蔓茎堇菜细胞悬浮培养的研究

对蔓茎堇菜细胞悬浮培养的条件进行了选择,并测定悬浮培养的生长动态。结果表明：蔓茎堇菜细胞悬浮培养的最适接种量为２．０～３．５ｇ（５０ｍＬ）;最适培养基为ＭＳ＋２．０ｍｇ／Ｌ２,４－Ｄ＋１．０ｍｇ／Ｌ ＺＴ＋３００ｍｇ／Ｌ ＬＨ＋２００ｇ／Ｌ蔗糖（或葡萄糖）,ｐＨ５．８;细胞悬浮培养一个周期过程中细胞数目增长的动态基本上是一条Ｓ型曲线,对数生长期明显;细胞鲜重（ｍＦＷ）和细胞干重（ｍＤＷ）则与细胞     

Reaction mode between Si and Fe and evaluation of optimal species in poly-silicic-ferric coagulant

A kind of Fe-polysilicate polymer, poly-silicic-ferric （PSF） coagulant was prepared by co-polymerization （hydroxylation of mixture of Fe^3＋ and fresh polysilicic acid （PS））, in which PSF0.5, PSF1 or PSF3 denotes Si/Fe molar ratio of 0.5, 1 or 3, respectively. The effects of Si/Fe ratio and reaction time （co-polymerization time or aging time） on the reaction mode between Si and Fe were studies, and the optimal species of PSF was evaluated by pH change during the preparation of PSF and coagulation tests. The results showed that the characteristics of PSF are largely affected by both reaction time and Si/Fe ratio. PSF is found to be a essential complex of Si, Fe, and many other ions. The reaction mode between Si and Fe differs with various Si/Fe ratios. The pH of PSF0.5, PSF1 or PSF3 tended to be stable when reaction time is 10, 25 or 55 rain, respectively, which is almost consistent with the time reaching the relative stable morphology that is just the optimal species of higher coagulation efficiency. The optimal reaction time reaching optimal species can be evaluated by measuring the pH change during the polymerization process.     

基于MODFLOW数值模拟法的地下水饮用水源保护区划分

我国城乡居民饮用水安全现状不容乐观,饮用水源污染已经成为较突出的社会问题,其中地下水饮用水源污染更为突出.饮用水源保护区划分是保证水质安全的重要措施,饮用水源保护区划分方法较多,其中数值模拟法能客观并详细地描述含水层结构与水文地质条件,适用于各种背景的地下水水源研究.本文以崇州市城区饮用水源为例,采用MODFLOW软件建立地下水渗流场,应用MODPATH对水源地抽水井进行粒子逆向示踪模拟,根据不同的时间标准确定一、二级保护区范围,并结合区域水文地质条件和地标、地界特点确定各级保护区的界线.     

高效破乳菌的培养条件优化及破乳效能研究

从大庆油田受石油污染土壤中分离到1株具有较强破乳能力的莫海威芽孢杆菌(Bacillus mojavensis),其24h破乳率>83%.通过正交试验优化了影响该破乳菌生长及破乳效能的发酵条件;考察了影响其破乳效能的环境因素.结果表明,破乳菌体生长的最佳发酵条件为培养温度25℃、摇床转速160r/min、pH9、接菌量10%、培养时间40h;全培养液破乳的最佳发酵条件为培养温度25℃、摇床转速160r/min、pH5、接菌量6%、培养时间20h;破乳的最佳环境条件为pH5~9,温度30~50℃、全培养液与模型乳状液体积比为1:5.     

一种船舶自修复防腐涂料的制备与表征

以脲醛树脂为囊壁、复合环氧树脂为囊芯,采用原位聚合法成功合成了脲醛树脂包覆环氧树脂体系微胶囊。采用扫描电子显微镜观察微胶囊的表面形貌,测量微胶囊的壁厚;利用红外光谱分析判定微胶囊壁材是否形成,芯材是否被完整包覆。结果表明,应用一步原位聚合法可以制备包覆完整、均匀分散、含有特殊芯材的微胶囊。合成的微胶囊形状基本呈球形,粒径分布均匀,平均粒径约为100μm;胶囊表面粗糙致密,粗糙表面主要是由纳米微胶囊沉积而成。微胶囊表面粗糙度的增加有利于增加微胶囊与基体的接触面积,改善微胶囊与基体的界面粘结力,从而提高自修复材料的修复效率。     

榆树皮提取液絮凝作用的实验研究

研究了榆树皮提取液的絮凝性能,其结果表明Fe3+可以显著地提高榆树皮提取液对硅藻土悬浊液的絮凝活性。当质量浓度10 g/L的榆树皮提取液用量为0.3 mL,质量浓度16 g/L的FeCl3溶液(溶质以FeCl3.6H2O计)加入量为0.7 mL,沉降时间为3 min,pH值为5～11时具有良好的絮凝效果,对模拟废水的絮凝率可达97.2%,低浓度河水86.4%。当榆树皮提取液用量为0.6 mL,FeCl3溶液加入量为1.4 mL时,对高浊度生活污水絮凝率可达92.7%。     

路面不平度时域模型模拟方法研究

路面不平度是引起汽车系统振动的重要激励,路面不平度时域模型是研究公路运输平顺性的基础。本文根据国标GB/T 7031-2005中对路面不平的相关规定,研究讨论了路面不平度时域模型模拟常见的傅里叶逆变换法、谐波叠加法、滤波白噪声方法,对三种方法进行简单对比,并给出相应的实用范围。     

乳状液膜法治理氧化铁氨氮废水的研究

研究了采用液膜分离技术从氧化铁行业生产氨氮废水中处理氨氮的工艺,并通过实际工业废水进行了验证。主要考察了表面活性剂的用量、外水相pH值、内相试剂的选择、油内比、乳水比等因素对氨氮去除率的影响。通过实验结果表明:以3%EA表面活性剂(质量分数),10%内水相硫酸浓度,油内比为2∶1的乳状液膜体系,处理初始浓度为1057mg/L氧化铁行业氨氮废水,在pH值为11.8,乳水比Rew为1∶8的传质条件下,氨氮去除率可达94%以上。     

高压顶空毛细管气相色谱法测定聚合物乳液中的残余单体

介绍测定５种残余单体的顶空分析方法,采用高压顶空进样技术,研究高压顶空的测定条件,方法操作简单、无需对样品进行预处理,线性范围１０＾３－１０＾４,精密度ＲＳＤ〈５％,检出限〈１μｇ／ｇ。     

Spatial distribution of soil heavy metal pollution estimated by different interpolation methods: accuracy and uncertainty analysis

Mapping the spatial distribution of contaminants in soils is the basis of pollution evaluation and risk control. Interpolation methods are extensively applied in the mapping processes to estimate the heavy metal concentrations at unsampled sites. The performances of interpolation methods (inverse distance weighting, local polynomial, ordinary kriging and radial basis functions) were assessed and compared using the root mean square error for cross validation. The results indicated that all interpolation methods provided a high prediction accuracy of the mean concentration of soil heavy metals. However, the classic method based on percentages of polluted samples, gave a pollution area 23.54-41.92% larger than that estimated by interpolation methods. The difference in contaminated area estimation among the four methods reached 6.14%. According to the interpolation results, the spatial uncertainty of polluted areas was mainly located in three types of region: (a) the local maxima concentration region surrounded by low concentration (clean) sites, (b) the local minima concentration region surrounded with highly polluted samples; and (c) the boundaries of the contaminated areas.