In
animal species, the brain–gut axis is a complex bidirectional
network between the gastrointestinal (GI) tract and the central nervous
system (CNS) consisting of numerous microbial, immune, neuronal, and
hormonal pathways that profoundly impact organism development and
health. Although nanoplastics (NPs) have been shown to cause intestinal
and neural toxicity in fish, the role of the neurotransmitter and
intestinal microbiota interactions in the underlying mechanism of
toxicity, particularly at environmentally relevant contaminant concentrations,
remains unknown. Here, the effect of 44 nm polystyrene nanoplastics
(PS-NPs) on the brain–intestine–microbe axis and embryo–larval
development in zebrafish (Danio rerio) was investigated.
Exposure to 1, 10, and 100 μg/L PS-NPs for 30 days inhibited
growth and adversely affected inflammatory responses and intestinal
permeability. Targeted metabolomics analysis revealed an alteration
of 42 metabolites involved in neurotransmission. The content of 3,4-dihydroxyphenylacetic
acid (DOPAC; dopamine metabolite formed by monoamine oxidase activity)
was significantly decreased in a dose-dependent manner after PS-NP
exposure. Changes in the 14 metabolites correlated with changes to
3 microbial groups, including Proteobacteria, Firmicutes, and Bacteroidetes, as compared
to the control group. A significant relationship between Firmicutes and homovanillic acid (0.466, Pearson correlation coefficient) was
evident. Eight altered metabolites (l-glutamine (Gln), 5-hydroxyindoleacetic
acid (5-HIAA), serotonin, 5-hydroxytryptophan (5-HTP), l-cysteine
(Cys), l-glutamic acid (Glu), norepinephrine (NE), and l-tryptophan (l-Trp)) had a negative relationship with Proteobacteria although histamine (His) and acetylcholine
chloride (ACh chloride) levels were positively correlated with Proteobacteria. An Associated Network analysis showed that Firmicutes and Bacteroidetes were highly
correlated (0.969). Furthermore, PS-NPs accumulated in the gastrointestinal
tract of offspring and impaired development of F1 (2 h post-fertilization)
embryos, including reduced spontaneous movements, hatching rate, and
length. This demonstration of transgenerational deficits is of particular
concern. These findings suggest that PS-NPs cause intestinal inflammation,
growth inhibition, and restricted development of zebrafish, which
are strongly linked to the disrupted regulation within the brain–intestine–microbiota
axis. Our study provides insights into how xenobiotics can disrupt
the regulation of brain–intestine–microbiota and suggests
that these end points should be taken into account when assessing
environmental health risks of PS-NPs to aquatic organisms.