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 Project logo 3.5 3.8 4.1 4.4 4.7 5.0 5.3 5.6 0 5 10 15 20 Cl/biphenyl Incuba/on Time (weeks) MPsPCBs 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/biphenyl Incuba/on Time (weeks) MPsPCBs 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) PCBdechlorina;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 (µFTIR). h[ps:// www.sintef.no/ projectweb/plastox/ Follow PLASTOX on Facebook x Background and aims Fieldbased 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.galloprovi ncialis C.aestuarii Nereis 0 0.5 1 1.5 2 2.5 3 3.5 Baiona Bellocchio Chioggia Average of MPs/organims 1 Alma Mater Studiorum University of Bologna, Italy; ; 2 FCTNOVA, Portugal; 3 IMARES Wageningen UR, Netherlands; 4 IVL Swedish Environmental Research Ins;tute, Sweden; 5 Ghent University, Belgium; 6 Na;onal University of Ireland Galway; 7 Norwegian University for Science and Technology; 8 SINTEF Materials and Chemistry, Norway. Stefania Piarulli 1 , Laura Airoldi 1 , Filipa Bessa 2 , Paolo Comandini 1 , Thomas Doyle 6 , Marco Capolupo 1 , Elena Fabbri 1 , Jan van Franeker 3 , Maria Grannberg 4 , Susanne Kuhen 3 , Rocco Mazzeo 1 , Kers/n Magnusson 4 , Silvia Pra/ 1 , Antonella Rosato 1 , Lurgi Salaverria 7 , Sara Scapinello 1 , Giorgia Sciu^o 1 , Paula Sobral 2 , Carl Van Colen 5 , Brecht Vanhove 5 , Alina Madita Wieczorek 6 , Joanne XW Wong 1 ,Giulio Zanaroli 1 , Andy Booth 8 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 PCBcontaminated MPs (Aroclor 1254 30 mg PCBs /kg MP ) 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 Microplastics ingestion frequency (%) 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. PCBdechlorina/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 (316 µm) Fluorescent (GF; 1µm) Fig. 5: Microcosms with MPs pellets inoculated with PCBdechlorina;ng culture enriched from a marine sediment Fig. 7:(AB) P and fluorecent GF inside Oxyrrhis marina; (CDE) all plas;cs pellets inside Calanus finmarchicus A B C 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) westSweden coastal areas; (e) MPs found in mesopelagic fishes from Atlan;c Ocean iden;fied with µFTIR. (e)

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Page 1: PLASTOX WP 3: MPs!uptake!and!food!web!transfer · Maria1 Grannberg4, Susanne1 Kuhen 3,1 Rocco1 Mazzeo1,1 Kers/n1 Magnusson4, Silvia Pra 1, Antonella1 Rosato1, LurgiSalaverria7, Sara

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/  

Follow  PLASTOX  on  Facebook  x  

   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)