ILLA SpA VIA GHISOLFI GUARESCHI, NOCETO (PR)

Similar documents
Test Report No. SH / CHEM Date: Apr. 28, 2008 Page 1 of 6

Test Report No. : CE/2009/34977 Date : 2009/03/25 Page : 1 of 10

Test Report. Report No. ECL01H Page 1 of 5

Test Report No. : CE/2008/38467 Date : 2008/04/07 Page : 2 of 11 Test Result(s) PART NAME NO.1 : BLACK PLASTIC TUBE Cadmium (Cd) Lead (Pb) Mercury (Hg

Determination of 24 PAHs in Drinking Water

Schedule of Accreditation issued by United Kingdom Accreditation Service 2 Pine Trees, Chertsey Lane, Staines-upon-Thames, TW18 3HR, UK

Application Note. Agilent Application Solution Analysis of PAHs in soil according to EPA 8310 method with UV and fluorescence detection.

Test Report. ECL01H Page 1 of 9. Report No.

Reviewing Material Safety Data Sheets to Verify Significant Drinking Water Threats

The Use of Tandem Quadrupole GC/MS/MS for the Determination of Polycyclic Aromatics Hydrocarbons (PAHs) in Food Products

Pursuant to Chapter 4 of the Code of Ethics, ETAD members may not manufacture or sell dyes referred to in Annexes A and B. Annex A

Sensitive and rapid determination of polycyclic aromatic hydrocarbons in tap water

Test Report No. : CE/2011/A5289 Date : 2011/11/02 Page : 2 of 18 Test Result(s) PART NAME No.1 : BLACK GRAINS Cadmium (Cd) Lead (Pb) Mercury (Hg) Test

Method 8270C PAH. FD- Field Duplicate Samples

Test Report. No. SHAHG Date: 07 Jun Page 1 of 7.

Multi-residue Analysis for PAHs, PCBs and OCPs on Agilent J&W FactorFour VF-Xms

Test Report. Report No.RLSZE Page 1 of 11

Accelerated Solvent Extraction GC-MS Analysis and Detection of Polycyclic Aromatic Hydrocarbons in Soil

UNSUITABILITY OF THE ZEK/AFPS TEST METHOD FOR THE DETERMINATION OF POLYCYCLIC AROMATIC HYDROCARBONS IN CARBON BLACK

METHOD 8100 POLYNUCLEAR AROMATIC HYDROCARBONS

Appendix 1: Polycyclic Aromatic Compounds: Nomenclature and Analysis

APPENDIX G. Data Management Rules. Dioxin Data Report Appendix G. Lower Duwamish Waterway Superfund Site: T-117 Early Action Area

Supporting Information

Results of a Sediment Survey in the Near Offshore Waters of the Proposed Quarry Site in the Vicinity of Whites Cove, Digby Neck, Nova Scotia

EL608. Deodorants [EL /1/ ]

Rely on Rxi -PAH Columns

Determination of Polycyclic Aromatic Hydrocarbons (PAHs) in Seafood Using GC/MS

PAH Analyses with High Efficiency GC Columns: Column Selection and Best Practices

Katherine K. Stenerson, Michael Ye, Michael Halpenny, Olga Shimelis, and Leonard M. Sidisky. Supelco, Div. of Sigma-Aldrich Bellefonte, PA USA

General considerations Dye manufacturers achieve an effective impurity profile by good manufacturing practices such as: - implementation of a suitable

Test Report. No. SHAEC Date: 15 Jul Page 1 of 5.

18/05/2010 Soil. 18/05/2010 Soil

Certificate of Analysis

Certificate of Analysis

Application Note. Abstract. Introduction. Determination of Polycyclic Aromatic Hydrocarbons in Seafood by an Automated QuEChERS Solution

The Suite for Environmental GC Analysis

ANALYTICAL RESULTS. Project: Mayflower, AR Pipeline Incident

This project has been funded with support from the European Commission. This publication reflects the views only of the authors, and the Commission

TETRA TECH, INC. December 8, Lynn Nakashima Berkeley Regional Office 700 Heinz Avenue, Suite 200C Berkeley, California 94710

ANALYTICAL RESULTS. Project: Mayflower, AR Pipeline Incident

Andrei Medvedovici, Florina Micăle, Florentin Tache

ANALYTICAL RESULTS. Project: Mayflower, AR Pipeline Incident

Environmental Forensic Principals for Sources Allocation of Polycyclic Aromatic Hydrocarbons

TEST REPORT. Test Report No. : Project No. :

CALIBRATION OF GC/MS METHOD AND VALIDATION OF THE MODIFIED SAMPLE PREPARATION FOR DETERMINATION OF POLYCYCLIC AROMATIC HYDROCARBONS

Facility: Mansfield Revision 3. Title: PAHs by SPME Page 1 of 11

Analysis of Polycyclic Aromatic Hydrocarbons in Soil with Agilent Bond Elut HPLC-FLD

Helcom Submerged Bonn

ENVIRONMENTAL analysis

Authorized By: For Intertek Testing Services Ltd., Shanghai. Joanne Li Deputy General Manager

The Effect of Unresolved Complex Mixtures (UCM) on Isotopic Profile of Aromatic Hydrocarbons

Annex 2 Formaldehyde

BOUCHARD B120 RELEASE SHORELINE SEGMENT SUMMARY

The Design of High Temperature Capillary Gas Chromatography Columns Based on Polydimethylsiloxane

Test Report No.GGN/F(C/M)/13/ Dated 03/08/2013

TECHNICAL MEMORANDUM June 16, 2011

IUS CR.FD 001 Page 1 of 6

Proposed Inventory of Emissions, Discharges and Losses of Substances, and Chemical Analysis Information

Analytische Qualitätssicherung Baden-Württemberg

Analysis of polycyclic aromatic hydrocarbons in. in vegetable oils combining gel permeation chromatography with solid phase extraction cleanup.

Semivolatile Organics Analysis Using an Agilent J&W HP-5ms Ultra Inert Capillary GC Column

Occupational exposure to polycyclic aromatic hydrocarbons in various technological processes i INTRODUCTION

Tar measurement by the Solid Phase Adsorption (SPA) method

Polycyclic Aromatic Hydrocarbons in Water by GC/MS PBM

BOUCHARD B120 RELEASE SHORELINE SEGMENT SUMMARY

MEASUREMENT OF DRY DEPOSITION AMOUNT OF PAHS IN ZONGULDAK REGION

DETERMINATION OF POLYCYCLIC AROMATIC HYDROCARBONS IN SOIL AT AL-NAHRAWAN BRICKS FACTORY Thamera K. M. Al-Rudaini 1 and Israa M.H.

Selection of a Capillary

Analysis. Priority LC GC. Zebron PAH Accurately quantitate EU and EPA PAHs in less than 28 minutes

Optimizing GC Parameters for Faster Separations with Conventional Instrumentation

Amec Foster Wheeler Environment & Infrastructure, Inc BIG SHANTY ROAD, NW, SUITE 100 KENNESAW, GEORGIA (770)

Guidance on the Major Source Determination for Certain Hazardous Air Pollutants

Materials Declaration

STANDARD OPERATING PROCEDURES

Application of an Analytical Technique for Determining Alkyl PAHs, Saturated Hydrocarbons and Geochemical Biomarkers

Developing Large Volume Injection (LVI) in Split / Splitless Inlets. Philip J. Koerner Phenomenex Inc. NEMC 2014

BOUCHARD B120 RELEASE SHORELINE SEGMENT SUMMARY

Table 1 Soil and Groundwater Sampling Summary Table

Substances Limits - Testing methods

The direct effect of the harbour. micropollutant concentration. Workshop Characterization of atmospheric pollution in harbour areas 26 June 2013

Determination of Polycyclic Aromatic Hydrocarbons (PAH) Adsorbed on Soot Formed in Pyrolysis of Acetylene at Different Temperatures

Selection of a Capillary GC Column

This document is meant purely as a documentation tool and the institutions do not assume any liability for its contents

APPENDIX K. Fingerprinting Justification Memo

Analysis of Alkyl PAHs And Geochemical Biomarkers

North Bay Wildfires: Response & Recovery

Test Report. No. NGBHG Date: 21 Nov Page 1 of 10.

*

SUPPLEMENTARY INFORMATION. Towards streamlined identification of dioxin-like compounds in

BOUCHARD B120 RELEASE SHORELINE SEGMENT SUMMARY

BOUCHARD B120 RELEASE SHORELINE SEGMENT SUMMARY

APPENDIX D Laboratory Analytical Reports

RAW MATERIAL SUPPLIER QUESTIONNAIRE

17. July 2018 / 07:49 PO No / Order of General tests Marabu GmbH & Co. KG, Mr. Düzgün Chilbuka Marabu GmbH & Co.

BOUCHARD B120 RELEASE SHORELINE SEGMENT SUMMARY

Meeting Challenging Laboratory Requirements for USEPA Method 8270 Using a Highly Sensitive, Robust, and Easy-to-Use GC/MS

Non-Potable Water A2LA Certificate

Environmental Resources Management

MODIFIED METHOD FOR DETERMINATION OF PAHs IN AMBIENT AIR IN BANGKOK USING GAS CHROMATOGRAPHY-MASS SPECTROMETRY

Appendix 2 Data Distributions for Contaminants in Water and Sediment Samples in Response to the Deepwater Horizon Oil Spill, 2010

Transcription:

FOOD PACKAGING MATERIALS FOOD CONTACTS 1265\FPM\FDC\15 12/11/2015 1 ILLA SpA VIA GHISOLFI GUARESCHI, 1 43015 NOCETO (PR) D.P.R. dated 23/08/1982, D.L. 108 dated 25/01/1992, D.M.34 dated 21/3/3 European Directives: 82/11/EEC GUCEE L 29 dated 23/10/82, 85/52/EEC GUCEE L 32 dated 31/12/1985, 93/8/EEC GU L90 dated 14/04/1993, 9/48/EC GUCE L 222 dated 12/8/9. Regulations 1935/2004/EC GUCE L 338 dated 13/11/04 and 1895/2005/EC GUCE L 302 dated 19/11/2005. Regulation 10/2011/EU, GUUE L 12 del 15/01/2011, and subsequent updatings. UNI EN 1186 1 15:2003 (see the overall migration test description for the identification of the technical standard part) ILLA SpA Sig. Nicola Ferrari Copy to Division Head

2 GENERALITIES - Sample receiving date: 14/10/2015 - Analysis start date: 19/10/2015 - Analysis end date: 10/11/2015 - Deviation from test methods: NO SAMPLE DESCRIPTION SAMPLING The initial sampling has been done by the customer. The sampling for the test has been done drawing casually part of the sample in our possession. DECLARATION The test results of the present report are related exclusively to the tested sample. The present test report cannot be partially reproduced without the authorization of CSI managing Director. The uncertainties are estimated as extended uncertainty obtained multiplying the standard uncertainty by the coverage factor k corresponding to a confidence level of about 95%. Normally, this factor = 2. PERFORMED DETERMINATIONS 1) DETERMINATION OF THE OVERALL MIGRATION UNI EN 1186-1:2003 + UNI EN 1186-9:2003 + UNI EN 1186-14:2003 D.P.R. dated 23/08/1982, D.L. 108 dated 25/01/1992, D.M.34 dated 21/3/3 European Directives: 82/11/EEC GUCEE L 29 dated 23/10/82, 85/52/EEC GUCEE L 32 dated 31/12/1985, 93/8/EEC GU L90 dated 14/04/1993, 9/48/EC GUCE L 222 dated 12/8/9. Regulations 1935/2004/EC GUCE L 338 dated 13/11/04 and 1895/2005/EC GUCE L 302 dated 19/11/2005. Food simulant Acetic acid in aqueous solution 3% w/v Isoctane Ethanol 95% V/V in aqueous solution Contact condition 2 hours at 100 C repeated contact 4 hours at 60 C repeated contact 6 ore a 60 C repeated contact Migration test was carried out by Article Filling. LOD (limit of detection): 5 mg/kg. Volume: 15 dl. Surface: 5.5 dm 2.

3 2) QUANTITATIVE DETERMINATION OF PRIMARY AROMATIC AMINES: METHOD L.00.00-6 (LMBG 35) METODO L.00.00-6 (LMBG 35) The procedure used to quantify the primary aromatic amines was a spectrophotometer method, based on the colour complex formed by a diazotization and a coupling reaction. The solution was further concentred and eluted on a solid phase column. The final solution was photometrically detected at 550 nm (Method Amtliche Sammiung von Untersuchungsverfahren method L.00.00-6 LMBG 35, del 1995 agg. 2002) An external calibration curve detected at 550 nm was used to quantify the primary aromatic amines. An aniline standard solution 0, 0.5, 1.0, 1.5, 2.0, 3.0, 4.0, 6.0 g in acetic acid 3% was detected. LOD: 0.2 µg /100 ml or LOD: 0.002 mg/kg or LOD: 0.0003 mg/dmq (the limit is originally expressed in mg/kg it is possible to convert the measure unit by dividend for the factor 6 to express them in mg/dmq.) 3) SPECIFIC MIGRATION OF METALS FOR COOKWARE WITH NON-STICK COATING MI_8920060_2015_Rev.0 Quantification of specific migration of chromium, cadmium, lithium, nickel and lead by ICP Plasma analysis technique, performed on each sample and simulant that the steel is usually for acetic acid 3% w/v resulting from the third contact brought to 100 C. LMS: 0.05 mg/kg/each. Li LOD:0.05mg/kg, LOD Cr: 0.05 mg/kg, LOD Pb: 0.05 mg/kg, LOD Cd: 0.05 mg/kg, Ni: 0.05 mg/kg 4) DETERMINATION OF POLYCYCLIC AROMATIC HYDROCARBONS (PAH) MI_89200485_2015_Rev.0 A note amount of sample was extracted with solvent with internal standard in ultrasonic bath at 60 c for 30 min. The solution was concentrated and analysed by gas-cromatography technique (SIM acquisition of ion of 18 compounds) for the determination of polycyclic aromatic hydrocarbons. This test has been carried out in accordance with the analysis method described in the document GS mark - Specification as per 21 Para. 1 No. 3 ProdSG. Limit Category 1: 0.2 mg/kg (ND) 5) SPECIFIC MIGRATION OF TETRAFLUOROETHYLENE MI_8920096_2015_Rev.0 Determination of the specific migration of tetrafluoroethylene (CAS No. 000116-14-3 - Ref No. 25120) made simulants arising from the release test by HS-GC/MS technique. The quantification is performed by an external calibration of tetrafluoroethylene in the same simulants LMS: 0.05 mg/kg LOD: 0.05 mg/kg.

4 RESULTS 1) DETERMINATION OF THE OVERALL MIGRATION Food simulant: Acetic acid in aqueous solution 3% w/v Contact condition: 2 hours at 100 C rep. cont. Measured value Average value Extended uncertainty Limit value 21/03/3) --- 60(+12) Food simulant: Isoctane Contact condition: 4 hours at 60 C rep. cont. Measured value Average value Extended uncertainty Limit value 21/03/3) --- 60(+20) Food simulant: Ethanol 95% v/v Contact condition: 6 ore a 60 C rep. cont. Measured value Average value Extended uncertainty Limit value 21/03/3) --- 60(+20)

5 2) QUANTITATIVE DETERMINATION OF PRIMARY AROMATIC AMINES: METHOD L.00.00-6 (LMBG 35) Food simulant: Acetic acid in aqueous solution 3% w/v Contact condition: 2 hours at 100 C rep. cont. Measured unit: mg/kg measured value average value standard deviation limit value (according to 10/2011) < 0.002 < 0.002 < 0.002 -- 0.010 mg/kg 3) SPECIFIC MIGRATION OF METALS FOR COOKWARE WITH NON-STICK COATING Food simulant: Acetic acid 3% w/v Contact conditions:2 hours at 100 C repeated contact Element Measured value LMS: 0.05 mg/kg each Cadmium Chromium Lead Lithium Nickel 4) DETERMINATION OF POLYCYCLIC AROMATIC HYDROCARBONS (PAH) (*) The results are reported in these table, the concentration is in ppm (mg/kg).

6 Compound Category 1 Unit Measured value Materials which are intended to be put in the mouth or materials contained in toys with intended and long-term skin contact (longer than 30 s) Benzo[a]pyrene < 0.1 < 0.2 Benzo[e]pyrene < 0.1 < 0.2 Benzo[a]anthracene < 0.1 < 0.2 Benzo[b]fluoranthene < 0.1 < 0.2 Benzo[j]fluoranthene < 0.1 < 0.2 Benzo[k]fluoranthene < 0.1 < 0.2 Chrysene < 0.1 < 0.2 Dibenzo[a,h]anthracene < 0.1 < 0.2 Benzo[ghi]perylene mg/kg < 0.1 < 0.2 lndeno[1 2,3-cd]pyrene < 0.1 < 0.2 Acenaphthylene, Acenaphthene, Fluorene, Phenanthrene, Pyrene, Anthracene, Fluoranthene < 0.1 < 1 Total Naphthalene < 0.1 < 1 Total 18 PAH < 0.1 <1 5) SPECIFIC MIGRATION OF TETRAFLUOROETHYLENE Food simulant: Acetic acid in aqueous solution 3% w/v Contact condition: 2 hours at 100 C rep. contact measured value average value Extended uncertainty limit value 21/03/3) --- 0.05

Food simulant: Rectified olive oil Contact condition: 2 hours at 15 C rep. contact measured value average value Extended uncertainty limit value 21/03/3) --- 0.05 CONCLUSIONS In the chosen test condition the samples are suitable to be used in contact with aqueous, acidic, alcoholic and oily or fatty foodstuffs for which simulants A, B, C and D are used. The sample tested by this Laboratory are therefore suitable to come in contact with foodstuff mentioned above on condition that they have been produced employing the monomers, additives and technical support agents according to in force legislation, specific migrations are respected and they do not induce any organoleptic modification on foodstuff. Date Division Head Managing Director 12/11/2015 Alberto Taffurelli Raoul Gatti