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Journal of Environmental Accounting and Management
António Mendes Lopes (editor), Jiazhong Zhang(editor)
António Mendes Lopes (editor)

University of Porto, Portugal

Email: aml@fe.up.pt

Jiazhong Zhang (editor)

School of Energy and Power Engineering, Xi'an Jiaotong University, Xi'an, Shaanxi Province 710049, China

Fax: +86 29 82668723 Email: jzzhang@mail.xjtu.edu.cn


Ecotoxicological Assessment of Virgin Plastic Pellet Leachates in Freshwater Matrices

Journal of Environmental Accounting and Management 6(4) (2018) 345--353 | DOI:10.5890/JEAM.2018.12.007

S. Schiavo$^{1}$,$^{2}$, M. Oliviero$^{1}$,$^{2}$, V. Romano$^{2}$, S. Dumontet$^{2}$, S. Manzo$^{1}$

$^{1}$ C.R ENEA, Portici Naples, Italy

$^{2}$ Department of Science and Technology, Parthenope University of Naples, Italy

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Abstract

The environmental contamination caused by the widespread diffusion of plastic material all over the world is a topic of high concern. Virgin plastic pellets of different polymers are often used in particle toxicity studies as reference materials. In this study we exposed organisms of different trophic levels, spanning form prokaryotes to eukaryotes, to leachate of polypropylene (PP) and polyethylene (PE), and polystyrene (PS) pellets in acute and chronic ecotoxicological tests. A toxicity test battery integrated index (TBI) was used to rank the relative toxicity of studied polymers and to define their possible ecotoxicological risk in freshwater environment. Daphnia magna showed the highest susceptibility in the chronic exposure tests (around 50% of effect) while Aliivibrio fischeri (around 25 % of effect) in the acute one. No relevant toxic effects were observed on Sorghum saccharatum, Lepidium sativum and Sinapis alba seeds, while significant toxicity for Vicia faba along 21 days of exposure was reported. TBI allowed us to rank the toxicity risk associated to the studied materials as follows: PP>PS>PE. PP toxicity could be related to the presence of solvents (methanol, oil, cyclohexane) employed for its production, whereas PS toxicity was probably due to the depolymerization, occurring in water, followed by styrene release, while the mild toxic effects of PE and its temporary bio stimulation could be attributable to the thermoregulatory additives present in the polyethylene resins. Our results highlighted that also the virgin plastic pellets could be responsible of toxic effects that should not be neglected.

References

  1. [1]  Abbott,W. (1925), A method of computing the effectiveness of an insecticide, J EconEntomol, 18, 265-267.
  2. [2]  Barnes, D.K.A., Galgani, F., Thompson, R.C., and Barlaz, M. (2009), Accumulation and fragmentation of plastic debris in global environments, Philosophical Transactions of the Royal Society B, 364, 1985-1998.
  3. [3]  Brede, C., Fjeldal, P., Skjevrak, I., and Herikstad, H. (2003), Increased migration levels of bisphenol A from polycarbonate baby bottles after dishwashing, boiling and brushing, Food Additives and Contaminants, 20, 684-689.
  4. [4]  Browne, M.A., Niven, S.J., Galloway, T.S., Rowland, S.J., and Thompson, R.C. (2013), Microplastic moves pollutants and additives to worms, reducing functions linked to health and biodiversity, Current Biology, 23, 2388-2392.
  5. [5]  Calow, P. and Forbes, V.E. (2003), Peer reviewed: Does ecotoxicology inform ecological risk assessment? Environmental Science & Technology, 146A-151A.
  6. [6]  Crompton, T.R. (2007), Additive migration from plastics into foods. A guide for the analytical chemist., Smithers Rapra Publishing, Shrewsbury.
  7. [7]  Da Costa, J.P. (2018), Micro-and nanoplastics in the environment: Research and policymaking, Current Opinion in Environmental Science & Health, 1, 12-16.
  8. [8]  Fernandes, A.R., Rose, M., and Charlton, C. (2008), 4-Nonylphenol (NP) in food-contact materials: analytical methodology and occurrence, Food Additives and Contaminants, 25, 364-372.
  9. [9]  Geyer, R., Jambeck, J.R., and Law, K.L. (2017), Production, use, and fate of all plastics ever made, Science Advances, 3(7), e1700782.
  10. [10]  Gibbs, B.F. and Mulligan, C.N. (1997), Styrene toxicity: an ecotoxicological assessment, Ecotoxicology and Environmental Safety, 38(3), 181-194.
  11. [11]  Grenni, P., Patrolecco, L., Ademollo, N., Di Lenola, M., and Caracciolo, A.B. (2018), Assessment of gemfibrozil persis tence in river water alone and in co-presence of naproxen, Microchemical Journal, 136, 49-55.
  12. [12]  Harding, K.G., Dennis, J.S., Von Blottnitz, H., and Harrison, S.T.L. (2007), Environmental analysis of plastic production processes: comparing petroleum-based polypropylene and polyethylene with biologically-based poly-β-hydroxybutyric acid using life cycle analysis, Journal of biotechnology, 130(1), 57-66.
  13. [13]  Hartwell, S. (1997), Demonstration of a toxicological risk ranking method to correlate measures of ambient toxicity and fish community diversity, Environmental Toxicology and Chemistry, 16, 361-371.
  14. [14]  Henneuse-Boxus, C. and Pacary, T. (2003), Emissions from plastics. Rapra Review Reports, Report 161, 14(5), Rapra Technology, Rapra Technology Limited, Shrewsbury.
  15. [15]  Hermabessiere, L., Dehaut, A., Paul-Pont, I., Lacroix, C., Jezequel, R., Soudant, P., and Duflos, G. (2017), Occurrence and effects of plastic additives on marine environments and organisms: A review, Chemosphere, 182, 781-793.
  16. [16]  ISPRA (2011), Batterie di saggi ecotossicologici per sedimenti di acque salate e salmastre. Manuali e linee guida 67/2011. ISBN: 978-88-448-0498-5.
  17. [17]  Kim, Y.J., Osako, M., and Sakai, S. (2006), Leaching characteristics of polybrominated diphenyl ethers (PBDEs) from flame-retardant plastics, Chemosphere, 65, 506-513.
  18. [18]  Latini, G., Verrotti, A., and De Felice, C. (2004), Di-2-ethylhexyl phthalate and endocrine disruption: a review. Current Drug Targets-Immune, Endocrine & Metabolic Disorders, 4(1), 37-40.
  19. [19]  Lithner, D., Damberg, J., Dave, G., and Larsson, A. (2009) Leachates from plastic consumer products-screening for toxicity with Daphnia magna, Chemosphere, 74(9), 1195-1200.
  20. [20]  Manzo, S., De Nicola, F., Picione, F.D.L., Maisto, G., and Alfani, A. (2008), Assessment of the effects of soil PAH accumulation by a battery of ecotoxicological tests Chemosphere, 71(10), 1937-1944.
  21. [21]  Monteiro, M.S., Santos, C., Soares, A.M.V.M., and Mann, R.M. (2009), Assessment of biomarkers of cadmium stress in lettuce, Ecotoxcology and Environmental Safety, 72(3), 811-818.
  22. [22]  Murphy, J. (Ed.) (2001), Additives for plastics handbook, Elsevier.
  23. [23]  Mutsuga, M., Kawamura, Y., Sugita-Konishi, Y., Hara-Kudo, Y., Takatori, K., and Tanamoto, K. (2006), Migration of formaldehyde and acetaldehyde into mineral water in polyethylene terephthalate (PET) bottles, Food Additives and Contaminants, 23, 212-218.
  24. [24]  Nobre, C.R., Santana, M.F.M., Maluf, A., Cortez, F.S., Cesar, A., Pereira, C.D.S., and Turra, A. (2015), Assessment of microplastic toxicity to embryonic development of the sea urchin Lytechinusvariegatus (Echinodermata: Echinoidea), Marine Pollution Bulletin, 92(1-2), 99-104.
  25. [25]  OECD (2004), Emission Scenario Document on Plastic Additives. Series on Emission Scenario Documents, No. 3. OECD Environmental Health and Safety Publications. Environment Directorate, Paris.
  26. [26]  OECD (2008), OECDOECD Guidelines for the Testing of Chemicals, Test No.211: Daphnia magna Reproduction Test (2008).
  27. [27]  Petrin, Z, Göran, E., and Björn, M. (2008), Contrasting effects of anthropogenic and natural acidity in streams: a metaanalysis., Proceedings of the Royal Society of London B: Biological Sciences, 275(1639), 1143-1148.
  28. [28]  Syberg, K., Khan, F.R., Selck, H., Palmqvist, A., Banta, G.T., Daley, J., and Duhaime, M.B. (2015), Microplastics: addressing ecological risk through lessons learned Environmental Toxicology and Chemistry, 34(5), 945-953.
  29. [29]  Teuten, E.L., Saquing, J.M., Knappe, D.R., Barlaz, M.A., Jonsson, S., Björn, A., and Ochi, D. (2009), Transport and release of chemicals from plastics to the environment and to wildlife, Philosophical Transactions of the Royal Society of London B: Biological Sciences, 364(1526), 2027-2045.
  30. [30]  Thaysen, C., Stevack, K., Ruffolo, R., Poirier, D., De Frond, H., De Vera, J., and Rochman, C.M. (2018), Leachate from Expanded Polystyrene Cups Is Toxic to Aquatic Invertebrates (Ceriodaphnia dubia), Frontiers in Marine Science, 5, 71.
  31. [31]  Tønning, K., Jacobsen, E., Pedersen, E., and Nilsson, N.H. (2010), Phthalates in products that children are in direct contact with Danish Technological Institute, Survey of chemical substances in consumer products, No. 109210, Danish Ministry of the Environment and EPA.
  32. [32]  UNI EN 12457-2:2004 'Lisciviazione - Prove di conformit à per la lisciviazione di rifiuti granulari e di fanghi'.
  33. [33]  US EPA (1993), A linear interpolation method for sublethal toxicity: the inhibition concentration (ICp) approach. National Effluent Toxicity Assessment Center Technical Report (pp. 0393). Duluth: Environmental Research Laboratory Google Scholar.
  34. [34]  Wagner,M. and Oehlmann, J. (2009), Endocrine disruptors in bottled mineral water: total estrogenic burden and migration from plastic bottles, Environmental Science and Pollution Research, 16(3), 278-286.
  35. [35]  Wagner, M., Scherer, C., Alvarez-Muñoz, D., Brennholt, N., Bourrain, X., Buchinger, S., Fries, E., Grosbois, C., Klasmeier, J., Marti, T., Rodriguez-Mozaz, S., Urbatzka, R., Vethaak, A.D., Winther-Nielsen, M., and Reifferscheid, G. (2014), Microplastics in freshwater ecosystems: what we know and what we need to know, Environmental Sciences Europe, 26(1), 12.
  36. [36]  Yang, C.Z., Yaniger, S.I., Jordan, V.C., Klein, D.J., and Bittner, G.D. (2011), Most plastic products release estrogenic chemicals: a potential health problem that can be solved, Environmental Health Perspectives, 119(7), 989.