“Forever Chemicals” May Disrupt Brain Development

Summary: Exposure to PFAS, chemicals found in everyday products, can disrupt brain development in zebrafish, a model often used to predict effects in humans. Researchers discovered that PFAS activate specific genes related to behavior changes in zebrafish larvae, particularly those in the ppar gene group.

The study found that exposure during early development caused hyperactivity in the fish, raising concerns about PFAS’ potential impact on human brain development. Further research will explore the neuroactive effects of other PFAS and their risks to human health.

Key Facts:

  • PFAS exposure in zebrafish triggers hyperactivity linked to altered ppar genes.
  • Hyperactivity in fish subsided once PFAS were removed from the environment.
  • The study may have implications for understanding PFAS effects on human brain development.

Source: UFZ

Because of their special properties – heat resistance, water and grease repellence, and high durability – PFAS are used in many everyday products (e.g. cosmetics, outdoor clothing, and coated cookware). But it is precisely these properties that make them so problematic.

“Because some PFAS are chemically stable, they accumulate in the environment and enter our bodies via air, drinking water, and food,” says UFZ toxicologist Prof Dr. Tamara Tal. Even with careful consumption, it is nearly impossible to avoid this group of substances, which has been produced since the 1950s and now includes thousands of different compounds.

This shows a pregnant woman.
Based on these responses, the researchers conclude that PFOS exposure is associated with abnormal consequences – particularly during sensitive developmental phases of the brain. Credit: Neuroscience News

“There is a great need for research, especially when it comes to developing fast, reliable, and cost-effective test systems for assessing the risks of PFAS exposure,” says Tal. So far, the environmental and health consequences have been difficult to assess.

In their current study, the researchers investigated how PFAS exposure affects brain development. To do this, they used the zebrafish model, which is frequently used in toxicology research.

One advantage of this model is that around 70% of the genes found in zebrafish (Danio rerio) are also found in humans. The findings from the zebrafish model can therefore likely be transferred to humans.

In their experiments, the researchers exposed zebrafish to two substances from the PFAS group (PFOS and PFHxS), which have a similar structure. The researchers then used molecular biological and bioinformatic methods to investigate which genes in the brains of the fish larvae exposed to PFAS were disrupted compared to the control fish, which were not exposed.

“In the zebrafish exposed to PFAS, the peroxisome proliferator-activated receptor (ppar) gene group, which is also present in a slightly modified form in humans, was particularly active”, says Sebastian Gutsfeld, PhD student at the UFZ and first author of the study.

“Toxicity studies have shown this to be the case as a result of exposure to PFAS – albeit in the liver. We have now also been able to demonstrate this for the brain”.

But what consequences does an altered activity of the ppar genes triggered by PFAS exposure have for brain development and behaviour of zebrafish larvae? The researchers investigated this in further studies using the zebrafish model. They used the CRISPR/Cas9 method, also known as gene scissors.

“Using genetic scissors, we were able to selectively cut individual or several par genes and prevent them from functioning normally,” explains Gutsfeld.

“We wanted to find out which ppar genes are directly linked to a change in larval behaviour triggered by PFAS exposure”. Proof of the underlying mechanism was directly provided. In contrast to genetically unaltered zebrafish, the knockdown fish in which the gene scissors were used should not show any behavioural changes after exposure to PFAS.

The two behavioural endpoints

In one series of experiments, the researchers continuously exposed zebrafish to PFOS or PFHxS during their early developmental phase between day one and day four, and in another series of experiments, only on day five. On the fifth day, the researchers then observed swimming behaviour. They used two different behavioural endpoints for this purpose.

In one endpoint, swimming activity was measured during a prolonged dark phase. PFAS-exposed fish swam more than fish not exposed to PFAS, whether continuously exposed to PFAS during brain development or shortly before the behaviour test.

Interestingly, hyperactivity was only present when the chemical was around. When the researchers removed PFOS or PFHxS, hyperactivity subsided. In the second endpoint, the startle response after a dark stimulus was measured.

“In zebrafish exposed to PFOS for four days, we observed hyperactive swimming behaviour in response to the stimulus”, says Gutsfeld. In contrast, zebrafish only exposed to PFOS or PFHxS on the fifth day did not have a hyperactive startle response.

Based on these responses, the researchers conclude that PFOS exposure is associated with abnormal consequences – particularly during sensitive developmental phases of the brain. Using knockdown zebrafish, the researchers identified two genes from the ppar group that mediate the behaviour triggered by PFOS.

“Because these genes are also present in humans, it is possible that PFAS also have corresponding effects in humans,” concludes Tal.

The scientists working with Tal want to investigate the neuroactive effects of other PFAS in future research projects and expand the method so that it can ultimately be used to assess the risk of chemicals in the environment, including PFAS.

About this neurodevelopment and environmental neuroscience research news

Author: Susanne Hufe
Source: UFZ
Contact: Susanne Hufe – UFZ
Image: The image is credited to Neuroscience News

Original Research: Open access.
Investigation of peroxisome proliferator-activated receptor genes as requirements for visual startle response hyperactivity in larval zebrafish exposed to structurally similar Per- and Polyfluoroalkyl Substances (PFAS)” by Tamara Tal et al. Environmental Health Perspectives


Abstract

Investigation of peroxisome proliferator-activated receptor genes as requirements for visual startle response hyperactivity in larval zebrafish exposed to structurally similar Per- and Polyfluoroalkyl Substances (PFAS)

Background:

Per- and polyfluoroalkyl Substances (PFAS) are synthetic chemicals widely detected in humans and the environment. Exposure to perfluorooctanesulfonic acid (PFOS) or perfluorohexanesulfonic acid (PFHxS) was previously shown to cause dark-phase hyperactivity in larval zebrafish.

Objectives:

The objective of this study was to elucidate the mechanism by which PFOS or PFHxS exposure caused hyperactivity in larval zebrafish.

Methods:

Swimming behavior was assessed in 5-d postfertilization (dpf) larvae following developmental (1–4 dpf) or acute (5 dpf) exposure to 0.43–7.86μ⁢M PFOS, 7.87–120μ⁢M PFHxS, or 0.4% dimethyl sulfoxide (DMSO). After developmental exposure and chemical washout at 4 dpf, behavior was also assessed at 5–8 dpf. RNA sequencing was used to identify differences in global gene expression to perform transcriptomic benchmark concentration–response (BMCT) modeling, and predict upstream regulators in PFOS- or PFHxS-exposed larvae.

CRISPR/Cas9-based gene editing was used to knockdown peroxisome proliferator-activated receptors (ppars) pparaa/abpparda/db, or pparg at day 0. Knockdown crispants were exposed to 7.86μ⁢M PFOS or 0.4% DMSO from 1–4 dpf and behavior was assessed at 5 dpf. Coexposure with the ppard antagonist GSK3787 and PFOS was also performed.

Results:

Transient dark-phase hyperactivity occurred following developmental or acute exposure to PFOS or PFHxS, relative to the DMSO control. In contrast, visual startle response (VSR) hyperactivity only occurred following developmental exposure and was irreversible up to 8 dpf. Similar global transcriptomic profiles, BMCT estimates, and enriched functions were observed in PFOS- and PFHxS-exposed larvae, and ppars were identified as putative upstream regulators. Knockdown of pparda/db, but not pparaa/ab or pparg, blunted PFOS-dependent VSR hyperactivity to control levels. This finding was confirmed via antagonism of ppard in PFOS-exposed larvae.

Discussion:

This work identifies a novel adverse outcome pathway for VSR hyperactivity in larval zebrafish. We demonstrate that developmental, but not acute, exposure to PFOS triggered persistent VSR hyperactivity that required ppard function.

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