Neurotoxicity in Marine Invertebrates: History
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Invertebrates represent about 95% of existing species, and most of them belong to aquatic ecosystems. Marine invertebrates are found at intermediate levels of the food chain and, therefore, they play a central role in the biodiversity of ecosystems. Furthermore, these organisms have a short life cycle, easy laboratory manipulation, and high sensitivity to marine pollution and, therefore, they are considered to be optimal bioindicators for assessing detrimental chemical agents that are related to the marine environment and with potential toxicity to human health, including neurotoxicity. In general, albeit simple, the nervous system of marine invertebrates is composed of neuronal and glial cells, and it exhibits biochemical and functional similarities with the vertebrate nervous system, including humans. In recent decades, new genetic and transcriptomic technologies have made the identification of many neural genes and transcription factors homologous to those in humans possible. Neuroinflammation, oxidative stress, and altered levels of neurotransmitters are some of the aspects of neurotoxic effects that can also occur in marine invertebrate organisms. The purpose of this review is to provide an overview of major marine pollutants, such as heavy metals, pesticides, and micro and nano-plastics, with a focus on their neurotoxic effects in marine invertebrate organisms.

  • nervous system
  • echinoderms
  • molluscs
  • crustaceans
  • emerging contaminants
  • heavy metals
  • pesti-cides
  • microplastics
  • omics

1. Marine Pollutants: Heavy Metals

Metals are natural constituents of the Earth’s crust present in all ecosystems at variable concentrations. The use of metals has accompanied civilization since prehistoric times, characterizing the Bronze and Iron Ages, the Industrial Revolution, up to the present modern society, where they are closely linked to anthropogenic activities, including agriculture, transport, arts, and medicine [1][2]. Metals are found in the wires, batteries, and microchips, as well as in many common everyday objects. Although some heavy metals are crucial for life, their excess can be toxic and therefore extreme attention is paid to the possible consequences for human health and environment [1]. Because of their accumulation in the environment and their significant toxicity, many metals and metalloids have been identified as “priority substances” and included in the list of the Annex II of the European Directive 2008/105/EC (Annex X, Water Framework Directive 2000, https://echa.europa.eu/ann-x-priority-subs-water-dir-2000-60). In this regard, several metals, such as arsenic, lead, and mercury, have been included in the 2019 Substance Priority List by the Agency for Toxic Substances and Disease Registry (ATSDR) (https://www.atsdr.cdc.gov/spl/). Based on their chemical characteristics, the concentrations of metals are variable in the marine system and some metals tend to accumulate in the bottom sediments. Numerous species of marine invertebrates hyperaccumulate metals (such as arsenic, copper, iron, and zinc), thus resulting in significant relevance to human health and aquatic toxicity [3]. In depth analyses on the speciation, bioavailability, and bioaccumulation of some metals have been well described in other reviews [3][4][5].

Although many of the harmful effects that are induced by exposure of some heavy metals are well known, the mechanisms underlying their toxicity in humans have not yet been fully clarified. Numerous studies mainly conducted on fishes and mammals have highlighted the close correlation between exposure of heavy metals and neuronal damage [6][7]. Many of heavy metals can cross the blood brain barrier (BBB) and accumulate in the nervous tissues, inducing oxidative stress, inflammation, and metabolic dysfunction linked to the development of several neurodegenerative diseases.

Albeit the marine organisms are ideal indicators for long-term monitoring of metal accumulation [4], only few studies have been aimed to better understand the neurotoxic effects of heavy metals in marine invertebrates. Through in vitro and in vivo experiments, most of these studies have been focused on the analysis of the AChE activity as a possible biomarker of neurotoxicity in response to excess metals. Some studies have analyzed the combined neurotoxic effects of the different metals that are present in the polluted areas, while very few others have investigated the mechanisms underlying the toxicity that is induced by these substances at the neuronal level, including sensory alterations and neuromuscular dysfunctions.

Here, we focused our attention on neurotoxic effects that are caused by the exposure of some metals (see Table 1) in some marine invertebrates also having key positions in food chains.

Table 1. Neurotoxic metals and metalloid *.

Metals

Essential

Non-Essential

Copper

Arsenic *

Iron

Cadmium

Manganese

Lead

Zinc

Mercury

 

Nickel

Table 1 shows the classification of neurotoxic metals and metalloids in essential and not essential (modified from Caito and Aschner 2015). *Metalloid.

2. Marine Pollutants: Pesticides

Pesticides are chemical compounds that are specifically introduced into the environment to prevent, destroy, or control harmful organisms (pests) mainly in agriculture, including insects, rodents, fungi, and unwanted plants, as well as to block vector borne diseases in public health. They are also used for the protection of plants or plant products during their production, storage, and transport.

Although their application serves many important purposes, the very nature of pesticides is to damage unwanted organisms, posing great concern for a potential risk, even for non-target organisms. Indeed, many molecular targets of pesticides are shared between pests and non-target species, including humans, which may lead to a variety of adverse health effects. The over-use and/or misuse of pesticides is playing a negative role to the environmental health, affecting many aquatic and terrestrial species, as much to be now considered as contaminants of emerging concern (CECs), i.e., “new” pollutants in aquatic environments. Besides, the replacement of marine ingredients with plant material in the feeds used in fish farms introduces new unwanted substances in the marine environment, such as pesticides that are used in terrestrial agriculture, thus affecting not only fishes, but also other marine organisms [8]. Actually, based on all of these considerations, it is really very difficult to find the right balance between benefits and harms deriving from the use of pesticides.

Pesticides are divided into many subclasses, which are classified by the target organism (herbicides, insecticides, fungicides, and rodenticides) as well as by their chemical structure, physical state, and source of origin (i.e., botanicals). For the purpose of this review, we will focus on some classes of pesticides that are known for their neurotoxicity to marine invertebrate organisms, as, for example, organochlorines, organophosphates, and carbamates [9]. Organochlorines are synthetic pesticides, which belong to the group of chlorinated hydrocarbon derivatives, widely used in agriculture and chemical industry. Nowadays, many of the organochlorines have been banned in developed countries, as they are highly toxic and their characteristically long lifespan increases the risk of their accumulation in the environment [10]. Organophosphates and carbamates are organic molecules, with the first containing one or more phosphate ester groups, whereas the second is derived from carbamic acid. They are among the most widely used pesticides, which have been considered to be a less damaging alternative to organochlorines (together with carbamates), although they are known for their neurotoxicity, mainly targeting the cholinergic system. In particular, organophosphates and carbamate affect AChE activity by irreversibly binding the enzyme active site [11].

This entry is adapted from the peer-reviewed paper 10.3390/biology10020161

References

  1. Caito, S.; Aschner, M. Neurotoxicity of Metals. In Handbook of Clinical Neurology; Lotti, M., Bleecker, M.L., Eds.; Elsevier BV: Amsterdam, The Netherlands, 2015; Volume 131, pp. 169–189.
  2. Doyle, D. Notoriety to respectability: A short history of arsenic prior to its present day use in haematology. Br. J. Haematol. 2009, 145, 309–317.
  3. Thompson, E.D.; Hogstrand, C.; Glover, C.N. From sea squirts to squirrelfish: Facultative trace element hyperaccumulation in animals. Metallomics 2018, 10, 777–793.
  4. Yllmaz, A.B.; Yanar, A.; Alkan, E.N. Review of heavy metal accumulation on aquatic environment in Northern East Medi-terrenean Sea part I: Some essential metals. Rev. Environ. Health 2017, 32, 119–163.
  5. Ansari, T.M.; Marr, I.L.; Tariq, N. Heavy Metals in Marine Pollution Perspective–A Mini Review. J. Appl. Sci. 2003, 4, 1–20.
  6. Sonone, S.S.; Jadhav, S.; Sankhla, M.S.; Kumar, R. Water contamination by heavy metals and their toxic effect on aquaculture and human health through food Chain. Lett. Appl. NanoBioScience 2021, 10, 2148–2166.
  7. Green, A.J.; Planchart, A. The Neurodevelopmental Toxicity of Heavy Metals: A Fish Perspective. Comp. Biochem. Physiol. C Toxicol. Pharmacol. 2018, 208, 12–19.
  8. Olsvik, P.A.; Larsen, A.K.; Berntssen, M.H.G.; Goksøyr, A.; Karlsen, O.A.; Yadetie, F.; Sanden, M.; Kristensen, T. Effects of Agricultural Pesticides in Aquafeeds on Wild Fish Feeding on Leftover Pellets Near Fish Farms. Front. Genet. 2019, 10, 1–18.
  9. Richardson, J.R.; Fitsanakis, V.; Westerink, R.H.S.; Kanthasamy, A.G. Neurotoxicity of pesticides. Acta Neuropathol. 2019, 138, 343–362.
  10. Jayaraj, R.; Megha, P.; Sreedev, P. Review Article. Organochlorine pesticides, their toxic effects on living organisms and their fate in the environment. Interdiscip. Toxicol. 2016, 9, 90–100.
  11. Kwong, T.C. Organophosphate Pesticides: Biochemistry and Clinical Toxicology. Ther. Drug Monit. 2002, 24, 144–149.
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