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利用含铜蚀刻废液生产碱式碳酸铜 总被引:14,自引:0,他引:14
介绍了利用含铜蚀刻废液生产碱式碳酸铜的生产工艺、技术特点、工艺流程和产品质量。以碳酸钠作蚀刻废液的除杂剂,对其进行除杂前处理,控制反应液的pH为3.5~4.0、反应液中碳酸钠的浓度为0.02~0.03mol/L。可除去其中大部分杂质。用碳酸钠与含铜溶液中的铜进行合成反应,控制反应温度为70~80℃、pH为8~9、碳酸钠和含铜溶液中铜的浓度均为1mol/L,反应生成碱式碳酸铜,此产品中铜的质量分数为56%,产品质量优于木材防腐用碱式碳酸铜国内外同类产品。 相似文献
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开发出一种以甘蔗渣为原料用水解-氧化-水解法制取草酸的工艺。最佳反应条件:硫酸浓度为70%(质量分数),物料浸泡时间为3h,硝酸与甘蔗渣质量比为2.24:1,氧化一水解反应时间为5h,反应温度为65~70℃。在这种条件下制得的草酸二水合物的收率可达80%左右。 相似文献
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用硝酸浸取铜钨合金废料中的铜,再用亚硫酸钠还原硝酸铜制备氧化亚铜。采用X射线衍射仪对氧化亚铜进行表征,考察了氧化亚铜产品对溶液中甲基橙的光催化效果,并与分析纯五水硫酸铜制备的氧化亚铜进行了对比。实验结果表明:在硝酸浓度为5.6 mol/L,硝酸用量为2.5 m L/g(为理论用量的1.5倍),浸取温度为40℃,浸取时间为6 h的最优浸取条件下,铜浸取率稳定在87%以上;在还原反应温度为80℃、还原反应时间为4h、硝酸铜浓度为0.8 mol/L的条件下,可制备得到较高纯度的氧化亚铜;在甲基橙质量浓度为20 mg/L、氧化亚铜加入量为2 g/L,500 W氙灯照射时间为2.5 h的条件下进行光催化反应,甲基橙降解率可达93%以上。与分析纯五水硫酸铜制备的氧化亚铜相比,两者形貌相似、光催化效果基本相当。 相似文献
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次氯酸钙法处理发泡剂生产废水 总被引:6,自引:0,他引:6
采用废漂白液(次氯酸钙)处理发泡剂偶氮二甲酰胺生产废水。废水pH为8~9时,加入质量分数3%~5%的漂白液和1‰PAM絮凝剂,反应2h,沉淀澄清。实验室试验中COD去除率为88%,工业处理试验中COD平均由626mg/L降为105mg/L,去除率为83.2%。该法工艺简单,以废治废,费用低,处理效果好。 相似文献
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短程硝化-铁炭微电解工艺处理焦化废水 总被引:7,自引:2,他引:5
以废刚玉石墨粉末和废铁屑作为电极,分别采用铁炭微电解工艺和短程硝化一铁炭微电解工艺对焦化废水进行脱氮处理。实验结果表明,采用短程硝化一铁炭微电解工艺对焦化废水脱氮效果好于只采用铁炭微电解工艺。铁炭微电解的最佳反应条件:废水初始pH为3.0,反应时间为70min,铁炭质量比[m(Fe):m(C)]为1.0:1.3,混凝pH为9.0。在此最佳反应条件下,铁炭微电解工艺TN去除率为8.0%,短程硝化一铁炭微电解工艺NO2--N的去除率为57.0%,TN的去除率为50.0%。 相似文献
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Emission of metals in the urbanenvironment is a growing concern throughout theworld. In order to identify metal emissionssources in the Stockholm metropolitan region, amethod for detailed mapping of roof coatings andother urban land covers has been developedconducted. High accuracy area calculation ofcopper roof coatings based on scanned aerialphotography was used. The geometric resolution ofthe digital photographs was 0.4 metre. Imagelayers with identified copper roof objects weremerged with a digital elevation model of 1 metregeometric resolution. The slope gradient for eachroof was calculated in order to account for slopein the calculation of roof areas. In total,622,590 m2 of copper roofs were accounted,of which 176,845 m2 and 447,745 m2represent new and patinated copper respectively.The number of copper roofs larger than 1,000m2 was 142. Applying corrosion and runoffrates on these figures, a yearly Cu flux ofapproximately 1,200 kg in Stockholm may bederived from copper coated building. 相似文献
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用Na_2CO_3催化焙烧法将CuS转化为Cu。最佳的转化条件;反应温度为750℃,CuS:Na_2CO_3(摩尔比)为1:2,在空气中反应90min。CuS的转化率可达到99%。 相似文献
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采用热解—氨浸工艺处理含铜废催化剂(w(Cu)为23.6%),优化了工艺条件,并通过蒸氨还原法制备出Cu2O产品。实验结果表明:热解工段中,控制管式热解炉的空气流量为3.0 m3/min,在升温速率20 ℃/min、热解终温600 ℃、终温保持时间90 min的优化条件下,含铜废催化剂中的有机物热解完全;氨浸工段中,以NH4Cl-NH3-H2O溶液为氨浸液,控制氨浸温度为40 ℃,在烧成料研磨时间90 min(粒径29.43 μm)、氨浸液总氨浓度4 mol/L、氨浸时间80 min的优化条件下,铜浸出率达到98%;经蒸氨还原法制得的Cu2O产品的质量符合HG/T 2961—2010《工业氧化亚铜》中的一等品标准,产率为24%。 相似文献
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以湖北省某化工企业含砷废水处理过程中产生的含硫化砷废渣为研究对象,采用氧化碱浸—沉淀工艺制备砷酸铜。考察了沉淀反应液pH、沉淀反应温度、搅拌转速对砷沉淀效果的影响。采用XRD和SEM技术对砷酸铜的物相及形貌进行了表征。实验结果表明:废渣在氧化碱浸过程的砷浸出率为96.53%;沉淀反应时间为30 min时,沉淀步骤的最佳工艺条件为沉淀反应液pH 5.0、搅拌转速500 r/min、沉淀反应温度50 ℃。验证实验结果表明,在该工艺条件下,砷沉淀率均达93.96%以上。SEM表征结果显示,砷酸铜产品为颗粒状,粒径约为500 nm。XRD表征结果显示,砷酸铜产品中主要含有Cu3As2O8,Cu4O(AsO4)2,Cu4(As2O7)O2。该方法工艺简单、无二次污染,为废渣的综合利用提供了一种新的技术路线。 相似文献
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Recently there has been anincreased environmental concern in severalcountries in Europe, in particular in Sweden andin the Netherlands regarding the amount of copperand zinc that is released from building materialsinto society. Due to lack of runoff data, thelegislators have so far used corrosion ratesmeasured during the last 20 years to calculatequantities of metal released from buildingsassuming that the quantity of metal corrosionequals the quantity of metal runoff. Withdecreasing levels of environmental pollutantsduring the last decade in Europe, it is importantto determine more recent and hence morerepresentative corrosion and runoff rates to beused in the calculations. For this reason a field exposure program was implemented during 48 weeks in an urbanatmosphere in Sweden determining corrosion andrunoff rates for copper and zinc of differentage. New copper exposed for 48 weeks in the urbanatmosphere shows a corrosion rate of 6.7gm-2y-1 and an almost constant runoff rate of1.3 gm-2y-1 during the period. Therunoff rate is significantly lower than thecorrosion rate and represents only a fraction(20%) of the total amount of corroded metalduring this period. Zinc shows a graduallydecreasing corrosion rate with time being 5.0gm-2y-1 after 48 weeks of exposure. Therunoff rate is relatively stable with an averagerate of 3.1 gm-2y-1 during the sameperiod. This value represents 60% of the totalamount of corroded zinc. The effect of panel age has been investigatedin parallel field and laboratory studies. Theresults show that naturally aged copper exhibitssomewhat higher average runoff rates (2 gm-2y-1) than new copper, probably due to acombined effect of storage and weatherconditions. No significant difference in runoffrate can be found between new and naturally agedzinc. The field and laboratory investigationsshow that precipitation rate and amount influence the magnitude of the runoff rate forboth copper and zinc. 相似文献