Aromatic amines derived from azo dyes

We offer two extended analysis packages for phthalates and plasticizers in various matrices using the GC-MS technique. The first package covers 22 compounds with reporting limits significantly lower than the industry standard of 0.001%: Substance name Abbreviation CAS No Reporting limit (LOD) (wt%) Dimethyl phthalate DMP 131-11-3 0.00005 Diethyl phthalate DEP 84-66-2 0.00005 Triethyl citrate TEC 77-93-0 0.00025 Diallyl phthalate DAP 131-17-9 0.00005 Dipropyl phthalate DPrP 131-16-8 0.00005 Diisobutyl phthalate DIBP 84-69-5 0.00005 Dibutyl phthalate DBP 84-74-2 0.00005 Di-n-pentyl phthalate DPP 131-18-0 0.00005 Di-n-hexyl phthalate DHXP 84-75-3 0.00005 Dibutyl sebacate DBS 109-43-3 0.00005 Acetyl tributyl citrate ATBC 77-90-7 0.00005 Benzyl butyl phthalate BBP 85-68-7 0.00005 Diethylhexyl adipate DEHA 103-23-1 0.00005 Dicyclohexyl phthalate DCHP 84-61-7 0.00005 Di-2-ethylhexyl phthalate DEHP 117-81-7 0.00005 Di-n-octyl phthalate DNOP 117-84-0 0.00005 DINCH DINCH 166412-78-8 0.00005 Di-2-ethylhexyl sebacate - 122-62-3 0.00005 Dioctyl terephthalate DOTP 6422-86-2 0.00005 Diisononyl phthalate DINP 28553-12-0 0.00025 Diisodecyl phthalate DIDP 26761-40-0 0.00025 Phthalic anhydride - 85-44-9 0.00005 The other package covers 43 compounds with a detection limit of 0.001%. The full list of target substances is available upon request. Please let us know which option you are interested in when requesting a quote.

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 using combustion ion chromatography (CIC). By default, TOF is analyzed as total fluorine (TF). If required, total inorganic fluorine (TIF) can be measured as well, and TOF calculated as the difference between TF and TIF. 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).

We offer several accredited methods for determining the total fluorine (TF) content of combustible materials: EN 14582, based on combustion ion chromatography (CIC). The method is recommended by the Nordic Council of Ministers as a quick and powerful total fluorine screening technique., EN 15408 using oxygen bomb combustion treatment followed by ion chromatography (IC). This method can be applied to plastic sheets and granules, and it is also possible to determine the total content of S, Cl, and Br. , ASTM D7359-23, based on oxidative pyrohydrolytic combustion, followed by CIC.. The most suitable method is typically selected based on the sample matrix. However, please let us know if you wish a specific standard to be followed. Sample preparation (air drying and milling of the sample to particles <1 mm) is included in the displayed price.

Analysis package for silicone elastomers intended for food contact: Test parameter Limit Test method Regulatory reference Volatile content 0.5% Bestimmung von flüchtigen Verbindungen in Bedarfsgegenständen aus Silikon (version 02, 09/2023) BfR recommendation XV Residual peroxides Not detected 58. Mitteilung zur Untersuchung von Kunststoffen: Bundesgesundheitsblatt 40, (1997) BfR recommendation XV Release of odor and flavor No deterioration of organoleptic properties DIN 10955:2024 Regulation (EC) 1935/2004 Upon request, analysis of cyclosiloxanes can be included in the test package. Cyclosiloxanes are known impurities in silicone articles, and their concentrations must be very low for products to be eligible for sustainability labels, such as the Nordic Swan Ecolabel.