Abstract
In order to explore the relationship between the structure and the toxicity to honey bees of seven-membered aza-bridged neonicotinoids, 16 novel seven-membered aza-bridged neonicotinoid analogues are synthesized by replacing the pyridine ring, and changing the substituents on the pyridine ring, the electron-withdrawing group NO2 and the imidazole ring of our previously developed aza-bridged neonicotinoid 1-[(6-chloropyridin-3-yl)methyl)]-10-(2,5-dimethylphenyl)-9-nitro-2,3,5,6,7,8-hexahydro-1H-5,8-epiminoimidazo azepine (
Introduction
Neonicotinoids have played an important role in the control of pests, particularly in sucking pests, coleopterans, and dipterans. 1 They are used worldwide, accounting for more than one-fourth of the global insecticide market.2,3 However, more and more research has found that, after more than 20 years of use, neonicotinoids represent a major threat to bees through increased mortality and decreased colony establishment, a condition which is known as colony collapse disorder (CCD).4–8 Bees contribute to about 80% of insect pollination, 9 so it is imperative to verify the causes of bee colony losses, which may threaten plant systems based on the key role of bees in pollination. It has been reported that imidacloprid-treated bees move more actively at first and then become exhausted. In addition, the foraging ability of bees may be reduced by low doses of neonicotinoids, which would lead to the loss of the weight and even death.5–10 At the same time, the survival of worker bees significantly decreased on a large scale. 11 These severe effects have resulted in the ban of three kinds of neonicotinoid: imidacloprid, clothianidin, and thiamethoxam in the European Union from May 2018, 12 and much more attention has been directed toward studying the toxicity of neonicotinoids to honey bees. 13 Thus, it is important to explore neonicotinoids with low bee toxicity. Novel neonicotinoid insecticides with low bee toxicity have gradually been developed, for example, sulfoxaflor14,15 and flupyradifurone16,17 are new members of the neonicotinoid family that act via the same mechanism, that is, as agonists of postsynaptic nicotinic acetylcholine receptors (nAChRs; Figure 1).

Some commercial nAChRs compounds.
The most recent one is reported to be an antagonist of nAChRs. 18 Even sulfoxaflor was banned by France in January 2020. Thus, the exploration of the relationship between structure change and bee toxicity is beneficial for finding new insecticidal lead compounds.
In our previous work, seven-membered aza-bridged neonicotinoid analogues were designed and synthesized on the basis of novel seven-membered oxa-bridged compounds and aza-bridged neonicotinoid analogues.
19
Unfortunately, the product with the highest activity of this series (compound

An aza-bridged compound.
In order to explore the relationship between the structure and bee toxicity and to decrease the bee toxicity by structure modification, we selected seven-membered aza-bridged neonicotinoid

The optimization of the
Results and discussion
Synthesis of the intermediates
The syntheses of the intermediates are summarized in Scheme 1 and the details are available in the experimental section. Intermediate

Synthetic routes to the intermediates.
To obtain the intermediate
Intermediates
Intermediate
General synthesis of the compounds
The target compounds were obtained by the reaction of the above-mentioned synthetic intermediates (

General synthesis for target compounds.
Insecticidal activity and the bee toxicity of the synthesized compounds
Compounds
Insecticidal activities of the target compounds against cowpea aphids.
The insecticidal activities of the synthesized compounds were tested at 100 mg L−1. When the mortality of the compound reached 100%, the concentration was decreased to 20 mg L−1 and the bioactivity was tested again. When the mortality was greater than 50% at 20 mg L−1, LC50 value was obtained.
Compounds possessing the feature structures of commercialized neonicotinoids were next synthesized (
These findings again indicated the importance of the N-[(6-chloro-3-pyridyl)methyl] group. Neonicotinoids bear-ing a CN group are regarded as insecticides with low bee toxicity,
23
so a cyano group
Next, the bee toxicities of the synthesized compounds with higher insecticidal activity were determined. The bee contact toxicities of the compounds are listed in Table 2.
Bee acute contact toxicity of several of the prepared compounds.
Coefficient of determination of the toxic regression equation, which represents the goodness of fit of the toxic regression equation.
The grade of the bee toxicity—Extreme toxicity: A; high toxicity: B; moderate toxicity: C; low toxicity: D.
All the tested compounds exhibited lower contact toxicity toward honey bees than
The bee oral toxicities of some of the prepared compounds with high insecticidal activity are listed in Table 3. These compounds all exhibited lower bee oral toxicity than
Bee acute oral toxicity of several of the prepared compounds.
Coefficient of determination of the toxic regression equation, which represents the goodness of fit of the toxic regression equation.
The grade of the bee toxicity—Extreme toxicity: A; high toxicity: B; moderate toxicity: C; low toxicity: D.
By comprehensively comparing the bee contact and oral toxicities of these compounds, there are two,
Based on the data of bee contact and oral toxicity at 24 and 48 h, it was found that the bee toxicity at 24 h was lower than that at 48 h. This indicates that the compounds were degraded after they entered the body of the honey bee and the degradation products exhibited higher bee toxicity than the parent compounds. It is known that
Conclusion
Sixteen novel seven-membered aza-bridged neonicotinoid analogues are synthesized on the basis of
Experimental
Instrumentation and chemicals
High-resolution mass spectra were recorded under electron impact (70 eV) conditions using a Micromass GCT CA 055 instrument. Melting points were recorded on a Büchi I-540 apparatus and are uncorrected. 1H NMR, 13C NMR and 19F NMR spectra were recorded on a Bruker AM-400 (400 MHz) spectrometer with CDCl3 or DMSO-d6 as the solvent and tetramethylsilane (TMS) as the internal standard. Chemical shifts are reported in δ (parts per million) values. Analytical thin-layer chromatography (TLC) was carried out on precoated plates (silica gel 60 F254), and spots were visualized with ultraviolet (UV) light.
Unless otherwise noted, reagents and solvents were purchased from Shanghai Tansoole Chemicals Company, Ltd. (Shanghai, China) and Shanghai Bide Pharmatech Ltd. (Shanghai, China).
Insecticidal assay
According to statistical requirements, the bioassay was repeated three times at 25 °C ± 1 °C. All compounds were dissolved in N, N-dimethylformamide and diluted with water containing Triton X-100 (0.1 mg L−1) to obtain series concentrations of 500.0, 100.0 mg L−1, and others for bioassays.
For cowpea aphids: The insecticidal activities of title compounds against cowpea aphids were tested according to the previously reported procedure. 24 Horsebean seedlings with 40−60 healthy apterous adults were dipped in diluted solutions of the chemicals containing Triton X-100 (0.1 mg L−1) for 5 s, and then the shoots were placed in a conditioned room (25 °C ± 1 °C, 50% relative humidity (RH) Water containing Triton X-100 (0.1 mg L−1) was used as control. The mortality rates were assessed after 24 h. Each treatment had three repetitions, and the data were corrected and subjected to probit analysis.
The LC50 values against Cowpea Aphids of low bee toxicity compounds were tested by similar method under different concentrations. The mortality rates of the cowpea aphids were recorded after 72 h. The test data were processed by the SPSS12.0 and obtained the LC50 for 72 h and 95% confidence limit.
Bee toxicity assay
All compounds were dissolved in acetone and diluted with water to obtain series concentrations for bioassays.
Contact assay: Honey bees were put into a dryer and were anesthetized by 5 mL diethyl ether for 3 min before the test. Then, different concentration solutions were dropwise added on the pronotums of the bees by 1.00 μL microdropper. The bees were enclosed in the cage in time before the bees fully recovered and were fed with 33% honey water. The cage was put on the laboratory table and covered by black cloth and acetone was used as control.
Uptake assay: Degrease cotton was dipped in diluted solutions of the chemicals, which was added to Tween 80 and diluted by 33% honey water until saturation. Then, degrease cotton was spread on gauze net in the cage and a 50 mL beaker was put on the degrease cotton so that the honey bees could suck up the liquid. The cage was put on the laboratory table and covered by the black cloth. The amount of acetone with Tween 80 was the same as the maximum concentration of diluted solution. It was used as control.
The mortality rates and poisoning symptoms were recorded 24 and 48 h after treatment. The test data were processed by the SPSS12.0 and obtained the LC50 (bee contact toxicity) for 24 and 48 h, LD50 (bee oral toxicity) for 24 and 48 h and 95% confidence limit.
General synthetic procedures
Intermediates 9–13
The synthetic procedures of intermediates
To a solution of commercially available halogen reagents
Intermediates 14–16
The synthetic procedures of intermediates
(E)-1-(4-chlorobenzyl)-2-(nitromethylene)hexahydropyrimidine 20
The synthetic procedures of intermediates
To a solution of 2-chloro-5-(chloromethyl)pyridine
(E)-N-((6-chloropyridin-3-yl)methyl)-N-methyl-2-nitroethene-1,1-diamine 23
The synthetic procedures of intermediate
A solution of methylamine in ethanol was added to the prepared intermediate
Intermediates 25–26
The synthetic procedures of intermediates
Intermediates 31–32
The synthetic procedures of intermediates
To a solution of intermediates
Target compounds, general procedure
The synthetic procedures of the target compounds are shown in Scheme 2. To a solution of intermediates
Succinaldehyde
A mixture of 2,5-dimethoxytetrahydrofuran (0.290 g, 2.2 mmol) and 0.4 mL of 10% aqueous HCl was stirred at room temperature. After 12 h, the pH value of the mixture was adjusted to 2−3 with saturated aqueous NaHCO3. The obtained solution could be used directly in the next step. 22
1-[(6-Bromopyridin-3-yl)methyl]-10-(2,5-dimethylphenyl)-9-nitro-2,3,5,6,7,8-hexahydro-1H-5,8-epiminoimidazo[1,2-a]azepine
10-(2,5-Dimethylphenyl)-1-[(6-fluoropyridin-3-yl)methyl]-9-nitro-2,3,5,6,7,8-hexahydro-1H-5,8-epiminoimidazo[1,2-a]azepine
2-Chloro-5-{[10-(2,5-dimethylphenyl)-9-nitro-2,3,5,6,7,8-hexahydro-1H-5,8-epiminoimidazo[1,2-a]azepin-1-yl]methyl}thiazole
1-Benzyl-10-(2,5-dimethylphenyl)-9-nitro-2,3,5,6,7,8-hexahydro-1H-5,8-epiminoimidazo[1,2-a]azepine
10-(2,5-Dimethylphenyl)-9-nitro-1-[(tetrahydrofuran-3-yl)methyl]-2,3,5,6,7,8-hexahydro-1H-5,8-epiminoimidazo[1,2-a]azepine
10-(2,5-Dimethylphenyl)-1-(2-fluoroethyl)-9-nitro-2,3,5,6,7,8-hexahydro-1H-5,8-epiminoimidazo[1,2-a]azepine
10-(2,5-Dimethylphenyl)-1-(3-fluoropropyl)-9-nitro-2,3,5,6,7,8-hexahydro-1H-5,8-epiminoimidazo[1,2-a]azepine
10-(2,5-Dimethylphenyl)-1-(4-fluorobutyl)-9-nitro-2,3,5,6,7,8-hexahydro-1H-5,8-epiminoimidazo[1,2-a]azepine
1-[(6-Chloropyridin-3-yl)methyl]-11-(2,5-dimethylphenyl)-10-nitro-1,2,3,4,6,7,8,9-octahydro-6,9-epiminopyrimido[1,2-a]azepine
N-[(6-Chloropyridin-3-yl)methyl]-8-(2,5-dimethylphenyl)-2-methyl-4-nitro-2,8-diazabicyclo[3.2.1]oct-3-en-3-amine
10-(2,5-Dimethylphenyl)-9-nitro-2,3,5,6,7,8-hexahydro-1H-5,8-epiminoimidazo[1,2-a]azepine
11-(2,5-Dimethylphenyl)-10-nitro-1,2,3,4,6,7,8,9-octahydro-6,9-epiminopyrimido[1,2-a]azepine
10-(2,5-Dimethylphenyl)-9-nitro-2,3,5,6,7,8-hexahydro-5,8-epiminothiazolo[3,2-a]azepine
11-(2,5-Dimethylphenyl)-10-nitro-3,4,6,7,8,9-hexahydro-2H-6,9-epimino[1,3]thiazino[3,2-a]azepine
1-[(6-Chloropyridin-3-yl)methyl]-10-(2,5-dimethylphenyl)-2,3,5,6,7,8-hexahydro-1H-5,8-epiminoimidazo[1,2-a]azepine-9-carbonitrile
1-[(6-Chloropyridin-3-yl)methyl]-10-(2,5-dimethylphenyl)-2,3,5,6,7,8-hexahydro-1H-5,8-epiminoimidazo[1,2-a]azepine-9-carboxylate
Supplemental Material
sj-pdf-1-chl-10.1177_17475198211012237 – Supplemental material for The structure modification of seven-membered aza-brigded neonicotinoids in order to investigate their impact on honey bees
Supplemental material, sj-pdf-1-chl-10.1177_17475198211012237 for The structure modification of seven-membered aza-brigded neonicotinoids in order to investigate their impact on honey bees by Yuce Chen, Xiaofeng Cao, Xi Chen, Zhong Li and Xiaoyong Xu in Journal of Chemical Research
Footnotes
Declaration of conflicting interests
The author(s) declared no potential conflicts of interest with respect to the research, authorship, and/or publication of this article.
Funding
The author(s) disclosed receipt of the following financial support for the research, authorship, and/or publication of this article: This work was financially supported by the National Natural Science Foundation of China (21672061) and the work was also supported by the Innovation Program of Shanghai Municipal Education Commission (201701070002E00037) and the Fundamental Research Funds for Central Universities. National Key Research Program of China (2018YFD0200105, 2017YFD0200505).
Supplemental material
Supplemental material for this article is available online.
References
Supplementary Material
Please find the following supplemental material available below.
For Open Access articles published under a Creative Commons License, all supplemental material carries the same license as the article it is associated with.
For non-Open Access articles published, all supplemental material carries a non-exclusive license, and permission requests for re-use of supplemental material or any part of supplemental material shall be sent directly to the copyright owner as specified in the copyright notice associated with the article.
