EMENDA SEMBIRING, ST., MT., M.Eng.Sc., Ph.D
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Transcript of EMENDA SEMBIRING, ST., MT., M.Eng.Sc., Ph.D
TANTANGAN PENGELOLAAN MIKROPLASTIK DI MASA DEPAN
OLEH:
EMENDA SEMBIRING, ST., MT., M.Eng.Sc., Ph.DDisampaikan pada WEBINAR
PUSAT STUDI LINGKUNGAN HIDUP ITB
18 MEI 2020
APAKAH MIKROPLASTIK?
Mikroplastik adalah plastik yang berukuran < 5 mm.
Jenis mikroplastik:• Primer• Sekunder
Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh 2
Plastik berdasarkan ukuranMega-Plastik (> 100 mm)
Makro-Plastik (> 20 mm)
Meso-Plastik (20 -5 mm)
Mikro-Plastik (5 mm -1μm)
Nano-Plastik (< 1 μm)
3
( Sumber: Barnes et al, 2009, GESAMP, 2015, Plastics Europe, 2017)
Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh
< 5 mm
Mikroplastik Primer dan Sekunder
Synthetic polymers
(Thermoplastics & Thermosets)Synthesized
biomassSynthesized
fossil fuel
Macro-sized productsMicro-sized products
Primary microplastics
Secondary microplastics
Photo degradation
Thermal degradation
Thermo oxidation
Biodegradation
Hydrolysis
Fragmentation
(Andrady, 2011)
Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh 4
Sumber Mikroplastik
Mikroplastik Primer Mikroplastik Sekunder
• Pemupukanpolysulfone, polyacrylonitrile, cellulose acetate coating (Jarosiewicz & Tomaszewska, 2003)
• WWTP dan lumpur
700,000 microfibers / 6 kg wash in a domestic washing machine (Napper & Thompson, 2016)
• Gesekan Ban MobilCar tyres: 0.81 kg/capita/year styrene-1.3-butadiene rubber (SBR) (Kole et al. 2017)
Kosmetika dan toiletries
4594 – 94,500 PE microbeads from a single facial wash per year in UK (Napper et al. 2015)
Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh 5
Source and Fate of Microplastic in the Environment
Source: Grida.no
6Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh
Transport and Fate 8
Horton, et al. (2017) Science of the Total EnvironmentEmenda Sembiring, PhD/FTSL-ITB/Webinarpslh 7
MISMANAGED PLASTICSCoastal countries generated close to 275 million tons of plastic waste in 2010, and 4.8 to 12.7 million tons of the plastic made it way to the oceans (Jambeck et al. 2015)
8Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh
Others1.026 MMT
(18,2 %)
Raw material plastic5.635 MMT
Import1.67 MMT
(80% ASEAN)
Country Production2.31 MMT
PackagingStyroform 0.017 MMT
(0.3 %)
Shopping bag0.366 MMT
(6,5 %)
Building0.845 MMT
(15 %)
Packaging2.254 MMT
(40%)
Household1.127 MMT
(20%)
Country Capacity2.66 MMT
Recycle1.655 MMT
Plastic Waste1.692 MMT
(29.4 %)
Material still consuming 3.061 (53.2 %)
Finished GoodsPlastic Impor
0.12 MMT
MaterialRecycle
1.001 MMT(17.4%)
ManagedWaste
1.522 MMT
Non-ManageWaste Litter0.17 MMT
Carry overplastic waste before
0.654 MMT
Source: BPS and InaplasData 2016
MATERIAL FLOW OF PLASTICS IN INDONESIA
12Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh
Plastics Consumption Plastics Waste
36%Landfill
44%Burning,
Dumping to River, Disposal
20%Recycle
Source: Damanhuri, 2018
Indonesia Plastics Flow
13Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh
Keberadaan Mikroplastik di Sungai Citarum
Location Particles/m3
Situ Cisanti (Upstream) 0.029 0.023 0.0166
Oxbow (Middle) 15.71 14.92 4.13
Muara Gembong (Downstream) 0.094 0.12 0.053
MuaraGembong
Situ Cisanti
Oxbow, DayeuhKolot
15
Microplastic Impact on Biota and Food Web
Avio et al., 2015: MP’s accumulate in stomach and liver in mullet fish 17Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh
Humans Consuming Microplastics
Household Dust and Air
Contaminated sea food
Drinking Water
THROUGH
INHALATION
INGESTION
EXPOSURE PATHWAYS
TOXICOKINETICS
Adsorption
Distribution
Metabolism
Excretion
ACUTE
CHRONICS
POTENTIAL EXPOSURE PATHWAYS
Source: Ministry of Health, Indonesia18Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh
Kemungkinan Dampak Pada Kesehatan Manusia
150 μm1.5 μm
Human hairBacteria WBC
No absorption into body
Into cells & blood stream Into liver & kidneys
DNA damage (UNFAO, 2018 & Lusher et al, 2017)
3.7 L / day
16 p / day
5800 p / year
2.7 L / day
12 p / day
4400 p / year
(American Institute of Medicine, 2017)
Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh 19
Strategi Penanggulangan Sampah Plastik di IndonesiaKeputusan Presiden No 83/2018
20
1. BEHAVIORAL CHANGE
2. REDUCED LAND-BASED LEAKAGE
3. REDUCED SEA-BASED LEAKAGE
4. ENHANCED LAW ENFORCEMENT AND FINANCIAL
5. RESEARCH AND DEVELOPMENT
JUMLAH KEGIATAN
Sumber: Kemenkomar
Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh
Penyisihan Mikroplastik di unit Pengolahan Air
• Microplastics removal of rapid sand filter (0.39 mm and 0.68 mm silica sand) is considered tobe quite effective in removing microplastics greater than 200 μm (Fajar dkk, 2019).
• For filter cloth, the largest percentage of microplastic removal is shown in the 57.5 µm filter,which is 89.5%, while the lowest removal is shown in the 194 µm filter which is 25% (Mahapatidan Sembiring, 2019)
Process Removal of Plastic Flakes
(%)
Removal of Tire Flakes
(%)
Pre sedimentation 27.01 – 30.31 87.19 – 89
Sedimentation 29.01 – 29.03 27.60 – 39.55
Rapid Sand Filter
ES of 0.39 mm
96.4 – 99.2 77.8 – 95.5
ES of 0.68 mm
90.53 – 96.58 76.47 – 93.550
10
20
30
40
50
60
70
80
90
100
40 mesh 70 mesh 40 mesh 70 mesh 40 mesh 70 mesh
194 µm 115 µm 57.5 µm
mic
ro
pla
stic
rem
ov
al (
%)
microplastic removal (min) microplastic removal (max)
Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh 21
Pemodelan keberadaan Mikroplastik di Sumber air Bakuair Minum
Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh 22
Sumber: Penelitian Ramdhan dan Sembiring 2020 (on going)
NO. ADVANCEDTREATMENT
% REMOVAL OFMP
PERFORMANCE OF UNITRELATED TO MP REMOVAL
1MEMBRANEBIOREACTOR(MBR)
99,9%
MBR TREATS PRIMARY CLARIFIED WASTEWATER WITH MUCHHIGHER MP COMPARED TO SECONDARY EFFLUENT; HAD THESMALLEST PORE SIZE (0,4 M) OF FOR ALL THE STUDIEDFILTERS. THIS GIVING A HIGHER REMOVAL PERCENTAGE.
2 RAPID SANDFILTER (RSF) 97%
MPS ARE CAUGHT BETWEEN THE SAND GRAINS OR ADHEREDTO THE SURFACE OF THE SAND GRAINS. THE ADHESIONCOULD BE POSSIBLY FURTHER IMPROVED WITH COAGULANT.
3 DISSOLVED AIRFLOTATION (DAF) 95%
MICROPLASTICS ARE TRANSPORTED TO THE SURFACE OF THEFLOCS DUE TO THEIR BUOYANCY. AS FLOTATION ISPARTICULARLY DESIGNED TO REMOVE LOW-DENSITYPARTICLES, IT CAN BE EXPECTED TO EFFICIENTLY REMOVEPLASTICS.
4 DISC FILTER 40-98,5%
EXCESSIVE POLYMER ADDITION RESULTED IN MEMBRANEFOULING, LED TO ACCELERATED BACKWASH FREQUENCY. DURING THE HIGH-PRESSURE BACKWASH, PART OF MPSPROBABLY PASSED THE FILTER CLOTH TO FINAL EFFLUENT, HENCE LOWERING THE REMOVAL EFFICIENCY.
Source: Talvitie et al., 2017
Beberapa Perbandingan Penyisihan Mikroplastik di Unit PengolahanAir Limbah
Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh
23
Pollution and Human Exposure
inge
stio
n Marine
Terrestrial
Fresh water
24
Investigating Atmospheric Microplastic in Total Suspended Particulate (TSP):
Inha
latio
nAtmosphere
Found that there are significant amount of microplastics in Total Atmospheric Fallouts (TAF)
Only few studies have been recorded
Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh
Sumber: Yudison, dkk, 2019
Referensi• Alam, F.C., Sembiring, E., Muntalif, B.S., Suendo, V., 2019. Microplastic distribution in surface water and sediment
river around slum and industrial area (case study: Ciwalengke River, Majalaya district, Indonesia). Chemosphere 224, 637–645. https://doi.org/10.1016/j.chemosphere.2019.02.188
• Andrady, A.L., 2017. The plastic in microplastics: A review. Marine Pollution Bulletin 119, 12–22. https://doi.org/10.1016/j.marpolbul.2017.01.082
• Avio, C.G., Gorbi, S., Regoli, F., 2015. Experimental development of a new protocol for extraction and characterization of microplastics in fish tissues: First observations in commercial species from Adriatic Sea. Marine Environmental Research, Particles in the Oceans: Implication for a safe marine environment 111, 18–26. https://doi.org/10.1016/j.marenvres.2015.06.014
• Barnes, D. A., Galgani, G., Thompson, R. C., & Barlaz, M. (2009). Accumulation and fragmentation of plastic debris in global environments. Philosophical Transactions of the Royal Society of London. B, 364(1526), 1985-1998.
• Cordova, M.R., Purwiyanto, A.I.S., Suteja, Y., 2019. Abundance and characteristics of microplastics in the northern coastal waters of Surabaya, Indonesia. Marine Pollution Bulletin 142, 183–188. https://doi.org/10.1016/j.marpolbul.2019.03.040
• Cordova, M. R., Hadi T. A., and Prayudha, B. 2018. Occurrence and abundance of microplastics in coral reef sediment: a case study in Sekotong, Lombok-Indonesia. AES Bioflux, 10.
• Damanhuri, E. 2018. Paparan pada launching Danone- Aqua #bijak berplastik movement. • Ellen MacArthur Foundation. 2016. The New Plastic Economy: Rethinking the Future of Plastics & Catalyzing Action.
Ellen MacArthur Foundation• Fajar, M. Sembiring, E. & Handajani, M. 2019. The Process of Microplastics Removal in Water using Rapid Sand Filter
– Single Media. Proceeding of International Conference of Microplastic Pollution in the Environment in Asia.
25Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh
Referensi (2)• GESAMP. (2015). Sources, fate and effects of microplastics in the marine environment: a global assessment. Joint Group of Experts on the Scientific
Aspects of Marine Environmental Protection.• Jambeck, J.R., Geyer, R., Wilcox, C., Siegler, T.R., Perryman, M., Andrady, A., Narayan, R., Law, K.L., 2015. Plastic waste inputs from land into the
ocean. Science 347, 768–771. https://doi.org/10.1126/science.1260352• Kementrian Kesehatan Republik Indonesia, 2019. Paparan pada Seminar International Conference of Microplastic Pollution in the Environment in Asia.• Lamb, J.B., Willis B.L., Fiorenza, E.A., Couch C.S., Howard R., Rader D.N., True J.D., Kelly L.A., Ahmad A., Jompa.J., Harvell, C.D. 2018. Plastic
waste associated with disease on coral reefs. Science. 359(6374):460-462• Mahapati, W.O.S W., Sembiring, E, • Müller, C., Townsend, K., Matschullat, J., 2012. Experimental degradation of polymer shopping bags (standard and degradable plastic, and
biodegradable) in the gastrointestinal fluids of sea turtles. Science of The Total Environment 416, 464–467. https://doi.org/10.1016/j.scitotenv.2011.10.069
• Mahapati, W. O. S. W., Sembiring, E., & Hidayat, S. 2019. Effect of Microplastic Particle Size on Performance of Polymer Woven Filter Media. Will be published in Proceeding of International Conference of Microplastic Pollution in the Environment in Asia.
• Napper, I. E., & Thompson, R. C. (2016). Release of synthetic microplastic plastic fibers from domestic washing mavhines: Effects of fabric type and washing conditions. Marine Pollution Bulletin, 112(1-2), 39-45.
• Purba, N.P., Handyman, D.I.W., Pribadi, T.D., Syakti, A.D., Pranowo, W.S., Harvey, A., Ihsan, Y.N., 2019a. Marine debris in Indonesia: A review of research and status. Marine Pollution Bulletin 146, 134–144. https://doi.org/10.1016/j.marpolbul.2019.05.057
• Rochman, C.M., Tahir, A., Williams, S.L., Baxa, D.V., Lam, R., Miller, J.T., Teh, F.-C., Werorilangi, S., Teh, S.J., 2015. Anthropogenic debris in seafood: Plastic debris and fibers from textiles in fish and bivalves sold for human consumption. Scientific Reports 5, 14340. https://doi.org/10.1038/srep14340
• Sembiring, E., Nitivattananon, V., 2010, Sustainable solid waste management toward an inclusive society: integration of the informal sector, Resources, Conservation & Recycling 54, p 802-809
• Sembiring, E., Damanhuri, E., Widyarsana, IMW., Agustina, E., 2019. Plastics Material Flow Study to Prove Possible Land Based Leakage: a Case Study of Sarbagita Region, Bali, Indonesia, Proceeding ISEE, 213-224.
• Talvitie, J., Mikola, A., Koistinen, A., & Setala, O. (2017). Solutions to microplastic pollution: Removal of microplastics from wastewater effluent with advanced wastewater treatment technologies. Water Research, 123, 401-407.
• Yudison, A.P., Tomo, H.S., Sembiring, E. 2019. Investigating Atmospheric Microplastic in Total SuspendedParticulate (TSP): Preliminary Study. Proceeding of International Conference of Microplastic Pollution in the Environment in Asia.
26Emenda Sembiring, PhD/FTSL-ITB/Webinarpslh