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MICROPLASTIC IN ENVIRONMENTAL SAMPLES: QUANTITATIVE DETERMINATION AND METROLOGICAL TRACEABILITY
ULRIKE BRAUN1, ROLAND BECKER1
CLAUS G. BANNICK2
RAINER STOSCH3
1 Bundesanstalt für Materialforschung und –prüfung (BAM)2 Umweltbundesamt (UBA)3 Physikalisch-Technische Bundesanstalt (PTB)
1st December 2015
Facts Microplastics (MP)
10 mm
• Increasing plastic production (300 mio t/a): founds in environment nearly everywhere
• Microplastics (few µm up to 5mm) • Primary microplastic: cosmetics, technical abrasives (~ 0,5 kilo t/a)
• Secondary microplastic: degradated polymers by UV, O2, mechanics (~ 8-10 mio t/a)
22015-12-01 EMPIR Workshop, Turin, Italy
MP Particles: Possible Risks
• Release of toxic decomposition products to environment during degradation (decomposition products of polymer, additives)
• Adsorption of persistent pollutants, ingestion to animals and accumulation of pollution in food chain
• Carrier for vectors of different biologic species
No verified data exist about the kind and amount, the source and the fate as well as the behaviour of microplastic particles in the
environment.
32015-12-01 EMPIR Workshop, Turin, Italy
Analytic problem: a few synthetic polymer particles with different material characteristics (density, solubility) beside many natural,
macromolecular particles in various environmental matrices
MP Particles in Environment: Analysis
4
• Harmonized sampling /sample preparation from various environmental matrices (water, soil, biota).
• Routine analysis for identification, quantitative determination and metrological traceability.
• Assessment of risks (persistent pollutants, microbiology).
2015-12-01 EMPIR Workshop, Turin, Italy
MP Particles in Environment: Analysis
5
• Routine analysis for identification, quantitative determination and metrological traceability.
2015-12-01 EMPIR Workshop, Turin, Italy
Raman Spectroscopy MappingExample: Sand + 2wt% PE, laser wavelength 488 nm
Mapping 472 cm-1Mapping 2888 cm-1
Spectra PE Spectra sand
62015-12-01 EMPIR Workshop, Turin, Italy
Raman Mapping Quantification
7
traceability to length (m)metrological AFM (PTB)
fcal,x/y
surface coverage:(x ± Ux) % px , py: structure period
2 µmpy
px
PTB Raman calibration standard
Raman mapping of calibrated„chessboard“ pattern
2015-12-01 EMPIR Workshop, Turin, Italy
Conclusion Raman Mapping
8
• Certain identification is possible, determination of particle sizes (microbiologic interaction).
• Non destructive method.
• Major disadvantage: fluorescence of matrix and high resolution /black matrix can lead to the melting of polymers.
• Automatisation by use of calibration standard and quantitative result.
2015-12-01 EMPIR Workshop, Turin, Italy
10 mm
Thermo-Analytic MethodsAssessment of a new method for the analysis of decomposition gases of polymers by a combining thermogravimetric solid-phase extraction and thermal desorption gas chromatography mass spectrometry, E. Duemichen, U. Braun, R. Senz, G. Fabian, H. Sturm, Journal of Chromatography A 2014, 1354, 117-128.
Adsorber (Twister)
Macroscopic sampling
9
TDS-GC-MS Analysis
• Characteristic decomposition products of polymers
• Identification via „fingerprint“ or spectra libraries
2015-12-01 EMPIR Workshop, Turin, Italy
10 12 14 16 18 20 22 24 26 28 30 32 34
14.6 14.7 17.4 20.0 22.4 22.6 25.0 27.2 29.3 31.3 31.4
PE
Suspended solids
Soil
Mussel
m/z = 55
Abu
ndan
ce
Retention time / min
PE
Suspended solids
Soil
Musselm/z = 55
6
912
15
1821
243
PE in Environmental SamplesAnalysis of polyethylene microplastics in environmental samples, using a thermal decomposition method, E. Dümichen, A.-K. Barthel, U. Braun, C. G. Bannick, K. Brand, M. Jekel, R. Senz Water Research Vol. 85, 2015, 451–457.
10
Retention time / min
Abu
ndan
ce
20 21 22 23 24 25 26
LD-PE
1,15-Hexadecadiene1-HexadeceneHexadecane
1,14-Pentadecadiene1-PentadecenePentadecane
HD-PE
new PE Microscrub
PE Microscrub after H2O2 treatment
Abu
ndan
ce
Retention time / min
PE after oxidativestorage (autoclave)
1,13-Tetradecadiene1-TetradeceneTetradecane
*
*
*
*
2015-12-01 EMPIR Workshop, Turin, Italy
• Certain identification of PE in sample
• Identification of polymers in environmental samples (PE, PP)
• Quantification (bulk method) is possible by use of calibration standards.
• Major disadvantages: destructive method, no information about particle contribution
• Improvement of method, automatisation, limit of detection.
Conclusion Thermo-Analytic Methods
112015-12-01 EMPIR Workshop, Turin, Italy
• Standardisation of methods for microplastic analysis in environmental samples: Raman Mapping, Thermo-analytic methods, ...
• Assessment of metrological traceability.
• Development and provision of reference materials.
Possible objective for a project contribution
122015-12-01 EMPIR Workshop, Turin, Italy
13
Thank you