| Literature DB >> 34987622 |
Dominique Turck, Torsten Bohn, Jacqueline Castenmiller, Stefaan De Henauw, Karen Ildico Hirsch-Ernst, Alexandre Maciuk, Inge Mangelsdorf, Harry J McArdle, Androniki Naska, Carmen Pelaez, Kristina Pentieva, Alfonso Siani, Frank Thies, Sophia Tsabouri, Marco Vinceti, Francesco Cubadda, Thomas Frenzel, Marina Heinonen, Miguel Prieto Maradona, Rosangela Marchelli, Monika Neuhäuser-Berthold, Morten Poulsen, Josef Rudolf Schlatter, Henk van Loveren, Eirini Kouloura, Helle Katrine Knutsen.
Abstract
Following a request from the European Commission, the EFSA Panel on Nutrition, Novel Foods and Food Allergens (NDA) was asked to deliver an opinion on Wolffia globosa powder as a novel food (NF) pursuant to Regulation (EU) 2015/2283. Wolffia globosa is an aquatic plant, one out of the 38 species of the water lentil family which is composed by five genera (i.e. Spirodela, Landoltia, Lemna, Wolffiella and Wolffia). The NF is produced by cultivation of Wolffia globosa plants under controlled conditions, washing with hot water and drying. The main constituents of the NF are protein, fibre and fat. The Panel notes that the concentration of trace elements and contaminants in the NF is highly dependent on the conditions of cultivation of the plant and the fertiliser composition. The NF is intended to be used as food ingredient in a variety of food categories and as food supplement. The target population is the general population except for food supplements which are intended to be consumed exclusively by adults. The Panel considers that with the exception of concerns related to the manganese intake, taking into account the composition of the NF and the proposed conditions of use, the consumption of the NF is not nutritionally disadvantageous. The subchronic toxicity study provided with the NF revealed a number of significant findings and the Panel considers the middle dose (6.5 g/kg body weight (bw) per day) as the no observed adverse effect level (NOAEL). Based on the protein concentration, the Panel considers that the consumption of the NF may trigger allergic reactions. The Panel concluded that an increase in manganese intake from the NF used as food ingredient or food supplements is of safety concern and the safety of the NF cannot be established.Entities:
Keywords: Novel food; Wolffia globosa; duckweed; food supplement; isolated from plants; water lentil
Year: 2021 PMID: 34987622 PMCID: PMC8693246 DOI: 10.2903/j.efsa.2021.6938
Source DB: PubMed Journal: EFSA J ISSN: 1831-4732
Batch to batch analysis of the NF
| Parameters | Unit | Batch | Method of analysis | ||||||
|---|---|---|---|---|---|---|---|---|---|
| #1 | #2 | #3 | #4 | #5 | #6 | #7 | |||
|
| % | NA | 2.6 | 4.2 | 4.4 | NA | 3.2 | 3.4 | AOAC 925.09 |
|
| % | NA | 45.62 | 43.17 | 44.92 | 45.13 | 45.44 | 43.31 | AOAC 990.03; AOAC 992.15 |
|
| % | 9.47 | 10.60 | NA | NA | NA | NA | 11.86 | AOAC 2001.11 (by acid hydrolysis) |
|
| % | 31.40 | 32.30 | 35.30 | 34.20 | 27.80 | 28.70 | 27.70 | AOAC 991.43 |
|
| % | NA | 11.1 | 19.8 | 25.0 | 28.2 | 12.1 | NA | Gravimetry (In‐house) |
|
| % | NA | 12.4 | 19.7 | 24.5 | 25.8 | 17.6 | NA | Gravimetry (In‐house) |
|
| % | 6.29 | 7.42 | 8.15 | 8.34 | 2.82 | 4.11 | 4.07 | AOAC 942.05 |
|
| % | NA | 36.02 | 37.29 | 35.33 | 39.91 | 38.01 | 40.03 | CFR 21‐calc. |
|
| % | NA | 1.3 | < 1.0 | < 1.0 | < 1.0 | 5.5 | NA | Gravimetry (In‐house) |
|
| % | NA | < 0.5 | 0.6 | 0.9 | 1.5 | 1.9 | NA | Gravimetry (In‐house) |
|
| % | NA | 0.11 | 0.19 | 0.24 | 0.27 | 0.10 | NA | Gravimetry (In‐house) |
|
| % | NA | NA | 3.2 | 3.6 | 4.2 | 3.5 | NA | AOAC 996.11 |
AOAC: Association of Official Analytical Collaboration; CFR: Code of Federal Regulations; NA: not available.
Concentration of micronutrients, trace elements and heavy metals in seven batches of the NF
| Parameters | Unit | Batch | Method of analysis | ||||||
|---|---|---|---|---|---|---|---|---|---|
| #1 | #2 | #3 | #4 | #5 | #6 | #7 | |||
|
| mg/kg | 3.3 | 12 | 4.6 | 4.2 | < 10 | < 10 | 16 | AOAC 993.14 Mod.; AOAC 965.17/985.01 mod.; DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | 4.9 | 6.8 | 7.4 | 5.4 | 8.2 | 26.7 | 5.3 | AOAC 993.14 Mod.;J.AOAC 92, 1484‐1518 (2009); DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | 59.7 | 53.9 | 36.0 | 31.0 | 40.2 | 45.4 | 39.8 | AOAC 993.14 Mod.;J.AOAC 92, 1484‐1518 (2009); DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | 5,640 | 5,130 | 4,400 | 4,500 | 6,880 | 10,400 | 5,750 | AOAC 965.17/985.01 mod.; AOAC 993.14; AOAC 984.27, 927.02, 985.01, 965.17 mod; DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | 0.6 | 4.0 | 3.5 | 2.3 | < 1.2 | 1.4 | 13 | AOAC 993.14 Mod.;DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | 0.15 | < 0.75 | < 0.2 | < 0.2 | < 0.75 | < 0.75 | < 0.75 | AOAC 993.14 Mod.;AOAC 965.17/968.08 modified; DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | 20.3 | 17 | 14.0 | 18.0 | NA | NA | 20 | AOAC 993.14 Mod.; AOAC 965.17/968.08 modified; DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | 387 | 723 | 600 | 450 | 534 | 1,590 | 726 | AOAC 965.17/985.01 mod.; AOAC 984.27, 927.02; DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | NA | NA | NA | NA | 0.5 | 0.5 | < 0.2 | J.AOAC 92, 1484‐1518 (2009) |
|
| mg/kg | 1,910 | 1,950 | 1,800 | 1,800 | 1,680 | 2,070 | 1,530 | AOAC 993.14 Mod.;DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | 226 | 292 | 210 | 200 | 206 | 197 | 219 | AOAC 993.14 Mod.; AOAC 965.17/985.01 mod.; DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | 3.3 | 3.6 | 3.5 | 5.1 | < 1.2 | < 1.2 | < 1.2 | AOAC 993.14 Mod.; AOAC 965.17/968.08 modified; DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | 0.273 | 1.3 | 1.4 | 1.0 | 0.23 | 0.22 | 5.64 | AOAC 993.14 Mod.; AOAC 965.17/968.08 modified; DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | 22,700 | 22,900 | 29,000 | 31,000 | 1,340 | 1,290 | 8,720 | AOAC 993.14 Mod.; AOAC 965.17/985.01 mod.;AOAC 984.27, 927.02;DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | 8,440 | 8,300 | 9,800 | 9,800 | 4,730 | 6,750 | 6,240 | AOAC 993.14 Mod.; AOAC 965.17/985.01 mod.; DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | < 0.23 | < 0.1 | < 0.2 | < 0.2 | < 0.1 | < 0.1 | < 0.1 | AOAC 993.14 Mod.; DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐MS |
|
| mg/kg | 22 | 24 | NA | NA | < 20 | 56 | 110 | AOAC 986.15 mod.; DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | 10 | 11 | 22.0 | 33.0 | < 10 | 26 | 50 | |
|
| mg/kg | 309 | 420 | 530 | 650 | 250 | 390 | 330 | AOAC 965.17/985.01 mod.; DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | 49.3 | 54.1 | 50.0 | 50.0 | 46.2 | 122.2 | 44.7 | AOAC 993.14; AOAC 2013.06; DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| mg/kg | 0.22 | < 25 | NA | NA | NA | NA | NA | AOAC 993.14; AOAC 965.17/968.08 modified |
|
| mg/kg | 0.83 | 2.6 | 0.9 | 0.6 | 0.5 | < 0.4 | 1.4 | AOAC 993.14 Mod. |
|
| mg/kg | 0.213 | < 0.20 | < 0.2 | < 0.2 | < 0.20 | < 0.20 | < 0.20 | AOAC 993.14 Mod.; DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐MS |
|
| mg/kg | 363 | 264 | 110 | 190 | 90 | 76 | 217 | AOAC 993.14 Mod.; AOAC 965.17/985.01 mod.; DIN EN ISO 11885, mod., CON‐PV 00006, ICP‐OES |
|
| |||||||||
|
| mg/kg | 0.031 | 0.064 | < 0.1 | 0.3 | 0.014 | 0.030 | 0.018 |
J. AOAC vol. 90 (2007) 844‐ 856 (Mod); AOAC 993.14 Mod. EN 15763:2009, CON‐PV 01274, ICP‐MS |
|
| mg/kg | 0.06 | 0.04 | 0.02 | 0.04 | < 0.01 | < 0.01 | < 0.01 |
J. AOAC vol. 90 (2007) 844‐ 856 (Mod); AOAC 993.14 Mod. EN 15763:2009, CON‐PV 01274, ICP‐MS |
|
| mg/kg | 0.23 | 0.50 | 0.33 | 0.92 | 0.07 | 0.09 | 0.05 |
J. AOAC vol. 90 (2007) 844‐ 856 (Mod); AOAC 993.14 Mod. EN 15763:2009, CON‐PV 01274, ICP‐MS |
|
| mg/kg | < 0.012 | < 0.011 | < 0.005 | < 0.005 | < 0.010 | 0.014 | < 0.010 |
J. AOAC vol. 90 (2007) 844‐ 856 (Mod); AOAC 993.14 Mod. EN 15763:2009, CON‐PV 01274, ICP‐MS |
AOAC: Association of Official Analytical Collaboration; CON‐PV: methods of Eurofins WEJ Contaminants GmbH; DIN: Deutsches Institut für Normung e.V.; EN: Europäische Norm (European Standards); ISO: International Organization for Standardization; ICP‐OES: Inductively Coupled Plasma Optical Emission Spectroscopy; ICP‐MS: Inductively Coupled Plasma Mass Spectrometry; NA: not available.
Additional analytical data were provided for two batches #8 and #9 (i.e. 0.019 and 0.040 mg/kg).
Additional analytical data were provided for two batches #8 and #9 (i.e. 0.014 and 0.005 mg/kg).
Additional analytical data were provided for two batches #8 and #9 (i.e. 0.112 and 0.222 mg/kg).
Additional analytical data were provided for two batches #8 and #9 (i.e. < 0.005 and < 0.005 mg/kg).
Trace element concentration in six additional batches of the NF
| Parameter | Unit | Batch number | |||||
|---|---|---|---|---|---|---|---|
| #10 | #11 | #12 | #13 | #14 | #15 | ||
| Aluminium | mg/kg | < 3 | 3.6 | 4.0 | < 3 | 3.6 | < 3 |
| Boron | mg/kg | 22.5 | 41.8 | 56.8 | 29.8 | 31.3 | 21.3 |
| Copper | mg/kg | 8.5 | 6.0 | 6.3 | 8.0 | 8.5 | 6.3 |
| Iron | mg/kg | 570.5 | 900.5 | 844.8 | 348.3 | 369.0 | 299.7 |
| Manganese | mg/kg | 116.4 | 59.6 | 116.3 | 105.8 | 101.6 | 69.5 |
| Molybdenum | mg/kg | < 1 | < 1 | < 1 | < 1 | < 1 | < 1 |
| Zinc | mg/kg | 136.7 | 158.9 | 91.6 | 170.0 | 165.9 | 112.3 |
Parameters were analysed by Inductively Coupled Plasma Optical Emission Spectroscopy (ICP‐OES).
(Pro‐)Vitamin content of seven batches of the NF
| Parameter | Unit | Batch number | Method of analysis | |||||||
|---|---|---|---|---|---|---|---|---|---|---|
| #1 | #2 | #3 | #4 | #5 | #6 | #16 | #7 | |||
|
| µg/100 g | 46,200 | 20,100 | 31,860 | 28,980 | 36,000 | 73,200 | 61,200 | 49,800 | AOAC 974.29 Mod. Official Methods of Analysis, Methods 992.04, 992.06, and 2001.13, AOAC International (Mod). |
|
| RAE/100 g | 3,850 | 1,712 | 2,655 | 2,553 | 3,000 | 6,100 | 5,100 | 4,150 | |
|
| mg/100 g | 0.0487 | 0.0564 | 0.0518 | 0.0418 | 0.0419 | 0.0428 | NA | 0.0658 | |
|
| mg/100 g | 1 | 0.9 | 1.5 | 1.5 | 0.4 | 0.4 | NA | 0.4 | Met. of Vitamin Assay, Interscience Publ., Ch.12 |
|
| mg/100 g | 6.3 | 5.5 | 7.8 | 7.7 | 0.3 | 0.4 | NA | 1.6 | AOAC 992.05 Mod. |
|
| mg/100 g | 0.9 | 0.6 | 0.9 | 0.7 | 0.0 | 0.1 | NA | 0.1 | AOAC 944.13 Mod. |
|
| µg/100 g | 4.4 | 2.2 | 2.8 | 2.6 | 0.7 | < 0.4 | NA | < 0.4 | AOAC 942.23 mod. |
|
| mg/100 g | 3.4 | 3.4 | 3.5 | 3.3 | 0.4 | < 0.2 | NA | < 0.4 | AOAC 952.20/45.2.02 |
|
| mg/100 g | 0.851 | 0.281 | 0.360 | 0.300 | < 0.055 | < 0.055 | NA | < 0.152 | AOAC 970.65 mod. |
|
| mg/100 g | 6.8 | 12.6 | 18.2 | 38.0 | 85.2 | 151.0 | NA | 272.0 | AOAC 945.74 (mod.) |
|
| mg/100 g | 31.37 | 16.15 | 22.2 | 16.8 | 23.1 | 34.4 | NA | 46.2 | AOAC 971.30 with HPLC quantification mod. |
|
| mg/100 g | NA | NA | NA | NA | 0.359 | 0.400 | NA | 0.661 | |
|
| mg/100 g | NA | NA | NA | NA | 0.141 | 0.143 | NA | 0.394 | |
|
| mg/100 g | NA | NA | NA | NA | < 0.100 | < 0.100 | NA | < 0.100 | |
|
| mg/100 g | NA | < 0.1 | < 0.1 | < 0.1 | < 0.2 | < 0.2 | 0.0143 | NA | USP 31 NF26 or EN14148 mod. |
|
| mg/100 g | NA | < 0.1 | < 0.1 | < 0.1 | < 0.2 | < 0.2 | 0.0146 | NA | USP 31 NF26 or EN14148 mod. |
|
| mg/100 g | NA | 6.70 | 2.56 | 8.37 | 8.71 | 11.10 | 9.58 | 5.88 |
EN 14148:2003 Official Methods of Analysis, Methods 992.27, 999.15, AOAC International (Mod). |
|
| mg/100 g | 1.25 | 1.25 | 1.27 | 1.10 | 0.27 | 0.35 | NA | 0.19 | JAOAC 88, 30‐37 |
|
| IU/100 g | NA | NA | NA | NA | < 4.00 | < 4.00 | NA | NA | EN 12821:2009 USP (modified) |
|
| IU/100 g | NA | NA | NA | NA | < 4.00 | < 4.00 | NA | NA | EN 12821:2009 USP (modified) |
AOAC: Association of Official Analytical Collaboration; EN: Europäische Norm (European Standards); USP: United States Pharmacopeia; HPLC: high‐performance liquid chromatography; NA: not available.
Microbiological parameters in five batches of the NF
| Parameter | Unit | Batch number | Method of analysis | ||||
|---|---|---|---|---|---|---|---|
| #2 | #18 | #3 | #19 | #4 | |||
|
| CFU/g | < 10 | 75 | 90 | 40 | 55 | SI 885/3 |
|
| CFU/g | < 50 | < 50 | < 50 | < 50 | < 50 | AOAC 980.31; BAM Chapter 14 |
|
| CFU/g | NA | NA | < 50 | < 50 | < 50 | BAM Chapter 12; SI 885/6 |
|
| CFU/g | < 10 | < 10 | < 10 | < 10 | < 10 | BAM Chapter 4; SI 885/4 |
|
| CFU/g | < 10 | < 10 | < 10 | < 10 | < 10 | BAM Chapter 4; ISO 16649‐2 |
|
| per 30 g | NA | ND | ND | ND | ND | ISO 16654 |
|
| CFU/g | 25 | < 10 | < 10 | < 10 | < 10 | BAM Chapter 18 |
|
| CFU/g | < 10 | < 10 | < 10 | < 10 | < 10 | SI 885/8 |
|
| per 25 g | ND | ND | ND | ND | ND | AOAC OMA 2004.02 |
|
| CFU/g | < 10 | < 10 | < 10 | < 10 | < 10 | SI 885/5 |
|
| per 25 g | ND | ND | ND | ND | ND | AOAC 2003.09 |
AOAC: Association of Official Analytical Collaboration; BAM: Bacteriological Analytical Manual; ISO: International Organisation for Standardization; OMA: Official method of analysis; SI: Israel Standards; ND: not detected; CFU: colony forming units; NA: not available.
Specifications of the NF
|
| |
|
| |
|
| Specification |
| Moisture | < 5% |
| Protein (N × 6.25) | 40–50% |
| Ash | 2.5–8.5% |
| Fat | 7–10% |
| Total fibre | 27–35% |
| Beta‐carotene | 200–750 mg/kg |
| Phylloquinone | 20–120 mg/kg |
| Folic acid | 3–15 mg/kg |
| Copper | < 8.6 mg/kg |
| Zinc | < 200 mg/kg |
| Iron | < 1,000 mg/kg |
| Manganese | < 116.5 mg/kg |
| Molybdenum | < 6 mg/kg |
| Boron | < 60 mg/kg |
| Oxalic acid | < 6,500 mg/kg |
|
| |
| Nitrate | < 3,100 mg/kg |
| Arsenic | < 1 mg/kg |
| Lead | < 1.5 mg/kg |
| Cadmium | < 0.6 mg/kg |
| Mercury | < 0.1 mg/kg |
| Total aflatoxins | < 10 μg/kg |
| Microcystins | < 25 μg/kg |
| Nodularins | < 25 μg/kg |
|
| |
| Total plate count | < 103 CFU/g |
|
| ND in 1 g |
| Coliforms | < 102 CFU/g |
| Moulds | < 102 CFU/g |
| Yeasts | < 102 CFU/g |
|
| ND in 25 g |
|
| ND in 1 g |
|
| ND in 25 g |
CFU: colony forming units; ND: not detected.
Food categories and maximum use levels intended by the applicant
| FAIM food category | Food category | Max use level (mg NF/kg) |
|---|---|---|
| 01.2 | Unflavoured milk products | 10,000 |
| 03 | Edible ices | 10,000 |
| 04.2 | Processed vegetables | 15,000 |
| 06.4 | Pasta | 20,000 |
| 06.5 | Noodles | 20,000 |
| 07.1 | Bread and rolls | 10,000 |
| 14.1.2.2 | Vegetable juices | 20,000 |
| 14.1.3 | Fruit nectars as defined by Directive 2001/112/EC and vegetable nectars and similar products | 10,000 |
| 16 | Desserts excluding products covered in category 1, 3 and 4 | 10,000 |
FAIM: Food Additives Intake Model.
Intake estimate resulting from the use of the NF as an ingredient in the intended food categories at the maximum proposed use levels calculated by the FAIM tool
| Population group | Age (years) | Mean intake (mg/kg bw per day) | P95th intake (mg/kg bw per day) | ||
|---|---|---|---|---|---|
| Lowest | Highest | Lowest | Highest | ||
| Infants | < 1 | 43.7 | 211 | 170 | 730 |
| Young children | 1 to < 3 | 123 | 261 | 241 | 555 |
| Other children | 3 to < 10 | 79.4 | 191 | 155 | 375 |
| Adolescents | 10 to < 18 | 40.5 | 95.7 | 81.1 | 198 |
| Adults | ≥ 18 | 43.2 | 71.3 | 75.7 | 139 |
bw: body weight; FAIM: Food Additives Intake Model; NF: novel food.
FAIM tool exposure estimate was generated on 01/06/2021. The lowest and the highest averages observed among all EU surveys are reported in these columns.
FAIM tool exposure estimate was generated on 01/06/2021. The lowest and the highest P95th observed among all EU surveys are reported in these columns (P95th based on < 60 individuals are not considered).
Referred as ‘toddlers’ in the EFSA food consumption comprehensive database (EFSA, 2011).
Includes elderly, very elderly, pregnant and lactating women.
Indispensable amino acid scoring
| Parameter (g/100 g protein) | #20 | Oat | Pea | Egg | Scoring pattern (indispensable amino acid reference profiles) for adults (WHO, |
|---|---|---|---|---|---|
|
| 2.0 | 1.4 | 2.0 | 1.8 | 1.5 |
|
| 3.8 | 2.0 | 2.9 | 3.1 | 3.0 |
|
| 7.2 | 5.9 | 7.1 | 7.1 | 5.9 |
|
| 6.0 | 2.0 | 5.9 | 5.3 | 4.5 |
|
| 8.1 | 6.6 | 7.9 | 8.0 | 3.8 |
|
| 4.0 | 2.3 | 3.1 | 3.9 | 2.3 |
|
| 4.9 | 3.1 | 3.4 | 3.9 | 3.9 |
|
| 2.8 | 0.8 | 0.6 | 3.5 | 2.2 |
|
| 2.1 | 0.6 |
Intake estimates of manganese resulting from the use of the NF as an ingredient in the intended food categories or as food supplement at the maximum proposed use levels
| Population group | Age (years) | Mean Mn intake (mg per day) | P95th Mn intake (mg per day) | ||
|---|---|---|---|---|---|
| Lowest | Highest | Lowest | Highest | ||
|
| < 1 | 0.0255 | 0.1231 | 0.0993 | 0.4254 |
|
| 1 to < 3 | 0.1724 | 0.3661 | 0.3378 | 0.7765 |
|
| 3 to < 10 | 0.2136 | 0.5140 | 0.4175 | 1.0093 |
|
| 10 to < 18 | 0.2049 | 0.4838 | 0.4100 | 1.0028 |
|
| ≥ 18 | 0.3527 | 0.5818 | 0.6177 | 1.1357 |
|
| 2.33 | ||||
Mn: manganese; NF: novel food.
FAIM tool exposure estimate was generated on 01/06/2021. The lowest and the highest averages observed among all EU surveys are reported in these columns.
FAIM tool exposure estimate was generated on 01/06/2021. The lowest and the highest P95th observed among all EU surveys are reported in these columns (P95th based on < 60 individuals are not considered).
Referred as ‘toddlers’ in the EFSA food consumption comprehensive database (EFSA, 2011).
Includes elderly, very elderly, pregnant and lactating women.
List of toxicological studies with the NF
| Reference | Type of study | Test system | Dose |
|---|---|---|---|
| Study No. T‐2791 (Kawamata et al., | Bacterial reverse mutation test (GLP, OECD TG 471) |
| Up to 5,000 µg/plate (absence and presence of S9 mix) |
| Study No. T‐G383 (Kawamata et al., |
| Human lymphoblastoid TK6 cells | Up to 500 μg/mL [short term (absence and presence of S9 mix) and continuous treatment] |
| Study No. HNM‐003‐TOX (Pharmaseed, |
Repeated dose 4‐day oral toxicity study (non‐GLP, inspired by OECD TG 423) | Female Sprague‐Dawley rats | Up to 3,400 mg/kg bw per day |
| Study No. NNI001‐TX01 (APS, | Repeated dose 28‐day oral toxicity study in rodents (GLP, OECD TG 407) | Wistar rats | Up to 1,200 mg NF/kg bw per day (20 g/kg feed) |
| Study No. NNI002‐TX01 (APS, | Repeated dose 28‐day oral toxicity study in rodents (GLP, OECD TG 407) | Male Wistar rats | 20 g/kg feed |
| Study No. B‐8508 (Kawamata et al., | 90‐day repeated dose oral toxicity study (GLP, OECD TG 408) | Sprague‐Dawley rats | Up to 13,164 mg/kg bw per day for males; 15,027 mg/kg bw per day for females |
| Study No. 1010 (NPHI, | 90‐day repeated dose oral toxicity study (non‐GLP) | Wistar rats | Approximately 400–500 mg/kg bw per day |
GLP: Good Laboratory Practice; OECD TG: Organisation for Economic Co‐operation and Development test guidelines; APS: American Preclinical Services; NPHI: National Public Health Institute; bw: body weight.
| Parameter (%) | Batch number | Method of analysis | |||||||
|---|---|---|---|---|---|---|---|---|---|
| #1 | #2 | #3 | #4 | #5 | #6 | #20 | #7 | ||
|
| 0.98 | 1.03 | 0.98 | 1.01 | 1.14 | 1.14 | 0.94 | 1.01 | AOAC 988.15 |
|
| 0.45 | 0.42 | 0.46 | 0.46 | 0.48 | 0.48 | 0.55 | 0.45 | AOAC 994.12 mod. |
|
| 0.93 | 0.87 | 0.84 | 0.86 | 0.91 | 0.93 | 0.72 | 0.87 | AOAC 994.12 mod. |
|
| 3.87 | 3.92 | 3.97 | 4.07 | 3.97 | 3.96 | 3.65 | 3.83 | AOAC 982.30 mod. |
|
| 1.94 | 1.95 | 1.92 | 1.97 | 2.08 | 2.07 | 1.82 | 1.94 | AOAC 982.30 mod. |
|
| 1.93 | 1.96 | 1.87 | 1.88 | 2.03 | 2.05 | 1.79 | 1.98 | AOAC 982.30 mod. |
|
| 4.56 | 4.66 | 4.56 | 4.64 | 4.8 | 4.71 | 4.42 | 4.58 | AOAC 982.30 mod. |
|
| 2.06 | 2.09 | 1.98 | 2.04 | 2.15 | 2.18 | 1.75 | 2.06 | AOAC 982.30 mod. |
|
| 2.41 | 2.39 | 2.34 | 2.39 | 2.47 | 2.47 | 2.01 | 2.35 | AOAC 982.30 mod. |
|
| 2.76 | 2.6 | 2.56 | 2.61 | 2.87 | 2.85 | 2.35 | 2.74 | AOAC 982.30 mod. |
|
| 2.66 | 2.66 | 2.6 | 2.66 | 2.66 | 2.55 | 2.21 | 2.55 | AOAC 982.30 mod. |
|
| 2.08 | 2.07 | 2.04 | 2.06 | 2.04 | 1.95 | 1.69 | 1.96 | AOAC 982.30 mod. |
|
| 3.91 | 4.03 | 3.86 | 3.92 | 4.21 | 4.17 | 3.25 | 3.99 | AOAC 982.30 mod. |
|
| 1.53 | 1.58 | 1.53 | 1.57 | 1.7 | 1.66 | 1.37 | 1.54 | AOAC 982.30 mod. |
|
| 2.48 | 2.51 | 2.4 | 2.45 | 2.62 | 2.58 | 2.27 | 2.40 | AOAC 982.30 mod. |
|
| 3.31 | 3.21 | 2.94 | 2.98 | 3.7 | 3.57 | 2.69 | 3.35 | AOAC 982.30 mod. |
|
| 0.95 | 0.96 | 0.92 | 0.95 | 1 | 1 | 0.90 | 0.95 | AOAC 982.30 mod. |
|
| 3.25 | 3.17 | 3 | 2.96 | 2.87 | 2.79 | 4.17 | 3.01 | AOAC 982.30 mod. |
AOAC: Association of Official Analytical Collaboration.