Persistence of a Neonicotinoid Insecticide, Acetamiprid on Chili (Capsicum annum L.)

Sanyal, Doyeli; Chakma, D.; Alam, Samsul

doi:10.1007/s00128-008-9479-5

Cited by 52 publications

(21 citation statements)

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“…As a promising insecticide, acetamiprid is used for controlling Hemiptera (especially aphids), Thysanoptera, Lepidoptera, and so on . However, acetamiprid is inevitably released into the environment due to its extensive use, and its residues can be detected in a variety of plants . Therefore, long term and intensive use of pesticides may contaminate agricultural land and water, adversely affecting nontarget organisms …”

Section: Introductionmentioning

confidence: 99%

“…3 However, acetamiprid is inevitably released into the environment due to its extensive use, and its residues can be detected in a variety of plants. [4][5][6] Therefore, long term and intensive use of pesticides may contaminate agricultural land and water, adversely affecting nontarget organisms. [7][8][9] The silkworm, Bombyx mori, is an important economic insect that belongs to the order of Lepidoptera.…”

Section: Introductionmentioning

confidence: 99%

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The mechanism of damage by trace amounts of acetamiprid to the midgut of the silkworm, Bombyx mori

Wang

et al. 2019

Environmental Toxicology

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Acetamiprid is widely used for agricultural pest control. However, it remains poorly understood whether the environmental residues of acetamiprid have the potential effects on economic insect. In this study, we evaluated the effects of acetamiprid on silkworm growth and development. The exposure to trace amounts of acetamiprid significantly decreased body weight, viability, and spinning ability. In addition, the activity of trypsin in the midgut was decreased after exposure. DGE and KEGG pathway enrichment analysis revealed that the significantly differentially expressed genes were mainly involved in nutrient metabolism, stress responses, and inflammation pathways. These results, in combination with hematoxylin‐eosin staining and transmission electron microscopy, indicated that acetamiprid could cause oxidative damage to midgut, lead to inflammatory responses, and affect the activities of midgut digestive enzymes, thus resulting in abnormal growth and development. Our findings greatly contributed to the evaluation of the effects of acetamiprid residues on other nontarget beneficial insect.

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Section: Introductionmentioning

confidence: 99%

Section: Introductionmentioning

confidence: 99%

The mechanism of damage by trace amounts of acetamiprid to the midgut of the silkworm, Bombyx mori

Wang

et al. 2019

Environmental Toxicology

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“…Acetamiprid exposure has been proven to have adverse effect on greenhouse workers spraying acetamiprid [8], soil microorganisms [25] and beneficial insects [24]. In recent years, acetamiprid residues in crops are receiving considerable attention due to their potential toxicity to humans [9], [10], and methods for the biotransformation of neonicotinoids are being actively researched. Microbial degradation is considered as an efficient “green” solution to eliminate environmental polluting chemicals [11], [12].…”

Section: Introductionmentioning

confidence: 99%

Microbial Degradation of Acetamiprid by Ochrobactrum sp. D-12 Isolated from Contaminated Soil

et al. 2013

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Neonicotinoid insecticides are one of the most important commercial insecticides used worldwide. The potential toxicity of the residues present in environment to humans has received considerable attention. In this study, a novel Ochrobactrum sp. strain D-12 capable of using acetamiprid as the sole carbon source as well as energy, nitrogen source for growth was isolated and identified from polluted agricultural soil. Strain D-12 was able to completely degrade acetamiprid with initial concentrations of 0–3000 mg·L−1 within 48 h. Haldane inhibition model was used to fit the special degradation rate at different initial concentrations, and the parameters q max, K s and K i were determined to be 0.6394 (6 h)−1, 50.96 mg·L−1 and 1879 mg·L−1, respectively. The strain was found highly effective in degrading acetamiprid over a wide range of temperatures (25–35°C) and pH (6–8). The effects of co-substrates on the degradation efficiency of acetamiprid were investigated. The results indicated that exogenously supplied glucose and ammonium chloride could slightly enhance the biodegradation efficiency, but even more addition of glucose or ammonium chloride delayed the biodegradation. In addition, one metabolic intermediate identified as N-methyl-(6-chloro-3-pyridyl)methylamine formed during the degradation of acetamiprid mediated by strain D-12 was captured by LC-MS, allowing a degradation pathway for acetamiprid to be proposed. This study suggests the bacterium could be a promising candidate for remediation of environments affected by acetamiprid.

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“…The absorption and translocation of acetamiprid in various crops have been previously assessed by researchers. It was reported that acetamiprid dissipated by about 5–21 and 25–38% on day 1 after the application of the recommended dose (5 g a.i./100 L water) and double the recommended dose (10 g a.i./100 L water) in chilli (Sanyal et al ., 2008). The dissipation of acetamiprid residues increased with increasing time after application, reaching 60–69 and 78–89% on day 7, after the application of the recommended and double the recommended doses.…”

Section: Resultsmentioning

confidence: 99%

“…In the Republic of Korea, acetamiprid was registered and has been used since 2001 and its maximum residue limits were established for 32 foodstuffs (Korea Food and Drug Administration, 2010). It was reported that the half‐life value of acetamiprid was 11.1 days under UV light, 25.1 days under sunlight in soil (Gupta et al ., 2008), 1–2 days in field soils (Tokieda et al ., 1999; Hong et al ., 2001), 1.02–1.59 days in the mustard plant (Pramanik et al ., 2006), 1.82 to 2.33 days in tea (Gupta and Shanker, 2008) and 2.24 days in chilli (Sanyal et al ., 2008).…”

Section: Introductionmentioning

confidence: 99%

Determination of acetamiprid residues in zucchini grown under greenhouse conditions: application to behavioral dynamics

Park

Choi

Kim

et al. 2010

Biomedical Chromatography

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A simple analytical method was developed for the determination of acetamiprid residues in zucchini and zucchini leaves grown under greenhouse conditions using liquid chromatography. Residues were confirmed via tandem mass spectrometry in positive-ion electrospray ionization mode. The calibration curves were linear with correlation coefficients in excess of 0.999. The limits of detection and limits of quantification were 0.01 and 0.03 µg/g and 0.02 and 0.06 µg/g, for the zucchini and zucchini leaves, respectively. For validation purposes, recoveries studies were carried out at low and high levels, yielding recovery rates ranged from 85.7 to 92.2% in zucchini and from 90.5 to 101.9% in zucchini leaves, with a relative standard deviation of <12%. The results demonstrated that the pattern of acetamiprid dissipation followed pseudo first-order kinetics with a half-life of 1.9 and 2.5 days, respectively. The residues in zucchini leaves were substantially higher than in the zucchini plant itself. No residues were detected at 7 days post-application. The results of this study suggest that acetamiprid is acceptable for application in/on zucchini under the recommended dosage conditions.

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Persistence of a Neonicotinoid Insecticide, Acetamiprid on Chili (Capsicum annum L.)

Cited by 52 publications

References 1 publication

The mechanism of damage by trace amounts of acetamiprid to the midgut of the silkworm, Bombyx mori

The mechanism of damage by trace amounts of acetamiprid to the midgut of the silkworm, Bombyx mori

Microbial Degradation of Acetamiprid by Ochrobactrum sp. D-12 Isolated from Contaminated Soil

Determination of acetamiprid residues in zucchini grown under greenhouse conditions: application to behavioral dynamics

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