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31.
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.  相似文献   
32.
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.  相似文献   
33.
Several cohort studies have reported that dioxin and dioxin-like polychlorinated biphenyls might impair the nervous system and lead to neurological or neurodegenerative diseases in the elder people, but there is limited research on the involved mechanism. By using microarray analysis, we figured out the differentially expressed genes between brain samples from SD rats after low-dose(0.1 μg/(kg?bw)) dioxin exposure for six months and controls. To investigate the function changes in the course of dioxin exposure, Gene Ontology(GO) annotation and Kyoto Encyclopedia of Genes and Genomes(KEGG) pathway analysis were performed on the differentially expressed genes. And the changes of several picked genes have been verified by real-time PCR. A total of 145 up-regulated and 64 down-regulated genes were identified. The metabolic processes, interleukin-1 secretion and production were significantly associated with the differentially expressed genes. And the genes regulated by dioxin also clustered to cholinergic synapse and long-term potentiation. Candidate biomarker genes such as egr1, gad2, gabrb3, abca1, ccr5 and pycard may be toxicological targets for dioxin. Furthermore, synaptic plasticity and neuro-immune system may be two principal affected areas by dioxin.  相似文献   
34.
BACKGROUND: In 1996, the Committee on the Assessment of Wartime Exposure to Herbicides in Vietnam of the National Academy of Sciences' Institute of Medicine (IOM) issued a report on an exposure model for use in epidemiological studies of Vietnam veterans. This exposure model would consider troop locations based on military records; aerial spray mission data; estimated ground spraying activity; estimated exposure opportunity factors; military indications for herbicide use; and considerations of the composition and environmental fate of herbicides, including changes in the TCDD content of the herbicides over time, the persistence of TCDD and herbicides in the environment, and the degree of likely penetration of the herbicides into the ground. When the final report of the IOM Committee was released in October 2003, several components of the exposure model envisioned by the Committee were not addressed. These components included the environmental fate of the herbicides, including changes in the TCDD content over time, the persistence of TCDD and herbicides in the environment, and the degree of likely penetration of herbicides into the ground. This paper is intended to help investigators understand better the fate and transport of herbicides and TCDD from spray missions, particularly in performing epidemiological studies. METHODS: This paper reviews the published scientific literature related to the environmental fate of Agent Orange and the contaminant, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), and discusses how this affected the potential exposure to TCDD of ground troops in Vietnam. Specifically, the mechanisms of dissipation and degradation as they relate to environmental distribution and bioavailability are addressed. RESULTS: The evaluation of the spray systems used to disseminate herbicides in Vietnam showed that they were capable of highly precise applications both in terms of concentrations sprayed and area treated. Research on tropical forest canopies with leaf area indices (a measure of foliage density) from 2 to 5 indicated that the amount of herbicide and associated TCDD reaching the forest floor would have been between 1 and 6% of the total aerial spray. Studies of the properties of plant surface waxes of the cuticle layer suggested that Agent Orange, including the TCDD, would have dried (i.e., be absorbed into the wax layer of the plant cuticle) upon spraying within minutes and could not be physically dislodged. Studies of Agent Orange and the associated TCDD on both leaf and soil surface have demonstrated that photolysis by sunlight would have rapidly decreased the concentration of TCDD, and this process continued in shade. Studies of 'dislodgeable foliar residues' (DFR, the fraction of a substance that is available for cutaneous uptake from the plant leaves) showed that only 8% of the DFR was present 1 hr after application. This dropped to 1% of the total 24 hrs after application. Studies with human volunteers confirmed that after 2 hrs of saturated contact with bare skin, only 0.15-0.46% of 2,4,5-T, one of the phenoxy acetic acid compounds that was an active ingredient of Agent Orange, entered the body and was eliminated in the urine. CONCLUSIONS: The prospect of exposure to TCDD from Agent Orange in ground troops in Vietnam seems unlikely in light of the environmental dissipation of TCDD, little bioavailability, and the properties of the herbicides and circumstances of application that occurred. Photochemical degradation of TCDD and limited bioavailability of any residual TCDD present in soil or on vegetation suggest that dioxin concentrations in ground troops who served in Vietnam would have been small and indistinguishable from background levels even if they had been in recently treated areas. Laboratory and field data reported in the literature provide compelling evidence on the fate and dislodgeability of herbicide and TCDD in the environment. This evidence of the environmental fate and poor bioavailability of TCDD from Agent Orange is consistent with the observation of little or no exposure in the veterans who served in Vietnam. Appreciable accumulation of TCDD in veterans would have required repeated long-term direct skin contact of the type experienced by United States (US) Air Force RANCH HAND and US Army Chemical Corps personnel who handled or otherwise had direct contact with liquid herbicide, not from incidental exposure under field conditions where Agent Orange had been sprayed.  相似文献   
35.
In this study, the development of a toxicity evaluation method for dioxins in human milk by enzyme-linked immunosorbent assay (ELISA) was reported. A total of 17 human milk samples were tested by ELISA and by gas chromatography/mass spectrometry (GC/MS) to assess whether the ELISA performed on samples obtained from primiparas could be considered as reliable enough for identifying a dioxins contamination in human milk. The concept of toxicity equivalent quantity (TEQ) screening was validated by comparing TEQ values for a set of human milk samples to the ELISA responses predicted for those samples. A fairly good correlation (r=0.920) between immunoassay and GC/MS was achieved for human milk. This ELISA should be useful for biological samples monitoring.  相似文献   
36.
37.
Chemical residue studies were conducted from 1977-1987 on sites where spills of Agent Orange had occurred in the Herbicide Storage Sites at the Naval Construction Battalion Center, Gulfport, Mississippi, and on Johnston Island, Central Pacific Ocean. The soil persistence time of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was significantly decreased when in the presence of massive amounts of phenoxy herbicides (> 62,000 microg of herbicide/g of soil). Although microbial populations doubled in the most highly contaminated sites, fungal species diversity decreased. The dominant fungal species that appeared to be associated with the metabolism of the residues were of the genera Penicillium, Mucor, and Fusarium. TCDD level decreased from a mean high of 180 ng/g (ppb) to less than 1 ng/g of soil over a ten-year period.  相似文献   
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