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1.
单嘧磺隆正辛醇-水分配系数的测定   总被引:1,自引:0,他引:1  
本文建立了水中微量单嘧磺隆的测定方法 ,方法的平均添加回收率为 97 6%—1 0 1 93%,变异系数为 0 47%— 3 96%,单嘧磺隆的最小检出量为 2× 1 0 - 9g ,最小检出浓度为 0 0 2 μg·ml- 1 .摇瓶法对单嘧磺隆正辛醇 水分配系数的测定结果表明 ,单嘧磺隆在二次蒸馏水和pH 7 0缓冲液中的Kow分别为 3 90± 0 1 4和 2 1 9± 0 1 4 ,lgKow分别为 0 5 9± 0 0 3和 0 34± 0 0 6,在双蒸水中的测定结果与EPIWIN程序的预测结果一致  相似文献   

2.
气溶胶水溶性无机物及有机物的离子色谱测定   总被引:14,自引:0,他引:14  
利用离子色谱技术同时测定大气气溶胶中的水溶性有机物 (WSOC)与各种无机成分 ,检测出 1 2种无机离子 (F- ,Cl- ,NO-2 ,NO-3 ,SO2 -3 ,SO2 -4 ,PO3-4 ,Na ,NH 4,K ,Mg2 ,Ca2 )及 7种WSOC (甲酸、乙酸、甲磺酸、乙二酸、丙二酸、丁二酸、戊二酸 ) .该方法对无机离子的线性范围为 0 0 1— 1 0 0 0 μg·m- 3,有机物的线性范围为 0 0 0 5—1 0 μg·m- 3,相关系数除NH 4以外均高于 99 9% ,最低检测限为 0 0 0 0 1— 0 0 0 0 5 μg·m- 3,相对标准偏差为 0 43— 1 32 % .利用该技术 ,对北京市 2 0 0 1— 2 0 0 2年度大气PM2 5中水溶性物种的浓度水平进行了测定 .结果表明 ,北京市PM2 5中主要的水溶性组分为SO2 -4 ,NO-3 和NH 4,其浓度水平分别为 1 1 1 ,7 8和 6 2 μg·m- 3,各占PM2 5 质量的 1 0 6% ,7 4%及5 7% ,而WSOC的浓度水平为 0 0 1 1— 0 1 1 8μg·m- 3,占PM2 5质量浓度的 0 0 1— 0 1 % ,其中 ,乙二酸的浓度最高 ,其次为乙酸、丁二酸 ,丙二酸等 .  相似文献   

3.
在设定的湿式氧化条件下 ,从若干种金属盐中筛选了Cu(NO3) 2 作为氧化甲醛废水的催化剂 ,考察了Cu(NO3) 2 用量、废水的初始浓度及温度对有机物去除率的影响 ,结果表明 :Cu(NO3) 2 以 5mg·l- 1 Cu2 计量投加为宜 ,甲醛初始浓度在 480mg·l- 1 — 1 5 0 0mg·l- 1 范围内一直保持较高的去除率 ,反应的适宜温度为 1 40℃以上 ;根据反应过程数据建立了该催化氧化反应的分段一级动力学模型 ,求得甲醛氧化动力学模型快、慢步骤的表观活化能分别为7 2 9kJ·mol- 1 和 1 4 45kJ·mol- 1 ;而COD降解动力学模型快、慢步骤的表观活化能则分别为2 0 47kJ·mol- 1 和 2 9 5 2kJ·mol- 1 .  相似文献   

4.
陕西省潼关采金地区汞污染的初步研究   总被引:6,自引:1,他引:5  
对采金地区水样、沉积物、土壤及部分水藻和苔藓的分析表明 :潼关采金地区已经受到严重的汞污染 .水体总汞浓度最高达 2 5 8 62 μg·l- 1 ,且水样中的汞以颗粒态为主 ,大都占 5 0 %以上 ,而活性汞和溶解态汞的平均浓度分别为 0 1 82± 0 2 4 2 μg·l- 1 和 0 72± 0 79μg·l- 1 ;沉积物中平均汞浓度为 34 98± 2 5 39μg·g- 1 ,最高达 1 1 96μg·g- 1 ;而土壤中汞的浓度最高也只有 1 9 5 0 μg·g- 1 .  相似文献   

5.
雷州无瓣海桑群落7种元素的生物累积和循环   总被引:1,自引:0,他引:1  
在雷州市附城镇岚北人工生态恢复的 7a生无瓣海桑群落生物量调查的基础上 ,对所采集的无瓣海桑进行了植物体各组分样品的灰分和元素含量测定与循环分析 ,结果表明 :无瓣海桑植物体不同组分的灰分含量范围为 2 .2 7%~ 2 6 .4 1% ,以细根的含量最高 ,枯枝的含量最低 .植物体各组分中 7种元素质量分数范围分别为K 0 .11%~ 1.5 6 % ,Na0 .11%~ 1.6 6 % ,Ca 0 .2 0 %~ 2 .6 6 % ,Mg 0 .15 %~ 1.5 9% ,Fe 0 .0 4× 10 -3 ~ 9.6 4× 10 -3 ,Zn 0 .0 5× 10 -4~ 1.0 3× 10 -4,Cu0 .16× 10 -5~ 1.5 0× 10 -5.其加权平均的富集系数为 0 .0 5~ 9.70 ,其中Ca >K >Cu >Na >Mg>Zn >Fe .群落现存生物量中的累积储量分别为K 10 9.76gm-2 ,Ca 138.89gm-2 ,Na 86 .5 7gm-2 ,Mg 81.0 7gm-2 ,Fe 13.139gm-2 ,Zn 0 .4 83gm-2 ,Cu 0 .10 8gm-2 .群落 2 0 0 1年的元素存留累积储量分别为Ca4 1.6 8gm-2 ,K 37.2 4gm-2 ,Mg 2 7.33gm-2 ,Na2 5 .5 6gm-2 ,Fe 4 .2 75gm-2 ,Zn 0 .188gm-2 ,Cu 0 .0 39gm-2 .2 0 0 1年归还量分别为Ca 2 8.5 9gm-2 ,K 16 .83gm-2 ,Mg 12 .0 7gm-2 ,Na 11.5 8gm-2 ,Fe 0 .916gm-2 ,Zn 0 .14 1gm-2 ,Cu 0 .0 2 6gm-2 .年吸收量分别为Ca 70 .2 7gm-2 ,K 5 4 .0 7gm-2 ,Mg 39.4 0gm-2 ,Na 37.1  相似文献   

6.
气溶胶水溶性有机物(WSOC)中二元羧酸的测定   总被引:5,自引:1,他引:5  
提出了BF3 /丁醇酯化衍生反应 GC/MS分析大气气溶胶水溶性有机物 (WSOC)中二元羧酸 (乙二酸、丙二酸和丁二酸 )的测定方法 .其相应酯化产物乙二酸二丁酯、丙二酸二丁酯和丁二酸二丁酯的线性范围为 1× 1 0 - 5mol·l- 1— 1× 1 0 - 2 mol·l- 1,精密度分别为 1 6 7% ,3 0 4 %和 5 2 8% ;最低检测限分别为 1 9× 1 0 - 7mol·l- 1,1 1×1 0 - 7mol·l- 1和 1 2 5× 1 0 - 6mol·l- 1.并实测了北京市秋、冬两季乙二酸、丙二酸和丁二酸的平均浓度水平 ,分别为 4 44ng·m- 3 ,4 0ng·m- 3 ,30 2ng·m- 3 .  相似文献   

7.
南方红豆杉种子的化学成分分析   总被引:10,自引:0,他引:10  
对南方红豆杉种子 (种仁 )的化学成分分析表明 :南方红豆杉干重 (DW)种子粗蛋白、粗脂肪、淀粉、可溶性糖的质量分数wDW分别为 9.92g (10 0g) -1,72 .86g (10 0g) -1,4 .15g (10 0g) -1,0 .38g (10 0g) -1;氨基酸的wDW为 9.10g (10 0g) -1,其中必需氨基酸占总氨基酸量的 2 8.0 5 % ;种子油脂肪酸组成以不饱和的油酸和亚油酸为主 ,其相对含量为 4 8.4 %和 4 2 .2 % ;种子元素质量分数分别为 :wDW(N) =15 87.2mg (10 0g) -1,wDW(P) =5 6 5 .4mg (10 0g) -1,wDW(K) =2 6 1.1mg(10 0g) -1,wDW(Ca) =18.4mg (10 0g) -1,wDW(Mg) =35 0 .5mg (10 0g) -1,其余微量元素含量由多到少依次为Zn >Fe>Na>Cu >Mn .表 4参 6  相似文献   

8.
报道了霸螨灵在苹果上残留动态的研究情况。霸螨灵在苹果果实中的原始沉积量 1995年和 1996年分别为 0 .4 70和 0 .761mg/kg,消解半衰期分别为 2 .5和 3.5d。两年试验结果消解趋势基本一致。按推荐剂量 2 0 0 0倍液和高剂量 10 0 0倍液分 2次和 3次施药 ,14 d后测定 ,霸螨灵在苹果中的残留量分别为 0 .0 98m g/kg和 0 .132 m g/kg,不超过 FAO/W HO关于霸螨灵在苹果中残留限量 1m g/kg的规定 ,因而对人是安全的  相似文献   

9.
川西米亚罗地区亚高山针叶林建群种云杉土壤种子库研究   总被引:3,自引:0,他引:3  
对川西米亚罗地区天然亚高山针叶林云杉种群的种子雨和土壤种子库进行了研究 .结果表明 :云杉种子雨过程从 2 0 0 2年 10月初到翌年 1月初 ,种子雨雨量 (n)为 5 79.99± 110 .84粒 /m2 ,其中种子下落主要集中在 11月 ,占种子雨总量的 5 7.80 % .种子雨分布格局呈集群分布 .于 2 0 0 3年春季 (3月 )和夏季 (8月 )两次对该天然云杉林土壤种子库取样 ,土壤种子库大小分别为 4 72 .8± 74 .82粒 /m2 和 185 .5± 89.95粒 /m2 ;腐烂种子分别为 39.6 0± 13.2 4粒 /m2和 12 0 .0± 6 3.39粒 /m2 ,腐烂种子比例由 8.39%增加到 6 4 .6 9% ;空粒种子分别为 118.8± 4 4 .6 6粒 /m2 和 6 5 .5± 2 6 .4 8粒 /m2 ,所占比例从 2 5 .14 %增加到 35 .31% .两次取样结果都表明 ,种子库种子主要集中在枯枝落叶层 ,分别占6 6 .17%和 6 6 .0 3% ,0~ 2cm层占 2 4 .73%和 2 3.4 5 % ,2~ 5cm层占 9.10 %和 10 .5 1% .到 8月 ,土壤中几乎所有云杉种子都失去活力 ,说明云杉种子库属于Thompson和Grime定义的第Ⅱ类型 ,即土壤种子库仅在冬季存在 ,在春季萌发 .土壤中春、夏、秋季种子很少或几乎没有 .林下云杉幼苗在 2 0 0 3年 6月 3号开始出现 ,在 6月中旬左右到达出苗高峰 ,累计平均幼苗数 4 .35株 /m2 .在川西米亚罗地区天然  相似文献   

10.
利用HPLC测定21个不同品种苦荞籽粉和麸皮中芦丁、山奈酚-3-芸香糖苷、槲皮素和山奈酚的含量.采用RP-HPLC,用Damonsil C18色谱柱(4.6 mm×250 mm,5μm),以乙腈-0.2%冰醋酸水溶液为流动相进行梯度洗脱,流速为1.0 m L/min,检测波长为354 nm,柱温30℃.结果显示,在室温状态下,21种不同品种的苦荞种子中水分含量在4.907 3%-6.993 6%之间,恒重状态下,麸皮质量分数为21.84%-30.03%,麸皮重量约占苦荞籽粒质量的1/4.芦丁、山奈酚-3-芸香糖苷、槲皮素和山奈酚的线性范围分别在20-400μg/m L、2-40μg/m L、1-20μg/m L、0.5-10μg/m L;不同品种苦荞籽粉中,芦丁、山奈酚-3-芸香糖苷、槲皮素和山奈酚的含量范围分别为12.137 0-20.318 6 mg/g、1.478 7-2.871 9 mg/g、0.014 6-0.901 5 mg/g、0-0.015 9 mg/g,4种主要黄酮的总含量为14.015 1-22.871 7 mg/g;麸皮中芦丁、山奈酚-3-芸香糖苷、槲皮素和山奈酚的含量范围分别为4.269 0-12.118 9 mg/g、0.258 5-1.014 9 mg/g、0.061 8-0.735 4 mg/g、0-0.026 3 mg/g,4种主要黄酮的总含量为4.651 1-13.148 6 mg/g.本研究表明,无论在籽粉还是麸皮中,芦丁都是含量最高的黄酮,其次为山奈酚-3-芸香糖苷和槲皮素,山奈酚的含量在万分之一以下;本研究可为苦荞籽粉和麸皮中主要黄酮的开发和优良品种的利用提供重要依据.  相似文献   

11.
Künnemann  H. 《Marine Biology》1973,18(4):260-271

Rhodeus amarus acclimated to 10° or 20°C die at 31.7° or 36.4°C, respectively (cessation of operculum movements). After raising the adaptation temperature (AT) from 10° to 20°C, adaptation is complete after 8 days. The toxicity of actinomycin D, injected intraperitoneally, is AT-dependent (e.g. at 5°C, LD50–7 days=0.8 μg/g fish; at 25°C, LD50–7 days=0.35 μg/g fish). In the following experiments 0.5 μg actinomycin/g fish were used. After actinomycin-injection, RNA-values in white dorsal muscle decreased about 50% within 12 h and the values of control individuals were finally attained after 16 days. Following an AT-change from 10° to 20°C, DNA-values in the white dorsal muscle increased about 10%, RNA-values about 30%, within 12 h. However, in fish injected intraperitoneally with actinomycin, no increase in DNA or RNA was noticed. Actinomycin injection per se causes increased heat resistance. This process lasts 10 days. If AT is raised now from 10° to 20°C, the new resistance level is reached later. The control fish gain resistance at a rate of about 1 C°/day during the first days after the temperature change. Actinomycin-treated individuals, however, exhibit an increase of 0.25 C°/day. Inhibition of resistance adaptation due to proteinbiosynthesis-inhibitors supports the view that protein synthesis is of importance for adjustments in heat resistance of intact animals.

  相似文献   

12.
Degradation of biochanin A, 400 μg (1.41 μmol) per gram of dry soil, was studied and the initial degradation products, dihydrobiochanin A, pratensein and genistein were identified and quantified. The maximum concentrations of these compounds were determined as 166 pmol/g dry soil after 2 days of incubation, 175 pmol/g dry soil after 1 day and 1,236 pmol/g dry soil after 1 day, respectively. Biochanin A and the initially formed products degrade too fast to be responsible for clover soil sickness (DT90 <20 days), but could be precursors for the responsible compounds. The immediate degradation products from biochanin A are all biologically active and are the prime candidates for a reduction of weed pressure caused by clover.  相似文献   

13.
Fifty sandworms, Nereis virens, were maintained in a closed aquarium system with continuous charcoal filtration at 12°C and 27.6‰ S. They were dosed orally for 10 consecutive days with a mixture of three pentachlorobiphenyls: 35 ng 2,4,6,2',4'-pentachloro[U-14C]biphenyl, 106 ng 2,4,5,2',5'-pentachlorobiphenyl, and 106 ng 2,3,4,2',5'-pentachlorobiphenyl per g of Nereis virens per day. At the end of the dosing period the accumulated compounds were measured in 5 worms, the remaining 45 specimens were divided into three groups for determining the PCB elimination under different conditions for 14 to 26 weeks: in the laboratory with feeding, in the laboratory without feeding, and in a cage moored in the Weser estuary.

The accumulation percentages for these PCB compounds were 41, 26 and 4% respectively. Times for the initial 50% decrease te50 were 4.4, 2.8 and 1.9 weeks respectively, and appeared the same in all three experimental groups. However, in the laboratory experiments the metabolites of the 14C-labelled compound amounted to ∼60%, compared to the field experiment with ∼30%. This extended the te50 for 14C activity (metabolites included) to ∼9 weeks in the laboratory experiments.  相似文献   

14.
以菘蓝(Isatis indigotica Fort)幼苗为实验材料,比较研究了He-Ne激光对增强UV-B(辐射强度:10.08kJ·m-2;照射时间8h·d-1;共照射8d)辐射损伤菘蓝叶片衰老的延缓作用.结果表明:与对照相比,UV-B辐射可导致环丁烷嘧啶二聚体(CPD)形成,显著降低蛋白酶、转氨酶、游离氨基酸、可溶性蛋白质含量,同时降低了叶绿素含量、气孔导度、水分利用率和生物量;而菘蓝幼苗经UV-B辐射处理后再用激光辐照(波长:633nm;功率密度:5.23mW·mm-2;束径:1.5mm;照射时间:5min·d-1),叶片中CPD含量显著降低,蛋白酶、转氨酶、游离氨基酸、可溶性蛋白质含量、叶绿素含量、气孔导度、水分利用率和生物量与单独UV-B处理组相比显著提高.上述结果表明激光辐照可以显著延缓UV-B损伤菘蓝叶片的衰老。  相似文献   

15.
Growth and metabolism of the winter flounder Pseudopleuronectes americanus were studied in the laboratory at 2°, 5° and 8°C. Dry-weight determinations of growth demonstrated significant direct regressions of growth on temperature. Mean, daily specific growth rates were 10.1%/day at 80°C, 5.8%/day at 50°C, and 2.6%/day at 2°C. Time to metamorphosis was 49 days at 8°C and 80 days at 5°C. Larvae did not survive to metamorphosis at 2°C. Absolute values of routine metabolism expressed in μl of oxygen consumed regressed on body weight were best described by a third-degree polynomial. Larval routine metabolism increased from hatching to metamorphosis, at which time it declined before again increasing. Temperature directly affected routine metabolism. Metabolism on a unit-weight basis decreased with increasing size and was also directly influenced by temperature.  相似文献   

16.
The average initial deposits of carbaryl were observed to be 1.4 and 3.1?mg?kg?1, respectively, following four applications of the insecticide at 4.95 and 9.9?kg active ingredient per hectare. Residues of carbaryl dissipated below its limit of quantification of 50?µg?kg?1 after 7 and 10 days at single and double the application dosage, respectively. The half-life values (t 1/2) of carbaryl were worked out to be 1.3 and 0.7 days, respectively, at single and double dosages. The acceptable daily intake (ADI) for carbaryl has been fixed at 8?µg?kg?1 body weight per day. Keeping in view the residues of carbaryl observed one day after the last application, a child of 10?kg and an adult of 60?kg will have an intake of 77 and 154?µg carbaryl after consumption of 100 and 200?g grapes, in comparison to its ADI of 80 and 480?µg; thus, no health risk is to be expected. Therefore, a waiting period of 1 day has been suggested for the safe consumption of carbaryl-treated grapes to avoid any health hazards.  相似文献   

17.
A field study was conducted to measure the dislodgeable residues of profenofos applied to jasmine (Jasminum sambac) and risk assessment was done for laborers engaged in picking of flower buds. Profenofos was applied at 0.10, 0.15, and 0.20% concentration and the jasmine bud samples were analysed for residues using GC. The initial deposit of 1.6–3.8, 3.8–7.1, and 5.2–7.6 µg cm?2 was detected on jasmine buds at 0.10, 0.15, and 0.20% concentration, respectively. At the recommended dose of 0.10%, the half-life was 1–2 days and the dislodgeable residues disappeared within 7 days. The results indicate faster disappearance of dislodgeable residues on jasmine buds. Risk assessment was done based on dislodgeable foliar residues and exposure estimates based on surrogate data and expressed as Margin of Exposure (MOE). The entry restrictions for exposure of jasmine flower pickers to profenofos, would be at least, 1 day following application, for the recommended concentration of 0.10% (MOE = 106) and 3 days, at higher concentrations of 0.15% (MOE = 156) and 0.20% (MOE = 115).  相似文献   

18.
Postelsia palmaeformis were collected from the lower intertidal at Pigeon Point, California, USA, in May 1987, and the proximate composition and allocation of energy to the various body components were determined. The holdfast and stipe have a proximate composition (% dry weight) of ca. 40% ash, 5.3% protein, 1% lipid, 2% soluble carbohydrate, and 55% insoluble carbohydrate. The fronds have a proximate composition of ca. 25% ash, 6.5% protein, 2% lipid, 3% soluble carbohydrate, and 65% insoluble carbohydrate. The energetic level was ca. 12 kJ g-1 dry wt and ca. 19 kJ g-1 ash-free dry wt. The relative proportion of three plant components varied, comprising 26, 39, and 35% wet wt and 20, 42, and 38% kJ for the holdfast, stipe, and fronds, respectively. A plant with a basal stipe diameter of 33 mm contains 114 g wet wt and 266 kJ. The maximal density found in May 1987 was 826 plants, 49 301 g wet wt, and 106 157 kJ m-2.P. palmaeformis differs in these characteristics from another intertidal pheophyte,Durvillaea antarctica, that is found in a high-energy intertidal zone.  相似文献   

19.
明日叶查尔酮对小鼠H22肝癌细胞增殖活性的抑制作用   总被引:1,自引:0,他引:1  
为研究明日叶查尔酮(AC)对小鼠H22+肝癌细胞增殖的抑制作用,采用如下方法进行实验:1)将50只荷H22肝癌小鼠随机分为5组,每组10只.低、中、高剂量组每日分别灌胃给予5、20和40 mg·kg-1明日叶查尔酮,肿瘤对照组给予生理盐水,环磷酰胺(CTX)组隔天腹腔注射20 mg· kg-1的CTX.饲养10 d后处...  相似文献   

20.
Oxidative stress and antioxidant responses of crucian carp, upon chronic exposure to endosulfan, were evaluated in vivo. The lethal concentration (LC50–96?h) was 70 μg L?1; on its basis, the fish were exposed to endosulfan at 20, 35, and 50 μg L?1 and autopsy was done on days 1, 2, 3, 4, 7, 14, 21, 28, and 35. Lipid peroxidation was induced in a concentration-dependent manner, being highest at 50 μg L?1 (3/4 LC50–96 h, sub-lethal concentration-I, SL-I) on day 4 (720% versus control), followed in its extent (490%) at 30 μg L?1 (1/2 LC50–96 h, sub-lethal concentration-II, SL-II) on day 7 and lowest (260%) at 10 μg L?1 (1/4 LC50–96 h, sub-lethal concentration-III, SL-III) on day 14. Glutathione showed a concentration- and time-dependent elevation in the initial phase, with highest level on day 4 (180%) at SL-I, but showed significant reduction in all test concentrations from day 21 of post-exposure. Superoxide dismutase was decreased significantly throughout the study, with highest reduction (63%) on day 4 at SL-I; catalase increased in all test concentrations up to day 14 but showed a significant decrease from the day 28 of post-exposure. The potential role of these parameters as indicators of pesticide pollution in aquatic systems is discussed.  相似文献   

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