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21.
文章建立了简单、快速的阿维菌素菌渣中阿维菌素残留量高校液相色谱检测方法以及利用水热法处理阿维菌素菌渣。采用固相萃取-高效液相色谱检测方法测定阿维菌素菌渣中阿维菌素残留量,提取剂为乙腈/水=4/1(V/V),采用HLB固相萃取柱进行净化。加标回收率90.3%~107.3%,相对标准偏差(RSD)为3.00%~5.69%,阿维2菌素标准曲线线性相关系数R~2=0.999 6,线性范围为1.0~1 000 mg/L。利用正交实验,水热法处理阿维菌素菌渣,在190℃的温度下处理2 h后,菌渣中阿维菌素残留量由991.30降至0.84 mg/kg,去除率达99.92%。处理前后的菌渣与有机肥标准作对比,除含水率外其余检测指标均达到有机肥标准要求。该项研究为阿维菌素菌渣的资源化利用提供了理论依据。  相似文献   
22.
左氧氟沙星的超声/H2O2联合降解研究   总被引:3,自引:0,他引:3  
采用超声/H2O2高级氧化技术对喹诺酮类抗生素左氧氟沙星进行降解,考察了H2O2浓度、超声功率、溶液初始pH值对反应过程的影响.结果表明,与单独超声和H2O2氧化相比,超声/H2O2对左氧氟沙星具有明显的协同降解作用. H2O2 添加浓度在3.0~20.0mmol/L范围, 左氧氟沙星的降解率随其添加浓度的增加而增加;超声功率在260W时降解效果最佳;左氧氟沙星初始浓度在10~30mg/L范围内,左氧氟沙星的降解量随其初始浓度的增加而增加;超声/H2O2降解左氧氟沙星在未调节(pH 7.14)效果最佳. HPLC分析发现降解过程主要有2种产物生成, 产物的生成和分布受体系pH的影响较大.  相似文献   
23.
摘要:文章采用实验室内部的非标准方法《底泥中阿特拉津残留量的液相色谱测定方法》测定底泥中的阿特拉津残留量。通过对影响测定结果的不确定度分量的分析和量化,求出被测量的标准不确定度,给出各分量对测定结果不确定度的相对贡献,对测定结果进行了表述。对实际河道底泥样品中的阿特拉津残留量进行了测定,得到阿特拉津农药残留量的拓展不确定度为0.23ug/g,k=2。  相似文献   
24.
建立了固相萃取-高效液相色谱法(SPE-HPLC)测定东湖水样中微囊藻毒素(MC)的方法,考察了不同流动相、淋洗液和洗脱液对MC-RR和MC-LR测定的影响。结果表明,MC-RR和MC-LR的方法检出限分别为0.0789μg/L和0.0234μg/L,其线性定量范围分别为0.1~10.0mg/L和0.06~10.0mg/L;样品测定回收率为78.4%~97.4%,RSD小于6.3%。该法灵敏度高,快速准确,用于实际水样测定的结果令人满意。  相似文献   
25.
For several decades, perfluorooctane sulfonate (PFOS) has widely been used as a fluorinated surfactant in aqueous film forming foams used as hydrocarbon fuel fire extinguishers. Due to concerns regarding its environmental persistence and toxicological effects, PFOS has recently been replaced by novel fluorinated surfactants such as Forafac®1157, developed by the DuPont company. The major component of Forafac®1157 is a 6:2 fluorotelomer sulfonamide alkylbetaine (6:2 FTAB), and a link between the trade name and the exact chemical structure is presented here to the scientific community for the first time. In the present work, the structure of the 6:2 FTAB was elucidated by 1H, 13C and 19F nuclear magnetic resonance spectroscopy and high-resolution mass spectrometry. Moreover, its major metabolites from blue mussel (Mytilus edulis) and turbot (Scophthalmus maximus) and its photolytic transformation products were identified. Contrary to what has earlier been observed for PFOS, the 6:2 FTAB was extensively metabolized by blue mussel and turbot exposed to Forafac®1157. The major metabolite was a deacetylated betaine species, from which mono- and di-demethylated metabolites also were formed. Another abundant metabolite was the 6:2 fluorotelomer sulfonamide. In another experiment, Forafac®1157 was subjected to UV-light induced photolysis. The experimental conditions aimed to simulate Arctic conditions and the deacetylated species was again the primary transformation product of 6:2 FTAB. A 6:2 fluorotelomer sulfonamide was also formed along with a non-identified transformation product. The environmental presence of most of the metabolites and transformation products was qualitatively demonstrated by analysis of soil samples taken in close proximity to an airport fire training facility.  相似文献   
26.
Hydrogen cyanide (HCN) poisoning due to amygdalin (AMY) in apricot seeds is one of the public health issues in Turkey. The aim of this study was to investigate the AMY content of 13 different apricot seeds including bitter and sweet ones, and which are either sulfurized or roasted. The AMY content was determined by a high-performance liquid chromatography. Release of HCN was predicted and total amount of seeds which can cause poisoning was calculated. The mean AMY content of bitter seeds was 26 ± 14 mg g?1 and that of sweet seeds was 0.16 ± 0.09 mg g?1. The consumption of small amounts of bitter seeds may cause cyanide poisoning.  相似文献   
27.
Dissipation curves of azoxystrobin and of the neonicotinoids acetamiprid and thiacloprid in peach; azinphos-methyl and carbaryl in pear and azoxystrobin, chlorfenapyr and chlorpyrifos in high-tunnel tomato crops were studied in the Southern region of Uruguay. An analytical methodology based on solid phase extraction (SPE) and detection by High Performance Liquid Chromatography with Diode Array Detector (HPLC/DAD) was used for acetamiprid and thiacloprid. Coupled SPE and detection by Gas Chromatography with Mass Selective Detector (GC/MSD) was used for the detection of azinphos-methyl, azoxystrobin, carbaryl, chlorfenapyr and chlorpyrifos residues. Curves were modeled mathematically with Solver program of Microsoft Excel®. The best fit for acetamiprid and thiacloprid in peach was achieved with the exponential model (r2=0.961 and 0.944, respectively). In the case of peach fruits there is not a Maximum Residue Limit (MRL) for acetamiprid in the Codex Alimentarius, while 0.5 mg/kg is the value rated for thiacloprid. The MRLs accepted by the European Union (EU) are 0.1 mg/kg for acetamiprid and 0.3 mg/kg for thiacloprid. According to the curves determined in these experiments, thiacloprid residues 10 to 12 days after application (daa) were below the MRLs established by both sources. In the case of acetamiprid, 25 daa would be required, according to the exponential mathematical model, to get residues levels below the MRL values established by the EU. For azinphos methyl in pear, the residues detected were mathematically fitted to an exponential model (r2=0.999). According to it, residue levels under the MRL established by the EU (0.05 mg/kg) are gotten in our conditions in 20 daa. In plastic tunnel tomato chlorfenapyr residues were not detected from 16 daa, having the dissipation curve an exponential trend. In the same condition, there was not a decay of the azoxystrobin concentration during a 24-day trial, being it around 0.40 ± 0.05 mg/kg.  相似文献   
28.
液相吸收-高效液相色谱法测量气相OH方法的建立   总被引:5,自引:0,他引:5  
利用水杨酸溶液相OH自由基,生成的荧光产物2,5-二羟苯甲酸用高效液相色谱法分离测定,推算得到气相OH浓度,根据此原理在实验室条件下,建立了气相OH自由基的测定方法,并利用气相OH标准发生源确定了最优实验条件,得到了气相OH浓度与荣光响应关系。由相吸收-高效液相色谱法测定的浓度与标准OH气流中的理论浓度比较一致。  相似文献   
29.
文中采用江苏盐城滩涂响水到滨海一带的滩涂土壤样品,利用索氏提取法提取、硅胶柱净化、高效液相色谱法分离检测土壤样品中的多环芳烃(PAHs),并用优化洗脱程序对滩涂土壤中PAHs的含量进行了测定。结果表明:11个滩涂土壤样品中检出萘、苊烯、菲、蒽、荧蒽、芘六种PAHs,其含量较低,说明该段滩涂土壤尚未受到多环芳烃的污染。  相似文献   
30.
高效液相色谱-原子荧光光谱联用分析土壤中形态砷   总被引:2,自引:0,他引:2  
采用高效液相色谱(HPLC)-原子荧光光谱(AFS)联用技术分析土壤中亚砷酸盐[As(Ⅲ)]、二甲基砷(DMA)、一甲基砷(MMA)和砷酸盐[As(Ⅴ)]等4种形态砷,以磷酸为提取剂、抗坏血酸为还原剂,优化了水浴提取条件。As(Ⅲ)、DMA、MMA和As(Ⅴ)在7 min之内实现了完全分离,在1.00μg/L~100μg/L范围内线性良好,实验室检出限分别为0.25μg/L、0.36μg/L、0.39μg/L和0.51μg/L,土壤标准样品平行测定的RSD≤7.4%,加标回收率为79.5%~95.0%,提取率为74.6%~90.4%。  相似文献   
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