Microplastics extraction from a sandy beach: methodology development - - PowerPoint PPT Presentation

microplastics extraction from a sandy beach methodology
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Microplastics extraction from a sandy beach: methodology development - - PowerPoint PPT Presentation

7 th International Conference on Sustainable Solid Waste Management Microplastics extraction from a sandy beach: methodology development and challenges D. Couceiro 1 , V. Oliveira 1,2 , D. T obaldi 2 , A. Branha 1,3 & C. Dias- Ferreira 1,4 1


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SLIDE 1

Microplastics extraction from a sandy beach: methodology development and challenges

  • D. Couceiro1, V. Oliveira1,2, D. T
  • baldi2, A. Branha1,3 & C. Dias-

Ferreira1,4

1CERNAS & Polytechnic Institute of Coimbra, Coimbra, Portugal 2CICECO, University of Aveiro, Aveiro, Portugal 3University of Santiago de Compostela, Galicia, Spain 4Universidade Aberta, Lisbon, Portugal

7th International Conference

  • n

Sustainable Solid Waste Management

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SLIDE 2

Worldwide plastic production

2

World plastic production almost reached 350 M t China is the largest producer of plastics

Europe 18.5% Asia 50.1 % CIS 2.6% NAFT A 17.7 %

Latin Ameri ca 4% Middl e East, Africa 7.1%

3.9% Japan 16.8% Rest

  • f Asia

29.4% China

64.4 million t 60 million t

2017 2016

335 million t 348 million t

2016 2017

WORL D

Source: PlasticEurope, 2018 Source: PlasticEurope, 2018

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SLIDE 3

Microplastics

  • Small plastic pieces smaller than 5 mm in size
  • Majority of items in the contaminated aquatic

ecosystems

  • Spherical beads, fjlms, irregular fragments,

fjlaments, foam, granules and fjbres

  • Poses a threat to aquatic life:

sorbent of toxic pollutants like HM or PCBs persistent bioaccumulation Entering the food chain by ingestion by marine species

3

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SLIDE 4

Microplastics

  • The Marine Strategy Framework Directive was amended to

highlight that the “composition of micro-particles (in particular microplastics) has to be characterized in marine litter and the marine coastal environment”.

  • There are still no harmonised analytical methods for

quantifying and determining the occurrence and composition of microplastics in those environments.

4

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SLIDE 5

Objectives

1 - Development of an extraction technique for separating microplastics (PP , LDPE, PS, PET and PVC) from a sandy beach by using routine laboratory equipment

  • using the principle of fmotation and decantation process to promote the

separation

2 - Assessment of the recovery effjciency of the proposed method for:

i) each microplastic material ii) microplastics fractions by size

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SLIDE 6

Preparation of microplastics samples

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Cutting (≈3 cm size) Groundin g in a mill Sieving (2, 1, 0.5, 0.2 and 0.05 mm) PV C P P

PP (polyproprylene), LDPE (low-density polyethylene), PS (polystyrene), PET (polyethylene terephthalate), PVC (polyvinyl chloride)

PE T LDP E PS

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SLIDE 7

Preparation of microplastics samples

PP (polyproprylene), LDPE (low-density polyethylene), PS (polystyrene), PET (polyethylene terephthalate), PVC (polyvinyl chloride)

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Size Plastic material used in spiked samples (g) PP LDPE PS PET PVC > 2 mm 2.5 2.5 2.5 2.5 2.5 2 – 1 mm 2.5 2.5 2.5 2.5 2.5 1 – 0.5 mm 2.5 1.0 2.5 2.5 2.5 0.5 – 0.2 mm 1.5 0.5 2.5 2.5 1.5 0.2 – 0.05 mm 0.5 0.0 1.0 0.5 0.0 T

  • tal (g)

9.5 6.5 11.0 10.5 9.0

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SLIDE 8

Sampling of sandy beach

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3 kg of sandy beach Dried (105°C) and sieved (2, 1, 0.5, 0.2 and 0.05mm)

Figueira da Foz, Coimbra, Portugal 2-1 mm: ≈2% 1-0.5 mm: 63% 0.5-0.2 mm: 35%

Washing of plastics out of the sand:

i) Stirring: sand + ZnCl2 ii) Supernatant was discarded (2x) iii) Rising with 0.001 M HCl

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SLIDE 9

Extraction method

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150 g of sand + microplastics + 250mL of ZnCl2 Pumping of 600 mL of ZnCl2, creating an

  • verfmow of the

top layer Sieving of supernatant (0.05 mm) Microplasti cs in the 0.05mm sieve Sand +

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SLIDE 10

Extraction method

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Microplastics in the sieve Rising (0.001M HCl) Drying (at 60°C, 48h) Sieving (2, 1, 0.5, 0.2 and 0.05mm) Weighing

Recovery effjciencies for the 1st fmotation procedure

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SLIDE 11

Extraction method

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+ 250mL of ZnCl2 Pumping of 600 mL of ZnCl2, creating an

  • verfmow of the

top layer Sieving of supernatant (0.05 mm) Microplasti cs in the 0.05mm sieve Sand Sand +

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SLIDE 12

Extraction method

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Microplastics in the sieve Rising (0.001M HCl) Drying (at 60°C) Sieving (2, 1, 0.5, 0.2 and 0.05mm) Weighing

Recovery effjciencies for the 2nd fmotation procedure

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SLIDE 13

Extraction method

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Sand Washed (0.001M HCl) Drying (at 105°C, 48h) Stored

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SLIDE 14

Recovery effjciencies of the proposed methodology - calculation

R

  • 14
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SLIDE 15

Overall recovery rates

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  • Range from 97 -

100%

  • > 94% of

microplastics were extracted in the 1st time fmotation

  • PS and PP registered a

slightly lower rate than LDPE, PET, and PVC (2-3%)

  • 2nd time fmotation can

be eliminated

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SLIDE 16

Recovery rates for microplastics with difgerent size

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  • Ranged from 51 ± 8 -

133 ± 1%

  • Microplastics fraction
  • 0.05-0.2mm displayed

the lowest recovery rates

  • PVC fraction 0.5-1mm

showed a very high recovery rate (≈133%)

0,05 - 0,2 0,2 - 0,5 0,5 - 1 1 - 2 > 2

20 40 60 80 100 120 140 PP LDPE PS PET PVC Particle size (mm) R ecovery rates (% )

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SLIDE 17

Challenges to overcome

  • Fibres contamination

from the working space

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Performing of blanks to quantify the impact of it on the overestimation of recovery rates

  • Presence of sand

grains and unknown fragments in the extracted microplastics

Cleaning procedure of extracted microplastics:

  • Stirring of the mixture of extracted

microplastics with ZnCl2

  • Sieving and rising with 0.001M HCl
  • Manual sieving of microplastics can

cause an over or underestimation of microplastics mass Automatic sieved to guaranty the same sample size

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SLIDE 18

Conclusions

  • The good recoveries rates
  • btained demonstrate the potential
  • f the proposed extraction

methodology

  • There are a few problems that need

to be addressed in further works

  • This analytical extraction method

can contribute to boosting advancements for determining the occurrence of microplastics in marine sediments.

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  • Application of the proposed

methodology to beach samples from Angola

  • Using of Fourier

Transformed Infrared spectroscopy (FT

  • IR) for

identifjcation of microplastics material

Further works

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SLIDE 19

Thank you for your attention.

veronica.oliveira@esac.pt

  • V. Oliveira gratefully acknowledges FCT – Fundação para a Ciência

e a T ecnologia (SFRH/BD/115312/2016) and CERNAS for fjnancial support (UID/AMB/00681/2013).

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