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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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:
nephrotoxicity
Type of information:
experimental study
Adequacy of study:
weight of evidence
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: Acceptable study report which meets basic scinetific principles.

Data source

Reference
Reference Type:
publication
Title:
Quantitation of a2-microglobulin after administration of structurally divergent chemical compounds
Author:
Hildebrand H, Hartmann E, Popp A, Bomhard E
Year:
1997
Bibliographic source:
Arch Toxicol 71: 351-359

Materials and methods

Test guideline
Qualifier:
no guideline followed
Principles of method if other than guideline:
The potential of the test substance to induce alpha-2-microglobulin binding and subsequent hyaline droplet accumulation (HDA) potential was tested alongside other chemicals. HDA is a known precursor of necrosis and kidney tumours exclusively found in male rats.
Type of method:
in vivo
Endpoint addressed:
repeated dose toxicity: oral

Test material

Constituent 1
Chemical structure
Reference substance name:
Sodium 1-amino-4-bromo-9,10-dioxoanthracene-2-sulphonate
EC Number:
228-391-5
EC Name:
Sodium 1-amino-4-bromo-9,10-dioxoanthracene-2-sulphonate
Cas Number:
6258-06-6
Molecular formula:
C14H8BrNO5S.Na
IUPAC Name:
sodium 1-amino-4-bromo-9,10-dioxo-9,10-dihydroanthracene-2-sulfonate
Details on test material:
- Name of test material (as cited in study report): 2-Anthracenesulfonic acid, 1-amino-4-bromo-9,10-dioxo-, monosodium salt

Test animals

Species:
rat
Strain:
Wistar
Sex:
male
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Strain: Wistar (Hsd Cpb:WU)
- Source: Harlan-Winkelmann
- Age at study initiation: 12 - 14 weeks
- Housing: individually in Macrolon cages
- Diet (ad libitum): Altromin 1324
- Water (ad libitum): tap water

Administration / exposure

Route of administration:
other: no data
Vehicle:
not specified
Analytical verification of doses or concentrations:
not specified
Duration of treatment / exposure:
no data
Frequency of treatment:
no data
Post exposure period:
7 days
Doses / concentrations
Remarks:
Doses / Concentrations:
1000 mg/kg bw/day
Basis:

No. of animals per sex per dose:
3
Control animals:
yes

Results and discussion

Any other information on results incl. tables

Alpha2-Microglobulin-induced nephropathy is a phenomenon which is exclusively found in adult male rats. Various chemicals are able to bind to alpha2-microglobulin thus inhibiting its proteolytic degradation in lysosomes of the P2 segment of the rat nephron. The accumulation of this protein in 'protein droplets' or 'hyaline droplets' leads to necrosis, followed by regeneration which possibly later results in the formation of tumours. Reported was the development of a monoclonal antibody which is specific for alpha2-microglobulin. It was utilized to measure alpha2-microglobulin concentrations in plasma and tissues, and to stain alpha2 -microglobulin in fixed tissue slides. In two studies compounds were administered to adult male Wistar rats: (1) one group of structurally diverse compounds, which gave an overview of chemical entities capable of inducing the accumulation of alpha2-microglobulin (under these the test substance); and (2) another group of structurally closely related compounds (i.e. substituted benzene derivatives) for the purpose of elucidating possible structure-activity relationships. The degree of alpha2-microglobulin-induced nephropathy was determined by immunohistochemical staining of kidney sections (only Group (2)). In addition, liver and kidney tissue and plasma concentrations of alpha2-microglobulin were measured by competitive ELISA: Animals, that were treated with the test substance showed no elevated levels in plasma, but pronounced effects were observed in liver (137% increase: 1.46 +/- 0.48 versus 1.07 +/- 0.22 (control) mg/g tissue) and in kidney (184% increase: 2.10 +/- 0.38 versus 1.14 +/- 0.26 (control) mg/g tissue).

Comparing structurally related benzene derivatives, the hyaline droplet accumulating (HDA) potential was found to depend both on the type of substituent and its position at the aromatic ring. In general HDA activity increased in the order benzene=phenol=alkylated phenols < halogenated phenols < halogenated benzenes.

Applicant's summary and conclusion