Bioavailability to grains of rice of aged and fresh DDD and DDE in soils

DDT had been widely used around the world before 1980s and is still under production and use for non-agricultural purposes in China. Because of their special physicochemical properties, p,p'-DDT and its main metabolites, p,p'-DDD and p,p'-DDE, accumulated and persisted in the environment, presenting potential menace on biota. A green-house study was conducted to determine the bioavailability of p,p'-DDD and p,p'-DDE to grains of rice and the influences of traditional Chinese farming practices on their bioaccumulation. Paddy rice and dry rice were grown in submerged paddy soils and non-submerged upland soils, respectively. Two types of soil, Hydragric Anthrosols (An) and Hydragric Acrisols (Ac), were employed. Bioaccumulation factors (BAFs) of DDE ranged from 0.67 for rice grown in non-submerged An to 0.84 in submerged An in the control group, whilst BAFs were all below 0.04 in experimental groups. BAFs of DDD varied from 1.39 for submerged An to 2.26 for submerged Ac in original soils. In contrast, BAFs were between 0.05 for non-submerged Ac and 0.08 for submerged An in DDD-contaminated soils. Flooding seemed to have two contradictory effects on the DDE/DDD accumulation by rice: on one hand, it made the pollutants more mobile and bioavailable; while on the other hand, it enhanced the degradation and binding of POPs. Adding rice straw to the soils protected DDE from being taken up yet promoted DDD accumulation by rice. Furthermore, the distinct inorganic component of the soils might also play an important role in the environmental activities of POPs.     

Characteristics of real-world vehicular emissions in Chinese cities

On-board emission measurements were performed on 49 light-duty gasoline vehicles in seven cities of China. Vehicle-specific power mode distribution and emission characteristics were analyzed based on the data collected. The results of our study show that there were significant differences in different types of roads. The emission factors and fuel consumption rates on arterial roads and residential roads were approximately 1.4-2 times those on freeways. The carbon monoxide, hydrocarbon, and nitrogen oxides emission factors of Euro II vehicles were on average 86.2, 88.2, and 64.5% lower than those of carburetor vehicles, respectively. The new vehicle emission standards implemented in China had played an important role in reducing individual vehicle emissions. More comprehensive measures need to be considered to reduce the total amount of emissions from vehicles.     

利用耗散结构中的熵变计算探讨城镇生态系统的发展方向

判断城镇生态系统的发展方向通常用系统的产值或利润 ,这不能全面地表达城镇生态系统的的物质流、能量流、信息流、人口流以及货币流对系统的作用。文章从城镇生态系统的本质出发 ,利用耗散结构理论 ,探讨了城镇生态系统的熵变计算公式 ,并将它应用到大丰市和锡山市 ,所得结论与实际基本相符。因此 ,建议将熵变作为城镇生态系统的一个综合参数加以利用。     

成都市城市环境与经济协调发展分析

从城市环境与经济发展的协调度方面分析了成都市１９９０－１９９７年间协调度的变化趋势,评估了成都市城市环境与经济协调发展的类型,得出了成都市属于总体协调发展类环境滞后型的结论。     

家庭生活用水与室内氡浓度研究与进展

文章论述了家庭生活水的氡浓度水平、生活用水对室内氡的贡献、水的使用过程中室内氡行为以及含氡水的使用与辐射照射剂量的关系等问题。指出家庭生活水的氡浓度高时,是室内氡的一个不可忽视的来源。对氡浓度特别高的家庭用水,建议先用活性炭等进行吸附后再使用。     

钝顶螺旋藻突变株FBL的生理特性

利用倍频Ｎｄ：ＹＡＧ激光（λ＝５３２ｎｍ,ｐ＝５００ｍＷ,Ｓ＝１６０ｍＷ／ｃｍ＾２）对钝顶螺旋藻进行诱变处理,辐照１０ｍｉｎ,经分离获得藻丝开矿变成直形的钝顶螺旋突变株ＦＢＬ。对该变株ＦＢＬ的生长特性、藻多糖、氨基酸、β－胡萝卜素、叶绿素ａ等生化组成的研究。结果表明：与出发株相比,突变株ＦＢＬ生长速度加快;β－胡萝卜素含量提高２２．３％;藻多糖提高４２．０％;氨基酸增幅５．２％,氨基酸的组成比例发     

雀形目八种鸟核型的比较研究

采用空气干燥法制备骨髓细胞染色体标本 ,报道了雀形目 5科 8种鸟的核型 ,其中八色鸫科为世界首次报道核型的科 .比较研究表明 :臂间倒位和小染色体缺失在所描述类群的染色体进化中起着重要作用 .图版 2表 6参 15     

汽爆麦草固态发酵木质素酶

木质素是地球上主要的可再生芳香族化合物 ,是地球上仅次于纤维素的第二丰富可再生天然资源 ,然而 ,对它的利用研究却很少 ,是天然高分子中未开发的领城[1] .80年代初发现了木质素过氧化物酶 (ＬｉＰ) [2 ,3] 和锰过氧化物酶 (ＭｎＰ) [4 ] 以后 ,木质素酶和木质素生物降解研究取得了一定进展 .但木质素微生物转化降解研究中仍存在许多问题 .( 1)由于木质素酶解是一种非专一性的、以自由基为基础的链反应过程[5] .因此 ,木质素酶在化学工业、煤化学和环境保护方面具有很大的开发前景 .而现在木质素酶的生产大多用合成培养基 ,必需添加昂贵的…     

谷氨酰胺转胺酶(MTG)分批发酵中温度对S.mobaraense生长及产酶影响的模型化

研究了2.5L小罐培养过程中控制温度为25℃～35℃时对细胞生长和MTG合成的影响.结果表明当控制相对较低的温度时,细胞生长的延滞期较长,当控制温度较高时,细胞生长的延滞期较短,达到最大DCW和最高MTG酶活的时间均较短;通过研究各种不同模型对细胞生长的影响得到最适合描述S.mobaraense生长与温度之间的关系方程为Schoolfield方程;通过对最大DCW和最大MTG酶活进行数学模拟,发现方程X(U)=-a     

生态恢复过程中的种群遗传学考虑

生态恢复是生态科学的最终实验,从种群角度看,恢复的目标是使种群（尤其是优势种或建群种）到具有生长、繁殖和适应进化变化的能力。要达到这个目标,种群遗传学知识必不可少。遗传变异是物种适应变化环境的基础,而局部适应则是种群适应局部环境遗传分化的结果,它们在生态恢复中起着重要的作用。分析了生态恢复过程中影响种群遗传变异因素,主要有取样误差和小种群效应（主要是瓶颈或建立者事件及其以后的近交和漂变等）,在进行