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Microplastic research in the Republic of Korea
Joint NOWPAP-TEMM Workshop on Marine Litter Management Toyama, Japan
2017.9.19
Sang Hee Honga,b*, Won Joon Shima,b
aOil and POPs Research Group, Korea Institute of Ocean Science and Technology bDepartment of Marine Environmental Sciences, Korea University of Science
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Paradigm Shift : fate and effect of marine debris
Mega Macro Meso Micro Nano
Hippo Dog Ant Dust mite Virus
Increasing …
Numbers Bioavailability Target organisms Toxicity Detection difficulty Cleanup difficulty
Decreasing …
Volume Entanglement Settling velocity
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Why microplastics? Increasing trend
(Thompson et al., 2004, Science; Classens et al., 2011, MPB) Ubiquitous from coast to Arctic
(Browne et al., 2011, ES&T; Hidalgo-Ruz et al., 2012)
Ingestion by small organisms (Boerger et al., 2010, MPB; Davison and Asch, 2011, MEPS)
Toxicity of microplastics (Browne et al., 2008, ES&T; Lee et al., 2013, ES&T)
Transporting media of pollutants (Tueten et al., 2009, Phil. Trans R. Soc.)
Nanoplastics by weathering (Shim et al., 2014, SETAC)
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Input source and pathway?
Toxicity?
Chemicals?
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Need to fill the knowledge gap
Growing need to conduct scientific research and monitoring
Is marine debris (microplastics) a ‘serious problem’ or a ‘red herring’?
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Research project: Assessment of environmental risk of microplastics in the marine environment (2015-2020)
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What are the exposure levels in the environment?
What are the effects at different exposure levels?
What are potential environmental effects of microplastics?
What are the ecological risk of microplastics?
Microplastics
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Targets for the assessment
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Microplastics
Chemical Cocktails
Associated Chemicals +
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Main research content
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Development of techniques for the assessment of microplastic pollution and biological effects
Assessment of microplastic pollution in the marine environment [water column, sediment, and biota / chemicals in microplastics]
Assessment of input pathway and transportation of microplastics [rivers, sewage treatment plants / weathering and fragmentation / transportation]
Assessment of effects of microplastics on marine organism [laboratory and field / MP, MP + chemicals]
Assessment of ecological risk of microplastics in the marine environment
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Monitoring and assessment protocols of floating microplastics
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-LMT (d=1.6 g/ml)
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Incheon / Gyunggi Bay
Youngil Bay
2016 (n=10)
2017 (n=10)
Surface water sampling with a Manta trawl net (330 µm)
Vertical (surface, middle and bottom water) sampling with a Hand net (20 µm)
Monitoring of floating microplastics (2012-2017) 2018-2020
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Microplastics Large MP (1-5 mm)
Small MP (< 1 mm)
Large MP (1-5 mm) and Mesoplastics (5-25 mm)
Fragment
Paint chip
Fiber
EPS
Sphere
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Horizontal and vertical distribution of MP (>20 µm) in Korean coastal water
Station
IC CS HP DR GY BS
Parti
cles
/m3
0
1000
2000
3000
4000
5000
6000Surface Middle Bottom
a
a
a a*
a
a b
b
b b b b
b* b*
b
b b
b
Duncan’s multiple-range test(p<0.05) * Kruskal-Wallis test(p<0.05)
0.2 0.2 0.2 0.2 0.2 0.2 6.1 19 9.9 19 4.5 8.5 6 11 9.6 18 8.3 19 Mean depth (m) Mean depth (m)
Particles/m3
0 1000 2000 3000 4000 5000 6000
Dep
th (m
)
0
2
4
6
8
10
12
14
16
18
20
22
24
26
28
30
32
34
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Size distribution of MP (>20 µm) in Korean coastal water
Size (m)
0 100 200 300 400 500 600 700 800 900 1000 1100 1200 1300 1400 1500 1600 1700 1800 1900 2000 2100
Ab
un
dan
ce (
par
ticl
es/m
3 )
0
5000
10000
15000
20000
25000
30000
35000
Size (m)
0 100 200 300 400 500 600 700 800 900 1000 1100 1200 1300 1400 1500 1600 1700 1800 1900 2000 2100
Abu
ndan
ce (p
artic
les/
m3 )
0
500
1000
1500
2000
2500
3000
Fragment
Fiber
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Sediment sample
1st Density separation
Sieving
Wet peroxide Oxidation (WPO)
2nd Density separation
Filtration
Analysis
Visual sorting - 1-5 mm
Pooling (<1 mm) - Composite sample - Total 2 L (160 ml/quadrat)
- Lithium metatungstate (LMT) - 500 ml sample + 1 L LMT
- Polycarbonate; 1 ㎛; 47 ㎜Φ
- LMT
FT-IR microscope
- ATR/microscope - Thermo Nicolet 6700 - 128 scans; 650-4000 𝒄𝒄𝒄𝒄−𝟏𝟏 - Resolution: 8 𝒄𝒄𝒄𝒄−𝟏𝟏
- Fe(Ⅱ), H₂O₂
Monitoring and assessment protocols of microplastics in sediment
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1mm < s < 5mm: Large-microplastics (L-MPs)
size < 1mm: Small-microplastics (S-MPs)
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Sediment sample
Sieving
L-MP (1-5 mm) pooling
S-MP (< 1 mm) pooling
0.5 m
0.5
m
Depth 2.5 cm
Monitoring of microplastics along the shoreline
Backshore (B)
Strandline (S)
Middle line (M)
Water edge (W)
Vegetation or artificial structure 100 m
25 m
wet sand
Sea
South Korea
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Tukey HSD p>0.05
t-test p>0.01
Tukey HSD p>0.05
L-MP (1-5 mm)
S-MP (0.02-1 mm)
East vs South vs West shore
L-MP vs S-MP
East vs South vs West shore
x53
Abundance of MP on sand beach
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1 to 5mm < 1 mm
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Non-target screening of marine plastic debris
Non-target Screening
Analysis
Identification of chemicals included in
plastic debris
Selection of Target Plastic Items
Food(18) ,Fisheries(17), Construction(2),Genera(12),Paint chip(5)
Antioxidant Plasticizer UV stabilizer Flame retardant Fatty acid Pesticide Lubricant Intermediate Toxin etc.
More than 200 chemicals EPS XPS
Flame retardants Anti-oxidant Fatty acids Toxin
PE Plasticizer UV-stabilizer
UV-stabilizer Anti-oxidant PlasticizerPP
PPPE
UV-stabilizer Flame retardants
Antioxidant UV-stabilizerAcrylic
Styrene
Rani et al. (2015) Arch Environ Contamin Toxicol 69: 352 16
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Quantitative analysis of chemicals in plastic samples
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Plasticizers, UV stabilizers Antioxidants,
HBCDs
PCBs, OCPs, PBDEs, PAHs
1mm < size < 5mm
Extraction (Soaking)
LC-TOF/MS LC-MS/MS
Extraction (Soaking)
Si/Al cleanup
GPC cleanup
GC-HRMS (EI) GC-MS(EI)(PAHs)
GC-MS (NCI) (PBDEs)
Surrogate standard
Internal standard Internal standard
Surrogate standard
Filtration (0.20 ㎛)
Concentration
< 1mm Size > 5 cm
Microplastic Sampling
Fragment, Fiber, EPS, Pellet, Film
Grinding
Polymer Identification
Film
EPS
Pellet Fiber
Fragment
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Antioxidants and UV stabilizers in plastic debris
Rani et al. (2017) Sci. Total Environ. 579: 745
Irg1076 Irg1010 BHT 2,4-DTBP UV320 UV326 UV327 UV328
Cne
w p
last
ic /
Cm
arin
e de
bris
0.0001
0.001
0.01
0.1
1
10
100
1000
10000
100000
Irganox1076
Irganox1010
2,4-DTBP
1 2 3 4 5 6 7
8 9 10 11 12 13 14 15
16 17 18 19 20 21 22
23 24 25 26 27 28 29 30
new vs debris
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A brominated flame retardant (HBCD) in EPS debris
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HBCDs concentraion (g/g)
0 5 10 15 20 25 1500 3000 4500 6000 7500 9000
USA (Alaska)
Peru
Canada
USA (California)
South Korea
Japan
Bangladesh
USA (Hawaii)
Thailand
Taiwan
Hong Kong
Brunei
Singapore
Vietnam
Sri Lanka 0.05
0.10
0.17
0.23
a)
Jang et al. (2017) Environ. Pollut. 231: 785
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From Scientific Findings to Policy change
SubstrateEPS HDPE Metal Rock
HB
CD
s in
mus
sel
0
50
100
2000
6000
10000(ng/g l.w.)
Br
BrBr
BrBr
Br
Br
BrBr
Br
Br
Br
High contamination of styrofoam MP Inclusion of hazardous chemical
Rapid fragmentation to microplastics Ingestion by marine organisms and chemical transfer
Jang et al. (2016) Environ. Sci. Technol. Song et al. (2017) Environ. Sci. Technol.
Rani et al. (2014) Chemosphere
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13%
Fishing rope8%
Glass bottle
7%
Plastic bag7%
Plastic food wrapper
6%Plastic cap/lid
5%Plastic bottle
5%
Strip5%
Other plastics
4%
Timble3%
Others37%
93%
5% 1% 1%
EPS particle
Pellet OthersFragment
> 2.5cm 1<s<5mm
EPSbuoy
Lee et al. (2013) Mar. Pollut. Bull.
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Weight of cost and benefits
Polluting beaches Aesthetical effects
Very cheap Easy to handle High buoyancy Styrofoam industry
Benefits of styrofoam buoy Cost of styrofoam buoy
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>90% in mesoplastics Rapid fragmentation Leaching HBCDs Ingestion by organisms
Polluting beaches Aesthetical effects
Increasing cost Easy to handle High buoyancy Effects on EPS industry
Replace EPS to alternative buoy (Government support 40% of price) Increase recovery rate of the used buoy (10% →30%) Regulate HBCD use in EPS buoy from 2017 Development of alternative buoy
Benefits of styrofoam buoy Cost of styrofoam buoy
Policy changed
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Acknowledgement
Thank you!