Xenobiotic Exposure and Migraine-Associated Signaling: A Multimethod Experimental Study Exploring Cellular Assays in Combination with Ex Vivo and In Vivo Mouse Models
- PMID: 37909725
- PMCID: PMC10619430
- DOI: 10.1289/EHP12413
Xenobiotic Exposure and Migraine-Associated Signaling: A Multimethod Experimental Study Exploring Cellular Assays in Combination with Ex Vivo and In Vivo Mouse Models
Abstract
Background: Mechanisms for how environmental chemicals might influence pain has received little attention. Epidemiological studies suggest that environmental factors such as pollutants might play a role in migraine prevalence. Potential targets for pollutants are the transient receptor potential (TRP) channels ankyrin 1 (TRPA1) and vanilloid 1 (TRPV1), which on activation release pain-inducing neuropeptide calcitonin gene-related peptide (CGRP).
Objective: In this study, we aimed to examine the hypothesis that environmental pollutants via TRP channel signaling and subsequent CGRP release trigger migraine signaling and pain.
Methods: A calcium imaging-based screen of environmental chemicals was used to investigate activation of migraine pain-associated TRP channels TRPA1 and TRPV1. Based on this screen, whole-cell patch clamp and in silico docking were performed for the pesticide pentachlorophenol (PCP) as proof of concept. Subsequently, PCP-mediated release of CGRP and vasodilatory responses of cerebral arteries were investigated. Finally, we tested whether PCP could induce a TRPA1-dependent induction of cutaneous hypersensitivity in vivo in mice as a model of migraine-like pain.
Results: A total of 16 out of the 52 screened environmental chemicals activated TRPA1 at 10 or . None of the investigated compounds activated TRPV1. Using PCP as a model of chemical interaction with TRPA1, in silico molecular modeling suggested that PCP is stabilized in a lipid-binding pocket of TRPA1 in comparison with TRPV1. In vitro, ex vivo, and in vivo experiments showed that PCP induced calcium influx in neurons and resulted in a TRPA1-dependent CGRP release from the brainstem and dilation of cerebral arteries. In a mouse model of migraine-like pain, PCP induced a TRPA1-dependent increased pain response ().
Discussion: Here we show that multiple environmental pollutants interact with the TRPA1-CGRP migraine pain pathway. The data provide valuable insights into how environmental chemicals can interact with neurobiology and provide a potential mechanism for putative increases in migraine prevalence over the last decades. https://doi.org/10.1289/EHP12413.
Figures

![Figures 2A and 2D are line graphs, plotting uppercase i (picoampere), ranging from negative 0.5 to 1 in increments of 0.5 and uppercase i (nanoampere), ranging from negative 5 to 10 in increments of 5 (y-axis) across membrane potential (millivolt), ranging from negative 100 to 100 in increments of 50 (x-axis) for wash, control, pentachlorophenol, and pentachlorophenol plus H C-030031 (transient receptor potential ankyrin 1 antagonist); and control, pentachlorophenol after 50 seconds, and pentachlorophenol plus H C-030031 (transient receptor potential ankyrin 1 antagonist). Figures 2B and 2E are line graphs, plotting uppercase i (picoampere), ranging from negative 5 to 10 in increments of 5 (y-axis) across time (second), ranging from 0 to 100 in increments of 50 and 0 to 150 in increments of 50 (x-axis) for pentachlorophenol and pentachlorophenol plus H C-030031 (transient receptor potential ankyrin 1 antagonist). Figures 2C and 2F are bar graphs, plotting uppercase i (nanoampere), ranging from 0 to 1 in increments of 0.2 and 0 to 10 in increments of 2 (y-axis) across control, pentachlorophenol, and pentachlorophenol plus H C-030031 (transient receptor potential ankyrin 1 antagonist); and control, pentachlorophenol peak, pentachlorophenol after 50 second, and pentachlorophenol plus H C-030031 (transient receptor potential ankyrin 1 antagonist) (x-axis). Figure 2G is a line graph, plotting picoampere per picofarad, ranging from 0 to negative 300 in decrements of 100 (y-axis) across [pentachlorophenol], micromolar, ranging from 0 to 1 in unit increments, 1 to 3 in increments of 2, 3 to 10 in increments of 7, and 10 to 30 in increments of 20 (x-axis). Figure 2H is a line graph, plotting current (picoampere), ranging from negative 1000 to 0 in increments of 200 (y-axis) across time (second), ranging from 0 to 150 in increments of 50 (x-axis) for pentachlorophenol. Figure 2I is a bar graph, plotting current (nanoampere), ranging from 0 to negative 800 in decrements of 200 (y-axis) across control and pentachlorophenol (x-axis).](https://cdn.ncbi.nlm.nih.gov/pmc/blobs/21f0/10619430/033659777aff/ehp12413_f2.gif)

![[Figures 4A to 4D are line graphs titled wild type brainstem (trigeminal nucleus caudalis) supercinnamaldehyde, transient receptor potential channels ankyrin 1 begin superscript negative per negative end superscript Brainstem (trigeminal nucleus caudalis) supercinnamaldehyde, Wild type Brainstem (trigeminal nucleus caudalis) pentachlorophenol, transient receptor potential channels ankyrin 1 begin superscript negative per negative end superscript Brainstem (trigeminal nucleus caudalis) pentachlorophenol, plotting calcitonin gene-related peptide (normalized to basal), ranging from 0 to 12 in increments of 2 (y-axis) across basal, 1 micromolar, 10 micromolar, and 100 micromolar (x-axis) for supercinnamaldehyde and vehicle; supercinnamaldehyde and vehicle; pentachlorophenol and vehicle; ; pentachlorophenol and vehicle, respectively. Figure 4E is a line graph titled myography of basilar artery, plotting dilation (percentage of 3 asterisk 10 to 7 molar U 46619), ranging from negative 100 to 50 in increments of 50 (y-axis) across log of [pentachlorophenol molar], ranging from negative 7 to 4 in unit increments (x-axis) for transient receptor potential channels ankyrin 1 begin superscript negative per negative end superscript, wild type plus calcitonin gene-related peptide antibodies, and wild type.](https://cdn.ncbi.nlm.nih.gov/pmc/blobs/21f0/10619430/5855ace4d5ca/ehp12413_f4.gif)
![Figures 5A and 5D are bar graphs titled acute hind paw sensitivity, plotting square root transformation [50 percent withdrawal threshold, gram], ranging from 0.0 to 1.5 in increments of 0.5 (y-axis) across baseline, 2 hours, and 4 hours (x-axis) for vehicle and pentachlorophenol; and transient receptor potential channels ankyrin 1 begin superscript negative per negative end superscript vehicle, transient receptor potential channels ankyrin 1 begin superscript negative per negative end superscript pentachlorophenol, and wild type pentachlorophenol. Figure 5B is a line graph titled chronic hind paw sensitivity, plotting square root transformation [50 percent withdrawal threshold, gram], ranging from 0.0 to 1.5 in increments of 0.5 (y-axis) across day 1, day 5, day 6, day 8, and day 10 (x-axis) for vehicle and pentachlorophenol. Figure 5C is a graph, plotting time on rotarod (second), ranging from 0 to 200 in increments of 50 (y-axis) across 2 hours, 4 hours, and controls (x-axis) for vehicle, saline, pentachlorophenol, and mida. Figure 5E is a set of three graphs, plotting time on rotarod (second), ranging from 0 to 200 in increments of 50 (y-axis) across transient receptor potential channels ankyrin 1 begin superscript negative per negative end superscript vehicle, transient receptor potential channels ankyrin 1 begin superscript negative per negative end superscript pentachlorophenol, and wild type pentachlorophenol; transient receptor potential channels ankyrin 1 begin superscript negative per negative end superscript vehicle, transient receptor potential channels ankyrin 1 begin superscript negative per negative end superscript pentachlorophenol, and wild type pentachlorophenol; and saline and mida (x-axis) for 2 hours, 4 hours, and controls.](https://cdn.ncbi.nlm.nih.gov/pmc/blobs/21f0/10619430/99d91a7fb3a0/ehp12413_f5.gif)

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