稻田环境与除草剂去草胺降解速率的关系

在稻田自然环境中,去草胺乳油和颗粒剂的残留半衰期,在田水中分别为1.65—2.84d和5.78—6.30d,在土壤中分别为2.67—5.33d和4.95—6.30d.经过水稻一个生育期,去草胺在糙米等样品中的最终残留量均降至可检水平以下.土壤微生物对去草胺的降解起着主导性的作用,在灭菌和不灭菌土壤中的残留半衰期分别为433d和18.50—29.40d.去草胶在涂土等四类不同属性的土壤中的渗漏性大小顺序,依次为涂土、小粉土、青紫泥和红壤.     

环境-经济系统双向控制模型的辨识

运用系统模型的辨识方法,讨论了环境-经济系统双向控制模型的辨识问题,重点探讨了这类模型体系中的最优控制模型,其途径是采用大系统建模思想.即在对大系统结构分析基础上,通过分解把整体建模转化为易于处理的子系统建模,再通过建立关联模型,得到整体模型,并进一步简化和进行参数辨识.     

土壤中砷的原子荧光法测定

将土壤粉末均匀稳定地悬浮于0.15％～0.2％琼脂溶胶中,采用悬浮样品直接进样,氢化物发生—非色散原子荧光法,测定其砷含量。以柠檬酸—NaOH缓冲液控制试样pH4.7,测定As~(3+);以HCl、KI和抗坏血酸还原As~(5+)为As~(3+),测定总砷量;用差减法求得As~(5+)含量。方法应用于测定不同类型土壤时,相对标准偏差为1％～6％,回收率为85％～106％。     

造纸废水综合治理技术的应用研究

采用“酸化 物化 生化”组合工艺并辅以芦苇湿地处理系统对造纸废水进行综合治理。通过优化工艺条件 ,逐级削减污染负荷 ,使废水排放达到国家标准     

城市草坪的生态热效益

分析了草坪的能量平衡机理以及与环境之间的热湿交换关系，说明了草坪对空气具有降温增湿作用。通过重庆市区一些草坪实测数据分析发现草坪日平衡温度与空气日平均温度相等，说明草坪与空气之间保持热量的生态平衡。     

论突发地质事件与形成胶莱盆地金矿关系

中生代后期 ,太平洋板块的俯冲作用使胶南地体拉分 ,断陷形成胶莱盆地。这一突发地质事件在盆地底部地势低洼部位形成局限水体 ,接受周围古老地层风化剥蚀产物的沉积而形成富含有机质、富金的莱阳群一段含矿岩系。此突发地质事件晚期的进一步改造成矿作用导致在含矿岩系不同岩性中形成不同类型的金矿床     

秦岭若干重要类型金矿床(体)快速定位预测

本文以西部秦岭地区八卦庙、双王、煎茶岭 3种重要类型金矿床为例 ,在成矿地质背景研究基础上 ,开展若干新方法新技术的找矿试验 ,研究发现 ,八卦庙式金矿岩石的烃含量与其金品位大致成正相关关系 ;而且金矿化强度和规模越大 ,相关系数值也越大 ;据此根据石英脉的烃含量对隐伏金矿床 (体 )和金矿化规模进行预测。双王式金矿原生晕的前缘晕元素为B、As、Sb、Hg,近矿晕元素为Au、Ba(-) ,尾晕元素为Mn、Bi。通过原生叠加晕垂向研究预测 ,双王和八卦庙金矿床现有的金矿体向下延伸还较大 ,在矿床的深部存在有盲矿体。煎茶岭式金矿的矿石铅同位素平均值比围岩要小 ,铅同位素曲线的低峰区往往就指示矿体所在 ;预测区的2 0 6Pb/ 2 0 4 Pb、2 0 8Pb/ 2 0 4 Pb比值变差椭圆图的形状和轴向斜率与已知矿区趋于一致 ,并且两者的变差椭圆图形大部分重叠 ,说明存在有同类型金矿体。以上研究成果为同期或后来的勘探工作或矿山采矿所验证。     

Occurrence and behaviour of nonylphenol and octylphenol in Nanming River, Guiyang City, China

Occurrence, variation and behaviour of nonylphenol (NP) and octylphenol (OP) were studied in surface water and groundwater in Guiyang, Guizhou Province, southwestern China. Discharge of wastewater from Guiyang City was the main source of alkylphenols (APs) entering the aquatic environment. The concentrations of NP and OP in river water ranged from 40 to 1582 ng L(-1) and from below the lowest limit of detection (LOD) to 67 ng L(-1), respectively. NP and OP were also detected in groundwater. Both NP and OP exhibited spatial and temporal variations in river water and groundwater. It was found that concentrations of NP and OP in river water was low upstream and dramatically increased downstream, and higher concentration of NP was found in winter compared to that in summer. Proportions of NP and OP were trapped by suspended particulate matter (SPM), which accounted for 7.6-50.0% and 3.4-25.6% of their total concentration in the river water system, respectively. Seasonal changes in water flow were responsible for the temporal variations of APs. To determine the behaviour of APs along the river, a mass balance equation based on chloride was used. The results showed that a mixing process was the predominant factor to determine upstream APs concentrations; while the discharge of wastewater controlled the concentrations of APs downstream. Considering the adverse effect of APs on organisms, combined effect modeling was used to assess the toxicity to fish. It was found that the predicted mixture effect for APs in river water on fish vitellogenin induction was low upstream and medium downstream, respectively.     

Spectrophotometric determination of persulfate by oxidative decolorization of azo dyes for wastewater treatment

Persulfate can efficiently decolorize azo dyes through oxidizing these compounds, which enabled us to develop a method of rapid spectrophotometric determination of persulfate for monitoring the wastewater treatment on the basis of the oxidation decolorization of azo dyes. Four azo dyes with different molecular structures were investigated as probes, and the influences of operation parameters including reaction time, solution pH, initial dye concentration, and initial concentration of activator Fe(2+) were checked on the determination of persulfate. Under optimum conditions, the decolorization degree of the dyes responded linearly with persulfate concentration for all the four azo dyes, and the linear range and detection limit were found to be 2.0-150 μmol L(-1) and 0.62 μmol L(-1) for rhodamine B, 2.0-100 μmol L(-1) and 0.42 μmol L(-1) for methylene blue, 4.0-150 μmol L(-1) and 0.50 μmol L(-1) for methyl violet, and 20-150 μmol L(-1) and 8.1 μmol L(-1) for orange II. A persulfate treatment of a spiked wastewater sample was satisfactorily monitored with the new method.