(i) If an initial threshold screening level cannot be determined under the provisions of
subdivision (a), (b), (c), (d), (e), (f), (g), or (h) of this subrule, then the initial threshold
screening level = 0.1 ug/m³.
(2) The averaging times to be used for ITSLs are as follows:
(a) If the ITSL is derived from an OEL as in subrule (1)(c) of this rule, then the averaging
time is 8 hours for ITSLs based on time-weighted average threshold limit values or
recommended exposure levels and 1 hour for ITSLs based on ceiling threshold limit values
or recommended exposure levels.
(b) If the ITSL is derived as in subrule (1)(a) or (b) of this rule, then the averaging time
is annual.
(c) If the ITSL is derived as in subrule (1)(d), (e), (f), (g), (h), or (i) of this rule, then the
averaging time is annual.
(d) The department may require shorter averaging times if necessary to provide adequate
protection from the acute effects of a toxic air contaminant.
Editor's Note: An obvious error in R 336.1232 was corrected at the request of the promulgating agency,
pursuant to Section 56 of 1969 PA 306, as amended by 2000 PA 262, MCL 24.256. The rule containing the
error was published in Annual Administrative Code Supplement, 2016. The memorandum requesting the
correction was published in Michigan Register, 2020 MR 24.