Admixture of maternal metaphases in first trimester direct chromosome preparations?

The autoradiographic labelling of different cell types in chorionic villi and decidual tissue was investigated after [³H]-thymidine incorporation in vitro. Although the extent of labelling was found to be lower in decidual than in villus tissue the possibility that direct chromosome preparations may contain maternal metaphases should be considered. The need for careful selection of villi for direct cytogenetic analysis was stressed.     

论“限期治理”的法律性质

“限期治理”是我国环境保护法的一项基本制度,文章从四个方面详尽地阐述了“限期治理”决定不是一种行政处罚行为,即“限期治理”决定不具有行政处罚的一般特征;“限期治理”决定并并未对行政管理相对人的权利作任何否定;该决定不会影响行政管理相对人固有权利义务的消长;从“环保法”法典的篇章结构安排上和行政行为的性质上分析,“限期治理”决定也不是一种行政处罚行为。正确理解“限期治理”的法律性质,可以避免对企业行     

近岸海域叶绿素和赤潮的AVHRR波段比值探测方法研究

提供了利用NOAAAVHRR的短波波段探测近岸海域叶绿素和赤潮的方法。本方法采用AVHRR的波段1(580～680nm)和波段2(720～1100nm)之间的比值水色因子C21[C21=(R2-Ra2)/(R1-Ra1)],建立了C21与辽东湾海域现场测定的叶绿素a之间的相关关系,相关系数为0.75。叶绿素a的最小探测浓度为2.22mg/m3,探测精度为±4mg/m3,同时也讨论了叶绿素探测的影响因素。     

分散剂及其与胜利原油的混合物对海洋围隔生态系内浮游动、植物的影响

分散剂对某些海洋生物的抑制以及促进初级生产力的现象已为一些研究所证实,而分散剂与原油的混合对生物的影响,由于其污染的增效作用更引起了人们的注意,但上述的研究多见于温带和寒带海域,对于热带、亚热带海域研究尚少。因而,了解污染物对亚热带海域生物区系的影响及地理位置的不同所引起的污染物效应的差别是本研究的中心问题。     

潮汐河口区河汊与干流之间污染物输移过程模拟方法研究

利用一维圣维南水动力方程和二维浅水潮波方程模拟潮汐河口区河汊与干流之间水流衔接冲天 此基础上利用正交曲线坐标系下和直角坐标系下的二维对流扩散方程，并结合拉格郎日水团追踪法，模拟污染物在潮汐河口区河汊与干流之间的输移街接过程。最后论述此方法在珠江口虎门某工厂排污的预测中的应用。     

环境监理工作思路必须转变

拓宽和深化环境监理工作的思路，必须使环境监理由某环节向全过程监理转变，由重点向全方位监理转变，由静态向动态监理转变，由被动向主动监理转变，由劳动密集型向科技型转变，由执法型向执法服务型监理转变，由独立向联合监理转变，由封闭型向开放型监理转变。     

Rate constants for the reaction of hydroxyl radicals with HFC-134a

ＲａｔｅｃｏｎｓｔａｎｔｓｆｏｒｔｈｅｒｅａｃｔｉｏｎｏｆｈｙｄｒｏｘｙｌｒａｄｉｃａｌｓｗｉｔｈＨＦＣ－１３４ａＺｈａｎｇＤｅｑｉａｎｇ，ＺｈｏｎｇＪｉｎｘｉａｎＲｅｓｅａｒｃｈＣｅｎｔｅｒｆｏｒＥｃｏＥｎｖｉｒｏｎｍｅｎｔａｌＳｃｉｅｎｃ...     

Approaches to municipal wastewater irrigation and environmental protection

To reuse the water and nutrient resources from ecological point of view the goals, criteria and constraint conditions of the scientifically municipal wastewater irrigation are discussed as well as the practice in major municipal wastewater irrigation areas in China is introduced, of which particularly the effects of municipal water irrigation mixing with oil refinery wastewater on the agricultural ecosystem are studied and described. It has been revealed that benzo(a)pyrene in various parts of paddy crop is attributed to air pollution, water-soil pollution and biosynthesis of plant. Of exogenous contributions of benzo(a)pyrene in paddy shoot system under natural condition, the dominant factor is the air pollution, whereas the water-soil factor is considered to be secondary. Therefore, it is mostly urgent to control the air pollution source of benzo(a)pyrene, to which the edible parts of various green plants are exposed directly.     

灌溉污水中苯并(a)芘最高容许浓度的探讨

苯并(a)芘是一种强致癌物,在环境和食品中普遍存在,并能在土壤和生物体内蓄积,最高容许浓度的确定应考虑到环境中的“本底”水平和灌溉水中的实际含量以及对机体的毒理危害程度,建议灌溉污水中苯并(a)芘的最高容许浓度为0.05μg/L.     

Studies in the Biodegradation of 5 PAHs (Phenanthrene,Pyrene, Fluoranthene,Chrysene und Benzo(a)pyrene) in the Presence of Rooted Poplar Cuttings

Cuttings of Populus nigra L. cv. Loenen were cultivated in sand treated with one of the following PAHs: phenanthrene (Phen), fluoranthene (Flt), pyrene (Pyr), chrysene (Chr) and benzo[a]pyrene (BaP). The PAHs were applied at varying levels of concentration to each test series. After 6 weeks the concentration and the distribution of the PAHs in the substrate of the various sets of tests were compared with the concentration in the substrate of the control. Additionally the substrate and the plant roots were tested for evidence of degradation products of PAHs. The results revealed that the levels of concentration of Phen and Pyr detected in the substrate surrounding the roots was in some cases significantly lower than in the corresponding section of substrate in the unplanted set (= control). This phenomenon did not occur for Flt and BaP and in the case of Chr only in those substrates, which had been treated with the highest levels of concentration. As the presence of lesser amounts of Phen and Pyr in the plant pots cannot only be attributed to their accumulation and metabolism in the roots, it is fair to assume that the chemical transformation of these three PAHs took place outside the roots. The set of tests treated with Phen revealed the presence of 2- or 3-hydroxy-Phen (main components), a hydroxy-methoxy-Phen, 9,10-Phenanthrenequinone and one unidentified compound in metabolite form. Altogether eleven metabolites of Pyr were identified in the root extracts, which can be divided into three groups: 1-Hydroxy-Pyr and derivatives, dihydroxy-Pyr and derivatives and ring fission products (4-Hydroxy-Pyr and a derivative of the 4-Phen-carbonic acid). However, the metabolite mass detected for Phen and Pyr represents only an insignificant percentage in comparison with the lesser amounts of PAHs observed in the planted set of tests. This indicates that the three PAHs were reduced to lower molecular compounds, which are methodically impossible to record, and subsequently translocated to other parts of the plant and integrated into the biomass. Although no lesser amount for Flt and BaP was found in the plant pots, 1-Hydroxy-Flt, an unidentified compound of Flt and 1-Methoxy-BaP were detected. These are presumably end products which were enhanced in the roots. It was not possible to identify any transformation products of Chr. It can be assumed that the majority of metabolites were not synthesised in the roots but are a result of microbial degradation in the rhizosphere. The test plants improved the conditions for the biotransformation of Phen and Pyr significantly and accumulated Flt, Pyr, Chr and BaP in their roots. It can therefore be concluded that the use of plants in the bioremediation of contaminated soils is a promising option.