United States      Prevention, Pesticides     EPA712-C-96-255
          Environmental Protection    and Toxic Substances     June 1996
          Agency        (7101)
&EPA   Health Effects Test
          Guidelines
          OPPTS 870.8360
          Pharmacokinetics of
          Isopropanal
                'Public Draft"

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                           INTRODUCTION
     This guideline is one of a series of test guidelines that have been
developed by the Office of Prevention, Pesticides and Toxic Substances,
United States Environmental Protection Agency for use in the testing of
pesticides and toxic substances, and the development of test data that must
be submitted to the Agency for review under Federal regulations.

     The Office of Prevention,  Pesticides and Toxic Substances (OPPTS)
has  developed this guideline through  a  process of harmonization that
blended the testing  guidance and requirements that existed in the Office
of Pollution Prevention and Toxics  (OPPT) and appeared in Title 40,
Chapter I,  Subchapter R of the Code of Federal Regulations  (CFR), the
Office of Pesticide Programs (OPP) which appeared in publications of the
National Technical  Information Service (NTIS) and the guidelines pub-
lished by the Organization for Economic Cooperation and Development
(OECD).

     The purpose of harmonizing these guidelines into a single set of
OPPTS  guidelines is to minimize variations among the testing procedures
that must be performed to meet the data requirements of the U. S. Environ-
mental Protection Agency under the Toxic  Substances Control Act (15
U.S.C. 2601) and the Federal Insecticide,  Fungicide and Rodenticide Act
(7U.S.C. I36,etseq.).

     Public Draft Access Information: This draft guideline is part of a
series of related harmonized guidelines that  need to  be considered as a
unit. For copies: These guidelines are available electronically from the
EPA Public Access  Gopher (gopher.epa.gov) under the heading "Environ-
mental Test Methods and Guidelines" or in paper by contacting the OPP
Public    Docket    at    (703)    305-5805    or     by    e-mail:
guidelines@epamail.epa.gov.

     To Submit Comments: Interested persons are invited to submit com-
ments. By mail: Public Docket and Freedom of Information Section, Office
of Pesticide Programs, Field Operations Division (7506C), Environmental
Protection Agency,  401  M  St.  SW.,  Washington, DC 20460. In  person:
bring to: Rm. 1132, Crystal Mall #2, 1921 Jefferson Davis Highway, Ar-
lington, VA. Comments may also be submitted  electronically by  sending
electronic mail (e-mail) to: guidelines@epamail.epa.gov.

     Final  Guideline Release: This guideline is available  from the U.S.
Government Printing Office, Washington, DC 20402 on The Federal Bul-
letin  Board.   By  modem   dial   202-512-1387,   telnet   and  ftp:
fedbbs.access.gpo.gov (IP 162.140.64.19),  or  call 202-512-0132 for disks
or paper copies.  This  guideline is also available electronically in ASCII
and PDF (portable document format) from the EPA Public Access  Gopher
(gopher.epa.gov) under the heading  "Environmental Test Methods and
Guidelines."

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OPPTS 870.8360  Pharmacokinetics of isopropanal.
     (a) Scope—(1) Applicability. This guideline is intended to meet test-
ing  requirements  of  both  the  Federal   Insecticide,   Fungicide,  and
Rodenticide Act (FIFRA) (7 U.S.C. 136, et seq.) and the  Toxic Substances
Control Act (TSCA) (15 U.S.C. 2601).

     (2) Background.  The source material  used in developing this har-
monized OPPTS test guideline is OPPT 40 CFR 795.231  Pharmacokinetics
of Isopropanal.

     (b) Purpose. The purpose of these studies is to ascertain whether the
pharmacokinetics and metabolism of the test substance are similar after
oral and inhalation administration; determine  bioavailability of the test sub-
stance  after oral and inhalation administration; and to  examine the effects
of repeated dosing on the pharmacokinetics and metabolism of  the test
substance.

     (c) Definitions. The definitions in section 3  of TSCA and in 40 CFR
Part  792—Good Laboratory Practice  Standards  (GLP) apply to this test
guideline. The following definitions also apply to  this test guideline.

     Bioavailability refers to the rate and relative amount of administered
test substance which reaches the systemic  circulation.

    Metabolism means the study  of the  sum of the processes by which
a particular  substance is handled in the body, and includes absorption,  tis-
sue distribution, biotransformation, and excretion.

     Pharmacokinetics  means the study of the rates of absorption, tissue
distribution, biotransformation, and excretion.

     (d) Test procedures—(1)  Animal  selection—(i)  Species.  The  rat
should be used because  it has been used extensively for metabolic and
toxicological studies.

     (ii) Test animals. For pharmacokinetics testing,  adult male  and fe-
male rats  (Fischer 344 or strain used  for major toxicity testing), 7 to 9
weeks  of  age, should be used. The animals should be purchased from a
reputable dealer and should be identified upon arrival at the testing labora-
tory. The animals should be selected at random for the testing groups and
any animal  showing signs of ill  health should not be used. In all studies,
unless  otherwise specified, each test  group  should contain at least four
animals of each sex for a total of at least eight animals.

     (iii) Animal care. (A) Animal care and housing should be in accord-
ance with DHEW Publication No. (NIH)-85-23 (1985), Guidelines for the
Care and Use of Laboratory Animals.

     (B) The animals  should be  housed in environmentally controlled
rooms  with at least 10 air changes per hour. The rooms should be main-

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tained at a temperature of 22 + 2 °C and humidity of 50 + 20 percent with
a 12-h light/dark cycle per day. The animals should be kept in a quarantine
facility for at least 7 days prior to  use  and should be acclimated to the
experimental environment for a minimum of 48 h prior to treatment.

     (C)  During the acclimatization period,  the animals should be housed
in suitable cages. All animals should be provided with certified feed and
tap water ad libitum.

     (2) Administration of test substance—(i) Test substance. The use
of radioactive  test substance is  required  for  all materials  balance  and
metabolite identification requirements of the study. The purity of both ra-
dioactive and nonradioactive test substance should be greater than 99 per-
cent.   The   radioactive   and  nonradioactive   substances   should   be
chromatographed separately and together to establish purity  and identity.
If the purity is  less than 99 percent or if the chromatograms differ signifi-
cantly, EPA should be consulted.

     (ii) Dosage and treatment—(A) Intravenous. The low dose of test
substance, in an appropriate vehicle, should be administered intravenously
to four rats of each sex.

     (B)  Oral. Two doses of test  substance  should be used in the  oral
portion of the study, a low dose  and a high dose. The high dose should
induce some  overt toxicity, such as weight loss. The low dose level should
correspond to a no-observed-effect level. The oral dosing should be ac-
complished by  gavage or by administering an encapsulated test substance.
If feasible, the same high and low doses should be used for oral and dermal
studies.

     (C)  Inhalation. Two concentrations of the test substance should be
used in this portion of the study, a low concentration and a high concentra-
tion. The high concentration should  induce  some overt toxicity, while the
low concentration should correspond to a no-observed-effect level. Inhala-
tion treatment should be conducted using a nose-cone or head-only appara-
tus to prevent ingestion of the test substance  through grooming.

     (iii) Dosing and sampling schedule. After administration of the test
substance, each rat should be placed in a separate metabolic unit to facili-
tate collection of excreta. For the inhalation studies, excreta from  the rats
should also be  collected  during the exposure periods. At the end  of each
collection period,  the metabolic units should be cleaned to recover any
excreta that might adhere to the cages.  All studies, except  the repeated
dose  study, should be terminated  at 7 days, or after  at least 90  percent
of the radioactivity has been recovered  in the excreta, whichever occurs
first.

     (A)   Intravenous   study.  Group  A  should   be  dosed  once
intravenousely at the low dose of test substance.

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     (B) Oral studies. (7) Group B should be dosed once orally with the
low dose of the test substance.

     (2) Group C  should be dosed once orally with the high dose of the
test substance.

     (C) Inhalation studies. A single 6-h exposure period should be used
for each group.

     (7)  Group D should be exposed to  a mixture of the test substance
in air at the low concentration.

     (2) Group E should be exposed to a mixture of test substance in  air
at the high concentration.

     (D) Repeated dosing study. Group F should receive a series of single
daily oral low  doses of nonradioactive test substance over a period  of at
least 7 consecutive days. A  single oral low dose of radioactive test sub-
stance should be administered 24 h after the last nonradioactive dose. Fol-
lowing dosing with radioactive substance, the rats should be placed in indi-
vidual metabolic units as described in paragraph (d)(2)(iii) of this guide-
line. The study should be terminated 7 days after the last dose, or after
at least  90 percent of the radioactivity has  been recovered in the excreta,
whichever occurs first.

     (3)  Types of studies—(i) Pharmacokinetics  studies. Groups  A
through F should  be used to determine the kinetics  of absorption of the
test substance. In groups administered the substance by intravenous or oral
routes, (i.e.,  Groups A, B, C, F), the concentration of radioactivity in blood
and excreta  including expired air should be measured following adminis-
tration.  In groups administered the substance  by the inhalation route (i.e.,
Groups  D and E),  the concentration of radioactivity  in blood should  be
measured at selected time intervals during  and following the exposure pe-
riod. In the  groups administered the substance by inhalation (i.e., Groups
D and E), the concentration of radioactivity in excreta (including expired
air) should be measured at selected time intervals following the exposure
period. In addition, in the groups administered the substance by inhalation,
the concentration of test substance in inspired air should  be measured at
selected time intervals during the exposure period.

     (ii) Metabolism studies. Groups A through F should be used to deter-
mine the  metabolism of the test substance. Excreta (urine, feces, and ex-
pired air) should be collected for identification and quantification of test
substance and metabolites.

     (4)  Measurements—pharmacokinetics. Four  animals  from  each
group should be used for these measurements.

     (i)  Bioavailability.  The levels of radioactivity should be determined
in whole blood, blood plasma or blood serum at  15 min, 30 min,  1, 2,

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3, 6, 9, and  18 h after dosing; and at 30 min,  3, 6, 6.5, 7, 8,  9,  12, and
18 h after initation of inhalation exposure.

     (ii) Extent of absorption. The total quantities of radioactivity should
be determined for excreta collected daily for 7 days, or after at least 90
percent of the radioactivity has been recovered in the excreta,  whichever
occurs first.

     (iii) Excretion. The quantities of radioactivity eliminated in the urine,
feces, and expired air should be determined separately at appropriate time
intervals.  The collection of the intact test substance or its metabolites, in-
cluding carbon dioxide, may be  discontinued  when  less than  1  percent
of the administered dose is found to be exhaled as radioactive carbon diox-
ide in 24 h.

     (iv) Tissue distribution. At the termination of each study,  the quan-
tities of radioactivity in blood and in various tissues, including bone, brain,
fat, gastrointestinal tract, gonads, heart, kidney, liver,  lungs, muscle, skin,
spleen, and residual carcass of each animal should be determined.

     (v)  Changes  in   pharmacokinetics.  Results of pharmacokinetics
measurements (i.e., biotransformation, extent of absorption, tissue distribu-
tion, and excretion) obtained in rats receiving the single low  oral dose
of test substance  (Group B) should be compared to the corresponding re-
sults obtained in rats receiving repeated oral doses of test substance (Group
F).

     (vi)  Biotransformation. Appropriate  qualitative and quantitative
methods should be used to assay urine, feces, and expired air collected
from rats.  Efforts should be made to identify any metabolite which com-
prises 5 percent or more of the dose eliminated.

     (vii) Changes  in biotransformation. Appropriate  qualitative  and
quantitative assay methodology should be used to compare the composition
of radioactive substances in excreta from the rats receiving a single  oral
dose (Groups B and C) with those in the excreta from rats receiving re-
peated oral doses (Group F).

     (e) Data and reporting. The final  test report should include the fol-
lowing:

     (1) Presentation  of results. Numerical data should be presented in
tabular form. Pharmacokinetics data should also be presented in graphical
form. Qualitative observations should be  reported.

     (2) Evaluation of results. All quantitative results should be evaluated
by an appropriate statistical method.

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     (3) Reporting  results. In addition to the reporting requirements as
specified in 40 CFR 792.185, the following specific information should
be reported:

     (i) Species and  strains of laboratory animals.

     (ii) Chemical characterization of the test substance, including:

     (A)  For the radioactive test substance, information on the  sites  and
degree of radiolabeling, including type of label, specific activity,  chemical
purity, and radiochemical purity.

     (B) For the nonradioactive substance, information on chemical purity.

     (C) Results of chromatography.

     (iii) A full description of the sensitivity, precision, and accuracy of
all procedures used to generate the data.

     (iv) Extent of absorption of the test substance as indicated by percent
absorption  of the administered oral dose and total body burden after inhala-
tion exposure.

     (v) Quantity and percent recovery of radioactivity in feces, urine, ex-
pired air, and blood.

     (vi) Tissue distribution reported as quantity of radioactivity in blood
and in various  tissues, including  bone,  brain, fat, gastrointestinal  tract, go-
nads, heart, kidney, liver, lung, muscle, skin, spleen and in residual carcass
of each rat.

     (vii) Biotransformation pathways  and quantities  of the test substance
and metabolites in  excreta collected after  administering single  high  and
low doses to rats.

     (viii) Biotransformation pathways  and quantities of the test substance
and metabolites in excreta collected after administering repeated low doses
to rats.

     (ix) Pharmacokinetics  models developed from the experimental data.

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