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Diss Factsheets

Administrative data

Endpoint:
three-generation reproductive toxicity
Remarks:
based on test type (migrated information)
Type of information:
migrated information: read-across from supporting substance (structural analogue or surrogate)
Adequacy of study:
key study
Study period:
1960-1962 (in-life phase)
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: Study in accordance with generally accepted methods, but limited level of parameters examined and data reported

Data source

Reference
Reference Type:
publication
Title:
Unnamed
Year:
1976

Materials and methods

Test guideline
Qualifier:
equivalent or similar to guideline
Guideline:
OECD Guideline 416 (Two-Generation Reproduction Toxicity Study)
Deviations:
yes
Remarks:
lower number of animals used and parameters examined
GLP compliance:
no
Limit test:
no

Test material

Constituent 1
Reference substance name:
Nickel sulfate hexahydrate (NiS04.6H20)
IUPAC Name:
Nickel sulfate hexahydrate (NiS04.6H20)
Details on test material:
Nickel sulfate hexahydrate fines containing 22.3% nickel by analysis (theoretically 22.32%) served as the test material in this study.

Test animals

Species:
rat
Strain:
other: Wistar derived
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Albino Farms, Red Bank, New Jersey, USA
- Age at study initiation: (P) 4 wks
- Weight at study initiation: (P) 56-65 g
- Fasting period before study: No data
- Housing: individually caged
- Use of restrainers for preventing ingestion (if dermal): yes/no
- Diet: ad libitum, Radlston Purina, St. Louis, Missouri, USA
- Water: ad libitum
- Acclimation period: No data

ENVIRONMENTAL CONDITIONS
No details provided

IN-LIFE DATES: From: 1960 To: 1962

Administration / exposure

Route of administration:
oral: feed
Vehicle:
other: Radlston Purina feed
Details on exposure:
DIET PREPARATION
- Rate of preparation of diet (frequency): weekly
- Mixing appropriate amounts with (Type of food): Finely ground laboratory chow served as the basic diet. Stock aqueous solutions of nickel sulfate hexahydrate were prepared in appropriate concentrations so that the addition of 100 mL for each 6 kg of diet resulted in the desired nickel content, respectively. Additions of nickel solutions were thoroughly blended into the diet by mixing in a rotary-type blender.
- Storage temperature of food: No data
Details on mating procedure:
- M/F ratio per cage: 1/1
- Length of cohabitation: 7 days
- Proof of pregnancy: No data
- Further matings after two unsuccessful attempts: No
- After successful mating each pregnant female was caged: individually
- Any other deviations from standard protocol: On the 20th mating day all males were removed.
Analytical verification of doses or concentrations:
no
Duration of treatment / exposure:
11 weeks prior to mating, during mating, gestation, and lactation
Frequency of treatment:
Daily
Details on study schedule:
Litters containing more than 10 offsprings were randomly reduced to 10 on day 5. All surviving F/1a siblings were sacrificed and autopsied at weaning. Approximately 10 days after weaning of F/1a litters, F/0 parent generation rats were remated for F/1b litters. Procedure and observations recorded were the same as those described for F/1a litters.

For the F/2 generation 30 male and 30 female F/1b offsprings from each diet level were continued on their respective parents' diet for 11 weeks at which time 20 of each sex within each group were mated and the same procedure followed as with the F/0 generation through production and weaning of F/2a and F/2b litters.

For the F/3 generation, the same procedure as with the previous generations was followed through the production of F/3a and F/3b litters. All matings in each generation were made with rats from different litters.
Doses / concentrations
Remarks:
Doses / Concentrations:
0, 250, 500 and 1000 ppm
Basis:
nominal in diet
equivalent to 0, 22.5, 45 and 90 mg/kg bw nickel, respectively
No. of animals per sex per dose:
30
Control animals:
yes, plain diet
Details on study design:
No further details provided
Positive control:
Not included

Examinations

Parental animals: Observations and examinations:
Weekly body weight records were obtained, except during mating through weaning of litters.
Records were maintained of mating and number of pregnancies.
Oestrous cyclicity (parental animals):
Not included
Sperm parameters (parental animals):
Not included
Litter observations:
Records were maintained of litters cast (alive and dead), pups in litter at 1, 5, and 21 days (weaning), and total weight of the litter at weaning.
Postmortem examinations (parental animals):
Following weaning of F/1b litters, surviving F/0 rats were sacrificed and autopsied.
Postmortem examinations (offspring):
At weaning of F/2b rats, F/1b parents were sacrificed and autopsied.
Histopathologic examinations were performed on 10 male and 10 female F/3b weanlings from each diet level. Absolute and relative organ-to-body weight ratios for heart, spleen, kidneys, liver, and testes were analysed statistically. Tissues preserved in formalin for histopathologic study were in addition to the above: lung, urinary bladder, stomach, small and large intestine, skeletal muscle, brain, skin, bone marrow, pituitary, thyroid, adrenal, pancreas, and gonad.
Statistics:
No data
Reproductive indices:
Fertility (F.l.) = (pregnancies/matings) x 100
Gestation (G. I.) = (litters cast/pregnancies) x 100
Offspring viability indices:
Viability (V.I.) = (live pups at day 5/live pups born) x 100
Lactation (L.I.) = (weaned/live pups-discards on day 5) x 100

Results and discussion

Results: P0 (first parental generation)

General toxicity (P0)

Clinical signs:
not specified
Body weight and weight changes:
effects observed, treatment-related
Description (incidence and severity):
decreased bodyweight at 1000 ppm (90 mg/kg)
Food consumption and compound intake (if feeding study):
effects observed, treatment-related
Description (incidence and severity):
decreased bodyweight at 1000 ppm (90 mg/kg)
Organ weight findings including organ / body weight ratios:
not examined
Histopathological findings: non-neoplastic:
not examined
Other effects:
not examined

Reproductive function / performance (P0)

Reproductive function: oestrous cycle:
not examined
Reproductive function: sperm measures:
not examined
Reproductive performance:
no effects observed

Details on results (P0)

BODY WEIGHT AND FOOD CONSUMPTION (PARENTAL ANIMALS)
Body weights for parent generation rats on 250 and 500 ppm diets (22.5 and 45 mg/kg nickel, resp.), before mating and at weaning of respective litters, were not adversely affected, but rats on 1000 ppm (90 mg/kg nickel) exhibited slightly lower body weights. The average decrease in body weight did not exceed 8% for females and 13% for males.

OTHER FINDINGS (PARENTAL ANIMALS)
On fertility and gestation indices, no adverse effects were noted at any of the dietary levels of nickel.

Effect levels (P0)

Dose descriptor:
NOAEL
Remarks:
reproductive toxicity
Effect level:
1 000 ppm (nominal)
Based on:
test mat.
Sex:
male/female

Results: F1 generation

General toxicity (F1)

Clinical signs:
not specified
Mortality / viability:
mortality observed, treatment-related
Description (incidence and severity):
higher incidence of stillborn in the first generation
Body weight and weight changes:
effects observed, treatment-related
Description (incidence and severity):
decreased at 1000 ppm (90 mg/kg nickel)
Sexual maturation:
no effects observed
Organ weight findings including organ / body weight ratios:
not examined
Gross pathological findings:
no effects observed
Histopathological findings:
no effects observed

Details on results (F1)

VIABILITY (OFFSPRING)
Data on the number of pups born dead showed higher incidence of stillborn in the first generation at all levels of nickel, not observed to any extent in subsequent generations. The number of siblings (alive and dead) cast per litter averaged 10.3, 10.6, 9.8, and 9.0 for 0, 250, 500, and 1000 ppm (0, 22.5, 45, and 90 mg/kg nickel, resp.) diets, respectively. The number of siblings weaned per litter were progressively fewer with increasing dietary level of nickel, averaging 8.1, 7.2, 6.8, and 6.4 for 0, 250, 500, and 1000 ppm (0, 22.5, 45, and 90 mg/kg nickel, resp.) diets, respectively.

BODY WEIGHT (OFFSPRING)
On average weaning body weight, a clear-cut adverse effect is only apparent in weanlings of females on 1000 ppm (90 mg/kg nickel) diet, averaging 73% of control. However, offsprings maintained on 1000 ppm (90 mg/kg nickel) diet from weaning to mating of succeeding generations recovered considerably from this deficit, averaging 92% of controls.

OTHER FINDINGS (OFFSPRING)
On viability and lactation indices, no adverse effects were noted at any of the dietary levels of nickel.

Effect levels (F1)

Dose descriptor:
LOAEL
Generation:
F1
Effect level:
250 ppm (nominal)
Based on:
test mat.
Sex:
male/female
Basis for effect level:
other: Higher incidence of stillborn

Overall reproductive toxicity

Reproductive effects observed:
not specified

Any other information on results incl. tables

Summary table of reproduction data for rats fed with nickel sulfate hexahydrate through 3 generations:

Generation

Dose (ppm)

Number of rats

Total number of pups

Weanlings mean body weight (g)

Indices (%)*

Mated **

Pregnant ***

Whelped§

Born alive

Born dead

Alive on day 5§§

Discarded§§§

Weaned

F.I.

G.I.

V.I.

L.I.

F0 =>

F1a

0

20(1)

15(1)

14

113

5

113(10)

2

89

37.5

79

93

100

87

250

20(1)

11

11(1)

72

17

69

5

60

40.1

58

100

96

94

500

19

14

14(1)

96

13

95

5

72

34.4

74

100

99

80

1000

20

12

12(1)

93

16

91

5

83

27.8

60

100

98

97

F1b

0

17

14

14

143

3

139

0(8)

137

33.8

82

100

97

99

250

19

16

16

164

6

150

0(12)

134

31.6

84

100

91

89

500

19

14

14(3)

109

27

106

0(9)

98

28.1

74

100

97

93

1000

20(1)

15

15

93

31

77

0(3)

67

25.1

79

100

83

87

F1b =>

F2a

0

20

15

15

142

0

138

13

115

35.9

75

100

97

92

250

20

18

18(1)

188

2

181

30

119

31.1

90

100

96

79

500

20

17

17

171

0

141

10

129

34.6

85

100

82

98

1000

20

16(2)

14

127

6

120

8

96

25.9

80

88

94

86

F2b

0

20

14

14(1)

149

1

146

30

116

37.9

70

100

98

100

250

20

17

17(1)

181

16

177

39

130

35.7

85

100

98

94

500

20

16(1)

15

166

0

160

22

131

36.9

80

94

96

95

1000

18

11

11(1)

109

3

103

10

90

26.9

61

100

94

97

F2b =>

F3a

0

20

18(1)

17

180

5

175

20

125

36.7

90

94

97

81

250

20

19

19

207

4

201

21

121

34.5

95

100

97

67

500

20

19(1)

18(1)

184

5

172

20

102

35.6

95

95

93

67

1000

20

20(1)

19

168

7

162(10)

6

107

280.

100

95

96

73

F3b

0

18

18

18

216

0

206

38

158

41.9

100

100

95

94

250

20

18

18

204

2

198

32

161

41.4

90

100

97

97

500

18

16

16(1)

142

6

138

22

102

41.2

89

100

97

88

1000

17

17

17

139

7

138

13

114

29.7

100

100

99

91

* Indices: F.I., G.I., V.I., and L.I. refer to Fertility, Gestation, Viability, and Lactation Index, respectively.

** Numbers within parentheses refers to non-pregnant dams found dead during mating period, not included in calculation of F.I.

*** Within parentheses, dams found dead and autopsied to confirm pregnancies.

§ Numbers within parentheses refers to litters born dead

§§ Numbers within parentheses refers to number of siblings sacrificed after day 5 and before weaning due to death of dam, not used in calculation of L.I.

§§§ To reduce litter size to 10 on day 5; and within parentheses are totals in excess of 10/litter not discarded as planned, due to oversight, and carried to weaning.

Applicant's summary and conclusion

Conclusions:
Based on the only occurrence of slightly decreased body weight at 1000 ppm (90 mg/kg nickel) in the parental generation, the NOAEL for parental reproductive toxicity can be set at 90 mg nickel/kg/day.
Based on increased lethality in F1 pups, the low dose of 250 ppm (22.5 mg/kg nickel) can be considered as a LOAEL.
Executive summary:

In a 3-generation study, Wistar-derived rats were fed with 0, 250, 500, or 1000 ppm of nickel sulfate hexahydrate (equivalent to 0, 22.5, 45, or 90 mg/kg of nickel, respectively).

In the parental generation, body weights for rats on 250 and 500 ppm diets (22.5 and 45 mg/kg nickel, resp.), before mating and at weaning of respective litters, were not adversely affected, but rats on 1000 ppm (90 mg/kg nickel) exhibited slightly lower body weights. The average decrease in body weight did not exceed 8% for females and 13% for males. On fertility and gestation indices, no adverse effects were noted at any of the dietary levels of nickel.

A higher incidence of stillborn was observed only in the first generation at all dietary levels of nickel and decreased body weights of weanings on 1000 ppm diet in all generations. On viability and lactation indices, no adverse effects were noted at any of the dietary levels of nickel.