热镀锌板表面钝化时的磷化工艺

热镀锌板表面钝化（铬酸盐钝化），主要是为了防止在使用过程中其表面被氧化。由于表面的钝化膜的存在。使得磷化工艺无法进行，从而影响涂装后涂层的附着力（铬酸盐钝化膜不如磷化膜附着性好）和耐蚀性能（铬离子不耐氯离子的腐蚀）。为了提高热镀锌板表面钝化后其表面的涂装性能，开发出一种适合上述条件的磷化工艺。     

SO2在碳钢初期大气腐蚀中的作用

通过自建的模拟大气腐蚀系统,借助金相显微镜、扫描电镜(SEM/EDX)、X-射线衍射(XRD)和x-射线光电子能谱(XPS),研究了SO2对碳钢初期大气腐蚀行为的影响,并进一步用原子力显微镜从更微观的角度观察了在SO2环境中初期阶段腐蚀形貌变化.研究结果表明:在SO2污染大气环境中,随SO2浓度的升高碳钢腐蚀加快.在体积分数为5×10(-6)SO2的大气环境中,碳钢和耐候钢表面腐蚀主要以条状物生长,随着SO2浓度的升高,腐蚀产物的形貌发生改变,在体积分数为5×10(-5)SO2的大气环境中,条状锈和胞状锈同时生长.在锈层中S元素以FeSO4·4H2O的形式存在,腐蚀产物中还有γ-FeOOH.SO2在初期阶段加速了碳钢的腐蚀,降低了碳钢的耐蚀性.     

考虑环空压力的生产套管CO2腐蚀速率预测

目的 预测考虑环空压力条件下不同产量、温度变化碳钢套管的腐蚀速率.方法 利用优化的经典半经验模型对碳钢套管的腐蚀速率进行预测.明确海洋环境碳钢套管CO2腐蚀的机理,找出海水中生产套管发生腐蚀的主要影响因素及腐蚀机理,通过CO2溶解度模型优化腐蚀速率预测模型,考虑温度、环空压力、产量等变化对腐蚀的影响规律,预测生产套管的腐蚀速率.结果 计算了产量变化后环空的压力分布,产量越大,环空压力相对越大,但产量增大到一定值后,环空压力的增加不再明显.产量会影响环空的温度分布,而温度的变化又关系着热膨胀压力,影响套管的腐蚀速率.通过高温高压室内腐蚀实验验证了腐蚀预测模型的可靠性,对比实验结果 ,模型的预测误差在10％以内,满足现场腐蚀预测需要.结论 产量、温度、CO2溶解度、环空压力等因素均对腐蚀有较大影响,考虑环空压力变化条件下生产套管总体的腐蚀速率远超NACE标准中度腐蚀的0.125 mm/a,需要采取一定的缓蚀措施.     

多孔氧化铝层制备的研究

采用预腐蚀与交流腐蚀相结合的方法．研究了多孔氧化铝层的制备工艺．探讨了制备工艺中各步骤的作用以及影响因素。利用扫描电镜，研究了多孔氧化铝层制备工艺对铝箔微观形貌的影响。研究表明．交流腐蚀工艺对铝箔表面微观形貌的改变作用最明显。一次后处理后铝箔表面蚀孔变密．氧化膜的结构更加疏松细腻。二次后处理，调整和热处理等步骤对铝箔表面的微观形貌影响不大。     

硝酸盐对铝合金点蚀行为的影响

采用动电位极化测量技术研究在一定氯离子存在下硝酸盐对 LY12CZ硬铝合金点蚀发生、发展行为的影响。试验认为,硝酸盐在 浓度较低时没有钝化作用,使铝合金电位从钝化区向活化区过渡,但 它使再钝化电位提高,在一定的钝化条件下,可促进氧化膜的修复; 当硝酸盐浓度大于某一数值时,铝的点蚀电位明显增加,能有效抑制 点蚀发生。这一值的大小与介质中存在的氯离子含量有关。     

2A12铝合金在模拟溶液中的周浸腐蚀行为

采用干湿周浸实验、失重法和电化学阻抗谱研究了2A12铝合金在0.6mol/L NaCl和0.6mol/L NaCl 0.02mol/L NaHSO3两种溶液中的腐蚀行为与规律, 利用扫描电镜(SEM)、能谱(EDX)和红外光谱(FTIR) 观察分析腐蚀产物表面形貌、结构和组成,测试了材料的力学性能.研究表明,随腐蚀时间的延长,腐蚀产物不断增多,失重增加,力学性能下降,阻抗模值逐渐减小;腐蚀产物形貌以团状和块状为主,在0.6mol/L NaCl溶液中腐蚀产物主要为铝的氯化物和氧化铝,在0.6mol/L NaCl 0.02mol/L NaHSO3溶液中腐蚀产物主要为氧化铝、铝的硫酸盐水合物和铝的氯化物;由于NaCl和NaHSO3共同作用,2A12合金在0.6mol/L NaCl 0.02mol/L NaHSO3溶液中腐蚀电流密度高,阻抗模值相对较小,腐蚀速率较高,腐蚀后失重大,力学性能下降幅度较大,腐蚀更严重.     

浅谈地表水透明度监测结果与现场光线的关系

在实际工作中我们发现现场光线影响塞氏盘透明度测定结果，本文对透明度与现场光线的关系进行了探讨，并提出了建议。     

城市地铁暗挖施工地层变形机理及控制实践

笔者结合深圳地铁一期工程的某些暗挖标段工程及地质条件 ,在土层性质试验研究的基础上 ,深入分析了地层大变形机理及其主要影响因素 ,由此确定了地层大变形控制的原则和技术措施。在施工中 ,应用地层变形控制原则及相应的综合技术措施后 ,使地层变形大幅度降低 ,满足了地表环境保护的要求 ,取得了预期的效果     

SIMULATING THE IMPACT OF DRAINAGE DESIGN IN A COLD CLIMATE WITH ADAPT1

ABSTRACT: Surface and subsurface drainage make crop production economically viable in much of southern Minnesota because drainage allows timely field operations and protects field crops from extended periods of flooded soil conditions. However, subsurface drainage has been shown to increase nitrate/nitrogen losses to receiving waters. When engaging in drainage activities, farmers are increasingly being asked to consider, apart from the economic profit, the environmental impact of drainage. The Agricultural Drainage and Pesticide Transport model (ADAPT) was used in this study to evaluate the impact of subsurface drainage design on the soil water balance over a two‐year period during which observed drainage discharge data were available. Twelve modeling scenarios incorporated four drainage coefficients (DC), 0.64 cm/d, 0.95 cm/d, 1.27 cm/d, and 1.91 cm/d, and three drain depths, 0.84 m, 1.15 m, and 1.45 m. The baseline condition corresponded to the drainage system specifications at the field site: a drain depth and spacing of 1.45 m and 28 m, respectively (DC of 0.64 cm/d). The results of the two‐year simulation suggested that for a given drainage coefficient, soils with the shallower drains (but equal DC) generally have less subsurface drainage and can produce more runoff (but reduced total discharge) and evapotranspiration. The results also suggested that it may be possible to design for both water/nitrate/nitrogen reduction and crop water needs.     

Occurrence of benzotriazoles (BTRs) in indoor air from Albany,New York,USA, and its implications for inhalation exposure

Despite the widespread use of benzotriazoles as corrosion inhibitors in many household goods, studies on the occurrence of these compounds in indoor air are scarce. In this study, five benzotriazole derivatives were measured in 83 indoor air samples collected from various locations in Albany, New York, USA. Benzotriazoles were found in a majority of the indoor air samples, and the concentrations of their sum in bulk (vapor plus particulate phases) indoor air ranged from below the method limit of quantification to 492 ng·m^?3 (geometric mean: 5.8 ng·m^?3). The highest geometric mean concentration was found in air samples collected in parking garages (155 ng·m^?3), followed by barbershops (13.6), public places (11.5), auto repair shops (5.2), automobiles (4.5), homes (4.5), offices (3.7), and laboratories (2.8). Inhalation exposure to benzotriazoles was calculated on the basis of the measured geometric mean concentrations and air inhalation rate. The highest exposure dose was found for teenagers, with a geometric mean inhalation exposure dose of 79 ng·day^?1. The body-weight normalized exposure dose, however, was the highest for infants, at 3.2 ng·(kg bw)^?1·day^?1.