Speciation analysis of trace elements in food and feed - status and future developments. Jens J. Sloth

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Transcription:

Speciation analysis of trace elements in food and feed - status and future developments Jens J. Sloth National Food Institute (DTU Food) Technical University of Denmark

- 1. Arsenic speciation analysis (importance of inorganic arsenic) - 2. Organotin n speciation analysis (food contact materials) - 3. Selenium speciation analysis (food fraud!) -...and...and a little bit of nano!

Foodstuffs MLs for Pb, Cd, Hg and Sn EU directive 2006/1881/EC Animal feedingstuffs MLs for As, Pb, Cd and Hg EU directive 2002/32/EC Only maximum levels for TOTAL CONCENTRATION of the metals

Example arsenic speciation Important for correct risk assessment 4 ~ 40 250 µg inorg As <10 µg inorg As 1 kg rice => 50-300 µg As 1 kg fish => 3000-10000 µg As There is most focus on rice from a food safety point of view why??? The chemical form of arsenic is important => Arsenic speciation

EFSA (2009) and JECFA (2010) opinions on arsenic in food Old PTWI value (WHO, 1988) was withdrawn (15 µg/kg bw/week) NEW! BMDL 1.0 = 0.3 8 µg/kg bw per day for inorganic arsenic => EU dietary exposures within this range for average and high level consumers => Risk to some consumers cannot be excluded NEW! BMDL 0.5 = 3 µg/kg bw per day for inorganic arsenic => 0.5% increased incidence of lung cancer for 12 y exposure there is a need to produce speciation data for different food commodities to support dietary exposure assessment more accurate information on the inorganic arsenic content of foods is needed to improve assessments of dietary exposures to inorganic arsenic need for validated methods for selective determination of inorganic arsenic in food matrices

Inorganic arsenic in wild caught fish => no concern Norwegian survey 900 individual fish samples Atlantic halibut Cod Greenland halibut Mackerel Herring Tusk Results Total arsenic..0.3-110 mg/kg Inorganic arsenic. < 0.01 mg/kg (only 37 samples > LOQ) Julshamn and Sloth, 2011, in prep

...but in bivalves high contents in some samples... Inorganic As / mg kg -1 7 6 5 4 3 2 1 Total As = 13.8 mg/kg Inorg As = 5.8 mg/kg Fraction = 42 % y = 0.51x - 1.51 R 2 = 0.9146 Data from 175 blue mussel (Mytilus edulis) samples collected along the Norwegian Coastline. 0 0 2 4 6 8 10 12 14 16 Total As / mg kg -1 NORWAY Sloth and Julshamn, 2008, J. Agri.Food Chem., 56, 1269-1273

Arsenic in rice products DK - survey ias vs total As 0,600 0,500 y = 0,8233x - 0,0099 R² = 0,863 Uorganisk As (mg/kg) 0,400 0,300 0,200 0,100 0,000 Chinese max level 0,15 mg/kg ias vs total As Lineær (ias vs total As) 0,00 0,10 0,20 0,30 0,40 0,50 0,60 0,70 Total As (mg/kg) 105 samples -white rice -brown rice -red rice -black rice -rice crackers 33 samples > 0,15 mg/kg -2 parboiled (20%) -4 brown (50%) -4 red (50%) -5 black (71%) -1 Basmati (10%) -1 Pudding rice (9%) -1 wild rice (20%) -15 rice crackers (100%) Sloth et al, in prep

Arsenic in rice products DK - survey ias vs total As 0,600 0,500 y = 0,8233x - 0,0099 R² = 0,863 Uorganisk As (mg/kg) 0,400 0,300 0,200 0,100 0,000 Future EU max level 0,2 mg/kg?? ias vs total As Lineær (ias vs total As) 0,00 0,10 0,20 0,30 0,40 0,50 0,60 0,70 Total As (mg/kg) 105 samples -white rice -brown rice -red rice -black rice -rice crackers 22 samples > 0,2 mg/kg -1 parboiled (10%) -1 brown (12%) -3 red (37%) -2 black (28%) -0 Basmati (0%) -0 Pudding rice (0%) -0 wild rice (0%) -15 rice crackers (100%) Rice cracker mean: 0.31 mg/kg intake 50 g/dag => 15 µg ias (~1 µg/kg bw @15 kg bw) > EFSA BMDL 01 0.3-8 µg/kg bw/dag? Sloth et al, in prep

Inorganic arsenic in chinese food supplements Name of Food supplement Total Arsenic ( g/g) Inorganic arsenic g/g ) Xiao Yao Wan 0.82 0.85 Bu Zhong Yi Qi Wan 0.62 0.50 Da Bu Yin Wan 0.59 0.55 Six Flavor teapills 0.72 N.D. Golden Book Teapills 0.58 0.57 Xiang Sha Liu Jun Zi Wan 0.94 0.80 Gan Mao Ling Ling 1.24 1.01 Chuan Xin Lian 5.00 3.17 Bi Yan Pian 0.70 0.58 Arouse power 1.12 1.02 Bio Chlorella 0.62 0.21 Unik Spirulina Kapsler 2.59 0.13 Chlorella 0.58 0.03 Ez-Biloba 0.63 0.67 Qvinde Dong Quai 0.68 0.48 Gan Mao Ling (against flu and common cold) Rec dose: 18 pills per day ias ~ 13 µg/day 0.22 µg/kg bw/day (@60 kg) Close to EFSA BMDL 01!! Hedegaard and Sloth, in prep

Inorganic As in SRM NIST1586a literature data Mean = 0.097 mg/kg Extraction solution Detection ias (μg/kg) Reference 1 2M TFA LC-ICPMS 87 +/- 9 Ackermann (2005) 2 Enzymatic, pepsin and pancreatin LC-ICPMS 101 +/- 7 Ackermann (2005) 3 2M TFA LC-ICPMS 92 +/- 2 Heitkemper (2001) 4 2M TFA LC-ICPMS 80 +/- 16 Williams (2005) 5 2M TFA LC-ICPMS 100 +/- 10 Williams (2006) 6 MeOH:H2O LC-ICPMS 109 +/- 3 D'Amato (2004) 7 Enzymatic, alfa-amylase LC-ICPMS 106 +/- 7 Kohlmeyer (2003) 8 Enzymatic, protease and alfa-amylase LC-ICPMS 88 +/- 6 Sanz (2005) 9 1M H3PO4 HG-AFS 102 +/- 2 Matosreyes (2007) 10 1% HNO3 LC-ICPMS 99 +/- 4 Raab (2009) 11 1% HNO3 LC-ICPMS 99 +/- - Sun (2008) 12 1% HNO3 LC-ICPMS 110 +/- 10 Sun (2009) 13 0,5 M TFA LC-ICPMS 77 +/- - Heitkemper (2009) 14 enzymatic, proteas and alfa-amylase LC-ICPMS 96 +/- 9 Mar (2009) 15 2M TFA LC-ICPMS 100 +/- 12 Meharg (2008) 16 water LC-ICPMS 96 +/- 3 Narukawa (2008) 17 0,07M HCL and 10%H2O2 LC-ICPMS 103 +/- 15 DTU Food (2009)

Animal feedingstuffs Commission directive 2009/114/EC (amendment) Max levels for undesirable substances in animal feed Only max levels for total arsenic FOOTNOTE Inorganic arsenic lower than 2 ppm

SPE-HG-AAS a speciation alternative µ-wave extraction Separation by SPE Detection by HG-AAS conditioning load wash elute Sequential elution for selective off-line separation of inorg As from organo As species by SPE OrganoAs compounds Rasmussen & Sloth, in prep Abundance 75000 70000 65000 60000 55000 50000 Inorganic As Time--> 45000 40000 35000 30000 25000 20000 15000 10000 5000 0 Sample load OrganoAs Ion 75.00 (74.70 to 75.70): 53.D Ion 75.00 (74.70 to 75.70): 54.D (*) Ion 75.00 (74.70 to 75.70): 63.D (*) Ion 75.00 (74.70 to 75.70): 64.D (*) Wash HPLC-ICPMS of SPE fractions Sample eluate inorganic As 0.50 1.00 1.50 2.00 2.50 3.00 3.50 4.00 4.50 5.00 5.50 6.00 6.50

SPE-HG-AAS µ-wave extraction Separation by SPE Detection by HG- AAS In-house validation data Parameter Result Analysis time 2 x 7 h for 24 samples LoD (mg/kg) 0.08 LoQ (mg/kg) 0.16 Repeatability (%RSD) 3-7 Accuracy (%) 90-104 Collaborative trial in marine feed material 10 labs provided results Method working range tested: 0.1 2.6 mg Kg -1 HorRat values <2 in the working range tested The method is fit for purpose Final publication as EN expected July 2012

Agriculture Antifoulings Industry Used in - Agriculture - Antifoulings - Industry - PVC-Materials TDI: 0.25 µg/kg bw/day Seafood Food, beverage Water Tap water pipes Sediment Seafood Household commodities Hoch, Appl. Geochem., 2001, 719-43 TBT, DBT, TPhT and DOT PVC-Materials

Legislation on OTCs in Food Contact Materials Compounds Maximum level (µg Sn/kg foodstuff) DBT, TBT, TPhT and DOT 40 (6) MMT, DMT 180 MOT 1200 MDDT 12000 (50) Assumptions: - 1 kg food per 6 dm 2-100 ml in contact with 0.6 dm 2 DDDT 24000 (50) Ref: EFSA (2005); proposed EFSA values in parenthesis - Max levels on organotin migrating from the packaging material - Testing by the use of food simulators (water, acid, oil, alcohol etc) - BUT no maximum levels on organotins in the foodstuff itself!! FCM Foodstuff migration

Organotin migration from Food Contact Materials II Small scale survey on 33 FCMs Baking paper, PVC cling films, silicone baking forms, lids with PVC gaskets PUR-agglomerated cork wine stoppers Abundance Time--> 8500 8000 7500 7000 6500 6000 5500 5000 4500 4000 3500 3000 2500 2000 1500 1000 500 0 Inorg Sn 4.07 IS TIC: 014SMPL.D 5.77 6.46 DBT Abundance 2.00 4.00 6.00 8.00 10.00 12.00 14.00 16.00 Output of DK survey: -33 samples -11 contained OT (mainly DBT) 4000 3500 3000 2500 2000 1500 1000-3 exceeded EFSA guideline limit 500 PVC lid 3% acetic acid Overlaid standard and sample DBT concentration: 9.9 µg/kg TIC: 005SMPL.D TIC: 014SMPL.D DBT > EFSA guideline value of 6 µg/kg Time--> 0 6.306.326.346.366.386.406.426.446.466.486.506.526.546.566.586.60 Sloth et al, in prep

Selenium in commercial food supplements Is the selenium source declared correctly??

Se speciation by HPLC-ICPMS Supplement declared as organic bound Selenium (125 µg/tablet) Se(IV) Signal Intensity / counts s-1 Organic Se Se(VI) Time / sec Larsen et al, unpublished data

Speciation summary speciation methods are more and more commonly used instrumentation is widely available legislation on species has started and more is expected in the future! standardised methods are not ready! but the need is known by authorities legislation is still behind! Lack of CRMs (e.g. for ias)

Perspective trace elements in nanoform NanoLyse Project "Nanoparticles in Food: Analytical methods for detection and characterisation" Validated methods for the determination of inorganic ENP in food extracts, based on size separation, size determination and specific detection silver nanoparticles in lean meat silica nanoparticles in tomato soup http://www.nanolyse.eu

DTU Food Analytical platform: AF4-MALS/DLS-ICP-MS 100000 138 Ba 90 Zr 140 Ce asymmetric flow field flow fractionation (AF4) particle separation according to their size (1nm few µm) optical detection multi angle (MALS) and dynamic light scattering (DLS), UVvis absorption and fluorescence particle detection size determination 0 0 50 90 130 170 210 250 m/z inductively coupled plasma mass spectrometry (ICP-MS) elemental detection chemical identity quantification Fractogram => www.nanolyse.eu Schmidt et al, Anal Chem, 83, 2461-2468 (2011)

Acknowledgements and funding sources Coworkers: Rie R. Rasmussen, Rikke V. Hedegaard, Bjørn Schmidt, Xenia T. Trier, Katrin Löschner and Erik H. Larsen Inge Rokkjær, Gudrun Hilbert and Dorthe L. Cederberg Kåre Julshamn and A.K. Lundebye Fernando Correiro-Raposo, Håkan Emteborg and Beatriz de la Calle Funding sources: European Community's Seventh Framework Programme European Committee for standardisation (CEN) Danish Food Administration (DFVA) Thanks for your attention!