Registration Dossier

Administrative data

Key value for chemical safety assessment

Genetic toxicity in vitro

Description of key information

Negative Ames tests with S. typhimurium TA 1535, TA 1537, TA 98 and TA 100, and E. coli WP2 uvr A, with and without metabolic activation.
Negative results in a mammalian cell gene mutation test using mouse lymphoma L5178Y cells, with and without metabolic activation.

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:
01 Sep 2009 - 23 Oct 2009
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: GLP-Guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 471 (Bacterial Reverse Mutation Assay)
Deviations:
no
GLP compliance:
yes
Type of assay:
bacterial reverse mutation assay
Target gene:
his operon (S. typhimurium), trp operon (E. coli)
Species / strain / cell type:
S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
Species / strain / cell type:
E. coli WP2 uvr A
Metabolic activation:
with and without
Metabolic activation system:
S9 mix from Delor 106-induced Wistar male rats. Delor 106 is a mixture of PCBs.
Test concentrations with justification for top dose:
Toxicity test in tester strain TA 98: 10, 100, 500, 1000, 2500, 5000 µg/plate
1st mutagenicity test: 50, 150, 500, 1500, 5000 µg/plate
2nd mutagenicity test: 15, 50, 150, 500, 1500 µg/plate
Vehicle / solvent:
- Vehicle(s)/solvent(s) used: water
- Justification for choice of solvent/vehicle: the test material is almost insoluble in any solvent. Water was used as suspension medium.
Untreated negative controls:
yes
Negative solvent / vehicle controls:
yes
Remarks:
0.1 mL water
True negative controls:
no
Positive controls:
yes
Positive control substance:
other: sodium azide (1.5 µg/plate), 4-nitro-o-phenylenediamine (20 µg/plate), 2-aminofluorene (10 µg/plate), 2-aminoanthracene (1 and 2.5 µg/plate), 9-aminoacridine hydrochloride monohydrate (100 µg/plate), N-methyl-N’-nitro-N-nitrosoguanidine (20 µg/plate)
Details on test system and experimental conditions:
METHOD OF APPLICATION: in agar (plate incorporation)


DURATION
- Exposure duration: 48-72 h


NUMBER OF REPLICATIONS: 3


DETERMINATION OF CYTOTOXICITY
- Method: cloning efficiency
Evaluation criteria:
The main criterion for the evaluation of results was the modified two-fold increase rule. According to this rule, a result is considered positive if a reproducible dose-effect and/or a doubling of the Rt/Rc ratio is reached (Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control).
Species / strain:
S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
Metabolic activation:
with and without
Genotoxicity:
negative
Cytotoxicity / choice of top concentrations:
other: Slight cytotoxic effect at 5000 µg/plate (thinner bacterial background) in preliminary toxicity test in strain TA 98 without metabolic activation. The effect was not reproducible in the first series of mutagenicity testing.
Vehicle controls validity:
valid
Untreated negative controls validity:
valid
Positive controls validity:
valid
Species / strain:
E. coli WP2 uvr A
Metabolic activation:
with and without
Genotoxicity:
negative
Cytotoxicity / choice of top concentrations:
not determined
Vehicle controls validity:
valid
Untreated negative controls validity:
valid
Positive controls validity:
valid

The effect of Ashes (residues) – Fly Ash on S. typhimurium TA 100 (two experiments).

Note: Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control.

 

 

Without metabolic activation (No. of revertants per plate)

With metabolic activation (No. of revertants per plate)

Doses (µg/plate)

Mean ± SD

Rt/Rc

Mean ± SD

Rt/Rc

Neg. control

149±10

-

138±2

-

Water (solvent control)

146±14

-

139±8

-

50

141±8

1.0

142±11

1.0

150

138±14

0.9

136±6

1.0

500

140±6

1.0

137±12

1.0

1500

149±9

1.0

134±16

1.0

5000

119±23

0.8

142±15

1.0

AS/2 -AF

441±13

3.0

1235±41

8.9

 

 

 

 

 

Neg. control

132±7

-

134±9

-

Water (solvent control)

142±8

-

138±8

-

15

133±4

0.9

136±17

1.0

50

133±5

0.9

121±12

0.9

150

128±4

0.9

121±5

0.9

500

132±11

0.9

120±6

0.9

1500

131±4

0.9

96±14

0.7

AS/2 -AF

489±3

3.5

1132±49

8.2

 

 

The effect of Ashes (residues) – Fly Ash on S. typhimurium TA 1535 (two experiments).

Note: Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control.

 

 

Without metabolic activation (No. of revertants per plate)

With metabolic activation (No. of revertants per plate)

Doses (µg/plate)

Mean ± SD

Rt/Rc

Mean ± SD

Rt/Rc

Neg. control

29±2

-

19±3

-

Water (solvent control)

27±1

-

21±2

-

50

26±5

1.0

17±1

0.8

150

27±1

1.0

18±3

0.9

500

25±1

0.9

22±3

1.0

1500

30±4

1.1

18±2

0.9

5000

25±6

0.9

21±1

1.0

AS/2-AA

431±5

15.9

203±13

9.6

 

 

 

 

 

Neg. control

25±4

-

15±3

-

Water (solvent control)

24±4

-

16±3

-

15

26±2

1.1

14±4

0.9

50

22±4

0.9

17±6

1.1

150

24±3

1.0

17±2

1.0

500

25±5

1.1

16±3

1.0

1500

22±3

0.9

17±1

1.0

AS/2-AA

567±14

24

228±21

14.2

 

 

The effect of Ashes (residues) – Fly Ash on S. typhimurium TA 98 (two experiments)

Note: Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control.

 

 

Without metabolic activation (No. of revertants per plate)

With metabolic activation (No. of revertants per plate)

Doses (µg/plate)

Mean ± SD

Rt/Rc

Mean ± SD

Rt/Rc

Neg. control

31±2

-

28±2

-

Water (solvent control)

27±4

-

25±3

-

50

25±1

0.9

29±6

1.2

150

35±8

1.3

25±4

1.0

500

23±2

0.9

29±4

1.2

1500

28±4

1.0

29±6

1.2

5000

25±5

0.9

26±5

1.1

NPD/2-AF

542±18

20.1

1261±64

51.1

 

 

 

 

 

Neg. control

30±5

-

34±4

-

Water (solvent control)

29±4

-

35±5

-

15

30±3

1.0

33±1

0.9

50

32±4

1.1

40±3

1.1

150

28±4

1.0

47±6

1.3

500

36±7

1.2

37±6

1.0

1500

31±1

1.0

32±5

0.9

NPD/2-AF

818±92

27.9

1722±67

48.7

 

 

The effect of Ashes (residues) – Fly Ash on S. typhimurium TA 1537 (two experiments)

Note: Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control.

 

 

Without metabolic activation (No. of revertants per plate)

With metabolic activation (No. of revertants per plate)

Doses (µg/plate)

Mean ± SD

Rt/Rc

Mean ± SD

Rt/Rc

Neg. control

13±3

-

12±1

-

Water (solvent control)

12±2

-

14±2

-

50

11±0

0.9

14±1

1.0

150

14±2

1.2

11±1

0.8

500

14±2

1.1

21±3

1.5

1500

11±1

0.9

14±2

1.0

5000

11±1

0.9

14±0

1.0

9-AAc/2-AA

1184±7

98.6

160±12

11.1

 

 

 

 

 

Neg. control

11±3

-

15±2

-

Water (solvent control)

11±2

-

16±2

-

15

15±5

1.3

17±2

1.0

50

12±1

1.1

17±2

1.0

150

13±1

1.2

15±1

0.9

500

14±1

1.2

15±2

0.9

1500

12±1

1.1

17±3

1.1

9-AAc/2-AA

1077±48

97.9

171±16

10.5

 

 

The effect of Ashes (residues) – Fly Ash on E. coli WP2 uvrA (two experiments)

Note: Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control.

 

 

Without metabolic activation (No. of revertants per plate)

With metabolic activation (No. of revertants per plate)

Doses (µg/plate)

Mean ± SD

Rt/Rc

Mean ± SD

Rt/Rc

Neg. control

28±3

-

32±4

-

Water (solvent control)

24±3

-

35±2

-

50

24±2

1.0

26±5

0.7

150

25±5

1.0

29±4

0.8

500

28±4

1.2

27±2

0.8

1500

26±2

1.1

36±2

1.0

5000

31±4

1.3

18±2

0.5

MNNG/2-AA

534±17

22.2

140±20

3.9

 

 

 

 

 

Neg. control

32±4

-

42±2

-

Water (solvent control)

40±3

-

35±5

-

15

39±8

1.0

45±3

1.3

50

33±6

0.8

40±3

1.1

150

41±5

1.0

39±7

1.1

500

32±4

0.8

39±0

1.1

1500

37±2

0.9

41±9

1.2

MNNG/2-AA

581±16

14.5

325±16

9.2

  

AS: sodium azide (1.5 µg/plate; TA 100 and TA 1535 without metabolic activation)

NPD: 4-nitro-o-phenylenediamine (20 µg/plate; TA 98 without metabolic activation)

2-AF: 2-aminofluorene (10 µg/plate; TA 100 and TA 98 with metabolic activation)

2-AA: 2-aminoanthracene (1 µg/plate with TA 1535; 2.5 µg/plate with TA 1537; 25 µg/plate with E. coli; all tests with metabolic activation)

9AAc: 9-aminoacridine hydrochloride monohydrate (100 µg/plate; TA 1537 without metabolic activation)

MNNG: N-methyl-N’nitro-N-nitrosoguanidine (20 µg/plate; E.coli without metabolic activation)

- : not evaluated

Conclusions:
Under the experimental conditions described, the test substance Ashes (residues) - Fly Ash was nonmutagenic in S. typhimurium strains TA 98, TA 100, TA 1535 and TA 1537 as well as in E. coli strain WP2 uvrA both with and without metabolic activation.
Endpoint:
in vitro gene mutation study in bacteria
Type of information:
experimental study
Adequacy of study:
key study
Study period:
16 Nov 2007 - 11 Jan 2008
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: GLP-Guideline study
Qualifier:
according to guideline
Guideline:
EU Method B.13/14 (Mutagenicity - Reverse Mutation Test Using Bacteria)
Deviations:
no
Qualifier:
equivalent or similar to guideline
Guideline:
OECD Guideline 471 (Bacterial Reverse Mutation Assay)
GLP compliance:
yes
Type of assay:
bacterial reverse mutation assay
Target gene:
his operon (S. typhimurium), trp operon (E. coli)
Species / strain / cell type:
S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
Species / strain / cell type:
E. coli WP2 uvr A
Metabolic activation:
with and without
Metabolic activation system:
S9 mix from Delor 106-induced Wistar male rats. Delor 106 is a mixture of PCBs.
Test concentrations with justification for top dose:
Toxicity test in tester strain TA 100: 10, 100, 500, 1000, 2500, 5000 µg/plate
1st and 2nd mutagenicity tests: 50, 150, 500, 1500, 5000 µg/plate
Vehicle / solvent:
- Vehicle(s)/solvent(s) used: DMSO
- Justification for choice of solvent/vehicle: Solubulity tests were performed prior to the main test. The test material is practically insoluble in any of the solvents commonly used and compatible with this mutagenicity test (water, dimethylsulfoxide (DMSO), dimethylformamide (DMFA), ethanol 96%, acetone, cyclohexane). DMSO was chosen due to the homogeneity of the suspensions obtained and its historical use in the testing laboratory.
Untreated negative controls:
yes
Negative solvent / vehicle controls:
yes
Remarks:
0.1 mL DMSO
True negative controls:
no
Positive controls:
yes
Positive control substance:
other: sodium azide (1.5 µg/plate), 4-nitro-o-phenylenediamine (20 µg/plate), 2-aminofluorene (10 µg/plate), 2-aminoanthracene (1 and 2.5 µg/plate), 9-aminoacridine hydrochloride monohydrate (100 µg/plate), N-methyl-N’-nitro-N-nitrosoguanidine (20 µg/plate)
Details on test system and experimental conditions:
METHOD OF APPLICATION: in agar (plate incorporation)


DURATION
- Exposure duration: 48-72 h


NUMBER OF REPLICATIONS: 3


DETERMINATION OF CYTOTOXICITY
- Method: cloning efficiency
Evaluation criteria:
The main criterion for the evaluation of results was the modified two-fold increase rule. According to this rule, a result is considered positive if a reproducible dose-effect and/or a doubling of the Rt/Rc ratio is reached (Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control).
Species / strain:
S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
Metabolic activation:
with and without
Genotoxicity:
negative
Cytotoxicity / choice of top concentrations:
other: no cytotoxicity as determined with tester strain TA 100 without metabolic activation
Vehicle controls validity:
valid
Untreated negative controls validity:
valid
Positive controls validity:
valid
Species / strain:
E. coli WP2 uvr A
Metabolic activation:
with and without
Genotoxicity:
negative
Cytotoxicity / choice of top concentrations:
not determined
Vehicle controls validity:
valid
Untreated negative controls validity:
valid
Positive controls validity:
valid

The effect of Ashes (residues) – Fly Ash on S. typhimurium TA 100 (two experiments).

Note: Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control.

 

 

Without metabolic activation (No. of revertants per plate)

With metabolic activation (No. of revertants per plate)

Doses (µg/plate)

Mean ± SD

Rt/Rc

Mean ± SD

Rt/Rc

Neg. control

87±7

-

108±3

-

DMSO (solvent control)

90±7

-

105±10

-

50

81±8

0.9

103±6

1.0

150

95±5

1.1

100±3

1.0

500

95±8

1.1

94±6

0.9

1500

100±8

1.1

93±2

0.9

5000

82±2

0.9

79±12

0.8

AS/2 -AF

476±16

5.3

527±22

5.0

 

 

 

 

 

Neg. control

125±6

-

137±4

-

DMSO (solvent control)

114±7

-

128±7

-

50

118±8

1.0

117±7

0.9

150

114±5

1.0

130±9

1.0

500

110±0

1.0

125±3

1.0

1500

108±0

1.0

129±6

1.0

5000

107±6

0.9

118±14

0.9

AS/2 -AF

560±30

4.9

998±53

7.8

 

 

The effect of Ashes (residues) – Fly Ash on S. typhimurium TA 1535 (two experiments).

Note: Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control.

 

 

Without metabolic activation (No. of revertants per plate)

With metabolic activation (No. of revertants per plate)

Doses (µg/plate)

Mean ± SD

Rt/Rc

Mean ± SD

Rt/Rc

Neg. control

23±

-

15±1

-

DMSO (solvent control)

20±13

-

18±0

-

50

24±1

1.2

17±2

0.9

150

24±2

1.2

22±2

1.2

500

23±3

1.1

16±1

0.9

1500

21±1

1.0

15±3

0.8

5000

22±3

1.1

18±2

1.0

AS/2-AA

475±22

23.3

216±17

11.8

 

 

 

 

 

Neg. control

25±1

-

21±2

-

DMSO (solvent control)

25±2

-

24±3

-

50

25±5

1.0

26±2

1.1

150

28±2

1.1

21±2

0.9

500

25±7

1.0

21±2

0.9

1500

24±2

1.0

17±1

0.7

5000

21±2

0.8

20±6

0.8

AS/2-AA

569±13

22.7

216±2

9.1

 

 

The effect of Ashes (residues) – Fly Ash on S. typhimurium TA 98 (two experiments)

Note: Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control.

 

 

Without metabolic activation (No. of revertants per plate)

With metabolic activation (No. of revertants per plate)

Doses (µg/plate)

Mean ± SD

Rt/Rc

Mean ± SD

Rt/Rc

Neg. control

29±4

-

32±4

-

DMSO (solvent control)

26±4

-

28±1

-

50

25±1

1.0

31±2

1.1

150

26±5

1.0

30±1

1.1

500

27±4

1.0

28±5

1.0

1500

30±3

1.2

29±9

1.0

5000

26±3

1.0

30±3

1.1

NPD/2-AF

621±14

23.9

886±71

31.3

 

 

 

 

 

Neg. control

37±3

-

36±2

-

DMSO (solvent control)

29±3

-

36±3

-

50

33±3

1.1

35±1

1.0

150

34±10

1.1

40±9

1.1

500

28±2

0.9

32±1

0.9

1500

31±5

1.0

34±6

0.9

5000

28±1

0.9

35±3

1.0

NPD/2-AF

984±132

33.5

1037±121

28.5

 

 

The effect of Ashes (residues) – Fly Ash on S. typhimurium TA 1537 (two experiments)

Note: Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control.

 

 

Without metabolic activation (No. of revertants per plate)

With metabolic activation (No. of revertants per plate)

Doses (µg/plate)

Mean ± SD

Rt/Rc

Mean ± SD

Rt/Rc

Neg. control

12±3

-

9±1

-

DMSO (solvent control)

13±1

-

11±3

-

50

14±2

1.0

12±1

1.1

150

9±3

0.7

14±2

1.3

500

12±2

0.9

13±4

12

1500

14±2

1.1

11±1

1.0

5000

8±0

0.6

10±2

0.9

9-AAc/2-AA

1008±30

77.5

176±25

16.5

 

 

 

 

 

Neg. control

18±2

-

17±2

-

DMSO (solvent control)

14±1

-

16±2

-

50

14±2

1.0

16±3

1.0

150

12±1

0.9

14±4

0.9

500

13±1

0.9

16±1

1.0

1500

13±3

0.9

15±1

1.0

5000

11±3

0.8

12±3

0.7

9-AAc/2-AA

958±123

68.4

169±20

10.8

 

 

The effect of Ashes (residues) – Fly Ash on E. coli WP2 uvrA (two experiments)

Note: Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control.

 

 

Without metabolic activation (No. of revertants per plate)

With metabolic activation (No. of revertants per plate)

Doses (µg/plate)

Mean ± SD

Rt/Rc

Mean ± SD

Rt/Rc

Neg. control

30±1

-

37±9

-

DMSO (solvent control)

30±0

-

30±6

-

50

25±1

0.8

28±5

0.9

150

28±6

0.9

27±1

0.9

500

29±1

1.0

34±2

1.1

1500

28±3

0.9

29±2

1.0

5000

32±6

1.1

32±7

1.1

MNNG/2-AA

773±43

25.8

109±7

3.6

 

 

 

 

 

Neg. control

26±5

-

30±5

-

DMSO (solvent control)

24±4

-

29±4

-

50

22±5

0.9

24±2

0.8

150

29±9

1.2

24±2

0.8

500

30±2

1.3

22±3

0.8

1500

30±5

1.2

24±4

0.8

5000

20±0

0.8

24±3

0.8

MNNG/2-AA

716±29

29.8

102±11

3.6

  

AS: sodium azide (1.5 µg/plate; TA 100 and TA 1535 without metabolic activation)

NPD: 4-nitro-o-phenylenediamine (20 µg/plate; TA 98 without metabolic activation)

2-AF: 2-aminofluorene (10 µg/plate; TA 100 and TA 98 with metabolic activation)

2-AA: 2-aminoanthracene (1 µg/plate with TA 1535; 2.5 µg/plate with TA 1537; 25 µg/plate with E. coli; all tests with metabolic activation)

9AAc: 9-aminoacridine hydrochloride monohydrate (100 µg/plate; TA 1537 without metabolic activation)

MNNG: N-methyl-N’nitro-N-nitrosoguanidine (20 µg/plate; E.coli without metabolic activation)

- : not evaluated

 

Conclusions:
Under the experimental conditions described, the test substance Ashes (residues) was nonmutagenic in S. typhimurium strains TA 98, TA 100, TA 1535 and TA 1537 as well as in E. coli strain WP2 uvrA both with and without metabolic activation.
Endpoint:
in vitro gene mutation study in bacteria
Type of information:
experimental study
Adequacy of study:
key study
Study period:
04 Sep 2009 - 26 Oct 2009
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: GLP-Guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 471 (Bacterial Reverse Mutation Assay)
Deviations:
no
GLP compliance:
yes
Type of assay:
bacterial reverse mutation assay
Target gene:
his operon (S. typhimurium), trp operon (E. coli)
Species / strain / cell type:
S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
Species / strain / cell type:
E. coli WP2 uvr A
Metabolic activation:
with and without
Metabolic activation system:
S9 mix from Delor 106-induced Wistar male rats. Delor 106 is a mixture of PCBs.
Test concentrations with justification for top dose:
Toxicity test: 10, 100, 500, 1000, 2500, 5000 µg/plate
1st mutagenicity test: 50, 150, 500, 1500, 5000 µg/plate
2nd mutagenicity test: 15, 50, 150, 500, 1500 µg/plate
Vehicle / solvent:
- Vehicle(s)/solvent(s) used: water
- Justification for choice of solvent/vehicle: the test material is almost insoluble in any solvent. Water was used as suspension medium.
Untreated negative controls:
yes
Negative solvent / vehicle controls:
yes
Remarks:
0.1 mL water
True negative controls:
no
Positive controls:
yes
Positive control substance:
other: sodium azide (1.5 µg/plate), 4-nitro-o-phenylenediamine (20 µg/plate), 2-aminofluorene (10 µg/plate), 2-aminoanthracene (1 and 2.5 µg/plate), 9-aminoacridine hydrochloride monohydrate (100 µg/plate), N-methyl-N’-nitro-N-nitrosoguanidine (20 µg/plate)
Details on test system and experimental conditions:
METHOD OF APPLICATION: in agar (plate incorporation)


DURATION
- Exposure duration: 48-72 h


NUMBER OF REPLICATIONS: 3


DETERMINATION OF CYTOTOXICITY
- Method: cloning efficiency
Evaluation criteria:
The main criterion for the evaluation of results was the modified two-fold increase rule. According to this rule, the result is positive when a reproducible dose-effect and/or a doubling of the Rt/Rc ratio is reached (Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control).
Species / strain:
S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
Metabolic activation:
with and without
Genotoxicity:
negative
Cytotoxicity / choice of top concentrations:
other: no cytotoxicity as determined with tester strain TA 98 without metabolic activation
Vehicle controls validity:
valid
Untreated negative controls validity:
valid
Positive controls validity:
valid
Species / strain:
E. coli WP2 uvr A
Metabolic activation:
with and without
Genotoxicity:
negative
Cytotoxicity / choice of top concentrations:
not determined
Vehicle controls validity:
valid
Untreated negative controls validity:
valid
Positive controls validity:
valid

The effect of Ashes (residues) – Slag on S. typhimurium TA 100 (two experiments).

Note: Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control.

 

 

Without metabolic activation (No. of revertants per plate)

With metabolic activation (No. of revertants per plate)

Doses (µg/plate)

Mean ± SD

Rt/Rc

Mean ± SD

Rt/Rc

Neg. control

132±7

-

134±9

-

Water (solvent control)

142±8

-

138±8

-

50

120±6

0.8

137±11

1.0

150

126±6

0.9

131±8

0.9

500

121±10

0.9

130±9

0.9

1500

133±9

0.9

140±10

1.0

5000

127±5

0.9

130±2

0.9

AS/2-AF

489±3

3.5

1132±49

8.2

 

 

 

 

 

Neg. control

112±3

-

124±6

-

Water (solvent control)

110±6

-

117±12

-

15

114±12

1.0

115±6

1.0

50

109±6

1.0

110±10

0.9

150

116±9

1.1

119±9

1.0

500

109±10

1.0

114±7

1.0

1500

114±2

1.0

110±7

0.9

AS/2-AF

517±6

4.7

1411±33

12.0

 

 

The effect of Ashes (residues) – Slag on S. typhimurium TA 1535 (two experiments).

Note: Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control.

 

 

Without metabolic activation (No. of revertants per plate)

With metabolic activation (No. of revertants per plate)

Doses (µg/plate)

Mean ± SD

Rt/Rc

Mean ± SD

Rt/Rc

Neg. control

25±4

-

15±3

-

Water (solvent control)

24±4

-

16±3

-

50

20±1

0.8

18±4

1.1

150

26±4

1.1

18±3

1.1

500

22±2

0.9

20±4

1.3

1500

18±3

0.8

16±3

1.0

5000

20±3

0.8

20±1

1.2

AS/2-AA

567±14

24.0

228±21

14.2

 

 

 

 

 

Neg. control

19±2

-

17±3

-

Water (solvent control)

19±5

-

18±4

-

15

15±0

0.8

19±3

1.1

50

19±4

1.0

18±2

1.0

150

17±2

0.9

19±3

1.1

500

14±3

0.7

18±1

1.0

1500

15±4

0.8

16±1

0.9

AS/2-AA

523±4

27.1

202±6

11.4

 

 

The effect of Ashes (residues) – Slag on S. typhimurium TA 98 (two experiments).

Note: Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control.

 

 

Without metabolic activation (No. of revertants per plate)

With metabolic activation (No. of revertants per plate)

Doses (µg/plate)

Mean ± SD

Rt/Rc

Mean ± SD

Rt/Rc

Neg. control

30±5

-

34±4

-

Water (solvent control)

29±4

-

35±5

-

50

27±6

0.9

42±2

1.2

150

28±4

0.9

41±7

1.2

500

27±6

0.9

30±5

0.8

1500

32±3

1.1

34±3

1.0

5000

27±4

0.9

31±3

0.9

NPD/2-AF

818±92

27.9

1722±67

48.7

 

 

 

 

 

Neg. control

39±6

-

37±7

-

Water (solvent control)

38±7

-

39±1

-

15

39±5

1.0

40±1

1.0

50

34±4

0.9

40±4

1.0

150

40±3

1.1

34±3

0.9

500

36±6

0.9

37±0

1.0

1500

36±5

1.0

30±1

0.8

NPD/2-AF

908±50

24.1

1604±45

41.5

 

 

The effect of Ashes (residues) – Slag on S. typhimurium TA 1537 (two experiments).

Note: Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control.

 

 

Without metabolic activation (No. of revertants per plate)

With metabolic activation (No. of revertants per plate)

Doses (µg/plate)

Mean ± SD

Rt/Rc

Mean ± SD

Rt/Rc

Neg. control

11±3

-

18±3

-

Water (solvent control)

11±2

-

17±2

-

50

13±0

1.2

17±3

1.0

150

13±1

1.2

14±4

0.8

500

11±3

1.0

15±2

0.9

1500

12±1

1.1

21±4

1.2

5000

10±4

0.9

9±2

0.5

9-AAc/2-AA

1077±48

97.9

139±3

8.2

 

 

 

 

 

Neg. control

13±3

-

15±2

-

Water (solvent control)

12±2

-

16±2

-

15

15±2

1.3

16±2

1.0

50

13±3

1.1

16±2

1.0

150

11±3

0.9

15±4

0.9

500

13±2

1.1

19±3

1.2

1500

14±2

1.2

18±1

1.1

9-AAc/2-AA

1184±7

98.6

171±16

10.5

 

 

The effect of Ashes (residues) – Slag on E. coli WP2 uvrA (two experiments).

Note: Rt/Rc: ratio of the number of revertants at the tested dose to the number of revertants in the negative control.

 

 

Without metabolic activation (No. of revertants per plate)

With metabolic activation (No. of revertants per plate)

Doses (µg/plate)

Mean ± SD

Rt/Rc

Mean ± SD

Rt/Rc

Neg. control

32±4

-

42±2

-

Water (solvent control)

40±3

-

35±5

-

50

34±2

0.9

47±3

1.3

150

32±1

0.8

35±4

1.0

500

34±2

0.9

40±8

1.1

1500

46±15

1.2

37±5

1.0

5000

35±7

0.9

40±5

1.1

MNNG/2-AA

581±16

14.5

325±16

9.2

 

 

 

 

 

Neg. control

39±0

-

33±4

-

Water (solvent control)

44±3

-

41±5

-

15

38±5

0.9

48±4

1.2

50

39±4

0.9

44±4

1.1

150

42±1

0.9

37±3

0.9

500

43±8

1.0

36±2

0.9

1500

41±3

0.9

49±8

1.2

MNNG/2-AA

599±14

13.6

169±8

4.1

 

AS: sodium azide (1.5 µg/plate; TA 100 and TA 1535 without metabolic activation)

NPD: 4-nitro-o-phenylenediamine (20 µg/plate; TA 98 without metabolic activation)

2-AF: 2-aminofluorene (10 µg/plate; TA 100 and TA 98 with metabolic activation)

2-AA: 2-aminoanthracene (1 µg/plate with TA 1535; 2.5 µg/plate with TA 1537; 25 µg/plate with E. coli; all tests with metabolic activation)

9AAc: 9-aminoacridine hydrochloride monohydrate (100 µg/plate; TA 1537 without metabolic activation)

MNNG: N-methyl-N’nitro-N-nitrosoguanidine (20 µg/plate; E.coli without metabolic activation)

- : not evaluated

 

 

Conclusions:
Under the experimental conditions described, the test substance Ashes (residues) - Slag was nonmutagenic in S. typhimurium strains TA 98, TA 100, TA 1535 and TA 1537 as well as in E. coli strain WP2 uvrA both with and without metabolic activation.
Endpoint:
in vitro gene mutation study in mammalian cells
Type of information:
experimental study
Adequacy of study:
key study
Study period:
09 Nov - 22 Dec 2009
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: GLP-Guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 476 (In Vitro Mammalian Cell Gene Mutation Test)
GLP compliance:
yes (incl. QA statement)
Remarks:
Behörde für Soziales, Familie, Gesundheit und Verbraucherschutz, Freie und Hansestadt Hamburg, Germany
Type of assay:
in vitro mammalian cell gene mutation tests using the thymidine kinase gene
Target gene:
TK locus
Species / strain / cell type:
mouse lymphoma L5178Y cells
Details on mammalian cell type (if applicable):
- Type and identity of media: The cells used during experimental studies were maintained in RPMI 1640 medium supplemented with 0.05% Pluronic® F68, 2 mM L-glutamine, 220 µg/mL sodium pyruvate, 100 µg/mL gentamycin, 2.5 µg/mL fungizone and horse serum (10% by volume), hereinafter referred to as growth medium. Treatment medium was growth medium without sodium pyruvate, gentamycin and fungizone. Cleansing medium used for reducing the spontaneous frequency of TK-/- mutants prior to experimental studies consists of growth medium supplemented with approximately 4.0 x 10E-5 M thymidine, 1.2 x 10E-4 M hypoxanthine, 3.3 x 10E-5 M glycine and 7.2 x 10E-7 M methotrexate. Recovery medium is similar to cleansing medium, except that the methotrexate component is removed. Selection medium is growth medium that contains 3 µg/mL of 5-trifluoro-thymidine (TFT).
- Properly maintained: yes
- Periodically checked for Mycoplasma contamination: yes
- Periodically "cleansed" against high spontaneous background: yes
Metabolic activation:
with and without
Metabolic activation system:
Aroclor 1254-induced rat S9 fraction
Test concentrations with justification for top dose:
9.77, 19.5, 39.1, 78.13, 156.3, 312.5, 625, 1250, 2500 µg/mL
Vehicle / solvent:
- Vehicle(s)/solvent(s) used: water
Untreated negative controls:
other: The vehicle served as the negative control.
Negative solvent / vehicle controls:
yes
Remarks:
water
True negative controls:
no
Positive controls:
yes
Positive control substance:
other: Methylmethanesulfonate (MMS) at 10 and 15 µL/mL without metabolic activation; 3-Methylcholanthrene at 2.5 and 4.0 µg/mL with metabolic activation
Details on test system and experimental conditions:
METHOD OF APPLICATION: in medium


DURATION
- Exposure duration: 3 and 24 h without S9 mix; 3 h with S9 mix
- Expression time (cells in growth medium): 2-3 days
- Selection time (if incubation with a selection agent): 11-12 days


SELECTION AGENT (mutation assays): 5-trifluoro-thymidine (TFT) at 3 µg/mL


DETERMINATION OF CYTOTOXICITY
- Method: cloning efficiency
Evaluation criteria:
A dose-related or toxicity-related increase in mutant frequency should be observed.
If the mutant frequency obtained for a single dose at or near the highest testable toxicity is ca. 4 times the concurrent background mutant frequency or greater, the test item will be considered mutagenic in a single trial. Smaller increases will require confirmation by a repeat assay.
Sometimes correlation between toxicity and applied concentration is poor. The proportion of the applied test item effectively interacting with the cells to cause genetic alterations is not always repeatable or under control. Conversely, measurable changes in frequency of induced mutants may occur with concentration changes causing only small changes in observed toxicity. Therefore, either parameter, applied concentration or toxicity, can be used to establish whether the increase in mutant frequency is related to an increase in effective treatment.
Treatments inducing less than 10% relative growth are included in the assay, but are not used as primary evidence for mutagenicity as it relates to risk assessment.
The ratio of small to large colonies will be calculated from the results of the determination of small to large colonies.
If the test item is positive, the small to large colony ratio for the test item will be compared with the corresponding ratios of the positive and negative controls. Based on this comparison the type of the mutagenic properties of the test item will be discussed.
A test item is evaluated as non-mutagenic in a single assay only if the minimum increase in mutant frequency is not observed for a range of applied concentrations that extends to toxicity causing 10% to 20% relative growth or in the case of relatively non-toxic items, a range or applied concentrations extending to the maximum of 5 mg/mL (or 0.01 M, or 5 µL/mL) or in the case of non-toxic, insoluble materials, a range of applied concentrations extending to at least twice the solubility limit in culture media.
Species / strain:
mouse lymphoma L5178Y cells
Metabolic activation:
with and without
Genotoxicity:
negative
Cytotoxicity / choice of top concentrations:
no cytotoxicity
Remarks:
up to a concentration of 2500 µg/mL. The top concentration of 5000 µg/mL was a deep black coloured suspension and, thus, not analysable .
Vehicle controls validity:
valid
Untreated negative controls validity:
valid
Positive controls validity:
valid
Additional information on results:
RANGE-FINDING/SCREENING STUDIES: A preliminary cytotoxicity experiment was performed to establish an appropriate concentration range for the mutation experiment. This study was performed both with and without S9 metabolic activation.
Cytotoxicity is defined as a reduction in the number of colonies by more than 50% compared with the vehicle control.
A wide range of test item concentrations of 25, 100, 250, 1000, 2500 and 5000 µg Ash/mL was tested for cytotoxicity. After an exposure time of 3 hours at approx. 37 °C on a roller drum at 10 - 15 rpm, the cells were washed and resuspended in growth medium. The cells were then adjusted to 8 cells/mL and for each dose 0.2 mL was plated into 32 microtiter wells. The plates were incubated at 37 °C in a humidified incubator gassed with 5% CO2 in air for 3 days. Wells containing viable clones were identified under a microscope and counted.
The preliminary cytotoxicity information was then used to select dose levels for the mutation assay. Doses were selected using the following criteria: At least eight analysable concentrations were used. Where there would be cytotoxicity, these concentrations covered a range from the maximum to little or no toxicity; this means that the concentration levels were separated by no more than a factor between 2 and √10. If the maximum concentration is based on cytotoxicity then it should result in approximately 10 - 20% (but not less than 10%) relative survival (relative cloning efficiency) or relative total growth. For relatively non-cytotoxic compounds the maximum concentration is 5 mg/mL, 5 µL/mL, or 0.01 M, whichever is the lowest.


COMPARISON WITH HISTORICAL CONTROL DATA: The mean values of mutation frequencies of the negative controls ranged from 78.84 to 83.78 per 10E6 clonable cells in the experiments without metabolic activation, and from 79.93 to 105.51 per 10E6 clonable cells in the experiments with metabolic activation and, hence, were well within the historical data-range.

The mutation frequencies of the cultures treated with Ash ranged from 61.08 to 123.73 per 106 clonable cells (3 hours exposure) and 80.56 to 110.66 per 106 clonable cells (24 hours exposure) in the experiments without metabolic activation and 56.77 to 111.66 per 106 clonable cells (3 hours exposure, first assay) and 68.53 to 97.16 per 106 clonable cells (3 hours exposure, second assay) in the experiments with metabolic activation. These results were within the range of the negative control values and, hence, no mutagenicity was observed according to the criteria for assay evaluation.

In addition, no change was observed in the ratio of small to large mutant colonies, ranging from 0.71 to 2.00 for Ash treated cells and from 0.51 to 1.36 for the negative controls.

The positive controls Methylmethanesulfonate (10 and 15 µL/mL) and 3-Methyl­cholanthrene (2.5 and 4.0 µg/mL) caused pronounced increases in the mutation frequency ranging from 4061.79 to 7547.15 per 106 clonable cells in the case of MMS and ranging from 3663.53 to 7380.73 per 106 clonable cells in the case of 3-MC.

In addition, the colony size ratio was moderately shifted towards an increase in small colonies, ranging from 1.65 to 2.72 in the case of MMS.

According to the evaluation criteria for this assay, these findings indicate that a suspension of Ash, tested up to the highest analysable concentration of 2500 µg/mL in the absence and presence of metabolic activation did neither induce mutations nor had any chromosomal aberration potential.

Conclusions:
Under the conditions of this study, a suspension of Ash, tested up to the highest analysable concentration of 2500 µg/mL in the absence and presence of metabolic activation in two independent experiments, was negative with respect to the mutant frequency in the L5178Y TK +/- mammalian cell mutagenicity test. Under these conditions positive controls exerted potent mutagenic effects.
In addition, no change was noted in the ratio of small to large mutant colonies. Therefore, Ash also did not exhibit clastogenic potential at the concentration-range investigated.
According to the evaluation criteria for this assay, these findings indicate that a suspension of Ash, tested up to the highest analysable concentration of 2500 µg/mL in the absence and presence of metabolic activation did neither induce mutations nor had any chromosomal aberration potential.
Endpoint conclusion
Endpoint conclusion:
no adverse effect observed (negative)

Genetic toxicity in vivo

Description of key information

Negative results in a mammalian erythrocyte micronucleus test in rats.

Link to relevant study records
Reference
Endpoint:
in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
Type of information:
experimental study
Adequacy of study:
key study
Study period:
27 Nov 2007 - 30 Jan 2008
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: GLP-Guideline study
Qualifier:
according to guideline
Guideline:
OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
Deviations:
no
GLP compliance:
yes
Type of assay:
mammalian erythrocyte micronucleus test
Species:
rat
Strain:
Wistar
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Breeding farm BioTest s.r.o., Konárovice, 28125, Czech Republic, RČH CZ 21760152
- Age at study initiation: 6-7 weeks
- Weight at study initiation: females 169.60 - 177.62 g, males 200.81 - 212.09 g
- Assigned to test groups randomly: yes
- Diet (e.g. ad libitum): Complete pelleted diet for rats ad libitum (ST 1 Bergman, Mill Kocanda, Jesenice by Prague)
- Water (e.g. ad libitum): Drinking water ad libitum
- Acclimation period: 7 days


ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 3
- Humidity (%):30-70
- Photoperiod (hrs dark / hrs light): 12/12


IN-LIFE DATES: From: 27 Nov 2007 To: 07 Dec 2007
Route of administration:
oral: gavage
Vehicle:
- Vehicle(s)/solvent(s) used: 0.5% methylcelulose in water
- Concentration of test material in vehicle: adjusted to body weight
- Amount of vehicle (if gavage or dermal): 1 mL/100 g bw
Details on exposure:
PREPARATION OF DOSING SOLUTIONS: The test substance was suspended in 0.5% methylcelulose in water prior to administration via oral gavage, the concentration in vehicle was adjusted to body weight in order to achieve a constant administration volume of 1 mL/100 g bw.
Duration of treatment / exposure:
24 and 48 h
Frequency of treatment:
single administration
Post exposure period:
not applicable
Dose / conc.:
2 000 mg/kg bw/day (nominal)
No. of animals per sex per dose:
30
Control animals:
yes, concurrent no treatment
yes, concurrent vehicle
Positive control(s):
- Positive control: Cyclophosphamide monohydrate
- Route of administration: intraperitoneal injection (solution in water)
- Doses / concentrations: 20 mg/kg bw . The dose level of cyclophosphamide was chosen on the basis of literature data.
- Duration of exposure: 24 h
- No. of animals per sex per dose: 5
Tissues and cell types examined:
Bone marrow cells from the femora
Details of tissue and slide preparation:
CRITERIA FOR DOSE SELECTION:
The appropriate concentrations of the test item were determined from a pilot experiment.

DETAILS OF SLIDE PREPARATION:
Bone marrow harvest
Bone marrow cells were obtained from the femora immediately after animal sacrifice. After excising and careful cleaning of the bone, both femur ends were clipped off. The bone marrow was gently flushed from the bone with 1 mL of bovine serum into a tube. The acquired bone marrow was suspended and mixed in the bovine serum using a syringe with thin needle.

Preparation of bone marrow smears
After centrifugation (5 min, 1000 rpm), the supernatant was gently removed. One drop of bovine serum was added to the cell sediment which was then resuspended by mixing. One drop of the cell suspension was placed onto a slide and a smear was prepared using a pusher slide. Two bone marrow smears were prepared per animal.

Staining of the bone marrow smears
After drying (20 minutes, 60 °C) the smears were fixed with ethanol for 5 min, rinsed twice with distilled water and stained with 5% Giemsa solution for 15 min.

Examination of the bone marrow smears
Stained smears were examined with a light microscope. 200 erythrocytes were evaluated per animal as to the proportion of immature (polychromatic) and mature (normochromatic) erythrocytes („cytotoxicity index“) in bone marrow. At least 2000 polychromatic erythrocytes per animal were scored for the incidence of micronucleated immature erythrocytes.

Criteria for distinguishing the micronuclei
colour: purple
form: generally round or almond shaped, (occasional lightly stained and ring shaped micronuclei may occur)
borders: sharp
size: 5-20% of polychromatic erythrocyte size

Scoring of micronucleated immature erythrocytes
- number of immature erythrocytes with micronuclei
Evaluation criteria:
The criteria for determining a positive result are dose-related increase in the number of micronucleated cells or a clear increase in the number of micronucleated cells in a single dose group at a single sampling time.
Statistics:
The proportion of immature erythrocytes (cytotoxic index) and the number of micronucleated immature erythrocytes were determiend for each animal. The final count of micronucleated immature erythrocytes was adjusted to counts per 2000 erythrocytes per animal.
Mean values and standard deviations were calculated for each group of animals.
The statistical analysis was performed by the Analysis of Variance (ANOVA) test (software QC.Expert 2.5, Trilobyte, Statistical Software, Czech Rep.). Each of treatment groups was compared to the negative control group.
Sex:
male/female
Genotoxicity:
negative
Toxicity:
no effects
Vehicle controls validity:
valid
Negative controls validity:
valid
Positive controls validity:
valid
Additional information on results:
RESULTS OF RANGE-FINDING STUDY
Pilot experiment:
The experiment was performed because there were no suitable data, which could be used for the dose selection. The pilot test was performed using the same strain of animals and the same treatment regimen used in the main study.
The test substance was administered by gavage using a stomach tube. Clinical symptoms of toxicity were monitored after application. After euthanasia the indication of cytotoxicity in the bone marrow was evaluated by the ratio of immature erythrocytes to the total number of erythrocytes (“cytotoxicity index”). This ratio was determined from 200 erythrocytes.

Dose levels in pilot experiment and duration of exposition:
In the pilot experiment, 15 females (12 in the treatment groups and 3 animals in the control group) were used.

Negative control and three dose levels of the test substance were tested in the pilot experiment:
1. 2000 mg/kg bw for 24 h (3 animals)
2. 2000 mg/kg bw for 48 h ( 3 animals)
3. 1000 mg/kg of bw for 24 h (3 animals)
4. 500 mg/kg bw for 24 h (3 animals)
5. negative control group: 0.5% methylcelulose in water (3 animals)

Clinical observations:
No symptoms of toxicity were observed at any dose level.

Bone marrow harvest:
For the determination of the “cytotoxicity index”, bone marrow was harvested from all animals at 24 h after application and at the dose level 2000 mg/kg bw also at 48 h after application.

Evaluation of the pilot experiment and selection of doses:
A decrease in the “cytotoxicity index” was not observed at any dose level.
For the main study the dose level 2000 mg/kg bw was chosen (limit test).


RESULTS OF DEFINITIVE STUDY
Clinical observations:
No animal died during the main experiment and no signs of toxicity were observed in any animal in the treatment groups as well as in the negative and positive control groups.

Examination of the bone marrow smears:
The ratio of immature erythrocytes to total erythrocytes is shown in Table 1.

No statistically significant changes in the ratio of immature erythrocytes to the total number of erythrocytes were observed. A statistically significant decrease was seen in the positive control group compared to the negative control.

Count of micronucleated immature erythrocytes:

The mean numbers of micronucleated immature erythrocytes (IME) in males and females are summarised in the tables 2 and 3, respectively.
No statistically significant change in the number of micronucleated immature erythrocytes were observed. A statistically significant increase in the number of micronucleated immature erythrocytes was observed in the positive control group compared to the negative control.

Table 1.   Cytotoxicity index -group means and standard deviations

 

MALES

FEMALES

Group

Mean

Standard deviation

Mean

Standard deviation

Negative control 24 h

0.378

0.05

0.398

0.05

Negative control 48 h

0.380

0.05

0.375

0.05

2000 mg/kg

24h

0.377

0.02

0.369

0.04

2000 mg/kg

48h

0.386

0.05

0.399

0.06

Positive control

24h

 0.249*

0.02

0.225*

0.03

Without application

0.361

0.04

0.378

0.02

Table 2.   Micronucleated immature erythrocytes - group means and standard deviations

MALES

Number of micronucleated IME per animal (per 2000 IME)

Percentage expression

      Group

Mean

Standard deviation

Mean

Standard deviation

Negative control 24 h

2.77

0.83

0.139

0.04

Negative control 48 h

2.58

0.54

0.129

0.03

2000 mg/kg

24h

2.58

0.55

0.129

0.03

2000 mg/kg

48h

2.77

0.83

0.138

0.04

Positive control

24 h

15.73*

1.60

0.786

0.08

Without application

2.17

0.82

0.109

0.04

 

 

Table 3.   Micronucleated immature erythrocytes - group means and standard deviations

FEMALES

Number of micronucleated IME per animal (per 2000 IME)

Percentage expression

       Group

Mean

Standard deviation

    Mean

Standard deviation

Negative control 24 h

2.38

0.88

0.119

0.04

Negative control 48 h

2.19

0.80

0.108

0.04

2000 mg/kg

24h

2.16

0.80

0.108

0.04

2000 mg/kg

48h

2.78

1.08

0.139

0.05

Positive control

24 h

18.50*

2.07

0.925

0.10

Without application

2.55

0.52

0.128

0.03

IME – immature erythrocytes

Conclusions:
Under the experimental conditions described, the test substance Ashes (residues) induced no cytogenetic damage as assessed in the micronucleus test.
Endpoint conclusion
Endpoint conclusion:
no adverse effect observed (negative)

Additional information

Bacterial gene mutation assays have been conducted with Ashes (residues), Ashes (residues) – Fly Ash and Ashes (residues) – Slag each following a protocol compliant with OECD guideline 471 and under GLP conditions. The direct plate incorporation procedure was performed with Salmonella typhimurium TA 98, TA 100, TA 1535 and TA 1537 as well as with Escherichia coli WP2 uvrA at concentrations up to 5,000 µg/plate in the absence and in the presence of a metabolic activator (Aroclor 1254-induced rat liver S9). Cytotoxic effects were observed and reported only for S. typhimurium TA 100 at the concentration of 5,000 µg/plate Ashes (residues) – Fly Ash, without metabolic activation. None of the Ashes (residues) tested induced mutations in the bacterial mutation tests in either the absence or presence of metabolic activator in any strain tested. The positive and negative controls included in the experiments showed the expected results (ČEZ Energetické produkty, 2008, 2009a, b, key).

Ashes (residues) were assayed in a gene mutation assay in cultured mammalian cells according to OECD guideline 476 and complying with GLP. The test material was suspended in water due to insolubility in any of the other solvents recommended. The suspension, tested up to the highest analysable concentration of 2500 µg/mL in the absence and presence of metabolic activation (S9 mix from Aroclor 1254-induced rats) in two independent experiments, was negative with respect to the mutant frequency in the L5178Y TK +/- mammalian cell mutagenicity test. The positive controls included in the study exerted potent mutagenic effects. No signs of cytotoxicity (decreased survival) were noted in the experiments without and with metabolic activation, immediately after treatment (3 and 24 h without S9 mix; 3 h with S9 mix) and in the following plating for 5-trifluoro-thymidine (TFT) resistance, up to the top concentration of 2500 µg/mL. In addition, no change was noted in the ratio of small to large mutant colonies. Therefore, Ashes (residues) also did not exhibit clastogenic potential at the concentration-range investigated. According to the evaluation criteria for this assay, these findings indicate that Ashes (residues), tested up to the highest analysable concentration of 2500 µg/mL in the absence and presence of metabolic activation did neither induce mutations nor had any chromosomal aberration potential (Evonik Degussa GmbH, 2010, key).

The potential of Ashes (residues) to induce cytogenetic damage in vivo was investigated using Wistar rats in a GLP-study conducted according to OECD 474. The test substance was administered to the test animals by stomach tube in single dose. A dose level of 2000 mg/kg bw was chosen according to the results of a pilot experiment. Bone marrow samples were taken 24 and 48 h after administration. The group of animals without administration and concurrent negative and positive controls were included. Each experimental group consisted of five males and five females. The smears obtained from the bone marrow were examined by light microscope. The test substance, at the dose level of 2000 mg/kg bw, did not induce a significant increase in the number of immature erythrocytes with micronuclei compared with the negative control group. It was therefore concluded that, under the experimental conditions of the study, Ashes (residues) did not give rise to the formation of micronuclei in immature erythrocytes in bone marrow of rat (ČEZ Energetické produkty, 2008, key).

 

Justification for classification or non-classification

The available data on the genotoxic potential of ashes (residues) is conclusive but not sufficient for classification.