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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Administrative data

Endpoint:
genetic toxicity in vivo
Remarks:
Type of genotoxicity: other: Hepatic cRNA array,
Type of information:
experimental study
Adequacy of study:
supporting study
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: Published

Data source

Reference
Reference Type:
publication
Title:
Comparison of the expression profiles induced by genotoxic and nongenotoxic carcinogens in rat liver
Author:
Ellinger-Ziegelbauer, H., Stuart, B., Wahle, B., Bomann, W., Ahr, H.J.
Year:
2005
Bibliographic source:
Mutation Research 575, 61-84

Materials and methods

Principles of method if other than guideline:
Groups of male Wistar rats was treated with 1200 mg/kg bw/day for 1, 3 or 7 days; liver were taken for histopathological evaluation and gene expression profiles analysed using Affimetriy RG_U34A arrays
GLP compliance:
not specified
Type of assay:
other: In vivo repeated dosing, enzyme induction/inhibition array

Test material

Constituent 1
Reference substance name:
Piperonyl butoxide
IUPAC Name:
Piperonyl butoxide
Constituent 2
Chemical structure
Reference substance name:
2-(2-butoxyethoxy)ethyl 6-propylpiperonyl ether
EC Number:
200-076-7
EC Name:
2-(2-butoxyethoxy)ethyl 6-propylpiperonyl ether
Cas Number:
51-03-6
Molecular formula:
C19H30O5
IUPAC Name:
2-(2-butoxyethoxy)ethyl 6-propylpiperonyl ether
Details on test material:
Purity 88.5%
Source Sigma, St Louis, MO, USA

Test animals

Species:
rat
Strain:
Wistar
Sex:
male
Details on test animals or test system and environmental conditions:
no data

Administration / exposure

Route of administration:
oral: gavage
Vehicle:
Carboxymethyl cellulose
Details on exposure:
no data
Duration of treatment / exposure:
1, 3, 7 days
Frequency of treatment:
daily
Post exposure period:
none
Doses / concentrations
Remarks:
Doses / Concentrations:
1200 mg/kg bw/day
Basis:
actual ingested
No. of animals per sex per dose:
5
Control animals:
yes, concurrent vehicle
Positive control(s):
Dimethylnitrosamine, 2-nitrofluorene, aflatoxin B1, 4-(methylnitrosamino)-1-(3pyridyl)-1-butanone (NNK)

Examinations

Tissues and cell types examined:
Liver
Details of tissue and slide preparation:
Livers were excised and processed for histopathological examination and RNA extraction
RNA isolation with Qiagen RNAeasy 96 well kits and quality control using RNA 6000 Nanaochips on Agilent 2001 Bioanalyzer (Agilent Technologies GmbH, Germany)
biotin labelled cRNA samples were prepared and hybridizatuion on Affymetrix Genechip RG_U34A arrays according to published procedures.
Evaluation criteria:
Data evaluation using Gene-Data Expression analyst software as published
Statistics:
Significantly deregulated genes (compared to time-matched controls) significances using twosample t-test with cut-off p-value 0.001.
Genes generally differntiating were obtsined by applying Welch's test

Results and discussion

Test results
Sex:
male
Genotoxicity:
negative
Toxicity:
no effects
Vehicle controls validity:
valid
Negative controls validity:
not specified
Positive controls validity:
valid
Additional information on results:
The profile of up-or down-regulated genes was clearly different for PBO as compared to genotoxic positive control treatments.

Applicant's summary and conclusion

Conclusions:
Interpretation of results (migrated information): negative
The profile of up-or down-regulated genes was clearly different for PBO as compared to genotoxic positive control treatments.
Thus Piperony butoxide was not genotoxic in the liver.
Executive summary:

Application of recently developed gene expression techniques using microarrays in toxicological studies (toxicogenomics) facilitate the interpretation of a toxic compound's mode of action and may also allow the prediction of selected toxic effects based on gene expression changes. In order to test this hypothesis, we investigated whether carcinogens at doses known to induce liver tumors in the 2-year rat bioassay deregulate characteristic sets of genes in a short term in vivo study and whether these deregulated genes represent defined biological pathways. Male Wistar rats were dosed with the four nongenotoxic hepatocarcinogens methapyrilene (MPy, 60 mg/kg/day), diethylstilbestrol (DES, 10 mg/kg/day), Wy-14643 (Wy, 60 mg/kg/day), and piperonylbutoxide (PBO, 1200 mg/kg/day). After 1, 3, 7, and 14 days, the livers were taken for histopathological evaluation and for analysis of the gene expression profiles on Affymetrix RG_U34A arrays. The expression profile of the four nongenotoxic carcinogens were compared to the profiles of the four genotoxic carcinogens 2-nitrofluorene (2-NF), dimethylnitrosamine (DMN), 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK), and aflatoxin B1 (AB1) from a similar study reported previously. By using statistical and clustering tools characteristically deregulated genes were extracted and functionally classified. Distinct cellular pathways were affected by the nongenotoxic carcinogens compared to the genotoxic carcinogens which at least partly correlated with the two-stage model of carcinogenesis. Characteristic to genotoxic carcinogens were a DNA damage response and the activation of proliferative and survival signaling. Nongenotoxic carcinogens showed responses to oxidative DNA or protein damage, as well as cell cycle progression and signs of regeneration. Many of the gene alterations found with the nongenotoxic carcinogens imply compound-specific mechanisms. Although neither a single gene nor a single pathway will be sufficient to discriminate the two classes of carcinogens, it became evident that combinations of pathway-associated gene expression profiles may be used to predict a genotoxic or nongenotoxic carcinogenic potential of a compound in short-term studies.