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Obserdose of noradrenaline bitartrate or KCl: Sub-maximal constriction of thoracic aorta was induced by 0.1 mmol/L noradrenaline bitartrate or W60 mmol/L KCl, and when constriction curve became stable, DL or nimodipine of different dosage was added.

记录电刺激心室乳头肌时收缩的幅度变化:1次/s,波宽3 ms,阈电压的120%强度电刺激以引发心室乳头肌同步收缩活动,待收缩曲线平稳后,分别用累加法加入二氢石蒜碱或尼莫地平。

Results The in vitro coupled bacterial luciferase:FMN-NADH oxidoreductase bioluminescent system was: 1mL crude extract, 27 mmol/L Dodecane 100 μL, 10 mmol/L FMN-Na 0.5 μL and 0.14 mmol/L NADH 300 μL.

利用从鳆发光杆菌提取并经部分纯化的荧光素酶和FMN-NADH氧化还原酶,通过优化体系中各底物的添加量,实现荧光素酶的体外发光。

Soil Ca2+ content increased by 0.749mmol/kg, Mg2+ content increased by 0.169mmol/kg, the Na++ K+ content dropped by 9.52mmol?kg, SO42- increased by 0.091mmol?kg, Cl- reduced by 1.727mmol?kg, the HCO3- content in the soil assumed the obvious dropping tendency, it might be explained that the advancement of HCO3- has transformed into CO32- in the oasis, and has formed precipitation with two price calcium magnesium heteropolar ,then fix in the soil layer.

4土壤Ca2+含量增加了0.749mmol/kg,Mg2+含量增加了0.169mmol/kg ,Na++K+含量下降了9.52 mmol∕kg,SO42-增加了0.091 mmol∕kg, Cl-降低了1.727 mmol∕kg,土壤中HCO3-的含量呈明显下降趋势,可解释为在绿洲化进程中HCO3-转化为CO32-,并与二价钙镁离子结合形成沉淀固定于土层中。

Methods Malonylaldehyde, hippuric acid and p-cresol were used as the representatives of uremic toxins.

以丙二醛(10 mmol/L)、马尿酸(20 mmol/L)和对甲酚(10 mmol/L)为尿毒素代表。

The incidence of abnormal lipid trigone in children with a family history of premature CHD or non premature CHD and the controls were 52.6%, 10.9% and 1.2%, respectively.

有早发CHD家族史者LDL-C/HDL-C(2.85±1.21)高于无早发家族史组(1.37±1.11)和对照组(0.96±0.68)(P均。01),HDL-C水平[(1.11±0.26) mmol/L]低于无早发家族史者[(1.59±0.47) mmol/L]和对照组[(1.72±0.53) mmol/L]。

The results showed that the seed germination rate decreased gradually as the NaCl concentration increased .The seed germination rate and imbibition rate was lowest when the seeds were treated with 200 mmol·L~(-1)NaCl; the recovery rate of ungerminated seeds in 150 and 200 mmol·L~(-1)NaCl had no significant difference with the control and it was more higher than the seeds in100 mmol·L~(-1)NaCl.

的种子,逐日测定萌发率、吸胀率;5 d、10 d后测定种皮和种胚的Na~+、K~+含量;培养15 d后,将含有NaCl的营养液中未萌发的种子分别转入1/4 Hoagland营养液继续培养,测定解除盐胁迫后种子萌发的恢复率;以探索不同浓度的NaCl处理对海滨木槿种子萌发及其种皮和胚的Na~+、K~+含量的影响。

The experimental results indicates that the optimum pH range was 1.60~2.20, and the optimum H2O2 concentration was 10.0 mmol/L. The degradation ratio increased with the increasing concentration of ammonium ferric oxalate in the range from 0.1 to 1.0 mmol/L, but no significant increase in degradation ratio was observed when the concentration was above 1.0 mmol/L. When the concentration of fuchsin basic increased, the degradation ratio dropped, while the concentration of degraded fuchsin basic rised. When the concentration of fuchsin basic was low, the degradation followed first-order kinetics, but when it was high, the degradation could be fitted by zero-order kinetics. The absorbtion of fuchsin basic at 543 nm disappeared quickly, while the absorbtion of intermediates formed during the course of fuchsin basic dagradation at 298 nm vanished slowly.

试验结果表明:碱性品红降解的最佳初始pH为1.60~2.20,最佳初始H2O2浓度为10.0mmol/L;草酸高铁铵的浓度在0.1~1.0mmol/L时,碱性品红的降解率随浓度的增大而增大;高于1.0mmol/L时,则降解率相差不大;碱性品红的初始浓度增大,降解率减小,而实际降解的浓度则增加;碱性品红的浓度在低和高时,降解动力学过程不一致;随降解的进行,碱性品红在可见光区的吸收峰迅速消失,而降解过程中形成的中间产物吸收峰却消失很慢。

In group of different blood glucose concentration, the incidence of HT was still highest, 24% in below 10 mmol/L, DN, DR had the rapidest rising speed, the group of above 15.1 mmol/L and below 10 mmol/L increased 3.13 times and 3.5 times, respectively.

在不同的血糖组仍然是高血压发病率最高,≤10mmol/L组已达到24%,以DN、DR上升最快,≥15.1mmol/L比≤10mmol/L组增长分别为3.13倍、3.5倍。

Oxalic acid loading substantially stimulated soil P release from A1 horizon, showing a linear relationship; but its effect on B horizon soil was relatively negligible, especially at low oxalic acid concentrations mmol L^(-1. Oxalate solutions 0.5~20.0 mmol L^(-1 oxalic acid adjusted to pH 5.16 with 10.0 mmol L^(-1) NaOH had a much higher (1.51~2.98 times) soil-P-release effect than oxalic acid solution the same in oxalate concentration. Therefore, the mechanism of oxalic acid/oxalate triggering release of soil phosphorus is assumed to be dominated by ligand-exchange or complexing reactions of oxalate anionC2O(superscript 2- subscript 4 but not simply acid-dissolving effect. The effect of oxalate anion on soil phosphorus release was found to be somewhat cumulative, i.e. the amount of P released was primarily controlled by the cumulative oxalate loading rate, relatively independent of the manner of oxalate addition (one-time or sequential).

结果表明,草酸能显著促进暗棕壤A层磷的释放,土壤磷溶出量随草酸溶液浓度升高而线性增加;但对B层土壤磷的释放效应相对较弱,草酸浓度低於5mmolL^(-1)时B层磷的释放不明显。pH5.16草酸钠溶液比相同浓度的草酸溶液具有更高的解磷效率,在设置二者浓度为0.5~20.0mmolL^(-1)时,前者的解磷量是后者的1.51~2.98倍,推断草酸盐溶液或凋落物淋洗液中草酸类物质促进暗棕壤磷释放的主要机理在於草酸阴离子C2O(上标 2-下标 4配位反应。

Mmol/L to juvenile Japanese sea bass, and 75.86, 63.46, 56.42 mmol/L to black rockfish. When pH is steady at 8.40 + 0.10, the 24-, 48-, 96-hour LC50 of Alk are 72. 79, 65. 28, 57. 92 mmol/L to Japanese sea bass, and 69. 47, 59. 37, 51. 96mmol/L to black rockfish. It is obvious that the toxicity of Alk to fish increases with the progressive increase of Alk or time when pH is at a constant level.3. According to analysis of variance of orthogonal test, pH and Alk have signification effects on the mortality rate of black rockfish.

pH在正常养殖范围时,通过碱度对海水鱼类鲈鱼、黑鲪的急性毒性试验,得到pH=8.10±0.10时,碱度对鲈鱼稚鱼(体长1.6~2.2cm)24、48、96h的半致死值为60.88、44.36、36.06mmol/L,安全浓度为7.07mmol/L;pH=8.05±0.10时,碱度对黑鲳幼鱼24、48、96h的半致死值为75.86、63.46、56.42mmol/L,安全浓度为13.32mmol/L.pH=8.40±0.10时,碱度对鲈鱼幼鱼24、48、96小时的半致死值为72.79、65.28、57.92mmol/L,安全浓度为15.76mmol/L;对黑鲪幼鱼24、48、96h的半致死值为69.47、59.37、51.96mmol/L,安全浓度13.01mmol/L。

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