Environmental and sustainability indicators and the concept of situational indicators. A systems approach

Through a systems approach indicators are shown to have the nature of variables, adopting different values or states, while other associated terms allude to special meanings assigned to specific values of the indicators. Practical implications are discussed. The concept of situational indicators of sustainability is introduced, representing a non-numerical function of both “pressures” or “driving forces” and “state” variables. A cost-effective multi-tiered approach to situational indicators is proposed. The concept of situational indicators is shown to be a particular case of indicators of systems behavior. A general systems formulation of the problem of sustainability highlights the importance of indicators of systems behavior and the central role of models in their definition.     

多介质环境目标值的应用

本文概述了多介质目标德的SAM/Ⅰ的方法。多介质目标值包括环境目标值和排放目标值。点源分析包括SAM/ⅠA,SAM/ⅠB,SAM/Ⅰ,SAM/Ⅱ。在缺少环境质量标准的情况下,使用多介质环境目标值有较强的适用性,且具有省时、省力、经济等特点。本文将多介质目标值的SAM/ⅠA点源分析方法引入聚氯乙烯生产废水的环境评价中,取得较为满意的结果。     

Determination of arsenic in grain and soil by hydride nondispersive atomic fluorescence method

Quantity of trace arsenic in grain and soil was determined by hydride nondispersive atomic fluorescence method.Optimum conditions of measurement were selected in the experiment including the pH of the medium, reductive agent, the concentration and flowing velocity of KBH4, rate of carrier gas and atomized temperature. The reference sample of rice C was determined and the linear relationship of the calibration curve was plotted, indicating that the method was highly precise. In the experiment of recovery rate, the method was quite satisfactory.Based on the determination of hundreds of samples, it is proved that atomic fluorescence method is rapid, sensitive and low in interference. It is very efficient on determination of trace arsenic in soils and grains, especially in grains.     

Non-random nectar unloading interactions between foragers and their receivers in the honeybee hive

Nectar acquisition in the honeybee Apis mellifera is a partitioned task in which foragers gather nectar and bring it to the hive, where nest mates unload via trophallaxis (i.e. mouth-to-mouth transfer) the collected food for further storage. Because forager mates exploit different feeding places simultaneously, this study addresses the question of whether nectar unloading interactions between foragers and hive-bees are established randomly, as it is commonly assumed. Two groups of foragers were trained to exploit a different scented food source for 5 days. We recorded their trophallaxes with hive-mates, marking the latter ones according to the forager group they were unloading. We found non-random probabilities for the occurrence of trophallaxes between experimental foragers and hive-bees, instead, we found that trophallactic interactions were more likely to involve groups of individuals which had formerly interacted orally. We propose that olfactory cues present in the transferred nectar promoted the observed bias, and we discuss this bias in the context of the organization of nectar acquisition: a partitioned task carried out in a decentralized insect society.     

天津地区大气污染状况和气溶胶硫酸盐的研究

我们于1980—1981年对天津市大气污染物浓度做了同步监测,对天津市大气污染状况,二氧化硫转化为硫酸盐的过程及其对大气能见度的影响做了研究。以超C_i几率和的方法处理数据,研究结果表明,大气污染以早晨最严重,傍晚次之,中午较轻:冬季比夏季污染严重。各种污染物中以硫酸盐对大气能见度的影响最大,总颗粒物次之。当大气相对湿度大于70%时,对大气能见度的影响比较突出。颗粒物中的苯溶物对大气能见度有一定的影响。城市中相对湿度高时硫酸盐浓度大,可能是产生冬季烟雾事件的原因。下风方向的硫酸根浓度与二氧化硫浓度的比值和硫酸根含硫浓度与大气总硫浓度的比值均比上风方向相应的数值高,说明城市燃煤烟气是硫酸盐的来源。城市中硫酸根浓度与二氧化硫浓度的相关系数为0.77,硫酸根与颗粒物浓度的相关系数为0.95。在形成硫酸根的过程中二氧化硫浓度和颗粒物可能有贡献。以一维有源简化模式估算二氧化硫转化为硫酸根的速率常数,约为2.3±1.1%/hr,冬季约1.5%/hr。二氧化硫的迁移距离约为17—340km。     

Technological system for sustainable development of Chinese agriculture

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螯合纤维的合成及其吸附重金属离子的研究

研究了含有胺肟基和胺腙基功能纤维的合成、结构表征和螯合性能。新型合纤维对多种重金属离子具有良好的吸附性能，能从被污染的水体和土壤中去除重金属离子，经洗脱后可回收金属，螯合纤维能反复使用。     

层控矿床的成岩成矿

本文从成岩分异,成岩交代,自生、脱水、泄水、压实、挤压、扩散和胶结作用等方面,论述层控矿床的成岩成矿作用。     

中国旅游资源分区的初步研究

本文是在8000个旅游资源实体数据的基础上,对旅游资源的区域特征和旅游环境的区域差异性进行定性和定量分析。形成了一个三级分区体系并得到一张中国旅游资源分区图。第一级区,有八个资源区。第二级区,有41个资源区。在每个二级区内有或多或少的三级区,然而,每个三级区必须是根据旅游资源数量、质量和交通条件得出的五类三级区中的某一类。分区程序采用从低级区向高级区归并的方式。本结果对管理旅游资源和发展中国旅游业有重要参考价值。