Browsing by Author "McCulloch, Megan"

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    Neurological risk of prolonged low dose exposure to imidacloprid in zebrafish
    (Stellenbosch : Stellenbosch University, 2022-11) McCulloch, Megan; Kellermann, Tracy; Smith, Carine; Faculty of Medicine and Health Sciences. Dept. of Medicine. Division of Clinical Pharmacology.
    ENGLISH ABSTRACT: Imidacloprid (IMI) is a systemic neonicotinoid insecticide intended to replace the organophosphate pesticides in agriculture. Extensive use of these pesticides increases the risk to the environment and non-target organisms such as humans due to their potential bioaccumulation and toxicity. Researchers studying the effect of IMI on human nicotinic receptors (α4β2) have reported that IMI may have more substantial side effects on humans than originally anticipated. This research project aimed to assess the possibility of long-term neurological risks following prolonged, low dose IMI exposure within an in vivo zebrafish model. Methods A protein precipitation extraction from zebrafish brain, liver and gill homogenate was applied followed by LC-MS/MS detection of neurotransmitters and IMI and its primary metabolites. Protein precipitation was conducted using methanol:acetonitrile (1:1 v/v) as the precipitating solvent. Phenethylamine-d4 and IMI-d4 were used as internal standards for the neurotransmitter and IMI LC-MS/MS methods, respectively. For the neurotransmitters, chromatographic separation was achieved using a Poroshell column (3.0 x 100 mm, 2.7 μm) using a gradient elution mode at a flow rate of 0.45 mL/min and an analysis time of 7 min. Mobile phase A and B consisted of water with 0.1% formic acid and acetonitrile, respectively. For IMI and its metabolites, chromatographic separation was achieved using a biphenyl column (2.1 x 100 mm, 2.7 μm) with gradient elution at a flow rate of 0.4 mL/min. The total analysis time was 8.5 min. Mobile phase A and B consisted of water and methanol respectively, both with 5 mM ammonium formate and 0.1% formic acid. The two developed methods underwent a partial validation to certify that both methods were precise, accurate and reliable. Zebrafish larvae were exposed to IMI at four and five days post fertilisation to determine the no observed adverse effect level (NOAEL) of IMI. After this, adult zebrafish were exposed to the NOAEL concentration for 21 days. Key endpoints included behaviour indicative of neurocognitive decline and possible bioaccumulation in the adult zebrafish brain, liver and gills. Neurotransmitter concentrations were measured in the adult zebrafish brain tissue at the end of the treatment period to evaluate changes in neurotransmitter signalling and potential neurological risks using the developed LC-MS/MS method. Bioaccumulation of IMI and its metabolites in zebrafish brain, liver and gills was evaluated using LC-MS/MS. Results The calibration curve fits a quadratic (weighted 1/C) regression over the concentration range of 31.3 - 1000 ng/mL for acetylcholine, gamma-aminobutyric acid, serotonin and dopamine. The calibration curve for IMI and its metabolites fits a quadratic (weighted 1/C) regression over the concentration range of 1.95 - 125 ng/Ml for imidacloprid-urea and IMI, 0.244 - 125 ng/mL for desnitro-imidacloprid and 3.91 - 125 ng/mL for 5-hydro imidacloprid. The NOAEL of IMI in zebrafish larvae was determined to be 2.5 μg/L. No significant morphological changes were observed in the adult zebrafish during the treatment period. Behavioural changes observed during the pesticide exposure period included decrease in appetite of the treatment group. The treatment group was also observed swimming at the bottom of the tank in comparison to the control group. Although IMI, IMI-urea and desnitro-IMI could not be detected in any of the tissue specimens, 5-hydro IMI was detected at relatively high concentrations in the liver (0.793 ng/mg tissue) and gill epithelial tissue (117 ng/mg tissue). Only concentrations of gamma-aminobutyric acid and acetylcholine were detected and quantified in both the treated and control group. The treated group showed a 1.4-fold decrease and 1.9-fold increase in acetylcholine and gamma-aminobutyric acid, respectively in comparison to the control. Serotonin and dopamine could not be detected due to their levels being below the limit of quantitation of this method. Conclusion Robust LC-MS/MS methods were developed for the detection and quantitation of IMI, desnitro-imidacloprid, imidacloprid-urea and 5-hydro-imidacloprid, as well as serotonin, dopamine, acetylcholine and gamma-aminobutyric acid neurotransmitters in 200 μL zebrafish brain, liver and gill epithelial tissue homogenate. The behavioural changes observed in the adult zebrafish could be an indication of one of two things, anxiety or sedative effect. This is verified by the increase in gamma-aminobutyric acid neurotransmitter levels. Together with the evaluation of bioaccumulation of imidacloprid and its metabolites within the brain, liver and gill epithelial tissue of zebrafish, this study provides an indication of the potential risk to human health following chronic neonicotinoid exposure. Overall, our findings further contribute to existing literature and suggest that IMI does pose a threat to more than just insects and therefore requires further investigation.