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Administrative data

Key value for chemical safety assessment

Genetic toxicity in vitro

Description of key information

In a reliable and valid gene mutation study in bacteria, conducted according to Japanese guidelines with a protocol similar to the OECD Test Guideline 471 and in compliance with GLP, dicyclopentyl(dimethoxy)silane (CAS 126990-35-0) did not induce mutagenic activity in Salmonella strains (Salmonella typhimurium TA1535, TA1537, TA98, TA100) at up to 313 μg/plate (limited by cytotoxicity) and in Escherichia coli (WP2 uvrA) at up to 5000 μg/plate, with and without S9. The test substance was concluded to be negative for mutagenicity to bacteria under the conditions of the test (BML Incorporation, 1993)

In a reliable in vitro mammalian chromosome aberration study conducted according to OECD Guideline 473 and in compliance with GLP, dicyclopentyl(dimethoxy)silane was not clastogenic to human lymphocytes at concentrations up to 565 μg/ml (limited by cytotoxicity) either in the presence or absence of metabolic activation by S9 (Safepharm Laboratories Limited, 1996)

Link to relevant study records

Referenceopen allclose all

Endpoint:
in vitro gene mutation study in bacteria
Type of information:
experimental study
Adequacy of study:
key study
Study period:
4 February to 16 March 1992
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
JAPAN: Guidelines for Screening Mutagenicity Testing Of Chemicals
Deviations:
no
Qualifier:
equivalent or similar to guideline
Guideline:
OECD Guideline 471 (Bacterial Reverse Mutation Assay)
Deviations:
yes
Remarks:
(only 2 replicate plates/concentration)
GLP compliance:
yes
Type of assay:
bacterial reverse mutation assay
Target gene:
histidine locus (Salmonella typhimurium strains)
tryptophan locus (Escherichia coli WP2 uvrA)
Species / strain / cell type:
other: Salmonella typhimurium TA1535, TA1537, TA98, TA100, Escherichia coli WP2 uvrA
Additional strain / cell type characteristics:
not applicable
Metabolic activation:
with and without
Metabolic activation system:
S9 microsomal fraction prepared from phenobarbital- and 5,6-benzoflavone-induced rat liver
Test concentrations with justification for top dose:
S. typhimurium strains:
0, 2.4, 4.9, 10, 20, 39 and 78 μg/plate, without S9
0, 2.4, 4.9, 10, 20, 39 and 78 μg/plate, with S9 for TA1535 and TA100
0, 10, 20, 39, 78, 156 and 313 μg/plate, with S9 for TA1537 and TA98
Escherichia coli WP2 uvrA:
0, 313, 625, 1250, 2500 and 5000 μg/plate, with or without S9
Vehicle / solvent:
- Vehicle(s)/solvent(s) used: DMSO
- Justification for choice of solvent/vehicle: test material insoluble in water, DMSO is included in the list of recommended solvents
Untreated negative controls:
no
Negative solvent / vehicle controls:
yes
Remarks:
DMSO
True negative controls:
no
Positive controls:
yes
Positive control substance:
furylfuramide
Remarks:
0.01 μg/plate TA100 and WP2 uvrA; 0.1 μg/plate TA98 (without S9)
Untreated negative controls:
no
Negative solvent / vehicle controls:
yes
Remarks:
DMSO
True negative controls:
no
Positive controls:
yes
Positive control substance:
sodium azide
Remarks:
0.5 μg/plate TA1535 (without S9)
Untreated negative controls:
no
Negative solvent / vehicle controls:
yes
Remarks:
DMSO
True negative controls:
no
Positive controls:
no
Positive control substance:
other: 2-methoxy-6-chloro-9-[3-(2-chloroethyl)-aminopropylamino]acridine.2HCl (ICR-191) 1 μg/plate TA1537 (without S9)
Untreated negative controls:
no
Negative solvent / vehicle controls:
yes
Remarks:
DMSO
True negative controls:
no
Positive controls:
yes
Positive control substance:
benzo(a)pyrene
Remarks:
5 μg/plate TA100, TA98 and TA1537 (with S9)
Untreated negative controls:
no
Negative solvent / vehicle controls:
yes
Remarks:
DMSO
True negative controls:
no
Positive controls:
yes
Positive control substance:
other: 2-aminoanthracene: 2 μg/plate TA1535; 5 μg/plate WP2 uvrA (with S9)
Details on test system and experimental conditions:
METHOD OF APPLICATION: preincubation

DURATION
- Preincubation period: 20 min
- Exposure duration: 48 h in plates

SELECTION AGENT (mutation assays): depleted levels of histidine or tryptophan in agar medium to select for mutants

NUMBER OF REPLICATIONS: 2 plates/concentration. 2 independent experiments, but in the second only TA1535, TA1537, TA98 and TA100 were tested without S9 and only TA1535 and TA100 were tested with S9.

DETERMINATION OF CYTOTOXICITY
- Method: relative total growth

OTHER:
- Type and composition of metabolic activation system:
- species and cell type: rat, S9 fraction
- quantity: 0.1 ml S9 fraction per 1 ml S9 mix, 0.5 ml S9 mix per plate
- induced or not induced: incuded
- chemicals used for induction: phenobarbital and 5,6-benzoflavone
- co-factors used: Boehringer Mannheim Yamanouchi KK, lot number 712.713; MgCl2 8.0 μmol; KCl 33 μmol; G6P 5 μmol; NADPH 4 μmol; NADH 4 μmol; Na-phosphate buffer (pH 7.4) 100 μmol.
Evaluation criteria:
Results considered positive if there was a reproducible increase in the mutant frequency of at least twice that of the solvent control at least one time point, or a concentration-related increase over more than one time point.
Statistics:
No data
Species / strain:
other: S. typhimurium TA1535, TA1537, TA98, TA100, E. coli WP2 uvrA
Metabolic activation:
with and without
Genotoxicity:
negative
Cytotoxicity / choice of top concentrations:
cytotoxicity
Remarks:
39 μg/plate in TA100, TA1535, TA1537 without S9; 78 μg/plate in TA98 without S9 and TA100, TA1535 with S9; 313 μg/plate in TA98, TA1537 with S9
Vehicle controls validity:
valid
Untreated negative controls validity:
not examined
Positive controls validity:
valid
Additional information on results:
TEST-SPECIFIC CONFOUNDING FACTORS
- Effects of pH: no data
- Effects of osmolality: no data
- Evaporation from medium: no data
- Water solubility: no data
- Precipitation: no data
- Other confounding effects: no data

RANGE-FINDING/SCREENING STUDIES: a range-finding study was conducted with 0, 1.2, 4.9, 20, 78, 313, 1250 and 5000 μg/plate. No growth inhibition was observed with WP2 uvrA. Growth inhibition was noted at 78 μg/plate and above without S9 for all Salmonella strains and with S9 for TA1535 and TA100. Growth inhibition was seen at 313 μg/plate and above with S9 for TA1537 and TA100.

COMPARISON WITH HISTORICAL CONTROL DATA: no data

ADDITIONAL INFORMATION ON CYTOTOXICITY: without S9, cytotoxicity occurred at 78 μg/plate for TA1535, TA98 and TA100 and at 39 μg/plate for TA1537. With S9, cytotoxicity was seen at 78 μg/plate for TA1535 and TA100 and at 156 μg/plate and above for TA1537 and TA98. No toxicity was observed with WP2 uvrA at up to 5000 μg/plate, with or without S9.
Remarks on result:
other: all strains/cell types tested

A doubling of revertants was seen in the first experiment at 4.9 μg/plate in TA1535 without S9, but this was not observed in the second experiment and, as no increase in mutant frequency was seen at any other concentration level, it was concluded that this was not related to the test material.

Table 1:Number of revertants per plate (mean of 2 plates) – Experiment 1

Bacterial strain

TA100

TA1535

TA98

Concentration of test material,
µg/plate

- MA

+ MA

Cytotoxic
(yes/no)

- MA

+ MA

Cytotoxic
(yes/no)

- MA

+ MA

Cytotoxic
(yes/no)

0*

104

107

(106)

104

130

(117)

no

11

11

(11)

16

16

(16)

no

26

23

(25)

31

33

(32)

no

2.4

122

137

(130)

141

123

(132)

no

16

13

(15)

13

18

(16)

no

18

23

(20)

no

4.9

100

127

(114)

139

118

(129)

no

22

21

(22)

16

16

(16)

no

22

24

(23)

no

10

135

120

(128)

106

122

(114)

no

19

12

(16)

22

8

(15)

no

22

20

(21)

37

26

(32)

no

20

105

105

(105)

102

100

(101)

no

15

8

(11)

14

18

(16)

no

20

20

(20)

30

29

(30)

no

39

83

84

(84)

138

128

(133)

no

17

10

(14)

10

13

(12)

no

21

23

(22)

28

23

(26)

no

78

89

81

(85)

93

92

(93)

yes

13

10

(12)

17

17

(17)

yes

28

20

(24)

31

24

(28)

yes –MA

no +MA

156

30

29

(30)

yes

313

35

29

(32)

yes

Positive control

AF-2

0.01 µg/plate

B[a]P

5.0 µg/plate

NaN3

0.5 µg/plate

2AA

2.0 µg/plate

AF-2

0.1 µg/plate

B[a]P

5.0 µg/plate

800

762

(781)

896

985

(941)

417

355

(386)

213

208

(211)

401

422

(412)

181

204

(193)

 

Table 1. (cont’d)

TA1537

WP2uvrA

- MA

+ MA

Cytotoxic
(yes/no)

- MA

+ MA

Cytotoxic
(yes/no)

0*

13

18

(16)

19

24

(22)

no

24

22

(23)

29

37

(33)

no

2.4

21

25

(23)

4.9

17

19

(18)

10

17

25

(21)

26

20

(23)

no

20

18

9

(14)

25

21

(23)

no

39

8

12

(10)

27

19

(23)

yes -MA

no +MA

78

10

10

(10)

22

18

(20)

yes –MA

no +MA

156

15

8

(12)

yes

313

14

19

(17)

yes

16

29

(23)

38

19

(29)

no

625

17

20

(19)

31

26

(29)

no

1250

14

33

(24)

21

15

(18)

no

2500

20

24

(22)

23

37

(30)

no

5000

27

21

(24)

25

28

(27)

no

Positive control

ICR-191

1.0 µg/plate

B[a]P

5.0 µg/plate

AF-2

0.01 µg/plate

2AA

10.0 µg/plate

1330

1256

(1293)

84

104

(94)

138174(156) 740692(716)

*solvent control (DMSO)

2AA, 2-aminoanthracene; AF-2, furylfuramide; B[a]P,benzo(a)pyrene; MA, metabolic activation; NaN3, sodium azide

 

Table 2:Number of revertants per plate (mean of 2 plates) – Experiment 2

Bacterial strain

TA100

TA1535

TA98

Concentration of test material,
µg/plate

- MA

+ MA

Cytotoxic
(yes/no)

- MA

+ MA

Cytotoxic
(yes/no)

- MA

+ MA

Cytotoxic
(yes/no)

0*

99

137

(118)

101

120

(111)

no

17

9

(13)

24

19

(22)

no

16

21

(19)

no

2.4

103

130

(117)

107

122

(115)

no

12

18

(15)

21

16

(19)

no

28

22

(25)

no

4.9

106

111

(109)

121

99

(110)

no

20

17

(19)

24

18

(21)

no

24

16

(20)

no

10

107

118

(113)

117

132

(125)

no

13

18

(16)

13

19

(16)

no

18

21

(20)

no

20

100

112

(106)

132

96

(114)

no

11

14

(13)

21

20

(21)

no

17

22

(20)

no

39

88

125

(107)

102

119

(111)

yes –MA

no +MA

8

13

(11)

17

20

(19)

yes –MA

no +MA

17

18

(18)

no

78

75

99

(87)

99

93

(96)

yes

17

9

(13)

17

9

(13)

yes

20

22

(21)

yes

Positive control

AF-2

0.01 µg/plate

B[a]P

5.0 µg/plate

NaN3

0.5 µg/plate

2AA

2.0 µg/plate

AF-2

0.1 µg/plate

768

784

(776)

821

819

(820)

397

395

(396)

226

214

(220)

417

412

(415)

 

Table 2. (cont’d)

TA1537

- MA

+ MA

Cytotoxic
(yes/no)

0*

11

9

(10)

no

2.4

18

16

(17)

no

4.9

13

11

(12)

no

10

9

10

(10)

no

20

8

11

(9)

no

39

8

9

(9)

yes

78

7

4

(6)

yes

Positive control

ICR-191

1.0 µg/plate

1208

1110

(1159)

*solvent control (DMSO)

2AA, 2-aminoanthracene; AF-2,furylfuramide; B[a]P,benzo(a)pyrene; MA, metabolic activation; NaN3, sodium azide

Conclusions:
In a reliable and valid gene mutation study in bacteria, conducted according to Japanese guidelines with a protocol similar to the OECD Test Guideline 471 and in compliance with GLP, dicyclopentyl(dimethoxy)silane did not induce mutagenic activity in Salmonella strains (Salmonella typhimurium TA1535, TA1537, TA98, TA100) at up to 313 μg/plate (limited by cytotoxicity) and in Escherichia coli (WP2 uvrA) at up to 5000 μg/plate, with and without S9.
Executive summary:

In a GLP study conducted according to Japanese guidelines, DCPMS was evaluated for its ability to induce mutation in a bacterial reverse mutagenicity (Ames) assay in four strains of Salmonella typhimurium and Escherichia coli WP2 uvrA, with and without a rat metabolic activation fraction (S9).

 

After a range-finding study, the S. typhimurium strains were exposed in a preincubation assay to the test material at up to 78 μg/plate without S9 (all four strains) and with S9 for TA1535 and TA100; at up to 313 μg/plate for TA1537 and TA98; E.coli WP2 uvrA was tested at up to 5000 μg/plate both with and without S9. The solvent, DMSO, was used as the vehicle control and appropriate known mutagens provided the positive controls. Plates were prepared in duplicate and incubated for 48 hours before counting the revertant colonies. Inhibition of the background lawn was noted as an indication of cytotoxicity. A second independent experiment was conducted, at up to 78 μg/plate using the four Salmonella strains without S9 and TA1535 and TA100 with S9.

No reproducible, concentration-related increase in mutant frequency was observed with any bacterial strain at any concentration of the test material, when compared to the solvent control. The positive controls induced the expected increases in mutant frequencies, confirming the validity of the assay. A thinning of the background lawn at the higher concentrations with the Salmonella strains indicated that the test material was cytotoxic to these strains but not to WP2 uvrA.

Under the conditions of this study, DCPMS showed no mutagenic potential in a bacterial reverse mutagenicity (Ames) assay with four strains of S. typhimurium and E. coli WP2 uvrA

Endpoint:
in vitro cytogenicity / chromosome aberration study in mammalian cells
Type of information:
experimental study
Adequacy of study:
key study
Study period:
30 August 1995 to 25 January 1996
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 473 (In Vitro Mammalian Chromosome Aberration Test)
Deviations:
no
Qualifier:
according to guideline
Guideline:
EU Method B.10 (Mutagenicity - In Vitro Mammalian Chromosome Aberration Test)
Version / remarks:
92/69/EEC, Method B10
Deviations:
no
GLP compliance:
yes (incl. QA statement)
Type of assay:
in vitro mammalian chromosome aberration test
Species / strain / cell type:
lymphocytes: human
Details on mammalian cell type (if applicable):
not applicable
Additional strain / cell type characteristics:
not applicable
Metabolic activation:
with and without
Metabolic activation system:
Aroclor 1254-induced S9 from the livers of male Sprague-Dawley rats
Test concentrations with justification for top dose:
With metabolic activation: 18, 35.5, 71, 141.3, 282.5, 565, 1130, 2260 µg/ml
Without metabolic activation: 2.25, 4.5, 9.0, 18, 35.5, 53.25, 71, 141.3 µg/ml
Vehicle / solvent:
- Vehicle(s)/solvent(s) used: acetone
- Justification for choice of solvent/vehicle: well known solvent
Untreated negative controls:
no
Negative solvent / vehicle controls:
yes
Remarks:
acetone
True negative controls:
no
Positive controls:
yes
Positive control substance:
ethylmethanesulphonate
Remarks:
in dimethyl sulphoxide. 500 µg/ml. For cultures in the absence of S9
Untreated negative controls:
no
Negative solvent / vehicle controls:
yes
Remarks:
acetone
True negative controls:
no
Positive controls:
yes
Positive control substance:
cyclophosphamide
Remarks:
in culture medium without serum. 25 µg/ml. For cultures in presence of S9
Details on test system and experimental conditions:
METHOD OF APPLICATION: in medium

DURATION
- Preincubation period: 48 h
- Exposure duration: 4 h (with S9), 20 h (without S9), 44 h (without S9)
- Expression time (cells in growth medium): 16 h, 40 h (both with S9). Cultures in the absence of S9 were treated continuously.

SPINDLE INHIBITOR (cytogenetic assays): demecolcine (Colcemid 0.1 µg/ml)
STAIN (for cytogenetic assays): 5% Gurrs Giemsa R66

NUMBER OF REPLICATIONS: 2

NUMBER OF CELLS EVALUATED: 100 per culture

DETERMINATION OF CYTOTOXICITY
- Method: mitotic index

OTHER EXAMINATIONS:
- Determination of polyploidy: yes
- Determination of endoreplication: yes

OTHER:
- Type and composition of metabolic activation system:
- species and cell type: rat, liver, S9 fraction
- quantity: 1 ml 10% S9 in standard co-factors added to each 9.0 ml culture
- induced or not induced: induced
- chemicals used for induction: Aroclor 1254, 500 mg/kg bw
- co-factors used: standard [no further information]
Evaluation criteria:
A positive response was recorded for a particular treatment if the percentage of cells with aberrations markedly exceeded that seen in the vehicle control, either with or without a clear concentration-response relationship. For modest increases in aberration frequency, a concentration-response relationship is generally required and appropriate statistical tests may be applied in order to record a positive response.
Statistics:
The frequency of cells with aberrations or polyploidy were compared with the results for the vehicle control using Fisher's Exact test or a Chi-squared test.
Species / strain:
lymphocytes: human
Metabolic activation:
without
Genotoxicity:
negative
Cytotoxicity / choice of top concentrations:
cytotoxicity
Remarks:
at 71 µg/ml, the mitotic index was 70% of the vehicle control
Vehicle controls validity:
valid
Untreated negative controls validity:
not examined
Positive controls validity:
valid
Species / strain:
lymphocytes: human
Metabolic activation:
with
Genotoxicity:
negative
Cytotoxicity / choice of top concentrations:
cytotoxicity
Remarks:
at least a 50% growth inhibition was observed at 565 µg/ml
Vehicle controls validity:
valid
Untreated negative controls validity:
not examined
Positive controls validity:
valid
Species / strain:
lymphocytes: human
Metabolic activation:
without
Genotoxicity:
negative
Cytotoxicity / choice of top concentrations:
cytotoxicity
Remarks:
insufficient scorable metaphases at 71 µg/ml and above 71 µg/ml
Vehicle controls validity:
valid
Untreated negative controls validity:
not examined
Positive controls validity:
valid
Species / strain:
lymphocytes: human
Metabolic activation:
with
Genotoxicity:
negative
Cytotoxicity / choice of top concentrations:
not determined
Remarks:
confounding results - a plateau of toxicity was observed, followed by decreased toxicity
Vehicle controls validity:
valid
Untreated negative controls validity:
not examined
Positive controls validity:
valid
Species / strain:
lymphocytes: human
Metabolic activation:
without
Genotoxicity:
negative
Cytotoxicity / choice of top concentrations:
cytotoxicity
Remarks:
no scorable metaphases observed at 71 µg/ml
Vehicle controls validity:
valid
Untreated negative controls validity:
not examined
Positive controls validity:
valid
Additional information on results:
TEST-SPECIFIC CONFOUNDING FACTORS
- Effects of pH: no data
- Effects of osmolality: no data
- Evaporation from medium: no data
- Water solubility: at higher concentrations, the test material (dissolved in acetone) appeared to float on the surface of the media
- Precipitation:
- Other confounding effects: at higher concentrations, the test material appeared to react with the plastic of the tissue culture flask

RANGE-FINDING/SCREENING STUDIES: the results for cultures in the absence of S9 are repeats using lower concentrations of DCPMS due to cytotoxicity showing no scorable metaphases at 71 µg/ml (original concentrations and data are not provided).

COMPARISON WITH HISTORICAL CONTROL DATA: a frequency of 0 to 4% of cells is judged to be acceptable for structural aberrations, including gaps, in lymphocyte control cultures. Excluding gaps, it is acceptable for 0 to 2% of cells to have structural aberrations, and 0 to 1% of cells to exhibit polyploidy. An observable concentration-response relationship is required for modest increases in aberration frequency.

ADDITIONAL INFORMATION ON CYTOTOXICITY: the plateau of toxicity, followed by decreased toxicity, particularly evident in the 20-hour cultures of experiment 2 in the presence of S9, may be explained by the confounding factors noted above.
Remarks on result:
other: all strains/cell types tested

Following the results of cytotoxicity testing, the cultures treated with the following concentrations of DCPMS were selected for metaphase spread analysis (alongside appropriate vehicle and positive controls):

Experiment 1:

Without S9: 35.5, 53.25, 71 µg/ml

With S9: 141.3, 282.5, 565 µg/ml

Experiment 2:

20 h, without S9: 17.8, 35.5, 53.25 µg/ml

20 h, with S9: 141.3, 282.5, 565 µg/ml

44 h, without S9: 53.25 µg/ml

44 h, with S9: 565 µg/ml

 

Table 1: Results of chromosome analysis – Experiment 1 – 20-hour harvest without metabolic activation

Concentration of test material

Control*

Low dose

35.5 µg/ml

Mid dose

53.25 µg/ml

High dose

71 µg/ml

Positive control

EMS

500 µg/ml

Cytotoxicity

no

no

no

no

yes

Mean (% of control)

Mitotic index

2.50 (100)

2.43 (97)

1.88 (75)

1.43 (57)

1.20 (48)

Chromosome aberrations

Total (per 100 cells)

Gaps

6 (3.0)

3(1.5)

2 (1.0)

3 (1.5)

45 (30.7)

Chromatid aberrations

breaks

2 (1.0)

4 (2.0)

2 (1.0)

0 (0.0)

66 (44.0)

interchanges

2 (1.0)

0 (0.0)

0 (0.0)

0 (0.0)

15 (10.0)

Isochromatidaberrations

breaks

1 (0.5)

0 (0.0)

2 (1.0)

0 (0.0)

6 (4.0)

interchanges

0 (0.0)

0 (0.0)

0 (0.0)

0 (0.0)

1 (0.7)

Total number of aberrant cells

including gaps

10 (5.0)

6 (3.0)

4 (2.0)

3 (1.5)

70 (46.7)

excluding gaps

5 (2.5)

3 (1.5)

3 (1.5)

0 (0.0)

54 (36.0)

Mean frequency (%)

Polyploidy

0.0

0.5

1.0

0.0

0.0

* solvent control (acetone)

EMS, ethylmethanesulphonate

 

Table 2: Results of chromosome analysis – Experiment 1 – 20-hour harvest with metabolic activation

Concentration of test material

Control*

Low dose

141.3 µg/ml

Mid dose

282.5 µg/ml

High dose

565 µg/ml

Positive control

CP

25 µg/ml

Cytotoxicity

no

no

no

yes

yes

Mean (% of control)

Mitotic index

9.23 (100)

5.00 (54)

4.93 (53)

3.08 (33)

2.00 (22)

Chromosome aberrations

Total (per 100 cells)

Gaps

0 (0.0)

0 (0.0)

1 (0.5)

0 (0.0)

21 (10.5)

Chromatid aberrations

breaks

0 (0.0)

0 (0.0)

0 (0.0)

0 (0.0)

25 (12.5)

interchanges

0 (0.0)

0 (0.0)

0 (0.0)

0 (0.0)

1 (0.5)

Isochromatidaberrations

breaks

0 (0.0)

0 (0.0)

0 (0.0)

0 (0.0)

4 (2.0)

interchanges

0 (0.0)

0 (0.0)

1 (0.5)

0 (0.0)

0 (0.0)

Total number of aberrant cells

including gaps

0 (0.0)

0 (0.0)

2 (1.0)

0 (0.0)

39 (19.5)

excluding gaps

0 (0.0)

0 (0.0)

1 (0.5)

0 (0.0)

24 (12.0)

Mean frequency (%)

Polyploidy

0.0

0.5

0.0

0.0

0.0

* solvent control (acetone)

CP, cyclophosphamide

 

Table 3: Results of chromosome analysis – Experiment 2 – 20-hour harvest without metabolic activation

Concentration of test material

Control*

Low dose

17.8 µg/ml

Mid dose

35.5 µg/ml

High dose

53.25 µg/ml

Positive control

EMS

500 µg/ml

Cytotoxicity

no

no

no

yes

yes

Mean (% of control)

Mitotic index

3.70 (100)

2.88 (78)

2.80 (76)

1.83 (49)

1.25 (34)

Chromosome aberrations

Total (per 100 cells)

Gaps

1 (0.5)

0 (0.0)

2 (1.0)

0 (0.0)

29 (19.3)

Chromatid aberrations

breaks

0 (0.0)

0 (0.0)

1 (0.5)

0 (0.0)

32 (21.3)

interchanges

0 (0.0)

0 (0.0)

0 (0.0)

0 (0.0)

10 (6.7)

Isochromatidaberrations

breaks

3 (1.5)

0 (0.0)

0 (0.0)

0 (0.0)

3 (2.0)

interchanges

0 (0.0)

0 (0.0)

0 (0.0)

0 (0.0)

0 (0.0)

Total number of aberrant cells

including gaps

3 (1.5)

0 (0.0)

3 (1.5)

0 (0.0)

53 (35.3)

excluding gaps

2 (1.0)

0 (0.0)

1 (0.5)

0 (0.0)

35 (23.3)

Mean frequency (%)

Polyploidy

0.5

0.5

0.0

0.0

0.0

* solvent control (acetone)

EMS, ethylmethanesulphonate

 

Table 4: Results of chromosome analysis – Experiment 2 – 20-hour harvest with metabolic activation

Concentration of test material

Control*

Low dose

141.3 µg/ml

Mid dose

282.5 µg/ml

High dose

565 µg/ml

Positive control

CP

25 µg/ml

Cytotoxicity

no

no

no

yes

no

Mean (% of control)

Mitotic index

5.65 (100)

4.35 (77)

4.13 (73)

2.43 (43)

3.28 (58)

Chromosome aberrations

Total (per 100 cells)

Gaps

1 (0.5)

1 (0.5)

0 (0.0)

0 (0.0)

15 (3.8)

Chromatid aberrations

breaks

0 (00)

6 (3.0)

1 (0.5)

0 (0.0)

11 (2.8)

interchanges

0 (0.0)

0 (0.0)

0 (0.0)

1 (0.6)

0 (0.0)

Isochromatidaberrations

breaks

0 (0.0)

0 (0.0)

0 (0.0)

0 (0.0)

0 (0.0)

interchanges

0 (0.0)

0 (0.0)

0 (0.0)

0 (0.0)

1 (0.3)

Total number of aberrant cells

including gaps

1 (0.5)

7 (3.5)

1 (0.5)

1 (0.6)

25 (6.3)

excluding gaps

0 (0.0)

6 (3.0)

1 (0.5)

1 (0.6)

12 (3.0)

Mean frequency (%)

Polyploidy

0.0

0.5

0.0

0.0

0.2

* solvent control (acetone)

CP, cyclophosphamide

 

Table 5: Results of chromosome analysis – Experiment 2 – 44-hour harvest without metabolic activation

Concentration of test material

Control*

53.25 µg/ml

Cytotoxicity

no

no

Mean (% of control)

Mitotic index

7.93 (100)

5.53 (70)

Chromosome aberrations

Total (per 100 cells)

Gaps

0 (0.0)

1 (0.5)

Chromatid aberrations

breaks

0 (0.0)

0 (0.0)

interchanges

0 (0.0)

0 (0.0)

Isochromatidaberrations

breaks

4 (2.0)

0 (0.0)

interchanges

0 (0.0)_

0 (0.0)

Total number of aberrant cells

including gaps

2 (1.0)

1 (0.5)

excluding gaps

2 (1.0)

0 (0.0)

Mean frequency (%)

Polyploidy

0.0

0.0

* solvent control (acetone)

 

Table 6: Results of chromosome analysis – Experiment 2 – 44-hour harvest with metabolic activation

Concentration of test material

Control*

565 µg/ml

Cytotoxicity

no

no

Mean (% of control)

Mitotic index

8.53 (100)

8.88 (104)

Chromosome aberrations

Total (per 100 cells)

Gaps

0 (0.0)

3 (1.5)

Chromatid aberrations

breaks

0 (0.0)

1 (0.5)

interchanges

0 (0.0)

0 (0.0)

Isochromatidaberrations

breaks

0 (0.0)

0 (0.0)

interchanges

0 (0.0)

0 (0.0)

Total number of aberrant cells

including gaps

0 (0.0)

4 (2.0)

excluding gaps

0 (0.0)

1 (0.5)

Mean frequency (%)

Polyploidy

0.0

0.5

* solvent control (acetone)

Conclusions:
In a reliable in vitro mammalian chromosome aberration study conducted according to OECD Guideline 473 and in compliance with GLP, dicyclopentyl(dimethoxy)silane was not clastogenic to human lymphocytes at concentrations up to 565 μg/ml (limited by cytotoxicity) either in the presence or absence of metabolic activation by S9.
Executive summary:

In this GLP study, carried out according to OECD guideline 473 (and EU Method B.10), DCPMS was examined for clastogenic activity in primary cultures of human lymphocytes, both with and without metabolic activation by the microsomal enzyme fraction S9.

In Experiment 1, cell cultures were treated with DCPMS at up to 2260 μg/ml (with S9) for 4 hours, or up to 71 μg/ml (without S9) for 20 hours, and harvested at 20 hours. Cultures were then harvested and fixed for cytotoxicity and metaphase spread evaluation. Experiment 2 was carried out in the same way, with additional cultures harvested at 44 hours. A concentration of 141.3 μg/ml was also included in the absence of metabolic activation. Cultures treated with up to 565 μg/ml (with S9) and 71 μg/ml (without S9) were chosen for metaphase analysis, based on cytotoxicity results.

No significant concentration-related increases in the frequency of cells with chromosome aberrations or an abnormal number of chromosomes were observed.

Endpoint conclusion
Endpoint conclusion:
no adverse effect observed (negative)

Genetic toxicity in vivo

Description of key information

There are two studies available from a closely related substance, cyclohexyl(dimethoxy)methylsilane (CAS 17865-32-6).

In a mammalian erythrocyte micronucleus test conducted according to OECD Test Guideline 474 and in compliance with GLP, the read-across substance, cyclohexyl(dimethoxy)methylsilane, induced micronuclei in the polychromatic erythrocytes of male mice given 5000 mg/kg bw by oral gavage, a highly toxic dose, but not in females or not in either sex at 2500 mg/kg bw, which was also toxic; the increase is considered to be a result of excessive toxicity (Life Science Research, 1987).


In a rodent dominant lethal assay conducted according to a protocol similar to OECD Test Guideline 478 and in compliance with GLP, there was no evidence of germ cell mutation in mice after oral dosing of cyclohexyl(dimethoxy)methylsilane at up to 1250 mg/kg bw/day, a toxic dose (Life Science Research, 1989).

Link to relevant study records

Referenceopen allclose all

Endpoint:
in vivo mammalian germ cell study: cytogenicity / chromosome aberration
Type of information:
experimental study
Adequacy of study:
key study
Study period:
9 August 1988 to 30 November 1988
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Qualifier:
equivalent or similar to guideline
Guideline:
OECD Guideline 478 (Genetic Toxicology: Rodent Dominant Lethal Test)
Deviations:
no
Principles of method if other than guideline:
A 6-week dominant lethal study in mice
GLP compliance:
yes
Type of assay:
rodent dominant lethal assay
Species:
mouse
Strain:
CD-1
Sex:
male
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Charles River Breeding Laboratories (UK), Margate, Kent, England
- Age at study initiation: no data
- Weight at study initiation: 24-31 g
- Assigned to test groups randomly: no data
- Fasting period before study: no data
- Housing:group-housed (4 or 5/cage) during acclimation and dosing, high density polypropylene cages with stainless steel tops
- Diet: ad libitum, laboratory animal diet LAD 1
- Water: ad libitum
- Acclimation period: at least 5 days prior to treatment

ENVIRONMENTAL CONDITIONS
- Temperature (°C): target 21, acceptable range 19-25
- Humidity (%): 55+/- 15
- Air changes (per hr): 15/hr
- Photoperiod (hrs dark / hrs light): 12 hr light/12 hr dark

IN-LIFE DATES: From: 19-Aug-1988 To:30-Nov-1988
Route of administration:
oral: gavage
Vehicle:
- Vehicle(s)/solvent(s) used: corn oil
- Justification for choice of solvent/vehicle: test material freely miscible with corn oil and adequately stable in corn oil over a 72-hr period
- Concentration of test material in vehicle: dosed at 10 ml/kg bw, so presumably 5-125 mg/ml
- Amount of vehicle (if gavage or dermal): 10 ml/kg bw
- Type and concentration of dispersant aid (if powder): not applicable
- Lot/batch no. (if required): no data
- Purity: no data
Details on exposure:
PREPARATION OF DOSING SOLUTIONS: Required volumes of CHMMS violently mixed with corn oil initially during dose preparation. Inversion of the dose container employed prior to dosing to ensure maintenance of an adequate mixture and to minimise introduction of air bubbles.

DIET PREPARATION
not applicable
Duration of treatment / exposure:
6 weeks
Frequency of treatment:
Vehicle control and treatment groups treated 5 days/week for 5 weeks and daily for week 6; positive control group treated daily for 3 days during week 6.
Post exposure period:
Mating to untreated females (2 females/male) on day following final treatment, then repeated with fresh females seven days later and repeated until 3 separate weekly matings were completed
Remarks:
Doses / Concentrations:
50, 250 or 1250 mg/kg bw/day (1250 mg/kg bw/day dose reduced to 750 mg/kg bw/day from Monday of week 3 onwards)
Basis:
actual ingested
No. of animals per sex per dose:
25 males
Control animals:
yes, concurrent vehicle
Positive control(s):
ethylmethanesulphonate
- Justification for choice of positive control(s): guideline recommendation
- Route of administration: oral gavage
- Doses / concentrations: 200 mg/kg bw/day for 3 consecutive days during week 6
Tissues and cell types examined:
Treated males were mated with untreated females and the pregnancy rate, pre-implantation loss and post-implantation loss assessed
Details of tissue and slide preparation:
CRITERIA FOR DOSE SELECTION: based on a preliminary toxicity test

TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields): On the day following the final treatment, each male mouse was housed for mating with two virgin females. The individual males were re-caged with fresh females seven days later, and this was repeated until 3 separate weekly matings were completed. Females were inspected daily, in the mornings, during the mating period for the presence of vaginal plugs. Sixteen days after introduction to the males, the pregnant females were killed and examined for total implant number and early and late deaths.
Evaluation criteria:
Comparisons were made between treated and vehicle control groups each week for pregnancy rate, average number of implants (live and dead) and proportions of total implants found dead. Vaginal plugs were recorded to identify mated females and comparisons were made between treated and control groups for the proportion of females found to be pregnant. The average number of implants, live or dead, was calculated for each individual male and for each individual female of the groups, non-pregnant females being excluded, and treated and control groups were compared. Counts of early and late deaths were combined and the proportion of total implants found dead was obtained for each male. Individual male values were then used to test the homogeneity of each group.
Statistics:
Proportion of pregnant females: The variation between each treated group and the vehicle control group was assessed by calculation of the term X2B and the significance of the difference between the groups determined from chi-squared distribution tables.
Average number of implants per male and per female: The values for the treated and control groups were compared using a computer-based calculation of the non-parametic Mann-Whitney "U" test.
Proportion of implants found dead per male: A modified chi-squared calculation was performed giving X2W values and subsequent pairwise comparisons of test and control groups were undertaken, with calculation of X2B values. Where X2W values for both groups were non-significant, the significance of any difference between the groups was assessed by consideration of X2B alone. Where one or both groups was not homogeneous, the variance ratio was calculated and the significance obtained from the tables of the variance ratio distribution.
Key result
Sex:
male
Genotoxicity:
negative
Toxicity:
yes
Remarks:
Overt signs of toxicity and death in a single male at the top dose level
Vehicle controls validity:
valid
Negative controls validity:
not examined
Positive controls validity:
valid
Additional information on results:
RESULTS OF RANGE-FINDING STUDY
- Dose range: 500, 750, 1250 or 2000 mg/kg bw/day
- Clinical signs of toxicity in test animals: A single male in the top dosed group was killed in extremis, showing general lethargy and hind-limb paralysis, after receiving its sixth treatment. At this time and on later days of treatment, the remaining 3 animals of this group showed hyperactivity and/or partial hind-limb paralysis (transient, with full recovery by the morning after each dose). A single male dosed at 1250 mg/kg bw/day, also showed partial hind-limb paralysis on the last day of dosing. No other significant treatment-related effects were observed.
- Rationale for exposure: With the exception of a single male dosed at 2000 mg/kg bw/day, surviving males impregnated both of the two females with which they were caged during the subsequent mating period. Based on these findings and the overt toxicity seen, a maximum dosage of 1250 mg/kg bw/day was selected for the main study.

RESULTS OF DEFINITIVE STUDY
- Appropriateness of dose levels and route: The maximum level of CHMMS administration employed was sufficient to produce overt toxicity, demonstrating that the test material was absorbed.
- Statistical evaluation: There were no statistically significant effects on pregnancy rate, pre-implantation loss or post-implantation loss in any of the CHMMS treated groups.

During week 2 of dosing, males given 1250 mg/kg bw/day showed transient ataxia, loss of gripping reflex and other behavioural abnormalities. The effects included a brief period of hyperactivity post-dose, followed by ataxia and, in some cases, apparent deep sedation. Recovery was complete within 3 -4.5 hours of dosing. A single male of this group was found dead at the end of week 2. After reducing the dose to 750 mg/kg bw/day, some animals showed post-dose hyperactivity during weeks 3 and 4, and ataxia and prominent testes were also observed. No obvious signs of adverse reactions were seen at the mid- and low-dose levels.

Table: Summary of group data  

Treatment

group

Mating

week

Pregnant females

Total implants

Dead implants

Mutagenic indexb

No.

%a

No.

Mean/female

No.

Mean/female

 

Vehicle controls (corn oil)

1

2

3

48

46

46

96

92

92

559

577

568

11.6

12.5

12.3

32

24

26

0.7

0.5

0.5

5.7

4.2

4.6

CHMMS, 50 mg/kg bw/day

1

2

3

42

47

48

91

94

96

529

573

566

12.6

12.2

11.8

29

30

41

0.7

0.6

0.9

5.5

5.2

7.2

CHMMS, 250 mg/kg bw/day

1

2

3

43

46

46

86

92

92

524

555

546

12.2

12.1

11.9

23

30

26

0.5

0.7

0.6

4.4

5.4

4.8

CHMMS, 1250-750 mg/kg bw/day

1

2

3

 

39

44

39

89

92

81

461

555

456

11.8

12.6

11.7

29

18

25

0.7

0.4

0.6

6.3

3.2

5.5

EMS, 200 mg/kg bw/day

1

2

3

43

26

43

86

52**

86

398

246

507

9.3

9.5*

11.8

200

100

41

4.7

3.8

1.0

50.3**

40.7**

8.1*

 

a - Percentage of all females caged with surviving, treated males and later confirmed as pregnant.

b - Mutagenic Index = (Total dead implants/total implants) x 100

* - Significantly different from Group 1 value, p<0.05 (based on "per male" analysis)

** - Significantly different from Group 1 value, p<0.001

Conclusions:
In a well-conducted dominant lethal test, using a protocol similar to OECD guideline 478 and in compliance with GLP, there was no evidence of germ cell mutation in mice after oral dosing of cyclohexyl(dimethoxy)methylsilane at up to 1250 mg/kg bw/day, a toxic dose.
Executive summary:

A well-conducted dominant lethal test was performed using a protocol similar to OECD guideline 478 and to GLP.

Groups of 25 male mice were given oral gavage doses of 50, 250 or 1250 mg CHMS/kg bw/day, 5 days/week for 5 weeks and 7 days/week during the 6th week. The highest tested dose level was reduced to 750 mg/kg bw/day from the beginning of the 3rd week of dosing following marked adverse reactions to treatment (hyperactivity, ataxia and sedation). A control group received vehicle only (corn oil) and a positive control group received ethylmethanesulphonate at 200 mg/kg bw/day on the last 3 days of week 6.

On the day following the last day of dosing, each male was individually caged with 2 virgin females and allowed to mate; evidence of mating was inspected daily. After 7 days, the females were removed and replaced with fresh virgin females. This process was repeated once more to give a total of 3, 1-week mating periods. Sixteen days after introduction to the males, each group of females was killed and the numbers of live and dead (early or late death) implants were recorded. Three separate parameters were investigated: pregnancy rate, pre-implantation loss and post-implantation loss.

There was no evidence of germ cell mutation in mice after oral dosing with CHMS at up to 1250 mg/kg bw/day, a toxic dose. A clear positive response was seen with the positive control.

Endpoint:
in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
Remarks:
Type of genotoxicity: chromosome aberration
Type of information:
experimental study
Adequacy of study:
key study
Study period:
9 April 1987 to 21 August 1987
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
guideline study with acceptable restrictions
Remarks:
The study was conducted according to an appropriate OECD test guideline with acceptable restrictions. The restrictions were: only 2 dose levels (guideline recommends 3)
Qualifier:
according to guideline
Guideline:
OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
Deviations:
yes
Remarks:
(only 2 dose levels, guideline recommends 3)
Qualifier:
according to guideline
Guideline:
EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
Deviations:
yes
Remarks:
(only 2 dose levels, guideline recommends 3)
Qualifier:
according to guideline
Guideline:
EPA OTS 798.5395 (In Vivo Mammalian Cytogenics Tests: Erythrocyte Micronucleus Assay)
Deviations:
not specified
GLP compliance:
yes
Type of assay:
micronucleus assay
Species:
mouse
Strain:
CD-1
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Charles River Italia S.p.A., Calco, Italy
- Age at study initiation: 5-6 weeks
- Weight at study initiation: males 28-37 g, females 24-33 g
- Assigned to test groups randomly: yes
- Fasting period before study: overnight
- Housing: 5 animals of one sex/cage, clear polycarbonate cages measuring 35.5 x 23.5 x 19 cm with stainless steel mesh lid and floor
- Diet: ad libitum, Altromin MT diet
- Water: ad libitum
- Acclimation period: at least 5 days

ENVIRONMENTAL CONDITIONS
- Temperature (°C): monitored daily
- Humidity (%): monitored daily
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): 12 hr light/12 hr dark

IN-LIFE DATES: From: 9-Apr-1987 To:21-Aug-1987


Route of administration:
oral: gavage
Vehicle:
- Vehicle(s)/solvent(s) used: corn oil
- Justification for choice of solvent/vehicle: no data, but well-known vehicle
- Concentration of test material in vehicle: no data, but presumably 250 or 500 mg/ml
- Amount of vehicle (if gavage or dermal): 10 ml/kg bw
- Type and concentration of dispersant aid (if powder): not applicable
- Lot/batch no. (if required): no data
- Purity: no data
Details on exposure:
PREPARATION OF DOSING SOLUTIONS: Fresh solutions of the test material were prepared for each day's work; solutions being prepared on a weight/volume basis without correction for the displacement due to the volume occupied by the test material.
Duration of treatment / exposure:
Single exposure, with harvest times of 24, 48 or 72 hours
Frequency of treatment:
Once
Post exposure period:
24, 48 and 72 hours
Remarks:
Doses / Concentrations:
2500 or 5000 mg/kg bw
Basis:
actual ingested
No. of animals per sex per dose:
5/sex per dose for each exposure period
Control animals:
yes, concurrent vehicle
Positive control(s):
mitomycin C
- Justification for choice of positive control(s): a well-known clastogen
- Route of administration: oral, gavage
- Doses / concentrations: 5.00 mg/kg bw
Tissues and cell types examined:
Femoral bone marrow cells obtained by flushing with foetal calf serum
Details of tissue and slide preparation:
CRITERIA FOR DOSE SELECTION: Based on a preliminary toxicity test

DETAILS OF SLIDE PREPARATION: Cells were centrifuged at 1000 rpm for 5 min and the supernatant completely removed. A concentrated suspension of the cells of the sediment was then prepared to make smears on slides. The slides were air-dried overnight and then stained with May-Gruenwald and Giemsa, and mounted with Eukitt. Three slides were made for each animal.

METHOD OF ANALYSIS: The slides were randomly coded by a person not involved in the subsequent microscope scoring. They were then examined under medium magnification and one slide from each animal was selected according to staining and quality of smears. Where the toxicity of the test substance was not so great as to inhibit cell proliferation, at least 1000 polychromatic erythrocytes (PCEs) were examined per animal at high magnification (100x) for the presence or absence of micronuclei. At the same time, the number of normochromatic erythrocytes (NCEs) and micronucleated NCEs was also recorded.
Evaluation criteria:
The ratio of PCEs to NCEs gives an indication of the toxicity of treatment; an increase in the ratio indicates inhibition of cell division. The incidence of micronucleated NCEs gives an indication of the pre-treatment status of the animals. The incidence of micronucleated PCEs provides an index of induced genetic damage. The test material will be considered to have induced micronuclei if a statistically significant and biologically meaningful increase in micronucleus incidence (at p<0.05) is observed in any treatment group, in the pooled data for both sexes, or in the data for male or female groups alone.
Statistics:
Only counts from polychromatic cells were subjected to statistical analysis. Using the original observations (and not the micronucleus frequencies per 1000 cells) a modified chi-squared calculation was employed to compare treated and control groups. The degree of heterogeneity within each group was first calculated, and where it was significant it was taken into account in the comparison between groups. If there was no significant within-group heterogeneity, the chi-squared test was used to compare treated groups with the controls. If there was significant within-groups heterogeneity, then that group was compared with the controls using a variance ratio (F) value calculated from the between-group and within-group chi-squared values.
Sex:
male
Genotoxicity:
positive
Remarks:
5000 mg/kg bw
Toxicity:
yes
Remarks:
See "any other information" section below
Vehicle controls validity:
valid
Negative controls validity:
not applicable
Positive controls validity:
valid
Sex:
female
Genotoxicity:
negative
Toxicity:
yes
Remarks:
See "any other information" section below
Vehicle controls validity:
valid
Negative controls validity:
not applicable
Positive controls validity:
valid
Sex:
male/female
Genotoxicity:
negative
Toxicity:
yes
Remarks:
See "any other information" section below
Vehicle controls validity:
valid
Negative controls validity:
not applicable
Positive controls validity:
valid
Additional information on results:
RESULTS OF RANGE-FINDING STUDY
- Dose range: 5000 mg/kg bw
- Solubility: no data
- Clinical signs of toxicity in test animals: There was no excessive lethality
- Evidence of cytotoxicity in tissue analyzed: not applicable
- Rationale for exposure: There was no excessive lethality in the preliminary study.
- Harvest times: not applicable
- High dose with and without activation: not applicable
- Other: no data

RESULTS OF DEFINITIVE STUDY
There was no marked increase in the number of micronucleated PCEs in any of the treatment groups at the 24- and 72-hour sampling times. At the 48-hour sampling time, a pronounced increase was observed at the high-dose level. A dose-related increase in the ratio of mature to polychromatic erythrocytes (NCE:PCE ratio) was seen at the 4- hour sampling time in the test material treatment groups. Similar increases were also seen at 24 hours, indicating that the test material exerted an inhibitory effect on the cell division of bone marrow erythropoietic cells.

When analysed by treatment group and the male and female data were combined, no statistically significant increases in the incidence of micronucleated PCEs were observed when compared with the vehicle control group at the 24-, 48- or 72-hour sampling times. When analysed by sex, no statistically significant increases in the incidences of micronucleated PCEs were seen for the female animals when compared with the vehicle controls at any of the sampling times. In the males, a single statistically significant increase was observed at the high-dose level, at the 48-hour sampling time (p<0.01), with increased micronucleus incidence being present in 3 of the 5 animals. This observed micronucleated PCE incidence lay outside the historical negative control values for the laboratory.

A range of toxic signs was observed including loss of consciousness, hyperactivity and hypoactivity, loss of equilibrium and unusual gait, fibrillations and tremors, blanching, piloerection and ungroomed appearance. At the high-dose level, seven of the 30 animals died following treatment and were substituted by reserve animals.

Table 1: Summary of Incidence of Micronucleated Cells

 

Sampling time: 48 hours

 

MALES

 

Incidence of Micronuclei per 1000 cells

Dose-level

Scored Cells

NCE/PCE

Polychromatic

Normochromatic

mg/kg

PCE

NCE

Ratio

Mean

SE

Min

Max

Mean

SE

Min

Max

0.00

5000

5609

1.12

1.6

0.6

0.0

3.0

1.1

0.6

0.0

2.8

2500

4013

4450

1.11

1.5

0.6

0.0

3.0

1.1

0.7

0.0

2.5

5000

3600

5387

2.02

5.6

2.2

0.0

11.0

1.9

0.7

0.9

4.5

Mitomycin C

5.00

1610

3632

2.84

16.1

1.3

13.5

18.0

2.5

1.0

0.6

4.0

 

 

 

 

 

 

 

 

 

 

 

 

FEMALES

 

Incidence of Micronuclei per 1000 cells

Dose-level

Scored Cells

NCE/PCE

Polychromatic

Normochromatic

mg/kg

PCE

NCE

Ratio

Mean

SE

Min

Max

Mean

SE

Min

Max

0.00

5062

3467

0.69

1.4

0.7

0.0

3.0

0.8

0.5

0.0

2.3

2500

4426

7110

1.69

2.3

0.8

0.0

5.0

0.9

0.2

0.0

1.3

5000

3770

7206

2.20

1.8

1.0

0.0

5.0

0.4

0.2

0.0

1.0

Mitomycin C

5.00

3080

5219

2.12

11.3

3.5

4.0

23.3

5.1

1.7

1.1

10.0

 

 

 

 

 

 

 

 

 

 

 

 

BOTH SEXES

 

Incidence of Micronuclei per 1000 cells

Dose-level

Scored Cells

NCE/PCE

Polychromatic

Normochromatic

mg/kg

PCE

NCE

Ratio

Mean

SE

Min

Max

Mean

SE

Min

Max

0.00 /

 

 

 

 

 

 

 

 

 

 

 

0.00

10062

9076

0.9

1.5

0.4

0.0

3.0

0.9

0.4

0.0

2.8

2500 /

 

 

 

 

 

 

 

 

 

 

 

2500

8439

11560

1.43

1.9

0.5

0.0

5.0

1.0

0.3

0.0

2.5

5000 /

 

 

 

 

 

 

 

 

 

 

 

5000

7370

12593

2.11

3.7

1.3

0.0

11.0

1.1

0.4

0.0

4.5

Mitomycin C

5.00

4690

8851

2.39

13.1

2.3

4.0

23.3

4.2

1.2

0.6

10.0

MEAN = group mean incidence of micronucleated PCEs/NCEs

SE = standard error of the mean incidence

MIN = Minimum value observed in an individual animal

MAX = maximum value observed in an individual animal

Table 2: Statistical analysis

 

Sampling time: 48 hours

 

STATISTICAL ANALYSIS – BOTH SEXES

Dose level mg/kg

Within animals of one group

Between each group and control group

Males

Females

X2

Sign.

X2

Sign.

F

Sign.

0.00

0.00

10.82

N.S.

 

 

 

 

2500

2500

10.05

N.S.

0.45

N.S.

 

 

5000

5000

25.25

**

 

 

4.17

N.S.

Mitomycin C

5 mg/kg

17.61

*

 

 

 

37.75***

 

 

 

 

 

 

 

 

MALES ONLY

0.00

0.00

4.51

N.S.

 

 

 

 

2500

2500

3.37

N.S.

0.02

N.S.

 

 

5000

5000

9.23

N.S.

10.09

**

 

 

Mitomycin C

5 mg/kg

 

N.C.

 

N.C.

 

N.C.

 

 

 

 

 

 

 

 

FEMALES ONLY

0.00

0.00

6.37

N.S.

 

 

 

 

2500

2500

5.66

N.S.

1.01

N.S.

 

 

5000

5000

8.63

N.S.

0.31

N.S.

 

 

Mitomycin C

5 mg/kg

14.09

**

 

 

9.24

*

 

 

 

 

 

 

 

 

DIFFERENCES BETWEEN SEXES

 

 

 

 

Between male and female groups

0.00

0.00

 

 

0.08

N.S.

 

 

2500

2500

 

 

0.65

N.S.

 

 

5000

5000

 

 

6.90

**

 

 

Mitomycin C

5 mg/kg

 

 

 

 

2.73

N.S.

The chi-squared statistic (X2) and significance level (Sign.) are presented for within-group heterogeneity.

The Chi-squared (X2) or F-statistic (F), and significance level (Sign.) are shown for the comparison between the control and treatment group (or between males and females in the same treatment groups, as appropriate)

N.C. = not calculated

N.S. = not significant

* = statistically significant at p<0.05

** = statistically significant at p<0.01

*** = statistically significant at p<0.001

Conclusions:
In a mammlian erythrocyte micronucleus test conducted according to OECD Test Guideline 474 and in compliance with GLP, cyclohexyl(dimethoxy)methylsilane induced micronuclei in the polychromatic erythrocytes of male mice given 5000 mg/kg bw by oral gavage, a toxic dose, but not in females or when the two groups were combined.
Executive summary:

In a reliable study, conducted to OECD guideline 474 and to GLP, five male and five female mice were treated with a single oral, gavage, dose of CHMS at 2500 or 5000 mg/kg bw. Negative control animals received the vehicle only (corn oil) and positive control animals were treated with mitomycin C. Animals were sacrificed 24, 48 or 72 hours after treatment and bone marrow smear slides were prepared, stained and assessed for micronucleus induction in the polychromatic erythrocytes. The results obtained at each sampling time were subjected to statistical analysis using a modified chi-squared test.

A dose-related increase in the ratio of mature to polychromatic erythrocytes was observed at the 48-hour sampling time in the treatment groups, indicating that the test material exerted an inhibitory effect on the cell division of bone marrow erythropoietic cells. Similar increases were observed at the 24 -hour sampling time. There were no statistically significant increases in the incidences of micronucleated PCEs at any dose-level or sampling time when the results for the male and female animals were combined or those of the females were considered separately and compared with the vehicle control values. For the male animals, a single statistically significant increase was observed at 5000 mg/kg bw at the 48 -hour sampling time, with increases in the micronucleus incidence being seen in three of the five animals and the observed micronucleated PCE incidence lying outside the historical negative control values for the laboratory.

Endpoint conclusion
Endpoint conclusion:
no adverse effect observed (negative)

Additional information

Information on dicyclopentyl(dimethoxy)silane (CAS 126990-35-0) is available from four reliable bacterial mutagenicity tests. The key study was conducted according to Japanese guidelines and in compliance with GLP. Dicyclopentyl(dimethoxy)silane showed no mutagenic potential in this reverse mutagenicity (Ames) assay in at up to 5000 μg/plate, with or without metabolic activation (BML Inc., 1993a). The three supporting studies were conducted according to OECD Test Guideline 471 and in compliance with GLP. Dicyclopentyl(dimethoxy)silane showed no mutagenic potential with or without metabolic activation in these bacterial mutagenicity assays in S. typhimurium strains TA98, TA100, TA1535, TA1537 and TA1538 at up to 5000 μg/plate (Cytotest Cell Research Gmbh 1995b; Safepharm Laboratories Limited, 1995; Huls AG, 1995). Reliable data are also available on the hydrolysis product of the registered substance, dicyclopentylsilanediol (DCPMS-OH2, CAS 211495-85-1). In a GLP study conducted according to Japanese guidelines, dicyclopentylsilanediol showed no mutagenic potential in an Ames assay in Salmonella typhimurium strains TA98, TA100, TA1535 and TA1537 and Escherichia coli WP2 uvrA at up to 1250 μg/plate, with and without metabolic activation (BML Inc., 1993b).

Further information is available from three reliable in vitro cytogenicity tests, all conducted according to OECD Test Guideline 473 and in compliance with GLP. In the key study dicyclopentyl(dimethoxy)silane

was not clastogenic to human lymphocytes in vitro at concentrations up to 565 μg/ml (limited by cytotoxicity) either in the presence or absence of metabolic activation (Safepharm Laboratories Limited, 1996). In the supporting studies, no clastogenicity was seen in Chinese hamster ovary cells at up to 200 µg/ml (Cytotest Cell Research GmbH, 1995a) or in Chinese hamster V79 cells at up to 120 µg/ml (Huntingdon Research Centre Ltd., 1995) either in the presence or absence of metabolic activation (in both studies, the highest concentration tested was limited by cytotoxicity). In a reliable study, conducted according to a protocol similar to OECD Test Guideline 473, the hydrolysis product was not clastogenic to Chinese hamster lung fibroblast cells at concentrations of up to 1.3 mg/ml (limited by cytotoxicity), either in the presence or in the absence of metabolic activation (BML Inc, 1992).

Two in vivo genotoxicity studies are available for a related substance, cyclohexyl(dimethoxy)methylsilane (CAS 17865-32-6). In a well-conducted dominant lethal test, using a protocol similar to OECD Test Guideline 478 and in compliance with GLP, there was no evidence of germ cell mutation in mice after oral dosing of cyclohexyl(dimethoxy)methylsilane for 2 weeks at up to 1250 mg/kg bw/day, a toxic dose (Life Science Research, 1989).

In a reliable study, conducted according to OECD Test Guideline 474 and in compliance with GLP, cyclohexyl(dimethoxy)methylsilane induced micronuclei in the polychromatic erythrocytes of male mice given 5000 mg/kg bw by oral gavage, a dose that was lethal to some of the animals. No statistically significant effect was seen in females, or when data for males and females were combined, and there was no increase in the frequency of micronuclei in either sex at 2500 mg/kg bw, a toxic dose (Life Science Research, 1987). The occurrence of a positive genotoxic response only at a dose high enough to induce severe toxicity is of questionable relevance to humans and OECD Test Guideline 474 requires testing only up to "the dose producing signs of toxicity such that higher dose levels would be expected to produce lethality." Read-across to the registered substance is considered appropriate as the silicon containing products of hydrolysis have similar functional groups (cyclopentyl/cyclohexyl and methyl), and do not include structural alerts for genotoxicity. The alkoxysilanes, excluding those with functional groups that are known to be associated with genetic toxicity (such as epoxy) are largely non-genotoxic.

The most reliable studies were chosen as key. Where there was more than one reliable study, the most recent was selected. The results of all the studies are in agreement. In view of the availability of in vivo data for the related substance, cyclohexyl(dimethoxy)methylsilane (CAS 17865-32-6) from studies in somatic cells and in germ cells, and the overall weight of evidence of the information available, it is considered that testing for mutagenicity to mammalian cells in vitro is not required, as the overall conclusion for genetic toxicity in the studies was negative.


Justification for classification or non-classification

Based on the available in vitro studies with dicyclopentyl(dimethoxy)silane and in vivo genotoxicity data for the analogue substance cyclohexyl(dimethoxy)methylsilane, dicyclopentyl(dimethoxy)silane does not require classification for mutagenicity according to Regulation (EC) No 1272/2008.