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Method Article
A detailed experimental protocol is presented in this paper for the evaluation of neurobehavioral toxicity of environmental pollutants using a zebrafish larvae model, including the exposure process and tests for neurobehavioral indicators.
Recent years more and more environmental pollutants have been proved neurotoxic, especially at the early development stages of organisms. Zebrafish larvae are a preeminent model for the neurobehavioral study of environmental pollutants. Here, a detailed experimental protocol is provided for the evaluation of the neurotoxicity of environmental pollutants using zebrafish larvae, including the collection of the embryos, the exposure process, neurobehavioral indicators, the test process, and data analysis. Also, the culture environment, exposure process, and experimental conditions are discussed to ensure the success of the assay. The protocol has been used in the development of psychopathic drugs, research on environmental neurotoxic pollutants, and can be optimized to make corresponding studies or be helpful for mechanistic studies. The protocol demonstrates a clear operation process for studying neurobehavioral effects on zebrafish larvae and can reveal the effects of various neurotoxic substances or pollutants.
In recent years more and more environmental pollutants have been proved neurotoxic1,2,3,4. However, the assessment of neurotoxicity in vivo after exposure to environmental pollutants is not as easy as that of endocrine disruption or developmental toxicity. In addition, early exposure to pollutants, especially at environmentally relevant doses, has attracted increasing attention in toxicity studies5,6,7,8.
Zebrafish is being established as an animal model fit for neurotoxicity studies during early development after exposure to environmental pollutants. Zebrafish are vertebrates that develop faster than other species after fertilization. The larvae do not need to be fed because the nutrients in the chorion are enough for sustain them for 7 days postfertilization (dpf)9. Larvae come out from the chorion at ~2 dpf and develop behaviors such as swimming and turning that can be observed, tracked, quantified, and analyzed automatically using behavior instruments10,11,12,13 starting at 3-4 dpf14,15,16,17,18. In addition, high-throughput tests can also be realized by behavior instruments. Thus, zebrafish larvae are an outstanding model for the neurobehavioral study of environmental pollutants19. Here, a protocol is offered using high-throughput monitoring to study the neurobehavioral toxicity of environmental pollutants on zebrafish larvae under light stimuli.
Our lab has studied the neurobehavioral toxicity of 2,2',4,4'-tetrabromodiphenyl ether (BDE-47)20,21, 6'-Hydroxy/Methoxy-2,2',4,4'-tetrabromodiphenyl ether (6-OH/MeO-BDE-47)22, deca-brominated diphenyl ether (BDE-209), lead, and commercial chlorinated paraffins23 using the presented protocol. Many labs also use the protocol to study the neurobehavioral effects of other pollutants on larvae or adult fish24,25,26,27. This neurobehavioral protocol was used to help provide mechanistic support showing that low-dose exposure to bisphenol A and replacement bisphenol S induced premature hypothalamic neurogenesis in embryonic zebrafish27. In addition, some researchers optimized the protocol to perform corresponding studies. A recent study eliminated the toxicity of amyloid beta (Aβ) in an easy, high-throughput zebrafish model using casein-coated gold nanoparticles (βCas AuNPs). It showed that βCas AuNPs in systemic circulation translocated across the blood-brain barrier of zebrafish larvae and sequestered intracerebral Aβ42, eliciting toxicity in a nonspecific, chaperone-like manner, which was supported by behavioral pathology28.
Locomotion, path angle, and social activity are three neurobehavioral indicators used to study the neurotoxicity effects of zebrafish larvae after exposure to pollutants in the presented protocol. Locomotion is measured by the swimming distance of larvae and can be damaged after exposure to pollutants. Path angle and social activity are more closely related with the function of the brain and the central nervous system29. The path angle refers to the angle of the path of animal motion relative to the swimming direction30. Eight angle classes from ~-180°-~+180° are set in the system. To simplify the comparison, six classes in the final outcome are defined as routine turns (-10° ~0°, 0° ~+10°), average turns (-10° ~-90°, +10° ~+90°), and responsive turns (-180° ~-90°, +90° ~+180°) according to our previous studies21,22. Two-fish social activity is fundamental of group shoaling behavior; here a distance of < 0.5 cm between two larvae valid is defined as social contact.
The protocol presented here demonstrates a clear process for studying neurobehavioral effects on zebrafish larvae and provides a way to reveal the neurotoxicity effects of various substances or pollutants. The protocol will benefit researchers interested in studying the neurotoxicity of environmental pollutants.
The protocol is in accordance with guidelines approved by the Animal Ethics Committee of Tongji University.
1. Zebrafish embryo collection
2. Preparation before exposure
3. Exposure of embryos
4. Preparation for the behavior test
5. Behavioral test
6. Data analysis
Here, we describe a protocol for studying the neurobehavioral effects of environmental pollutants using zebrafish larvae under light stimuli. The locomotion, path angle, and social activity tests are defined in the introduction. The setup of the microplates in the locomotion and path angle tests and the images of the software are shown below. In addition, our own research results are presented as examples. Two studies present the locomotion and path angle effects after exposure to BDE-47 ...
This work provides a detailed experimental protocol to evaluate the neurotoxicity of environmental pollutants using zebrafish larvae. Zebrafish go through the process from embryos to larvae during the exposure period, which means that good care of the embryos and larvae is essential. Anything that affects the development of the embryos and larvae can influence the final result. Here the culture environment, exposure process, and experimental conditions are discussed to ensure the success of the whole assay.
The authors have nothing to disclose.
The authors are grateful for the financial support by the National Natural Science Foundation of China (21876135 and 21876136), the National Major Science and Technology Project of China (2017ZX07502003-03, 2018ZX07701001-22), the Foundation of MOE-Shanghai Key Laboratory of Children's Environmental Health (CEH201807-5), and Swedish Research Council (No. 639-2013-6913).
Name | Company | Catalog Number | Comments |
48-well-microplate | Corning | 3548 | Embyros housing |
6-well-microplate | Corning | 3471 | Embyros housing |
BDE-47 | AccuStandard | 5436-43-1 | Pollutant |
DMSO | Sigma | 67-68-5 | Cosolvent |
Microscope | Olympus | SZX 16 | Observation instrument |
Pipette | Eppendorf | 3120000267 | Transfer solution |
Zebrabox | Viewpoint | ZebraBox | Behavior instrument |
Zebrafish | Shanghai FishBio Co., Ltd. | Tubingen | Zebrafish supplier |
ZebraLab | Viewpoint | ZebraLab | Behavior software |
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