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    請使用永久網址來引用或連結此文件: http://ir.lib.ncu.edu.tw/handle/987654321/78024


    題名: 印刷電路板產業濕式製程廢液回收鈀金屬可行性之研究;Study of recovery of palladium from wet Process waste liquid in Printed Circuit Board Industry
    作者: 李建志;LEE, CHIEN-GHIH
    貢獻者: 環境工程研究所在職專班
    關鍵詞: 印刷電路板含鈀廢液;鋅置換;還原劑;回收鈀金屬;硼氫化鈉;二甲基胺硼烷;次磷酸鈉;Palladium Recovery;Palladium Wastewater;Printed Circuit Boards;Zinc Replacement;Reducing Agents;Recycled Palladium Metal;sodium borohydride;Dimethylaminoborane;sodium hypophosphite
    日期: 2018-07-27
    上傳時間: 2018-08-31 15:08:58 (UTC+8)
    出版者: 國立中央大學
    摘要: 印刷電路板製程廢液大部份是含銅廢液,其在高濃度部份因牽涉
    廢棄物清理法及考量產業生產運作成本,大部份高濃度廢液都是委外
    清運及回收,低濃度貴金屬鈀廢液則直接排入廢水廠處理,本研究主
    要目的在於探討以低成本方式將低濃度廢液中之貴金屬鈀進行廠內
    回收。
    研究結果顯示,使用不同種類還原劑對印刷電路板廠之含鈀廢液
    進行還原及回收,以實驗室及實廠操作結果並以藥劑成本、反應時間、
    pH、沉積型態及回收鈀成分多寡為評估條件,其中鋅粉為最佳可行方
    案,本研究五種含鈀廢液中以E 廠回收率最大,推測為COD 值較小,
    溶液中以單純置換反應存在,顯示pH 值範圍1~3.5 為最佳,加藥量
    愈大鈀回收率亦越高,最佳鋅加藥量為6~7 g/l,可得最佳回收率,而
    在錫鈀系統中因錫離子之競爭關係回收率較低,故當廢液中錫、銅愈
    多所犧牲的鋅量亦愈大。以鋅為還原劑回收含鈀廢液,反應速率隨著
    初始濃度的增加而增加,此反應依循Nernst 方程式反應,還原物質初
    始濃度越高化學驅動力(ΔE)越大,在不同反應時間實驗中,顯示三種
    還原劑(鋅、硼氫化鈉、二甲基胺硼烷)在0.5 hr 即達到85%以上之反
    應,而隨時間的增加有回溶現象造成,故以0.5 hr 為最佳反應時間。
    XRD 分析,以A、E 廠之活化鈀廢液並以鋅置換還原法,所得之
    粉末經XRD 分析、比對結果為鈀,再將粉末以王水消化回流後由原
    子吸收光譜儀(AA)測定鈀含量為49.2%及52.7%,為本研究所選定之
    還原劑中最高回收含量。
    經SEM 分析得知,以鋅為還原劑時回收鈀粉粒徑4~10 μm,以
    硼氫化鈉所得粒徑70~100 nm,以次磷酸鈉所得粒徑0.5~2μm,二甲
    基胺硼烷所得粒徑50~70 nm,可見二甲基胺硼烷可得較小的粒徑,
    但以實廠回收鈀金屬的角度來說不利於過濾,使回收率下降,而鋅與
    硼氫化鈉可得到絮凝狀之鈀泥,可增進過濾效率。ASAP 表面孔隙分
    析,顯示以硼氫化鈉為還原劑時可得較大的比表面積與較小的孔隙度,
    雖硼氫化鈉之還原力較強,但若以回收的角度而言仍以鋅粉為較佳。;Most of the wastes from the PCB manufacturing processes are copper-containing waste liquids. Due to the waste cleaning method and the consideration of industrial production operating costs in high-concentration portions most of the high-concentration waste solutions are shipped to contractors and recovered. The low-concentration noble metal palladium waste is directly discharged into the wastewater treatment plant. The main purpose of this study is to explore a cost-effective way to recover the precious metal palladium from the low-concentration waste liquid.

    The results of the study show that the use of different types of reducing agents for the reduction and recovery of palladium-containing wastes from PCBs are based on the laboratory and actual plant operating results with the cost of reagents, reaction time, pH, deposition type, and recycled palladium content. In order to evaluate the conditions, zinc powder is the best feasible solution. In this study, the recoveries of E-plants in the five Pd-bearing waste liquids are the largest. It is estimated that the COD value is small, and the solution only exists as a single substitution reaction, indicating a pH range of 1~ 3.5 is the best.The more dosing the higher the palladium recovery rate. The best dosage of zinc is 6~7 g/l, and the best recovery rate can be obtained. In the tin-palladium system, due to the tin ion competition, the recovery rate is low resulting in more zinc and copper loss in the waste liquid. Recovery of palladium-containing waste liquor with zinc as a reducing agent, the reaction rate increased with the initial concentration. This reaction follows the Nernst equation reaction, the higher the initial concentration of reduced material, the greater the chemical driving force (ΔE). In different reaction time experiments, it shows that the three reducing agents (zinc, sodium borohydride, dimethylamineborane) reach a reaction of more than 85% at 0.5 hr, but it is caused by the back dissolution phenomenon with time. pH 0.5 is the best reaction time.

    XRD analysis is performed on activated palladium wastes of A and E plants and zinc reduction method. The powder is analyzed by XRD and the result of the alignment is palladium. The powder is digested with aqua regia and refluxed and determined by atomic absorption spectrometry (AA). The palladium content is 49.2% and 52.7%, which is the highest recovery content of the reducing agent selected for this study.


    According to SEM analysis, the recoverable palladium particle size is 4-10 μm when zinc is used as a reducing agent. And the particle size is 70-100 nm with sodium borohydride, and the particle size is 0.5-2 μm with sodium hypophosphite, Dimethylaminoborane. The particle size obtained by the alkane is 50~70 nm. It can be seen that the dimethylamine borane can get smaller particle size, but it is not good for the recovery of palladium metal from the actual plant., The recovery rate is reduced, while zinc and sodium borohydride are decreased. Flocculated palladium sludge can be obtained to increase filtration efficiency. ASAP surface pore analysis shows that the specific surface area and the smaller porosity can be obtained with sodium borohydride as a reducing agent. Although the sodium borohydride has a stronger reducing power, it is still a zinc powder if it is better recycled.
    顯示於類別:[環境工程研究所碩士在職專班] 博碩士論文

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