999精品在线视频,手机成人午夜在线视频,久久不卡国产精品无码,中日无码在线观看,成人av手机在线观看,日韩精品亚洲一区中文字幕,亚洲av无码人妻,四虎国产在线观看 ?

Double-edged sword acetochlor:Status and challenges of toxicology

2023-12-26 12:47:42JIAOYaQiJIAJunXinWANGSaLIHuiGAOJinShengLILi
黑龍江大學工程學報 2023年4期

JIAO Ya-Qi,JIA Jun-Xin,WANG Sa,LI Hui,GAO Jin-Sheng,LI Li,*

(Heilongjiang University a.Postdoctoral research workstation of Heilongjiang Pesticide Engineering Technology Research Center;b.College of Advanced Agriculture and Ecological Environment,Harbin 150086,China)

Abstract:This paper examines the environmental and ecological impacts of the widely used pre-seedling herbicide acetochlor in agriculture. A comprehensive scientific review on acetochlor toxicity studies from 2012-2022 was conducted using CiteSpace 5.7 R2 software. The detrimental effect of acetochlor on non-target organisms has been widely documented,including soil,plants,aquatic and terrestrial organisms,and even humans. The toxic effects on organisms are attributed to its binding with antioxidant enzymes through hydrophobic interactions and hydrogen bonds,leading to excessive ROS accumulation and activation of toxic pathways. Integrating the existing literature on acetochlor environmental effects,this review identifies challenges and offers solutions for acetochlor in the environment and sustainable development. It also provides a theoretical framework for solving ecological environmental stability issues.

Key words:acetochlor;toxic effect;ROS;CiteSpace

0 Introduction

Organic pollutants,including polycyclic aromatic hydrocarbons (PAHs),organic pesticides (OPs),polychlorinated biphenyls (PCBs),polybrominated diphenyl ethers (PBDEs),endocrine disruptors (EDCs),pharmaceuticals,and personal care products (PPCPs),have exacerbated the degradation of farmland soil environmental quality and reduced the stability of farmland ecosystems. Herbicides,which are a component of OPs,have increasingly been used to enhance agricultural productivity and crop yields,thus exerting significant impacts on farmland ecosystems[1]. Acetochlor,a high-efficiency herbicide with the full name of 2-chloro-N-(ethoxymethyl)-N-(2-ethyl-6-methylphenyl)acetamide (C14H2OClNO2),primarily penetrates weeds cell through shoots or roots upon topsoil application,leading to weed death through inhibition of cells division[2-3]. According to the United States Environmental Protection Agency (USEPA),acetochlor is ranked as the third most commonly utilized herbicide in the agricultural market,with an estimated usage of 30-35 million pounds in 2001. Furthermore,it is widely employed in China,where annual usage surpasses 100 000 tons.Continuous application of acetochlor leads to its gradual resistance to microbial degradation in environmental microorganisms,thereby maintaining stable activity in the environment. Consequently,the residual amount of acetochlor and its degradation products is widely present in the environment,classifying them as persistent organic pollutants[1,4]. The exceptional structural stability and water solubility of acetochlor enable its easy infiltration into soil and water,persisting in ecosystems for extended periods,creating health risks for non-target organisms and humans[5]. Acetochlor has been identified as a suspected endocrine disruptor in a variety of vertebrates by the USEPA and the European Union (2010)[4]and classified as a potential human carcinogen[6]. However,there is still a lack of systematic statistics and comprehensive analysis on the toxicity of acetochlor.

CiteSpace 5.7 R2 software was employed to perform a comprehensive scientometric analysis of literature accumulated over the past decade. The software was utilized to analyze the co-occurrence network of countries and keywords,thus delineating recent research trends (Fig.1)[7]. The study observed a consistent annual increased in research on acetochlor,which was found to be closely associated with the agricultural levels of different countries,notably China,the United States,and France serving as the primary contributors to acetochlor research publications. Notably,toxicology and remediation emerged as influential research domains within this field,and analysis revealed extensive research activity in these areaas over the past decade. Thus,this review conducted a literature search using Web of Science (www.isiwebofknowledge.com/),Google Scholar (https://scholar.google.co.kr),and Science Direct (https://www.sciencedirect.com/)to analyze the toxicity of acetochlor to organisms. This review highlights the current understanding of acetochlor toxicity in the environment,while also identifying literature gaps. These findings can serve as valuble references for future research endeavors.

Fig.1 (a)Number of publications related to acetochlor research over the past decade. Based on the analysis conducted using Citespace software,researches on acetochlor over the past decade;(b)country analysis;(c)keyword analysis;(d)keyword cluster analysis

1 Toxic effects of acetochlor

Acetochlor is widely used in farmland,leading to its release into different environmental systems. Therefore,research has been conducted on the toxicity of acetochlor in soil,water and air,with a predominant focus on its impact on vertebrates,invertebrates,plants,microorganisms,and other organisms (Fig.2). Due to the sensitivity of organisms to pollutants,diverse organisms are selected for ecotoxicological studies,enabling the development of standardized procedures to interpret results and facilitate comparisons with other studies.

Fig.2 Environmental effects of acetochlor

1.1 Toxic effects of acetochlor in the air on organisms

Considered as a peril to the health of living organisms,air pollutant exerts a strong influence as air-borne pollutants can directly infiltrate the respiratory system,reaching the alveoli[8]. Xu et al.[3]found that during pesticides spraying,some pesticides exhibit a drifting effect that specifically impact on natural enemy insects. For instance,acetochlor moderately endangersTrichogrammaostriniaeandEncarsiaformosa. Therefore,the widespread application of chemical pesticides not only significantly hampers the control efficacy of using natural enemies for pest management but also disrupts ecological balance.

1.2 Toxicity to the soil environment

1.2.1 Toxicity of acetochlor to soil

Acetochlor’s weed control may impact the soil ecosystem. Acetochlor exposure can significantly alter soil enzyme activities (phosphatase,polyphenol oxidase,catalase,soil urease),respiration intensity[9-11],and nitrogen conversion[12-15]. Especially,changes in soil-related physiological indicators can influence the composition of soil microbial communities (Table 1). Maintaining proper soil microbial community structure and diversity is crucial for the sustainability and productivity of soil ecosystems[16]. Hao et al.[17]found that the recommended field dose of acetochlor (5 mg·kg-1)reduced the activities of catalase,dehydrogenase,and invertase in the soil. High-throughput sequencing results showed a decrease in the abundance ofProteobacteria,Actinobacteria,andChytridiomycota,while an increase in the abundance ofAcidobacteriaandZygomycotadue to acetochlor. Bai et al.[18]discussed the effect of acetochlor on microbial biomass and community structure in both rhizosphere and bulk soil after one month of application. It was found that the rhizosphere microbial community showed higher susceptibility to acetochlor compared to the bulk soil,resulting in increased soil microbial biomass carbon content and bacterial growth,along with unhibited fungal growth. Through principal component analysis of the phospholipid fatty acid,it was determined that acetochlor significantly affected the composition of the soil microbial community in the early application stage,with a diminishing effect in the later stage. Moreover,acetochlor exposure also lead to affect significant changes in the abundance of suborders within the dominant group of soil animals in farmland[19]. In summary,acetochlor application affects soil health and disturbs soil microflora. However,disruptions in the microbial community can,in turn,affect soil fertility and quality,leading to adverse effects on plant growth and yields.

Table 1 Effects of exposure to acetochlor on soil environment

1.2.2 Acetochlor toxicity in plants

Table 2 depicts the toxic effect of acetochlor on plants. In general,the normal field application rate of acetochlor may not adversely affect the growth of plants likeScutellariabaicalensisgeorg,peas,corn,and soybeans[20-24]. However,prolonged or excessive spraying may result in toxic effects. Li et al.[25]and Gao[26]found that exposure to high concentrations of acetochlor had an impact on wheat root cell membrane permeability,antioxidant enzyme activity,and root tip cell tissue differentiation[27]. Importantly,prolonged acetochlor application can reduce the emergence rate,leaf number,stem thickness,and plant height of peanut and soybean seedlings,significantly restricting their growth. Acetochlor can also significantly reduce the antioxidant enzyme activity in plants. Over 12 years,continuous application of acetochlor led to decreased yields of peanuts and soybeans,with the decline in yield escalating as the application years increased[28]. Certain plants,like rice,Chuzhou chrysanthemum seedlings (DendranthemamorifoliumL.),pumpkins,grapes,and sorghum are not treated with acetochlor as an herbicide. Exposure to acetochlor during the growth of these plants can induce envident toxicological effects. It diminishes plant antioxidant enzyme activity,leading to ROS accumulation,and subsequently inhibiting germination,root vitality,photosynthesis,and growth,causing significant plant damage and yield reduction[29-35]. Clearly,exposure to acetochlor can have varying degrees of impact on plant health. Considering the harm acetochlor inflicts on the soil,it is reasonable to surmise its impact on plants damage. Moreover,alterations in the soil environment can indirectly influence plant growth beyond the direct toxic effects.

1.2.3 Acetochlor toxicity in soil organisms and nematodes

Pesticides directly affect non-target soil organisms,including environmental engineer earthworms in the soil (Table 3). Earthworms typically serve as favored food sources for amphibians,reptiles,birds,and mammals. As a result,the presence of pesticides poses a potential risk for biomagnification effects[36]. Wang et al.[37-38]investigated the acute toxicity of numerous commonly used herbicides toEiseniafetida,revealing high and moderate toxicity of acetochlor to earthworms. Acetochlor can significantly increases the hydroxyl radical (·OH-) content,superoxide dismutase (SOD),and antioxidant enzyme catalase (CAT)activities,as well as cytochrome P450 content in earthworms. It also considerably inhibits acetylcholinesterase (AchE)activity,leading to lipid peroxidation and DNA damage[39]. Furthermore,comprehending the availability and susceptibility of nematodes in toxicity testing can enhance the impact of harmful substances on soil ecosystem health. Nevertheless,exposure to acetochlor can impact the mortality,growth,and reproduction of soil nematodes likeCaenorhabditiselegansandPristionchuspacificus[40].

In summary,acetochlor exposure can directly impact soil enzyme activities and microbial community structure,and directly and indirectly influence plant growth,as well as the health of earthworms and nematodes. It can be seen that the disorder of the antioxidant system is the main cause of harm to animals and plants. Furthermore,in the soil environment,while acetochlor spraying effectively eliminates weeds,its toxic effects on the soil environment should not be disregarded.

1.3 Toxic effects of acetochlor on aquatic organisms

Acetochlor has been identified as the predominant contributor to the projected chronic pesticide toxicity index in fish[41]. Zebrafish is commonly utilized as a model aquatic animal to assess the toxicological impact of substances,The 96 h-LC50 values of acetochlor on zebrafish embryos,larvae,juveniles,and adults were found to be 5.82,1.34,3.00,and 1.44 mg·L-1,correspondingly[42]. According to the classification standards outlined by the Scientific Issues of Marine Environmental Protection,the ecotoxicological risk of acetochlor to zebrafish is considered moderately toxic[43]. Acetochlor exposure can lead to reduced hatching rate,induction of pericardial cyst edema,bradycardia,circulatory defects,thrombosis,sac closure,trunk bending,and other symptoms in zebrafish embryos (Table 4). Circulatory disturbances induced by bradycardia may lead to thrombus formation. In addition,the down-regulation of Nkx2.5 and Gata4,associated with cardiac procedures induction,may underpin the cardiovascular toxicity of acetochlor in zebrafish[44-45]. Studies of Hu et al.[46]and Xu et al.[47]further confirmed additional other toxic effects of acetochlor. Specific toxic mechanisms are evident in zebrafish genes involved in oxidative stress (CAT,GPX,GPX1a,Cu/Zn-SOD,andOgg1),the hypothalamic-pituitary-gonad/thyroid (HPG / HPT)axis (asd1,dio1,dio2,tpo,trα,trβ,s1c5a5,crh,tsh,VTG1,ERβ1,CYP19a,ugt1ab,ttr),apoptosis pathway (Bcl2,Bax,P53,andCas8),and innate immunity (CXCL-C1C,IL-1β,TNFα,cc-chemokine,il-8),significantly affected following acetochlor exposure[48-50]. Changes in these genes result in oxidative stress,apoptosis,immunotoxicity,and endocrine toxicity,with interplay between these systems. Subsequent investigations have substantiated the neurotoxicity of acetochlor. Acetochlor exposure can lead to morphological abnormalities,altered spontaneous tail curling in zebrafish embryos,and concentration-dependent reduction in larvae locomotor behavior. The neurotoxic effects of acetochlor appear to be associated with decreased AChE activity and oxidative stress. Excessive ROS production and reduced CAT activity contribute to the latter,ultimately disrupting the expression of nervous system genes and apoptosis-related genes,potentially resulting in cell apoptosis and morphological abnormalities[51]. Zhang et al.[52]also identified an estrogenic effect of acetochlor,stimulating the synthesis of zebrafish estradiol (E2)and ovarian vitellogenin (Vtg),thereby promoting ovarian development. However,long-term exposure to high acetochlor doses can diminish ovarian resistance to oxidative stress,leading to detrimental effects on developing ovaries. In addition,acetochlor has shown toxic effects on various other aquatic animals,such as Procambarus clarkii,Freshwater Cladoceran (Daphniacarinata),Nile tilapia (Oreochromisniloticus),etc.[53-56]

Table 4 Study on the toxicity of acetochlor to aquatic organisms

It is worth noting that acetochlor exposure in aquatic environments also has diverse effects on aquatic plants,including impacts on total chlorophyll content in Lemna minor aquatic macrophyte[57],disruption of the antioxidant systems inMicrocystisaeruginosaandSpirodelaoligorrhizacausing lipid peroxidation[58-60],and affect the growth and photosynthesis ofChlorellapyrenoidosaandMicrocystisflos-aquae[61-62]. Collectively,residual acetochlor in aquatic habitats can exert variable degrees of toxicity on nearly all aquatic organisms,from cellular to tissues,organs,and systems. Interactions among these systems may lead to additional harm,posing a threat to the overall health of organisms. Unfortunately,many areas lack customized water quality standards for acetochlor. Nevertheless,given the high detection and usage rate,as well as the toxic effects of acetochlor on aquatic organisms,standards still need to be supervised.

1.4 Other biological toxicity

Numerous other toxicological tests have also verified the toxic effects of acetochlor. Acetochlor can cause significant histopathological changes and antioxidant system dysfunction in the liver,kidney,and sexual organs of rats[63]. Urine metabolomics analysis showed that both high- and low-dose acetochlor led to alterations in rats urine metabolomics. These changes may affect the nervous and endocrine systems by modulating tyrosine levels[64]. Furthermore,Counihan et al.[65]utilized a chemical proteomics platform to comprehensively map the cysteine reactivity of the entire proteome in mice exposed to acetochlor,aiming to elucidate its toxicity mechanism. The results revealed that acetochlor impaired fatty acids oxidation,yet the unoxidized fatty acids were redirected to alternative lipid pathways,leading to elevated levels of free fatty acids,triglycerides,cholesterol esters,and other lipid species in the liver. Additionally,Daam et al.[66],Liu et al.[67],and Moutinho et al.[68]corroborated the toxic effect of acetochlor on amphibians (Physalaemuscuvieri,Hypsiboaspardalis,Microhylapulchra,Bufomelanostictus,Boanapardalis,Xenopustropicalis),manifesting as abdominal edema,facial deformity,spine curvature,tail curvature,head deformity,and other embryonic deformities and DNA damage.

1.5 Human and cells

Typically,human exposure to acetochlor occurs through airborne and food chain transmission routes. Studies on the toxicity of acetochlor in model organisms have confirmed its biological toxic effects,which may also manifest in humans. Huang et al.[1],and Wang et al.[69]employed human liver cancer cells (HepG2)to assess the specific toxicity potential and mechanism of acetochlor. The findings indicated that acetochlor reduces cellular antioxidant response and membrane potential,activates the apoptosis signaling pathway,up-regulates the expression ofBax/BcL-2,causing a cascade reaction,activatingcasepase-3andcasepase-9,and lysing PARP,eventually leading to cells death. Concurrently,mitochondrial dysfunction and disruption of cell cycle regulation jointly inhibited the proliferation of HepG2 cells. Notably,acetochlor also exerts toxic effects on human alveolar A549 cells and human erythrocytes,causing hemolysis,lipid peroxidation,and apoptosis[4,6].

Demonstrably,acetochlor exposure may cause ROS accumulation in plants,affecting plant seed germination,root system,stem and leaf growth,as well as leaf photosynthesis,etc. For animals or humans,exposure to acetochlor can profoundly affect the damage to diverse tissues and organs,and even lead to cancer. Specifically,acetochlor can cause ROS accumulation in animals,leading to metabolic disorders,endocrine disorders,immunosuppression,and neurotoxicity. Interactions among various systems can trigger cell apoptosis,further inducing developmental toxicity and mortality. Notably,acetochlor appears to be implicated in oxidative stress across a wide range of organisms. Some studies have shown that the overproduction and accumulation of ROS are the main cause of organismal mortality[70]. This view further corroborated this perspective by conducting molecular docking of acetochlor with two antioxidant enzymes (SOD and CAT). The findings demonstrated that acetochlor can form complexes with both proteins,with binding free energies ΔG of -4.9 and -6.3 kcal·mol-1(Fig.3). The formation of complexes between acetochlor and proteins primarily arises from hydrogen bonding and hydrophobic interactions,both critical for molecular recognition and binding. The interaction between acetochlor and antioxidant enzymes may result in the occupation of the enzymes’s activity sites,hindering the decomposition of excessive ROS. This can lead to the onset of oxidative stress in organisms,ultimately culminating in biological toxicity[71].

2 Conclusion and outlook

In agricultural production,acetochlor has become an indispensable herbicide due to its ability to increase crop yields. This has led to significant economic benefits. However,the widespread use of acetochlor,driven by its advantages has resulted in large quantities being used without regard for the consequences. The herbicide’s medium water solubility and low soil adsorption capacity have led to extensive accumulation in the environment and easy migration,seriously threatening ecological security. At present,many studies have elucidated the adverse effects of acetochlor on various organisms,including soil and soil organisms,aquatic organisms,other organisms,and human health,all of which are negatively impacted by acetochlor. The complexation between acetochlor and antioxidant enzymes leads to excessive accumulation of ROS,impacting the growth,development,and survival of organisms.

Research on acetochlor has also garnered significant attention in recent years. However,there are still areas that require further investigation,such as the toxicity of acetochlor metabolites,and compound pollution. This review provides a comprehensive analysis of the current research on acetochlor toxicity,offering valuable insights for the development of new research programs in this critical field.

主站蜘蛛池模板: 精品夜恋影院亚洲欧洲| 最近最新中文字幕在线第一页| 精品久久高清| 免费毛片a| 国产成本人片免费a∨短片| 1769国产精品免费视频| 精品视频福利| 成人综合网址| 丰满人妻久久中文字幕| 一区二区午夜| 91小视频在线| 日本影院一区| 亚洲欧洲自拍拍偷午夜色| 亚洲国产精品日韩av专区| 亚洲 欧美 偷自乱 图片| 亚洲欧美成人在线视频| 美女被操91视频| 国产日本视频91| 少妇露出福利视频| 精品国产免费观看一区| 成人福利在线看| 另类欧美日韩| 亚洲va视频| 成人av专区精品无码国产| 日韩欧美中文| 久久久久亚洲精品成人网| 国产精品一老牛影视频| 久久精品嫩草研究院| 黄色国产在线| 欧美一级视频免费| 成人亚洲天堂| 亚洲无码高清免费视频亚洲| 国产黑丝一区| 亚洲综合精品第一页| 国产精品亚洲片在线va| 免费国产好深啊好涨好硬视频| www亚洲精品| 国产网站免费观看| 亚洲国产天堂久久综合| 免费女人18毛片a级毛片视频| 手机成人午夜在线视频| 播五月综合| 日韩欧美国产区| 自拍偷拍欧美日韩| AV片亚洲国产男人的天堂| 欧美高清视频一区二区三区| 久热中文字幕在线| 国产欧美日韩综合一区在线播放| 九九九久久国产精品| 91麻豆国产视频| 欧美全免费aaaaaa特黄在线| 久久精品波多野结衣| 99久久国产综合精品2020| 在线精品亚洲一区二区古装| 色哟哟国产精品| 日韩少妇激情一区二区| 日韩毛片免费观看| 人妻精品全国免费视频| 欧美成人免费| 在线中文字幕日韩| 9999在线视频| 亚洲AV无码乱码在线观看代蜜桃 | 欧洲日本亚洲中文字幕| 亚洲首页在线观看| 精品乱码久久久久久久| 福利在线不卡| 99re在线视频观看| 欧美自慰一级看片免费| 国模视频一区二区| 亚洲欧美人成电影在线观看| 国产成人综合在线视频| 三区在线视频| 亚洲黄网在线| 亚洲国产天堂久久综合| 国产白浆在线观看| 国产91视频观看| 国产成人AV综合久久| 亚洲欧美自拍视频| 亚洲天堂在线视频| 在线看国产精品| 国产综合无码一区二区色蜜蜜| 亚洲另类第一页|