起始浓度的英文

• initial concentration
• threshold concentration

• "起始"英文翻译    origin; origination; parenta ...
• "浓度"英文翻译    potency; thickness; concentr ...
• "dna起始浓度" 英文翻译 :    initial concentration of dna
• "原始浓缩常数,不变的起始浓度" 英文翻译 :    constant initial concentration
• "初始浓度" 英文翻译 :    initial concentration of dust
• "原始浓度" 英文翻译 :    primary concentration
• "起始" 英文翻译 :    origin; origination; parentage; germ; initiation 他的这个问题起始于孩提时代。 his problem began when he was a child
• "浓度" 英文翻译 :    potency; thickness; concentration; consistence; strength; consistency; density 当量浓度 [化学] equivalent concentration; 高浓度 high concentration; 矿浆浓度 pulp density
• "起始段；起始值" 英文翻译 :    threshold
• "卷起始" 英文翻译 :    volume initialization
• "链起始" 英文翻译 :    chain initiation
• "起始；预置" 英文翻译 :    initialize
• "起始板" 英文翻译 :    starting sheet
• "起始边" 英文翻译 :    initial side
• "起始槽" 英文翻译 :    starting vessel
• "起始层" 英文翻译 :    starting course
• "起始场" 英文翻译 :    initial field
• "起始处" 英文翻译 :    b0t; beginning of tape marker (bot)(btm); section start
• "起始的" 英文翻译 :    incipient; initiative; parent
• "起始地" 英文翻译 :    ground one
• "起始点" 英文翻译 :    initial point; initial station; initiation point; initiation site; poi point of initiation; point of initiation poi; point of origin; starting point; the point of beginning
• "起始端" 英文翻译 :    beginning end; initiating terminal
• "起始段" 英文翻译 :    start paragraph
• "起始符" 英文翻译 :    start symbol
• "起始混" 英文翻译 :    initial contamination

• When shaded , no remarkable allelopathic effect on each kind of algae was showed
  水华鱼腥藻起始浓度越小，菖蒲种植水对其化感抑制作用越显著。
• If you have ever worked in a lab you probably know how time consuming these calculations are
  应用化学计算器，只需输入最终浓度（摩尔浓度或百分浓度） 、起始浓度以及需配制的体积，便给出配制用量，非常方便。
• For each method final system ph value , circumstance temperature and the concentration of starting materials have different influence on fonnation of sol
  在制备溶胶过程中，最终体系ph值、环境温度和反应物起始浓度对各方法的影响不同。
• Results indicated that hrp could effectively oxidate pcp in aqueous solution . factors , such as acidity , temperature , enzyme activity , and initial concentration of pcp and h
  采用辣根过氧化物酶催化去除模拟废水中的五氯酚，使其形成沉淀并探讨了影响反应的因素如溶液酸度酶浓度五氯酚起始浓度过氧化氢起始浓度以及温度等。
• In this dissertation , the synthesized conditions , such as the initial concentration of ti4 + , the initial acidity , the reactive temperature and the reactive time , have been studied with their effects on the photochemical activity of the product and the four preparation methods have been compared and optimized
  并分别实验研究了钛液起始浓度、反应液起始酸度、反应温度、反应时间等实验条件对产品光化活性的影响，并对各制备方法进行实验条件优化和优劣比较。
• Nano - cuo powders were successfully prepared by pressure - hydrothermal method with cuso4 5h2o and naoh as materials . xrd , sem and tem were used to characterize the samples . the influence of raw materials " initial concentration , thermal treatment " temperature , pressure and thermal treatment " time on the morphology and size of cuo were analyzed , and the possible growth mechanism was also discussed
  以硫酸铜和氢氧化钠为原料，用压力-热液法合成了纳米氧化铜粉体，用xrd 、 sem 、 tem对所制得的氧化铜进行了观察与表征，分析了原料起始浓度、热处理温度、压力、 ph值及热处理时间对氧化铜形态和大小的影响，初步探讨了不同形态氧化铜的生长机理。
• The assay system of the biological activity of lymphotoxin was established using l929 cell as the sensitive target , lt international standard as the positive control and crystal violet staining method to detect viable cell after treated with lt . the best relationship between dosage and effect could be got if the cell seeding density in cell plate was 1 . 6 0 . 1 104 the dosage of amd was lug / ml , and the starting concentration of dilution in the plate of lt standard was 10 iu / ml with two fold dilution . the credibility of the established system was detected with rhtnfp developed by r & d
  为确定经上述步骤纯化后得到的目的蛋自lt 27的生物活性，本研究以l929细胞为靶细胞、淋巴毒素国际标准品为参照，采用结晶紫染色法检测经淋巴毒素处理后存活的细胞，对淋巴毒素生物活性测定的细胞接种浓度、淋巴毒素标准品板上稀释的起始浓度和梯度稀释的倍数、放线菌素d的使用剂量等进行条件实验后，建立了人淋巴毒素生物活性测定方法。
• A number of factors will affect efficiency of the biosorption , and these factors were studied in chapter three , including the ph value , initial biomass loading and content of heavy metal ions , ion strength of the solution , etc . although the research for new and innovative treatment technologies has focus attention on the metal binding capacities of various biomass , the exact interaction between the ligands of the metal uptake process and the description of the thermal properties of the biosorption remain essentially unknown
  藻类对重金属离子的吸附效率受藻类细胞表面及溶液的物理化学状态的影响，本文从ph 、藻粉的起始含量及重金属离子的起始浓度、离子强度等四个方面做了研究。第四章是大型海藻生物吸附平衡的热力学研究，我们对平衡数据做了langmuir方程的回归分析，得到了两种海藻吸附各重金属离子的最大吸附容量；我们还以cu为例研究了温度对吸附容量的影响，并计摘要算了其吸附热。
• It seems that micro - organism in soil played a very important role to decompose the herbicide with the results of microbial degradation , which the half - lifves of quizalofop - p - ethyl with a level of 50 mg / kg in clay and red soil were 9 . 9 and 15 . 7 days comparing with that in the two types of soil sterilized , 29 . 8 and 37 . 5 days , respectively
  土壤微生物对精喹禾灵在土壤环境中的降解发挥了重要的作用。起始浓度为50mg kg的精喹禾灵在未灭菌、灭菌处理青紫泥中的降解半衰期( t1c2 )分别为9 . 9和29 . 8d ，在红壤中降解半衰期分别为15 . 7和37 . 5d 。

• 起始浓度的日语：フレツシュ濃度 フレツシュのうど