Aromatic amines derived from azo dyes

Phthalates are a group of chemicals widely used as plasticizers, which make plastics more flexible and durable. They have also been used as additives in products such as cosmetics and personal care items. Several phthalates have been identified as endocrine-disrupting agents or as chemicals toxic to reproduction. Exposure to phthalates can occur through: Oral exposure Food: Exposure occurs via migration from food packaging., Children's toys: Children often put toys in their mouths.., Inhalation: Breathing in dust from vinyl flooring or fragrances (like perfumes) can cause exposure to phthalates via inhalation., Skin contact: Phthalates present in cosmetics, lotions, and soaps can be absorbed through the skin.. For other listed matrices apart from cosmetics, the analysis package covers the following substances included in the REACH Authorization List: Substance Abbreviation CAS number Diisobutyl phthalate DIBP 84-69-5 Dibutyl phthalate DBP 84-74-2 Benzyl butyl phthalate BBP 85-68-7 Bis(2-ethylhexyl) phthalate DEHP 117-81-7 Di(n-octyl) phthalate DNOP 117-84-0 Diisononyl phthalate DINP 68515-48-0 Diisodecyl phthalate DIDP 26761-40-0 Products that contain restricted phthalates in concentrations higher than 0.1% may be removed from the market. The analysis package for cosmetic products contains the following phthalates: Substance Abbreviation CAS number Bis(2-ethylhexyl) phthalate DEHP 117-81-7 Benzyl butyl phthalate BBP 85-68-7 Dibutyl phthalate DBP 84-74-2 Diisononyl phthalate DINP 68515-48-0 Di(n-octyl) phthalate DNOP 117-84-0 Diisodecyl phthalate DIDP 26761-40-0 All the above-mentioned substances are prohibited in cosmetic products (Annex II of Regulation (EC) No 1223/2009).

Analysis for quantifying dioxins and furans (PCDD/F) in various packaging materials (e.g. food and cosmetics packaging) and their raw materials, including plastics, paper, and rubber. Dioxins and furans are a family of chlorine-containing chemicals considered bioaccumulating, persistent organic pollutants (POPs) that can be toxic even at low doses. While regulatory limits apply mainly to food and feed, packaging materials can be a source of indirect exposure to dioxins and furans. Recycled materials tend to pose relatively high risks, depending on the quality of the raw material and the effectiveness of the decontamination process. The following substances are included in the analysis: Dibenzo-p-dioxins (PCDDs) Polychlorinated dibenzofurans (PCDFs) 2,3,7,8-TCDD. 2,3,7,8-TCDF. 1,2,3,7,8-PeCDD. 1,2,3,7,8-PeCDF. 1,2,3,4,7,8-HxCDD. 2,3,4,7,8-PeCDF. 1,2,3,6,7,8-HxCDD. 1,2,3,4,7,8-HxCDF. 1,2,3,7,8,9-HxCDD. 1,2,3,6,7,8-HxCDF. 1,2,3,4,6,7,8-HpCDD. 1,2,3,7,8,9-HxCDF. OCDD. 2,3,4,6,7,8-HxCDF. 1,2,3,4,6,7,8-HpCDF. 1,2,3,4,7,8,9-HpCDF. OCDF. Testing is often performed for the following reasons: Analyzing recycled PE, PP, and LDPE intended for cosmetics packaging according to CosPaTox guidelines., Analyzing paper and board bleached with elementary chlorine according to the requirements of TemaNord 2008:515 guidelines..

Determination of the total organic fluorine (TOF) content in combustible materials by combustion ion chromatography (CIC). TOF analysis gives information about the total amount of organic fluorinated compounds. It can also be used to evaluate the presence of per- and polyfluoroalkyl substances (PFAS) in the material, even though individual PFAS compounds can't be analyzed with this method. The analysis is suitable for many different materials. Please describe the sample in detail when requesting an offer to help us prepare a quote quickly.

Screening of volatile organic compounds (VOC) from paper, board, and plastics. The method can be used to analyze volatile residues from printed packaging. For evaluation of recycling process efficiency, please see our extended package for VOC screening. The following substances are included in this analysis package: Substance CAS No Methyl propylene glycol (1-methoxy-2-propanol) 107-98-2 Buthyl glycol (2-Butoxy ethanol) 111-76-2 Ethyl glycol (2-Ethoxyethanol) 110-80-5 Ethyl glycol acetate (2-Ethoxyethyl acetate) 111-15-9 Methyl glycol (2-Methoxyethanol) 109-86-4 Methyl glycol acetate (2-Methoxyethanol acetate) 110-49-6 3-Ethoxy-1-propanol 111-35-3 Acetyl acetone 123-54-6 Acetone 67-64-1 Ethanol 64-17-5 Isobutanol 201-148-0 2-propanol, Isopropanol (IPA) 67-63-0 Methanol 67-56-1 1-Butanol 71-36-3 1-Propanol 71-23-8 Benzene 71-43-2 Cyclohexane 110-82-7 Ethylbenzene 100-41-4 Ethyl acetate 141-78-6 Isobutyl acetate 110-19-0 Isopropyl acetate 108-21-4 Isooctane 540-84-1 2-butanone, methyl ethyl ketone (MEK) 78-93-3 Methyl isobutyl ketone (MIBK) 108-10-1 Methyl acetate 79-20-9 Toluene 108-88-3 Trichloroethylene 79-01-6 Xylene 1330-20-7 n-Butyl Acetate 123-86-4 n-Heptane 142-82-5 n-Hexane 110-54-3 n-Octane 111-65-9 n-Propyl acetate 109-60-4

Specific migration of dialkyl ketones (DAKs) that originate from alkyl ketene dimer (AKD) hydrophobic sizing agent of paper and board. According to BfR XXXVI recommendation, the limitation for the migration of AKD DAKs is 5 mg/kg of food or food simulant.

Determination of mineral oil saturated hydrocarbons (MOSH) with polyolefin oligomeric saturated hydrocarbons (POSH) and mineral oil aromatic hydrocarbons (MOAH) in various matrices, including: Food contact materials (e.g., paper, board, plastics, rubber), Printing inks (incl. carbon black), Cosmetic products and raw materials, Lubricating oils and greases, white oils. The results are reported as the concentrations of fractions of MOSH/POSH and MOAH, with grouping based on the number of carbon atoms in the substances. The reported fractions are listed in the table below: MOSH/POSH (C10-C50), total MOAH (C10-C50), total MOSH/POSH (≥C10-≤C16) MOAH (≥C10-≤C16) MOSH/POSH (>C16-≤C20) MOAH (>C16-≤C25) MOSH/POSH (>C20-≤C25) MOAH (>C25-≤C35) MOSH/POSH (>C25-≤C35) MOAH (>C35-≤C50) MOSH/POSH (>C35-≤C40) MOSH/POSH (>C40-≤C50) In case the sample contains high amounts of MOSH, POSH, or poly alpha olefins (PAO), the levels should be indicated before shipping samples. Moreover, the LOQ is higher for samples with high MOSH, POSH, or PAO content due to dilution. Additionally, the safety data sheets (SDS) should be supplied with the samples when available.

Determination of bisphenol S content in various matrices, including: Consumer goods made from plastic, elastomers, and rubber, Food packaging (plastic, paper, multi-materials). Testing is recommended especially for paper and board food packaging that contains recycled fibers and comes into contact with moist and fatty foods. To be compliant with German BfR Recommendation XXXVI, such packaging must not release bisphenol S into food in amounts exceeding 0.05 mg/kg. Extraction is possible with various techniques, including: Solvent extraction, Cold water extract (EN 645), Hot water extract (EN 647), Solvent extract (EN 15519).

GC-MS analysis of 16 PAH compounds, which are listed as high-priority pollutants by the U.S. Environmental Protection Agency (EPA). The analyzed PAH compounds are: naphthalene [CAS: 91-20-3], acenaphthylene [CAS: 208-96-8], acenaphthene [CAS: 83-32-9], fluorene [CAS: 86-73-7], phenanthrene [CAS: 85-01-8], anthracene [CAS: 120-12-7], fluoranthene [CAS: 206-44-0], pyrene [CAS: 129-00-0], benz(a)anthracene [CAS: 56-55-3], chrysene [CAS: 218-01-9], benzo(b)fluoranthene [CAS: 205-99-2], benzo(k)fluoranthene [CAS: 207-08-9], benzo (a) pyrene [CAS: 50-32-8], dibenzo(ah)anthracene [CAS: 53-70-3], benzo (ghi) perylene [CAS: 191-24-2], indeno (123cd) pyrene [CAS: 193-39-5].

Anthraquinone is an additive used in paper pulp manufacturing processes. According to BfR XXXVI, the application of anthraquinone as an additive to raw material is no longer recommended.

As there is no harmonized EU regulation for using wood in food contact applications, compliance should be assessed based on other resources, such as the national legislation of member states. This test package is based on the requirements of French Information note n°2012-93 (Note d'information n° 2012-93) for coated and non-coated wood intended for food contact. The following analyses are included in the displayed price: Test parameter Test method/standard Method of extraction or preparation Transfer of odor and flavor into food DIN 10955 Water extract or contact with model food Heavy metals in water extract (Pb, Cd, Hg) ICP-MS Cold or hot water extract (EN 645 / EN 647) Formaldehyde in water extract EN 1541 Cold or hot water extract (EN 645 / EN 647) Polychlorinated biphenyls (PCB28, PCB52, PCB101, PCB118, PCB153, PCB180) GC-MS In-house method Pentachlorophenol (PCP) content GC-MS CEN/TR 14823 In addition to the tests listed above, a pesticide screening should be performed for wood treated with antifungal substances (so-called "anti-blue" protection). The analysis covers 715 substances and is available for an additional cost of 298 EUR. In most cases, this test package is sufficient to establish food contact compliance of non-coated wood or articles thereof. If the wood has been coated with a lacquer or varnish, has been painted, or contains adhesives, complementary testing could be required (e.g., migration of primary aromatic amines, migration of mineral oil (MOSH/POSH and MOAH hydrocarbons). Our experts are happy to support you by reviewing the documentation of the coating material and/or the adhesive to determine the full scope of required testing.