Cyanobacterial lipopeptides puwainaphycins and minutissamides induce disruptive and pro-inflammatory processes in Caco-2 human intestinal barrier model
Graphical abstract
Introduction
Adverse effects of cyanobacterial toxins on human health are well documented and recognized as an emerging environmental health issue due to increasing presence of toxic cyanobacteria in different ecosystems worldwide (Huisman et al., 2018). Along with well-recognized and studied cyanobacterial toxins, such as microcystins (MC) or cylindrospermopsin (CYN), cyanobacteria are known to produce tremendous diversity of other chemical structures. It is estimated that chemical structure of only about 20% of cyanobacterial compounds have been described to date (Berdy, 2005; Hrouzek et al., 2011; Welker and von Dohren, 2006). Moreover, only in few of the known metabolites the molecular mechanisms of their biological activity has been identified (Janssen, 2019). Some cyanobacterial metabolites are cytotoxic to various human cell models (Buratti et al., 2017; Janssen, 2019; Maru et al., 2010; Moon et al., 1992), but for most of them, the possible toxic effects are unknown (Maru et al., 2010; Moon et al., 1992).
One of such groups are cyanobacterial cyclic lipopeptides. Hundreds of such structures are described from various cyanobacterial strains and genome surveys are estimating that their occurrence might be quite frequent especially in soil or benthic cyanobacteria (Galica et al., 2017) but they were documented also in planktonic strains (Vestola et al., 2014). Puwainaphycins (PUW) A−G and minutissamides (MIN) A-L are structurally analogous cyclic decapeptides containing β-amino fatty acids and so far they have been isolated from soil and benthic cyanobacteria of genera Anabaena, Cylindrospermum and Symplocastrum (Gregson et al., 1992; Hrouzek et al., 2012; Kang et al., 2011, 2012; Mares et al., 2019; Moore et al., 1989). However, there are also indications that these compounds are produced by the planktonic cyanobacterial species forming cyanobacterial water blooms such as Microcystis and Sphaerospermopsis (Pancrace et al., 2019; Zapomelova et al., 2009). They share a common biosynthetic origin and their structures can vary especially concerning the length and substitution of the fatty acid moiety (Mares et al., 2019). PUW/MIN affect cell proliferation and viability of various human cell lines in low micromolar range (Hrouzek et al., 2012; Kang et al., 2011, 2012). Specifically, PUW F induces calcium influx into the HeLa cells (Hrouzek et al., 2012) and PUW C has a strong positive ionotropic effect on isolated mouse atria (Moore et al., 1989). Except for these observations, little is known about their interactions with specific cell types or tissues and overall potential bioactivity of PUW/MIN in mammals.
The most probable route of human exposure to PUW/MIN is oral consumption of cyanobacteria-contaminated soil, food and/or water. Thus the primary target of their biological activity would be the intestinal epithelium (Kubickova et al., 2019). Its selective permeability is determined mainly by tight junctions (TJ) (Turner, 2009). TJ are formed by transmembrane proteins, e.g. claudins and occludin. In vitro studies show that switching of the different claudins expression could be the mechanism beyond increased intestinal permeability (Luissint et al., 2016). These changes are also seen in vivo in patients with inflammatory bowel diseases or with epithelial cancers (Gunzel and Fromm, 2012). Transmembrane proteins bind to scaffolding/adapter proteins linking them to cytoskeleton. The most well-known are zonula occludens (ZO) 1, 2 and 3 (Lee, 2015). Overall, a modulation of TJ protein expressions and interactions in intestinal epithelial cells can have detrimental pathological consequences for bowel physiological functions.
In order to identify potential human health hazards of these understudied cyanobacterial metabolites - PUW/MIN, their toxicity and ability to affect intestinal epithelial barrier functions were studied employing differentiated Caco-2 cell model.
Section snippets
Material
In the present study, one PUW and three MIN variants were tested (Fig. 1). All the lipopeptides have and identical peptide cycle and differ in the fatty acid moiety:
PUW F possess 3-amino-2hydroxy-4methyl-tetradecanoid acid,
MIN A possess 3-amino-2hydroxy-4methyl-dodecanoic acid,
MIN C possess 3-amino-2hydroxy-4methyl-14-oxo-hexadecanoic acid,
MIN D possess 3-amino-2hydroxy-4methyl-14‑hydroxy‑hexadecanoic acid.
PUW F and MIN A were isolated from Cylindrospermum alatosporum CCALA 988 according to the
Cytotoxic and pro-inflammatory effects of PUW/MIN
PUW F was found to be the most potent compound showing cytotoxicity resulting not only in significant LDH activity (Fig 2A) but also in decrease in total protein concentration (84% and 76% of control, respectively) in two highest concentrations 5 a 10 µM (Fig 2B). Lower PUW F concentrations 1 and 2.5 µM did not reveal either acute cytotoxic effects (Fig 2A) or caspase 3 activation (Supplementary Fig 1). MIN A and C caused significant LDH activity in both highest concentrations too (Fig 2A), but
Discussion
For the first time, specific cellular effects of non-cytotoxic concentrations of cyanobacterial lipopeptides PUW/MIN probably resulting in dysregulation of intestinal epithelial barrier are described in this article.
It is known from the literature that PUW are cytotoxic for human cervical adenocarcinoma HeLa cells (Hrouzek et al., 2012), where 10 µM concentration of PUW F rapidly decreases the viability of the cells, to approximately 20% of the control within the first hour of exposure.
Conclusion
Taken together, PUW F and MIN A and C are shown to be highly cytotoxic compounds for human intestinal epithelial cells. Moreover, these cyanobacterial lipopeptides elicited effects in differentiated Caco-2 cells which could lead to dysregulation of intestinal barrier function and inflammatory responses. Taking into account that these newly recognized compounds, or genetic elements for their biosynthesis, have been recently detected in a variety of different, environmentally prevalent
Authors' contributions
OV – experiments designing and performing, writing and editing the manuscript; JH – isolation of PUW/MIN; LB – LC-MS/MS analysis, methodology writing; PH – writing and editing the manuscript, project administration; PB – review and editing the manuscript, project administration; LK - review and editing the manuscript; LŠ - experiments designing, writing and editing the manuscript, project administration.
Declaration of interests
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgement
We wish to thank Hana Vereščáková for her excellent expert technical assistance. This work was financially supported by Czech National Science Foundation (GACR) project 16-24949S, by the National Program for Sustainability project Algatech Plus - LO1416 (Institute of Microbiology) and by the Institute of Botany by long-term research development project no. RVO 67985939. RECETOX Research Infrastructure was supported by projects LM2018121 and CETOCOEN Excellence Teaming 2 project funded by Czech
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