annex a hazard id and characterisation rev 4 clean...e ] l o ] v ( } } v ] v l ] v p Á Á Á Á x (...

18
Nickel in food and drinking water www.efsa.europa.eu/efsajournal 1 EFSA Journal 20YY;volume(issue):NNNN Annex to: 1 EFSA CONTAM Panel (EFSA Panel on Contaminants in the Food Chain), Dieter Schrenk, Margherita 2 Bignami, Laurent Bodin, James Kevin Chipman, Jesús del Mazo, Bettina Grasl-Kraupp, Christer 3 Hogstrand, Laurentius (Ron) Hoogenboom, Jean-Charles Leblanc, Carlo Stefano Nebbia, Evangelia 4 Ntzani, Annette Petersen, Salomon Sand, Tanja Schwerdtle, Christiane Vleminckx, Heather Wallace, 5 Thierry Guérin, Peter Massanyi, Henk Van Loveren, Katleen Baert, Petra Gergelova and Elsa Nielsen, 6 20YY. Scientific opinion on the update of the risk assessment of nickel in food and drinking water. EFSA 7 Journal 20YY;volume(issue):NNNN, NN pp. doi:10.2903/j.efsa.20YY.NNNN 8 © 20YY European Food Safety Authority. EFSA Journal published by John Wiley and Sons Ltd on behalf 9 of European Food Safety Authority. 10 11 Annex A – Benchmark dose analysis 12 A.1. Post-implantation loss 2GEN F1F2 study 13 A.1.1. Data description 14 The incidence of post-implantation losses as reported for the F1/F2 generation in the 2-generation 15 study (SLI, 2000b). 16 A.1.2. Selection of the benchmark response 17 A default benchmark response (BMR) of 10% (extra risk) and a 90% confidence interval around the 18 benchmark dose (BMD) were selected as recommended by the EFSA Scientific Committee (2017). 19 A.1.3. Software used 20 Results are obtained using the EFSA web tool for BMD analysis, which uses the R-package PROAST, 21 version 67.0, for the underlying calculations. 22 A.1.4. Specification of deviations from default assumptions 23 General assumptions 24 No deviation from the recommended defaults (e.g. gamma distributional assumption instead of log- 25 normal, heteroscedasticity instead of homoscedasticity) was made. 26 Dose–response models 27 No deviation from the recommended defaults. Default set of fitted models: 28 Model Number of parameters Formula Null 1 = Full no. of groups = group mean Logistic 2 = 1 1 + exp( ) Probit 2 = (( ) ) Log-logistic 3 = + 1 1 + exp log Log-probit 3 = + (1 ) log

Upload: others

Post on 15-Jul-2020

4 views

Category:

Documents


0 download

TRANSCRIPT

Page 1: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 1 EFSA Journal 20YY;volume(issue):NNNN

Annex to: 1

EFSA CONTAM Panel (EFSA Panel on Contaminants in the Food Chain), Dieter Schrenk, Margherita 2 Bignami, Laurent Bodin, James Kevin Chipman, Jesús del Mazo, Bettina Grasl-Kraupp, Christer 3 Hogstrand, Laurentius (Ron) Hoogenboom, Jean-Charles Leblanc, Carlo Stefano Nebbia, Evangelia 4 Ntzani, Annette Petersen, Salomon Sand, Tanja Schwerdtle, Christiane Vleminckx, Heather Wallace, 5 Thierry Guérin, Peter Massanyi, Henk Van Loveren, Katleen Baert, Petra Gergelova and Elsa Nielsen, 6 20YY. Scientific opinion on the update of the risk assessment of nickel in food and drinking water. EFSA 7 Journal 20YY;volume(issue):NNNN, NN pp. doi:10.2903/j.efsa.20YY.NNNN 8

© 20YY European Food Safety Authority. EFSA Journal published by John Wiley and Sons Ltd on behalf 9 of European Food Safety Authority. 10

11

Annex A – Benchmark dose analysis 12

A.1. Post-implantation loss 2GEN F1F2 study 13

A.1.1. Data description 14 The incidence of post-implantation losses as reported for the F1/F2 generation in the 2-generation 15 study (SLI, 2000b). 16

A.1.2. Selection of the benchmark response 17 A default benchmark response (BMR) of 10% (extra risk) and a 90% confidence interval around the 18 benchmark dose (BMD) were selected as recommended by the EFSA Scientific Committee (2017). 19

A.1.3. Software used 20 Results are obtained using the EFSA web tool for BMD analysis, which uses the R-package PROAST, 21 version 67.0, for the underlying calculations. 22

A.1.4. Specification of deviations from default assumptions 23

General assumptions 24

No deviation from the recommended defaults (e.g. gamma distributional assumption instead of log-25 normal, heteroscedasticity instead of homoscedasticity) was made. 26

Dose–response models 27

No deviation from the recommended defaults. Default set of fitted models: 28

Model Number of parameters Formula

Null 1 𝑦 = 𝑎

Full no. of groups 𝑦 = group mean

Logistic 2 𝑦 =

1

1 + exp(−𝑎 − 𝑏𝑥)

Probit 2 𝑦 = 𝑝𝑛𝑜𝑟𝑚((𝑥 − 𝑎) ⋅ 𝑏)

Log-logistic 3 𝑦 = 𝑎 +

1 − 𝑎

1 + exp 𝑐 ⋅ log𝑏𝑥

Log-probit 3 𝑦 = 𝑎 + (1 − 𝑎) ⋅ 𝑝𝑛𝑜𝑟𝑚 𝑐 ⋅ log

𝑥

𝑏

Page 2: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 2 EFSA Journal 20YY;volume(issue):NNNN

Weibull 3 𝑦 = 𝑎 + (1 − 𝑎) 1 − exp −

𝑥

𝑏

Gamma 3 𝑦 = 𝑝𝑔𝑎𝑚𝑚𝑎(𝑏𝑥; 𝑐)

Two-stage 3 𝑦 = 𝑎 + (1 − 𝑎) 1 − exp −

𝑥

𝑏− 𝑐

𝑥

𝑏

Exp model 3 3 𝑦 = 𝑎 ⋅ exp(𝑏𝑥 )

Exp model 5 4 𝑦 = 𝑎 ⋅ (𝑐 − (𝑐 − 1)exp(−𝑏𝑥 ))

Hill model 3 3 𝑦 = 𝑎 ⋅ 1 −

𝑥

𝑏 + 𝑥

Hill model 5 4 𝑦 = 𝑎 ⋅ 1 + (𝑐 − 1)

𝑥

𝑏 + 𝑥

For the Exp and Hill family, we fit models with 3 and 4 parameters as listed in the table. The 3-parameter 29 model is selected if the difference in AIC is smaller than 5, otherwise the 4-parameter model is selected. 30

Procedure for selection of the BMDL 31

There was no deviation from the procedure described in the flow chart to obtain the final BMD 32 confidence interval. 33

Page 3: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 3 EFSA Journal 20YY;volume(issue):NNNN

34

Figure A.1. Flowchart for selection of BMDL 35

A.1.5. Results 36

Table A.1: Results for the incidence of post-implantation loss in rats studied in the F1/F2 generation 37 of the two-generation study 38

model No.par loglik AIC accepted BMDL BMDU BMD conv

null 2 -503.87 1011.74 NA NA NA NA

full 6 -502.76 1017.52 NA NA NA NA

two.stage 4 -503.50 1015.00 no NA NA NA yes

log.logist 4 -502.87 1013.74 no NA NA NA yes

Weibull 4 -502.87 1013.74 no NA NA NA yes

log.prob 4 -502.87 1013.74 no NA NA NA yes

Page 4: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 4 EFSA Journal 20YY;volume(issue):NNNN

model No.par loglik AIC accepted BMDL BMDU BMD conv

gamma 4 -502.87 1013.74 no NA NA NA no

logistic 3 -503.53 1013.06 no NA NA NA yes

probit 3 -503.52 1013.04 no NA NA NA yes

LVM: Expon. m3- 4 -502.94 1013.88 no NA NA NA yes

LVM: Hill m3- 4 -502.93 1013.86 no NA NA NA yes

None of the fitted models is better than the null model: All fitted models’ AIC values are larger than 39 null model’s AIC – 2. 40

Estimated model parameters 41

two.stage 42

estimate for alfa- : 4.73 43 estimate for a- : 0.07186 44 estimate for BMD- : 11.72 45 estimate for c : 1e-06 46

log.logist 47

estimate for alfa- : 4.936 48 estimate for a- : 0.05952 49 estimate for BMD- : 58090 50 estimate for c : 0.1302 51

Weibull 52

estimate for alfa- : 4.936 53 estimate for a- : 0.05952 54 estimate for BMD- : 49710 55 estimate for c : 0.1284 56

log.prob 57

estimate for alfa- : 4.938 58 estimate for a- : 0.05953 59 estimate for BMD- : 164500 60 estimate for c : 0.05511 61

gamma 62

estimate for alfa- : 4.935 63 estimate for a- : 0.05952 64

estimate for BMD- : 41760 65 estimate for cc : 0.1268 66

logistic 67

estimate for alfa- : 4.716 68 estimate for a- : -2.548 69 estimate for BMD- : 9.027 70

probit 71

estimate for alfa- : 4.718 72 estimate for a- : -1.458 73 estimate for BMD- : 9.387 74

EXP 75

estimate for alfa- : 4.946 76 estimate for a- : 1.47 77 estimate for CED- : 110.7 78 estimate for d- : 0.25 79 estimate for th-1(fixed) : 0 80 estimate for sigma(fixed) : 0.25 81

HILL 82

estimate for alfa- : 4.947 83 estimate for a- : 1.471 84 estimate for CED- : 129.5 85 estimate for d- : 0.25 86 estimate for th-1(fixed) : 0 87 estimate for sigma(fixed) : 0.25 88

89

Page 5: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 5 EFSA Journal 20YY;volume(issue):NNNN

Visualisation 90

91

A.2. Post-implantation loss DRF and 2GEN F0F1 studies; BMR 5% 92

A.2.1. Data description 93 The incidence of post-implantation losses as reported for the DRF study (SLI, 2000a) and the F0/F1 94 generation in the 2-generation study (SLI, 2000b). The study was used as covariate. 95

A.2.2. Selection of the benchmark response 96 A BMR of 5% (extra risk) was used as recommended by U.S. EPA (2012) for reproductive and 97 developmental studies with nested study designs. A 90% confidence interval around the BMD was 98 selected as recommended by the EFSA Scientific Committee (2017). 99

A.2.3. Software used 100 Results are obtained using the EFSA web tool for BMD analysis, which uses the R-package PROAST, 101 version 67.0, for the underlying calculations. 102

Page 6: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 6 EFSA Journal 20YY;volume(issue):NNNN

A.2.4. Specification of deviations from default assumptions 103

General assumptions 104

No deviation from the recommended defaults (e.g. gamma distributional assumption instead of log-105 normal, heteroscedasticity instead of homoscedasticity) was made. 106

Dose–response models 107

No deviation from the recommended defaults (see Section A.1.4). 108

As a covariate is included in the analysis, these models will also be fitted assuming that some of the 109 parameters (background response parameter (a), potency parameter (BMD) and/or variance (var)) 110 depend on the subgroup defined by the covariate. Therefore the number of parameters in each model 111 might be larger than indicated in the table above. 112

Procedure for selection of the BMDL 113

There was no deviation from the procedure described in the flow chart (see Section A.1.4) to obtain 114 the final BMD confidence interval. 115

A.2.5. Results 116

Table A.2: Results for the incidence of post-implantation loss in rats studied in the F1/F2 generation 117 of the two-generation study using a BMR of 5% 118

model No.par loglik AIC accepted BMDL BMDU BMD sens.subgr conv

null 3 -830.99

1667.98 NA NA NA NA

full 12 -816.37

1656.74 NA NA NA NA

two.stage 4 -824.67

1657.34 no NA NA 2.820 – yes

log.logist 4 -823.33

1654.66 yes 0.0730 3.05 0.666 – yes

Weibull 4 -823.27

1654.54 yes 0.0725 3.08 0.663 – yes

log.prob 4 -823.55

1655.10 yes 0.0711 3.03 0.641 – yes

gamma 4 -823.21

1654.42 yes 0.0713 3.01 0.652 – yes

logistic-b 4 -824.20

1656.40 no NA NA 1.770 2GEN yes

LVM: Expon. m3-

4 -823.04

1654.08 yes 0.1730 3.15 0.653 2GEN yes

LVM: Hill m3- 4 -823.09

1654.18 yes 0.1460 3.12 0.657 2GEN yes

Confidence intervals for the BMD are based on generated data sets. 119

Estimated model parameters 120

two.stage 121

estimate for alfa- : 1.002 122 estimate for a-2GEN : 0.08402 123 estimate for a-DRF : 2.822 124 estimate for BMD-2GEN : 1e-06 125

estimate for BMD-DRF : 1.002 126 estimate for c : 0.08402 127

log.logist 128

estimate for alfa- : 1.024 129

Page 7: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 7 EFSA Journal 20YY;volume(issue):NNNN

estimate for a-2GEN : 0.05898 130 estimate for a-DRF : 0.6656 131 estimate for BMD-2GEN : 0.4933 132 estimate for BMD-DRF : 1.024 133 estimate for c : 0.05898 134

Weibull 135

estimate for alfa- : 1.025 136 estimate for a-2GEN : 0.05882 137 estimate for a-DRF : 0.6631 138 estimate for BMD-2GEN : 0.4714 139 estimate for BMD-DRF : 1.025 140 estimate for c : 0.05882 141

log.prob 142

estimate for alfa- : 1.02 143 estimate for a-2GEN : 0.05902 144 estimate for a-DRF : 0.641 145 estimate for BMD-2GEN : 0.2404 146 estimate for BMD-DRF : 1.02 147 estimate for c : 0.05902 148

gamma 149

estimate for alfa- : 1.026 150 estimate for a-2GEN : 0.05855 151 estimate for a-DRF : 0.652 152

estimate for BMD-2GEN : 0.4481 153 estimate for BMD-DRF : 1.026 154 estimate for cc : 0.05855 155

logistic 156

estimate for alfa- : 1.03 157 estimate for a-2GEN : -2.42 158 estimate for a-DRF : 1.771 159 estimate for BMD-2GEN : 4.806 160 estimate for BMD-DRF : 1.03 161

EXP 162

estimate for alfa- : 1.029 163 estimate for a- : 1.481 164 estimate for CED- : 0.6525 165 estimate for d- : 0.3373 166 estimate for th-1(fixed) : 0 167 estimate for sigma(fixed) : 0.25 168

HILL 169

estimate for alfa- : 1.028 170 estimate for a- : 1.48 171 estimate for CED- : 0.6571 172 estimate for d- : 0.3596 173 estimate for th-1(fixed) : 0 174 estimate for sigma(fixed) : 0.25 175

176

Weights for model averaging 177

two.stage log.logist Weibull log.prob gamma logistic EXP HILL

0.04 0.14 0.15 0.11 0.15 0.06 0.18 0.17

178

Final BMD values 179

subgroup BMDL BMDU

2GEN 0.12 4.18

DRF 0.06 5.17 Confidence intervals for the BMD are based on 200 bootstrap data sets. 180

181

Page 8: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 8 EFSA Journal 20YY;volume(issue):NNNN

Visualisation 182

183

184

A.3. Incidence of clinically cutaneous reactions to nickel following 185

oral exposure in nickel-sensitive persons as reported by Jensen 186

et al. (2003) 187

A.3.1. Data description 188 The incidence of clinically cutaneous reactions to nickel following oral exposure in nickel-sensitive 189 persons as reported by Jensen et al. (2003) as summarised in Table A.3 was used for the BMD analysis. 190

Page 9: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 9 EFSA Journal 20YY;volume(issue):NNNN

Table A.3: Incidence of clinically cutaneous reactions to nickel following oral exposure in nickel-191 sensitive persons as reported by Jensen et al. (2003) 192

Dose (mg Ni/person) N with clinically cutaneous reactions(a) N

0.0 1 10

0.3 4 10

1.0 4 10

4.0 7 10 N: number of nickel-sensitive persons. 193 (a): Flare-up reactions and widespread clinical reactions, including any large or small clinical eruption on previously unaffected 194

skin. 195 196

A.3.2. Selection of the benchmark response 197 A default BMR of 10% (extra risk) and a 90% confidence interval around the BMD were selected as 198 recommended by the EFSA Scientific Committee (2017). 199

A.3.3. Software used 200 Results are obtained using the EFSA web tool for BMD analysis, which uses the R-package PROAST, 201 version 67.0, for the underlying calculations. 202

A.3.4. Specification of deviations from default assumptions 203

General assumptions 204

No deviation from the recommended defaults (e.g. gamma distributional assumption instead of log-205 normal, heteroscedasticity instead of homoscedasticity) was made. 206

Dose–response models 207

No deviation from the recommended defaults (see Section A.1.4.). 208

Procedure for selection of the BMDL 209

There was no deviation from the procedure described in the flow chart (see Section A.1.4) to obtain 210 the final BMD confidence interval. 211

A.3.5. Results 212

Table A.4: Results of the model fitting for the incidence of clinically cutaneous reactions to nickel 213 following oral exposure in nickel-sensitive persons as reported by Jensen et al. (2003) using a BMR of 214 10% 215

model No.par loglik AIC accepted BMDL BMDU BMD conv

null 1 -26.92 55.84 NA NA NA NA

full 4 -22.82 53.64 NA NA NA NA

two.stage 3 -23.66 53.32 yes 0.19600 1.28 0.3840 yes

log.logist 3 -23.06 52.12 yes 0.00000 2.04 0.0358 yes

Weibull 3 -23.02 52.04 yes 0.00000 1.89 0.0249 yes

log.prob 3 -23.07 52.14 yes 0.00000 2.04 0.0431 yes

gamma 3 -23.00 52.00 yes 0.00000 1.70 0.0154 yes

logistic 2 -23.93 51.86 yes 0.44200 1.74 0.7210 yes

probit 2 -23.92 51.84 yes 0.45000 1.71 0.7030 yes

Page 10: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 10 EFSA Journal 20YY;volume(issue):NNNN

model No.par loglik AIC accepted BMDL BMDU BMD conv

LVM: Expon. m3- 3 -23.00 52.00 yes 0.00285 1.90 0.0151 yes

LVM: Hill m3- 3 -23.01 52.02 yes 0.00166 1.79 0.0187 yes

216

Estimated model parameters 217

two.stage 218 estimate for a- : 0.1996 219 estimate for BMD- : 0.3844 220 estimate for c : 1e-06 221

log.logist 222 estimate for a- : 0.1029 223 estimate for BMD- : 0.03577 224 estimate for c : 0.5728 225

Weibull 226 estimate for a- : 0.1028 227 estimate for BMD- : 0.02486 228 estimate for c : 0.4442 229

log.prob 230 estimate for a- : 0.1023 231 estimate for BMD- : 0.04308 232 estimate for c : 0.3521 233

gamma 234 estimate for a- : 0.1021 235 estimate for BMD- : 0.01538 236

estimate for cc : 0.3438 237

logistic 238 estimate for a- : -1.113 239 estimate for BMD- : 0.7205 240

probit 241 estimate for a- : -0.6901 242 estimate for BMD- : 0.7034 243

EXP 244 estimate for a- : 1.371 245 estimate for CED- : 0.01513 246 estimate for d- : 0.2637 247 estimate for th(fixed) : 0 248 estimate for sigma(fixed) : 0.25 249

HILL 250 estimate for a- : 1.371 251 estimate for CED- : 0.01872 252 estimate for d- : 0.3055 253 estimate for th(fixed) : 0 254 estimate for sigma(fixed) : 0.25 255

256

Weights for model averaging 257

two.stage log.logist Weibull log.prob gamma logistic probit EXP HILL

0.06 0.11 0.12 0.11 0.12 0.13 0.13 0.12 0.12

258

Final BMD values 259

subgroup BMDL BMDU

Jensen 2.66e-05 1.63 Confidence intervals for the BMD are based on 1000 bootstrap data sets. 260

Page 11: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 11 EFSA Journal 20YY;volume(issue):NNNN

Visualisation 261

262

Page 12: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 12 EFSA Journal 20YY;volume(issue):NNNN

263

A.4. Incidence of flare-up reactions to nickel following oral exposure 264

in nickel-sensitive persons as reported by Jensen et al. (2003) 265

A.4.1. Data description 266 The incidence of flare-up reactions to nickel following oral exposure in nickel-sensitive persons as 267 reported by Jensen et al. (2003) as summarised in Table A.5 was used for the BMD analysis. 268

Table A.5: Incidence of flare-up reactions to nickel following oral exposure in nickel-sensitive 269 persons as reported by Jensen et al. (2003) 270

Dose (mg Ni/person) N with flare-up of previous sites of dermatitis N

0.0 1 10

0.3 4 10

1.0 4 10

4.0 6 10 N: number of nickel-sensitive persons. 271

A.4.2. Selection of the benchmark response 272 A default BMR of 10% (extra risk) and a 90% confidence interval around the BMD were selected as 273 recommended by the EFSA Scientific Committee (2017). 274

A.4.3. Software used 275 Results are obtained using the EFSA web tool for BMD analysis, which uses the R-package PROAST, 276 version 67.0, for the underlying calculations. 277

Page 13: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 13 EFSA Journal 20YY;volume(issue):NNNN

A.4.4. Specification of deviations from default assumptions 278

General assumptions 279

No deviation from the recommended defaults (e.g. gamma distributional assumption instead of log-280 normal, heteroscedasticity instead of homoscedasticity) was made. 281

Model averaging 282

Model averaging was not used since the aim of this analysis was to evaluate the fitting of the models. 283

Dose–response models 284

No deviation from the recommended defaults (see Section A.1.4). 285

Procedure for selection of the BMDL 286

There was no deviation from the procedure described in the flow chart (see Section A.1.4) to obtain 287 the final BMD confidence interval. 288

A.4.5. Results 289

Table A.6: Results of the model fitting for the incidence of flare-up reactions to nickel following oral 290 exposure in nickel-sensitive persons as reported by Jensen et al. (2003) using a BMR of 10% 291

model No.par loglik AIC accepted BMDL BMDU BMD conv

null 1 -26.46 54.92 NA NA NA NA

full 4 -23.44 54.88 NA NA NA NA

two.stage 3 -24.45 54.90 no NA NA NA yes

log.logist 3 -23.55 53.10 no NA NA NA yes

Weibull 3 -23.54 53.08 no NA NA NA yes

log.prob 3 -23.55 53.10 no NA NA NA yes

gamma 3 -23.53 53.06 no NA NA NA yes

logistic 2 -24.65 53.30 no NA NA NA yes

probit 2 -24.64 53.28 no NA NA NA yes

LVM: Expon. m3- 3 -23.58 53.16 no NA NA NA yes

LVM: Hill m3- 3 -23.55 53.10 no NA NA NA yes

None of the fitted models is better than the null model: All fitted models’ AIC values are larger than 292 null model’s AIC – 2. 293

Estimated model parameters 294

two.stage 295 estimate for a- : 0.2221 296 estimate for BMD- : 0.5424 297 estimate for c : 1e-06 298

log.logist 299 estimate for a- : 0.1009 300 estimate for BMD- : 0.008858 301 estimate for c : 0.3769 302

Weibull 303 estimate for a- : 0.1009 304 estimate for BMD- : 0.005425 305 estimate for c : 0.2988 306

log.prob 307 estimate for a- : 0.1007 308 estimate for BMD- : 0.01209 309 estimate for c : 0.2321 310

gamma 311 estimate for a- : 0.1008 312 estimate for BMD- : 0.002801 313 estimate for cc : 0.2321 314

logistic 315 estimate for a- : -1.062 316 estimate for BMD- : 0.9157 317

Page 14: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 14 EFSA Journal 20YY;volume(issue):NNNN

probit 318 estimate for a- : -0.6593 319 estimate for BMD- : 0.8908 320

EXP 321 estimate for a- : 1.347 322 estimate for CED- : 0.0159 323 estimate for d- : 0.25 324 estimate for th(fixed) : 0 325

estimate for sigma(fixed) : 0.25 326

HILL 327 estimate for a- : 1.361 328 estimate for CED- : 0.01032 329 estimate for d- : 0.25 330 estimate for th(fixed) : 0 331 estimate for sigma(fixed) : 0.25 332

333

Visualisation 334

335

Page 15: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 15 EFSA Journal 20YY;volume(issue):NNNN

A.5. Incidence of clinically cutaneous reactions to nickel following 336

oral exposure in nickel-sensitive persons as reported by Jensen 337

et al. (2003) and Gawkrodger et al. (1986) 338

A.5.1. Data description 339 The incidence of clinically cutaneous reactions to nickel following oral exposure in nickel-sensitive 340 persons as reported by Gawkrodger et al. (1986) and Jensen et al. (2003) as summarised in Table A.7 341 was used for the BMD analysis. 342

Table A.7: Incidence of clinically cutaneous reactions to nickel following oral exposure in nickel-343 sensitive persons as reported by Gawkrodger et al. (1986) and Jensen et al. (2003) 344

Dose (mg Ni/person) N with clinically cutaneous reactions(a) N

0.0 1 10

0.3 4 10

0.4 5 10

1.0 4 10

2.5 5 10

4.0 7 10

5.6 6 6 N: number of nickel-sensitive persons. 345 Flare-up reactions and widespread clinical reactions, including any large or small clinical eruption on previously unaffected skin. 346

A.5.2. Selection of the benchmark response 347 A default BMR of 10% (extra risk) and a 90% confidence interval around the BMD were selected as 348 recommended by the EFSA Scientific Committee (2017). 349

A.5.3. Software used 350 Results are obtained using the EFSA web tool for BMD analysis, which uses the R-package PROAST, 351 version 67.0, for the underlying calculations. 352

A.5.4. Specification of deviations from default assumptions 353

General assumptions 354

No deviation from the recommended defaults (e.g. gamma distributional assumption instead of log-355 normal, heteroscedasticity instead of homoscedasticity) was made. 356

Dose–response models 357

No deviation of the recommended defaults (see Section A.1.4). 358

Procedure for selection of the BMDL 359

There was no deviation from the procedure described in the flow chart (see Section A.1.4) to obtain 360 the final BMD confidence interval. 361

Page 16: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 16 EFSA Journal 20YY;volume(issue):NNNN

A.5.5. Results 362

Table A.8: Results of the model fitting for the incidence of clinically cutaneous reactions to nickel 363 following oral exposure in nickel-sensitive persons as reported by Gawkrodger et al. (1986) and 364 Jensen et al. (2003) using a BMR of 10% 365

model No.par loglik AIC accepted BMDL BMDU BMD conv

null 1 -45.72 93.44 NA NA NA NA

full 7 -36.68 87.36 NA NA NA NA

two.stage 3 -39.48 84.96 no NA NA 0.7810 yes

log.logist 3 -39.41 84.82 yes 0.00e+00 4.100 0.0390 yes

Weibull 3 -39.20 84.40 yes 0.00e+00 4.430 0.0326 yes

log.prob 3 -39.40 84.80 yes 2.30e-06 4.070 0.0472 yes

gamma 3 -39.05 84.10 yes 0.00e+00 3.670 0.0201 yes

logistic 2 -39.52 83.04 yes 4.41e-01 1.010 0.6310 yes

probit 2 -39.43 82.86 yes 4.46e-01 0.985 0.6180 yes

LVM: Expon. m3- 3 -39.06 84.12 yes 2.97e-03 3.170 2.2600 yes

LVM: Hill m3- 3 -39.12 84.24 yes 1.78e-03 3.100 2.4000 yes

366

Estimated model parameters 367

two.stage 368 estimate for a- : 0.2939 369 estimate for BMD- : 0.7809 370 estimate for c : 4.328 371

log.logist 372 estimate for a- : 0.1084 373 estimate for BMD- : 0.03898 374 estimate for c : 0.6312 375

Weibull 376 estimate for a- : 0.1117 377 estimate for BMD- : 0.03265 378 estimate for c : 0.5026 379

log.prob 380 estimate for a- : 0.1066 381 estimate for BMD- : 0.04723 382 estimate for c : 0.3921 383

gamma 384 estimate for a- : 0.1086 385 estimate for BMD- : 0.02006 386

estimate for cc : 0.386 387

logistic 388 estimate for a- : -0.9493 389 estimate for BMD- : 0.6308 390

probit 391 estimate for a- : -0.5917 392 estimate for BMD- : 0.6182 393

EXP 394 estimate for a- : 1.097 395 estimate for CED- : 2.261 396 estimate for d- : 3.108 397 estimate for th(fixed) : 0 398 estimate for sigma(fixed) : 0.25 399

HILL 400 estimate for a- : 1.094 401 estimate for CED- : 2.402 402 estimate for d- : 3.689 403 estimate for th(fixed) : 0 404 estimate for sigma(fixed) : 0.25 405

406

Weights for model averaging 407

two.stage log.logist Weibull log.prob gamma logistic probit EXP HILL

0.07 0.07 0.09 0.08 0.11 0.18 0.2 0.11 0.1 408

Page 17: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 17 EFSA Journal 20YY;volume(issue):NNNN

Final BMD values 409

subgroup BMDL BMDU

0.0124 2.43

Confidence intervals for the BMD are based on 1000 bootstrap data sets. 410

Visualisation 411

412

Page 18: Annex A Hazard id and characterisation rev 4 clean...E ] l o ] v ( } } v ] v l ] v P Á Á Á Á X ( X µ } X µ l ( i } µ v o ï &^ : } µ v o î ìzz V À } o µ u ~ ] µ WEEEE

Nickel in food and drinking water

www.efsa.europa.eu/efsajournal 18 EFSA Journal 20YY;volume(issue):NNNN

413