Identification of hazardous nanoparticles present in the Caribbean Sea for the allocation of future preservation projects

https://doi.org/10.1016/j.marpolbul.2021.112425Get rights and content

Highlights

  • The diverse sources of nanoparticles increasingly induce their exposure in the waters of the Caribbean Sea.

  • The nanoparticles caused the formation of potentially hazardous elements.

  • The identification of nanoparticles is of paramount importance due to being more reactive.

  • As, Cd, Pb, Mg, Ni, and V were detected used advanced characterizations.

  • The results expound useful information in assessing the environmental risks and for public health.

Abstract

The deposition of remaining nanoparticles in the Caribbean Sea generates the formation of potentially dangerous elements, which influence at the imbalance of ecosystems. The detection of nanoparticles is not simple and the use of conventional methods is difficult application, which is why we highlight the immediacy and importance of this research for the areas of marine biology, urbanism, engineering and geosciences, applied in the Caribbean Sea. The general objective of this study is to evaluate the use of advanced methods for the determination of toxic nanoparticles, which can directly affect the development of marine organisms in the aquatic ecosystem in waters of the Caribbean Sea, favoring the construction of future international public policies with the elaboration of projects capable of mitigating these levels of contamination. The morphology and structure of nanoparticles were analyzed by emission scanning electron microscope with a high-resolution electron microscope. The nanoparticles smaller than 97 nm were identified in different proportions. The morphological analyses indicated nanoparticles' presence in the form of nanotubes, nanospheres, and nanofibers, which were shown in an agglomerated form. The presence of potentially hazardous elements, such as As, Cd, Pb, Mg, Ni and V were verified. In addition, the presence of asbestos in the form of minerals was confirmed, and that of titanium dioxide was found in large quantities. The results provide new data and emphasize the possible consequences to the in the Caribbean Sea, with the identification of dangerous elements (As, Cb, Pb, Hg, Ni and V), harmful to the marine ecosystem. Therefore, there is a need for strict control to reduce contamination of the Caribbean Sea and avoid risks to the ecosystem and public health, through suggestions of international public policies, through constant monitoring and the application of environmental recovery projects in this marine estuary.

Introduction

The presence of potentially dangerous nanoparticles (NPs) in the sea affects the fertilization and development of marine embryos and other existing organisms. These harmful concentrations of dangerous elements negatively enhance biological changes in fauna and flora, directly affecting humans and the ecosystem (Freitas et al., 2018; Gallo et al., 2018; Xia et al., 2018; Silva et al., 2020a; Oliveira et al., 2021). It is estimated that NPs can cause direct toxicity, changes in nutrient bioavailability and secondary risks caused by contact with organic mixtures, provoking alterations in environmental structure (Peralta-Videa et al., 2011; Caspah et al., 2016; Nguyen et al., 2020; Alnadhari et al., 2021). Therefore, the identification and characterization NPs origin are extremely important to avoid these environmental changes, through public policies, with environmental recovery projects.

The NPs can be of organic, inorganic origin or a mixture, from natural sources (for example pollen, sea salt, sand, erosion), secondary causes (oil refinery practices, vehicular traffic, and mining) or from syntheses (carbon nanotubes and metal hydr/oxides) (Civeira et al., 2016; Graca et al., 2018; Oliveira et al., 2019; Silva et al., 2020b). Whether natural or from anthropogenic sources, they appear as spherical, cylindrical or irregularly shaped compounds from connected, accumulated or agglomerated arrangements (Silva et al., 2011a, Silva et al., 2011b). The identification and characterization of these NPs influence their reactivity and the determination of toxicity due to their nanoscale (NIOSH, 2013). Therefore, the geochemical impact as a consequence of the accumulation of NPs is different from the behavior of macromolecules because NPs are, normally, more reactive in the environment (Wigginton et al., 2007; Barreto et al., 2021).

The deposit of NPs in the sea may be due to their presence in atmospheric air or from adsorption/desorption routes of existing organic materials, or even by autogenesis processes (Barreto et al., 2021). The accumulation and permanence of these NPs can induce the formation of potentially hazardous elements (PHEs) (Oliveira et al., 2021). Among these elements are Pb, Cd, TiO2, As, that are highly toxic, carcinogenic compounds, which can cause autophagy and even changes in the nervous system of the human being (Freitas et al., 2018; Hu et al., 2018; Rojas et al., 2019; Silva et al., 2020a).

However, the methods of identifying EPS in seawater are restricted, and some have precariousness in the technique due to the lack of equipment capable of carrying out complex and advanced analyzes for the identification of these levels of contamination (Wigginton et al., 2007; Restrepo et al., 2012; Gallo et al., 2018; Gonçalves and Bebianno, 2021). Thereby, the identification of PHEs in sea samples through X-ray spectroscopy with energy dispersion (EDS) can be enhanced when coupled with advanced microscopy (Arai et al., 2019; Oliveira et al., 2021). This technique has advantages in providing simple sampling and does not compromise the integrity of the sample, justifying the possibility of identifying the dangerous NPs present in the waters of the Caribbean Sea of 8 different islands located in the city of Cartagena in Colombia through advanced microscopy, the which makes it possible to assess these contamination risks present in this marine estuary.

The general objective of this study is to evaluate the use of advanced methods for the determination of toxic NPs, which can directly affect the development of marine organisms in the aquatic ecosystem in waters of the Caribbean Sea, favoring the construction of future international public policies with the elaboration of projects capable of mitigating these levels of contamination.

Section snippets

Sampling and sample preparation

The city of Cartagena, Colombia, experienced an intense urbanization process, totaling a population of approximately 1,043,926 inhabitants in 2021 (Dane, 2021). Eight estuaries were considered for the study, with an abundance of marine fauna and flora in the city of Cartagena. The study area is directly influenced by the high amount of urban, industrial and port expansion, characterized by a dry tropical climate, with an average annual rainfall of 900 mm and a temperature of 29 °C (

Results and discussion

In general, identification of NPs is problematic when is not combined with specific analytical methods that connect light scattering, laser diffraction, NPs tracking analysis, or high-resolution microscopic methods (Ribeiro et al., 2010; León-Mejía et al., 2018; Arai et al., 2019; Oliveira et al., 2021). In the last years, different techniques for the identification of NPs were tested, but most of them presented errors if there was no coupling with other analytical procedures (Petersen et al.,

Conclusion

The advanced microscopy methods suggested for sampling Caribbean seawater allowed the determination of variable NPs and their morphological behavior. The NPs detected in the Caribbean waters varied in size between 2 and 93 nm. Among these NPs, it is worth mentioning the identification of As, Cb, Pb, Hg, Ni, and V, which are indicated as possible hazardous elements. In addition, the presence of particles of silica nanofibers, nanofibers composed of Mn, Ba, K, Cl, and Fe oxides, and spherical

CRediT authorship contribution statement

Luis F.O. Silva: Conceptualization, Data curation, Writing - original draft. Liliana P. Lozano: Formal analysis. Marcos L.S. Oliveira: Funding acquisition, Investigation, Methodology. Kátia da Boit: Project administration, Resources. Janaína O. Gonçalves: Supervision, Validation. Alcindo Neckel: Writing – review & editing.

Declaration of competing interest

The authors have not conflict of interest.

Acknowledgments

The authors thank CAPES (Coordination for the Improvement of Higher Education Personnel) and CNPq (National Council for Scientific and Technological Development) for the financial support.

References (61)

  • A. Gallo et al.

    Cytotoxicity and genotoxicity of CuO nanoparticles in sea urchin spermatozoa through oxidative stress

    Environ. Int.

    (2018)
  • J.M. Gonçalves et al.

    Nanoplastics impact on marine biota: a review

    Environ. Pollut.

    (2021)
  • B. Graca et al.

    Origin and fate of nanoparticles in marine water e preliminary results

    Chemosphere.

    (2018)
  • C. He et al.

    The impact of flood and post-flood cleaning on airborne microbiological and particle contamination in re- sidential houses

    Environ. Int.

    (2014)
  • J. Hu et al.

    Effect of TiO2 nanoparticle aggregation on marine microalgae Isochrysis galbana J

    Environ. Sci.

    (2018)
  • R. Kaegi

    Synthetic TiO2 nanoparticle emission from exterior facade into the aquatic environment

    Environ. Pollut.

    (2008)
  • G. León-Mejía et al.

    Intratracheal instillation of coal and coal fly ash particles in mice induces DNA damage and translocation of metals to extrapulmonary tissues

    Sci. Total Environ.

    (2018)
  • G. Liu et al.

    Effects of biochar input on the properties of soil nanoparticles and dispersion/sedimentation of natural mineral nanoparticles in aqueous phase

    Sci. Total Environ.

    (2018)
  • A.P. Nordin et al.

    In vitro genotoxic effect of secondary minerals crystallized in rocks from coal mine drainage

    J. Hazard. Mater.

    (2018)
  • M.L. Oliveira et al.

    Nanoparticles from construction wastes: a problem to health and the environment

    J. Clean. Prod.

    (2019)
  • M.L.S. Oliveira et al.

    Environmental aspects of the depreciation of the culturally significant wall of Cartagena de Indias – Colombia

    Chemosphere

    (2021)
  • J.R. Peralta-Videa et al.

    Nanomaterials and the environment: a review for the bi-ennium

    J. Hazard. Mater.

    (2011)
  • M. Piccardo et al.

    Nanoplastics in the oceans: theory, experimental evidence and real world

    Mar. Pollut. Bull.

    (2020)
  • J.C. Restrepo et al.

    Shoreline changes between 1954 and 2007 in the marine protected area of the Rosario Island archipelago (Caribbean of Colombia)

    Ocean Coast. Manag.

    (2012)
  • J. Ribeiro et al.

    Identification of nanominerals and nanoparticles in burning coal waste piles from Portugal

    Sci. Total Environ.

    (2010)
  • J.C. Rojas et al.

    Exposure to nanometric pollutants in primary schools: environmental implications

    Urban Clim.

    (2019)
  • L.F.O. Silva et al.

    Brazilian coal mining residues and sulphide oxidation by Fenton’s reaction: an accelerated weathering procedure to evaluate possible environmental impact

    J. Hazard. Mater.

    (2011)
  • L.F.O. Silva et al.

    The impact of air pollution on the rate of degradation of the fortress of Florianópolis Island, Brazil

    Chemosphere

    (2020)
  • L.F.O. Silva et al.

    Multiple hazardous elements in nanoparticulate matter from a Caribbean industrialized atmosphere

    Chemosphere.

    (2020)
  • H.S. Sofi et al.

    Regenerated cellulose nanofibers from cellulose acetate: incorporating hydroxyapatite (HAP) and silver (AG) nanoparticles (NPs), as a scaffold for tissue engineering applications

    Mater. Sci. Eng. C

    (2021)
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