Nodularins - hepatotoxic cyclic pentapeptides – University of Copenhagen

NaToxAq > Toxin of the week > Nodularins

27 November 2017

Nodularins - hepatotoxic cyclic pentapeptides

Natural toxin

Nodularins are produced by the cyanobacteria Nodularia spumigena

Cyanobacterial blooms and Nodularia spumigena

Nodularins (NODs) are produced almost exclusively by filamentous diastrophic Nodularia spumigena. This cyanobacterium typically occurs in brackish waters and estuaries. NODs were firstly described in 1988, and since that time seven naturally occurring variants of NOD have been identified, being NOD-R the most abundant variant. The general structure of NODs: cyclo-(D-MeAsp-L-Arg-Adda-D-glutamate-Mdhb) in which L-Arg is L-arginine, D-MeAsp is D-erythro-β -methylaspartic acid, Mdhb is 2-(methylamino)-2- dehydrobutyric acid and the amino acid Adda is (2S,3S,8S,9S)-3-amino-9-methoxy-2,6,8-trimethyl-10-phenyldeca-4,6-dienoic acid. According to the structure, NODs are similar to microcystins (MCs), which are also relatively polar molecules, but Adda moiety provides partially hydrophobic characteristics.

Structure of NOD. Click image for 3D structure

Similarly to MCs, NODs are toxic due to inhibition of the protein phosphatases (PPs), which leads to functional disturbance and structural liver disruption. Contrary to MCs, NOD cannot interact covalently with PPs due to the scarcity of methyldehydroalanine (Mdha) residue.

Human poisonings by N. spumigena ingestion were not yet reported. However, negative impact on the zooplankton and fish was observed. NOD was detected in different organs, being liver the main organ of accumulation.

Regarding occurrence, NODs have been found in Australia, New Zealand, Tasmania, Northern Europe and Baltic Sea. Nowadays, the majority of studies is focusing on Baltic Sea because this region provides a high amount of fish for human consumption. NODs are mainly found in the intracellular form. Concentrations of intracellular NODs increase with an elevation of temperature, phosphate concentrations and irradiance.

SMILES: C/C=C\1/C(=O)N[C@H]([C@@H](C(=O)N[C@H](C(=O)N[C@H]([C@@H](C(=O)N[C@H](CCC(=O)N1C)C(=O)O)C)/C=C/C(=C/[C@H](C)[C@H](CC2=CC=CC=C2)OC)/C)CCCNC(=N)N)C)C(=O)O

References:

  • Apeldoorn, Marian E. Van, Hans P. Van Egmond, Gerrit J.A. Speijers, and Guido J.I. Bakker. 2007. “Toxins of Cyanobacteria.” Molecular Nutrition and Food Research 51 (1): 7–60. doi:10.1002/mnfr.200600185.
  • Buratti, Franca M., Maura Manganelli, Susanna Vichi, Mara Stefanelli, Simona Scardala, Emanuela Testai, and Enzo Funari. 2017. “Cyanotoxins: Producing Organisms, Occurrence, Toxicity, Mechanism of Action and Human Health Toxicological Risk Evaluation.” Archives of Toxicology 91 (3). Springer Berlin Heidelberg: 1049–1130. doi:10.1007/s00204-016-1913-6.
  • Chen, Yun, Danfeng Shen, and Danjun Fang. 2013. “Nodularins in Poisoning.” Clinica Chimica Acta 425. Elsevier B.V.: 18–29. doi:10.1016/j.cca.2013.07.005.
  • Sotton, Benoît, Isabelle Domaizon, Orlane Anneville, Franck Cattanéo, and Jean Guillard. 2014. “Nodularin and Cylindrospermopsin: A Review of Their Effects on Fish.” Reviews in Fish Biology and Fisheries 25 (1): 1–19. doi:10.1007/s11160-014-9366-6.