乙烯菌核利在水溶液中的光解动力学

以高压汞灯和太阳光为光源,研究乙烯菌核利在重蒸水、自来水、湖水及pH缓冲液中的光解动力学。高压汞灯下,乙烯菌核利在重蒸水中的光解半衰期约为28 m in,而在太阳光下为3.86 h。自来水和湖水中溶解性物质对乙烯菌核利在高压汞灯下的光解动力学仅有微弱的淬灭效应,但在太阳光下表现出显著的敏化效应,照光3 h的敏化效率分别为138%和126%。2种光源下,pH 5.0和pH 7.0缓冲液对乙烯菌核利的光解均表现为光淬灭效应,高压汞灯照光60 m in的淬灭效率分别为69%和57%,太阳光照光7 h的淬灭效率分别为77%和33%;pH 9.0缓冲液则表现出显著的敏化效应,高压汞灯照光20 m in的敏化效率为58%,而太阳光照光1 h的敏化效率则达到了415%。     

乙烯菌核利在水溶液中的光解动力学

以高压汞灯和太阳光为光源，研究乙烯菌核利在重蒸水、自来水、湖水及pH缓冲液中的光解动力学。高压汞灯下，乙烯菌核利在重蒸水中的光解半衰期约为28min，而在太阳光下为3．86h。自来水和湖水中溶解性物质对乙烯菌核利在高压汞灯下的光解动力学仅有微弱的淬灭效应，但在太阳光下表现出显著的敏化效应，照光3h的敏化效率分别为138％和126％。2种光源下，pH5．0和pH7．0缓冲液对乙烯菌核利的光解均表现为光淬灭效应，高压汞灯照光60min的淬灭效率分别为69％和57％，太阳光照光7h的淬灭效率分别为77％和33％；pH9．0缓冲液则表现出显著的敏化效应，高压汞灯照光20min的敏化效率为58％，而太阳光照光1h的敏化效率则达到了415％。     

低浓度二噁英抑制青鳉幼鱼耳泡生成与SOX9b相关联

2,3,7,8-四氯二苯并对二恶英(2,3,7,8-Tetrachlorodibenzo-p-Dioxin,TCDD)是一种持久性环境有机污染物质,它在有机体内的蓄积性引起研究人员的重视。以青鳉胚胎作为实验动物模型,使用原位杂交和定量聚合酶链锁反应(Polymerase Chain Reaction,PCR)技术从分子水平探讨了TCDD对胚胎耳泡的发育及其毒性作用机制。结果表明,TCDD造成青鳉幼鱼耳泡生成障碍。通过原位杂交和q PCR分析表明,TCDD引起软骨发育的变化与SOX9b表达降低有密切的关联。研究认为青鳉胚胎是一种非常敏感的TCDD模式动物,其耳泡软骨发育以及SOX9b基因表达可能是一种二恶英发育毒性的效应标记物。     

甲基对硫磷对三种拟除虫菊酯杀虫剂的光敏降解研究

本文以高压汞灯和自然阳光为光源，研究了甲基对硫磷对氧氰菊酯、溴氰菊酯和氰茂菊酯在玻片表面光致降解的影响。结果表明：甲基对硫磷与三种拟除虫菊酯农药混合照光处理后，可使拟除虫菊酯农药的光解速度加快。氯氰菊酯、氰戊菊酯和溴氰菊酯的光解半衰期，在高压汞灯下比其单独照光分别缩短１２．１８、８．４６和７．３３倍，在阳光下则分别缩短４．７３，２．６５，和４．４６倍。甲基对硫磷对三种拟除虫菊酯农药表现出显著的光敏     

Protective effects of curcumin on antioxidant status,body weight gain,and reproductive parameters in male rats exposed to subchronic 2,3,7,8-tetrachlorodibenzo-p-dioxin

The aim of this study was to investigate the effects of curcumin (CUR) on antioxidant status, body weight (BW) gains, and some reproductive parameters in male rats exposed to subchronic doses of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Thirty-two rats were divided into four groups. The first group was kept as control. The second group (TCDD group) was given TCDD at a dose of 50 ng·kg^?1 BW per day; the third group (CUR group) was treated with CUR at a dose of 80 mg·kg^?1 BW per day. The fourth group (TCDD + CUR group) was given TCDD and CUR at the same doses simultaneously. Malondialdehyde (MDA) levels were significantly increased in the TCDD group. In addition, TCDD exposure decreased liver superoxide dismutase (SOD) activity, catalase (CAT) activities of kidney and brain, glutathione peroxidase (GSH-Px) activities of liver, kidney, and brain, and glutathione levels of liver, kidney, and heart. However, CUR treatment with TCDD exposure decreased MDA levels in all tissues and increased SOD activities of liver, kidney, and brain, CAT activity of heart, and GSH-Px activities of heart and brain. TCDD caused a decrease in BW gain, and CUR partially eliminated this effect of TCDD. In addition, while reproductive organ weights, sperm concentration, and sperm motility tended to decrease with TCDD exposure, these effects tended to be close to normal levels by CUR treatment. In conclusion, CUR was seen to be effective in the treatment and prevention of toxicity induced by subchronic TCDD exposure.     

Use of mercury in agriculture and its relationship to environmental pollution

Linuron samples at 75mg/L concentration were photolyzed with ultraviolet lamps or with natural sunlight. Ten photoproducts were identified and yields were determined for the more significant photoproducts resulting from either sunlight or ultraviolet lamp photolysis.     

2,3,7,8-四氯二苯并二噁英和Aroclor 1254对大鼠睾丸的单独和联合毒性效应

为了探讨2,3,7,8-四氯二苯并二噁英(TCDD)和Aroclor1254对大鼠睾丸的单独和联合毒性效应,采用2×2析因设计将SD大鼠随机分为4组,即对照组、Aroclor1254单独染毒组(10mg·kg-1)、TCDD单独染毒组(10μg·kg-1)和联合染毒组(TCDD10μg·kg-1+Aroclor125410mg·kg-1),每组5只.灌胃染毒,每天1次,连续12d.染毒结束后处死大鼠,称睾丸湿重、检测睾丸组织病理学及睾丸组织脂质过氧化状况.结果表明,各染毒组大鼠的睾丸均呈现毒性效应,表现为睾丸湿重降低,睾丸组织出现明显的病理学改变,丙二醛(MDA)水平升高、超氧化物歧化酶(SOD)和谷胱甘肽过氧化物酶(GSH-Px)活性降低,这些毒性效应多数在联合染毒组表现更为明显.析因分析结果表明TCDD与Aroclor1254对大鼠睾丸的联合毒性效应为相加作用.以上结果提示TCDD与Aroclor1254单独和联合染毒均具有睾丸毒性,且二者的联合效应为相加作用,在对二噁英和PCBs进行环境风险评价时应考虑这种联合作用.     

2,3,7,8-四氯苯并二噁英（TCDD）短期染毒可造成着床前胚胎丢失并伴随雌性生殖器官中毒物相关蛋白的诱导表达（Short Time Exposure of TCDD Causing Loss of Implantation Failure of Embryos and Its Associated with Induced Expression of Relevant Proteins）

为探明妊娠早期胚胎的丢失是否与卵巢、输卵管、子宫组织受到2,3,7,8-四氯苯并二噁英(TCDD)直接毒害有关,检测了NIH小鼠胚胎着床前期和后期TCDD暴露对胚胎毒性影响的敏感性,并利用免疫组化方法分析了模型动物肝脏、子宫、输卵管和卵巢组织中TCDD所引起的AhR、ARNT以及Cyp1a2分子标记物的变化.检测发现:妊娠第9d,100ng·kg-1·d-1剂量TCDD经口染毒,造成胚胎着床数量减少,且着床前期暴露的影响大于着床后期;子宫蜕膜反应受到明显抑制;胚胎迁移率没有明显变化,但胚胎数量减少.免疫组织化学分析发现正常组小鼠的肝脏、子宫、输卵管和卵巢组织中有AhR和Cyp1a2弱阳性信号表达,ARNT有细胞核的强阳性信号表达;妊娠第1～8d、第1～3d和第4～8d处理组小鼠肝脏、子宫、输卵管和卵巢组织中的AhR、Cyp1a2的阳性面积和光密度值均高于正常组;随处理时间和组织蓄积量的增加,ARNT在组织中的变化由胞核(妊娠第1～3d组)表达到胞浆(妊娠第4～8d组)表达,然后完全无表达(妊娠第1～8d组).以上研究结果表明:TCDD对早期妊娠小鼠子宫、输卵管和卵巢组织中的AhR、ARNT和Cyp1a2的激活和代谢方式与肝脏相同,说明雌性生殖系统中的组织有TCDD蓄积和代谢活性,这可能是导致早期胚胎迁移、着床等过程改变,造成胚胎丢失的重要原因.     

Photolysis of 3‐(3,4‐dichlorophenyl)‐1, 1 ‐Dimethylurea (Diuron) in dilute aqueous solution

Diuron samples at 40mg/L concentration were photolyzed with ultraviolet lamps and with natural sunlight to determine if data from ultraviolet lamp photolysis could be used to predict results from sunlight photolysis. Seven photoproducts were identified from the photolysis experiments. The identified photoproducts and the photoproduct yields were essentially the same for the two light sources.     

Relationships between exposure to polyhalogenated aromatic hydrocarbons and organochlorine pesticides and the risk for developing type 2 diabetes: a systematic review and a meta-analysis of exposures to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)

A systematic review was performed to evaluate the association between environmental exposures to polyhalogenated aromatic hydrocarbons (PHAHs) and organochlorine (OC) pesticides and the risk for type 2 diabetes (T2D). Searches of EMbase, Google Scholar, Medline, and Scopus were performed. Reports were included if they were original human studies whose design included a control group and if the sample size was larger than 10 participants per group. The articles were excluded if the type of diabetes was unknown or Type 1. Odds ratios (OR), 95% confidence intervals (CI), and modified Naranjo scores for the effects of environmental contaminants were determined for each study. Of the 35 eligible studies, six were included in the meta-analysis; these focused specifically on 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Meta-analysis of these studies showed no significant increased OR for the development of T2D from exposure to TCDD. However, subgroup analysis showed significant elevated OR for the development of T2D if exposure is repeated and accompanied by exposure to other persistent pesticides (OR?=?1.48; 1.10–1.90) but a decreased odds for T2D with exposure resulting from accidental exposure (OR?=?0.46; 0.39–0.52). Our results suggest that there are significant risks of developing T2D in populations with recurring exposures to TCDD in concert with other persistent chlorinated pesticides. A mean Naranjo score of 2.0 was determined for all 35 articles; this score was 2.5 when examining only TCDD studies and 2.1 when examining studies that looked only at T2D. Each of these Naranjo scores suggests a possible association between the prevalence of T2D and exposure to PHAHs or OC pesticides.     

2,3,7,8-四氯二苯并二噁英与Aroclor 1254单独与联合作用对大鼠外周血淋巴细胞DNA的损伤效应(Damage Effects of Individual and Combined Exposure to 2,3,7,8-Tetrachlorodibenzo-p-Dioxin and Aroclor 1254 on DNA in Peripheral Blood Lymphocyte of Rats)

为探讨2,3,7,8-四氯二苯并二噁英(TCDD)和多氯联苯(Aroclor 1254)联合染毒对大鼠外周血淋巴细胞DNA的损伤效应,将20只雄性Sprague-Dawley(SD)大鼠随机均分为4组,即对照组(橄榄油)、Aroclor 1254单独染毒组(10mg·kg-1)、TCDD单独染毒组(10μg·kg-1)和联合染毒组(TCDD 10μg·kg-1+Aroclor 1254 10 mg·kg-1).大鼠每天灌胃染毒1次,连续染毒6d.染毒过程中记录大鼠的体征和体重.末次染毒后24h取外周血,分离淋巴细胞,采用碱性单细胞凝胶电泳技术(彗星试验)检测外周血淋巴细胞DNA损伤,并采用CASP软件分析各组彗星的尾部DNA百分含量(Tail DNA%)、尾长(Tail Length)和尾矩(Tail Moment).结果表明,染毒结束时TCDD单独染毒和联合染毒组大鼠体重显著低于对照组,且联合染毒组表现更为明显.TCDD单独染毒组和联合染毒组大鼠外周血淋巴细胞DNA可见明显损伤,TailDNA%、Tail Length和Tail Moment均显著高于对照组(p<0.05),且联合染毒组大鼠细胞DNA损伤更为严重,但Arolor 1254单独染毒组大鼠未见明显DNA损伤.析因分析提示TCDD与Aroclor 1254对大鼠外周血淋巴细胞DNA损伤的联合毒性效应为协同作用.本研究结果表明TCDD与Aroclor 1254联合染毒可加重大鼠外周血淋巴细胞DNA损伤,在对PCBs与二噁英的混合暴露进行危险性评估时要注意这种联合毒性作用.     

2,3,7,8-四氯二苯并二噁英和β-萘黄酮暴露对斑马鱼肝和鳃MROD酶活性的影响

为了研究2,3,7,8-四氯二苯并二噁英(TCDD)和β-萘黄酮(β-NF)对斑马鱼(Danio rerio)肝脏和鳃CYP1A依赖性7-甲氧基-3-异酚噁唑酮-脱甲基酶(MROD)活性的影响,分别利用不同浓度的TCDD(0、0.05、0.1、0.2、0.4μg·L-1)和β-NF(0、25、50、100、200μg·L-1)对斑马鱼进行水浴暴露,48h后取样测定肝脏和腮MROD活性.结果表明,与对照组比较,TCDD暴露组和β-NF暴露组斑马鱼肝脏和鳃MROD活性均显著增强(p<0.01),且MROD活性的增加与TCDD或β-NF暴露浓度呈现明显的剂量-效应关系.初步推断斑马鱼肝脏和鳃CYP1A依赖性MROD酶活性可能能够作为TCDD或β-NF污染的生物标志物.     

2,3,7,8-TCDD的短期暴露对HepG2肝癌细胞内小分子代谢产物的影响

为了研究二恶英对细胞的代谢毒性,探究其肝毒性的作用机制,以二恶英中毒性最强的2,3,7,8-四氯代二苯并-对-二恶英(TCDD)为代表污染物,以HepG2肝癌细胞为受试对象,采用四甲基偶氮唑蓝(MTT)法和高效液相色谱/串联质谱法考察了TC-DD的24h暴露对HepG2细胞的增殖活性以及细胞的葡萄糖、氨基酸、尿素和甘油等小分子代谢物的影响。结果显示,短暂的TCDD暴露对HepG2细胞的增殖活性无显著影响。24h的TCDD暴露对细胞的葡萄糖消耗量无显著影响,但当TCDD浓度增至1nmol·L-1时,葡萄糖的消耗量表现出一定的降低趋势。0.01nmol·L-1TCDD就会使细胞脯氨酸和谷氨酸的合成能力下降,且谷氨酸的变化表现出明显的剂量-效应关系;TCDD可刺激细胞对缬氨酸、苏氨酸、酪氨酸、甲硫氨酸以及亮氨酸与异亮氨酸的吸收,并具有明显的浓度依赖性。随着TCDD浓度的增加,甘油和尿素产生量的降低趋势逐渐明显,1nmol·L-1TCDD处理24h后,甘油和尿素的产生量仅为对照组的1%和18%。研究表明,TCDD在短时间内使HepG2细胞内的一系列小分子代谢产物发生了不同程度的改变,且呈现出一定的剂量-效应关系。可见,TCDD可通过干扰HepG2肝癌细胞的代谢过程产生毒性。     

Protein expression profile in the testis of rats chronically exposed to low-dose 2, 3, 7, 8-tetrachlorodibenzo-p-dioxin

The chronic effects low-dose 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) were examined on protein expression profiles in rat testis, sperm, and serum gonadal hormones. A total of 32 male rats were randomly divided into three TCDD-exposed groups, administered either 140, 350, or 875 ng TCDD/kg/week for 29 weeks, respectively, and one control group receiving only corn oil. The proteins from rat testis were separated and analyzed by two-dimensional gel electrophoresis and mass spectrometry. TCDD induced significant decreases in sperm counts and serum gonadal hormone levels compared with controls. TCDD altered testicular protein expression levels. Several interesting volume-altered proteins that were related to the reproductive toxicities or other toxicities of TCDD were identified. Among these proteins, PERF15 was the only down-regulated protein; sperm protein SSP411, ubiquitin carboxyl-terminal hydrolase L-3, and eukaryotic translation elongation factor 1 gamma were up-regulated by TCDD. The differentially expressed proteins and other data provide further insight into the mechanisms of reproductive toxicity mediated by low-dose TCDD exposure.     

2,3,7,8-四氯二苯并对二噁英对大鼠卵巢颗粒细胞雌二醇和孕酮分泌的影响

为研究2,3,7,8-四氯二苯并对二噁英(TCDD)对体外原代培养大鼠卵巢颗粒细胞活力和雌二醇(Estradiol,E2)、孕酮(Progestone,P)分泌的影响,探索TCDD对卵巢颗粒细胞的毒性作用阈值和程度,对未成熟SD大鼠卵巢颗粒细胞进行了原代培养,并设2组体外染毒实验:终浓度分别为0.1、1、10、100nmol·L-1TCDD染毒24h和10nmol·L-1TCDD染毒1、3、6、18、24h.染毒结束后采用MTT法检测细胞活力,RIA法检测收集培养液中的E2和P含量.结果表明,1、10、100nmol·L-1TCDD可显著抑制大鼠卵巢颗粒细胞活力和E2、P的分泌,与阴性对照、0.1%DMSO组、0.1nmol·L-1TCDD组比较差异均有显著性(p<0.05);10nmol·L-1TCDD染毒6、18、24h可明显抑制细胞活力和E2、P的分泌,与对照组和短期染毒组(1h、3h)差异均有显著性(p<0.05).痕量的TCDD可显著降低大鼠卵巢颗粒细胞活力并抑制细胞E2和P分泌,对大鼠卵巢颗粒细胞的毒性作用阈值可能为1nmol·L-1或更低.TCDD的生殖毒性作用可能与直接对卵巢颗粒细胞的毒性作用和抑制甾体激素的生物合成以及分泌有关.     

蒽醌类化合物对大型蚤(Daphnia magna)的急性光致毒性研究

通过测定模拟光照和无光照条件下20种蒽醌类化合物对大型(Daphnia magna)的48h半数活动抑制浓度(EC50), 研究了该类化合物的光致毒性．比较了两种助溶剂(二甲基亚砜和丙酮)对这些化合物光致毒性的影响,初步讨论了光致毒性的机理．结果表明,所研究的助溶剂不影响这些化合物对大型潘的光致毒性．蒽醌类化合物因其取代基的不同(-NH2、-OH、-Cl、-Br、-NO2)、取代基位置的不同和取代基数目的不同,而表现出对大型潘光致毒性的不同．最低未占据分子轨道能(ELUMO)和最高占据分子轨道能(EHOMO)之间的能级差,可用于初步判断蒽醌类化合物 溞大型的潜在光致毒性．     

克螨特和霸螨灵及其混剂在水中的光降解

研究了克螨特、霸螨灵在几种水体中的光降解以及 2种农药之间的光敏化或光猝灭效应。结果表明 ,在 3 0 0W高压汞灯光照处理时 (试验试管距光源 8cm) ,克螨特和霸螨灵都极易降解 ,克螨特的光解半衰期为 9.0 6min ,霸螨灵的光解半衰期仅为 1 .4 8min。克螨特在不同水体中的光解率为 :重蒸馏水 >鱼塘水 >河水 >井水 ,霸螨灵的光解率为 :井水 >重蒸馏水 >鱼塘水 >河水 ;2种农药在现采水、过滤水、灭菌水中的光解率依次降低。克螨特和霸螨灵混剂在重蒸馏水中互为光猝灭剂 ,在井水、河水和塘水中霸螨灵对克螨特有极显著的光敏化作用 ,而克螨特对霸螨灵有极显著的光猝灭效应。克螨特、霸螨灵在pH 5和 pH 9缓冲液中光解率比之在 pH 7缓冲液中稍快 ,光猝灭效应也较强烈。在重蒸馏水中太阳光照处理时 ,克螨特和霸螨灵互为光敏剂 ,而高压汞灯下则互为光猝灭剂。     

运动对2,3,7,8-四氯二苯并二噁英持续暴露大鼠肝脏氧化应激的影响

为探索运动对2,3,7,8-四氯二苯并二噁英(2,3,7,8-TCDD)持续暴露大鼠肝脏氧化应激的影响,本研究将7周龄雄性SD大鼠适应性喂养1周后,随机分为对照(NC)、运动对照(EC)、染毒1(NT1)、运动染毒1(ET1)、染毒2(NT2)、运动染毒2(ET2)、染毒3(NT3)、运动染毒3(ET3)、染毒4(NT4)及运动染毒4(ET4)共10组。染毒组(NTs、ETs)腹腔注射TCDD(溶于玉米油),对照组及各染毒组首次剂量依次为0、0.4、1.6、6.4、25.6μg·kg~(-1)(以单位体重计),之后每周给予上述剂量的21%作为维持剂量,持续染毒8周;运动组尾部负重5%游泳,每周5 d,每次30 min。实验结束取材,测定血清丙氨酸氨基转移酶(ALT)、天冬氨酸氨基转移酶(AST)、肝组织超氧化物歧化酶(SOD)、过氧化氢酶(CAT)、谷胱甘肽过氧化物酶(GSH-Px)活性及丙二醛(MDA)、活性氧(ROS)含量。结果显示:1)染毒可升高各染毒组大鼠血清AST活性及NT4组大鼠血清ALT活性,增加NT2、NT3组肝脏MDA含量,而降低NT1、NT2组大鼠血清ALT活性;2)运动可升高大鼠血清AST及ALT活性,增加大鼠肝组织GSH-Px活性;3)运动可升高染毒大鼠血清AST活性(T1剂量),降低染毒大鼠血清ALT活性(T1剂量),降低染毒大鼠血清AST活性(T3剂量),升高染毒大鼠血清ALT活性(T3、T4剂量),增加染毒大鼠肝组织SOD活性(T2、T3剂量)、CAT活性(T1、T2、T3剂量)及GSH-Px活性(T2、T3、T4剂量),降低染毒大鼠肝组织MDA含量(T2、T3、T4剂量)及ROS含量(T1、T3剂量)。结果表明,2,3,7,8-TCDD持续暴露8周可引起大鼠肝细胞氧化应激损伤,并产生剂量依赖效应;而有氧运动可增加2,3,7,8-TCDD持续暴露(T2、T3剂量)大鼠肝组织抗氧化酶活性,有效降低氧化应激损伤而减轻肝毒性。     

Combined effects of 2,3,7,8-tetrachlorodibenzo- p -dioxin and polychlorinated biphenyl congeners in rats

The objective of this work was to evaluate potential interactions between 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and polychlorinated biphenyls congeners (PCBs) in rats. Groups of five adult female rats were given 0, 2.5, 25, 250, or 1000?ng TCDD/kg body weight/day or TCDD in combination with a mixture of PCB congeners at a concentration of 2 or 20?µg?kg^?1 body weight/day by gavage for 28 days. After the 28-day treatment period, the rats were killed for the analysis of biochemical, liver enzyme activities, and hematological and pathological end points. Growth suppression, increased absolute and relative liver weights, and decreased thymic weight were observed in the 1000?ng TCDD group alone, or the groups receiving a mixture of 1000?ng TCDD and 2 and 20?µg PCBs. TCDD-increased liver and thymic weights were not altered by PCBs; however, growth suppression was more pronounced in animals receiving 1000?ng TCDD and 2?µg PCBs. Increased hepatic microsomal methoxy resorufin-O-demethylase and ethoxy resorufin-O-deethylase activities occurred in 250 and 1000?ng?kg^?1 TCDD-treated animals, which were antagonized by PCBs. Effects of 250?ng TCDD on serum cholesterol and liver uridine diphosphate glucuronosyl transferase activity were reduced by 20?µg PCBs. Treatment with 1000?ng TCDD increased serum albumin, decreased liver vitamin A, increased kidney vitamin A, and liver microsomal glutathione-S-transferase activity, which were not affected by PCBs. Decreased hemoglobin, platelet, packet cell volume, and red cell indices were observed in TCDD-treated rats, but no interactive effects were seen. Histopathological evaluation revealed that liver, thyroid, and thymus were the target organs, but the effects of co-exposure to PCBs and TCDD were variable. These results indicate that the mixture effects of PCBs and TCDD may be additive, synergistic, or antagonistic depending on the dose level and end points measured.