Oecd for chronic toxicity

OECD GUIDELINES FOR CHRONIC
TOXICITY STUDIES (452)
Presented by
PAVAN REDDY
1ST SEM M.PHARM (PHARMACOLOGY)
COPS ,DSU

CONTENTS
Introduction
Initial consideration
Principle
Selection of animals
Method description
Procedure
Observations
Data and reporting

INTRODUCTION
Original guideline 452 was adopted in 1981
Designed to use in testing of chemicals including pesticides
Most of the studies using rodents
3 main routes used oral, dermal & inhalation
Roa depends on physio-chemical characteristics of the test chemicals
412 , 413 & acute inhalation testing should be considered in design of inhalation testing
410 in dermal

Objectives
The identification of the
chronic toxicity of a
chemical
The identification of
target organs
Characterisation of the
dose-response
relationship
The prediction of
chronic toxicity effects
at human exposure
levels
Provision of data to test
hypotheses regarding
mode of action

INITIAL CONSIDERATIONS
Information that will assist in the study design includes the identity, chemical structure, and
physicochemical properties of the test chemical; any information on the mode of action; results
of any in vitro or in vivo toxicity tests; anticipated use(s) and potential for human exposure;
available (Q)SAR data and toxicological data on structurally-related substances; available
toxicokinetic data (single dose and also repeat dose kinetics where available) and data derived
from other repeated exposure studies.
The determination of chronic toxicity should only be carried out after initial information on
toxicity has been obtained from repeated dose 28-day and/or 90-day toxicity tests.

PRINCIPLE
Test chemical administered daily in graduated dose for 12 months (oral)
Duration is chosen based on regulatory requirements
Deviation should be justified in the case of short duration
1 or more interim kills (3 or 6 months) additional grp of animals may include to accommodate
this
During administration animals are observed for signs of toxicity
Animals which die or are killed during the test are necropsied and, at the conclusion of the test,
surviving animals are killed and necropsied.

Description of the method
Selection of animal species ;
Rodents are mostly used,(rat or mouse) for non-rodents follow TG 409 Repeated
dose 90 day oral toxicity
The animals used in preliminary toxicity studies of shorter duration same strain
& source of animals should be used in chronic toxicity
The females should be nulliparous and non pregnant

Housing and feeding conditions
Temp ; 22°C (± 3°C).
The relative humidity should be at least 30% and preferably not exceed 70%
12HRS light and dark cycle
Analytical information on the nutrient and dietary contaminant levels should be generated
periodically,

Preparation of animals
Healthy animals, which have been acclimated to laboratory conditions for at least 7 days and
have not been subjected to previous experimental procedures, should be used.
In case of rodents before the animals are 8 weeks old
Animals characterized acc; species, strain, source, sex, weight and age.
Weight variation for each sex of animals should be minimal and not exceed ± 20 % of the mean
weight of all the animals within the study, separately for each sex.
Randomly assigned to control and std grp If there are statistically significant differences, then
the randomisation step should be repeated, if possible.
Each animal should be assigned a unique identification number, and permanently marked with
this number by tattooing, microchip implant, or other suitable method.

Procedure
Number & sex of animals:
Both sexes should be used with sufficient number
For rodents at least 20/sex grp at each dose level, non rodents 4/sex grp

Provision for interim kills, satellite groups
and sentinel animals
The study may make provision for interim kills (at least 10 animals/sex/group), e.g. at 6 months,
to provide information on progression of toxicological changes and information & it should be
scientifically justified
Satellite groups may also be included to monitor the reversibility of any toxicological changes
induced by the chemical under investigation; these will normally be restricted to the highest
dose level of the study plus control.
An additional group of sentinel animals (typically 5 animals per sex) may also be included for
monitoring of disease status

Dose groups & dosage
3 dose levels & a control should be used
Dose levels are based on results of repeated toxicity (short term) studies & also any toxicological
& toxicokinetic data if available on the test chemical & related subs
Data generated is adequate to fulfil regulatory req of oecd countries
The highest dose level should normally be chosen to identify the principal target organs and
toxic effects while avoiding suffering, severe toxicity, morbidity, or death
The highest dose level should be chosen to elicit evidence of toxicity, as evidenced by, for
example, depression of body weight gain (approximately 10%).
Top dose should not exceed 1g/kg/day

Preparation of doses and administration
of test chemical
The test chemical is normally administered orally, via the diet or drinking water, or by gavage.
The roa is dependent on the purpose of the study, the physical/chemical properties of the test
chemical, its bioavailability
The use of an aqueous solution/suspension be considered first, followed by consideration of a
solution/ emulsion in oil (e.g., corn oil) and then by possible solution in other vehicles
Toxic info of vehicle should be known
concentration of the chemical in the feed should not normally exceed an upper limit of 5% of
the total diet

In the case of oral administration, the animals are dosed with the test chemical daily (seven days
each week), normally for a period of 12 months. (1ml/100g for rodents)
In the case of dermal administration, animals are normally treated with the test chemical for at
least 6 hours per day, 7 days per week, as specified in TG 410 (11), for a period of 12 months.
Exposure by the inhalation route is carried out for 6 hours per day, 7 days per week, but exposure
for 5 days per week may also be used, if justified. The period of exposure will normally be for a
period of 12 months

Duration of study
Normally 12 months
but can extend to long term(18 or 24) & can be reduced to short depends on req of regulatory
regimes
Deviation should be justified

Observation
All animals should be checked for morbidity or mortality, usually at the beginning and end of
each day, including at weekends and holidays. Same time everyday
Signs noted should include, but not be limited to, changes in skin, fur, eyes, mucous membranes,
occurrence of secretions and excretions and autonomic activity (e.g., lacrimation, piloerection,
pupil size, and unusual respiratory pattern). Changes in gait, posture and response to handling as
well as the presence of clonic or tonic movements, stereotypies (e.g., excessive grooming,
repetitive circling) or bizarre behaviour (e.g., self-mutilation, walking backwards) should also be
recorded (24).
Ophthalmological examination, using an ophthalmoscope or other suitable equipment, should
be carried out on all animals prior to the first administration of the test chemical. Compared
after termination of study

For chemicals where previous repeated dose 28-day and/or 90-day toxicity tests indicated the
potential to cause neurotoxic effects, sensory reactivity to stimuli of different types (e.g.,
auditory, visual and proprioceptive stimuli) (optional)
Conducted before study & after 3 month interval
For immunotoxicity investigations done at end point

Body weight, food/water consumption
and food efficiency
Checked before studies, once a week for 13 weeks thereafter at monthly intervals

Haematology and clinical biochemistry
For rodents, haematological examinations should be carried out in at least 10 male and 10
female animals per group, at 3, 6, and 12 months, as well as at study termination (if longer than
12 months), using the same animals throughout
In non-rodent studies, samples will be taken from smaller numbers of animals (e.g. 4 animals
per sex and per group in dog studies), at interim sampling times and at termination as described
for rodents.
Samples should taken from retro orbital or cardiac puncture under anaesthesia
In no sign of toxicity at 3month evaluation no need to study

Parameters
Haematology : Total and differential leukocyte count, erythrocyte count, platelet count,
haemoglobin concentration, haematocrit (packed cell volume), mean corpuscular volume
(MCV), mean corpuscular haemoglobin (MCH), mean corpuscular haemoglobin concentration
(MCHC), prothrombin time, and activated partial thromboplastin time
Clinical biochemistry : glucose, urea (urea nitrogen), creatinine, total protein, albumin,
calcium, sodium, potassium, total cholesterol, at least two appropriate tests for hepatocellular
evaluation (alanine aminotransferase, aspartate aminotransferase, glutamate dehydrogenase,
total bile acids)(31), and at least two appropriate tests for hepatobiliary evaluation (alkaline
phosphatase, gamma glutamyl transferase, 5'-nucleotidase, total bilirubin, total bile acids)
Other clinical chemistry parameters such as fasting triglycerides, specific hormones and
cholinesterase may be measured as appropriate,

Urinalysis : appearance, volume, osmolality or specific gravity, pH, total protein, and glucose.
Other determinations include ketone, urobilinogen, bilirubin, and occult blood.

Pathology
Gross necropsy:
All animals in the study shall normally be subjected to a full, detailed gross necropsy which
includes careful examination of the external surface of the body, all orifices, and the cranial,
thoracic and abdominal cavities and their contents
Organ weights should be collected from all animals, The adrenals, brain, epididymides, heart,
kidneys, liver, ovaries, spleen, testes, thyroid (weighed post-fixation, with parathyroids), and
uterus of all animals should be trimmed of any adherent tissue, as appropriate, and their wet
weight is taken.
In a study using mice, weighing of the adrenal glands is optional.

Histopathology
 All tissues from the high dose and control groups;
 All tissues from animals dying or killed during the study;
 All tissues showing macroscopic abnormalities;
 Target tissues, or tissues which showed treatment-related changes in the high dose group,
from all animals in all other dose groups;
 In the case of paired organs, e.g., kidney, adrenal, both organs should be examined.

DATA AND REPORTING
Individual animal data should be provided for all parameters evaluated. Additionally, all data
should be summarised in tabular form showing for each test group the number of animals at the
start of the test, the number of animals found dead during the test or killed for humane reasons
and the time of any death or humane kill, the number showing signs of toxicity, a description of
the signs of toxicity observed, including time of onset, duration, and severity of any toxic effects,
the number of animals showing lesions, the type of lesions and the percentage of animals
displaying each type of lesion. Summary data tables should provide the means and standard
deviations (for continuous test data) of animals showing toxic effects or lesions, in addition to
the grading of lesions.
Historical data is compared with current data

TEST REPORT :
The test report should include the following information:
Test chemical: physical nature, purity, and physicochemical properties;
identification data;
source of substance;
batch number;
certificate of chemical analysis

Vehicle (if appropriate):
 justification for choice of vehicle (if other than water).
 Test animals:
 species/strain used and justification for choice made;
 number, age, and sex of animals at start of test;
 source, housing conditions, diet, etc.;
 individual weights of animals at the start of the test.
Test conditions:
 rationale for route of administration and dose selection;
 when applicable, the statistical methods used to analyse the data;
 details of test chemical formulation/diet preparation;
 analytical data on achieved concentration, stability and homogeneity of the preparation;
 route of administration and details of the administration of the test chemical;
 for inhalation studies, whether nose only or whole body;
 actual doses (mg/kg body weight/day), and conversion factor from diet/drinking water test chemical concentration
(mg/kg or ppm) to the actual dose, if applicable;
 details of food and water quality.

Results:(summary tabulated data and individual animal data should be presented):
 survival data;
 body weight/body weight changes;
 food consumption, calculations of food efficiency, if made, and water consumption if
applicable;
 toxic response data by sex and dose level, including signs of toxicity;
 nature, incidence (and, if scored, severity), and duration of clinical observations ((whether
transitory or permanent);
 ophthalmological examination;
 haematological tests; clinical biochemistry tests;
 urinalysis tests;
 outcome of any investigations of neurotoxicity or immunotoxicity

 terminal body weight;
 organ weights (and their ratios, if applicable);
 necropsy findings;
 a detailed description of all treatment-related histopathological
findings; absorption data if available;
 Statistical treatment of results, as appropriate
 Discussion of results including:
 Dose : response relationships
 Consideration of any mode of action information
 Discussion of any modelling approaches
 BMD, NOAEL or LOAEL determination
 Historical control data
 Relevance for humans

reference
Oecd guidelines for testing of chemicals 452 (2018)

Oecd for chronic toxicity

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