二氧化硫与1—己烯的光化学反应动力学

利用ＧＣ／ＭＳ方法研究了ＳＯ２与１－己烯在无氧和有氧体系中光化学反应动力学，确定了ＳＯ２与１－己烯光化学反应的级数，给出了２９３－３３３Ｋ温度范围内总的反应速度常数Ｋ，以及Ｋ与温度的关系、反应的活化能和指前因子。另外，对反应物己醛和２－己酮的生成反应速度常数及其活化能也进行了计算和讨论。     

城市煤气化综合效益实例分析

本文以煤气化工程的典型实例分析为基础，通过对气源厂经济效益的分析，提出了以气化替煤量和节煤量两项指标，进行宏观经济效益、社会效益和环境效益的综合效益分析的步骤及相应的计算公式与方法。     

转sck单价基因和cry1Ac/sck双价基因水稻对二化螟的致死效应及中肠组织病理变化观察

室内采用离体叶片法研究了转sck单价基因抗虫水稻86AS1和转cry1Ac/sck双价基因抗虫水稻MSB不同生育期主茎顶叶对二化螟幼虫的杀虫效果.结果发现,不同生育期的MSB对二化螟初孵幼虫表现出了很强的毒杀效果,二化螟幼虫校正死亡率在扬花期前均达到90%以上;扬花期和灌浆期抗虫性有所下降,校正死亡率高于80%;成熟期校正死亡率在60%以上.在整个生育期,二化螟幼虫取食86AS1主茎顶叶的校正死亡率均未超过50%.MSB对二化螟幼虫的毒杀效果明显高于86AS1.采用透射电镜观察二化螟幼虫取食转cry1Ac/sck双价基因抗虫水稻和转sck单价基因抗虫水稻主茎顶叶后中肠组织的病理变化.结果发现,两种转基因水稻都能够引起二化螟幼虫中肠组织发生病理变化,但病变程度有明显差异.二化螟幼虫取食转cry1Ac/sck双价基因抗虫水稻3d,中肠组织受到严重破坏且病理变化明显;取食转sck单价基因抗虫水稻3d,幼虫中肠组织的病理变化却较缓慢.图2参10     

不同碳源条件下草菇内切型纤维素酶基因（eg1）转录表达的分析

利用Northernblot方法分析了不同碳源条件下草菇切型纤维素酶基因(eg1)的表达.结果发现,在含有纤维素的液体培养基中生长10d,eg1在草菇菌丝中有高效表达;纤维二糖、α-乳糖、β-乳糖,也能诱导eg1的表达,但和纤维素相比,eg1的表达量相对较低,并且它们的诱导效应在加入这类糖12h后迅速减弱;槐糖和龙胆二糖的诱导作用非常弱.在天然稻草为基质的固体栽培料生长时,草菇eg1的表达和草菇菌丝生长与出菇相对应,在菌丝生长期(d8)可见eg1的表达,d12时菌丝已长满,表达减弱,在出菇及菇体的分化及增大期,eg1的表达量逐渐增强,在成熟期达到最高水平;表明在草菇菇体发育中需要更多碳源及能源的补充,eg1在这方面起着非常重要的作用.图4参14     

应用HYDRUS-1D模型模拟农田土壤水渗漏及硝态氮淋失特征

在定位试验基础上,应用HYDRUS-1D模型对黄淮海平原典型土壤(黄潮土)中土壤水渗漏及硝态氮淋失动态进行了模拟分析。结果表明:在传统水氮管理模式下,黄潮土2m土体深处的土壤水渗漏和硝态氮淋失非常严重,2个轮作期内,土壤水渗漏总量占地表总入水量的23.7%,硝态氮淋失总量占总输入N量的15.9%,冬小麦生长季的硝态氮淋失量大于夏玉米生长季;改良灌溉和改良施肥模式下产生的硝态氮淋失量比传统灌溉和传统施肥模式减少74.7%,节约灌溉水211.5mm、节省施N423.5kg·hm-2。     

假单胞菌XD-1(Pseuomonas XD-1)的产表面活性剂性能研究

从含油废水中分离到1株表面活性剂产生菌,经鉴定为假单胞菌(Pseuomonassp.),命名为XD 1.对假单胞菌XD 1的产表面活性剂性能进行研究,实验结果表明,在正交优化的培养基中发酵培养时,菌XD 1可将培养液的表面张力从70 0mN·m-1降至30 2mN·m-1,其产表面活性剂方式为生长相关型;经提取分析,菌XD 1所产表面活性剂为脂肽类和糖脂类物质的混合物,脂肽类物质为主要成分;菌XD 1所产表面活性剂的CMC值为50mg·L-1,在pH=6 0时表面活性剂表现出最佳活性;菌XD 1所产表面活性剂主要积累在胞内特定的细胞器中,并在细胞壁上产生一层粘附的表面活性剂膜,膜厚140nm,在生长过程中,菌体会将细胞器和细胞壁上的表面活性剂释放到胞外.将培养72h的菌体浸入双蒸水中,6h后菌体能把积累在细胞器和细胞壁上的表面活性剂释放到水体中.     

物理化学法治理印染废水的研究

本文提出了两个治理印染废水的综合物化流程:(1)SE—J型絮凝剂絮凝→气浮→次氯酸钙氧化→炉渣吸附;(2)SE—型絮凝剂絮凝→气浮→活性炭吸附,并对每个处理过程进行了条件实验。实验结果表明:废水经流程(1)处理后,COD去除率达82—87%,色度去除率达88—92%,废水经流程(2)处理后,COD去除率达89—92%,色度去除率达97—98%。经两个流程处理后的出水水质分别接近或达到国家排放标准。     

合肥台CTS-1分析系统网络组建

本文阐述了利用UNIX和WIN98/2000互联的局域网技术,对CTS-1系统进行优化配置,组建CTS-1网络分析系统,实现CTS-1系统数据共享,提高地震分析的效率,确保数据备份。利用代理软件用一个MODEM让各个子机同时上网,同时充分利用台站现有的计算机设备,最大限度的实现地震监控、速报、分析以及地震研究的同时开展。     

Two-site kinetic modeling of bacteriophages transport through columns of saturated dune sand

Breakthrough curves, on a semi-log scale, from tests in porous media with block-input of viruses, bacteria, protozoa and colloidal particles often exhibit a typical skewness: a rather slowly rising limb and a smooth transition of a declining limb to a very long tail. One-site kinetic models fail to fit the rising and declining limbs together with the tail satisfactorily. Inclusion of an equilibrium adsorption site does not seem to improve simulation results. This was encountered in the simulation of breakthrough curves from a recent field study on the removal of bacteriophages MS2 and PRD1 by passage through dune sand. In the present study, results of laboratory experiments for the study of this issue are presented. Breakthrough curves of salt and bacteriophages MS2, PRDI, and phiX174 in 1 D column experiments have been measured. One- and two-site kinetic models have been applied to fit and predict breakthrough curves from column experiments. The two-site model fitted all breakthrough curves very satisfactorily, accounting for the skewness of the rising limb as well as for the smooth transition of the declining limb to the tail of the breakthrough curve. The one-site model does not follow the curvature of the breakthrough tail, leading to an overestimation of the inactivation rate coefficient for attached viruses. Interaction with kinetic site 1 is characterized by relatively fast attachment and slow detachment, whereas attachment to and detachment from kinetic site 2 is fast. Inactivation of viruses and interaction with kinetic site 2 provide only a minor contribution to removal. Virus removal is mainly determined by the attachment to site 1. Bacteriophage phiX174 attached more than MS2 and PRD1, which can be explained by the greater electrostatic repulsion that MS2 and PRD1 experience compared to the less negatively charged phiX174.     

Environmental occurrence of Q1, a C9H3C17N2 compound,that has been identified as a natural bioaccumulative organochlorine

Environmental appearance of Q1, a natural heptachloro compound with the molecular formula C₉H₃Cl₇N₂, was studied in samples from different sites all over the world. Q1 was expected to have a bipyrrole backbone, similar to other compounds ascribed to natural sources. A method for isolation of Q1 was developed by combination of adsorption chromatography on silica and normal phase HPLC with an amino phase. UV-detection of Q1 supports the aromatic character of the compound.

The high levels detected in samples of marine mammals and birds suggested that Q1 is both a persistent and a bioaccumulative contaminant. This was underscored by calculated log K_OW in the range of other lipophilic organohalogens. In accordance with earlier studies, highest Q1 concentrations were found in the Southern Hemisphere, but with a highly selective GC/ECNI-MS-SIM method, detection of Q1 was also achieved in many samples from the Northern Hemisphere. In addition to marine mammals and birds, Q1 was also detected in fish from the Mediterranean Sea and the Antarctic. Traces were also detected in SRM 1588 certified cod liver oil, but Q1 was not detected in fish from Hong Kong and Lake Baikal.