Carbon dioxide (CO2) transmission rate of films and sheeting

This test is designed to measure the oxygen transmission rate of finished packages, including cups, bottles, trays, and containers. Two replica measurements are included in the displayed price. Temperature can be adjusted from 15 to 55 °C, and relative humidity can be either 0% or between 5 and 90% RH. This test is not suitable for films. Please see the oxygen transmission rate (OTR) of films and sheeting if you need testing for film samples. Please specify the sample dimensions and testing conditions upon ordering.

Determination of the oxygen transmission rate of plastic films and sheet-like materials. The test is performed on two parallel samples simultaneously. Measurement conditions (temperature and relative humidity) can be chosen according to the intended use of the material. Oxygen permeability is typically measured at 23 °C and 0% relative humidity as per standard ASTM D3985. In moist conditions, for example at 38 °C and 90% relative humidity, standard ASTM F1927 is used. Please disclose the desired temperature (from 10 °C to 38 °C) and relative humidity (either 0% or from 20% to 90%) upon ordering. This measurement is suitable for plastic films with OTR values between 0.05 to 20 000 cm³/(m² * day).

Water vapor transmission rate testing can be used to evaluate the breathability of textiles. This test, performed according to ASTM E96, measures the amount of water vapor that passes through the fabric in a controlled environment. The standard conditions are 20 °C and 65% relative humidity. The result will be reported in g/m²/day. For a more comprehensive evaluation of technical textiles' barrier properties, this test can be combined with the ISO 811 resistance to water penetration test and the ISO 9237 air permeability measurement. Do not hesitate to ask our experts for an offer for the full set of analyses.

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.

Determination of the water vapor transmission rate (WVTR) of ultra-high barrier materials. The method can also be used to test moderate barrier materials at high-temperature conditions. Please disclose the desired temperature (from 10 to 85 °C) and the desired relative humidity (from 60% to 100%) when placing the order. This measurement is applicable for films and sheeting materials with WVTR values between 1x10-6 and 10 g/m2/day. If you wish to test finished packaging instead, check out the WVTR measurement for packages. The price of the test consists of a flat rate cost per sample plus one day measurement time. Please contact our experts for an offer.

Recyclability testing of paper and cardboard packaging according to the Aticelca 501:2023 method. The method is based on the Italian UNI 11743: 2019 standard. The following properties are evaluated: Disintegration behavior and recyclable content, Impurity content (e.g., plastic, coatings, adhesives), Visual appearance. Based on the results, the material is given a recyclability classification of A+, A, B, or C. A+ indicates a highly recyclable material, while C indicates a product with poor recyclability. The material can also be classified as non-recyclable with paper.

Determination of the oxygen transmission rate of paper and cardboard materials. The test is performed on three identical samples to ensure repeatability. Measurement conditions (temperature and relative humidity) can be chosen according to the intended use of the material. The oxygen transmission rate is typically measured at 23 °C and 0% relative humidity as per standard ASTM D3985. In moist conditions, for example at 38 °C and 90% relative humidity, standard ASTM F1927 is used. Please disclose the desired temperature (from 5 °C to 95 °C) and relative humidity (either 0% or 10% to 90%) upon ordering. This measurement is suitable for paper and board materials with OTR values between 0.05 to 5000 cm3/(m2 * day).

Extended analysis package for phthalates in various matrices using the GC-MS technique. Phthalates are a group of chemicals widely used as plasticizers, which make plastics more flexible and durable. Phthalates are also found as additives in products, including cosmetics and personal care items. Several phthalates have been identified as being endocrine-disrupting or toxic to reproduction. Exposure to phthalates can occur, e.g., through food (chemicals can transfer from packaging), children's toys (when put in their mouths), and dust from vinyl flooring. The following 43 compounds are detected as part of this analysis: Compound Abbreviation CAS number Phthalic anhydride - 85-44-9 Dimethyl phthalate DMP 0131-11-3 Diethyl phthalate DEP 84-66-2 Ethyl Isobutyl phthalate - 94491-96-0 Diallyl phthalate DAP 131-17-9 Dipropyl phthalate DPP2 131-16-8 Diisobutyl phthalate DIBP 84-69-5 Dibutyl phthalate DBP 84-74-2 Dimethylglycol phthalate DMEP 117-82-8 Diizopentyl phthalate DIPP 605-50-5 N-pentyl-isopentyl phthalate PIPP 84777-06-0 N-pentyl-isopentylphtalate - 776297-69-9 Di(2-ethoxyethyl) phthalate DEEP 605-54-9 Diamyl phthalate DPP 131-18-0 Tri-n-butylacetyl citrate - 77-90-7 Diisohexyl phthalate DMPP 146-50-9; 71850-09-4 Di(n-hexyl) phthalate DNHP 84-75-3 Butyl Octyl phthalate BOP 84-78-6 Adipic acid, bis(2-ethylhexyl) ester - 103-23-1; Ref.: 31920 Butyl benzyl phthalate BBP 85-68-7 Di( 2-ethylhexyl) phthalate DEHP 117-81-7 Di-n -hexyl azelate - 109-31-9 Dicyclohexyl phthalate DCHP 84-61-7 Di(n-octyl) phthalate DNOP 117-84-0 Dioctyl terephthalate DOTP 6422-86-2 Dibenzyl phthalate DBP2 523-31-9 Bis(2-propylheptyl) phthalate - 53306-54-0 Dinonyl phthalate DNP 84-76-4 Hexyl-2-ethylhexyl phthalate (HEHP) HEHP 75673-16-4 Diundecylphthalat - 3648-20-2 Bis(4-Methyl-2-pentyl)phthalate - 84-63-9 Diphenyl phthalate DPhP 84-62-8 1,2-benzenedicarboxylic acid, di-C6-8-branched alkyl ester, C7-rich DIHP 71888-89-6 Diisononyl phthalate DINP 28553-12-0; 68515-48-0 Diisodecylphtalate DIDP 26761-40-0; 68515-49-1 1,2-benzenedicarboxylic acid, dihexyl ester, branched and linear - 68515-50-4 1,2-benzenedicarboxylic acid, di C7-11 branched and linear alkyl esters DHNUP 68515-42-4 1,2-Benzenedicarboxylic acid, mixed decyl and hexyl and octyl diesters - 68648-93-1 1,2-Benzenedicarboxylic acid, di-C6-10-alkyl esters - 68515-51-5 Diisooctyl phthalate - 27554-26-3 Bis(6-methylheptyl) phthalate - 96507-86-7 1,2-cyclohexanedicarboxylic acid, diisononyl ester - 166412-78-8; Ref.: 45705 Dibutyl adipate - 105-99-7