Imidacloprid induces adverse effects on fish early life stages that are more severe in Japanese medaka (Oryzias latipes) than in zebrafish (Danio rerio)

Vignet, Caroline; Cappello, Tiziana; Fu, Qiuguo; Lajoie, Kévin; Marco, Giuseppe De; Clérandeau, Christelle; Mottaz, Hélène; Maisano, Maria; Hollender, Juliane; Schirmer, Kristin; Cachot, Jérôme

doi:10.1016/j.chemosphere.2019.03.002

Cited by 76 publications

(47 citation statements)

References 47 publications

(48 reference statements)

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“…There is a lot of evidence that imidacloprid has the potential to adversely impact ecosystems and human health. For instance, it was gradually discovered that imidacloprid is toxic to humans, and that imidacloprid is lethal to non-target organisms such as bats, earthworms, bees, fish, and shrimp (Table 1) [17][18][19][20][21]. Inhibits thyroid hormone secretion, causes abnormal alignment of the spermatogenic epithelium, epididymal hyperplasia, and oligospermia in male lizards [28][29][30] 7.…”

Section: Toxicity Of Imidaclopridmentioning

confidence: 99%

“…Inhibits thyroid hormone secretion, causes abnormal alignment of the spermatogenic epithelium, epididymal hyperplasia, and oligospermia in male lizards [28][29][30] 7. Brown shrimp 0.5 g•L −1 Sublethal effect, especially in dehulling delay and growth reduction [20,31] 8. Zebrafish (Danio rerio) 400 µg•L −1 Sublethal effect, especially in dehulling delay and growth reduction [20] 9.…”

Section: Toxicity Of Imidaclopridmentioning

confidence: 99%

“…Brown shrimp 0.5 g•L −1 Sublethal effect, especially in dehulling delay and growth reduction [20,31] 8. Zebrafish (Danio rerio) 400 µg•L −1 Sublethal effect, especially in dehulling delay and growth reduction [20] 9. Medaka (Japanese rice fish) 0.2 µg•L −1 Causes deformity and reduces growth [20] 10.…”

Section: Toxicity Of Imidaclopridmentioning

confidence: 99%

“…Zebrafish (Danio rerio) 400 µg•L −1 Sublethal effect, especially in dehulling delay and growth reduction [20] 9. Medaka (Japanese rice fish) 0.2 µg•L −1 Causes deformity and reduces growth [20] 10.…”

Section: Toxicity Of Imidaclopridmentioning

confidence: 99%

“…Although imidacloprid has a fast photolysis rate, it still exists in the water column of the aquatic system [47]. Neonicotinoid concentrations can affect aquaculture populations [48], and imidacloprid has a sublethal effect on brown shrimp and zebrafish in the natural environment, especially in dehulling delay and growth reduction [20,31].…”

Section: Toxicity To Aquatic Organismsmentioning

confidence: 99%

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Insights into the Toxicity and Degradation Mechanisms of Imidacloprid Via Physicochemical and Microbial Approaches

Pang

Lin

Zhang

et al. 2020

Toxics

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Imidacloprid is a neonicotinoid insecticide that has been widely used to control insect pests in agricultural fields for decades. It shows insecticidal activity mainly by blocking the normal conduction of the central nervous system in insects. However, in recent years, imidacloprid has been reported to be an emerging contaminant in all parts of the world, and has different toxic effects on a variety of non-target organisms, including human beings, due to its large-scale use. Hence, the removal of imidacloprid from the ecosystem has received widespread attention. Different remediation approaches have been studied to eliminate imidacloprid residues from the environment, such as oxidation, hydrolysis, adsorption, ultrasound, illumination, and biodegradation. In nature, microbial degradation is one of the most important processes controlling the fate of and transformation from imidacloprid use, and from an environmental point of view, it is the most promising means, as it is the most effective, least hazardous, and most environmentally friendly. To date, several imidacloprid-degrading microbes, including Bacillus, Pseudoxanthomonas, Mycobacterium, Rhizobium, Rhodococcus, and Stenotrophomonas, have been characterized for biodegradation. In addition, previous studies have found that many insects and microorganisms have developed resistance genes to and degradation enzymes of imidacloprid. Furthermore, the metabolites and degradation pathways of imidacloprid have been reported. However, reviews of the toxicity and degradation mechanisms of imidacloprid are rare. In this review, the toxicity and degradation mechanisms of imidacloprid are summarized in order to provide a theoretical and practical basis for the remediation of imidacloprid-contaminated environments.

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Section: Toxicity Of Imidaclopridmentioning

confidence: 99%

Section: Toxicity Of Imidaclopridmentioning

confidence: 99%

Section: Toxicity Of Imidaclopridmentioning

confidence: 99%

Section: Toxicity Of Imidaclopridmentioning

confidence: 99%

Section: Toxicity To Aquatic Organismsmentioning

confidence: 99%

See 3 more Smart Citations

Insights into the Toxicity and Degradation Mechanisms of Imidacloprid Via Physicochemical and Microbial Approaches

Pang

Lin

Zhang

et al. 2020

Toxics

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Exposure to Contaminated River Water is Associated with Early Hatching and Dysregulation of Gene Expression in Early Life Stages of the Endangered Copper Redhorse (Moxostoma hubbsi)

Marchand

Barst

Boulanger

et al. 2022

Enviro Toxic and Chemistry

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The copper redhorse (Moxostoma hubbsi) is an endangered fish that spawns exclusively in the Richelieu River (Quebec, Canada). Tributaries of the Richelieu are contaminated with high levels of current‐use pesticides, which may impact early–life stage (ELS) copper redhorse and other native fishes. We assessed the effects of exposure to contaminated river water on ELS copper redhorse and river redhorse (Moxostoma carinatum), a related fish that shares the copper redhorse's spawning grounds and nursery habitat. A riverside flow‐through system was used to expose copper and river redhorse embryos (1000 each) to Richelieu River water or laboratory water as a control. Fish were maintained until 14 days posthatch, and water samples were taken daily for chemical analysis. Following a heavy rain event, concentrations of two neonicotinoid pesticides, clothianidin and thiamethoxam, exceeded water quality guidelines for aquatic life (20 ng/L). Using nontargeted screening, we tentatively identified an additional 24 pharmaceutical and personal care products and 23 pesticides in river water. Effects of river water on ELS fish were observed in both species, but the copper redhorse appeared to be more sensitive. Fish exposed to river water hatched 10.7 (copper redhorse) and 2.4 (river redhorse) cumulative degree days earlier than controls. Copper redhorse survival was significantly lower in river water (73 ± 16%) compared to laboratory water (93 ± 3%), whereas river redhorse survival was similar between treatments (84 ± 6% and 89 ± 4%, respectively). Sequencing of copper redhorse larvae RNA revealed 18 differentially expressed genes (DEGs) following 14 days of exposure to river water. Eight up‐regulated DEGs were linked to immune function and injury response, and seven down‐regulated DEGs were involved with digestion and nutrient absorption. The present study provided valuable data on the effects of ELS exposure to a real‐world mixture of contaminants in two fish species of concern. Environ Toxicol Chem 2022;41:1950–1966. © 2022 SETAC

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Chronic Exposure to Environmentally Relevant Concentrations of Imidacloprid Impact Survival and Ecologically Relevant Behaviors of Fathead Minnow Larvae

Jeninga,

Wallace,

Victoria

et al. 2023

Enviro Toxic and Chemistry

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Imidacloprid (IM) has emerged as a contaminant of concern in several areas within the United States due to its frequent detection in aquatic ecosystems and its pseudo‐persistence, which pose potential risks to nontarget species. We evaluated the sublethal toxicity of IM to fathead minnow larvae following chronic exposure beginning just after fertilization. Our in silico analysis and in vivo bioassays suggest that IM has a low binding affinity for the vertebrate nicotinate acetylcholine receptor (nAChR), as expected. However, chronic exposure to ≥0.16 µg IM/L reduced survival by 10%, and exposure to ≥18 µg IM/L reduced survival by approximately 20%–40%. Surviving fish exposed to ≥0.16 µg IM/L showed reduced growth, altered embryonic motor activity, and premature hatching. Furthermore, a significant proportion of fish exposed to ≥0.16 µg IM/L were slower to respond to vibrational stimuli and slower to swim away, indicating that chronic exposure to IM has the potential to impair the ability of larvae to escape predation. The adverse health effects we observed indicate that chronic exposure to environmentally relevant concentrations of IM may elicit sublethal responses that culminate in a significant increase in mortality during early life stages, ultimately translating to reduced recruitment in wild fish populations. Environ Toxicol Chem 2023;00:1–9. © 2023 SETAC

show abstract

Imidacloprid induces adverse effects on fish early life stages that are more severe in Japanese medaka (Oryzias latipes) than in zebrafish (Danio rerio)

Cited by 76 publications

References 47 publications

Insights into the Toxicity and Degradation Mechanisms of Imidacloprid Via Physicochemical and Microbial Approaches

Insights into the Toxicity and Degradation Mechanisms of Imidacloprid Via Physicochemical and Microbial Approaches

Exposure to Contaminated River Water is Associated with Early Hatching and Dysregulation of Gene Expression in Early Life Stages of the Endangered Copper Redhorse (Moxostoma hubbsi)

Chronic Exposure to Environmentally Relevant Concentrations of Imidacloprid Impact Survival and Ecologically Relevant Behaviors of Fathead Minnow Larvae

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