plastox wp 3: mps!uptake!and!food!web!transfer · maria1 grannberg4, susanne1 kuhen 3,1 rocco1...
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Project info
This project has received funding iunder the framework of JPI Oceans
Project logo
Project info
Acknowledgement of relevant funding agencies. Please find all logo’s on the following website: https://epss-jpi-oceans.ptj.de/partners
Project logo
3.5 3.8 4.1 4.4 4.7 5.0 5.3 5.6
0 5 10 15 20
Cl/biphe
nyl
Incuba/on Time (weeks)
MPs-‐PCBs in sediment
PE PET PS PP PVC
3.5 3.8 4.1 4.4 4.7 5.0 5.3 5.6
0 5 10 15 20
Cl/biphe
nyl
Incuba/on Time (weeks)
MPs-‐PCBs in water
PE PET PS PP PVC
A B
-‐ Clear inges;on of PS and GF -‐ Possible preferen;al inges;on of PS. -‐ No evidence of excre;on.
Fig. 8: Reduc;ve dechlorina;on of PCB (Aroclor 1254) adsorbed to different MPs in sediment (A) and water (B) PCB-‐dechlorina;ng marine cultures.
Microplas;cs (MPs) are increasingly documented in marine organisms, including species involved in human consump;on such as molluscs, crustaceans and fishes. Physiochemical proper;es (size, density, shape, chemical composi;on) of MPs might influence their inges;on by organisms and subsequent food web transfer. Most knowledge is from laboratory work, and there is li[le empirical informa;on on the distribu;on and detec;on of MPs in nature. The aims of the work are to: • Quan;fy and characterise MPs
occurrence in key marine species with different feeding strategies from relevant coastal ecosystems around Europe.
• Iden;fy relevant spa;al distribu;on pa[erns of MPs
• Understand which proper;es tend to favour MPs inges;on and reten;on by the organisms
PLASTOX is supported by national funding agencies in the framework of JPI Oceans and other institutions
PLASTOX WP 3: MPs uptake and food web transfer
• The presence of MPs in our organisms was consistently rather small compared to previous data from the literature.
• The
Organisms from different trohic levels were processed for MPs extrac/on, quan/fica/on and characteriza/on (µ-‐FTIR).
h[ps://www.sintef.no/projectweb/plastox/
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Background and aims
Field-‐based and laboratory studies at sta/ons represen/ng a wide range of European marine environments (Adria/c, North Sea, Atlan/c Ocean) and habitats (saltmarshes, sedimentary coastal habitats and pelagic coastal systems)
MPs in food webs_ field studies
Location B
Location C
Site 1 Site 2 Site 3
Site 1 Site 2 Site 3
Site 1 Site 2 Site 3
C.galucum
M.galloprovincialis
C.aestuarii
Nereis
0
0.5
1
1.5
2
2.5
3
3.5
Baiona Bellocchio Chioggia
Average of M
Ps/organ
ims
1Alma Mater Studiorum -‐ University of Bologna, Italy; ; 2 FCT-‐NOVA, Portugal; 3IMARES Wageningen UR, Netherlands; 4 IVL Swedish Environmental Research Ins;tute, Sweden; 5 Ghent University, Belgium; 6Na;onal University of Ireland Galway; 7Norwegian University for Science and Technology; 8SINTEF Materials and Chemistry, Norway.
Stefania Piarulli1, Laura Airoldi1, Filipa Bessa2, Paolo Comandini1, Thomas Doyle6, Marco Capolupo1, Elena Fabbri1, Jan van Franeker3, Maria Grannberg4, Susanne Kuhen3, Rocco Mazzeo1, Kers/n Magnusson4, Silvia Pra/1, Antonella Rosato1, Lurgi Salaverria7, Sara Scapinello1, Giorgia Sciu^o1, Paula Sobral2, Carl Van Colen5, Brecht Vanhove5, Alina Madita Wieczorek6, Joanne XW Wong1,Giulio Zanaroli1, Andy Booth8
Location A
Uptake & accumula/on_lab experiments
PE
PS
GF -‐ MP concentra;on: 75, 750 & 7500 par;cles mL-‐1 -‐ Exposure ;me: O. marina: ≤1 h; C. finmarchicus: ≤96 h -‐ Sta;c exposure on custom made plankton wheels
PCB-‐dechlorina/ng marine cultures -‐ Incuba;on in sediment vs. water -‐ PCB-‐contaminated MPs (Aroclor 1254 30 mgPCBs/kgMP) vs. pris;ne MPs
MPs in marine food webs Experimental approaches
0
10
20
30
40
50
60
70
80
90
100
Diplodus vulgaris Dicentrarchus labrax
Platichthys flesus Mic
ropl
astic
s in
gest
ion
freq
uenc
y (%
) Downstream
Upstream
Uptake & accumula/on Oxyrrhis marina
Calanus finmarchicus
• Adults and nauplii ingested all MP types.
• MPs excreted in faecal pellets.
• Faecal pellet produc;on reduced in the absence of algae.
• MPs may be retained for prolonged period.
PCB-‐dechlorina/ng marine cultures
-‐ The presence of MPs consistently rather small compared to previous data. -‐ The majority of MPs extracted were fibres par;cularly in invertebrates species. -‐ Higher presence of MPs in organisms from areas with stronger anthropogenic ac;vi;es -‐ Very high variability in the MPs gastrointes;nal contents among individuals
Fig 1: Red circles indicates european marine stations where field and laboratory studies have been performed.
Fig 2: Experimental design for organisms collection along the trophic chain.
A B C
Fig 3: (A) organism dissection; (B) digestion solution; (C) Filters (20 µm) with inorganic and synte;c par;cles aker filtra;on
Fig 4: Commercially available microplas;cs:
PS (10 µm) PE (3-‐16 µm) Fluorescent (GF; 1-‐µm)
Fig. 5: Microcosms with MPs pellets inoculated with PCB-‐dechlorina;ng culture enriched from a marine sediment
Fig. 7:(A-‐B) P and fluorecent GF inside Oxyrrhis marina; (C-‐D-‐E) all plas;cs pellets inside Calanus finmarchicus
A BC
D
E
(a)
(b)
(c) (d)
Fig 6: MPs distribu;on in different species from four european marine sta;ons: (a) Adria;c Saltmarshes; (b) North sea saltmarshes; (c) Atlan;c Ocean; (d) west-‐Sweden coastal areas; (e) MPs found in mesopelagic fishes from Atlan;c Ocean iden;fied with µ-‐FTIR.
(e)