臭氧降解乐果机理探讨

研究了臭氧对乐果的降解效果及其影响因素。试验结果表明,当初始臭氧浓度为10mg·L-1时,5min内可使乐果降解80%左右,延长反应时间,乐果降解率无明显增加。同时,通过在乐果和臭氧的反应液中再分别添加重碳酸盐与叔丁醇,探讨臭氧降解乐果的反应机理,结果表明臭氧降解乐果是分子反应。GC-MS检测经臭氧处理的水样发现有氧化乐果存在,表明若臭氧处理不完全,水样中可产生毒副产物。     

氧化乐果对小球藻的毒性研究

以小球藻(Chlorella vulgaris)为实验生物,通过研究不同浓度(0、1、5、10、15、20 mg·L-1)的氧化乐果对小球藻生长发育及EC50,硝酸还原酶活性,叶绿素含量的影响,初步探讨了氧化乐果对小球藻的毒性作用。实验结果表明:氧化乐果对小球藻96 hEC50值为4.88 mg·L-1;低浓度氧化乐果(1 mg·L-1)在前6天对小球藻细胞增长影响不大,高浓度氧化乐果(大于5 mg·L-1)则在初期就表现为抑制,氧化乐果浓度与细胞数量之间表现为负相关(R2=0.65755);在第8天,氧化乐果各浓度组的硝酸还原酶的相对酶活也表现"低促高抑"作用,但是仍然高于对照组的酶活,整体表现为促进作用;随着氧化乐果浓度的增加,小球藻叶绿素含量呈现明显降低的趋势。     

超临界水氧化法降解氧乐果的研究

实验研究了有机磷农药氧乐果在超临界水中的氧化降解．结果表明,超临界水氧化技术能有效地降解氧乐果废水．随着反应温度的升高、压力的增大、停留时间的延长,COD去除率也随之提高氧乐果在超临界水中氧化降解的动力学方程为：－d［COD］/dτ＝1.60eｘp（－2.25×10⁴/RT）［COD］^0.90［O₂］₀^-0.38［H₂O₀^0.053.     

Clinical and toxicological data in Fenthion and omethoate acute poisoning

Abstract

This study paper reports on two cases of poisoning with the organophosphorus insecticides, fenthion and omethoate. The two victims were admitted in the Intensive Care Unit (ICU) a few hours after ingestion of the two insecticides. They received appropriate treatment for organophosphorous poisoning (gastric lavage, activated charcoal, atropine and pralidoxime) and supportive care. Both patients survived. Organophosphate blood levels were determined on admission (fenthion 2.9 (ig/ml, omethoate 1.6 Hg/ml) and during the hospitalisation and proved to be considerably high. Slow elimination rate of the poison already distributed in the body was indicated for both pesticides. The patient with omethoate poisoning remained clinically well (Glasgow Coma Scale : 15) and was discharged three days later. The patient with fenthion poisoning, who had also ingested 30 mg of bromazepam and 720 mg of oxetoron, developed cholinergic crisis six hours after admission and was intubated for 24 days, with concomitant complications.     

细胞融合高效菌株对氧乐果生产废水中有机磷的去除

两株具有单重抗药性的突变菌株S-8菌株(Str+,Kan-)和K-17菌株(Str-,Kan+),其活性污泥对氧乐果生产废水有机磷的去除率分别达58%和51%,对COD的去除率分别达78%和82%。以S-8菌株和K-17菌株作为亲本菌株进行原生质体融合,其正交试验的优化条件为:PEG浓度40%;促融时间4min;用0.015 mol/LCa2+处理;pH 10.0;添加20μL/ml细胞壁再生引物,融合率达4.617×10-5。用双层药物平板筛选融合细胞,获取了既能降解有机磷又能降低COD值的融合子F2。结果表明,用融合子F2菌株增殖而成的活性污泥对上述氧乐果生产废水有机磷的去除率达78%,COD的去除率达88%。     

氧化乐果曲霉降解特性和中间产物的研究

在氧化乐果和葡萄糖共基质条件下,曲霉G21优先利用葡萄糖作为碳源,葡萄糖耗尽后开始快速降解氧化乐果,高浓度氧化乐果抑制了曲霉G21的生物降解活性.GC-MS分析表明,曲霉G21降解氧化乐果的主要中间产物为O,O,S-三甲基磷酸酯,氧化乐果降解率提高不会导致该有毒中间产物的累积效应.     

Sonochemical degradation of organophosphorus pesticide in dilute aqueous solutions

Ultrasonic irradiation was found to accelerate the rate of hydrolysis of omethoate in aqueous solution over the pH range of 2—12. Process parameters studied include pH, steady-state temperature, concentration, and the type of gases, Greater than 96% hydrolysis was observed in 30 minutes through this process and the rate of destruction increased with the help of more soluble and low thermal inert gas. So with Krypton, omethoate was found to undergo rapid destruction as compared with Argon. In the presence of ultrasound, the observed first-order rate of hydrolysis of omethoate is found to be independent of pH. The formation of transient supercritical water(SCW) appears to be an important factor in the acceleration of chemical reactions in the presence of ultrasound. A detaiied chemical reaction mechanism for omethoatedestruction in water was formulated. Experimental results and theoretical kinetic mechanism demonstrated that the most of the omethoate undergo destruction inside the cavitating holes. A very less effect of temperature on the degradation of omethoate within a temperature range of 20——70℃ proves that a small quantity of omethoate undergoes secondary destruction in the bulk liquid.     

水解法去除氧化乐果合成废水中有机磷的研究

通过对氧化乐果合成废水中有机磷水解的研究,求得有机磷的水解反应级数和速度常数。结果表明,有机磷的水解率,主要取决于废水的pH值和温度。较低的pH值和较高的废水温度,可提高其水解速度和水解率。