TW201628975A - Recovery system and method for underwater heavy metals - Google Patents

Recovery system and method for underwater heavy metals Download PDF

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TW201628975A
TW201628975A TW104104078A TW104104078A TW201628975A TW 201628975 A TW201628975 A TW 201628975A TW 104104078 A TW104104078 A TW 104104078A TW 104104078 A TW104104078 A TW 104104078A TW 201628975 A TW201628975 A TW 201628975A
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heavy metal
cation exchange
exchange resin
module
tank
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TW104104078A
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Chinese (zh)
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TWI589534B (en
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ming-zhi Liao
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ming-zhi Liao
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Abstract

A recovery system for heavy metals in water comprises a first heavy metal removal module, a second heavy metal removal module, a heavy metal recovery module, a wastewater tank, and a recovery solution tank. The first heavy metal removal module is connected, via pipelines, respectively to the wastewater tank and the heavy metal recovery module, and the first heavy metal removal module has at least one cation exchange resin and a first drain pipeline. The second heavy metal removal module is connected, via pipelines, to the wastewater tank and the heavy metal recovery module respectively, and the second heavy metal removal module has at least one cation exchange resin and a second drain pipeline. The heavy metal recovery module is connected, via pipelines, to the wastewater tank and the recovery solution tank respectively, and the heavy metal recovery module has at least one cation exchange resin.

Description

水中重金屬回收系統及回收方法Heavy metal recovery system and recovery method in water

本發明係關於水中重金屬回收系統及回收方法,特別是有關於一種可以使廢水中的重金屬完全與陽離子交換樹脂結合,而排放釋出的廢水中重金屬含量可低於排放標準,且可得到高濃度重金屬回收液的回收系統及回收方法。The invention relates to a heavy metal recovery system and a recovery method in water, in particular to a method capable of completely combining heavy metals in waste water with a cation exchange resin, and the heavy metal content in the discharged wastewater can be lower than the discharge standard, and a high concentration can be obtained. Recovery system and recovery method for heavy metal recovery liquid.

印刷電路板與半導體製造產業的製程中會產生大量且高濃度含重金屬的廢液,這些廢液若處置不當,將會造成嚴重的環境污染。再者,近年來由於環保意識的抬頭,各國政府對於含重金屬的工業廢水的排放標準日趨嚴格,因此,如何有效地將水中的重金屬分離,確保排放之廢水中重金屬含量低於排放標準,乃是產業界所關注的問題之一。In the manufacturing process of the printed circuit board and the semiconductor manufacturing industry, a large amount of high-concentration waste liquid containing heavy metals is generated, and if this waste liquid is improperly disposed, it will cause serious environmental pollution. Furthermore, in recent years, due to the rise of environmental awareness, governments have increasingly stricter standards for the discharge of industrial wastewater containing heavy metals. Therefore, how to effectively separate heavy metals from water to ensure that the content of heavy metals in discharged wastewater is lower than the discharge standard is One of the concerns of the industry.

除了確保處理過的廢水低於排放標準之外,現今對於含重金屬廢水的處理已朝向回收重金屬的方向發展,不僅可以解決工業廢水處理的問題,亦可將回收之重金屬進一步製成高價值的奈米微粒,達到資源回收的目的。In addition to ensuring that treated wastewater is below emission standards, today's treatment of heavy metal-containing wastewater has moved toward the recovery of heavy metals, which not only solves the problem of industrial wastewater treatment, but also further processes the recovered heavy metals into high-value Rice particles, for the purpose of recycling resources.

電解法是習用最常見的重金屬離子回收方法,該方法係利用直流電將廢水中的重金屬離子沉積在陰極上再加以回收;然而,當廢水中的重金屬離子濃度過低時,電解回收重金屬的效率會大幅降低,而增加回收成本。因此,在電解含重金屬的廢水之前,先以陽離子交換樹脂處理,使廢水中的重金屬先與陽離子交換樹脂結合,而處理後之廢水的水質亦可低於排放標準而被排出或回收再利用;接著,再以陰離子再生劑流洗該陽離子交換樹脂,使重金屬離子脫離該陽離子交換樹脂,陽離子交換樹脂可再利用,而脫離之重金屬離子則進行電解回收。Electrolysis is the most common method for recovering heavy metal ions. It uses DC electricity to deposit heavy metal ions in wastewater on the cathode and recover it. However, when the concentration of heavy metal ions in wastewater is too low, the efficiency of electrolytic recovery of heavy metals will be Significantly reduce and increase recycling costs. Therefore, before electrolyzing the wastewater containing heavy metals, the cation exchange resin is first treated to combine the heavy metals in the wastewater with the cation exchange resin, and the treated water can be discharged or recycled after being discharged below the discharge standard; Next, the cation exchange resin is further washed with an anion regenerant to remove heavy metal ions from the cation exchange resin, and the cation exchange resin can be reused, and the separated heavy metal ions are electrolyzed and recovered.

習用之水中重金屬回收系統1如圖一所示,為增加回收效率,由第一陽離子交換樹脂11與第二陽離子交換樹脂12輪流處理廢水;含重金屬的廢水首先自廢水槽13流入該第一陽離子交換樹脂11進行處理,使廢水中的重金屬先與該第一陽離子交換樹脂11結合,處理後的水則由排水槽14排出,當該第一陽離子交換樹脂11接近飽和時,將廢水槽13中的廢水管線切換至第二陽離子交換樹脂12繼續進行處理,而此時以陰離子再生劑流洗該第一陽離子交換樹脂11,使重金屬脫離該第一陽離子交換樹脂11,該第一陽離子交換樹脂11可再重複使用,而脫離之重金屬則收集至回收液槽15,以待進行電解回收;當該第二陽離子交換樹脂12接近飽和時,將廢水槽13中的廢水管線切換至該第一陽離子交換樹脂11繼續進行處理,而此時以陰離子再生劑流洗該第二陽離子交換樹脂12,使重金屬脫離該第二陽離子交換樹脂12,該第二陽離子交換樹脂12可再重複使用,而脫離之重金屬則收集至回收液槽15,以待進行電解回收。In the conventional heavy metal recovery system 1 shown in FIG. 1, in order to increase the recovery efficiency, the first cation exchange resin 11 and the second cation exchange resin 12 are used to treat the wastewater in turn; the heavy metal-containing wastewater first flows from the wastewater tank 13 into the first cation. The exchange resin 11 is treated so that the heavy metal in the wastewater is first combined with the first cation exchange resin 11, and the treated water is discharged from the drain tank 14, and when the first cation exchange resin 11 is nearly saturated, the waste water tank 13 is The waste water line is switched to the second cation exchange resin 12 to continue the treatment, and at this time, the first cation exchange resin 11 is washed with an anion regenerant to remove the heavy metal from the first cation exchange resin 11, the first cation exchange resin 11 It can be reused, and the separated heavy metal is collected into the recovery liquid tank 15 to be subjected to electrolytic recovery; when the second cation exchange resin 12 is nearly saturated, the waste water line in the wastewater tank 13 is switched to the first cation exchange The resin 11 is further processed, and at this time, the second cation exchange resin 12 is washed with an anion regenerant to make heavy metals From the second cation exchange resin 12, the second cation exchange resin 12 may be reused, while the heavy metals from the collector to the recovery tank 15 is to be subjected to electrolytic recovery.

由此可知,習用之水中重金屬回收系統中,各陽離子交換樹脂皆負責清除廢水中的重金屬,使廢水低於排放標準,而分離的重金屬即直接進行回收再利用。然而,處理後廢水是否低於排放標準與陽離子交換樹脂的吸附飽和度有關,越接近飽和時,處理後廢水無法低於排放標準的風險越高;為了確保處理後廢水可低於排放標準,於陽離子交換樹脂尚未達到飽和狀態時便切換管路,停止處理含重金屬廢水,而以陰離子再生劑進行再生,但因為該陽離子交換樹脂所結合之重金屬含量低,再生處理後回收液中的重金屬的濃度低,會使得後續電解回收的效率大幅降低。因此,何時該切換陽離子交換樹脂的管線,以確保處理後廢水可低於排放標準,且回收的重金屬濃度不至於太低,乃是習用水中重金屬回收系統所面臨的困難點,而亟需被改良之處。It can be seen that in the conventional heavy metal recovery system in water, each cation exchange resin is responsible for removing heavy metals in the wastewater, so that the wastewater is lower than the discharge standard, and the separated heavy metals are directly recycled and reused. However, whether the treated wastewater is lower than the discharge standard is related to the adsorption saturation of the cation exchange resin. The closer to saturation, the higher the risk that the treated wastewater cannot be lower than the discharge standard; in order to ensure that the treated wastewater can be lower than the discharge standard, When the cation exchange resin has not reached saturation state, the pipeline is switched, the heavy metal-containing wastewater is stopped, and the regeneration is carried out with an anion regenerant. However, because the cation exchange resin is combined with a low heavy metal content, the concentration of heavy metals in the recovered liquid after the regeneration treatment is stopped. Low, will greatly reduce the efficiency of subsequent electrolytic recovery. Therefore, when to switch the pipeline of the cation exchange resin to ensure that the treated wastewater can be lower than the discharge standard, and the concentration of the recovered heavy metal is not too low, it is a difficult point faced by the heavy metal recovery system in the water, and it is urgent to be Improvements.

為解決上述問題,本發明之主要目的在於提供一種水中重金屬回收系統,藉由增設一重金屬回收模組,而將陽離子交換樹脂的清除水中重金屬功能與回收重金屬功能分開,負責清除水中重金屬功能的重金屬清除模組可在陽離子交換樹脂尚未達到飽和前進行再生,以確保廢水中的重金屬完全與陽離子交換樹脂結合,而排放釋出的廢水中重金屬含量低於排放標準,符合規定而不會對環境造成污染。In order to solve the above problems, the main object of the present invention is to provide a heavy metal recovery system in water. By adding a heavy metal recovery module, the function of removing heavy metal from the cation exchange resin in the water is separated from the function of recovering heavy metals, and is responsible for removing heavy metals in the water. The cleaning module can be regenerated before the cation exchange resin has reached saturation, to ensure that the heavy metals in the wastewater are completely combined with the cation exchange resin, and the discharged heavy metal content is lower than the emission standard, which is in compliance with regulations and does not cause environmental damage. Pollution.

本發明之次一目的在於提供一種水中重金屬回收系統,該系統具有一個以上之重金屬清除模組與一重金屬回收模組,該重金屬回收模組可集中收集由該重金屬清除模組分離而來的重金屬,待該重金屬回收模組中的陽離子交換樹脂之重金屬吸附達完全飽和時再進行再生,以得到高濃度重金屬回收液,而可提高後續重金屬電解回收之效率。A second object of the present invention is to provide a heavy metal recovery system in water, which has more than one heavy metal removal module and a heavy metal recovery module, and the heavy metal recovery module can collectively collect heavy metals separated by the heavy metal removal module. When the heavy metal adsorption of the cation exchange resin in the heavy metal recovery module reaches full saturation, the regeneration is performed to obtain a high concentration heavy metal recovery liquid, thereby improving the efficiency of subsequent heavy metal electrolytic recovery.

本發明於第一方面揭示一種水中重金屬回收系統,包含:一第一重金屬清除模組、一第二重金屬清除模組、一重金屬回收模組、一廢水槽,以及一回收液槽;且該第一重金屬清除模組分別與該廢水槽以及該重金屬回收模組以管路連接,且該第一重金屬清除模組具有至少一個陽離子交換樹脂以及一第一排水管路;該第二重金屬清除模組分別與該廢水槽以及該重金屬回收模組以管路連接,且該第二重金屬清除模組具有至少一個陽離子交換樹脂以及一第二排水管路;以及該重金屬回收模組分別與該第一重金屬清除模組、該第二重金屬清除模組、該廢水槽、以及該回收液槽以管路連接,且該重金屬回收模組具有至少一個陽離子交換樹脂。 【00010】  於一較佳實施例中,該水中重金屬回收系統進一步具有一排水槽,該第一排水管路係連接該第一重金屬清除模組與該排水槽,且該第二排水管路係連接該第二重金屬清除模組與該排水槽。 【00011】  於一較佳實施例中,該重金屬回收模組與該廢水槽之間連接的重金屬回收模組-廢水槽管路上設有一取樣點。 【00012】  本發明於第二方面揭示一種水中重金屬回收方法,包含: 提供一如申請專利範圍第1項所述之水中重金屬回收系統; 將水自該回收系統的廢水槽流至該回收系統的第一重金屬清除模組進行處理,使水中的重金屬與該第一重金屬清除模組中的陽離子交換樹脂結合,處理後的水由該第一排水管路排出; 在該第一重金屬清除模組中的陽離子交換樹脂尚未飽和時,將該廢水槽中的廢水管線切換至該回收系統的第二重金屬清除模組進行處理,使水中的重金屬與該第二重金屬清除模組中的陽離子交換樹脂結合,處理後的水由該第二排水管路排出; 以陰離子再生劑流洗該第一重金屬清除模組中的陽離子交換樹脂,使重金屬脫離該第一重金屬清除模組中的陽離子交換樹脂,該第一重金屬清除模組中的陽離子交換樹脂可重複使用,並將脫離之重金屬流洗至該重金屬回收模組,使脫離之重金屬與該重金屬回收模組中的陽離子交換樹脂結合; 在該第二重金屬清除模組中的陽離子交換樹脂尚未接近飽和時,將該廢水槽中的廢水管線切換至該第一重金屬清除模組進行處理,並以陰離子再生劑流洗該第二重金屬清除模組中的陽離子交換樹脂,使重金屬脫離該第二重金屬清除模組中的陽離子交換樹脂,該第二重金屬清除模組中的陽離子交換樹脂可再重複使用,並將脫離之重金屬流洗至該重金屬回收模組,使脫離之重金屬與該重金屬回收模組中的陽離子交換樹脂結合;以及 將通過該重金屬回收模組的流洗液經由該重金屬回收模組-廢水槽管路輸入至該廢水槽,當該重金屬回收模組中的陽離子交換樹脂吸附達到飽和時,以陰離子再生劑流洗該重金屬回收模組中的陽離子交換樹脂,使重金屬脫離該重金屬回收模組中的陽離子交換樹脂,並將脫離之重金屬收集至該回收系統的回收液槽,得到高濃度重金屬回收液。 【00013】  於一較佳實施例中,該重金屬回收模組中的陽離子交換樹脂吸附飽和度係透過該重金屬回收模組-廢水槽管路上的取樣點取樣分析流洗液中的重金屬含量而決定。 【00014】  本發明於第三方面揭示一種水中重金屬回收系統,包含:一第一陽離子交換樹脂、一第二陽離子交換樹脂、一第三陽離子交換樹脂、一重金屬回收模組、一廢水槽、一排水槽,以及一回收液槽;且該第一陽離子交換樹脂、該第二陽離子交換樹脂、該第三陽離子交換樹脂分別以管路互相串聯,且該第一陽離子交換樹脂、該第二陽離子交換樹脂、該第三陽離子交換樹脂各自分別與該重金屬回收模組、該廢水槽以及該排水槽以管路連接;以及該重金屬回收模組係為一第四陽離子交換樹脂,且該重金屬回收模組並分別與該廢水槽以及該回收液槽以管路連接。 【00015】  於一較佳實施例中,該重金屬回收模組與該廢水槽之間連接的重金屬回收模組-廢水槽管路上設有一取樣點。 【00016】  本發明於第四方面揭示一種水中重金屬回收方法,包含: 提供一如申請專利範圍第6項所述之水中重金屬回收系統; 將水自該回收系統的廢水槽流至該第一陽離子交換樹脂進行處理,使水中的重金屬與該第一陽離子交換樹脂結合,處理後的水接著流入該第二陽離子交換樹脂進行處理,使水中殘餘的重金屬與該第二陽離子交換樹脂結合,並將處理後的水經由該排水槽3排出; 在該第一陽離子交換樹脂尚未接近飽和時,將該廢水槽中的廢水管線切換至該第二陽離子交換樹脂進行處理,使水中的重金屬與該第二陽離子交換樹脂結合,處理後的水接著流入該第三陽離子交換樹脂進行處理,使水中殘餘的重金屬與該第三陽離子交換樹脂結合,並將處理後的水經由該排水槽排出,並以陰離子再生劑流洗該第一陽離子交換樹脂,使重金屬脫離該第一陽離子交換樹脂,該第一陽離子交換樹脂可再重複使用,而將脫離之重金屬流洗至該重金屬回收模組,使脫離之重金屬與該第四陽離子交換樹脂結合,並將通過該第四陽離子交換樹脂的流洗液經由該重金屬回收模組-廢水槽管路輸入至該廢水槽; 在該第二陽離子交換樹脂尚未接近飽和時,將該廢水槽中的廢水管線切換至該第三陽離子交換樹脂進行處理,使水中的重金屬與該第三陽離子交換樹脂結合,處理後的水接著流入該再生的第一陽離子交換樹脂進行處理,使水中殘餘的重金屬與該第一陽離子交換樹脂結合,並將處理後的水經由該排水槽排出,並以陰離子再生劑流洗該第二陽離子交換樹脂,使重金屬脫離該第二陽離子交換樹脂,該第二陽離子交換樹脂可再重複使用,而將脫離之重金屬流洗至該重金屬回收模組,使脫離之重金屬與該第四陽離子交換樹脂結合,並將通過該第四陽離子交換樹脂的流洗液經由該重金屬回收模組-廢水槽管路輸入至該廢水槽; 在該第三陽離子交換樹脂尚未接近飽和時,將該廢水槽中的廢水管線切換至該第一陽離子交換樹脂進行處理,使水中的重金屬與該第一陽離子交換樹脂結合,處理後的水接著流入該再生的第二陽離子交換樹脂進行處理,使水中殘餘的重金屬與該第二陽離子交換樹脂結合,並將處理後的水經由該排水槽排出,並以陰離子再生劑流洗該第三陽離子交換樹脂,使重金屬脫離該第三陽離子交換樹脂,該第三陽離子交換樹脂可再重複使用,而將脫離之重金屬流洗至該重金屬回收模組,使脫離之重金屬與該第四陽離子交換樹脂結合,並將通過該第四陽離子交換樹脂的流洗液經由該重金屬回收模組-廢水槽管路輸入至該廢水槽; 當該第四陽離子交換樹脂吸附達到飽和時,以陰離子再生劑流洗該第四陽離子交換樹脂,使重金屬脫離該第四陽離子交換樹脂,並將脫離之重金屬收集至該回收系統的回收液槽,得到高濃度重金屬回收液。 【00017】  於一較佳實施例中,該第四陽離子交換樹脂吸附飽和度係透過該重金屬回收模組-廢水槽管路上的取樣點取樣分析流洗液中的重金屬含量而決定。The first aspect of the invention discloses a heavy metal recovery system for water, comprising: a first heavy metal removal module, a second heavy metal removal module, a heavy metal recovery module, a wastewater tank, and a recovery liquid tank; a heavy metal removal module is respectively connected to the wastewater tank and the heavy metal recovery module by a pipeline, and the first heavy metal removal module has at least one cation exchange resin and a first drainage pipeline; the second heavy metal removal module Separating the wastewater tank and the heavy metal recovery module with a pipeline, and the second heavy metal removal module has at least one cation exchange resin and a second drainage pipeline; and the heavy metal recovery module and the first heavy metal The cleaning module, the second heavy metal removal module, the waste water tank, and the recovery liquid tank are connected by a pipeline, and the heavy metal recovery module has at least one cation exchange resin. [00010] In a preferred embodiment, the underwater heavy metal recovery system further has a drain tank connected to the first heavy metal removal module and the drain tank, and the second drain line system Connecting the second heavy metal removal module to the drain groove. [00011] In a preferred embodiment, a sampling point is disposed on the heavy metal recovery module-wastewater tank line connecting the heavy metal recovery module and the wastewater tank. [0001] The present invention discloses a method for recovering heavy metals in water, comprising: providing a heavy metal recovery system in water as described in claim 1; flowing water from the wastewater tank of the recovery system to the recovery system The first heavy metal removal module is processed to combine the heavy metal in the water with the cation exchange resin in the first heavy metal removal module, and the treated water is discharged from the first drainage pipeline; in the first heavy metal removal module When the cation exchange resin is not saturated, the waste water line in the waste water tank is switched to the second heavy metal removal module of the recovery system for treatment, so that the heavy metal in the water is combined with the cation exchange resin in the second heavy metal removal module. The treated water is discharged from the second drain line; the cation exchange resin in the first heavy metal removal module is washed by an anion regenerant to remove the heavy metal from the cation exchange resin in the first heavy metal removal module, The cation exchange resin in a heavy metal removal module can be reused and the detached heavy metal stream is washed until The heavy metal recovery module combines the detached heavy metal with the cation exchange resin in the heavy metal recovery module; when the cation exchange resin in the second heavy metal removal module is not near saturation, the waste water line in the wastewater tank is switched Processing to the first heavy metal removal module, and washing the cation exchange resin in the second heavy metal removal module with an anionic regenerant to remove heavy metals from the cation exchange resin in the second heavy metal removal module, the second The cation exchange resin in the heavy metal removal module can be reused, and the detached heavy metal is washed to the heavy metal recovery module to combine the detached heavy metal with the cation exchange resin in the heavy metal recovery module; and the heavy metal will pass through The flow washing liquid of the recovery module is input to the waste water tank through the heavy metal recovery module-waste water tank line, and when the cation exchange resin in the heavy metal recovery module is saturated, the heavy metal recovery mold is washed by an anion regenerant. a cation exchange resin in the group to remove heavy metals from the heavy metal recovery module Cation exchange resin, and collection tank to the recovery of heavy metals from the recovery system to obtain a high concentration of heavy metals recovery solution. [00013] In a preferred embodiment, the cation exchange resin adsorption saturation in the heavy metal recovery module is determined by sampling the sampling point on the heavy metal recovery module-wastewater tank line to analyze the heavy metal content in the flow washing liquid. . [00014] The third aspect of the invention discloses a heavy metal recovery system for water, comprising: a first cation exchange resin, a second cation exchange resin, a third cation exchange resin, a heavy metal recovery module, a wastewater tank, and a a drain tank, and a recovery liquid tank; and the first cation exchange resin, the second cation exchange resin, and the third cation exchange resin are connected in series with each other, and the first cation exchange resin and the second cation exchange The resin and the third cation exchange resin are respectively connected to the heavy metal recovery module, the wastewater tank and the drainage tank by a pipeline; and the heavy metal recovery module is a fourth cation exchange resin, and the heavy metal recovery module And respectively connected to the wastewater tank and the recovery liquid tank by a pipeline. [00015] In a preferred embodiment, a sampling point is disposed on the heavy metal recovery module-wastewater tank line connecting the heavy metal recovery module and the wastewater tank. [00016] In a fourth aspect, the invention discloses a method for recovering heavy metals in water, comprising: providing a heavy metal recovery system in water as described in claim 6; flowing water from the wastewater tank of the recovery system to the first cation The exchange resin is treated to combine heavy metals in the water with the first cation exchange resin, and the treated water is then flowed into the second cation exchange resin for treatment, and the residual heavy metal in the water is combined with the second cation exchange resin and treated. The water after the drain is discharged through the drain tank 3; when the first cation exchange resin is not near saturation, the waste water line in the waste water tank is switched to the second cation exchange resin for treatment to make the heavy metal in the water and the second cation The exchange resin is combined, and the treated water is then flowed into the third cation exchange resin for treatment, the residual heavy metal in the water is combined with the third cation exchange resin, and the treated water is discharged through the drainage tank, and an anionic regenerant is used. Flowing the first cation exchange resin to remove the heavy metal from the first cation a sub-exchange resin, the first cation exchange resin can be reused, and the detached heavy metal stream is washed to the heavy metal recovery module, the detached heavy metal is combined with the fourth cation exchange resin, and the fourth cation exchange is performed. a flow washing liquid of the resin is input to the waste water tank via the heavy metal recovery module-waste water tank line; and when the second cation exchange resin is not near saturation, the waste water line in the waste water tank is switched to the third cation exchange resin Processing, combining heavy metal in water with the third cation exchange resin, and the treated water is then flowed into the regenerated first cation exchange resin for treatment, and the residual heavy metal in the water is combined with the first cation exchange resin, and treated The water after the drain is discharged through the drain tank, and the second cation exchange resin is washed by an anion regenerant to remove the heavy metal from the second cation exchange resin, and the second cation exchange resin can be reused, and the heavy metal stream to be detached Washing the heavy metal recovery module to remove the heavy metal from the fourth cation exchange tree Binding, and the flow washing liquid passing through the fourth cation exchange resin is input to the wastewater tank through the heavy metal recovery module-waste water tank line; when the third cation exchange resin is not near saturation, the waste water tank is in the waste water tank The waste water line is switched to the first cation exchange resin for treatment, the heavy metal in the water is combined with the first cation exchange resin, and the treated water is then flowed into the regenerated second cation exchange resin for treatment to make residual heavy metals in the water The second cation exchange resin is combined, and the treated water is discharged through the drainage tank, and the third cation exchange resin is washed by an anion regenerant to remove the heavy metal from the third cation exchange resin, and the third cation exchange resin may be Repeatedly, the detached heavy metal is washed to the heavy metal recovery module, the detached heavy metal is combined with the fourth cation exchange resin, and the flow washing liquid passing through the fourth cation exchange resin is passed through the heavy metal recovery module. - a waste water tank line is input to the waste water tank; when the fourth cation exchange resin is adsorbed And when the anion regenerant stream to the fourth washing the cation exchange resin, the heavy metal from the fourth cation exchange resin, and collection tank to the recovery of heavy metals from the recovery system to obtain a high concentration of heavy metals recovery solution. [00017] In a preferred embodiment, the fourth cation exchange resin adsorption saturation is determined by sampling the sample points on the heavy metal recovery module-wastewater tank line to analyze the heavy metal content in the flow wash.

【00021】  以下將配合所附圖示詳細說明本發明之實施例,然而應注意的是,該些圖示均為簡化之示意圖,僅以示意方法來說明本發明之基本架構或實施方法,故僅顯示與本案有關之元件與組合關係,圖中所顯示之元件並非以實際實施之數目、形狀、尺寸做等比例繪製,某些尺寸比例與其他相關尺寸比例或已誇張或是簡化處理,以提供更清楚的描述。實際實施之數目、形狀及尺寸比例為一種選置性之設計,詳細之元件佈局可能更為複雜。 【00022】  根據本發明之第一實施例,一種水中重金屬回收系統舉例說明如圖二之架構示意圖所示。本發明之水中重金屬回收系統2包含一第一重金屬清除模組21、一第二重金屬清除模組22、一重金屬回收模組23、一廢水槽24、一排水槽25,以及一回收液槽26。該第一重金屬清除模組21分別與該廢水槽24以及該重金屬回收模組23以管路連接,且該第一重金屬清除模組21具有至少一個陽離子交換樹脂以及一第一排水管路211,該第一排水管路211係連接該第一重金屬清除模組21與該排水槽25。該第二重金屬清除模組22分別與該廢水槽24以及該重金屬回收模組23以管路連接,且該第二重金屬清除模組22具有至少一個陽離子交換樹脂以及一第二排水管路221,該第二排水管路221係連接該第二重金屬清除模組22與該排水槽25。該重金屬回收模組23分別與該第一重金屬清除模組21、該第二重金屬清除模組22、該廢水槽24、以及該回收液槽26以管路連接,且該重金屬回收模組23具有至少一個陽離子交換樹脂。該重金屬回收模組23與該廢水槽24之間連接的重金屬回收模組-廢水槽管路231上設有一取樣點232。 【00023】  請繼續參閱圖二,本發明之第一實施例的水中重金屬回收方法為:含重金屬的廢水首先自廢水槽24流入該第一重金屬清除模組21進行處理,使廢水中的重金屬與該第一重金屬清除模組21中的陽離子交換樹脂結合,處理後的水則由該第一排水管路211排出;於一固定時間後,當該第一重金屬清除模組21中的陽離子交換樹脂尚未接近飽和時(例如,僅達到40%~60%的飽和度),將該廢水槽24中的廢水管線切換至第二重金屬清除模組22進行處理,使廢水中的重金屬與該第二重金屬清除模組22中的陽離子交換樹脂結合,處理後的水則由該第二排水管路221排出;此時並以陰離子再生劑流洗該第一重金屬清除模組21中的陽離子交換樹脂,使重金屬脫離該第一重金屬清除模組21中的陽離子交換樹脂,該第一重金屬清除模組21中的陽離子交換樹脂可再重複使用;而脫離之重金屬則流洗至該重金屬回收模組23,使脫離之重金屬與該重金屬回收模組23中的陽離子交換樹脂結合;於一固定時間後,當該第二重金屬清除模組22中的陽離子交換樹脂尚未接近飽和時(例如,僅達到40%~60%的飽和度),將該廢水槽24中的廢水管線再次切換至該第一重金屬清除模組21進行處理,而此時以陰離子再生劑流洗該第二重金屬清除模組22中的陽離子交換樹脂,使重金屬脫離該第二重金屬清除模組22中的陽離子交換樹脂,該第二重金屬清除模組22中的陽離子交換樹脂可再重複使用;而脫離之重金屬則流洗至該重金屬回收模組23,使脫離之重金屬與該重金屬回收模組23中的陽離子交換樹脂結合;通過該重金屬回收模組23的流洗液經由該重金屬回收模組-廢水槽管路231輸入至該廢水槽24,並透過該取樣點232取樣分析流洗液中的重金屬含量,當該流洗液中的重金屬含量達到一定標準時,表示該重金屬回收模組23中的陽離子交換樹脂吸附達到飽和,此時以陰離子再生劑流洗該重金屬回收模組23中的陽離子交換樹脂,使重金屬脫離該重金屬回收模組23中的陽離子交換樹脂,而脫離之重金屬則收集至回收液槽26,得到高濃度重金屬回收液,以待後續進行電解回收。 【00024】  根據本發明之第二實施例,如圖三A所示,本發明之第二實施例的水中重金屬回收系統3的第一重金屬清除模組以及第二重金屬清除模組是由一第一陽離子交換樹脂A、一第二陽離子交換樹脂B以及一第三陽離子交換樹脂C共同組成,該第一陽離子交換樹脂A、第二陽離子交換樹脂B、第三陽離子交換樹脂C分別以管路互相串聯,且該第一陽離子交換樹脂A、第二陽離子交換樹脂B、第三陽離子交換樹脂C各自分別與一重金屬回收模組33、一廢水槽34、一排水槽35以及一再生劑槽37以管路連接。該重金屬回收模組33係為一第四陽離子交換樹脂D,且該重金屬回收模組33並分別與該廢水槽34、一回收液槽36以及該再生劑槽37以管路連接,且該重金屬回收模組33與該廢水槽34之間連接的重金屬回收模組-廢水槽管路331上設有一取樣點332。 【00025】  本發明之第二實施例的水中重金屬回收方法如圖三B至圖三F所示。首先請參閱圖三B,含重金屬的廢水首先自廢水槽34流入該第一陽離子交換樹脂A進行處理,使廢水中的重金屬與該第一陽離子交換樹脂A結合,處理後的水接著流入該第二陽離子交換樹脂B進行處理,使水中殘餘的重金屬與該第二陽離子交換樹脂B結合,以確保處理後的廢水中重金屬含量低於排放標準,接著將處理後的廢水經由該排水槽35排出。 【00026】  請參閱圖三C,於一固定時間後,當該第一陽離子交換樹脂A尚未接近飽和時(例如,僅達到40%~60%的飽和度),將該廢水槽34中的廢水管線切換至該第二陽離子交換樹脂B進行處理,使廢水中的重金屬與該第二陽離子交換樹脂B結合,處理後的水接著流入該第三陽離子交換樹脂C進行處理,使水中殘餘的重金屬與該第三陽離子交換樹脂C結合,以確保處理後的廢水中重金屬含量低於排放標準,接著將處理後的廢水經由該排水槽35排出。此時並以陰離子再生劑流洗該第一陽離子交換樹脂A,使重金屬脫離該第一陽離子交換樹脂A,該第一陽離子交換樹脂A可再重複使用;而脫離之重金屬則流洗至該重金屬回收模組33,使脫離之重金屬與該第四陽離子交換樹脂D結合,而通過該第四陽離子交換樹脂D的流洗液則經由該重金屬回收模組-廢水槽管路331輸入至該廢水槽34。 【00027】  請參閱圖三D,於一固定時間後,當該第二陽離子交換樹脂B尚未接近飽和時(例如,僅達到40%~60%的飽和度),將該廢水槽34中的廢水管線切換至該第三陽離子交換樹脂C進行處理,使廢水中的重金屬與該第三陽離子交換樹脂C結合,處理後的水接著流入該再生的第一陽離子交換樹脂A進行處理,使水中殘餘的重金屬與該第一陽離子交換樹脂A結合,以確保處理後的廢水中重金屬含量低於排放標準,接著將處理後的廢水經由該排水槽35排出。此時並以陰離子再生劑流洗該第二陽離子交換樹脂B,使重金屬脫離該第二陽離子交換樹脂B,該第二陽離子交換樹脂B可再重複使用;而脫離之重金屬則流洗至該重金屬回收模組33,使脫離之重金屬與該第四陽離子交換樹脂D結合,而通過該第四陽離子交換樹脂D的流洗液則經由該重金屬回收模組-廢水槽管路331輸入至該廢水槽34。 【00028】  請參閱圖三E,於一固定時間後,當該第三陽離子交換樹脂C尚未接近飽和時(例如,僅達到40%~60%的飽和度),將該廢水槽34中的廢水管線切換至該第一陽離子交換樹脂A進行處理,使廢水中的重金屬與該第一陽離子交換樹脂A結合,處理後的水接著流入該再生的第二陽離子交換樹脂B進行處理,使水中殘餘的重金屬與該第二陽離子交換樹脂B結合,以確保處理後的廢水中重金屬含量低於排放標準,接著將處理後的廢水經由該排水槽35排出。此時並以陰離子再生劑流洗該第三陽離子交換樹脂C,使重金屬脫離該第三陽離子交換樹脂C,該第三陽離子交換樹脂C可再重複使用;而脫離之重金屬則流洗至該重金屬回收模組33,使脫離之重金屬與該第四陽離子交換樹脂D結合,而通過該第四陽離子交換樹脂D的流洗液則經由該重金屬回收模組-廢水槽管路331輸入至該廢水槽34。 【00029】  請參閱圖三F,於一段時間後,透過該取樣點332取樣分析流洗液中的重金屬含量,當該流洗液中的重金屬含量達到一定標準時,表示該第四陽離子交換樹脂D吸附達到飽和,此時以陰離子再生劑流洗該第四陽離子交換樹脂D,使重金屬脫離該第四陽離子交換樹脂D,而脫離之重金屬則收集至回收液槽36,得到高濃度重金屬回收液,以待後續進行電解回收。 【00030】  因此,由上述之說明可知,本發明具有下列之優點: 【00031】  本發明所提供之水中重金屬回收系統藉由增設一重金屬回收模組,以將陽離子交換樹脂的清除水中重金屬功能與回收重金屬功能分開,負責清除水中重金屬功能的重金屬清除模組可在陽離子交換樹脂尚未達到飽和前進行再生,以確保廢水中的重金屬完全與陽離子交換樹脂結合,而排放釋出的廢水中重金屬含量低於排放標準,符合規定而不會對環境造成污染。 【00032】  此外,本發明所提供之水中重金屬回收系統具有一重金屬回收模組,可集中收集由該重金屬清除模組分離而來的重金屬,待該重金屬回收模組中的陽離子交換樹脂之重金屬吸附達完全飽和時再進行再生,以得到高濃度重金屬回收液,而可提高後續重金屬電解回收之效率。 【00033】  上列詳細說明係針對本發明之一可行實施例之具體說明,惟該實施例並非用以限制本發明之專利範圍,凡未脫離本發明技藝精神所為之等效實施或變更,均應包含於本案之專利範圍中。 【00034】  綜上所述,本案所揭露之技術特徵已充分符合新穎性及進步性之法定發明專利要件,爰依法提出申請,懇請 貴局核准本件發明專利申請案,以勵發明,至感德便。The embodiments of the present invention will be described in detail below with reference to the accompanying drawings, which are to be understood Only the components and combinations related to the case are shown. The components shown in the figure are not drawn in proportion to the actual number, shape and size of the actual implementation. Some size ratios are proportional to other related dimensions or have been exaggerated or simplified. Provide a clearer description. The actual number, shape and size ratio of the implementation is an optional design, and the detailed component layout may be more complicated. [00022] According to a first embodiment of the present invention, an underwater heavy metal recovery system is illustrated as shown in the schematic diagram of FIG. The underwater heavy metal recovery system 2 of the present invention comprises a first heavy metal removal module 21, a second heavy metal removal module 22, a heavy metal recovery module 23, a waste water tank 24, a drain tank 25, and a recovery liquid tank 26 . The first heavy metal removal module 21 is connected to the wastewater tank 24 and the heavy metal recovery module 23 by a pipeline, and the first heavy metal removal module 21 has at least one cation exchange resin and a first drainage pipeline 211. The first drain line 211 is connected to the first heavy metal removal module 21 and the drain groove 25. The second heavy metal removal module 22 is connected to the wastewater tank 24 and the heavy metal recovery module 23 by a pipeline, and the second heavy metal removal module 22 has at least one cation exchange resin and a second drainage pipeline 221. The second drain line 221 is connected to the second heavy metal removal module 22 and the drain groove 25 . The heavy metal recovery module 23 is connected to the first heavy metal removal module 21, the second heavy metal removal module 22, the waste water tank 24, and the recovery liquid tank 26 by a pipeline, and the heavy metal recovery module 23 has At least one cation exchange resin. A sampling point 232 is disposed on the heavy metal recovery module-wastewater tank line 231 connected between the heavy metal recovery module 23 and the wastewater tank 24. [00023] Please continue to refer to FIG. 2, the method for recovering heavy metals in water according to the first embodiment of the present invention is that wastewater containing heavy metals first flows into the first heavy metal removal module 21 from the wastewater tank 24 for treatment, so that heavy metals in the wastewater are The cation exchange resin in the first heavy metal removal module 21 is combined, and the treated water is discharged from the first drainage line 211; after a fixed time, the cation exchange resin in the first heavy metal removal module 21 When the saturation is not near (for example, only 40% to 60% saturation), the wastewater line in the wastewater tank 24 is switched to the second heavy metal removal module 22 for treatment to make heavy metals in the wastewater and the second heavy metal. The cation exchange resin in the cleaning module 22 is combined, and the treated water is discharged from the second drain line 221; at this time, the cation exchange resin in the first heavy metal removal module 21 is washed by an anion regenerant, so that The heavy metal is separated from the cation exchange resin in the first heavy metal removal module 21, and the cation exchange resin in the first heavy metal removal module 21 can be reused; The heavy metal is flow-washed to the heavy metal recovery module 23 to combine the detached heavy metal with the cation exchange resin in the heavy metal recovery module 23; after a fixed time, the cation exchange resin in the second heavy metal removal module 22 When the saturation is not near (for example, only 40% to 60% saturation), the waste water line in the wastewater tank 24 is again switched to the first heavy metal removal module 21 for treatment, and at this time, the anion regenerator flow Washing the cation exchange resin in the second heavy metal removal module 22 to remove the heavy metal from the cation exchange resin in the second heavy metal removal module 22, and the cation exchange resin in the second heavy metal removal module 22 can be reused; The detached heavy metal is washed to the heavy metal recovery module 23, and the detached heavy metal is combined with the cation exchange resin in the heavy metal recovery module 23; the flow washing liquid passing through the heavy metal recovery module 23 passes through the heavy metal recovery module. - a waste water tank line 231 is input to the waste water tank 24, and is sampled through the sampling point 232 to analyze the heavy metal content in the flow wash liquid, when the flow wash liquid is heavy When the metal content reaches a certain standard, it indicates that the cation exchange resin in the heavy metal recovery module 23 is saturated, and the cation exchange resin in the heavy metal recovery module 23 is washed by an anion regenerant to remove the heavy metal from the heavy metal recovery module. The cation exchange resin in 23, and the detached heavy metal is collected into the recovery liquid tank 26 to obtain a high concentration heavy metal recovery liquid to be subjected to subsequent electrolytic recovery. [00024] According to a second embodiment of the present invention, as shown in FIG. 3A, the first heavy metal removal module and the second heavy metal removal module of the underwater heavy metal recovery system 3 of the second embodiment of the present invention are a cation exchange resin A, a second cation exchange resin B and a third cation exchange resin C are co-constituted, and the first cation exchange resin A, the second cation exchange resin B, and the third cation exchange resin C are respectively lined with each other. In series, the first cation exchange resin A, the second cation exchange resin B, and the third cation exchange resin C are respectively combined with a heavy metal recovery module 33, a wastewater tank 34, a drain tank 35, and a regenerant tank 37. Pipe connection. The heavy metal recovery module 33 is a fourth cation exchange resin D, and the heavy metal recovery module 33 is connected to the wastewater tank 34, a recovery liquid tank 36 and the regenerant tank 37, respectively, and the heavy metal A sampling point 332 is disposed on the heavy metal recovery module-wastewater tank line 331 connected between the recovery module 33 and the wastewater tank 34. [00025] The method for recovering heavy metals in water according to the second embodiment of the present invention is shown in FIG. 3B to FIG. Referring first to FIG. 3B, the heavy metal-containing wastewater first flows into the first cation exchange resin A from the wastewater tank 34 for treatment, so that the heavy metal in the wastewater is combined with the first cation exchange resin A, and the treated water then flows into the first The cation exchange resin B is treated to combine residual heavy metals in the water with the second cation exchange resin B to ensure that the heavy metal content in the treated wastewater is lower than the discharge standard, and then the treated wastewater is discharged through the drain tank 35. [00026] Referring to Figure 3C, after a fixed time, when the first cation exchange resin A is not near saturation (for example, only 40% to 60% saturation), the wastewater in the wastewater tank 34 The pipeline is switched to the second cation exchange resin B for treatment, the heavy metal in the wastewater is combined with the second cation exchange resin B, and the treated water is then flowed into the third cation exchange resin C for treatment to make residual heavy metals in the water The third cation exchange resin C is combined to ensure that the heavy metal content in the treated wastewater is lower than the discharge standard, and then the treated wastewater is discharged through the drain tank 35. At this time, the first cation exchange resin A is washed by an anion regenerant to remove the heavy metal from the first cation exchange resin A, and the first cation exchange resin A can be reused; and the separated heavy metal is washed to the heavy metal. The recovery module 33 is configured to combine the detached heavy metal with the fourth cation exchange resin D, and the flow washing liquid passing through the fourth cation exchange resin D is input to the wastewater tank via the heavy metal recovery module-wastewater tank line 331. 34. [00027] Please refer to FIG. 3D, after a fixed time, when the second cation exchange resin B is not near saturation (for example, only 40% to 60% saturation), the wastewater in the wastewater tank 34 The pipeline is switched to the third cation exchange resin C for treatment, the heavy metal in the wastewater is combined with the third cation exchange resin C, and the treated water is then flowed into the regenerated first cation exchange resin A for treatment to make residual water The heavy metal is combined with the first cation exchange resin A to ensure that the heavy metal content in the treated wastewater is lower than the discharge standard, and then the treated wastewater is discharged through the drain tank 35. At this time, the second cation exchange resin B is washed by an anion regenerant to remove the heavy metal from the second cation exchange resin B, and the second cation exchange resin B can be reused; and the separated heavy metal is washed to the heavy metal. The recovery module 33 is configured to combine the detached heavy metal with the fourth cation exchange resin D, and the flow washing liquid passing through the fourth cation exchange resin D is input to the wastewater tank via the heavy metal recovery module-wastewater tank line 331. 34. [00028] Please refer to FIG. 3E, after a fixed time, when the third cation exchange resin C is not near saturation (for example, only 40% to 60% saturation), the wastewater in the wastewater tank 34 The pipeline is switched to the first cation exchange resin A for treatment, the heavy metal in the wastewater is combined with the first cation exchange resin A, and the treated water is then flowed into the regenerated second cation exchange resin B for treatment to make residual water The heavy metal is combined with the second cation exchange resin B to ensure that the heavy metal content in the treated wastewater is lower than the discharge standard, and then the treated wastewater is discharged through the drain tank 35. At this time, the third cation exchange resin C is washed by an anion regenerant to remove the heavy metal from the third cation exchange resin C, and the third cation exchange resin C can be reused; and the separated heavy metal is washed to the heavy metal. The recovery module 33 is configured to combine the detached heavy metal with the fourth cation exchange resin D, and the flow washing liquid passing through the fourth cation exchange resin D is input to the wastewater tank via the heavy metal recovery module-wastewater tank line 331. 34. [00029] Please refer to FIG. 3F. After a period of time, the sample is analyzed by sampling point 332 to analyze the heavy metal content in the flow washing liquid. When the heavy metal content in the flow washing liquid reaches a certain standard, the fourth cation exchange resin D is indicated. The adsorption reaches saturation. At this time, the fourth cation exchange resin D is washed by the anion regenerant to remove the heavy metal from the fourth cation exchange resin D, and the separated heavy metal is collected into the recovery liquid tank 36 to obtain a high concentration heavy metal recovery liquid. Wait for subsequent electrolytic recovery. [00030] Therefore, from the above description, the present invention has the following advantages: [00031] The water heavy metal recovery system provided by the present invention adds a heavy metal recovery module to remove the heavy metal function of the cation exchange resin from water. The function of recovering heavy metals is separate. The heavy metal removal module responsible for removing heavy metals in water can be regenerated before the cation exchange resin has reached saturation, to ensure that the heavy metals in the wastewater are completely combined with the cation exchange resin, and the discharged waste water has low heavy metal content. The emission standards are in compliance with the regulations and do not pollute the environment. In addition, the heavy metal recovery system provided by the invention has a heavy metal recovery module, which can collect the heavy metal separated by the heavy metal removal module, and absorb the heavy metal of the cation exchange resin in the heavy metal recovery module. When it is fully saturated, it is regenerated to obtain a high-concentration heavy metal recovery liquid, which can improve the efficiency of subsequent heavy metal electrolysis recovery. The detailed description of the preferred embodiments of the present invention is not intended to limit the scope of the present invention. It should be included in the patent scope of this case. [00034] In summary, the technical features disclosed in this case have fully complied with the novelty and progressive statutory invention patent requirements, and the application is filed according to law, and you are requested to approve the invention patent application, in order to invent invention, to the sense Will.

【00035】
1‧‧‧習用之水中重金屬回收系統
11‧‧‧第一陽離子交換樹脂
12‧‧‧第二陽離子交換樹脂
13‧‧‧廢水槽
14‧‧‧排水槽
15‧‧‧回收液槽
2‧‧‧水中重金屬回收系統
21‧‧‧第一重金屬清除模組
211‧‧‧第一排水管路
22‧‧‧第二重金屬清除模組
221‧‧‧第二排水管路
23‧‧‧重金屬回收模組
231‧‧‧重金屬回收模組-廢水槽管路
232‧‧‧取樣點
24‧‧‧廢水槽
25‧‧‧排水槽
26‧‧‧回收液槽
3‧‧‧水中重金屬回收系統
A‧‧‧第一陽離子交換樹脂
B‧‧‧第二陽離子交換樹脂
C‧‧‧第三陽離子交換樹脂
33‧‧‧重金屬回收模組
331‧‧‧重金屬回收模組-廢水槽管路
332‧‧‧取樣點
D‧‧‧第四陽離子交換樹脂
34‧‧‧廢水槽
35‧‧‧排水槽
36‧‧‧回收液槽
37‧‧‧再生劑槽
【00035】
1‧‧‧Used water heavy metal recovery system
11‧‧‧First cation exchange resin
12‧‧‧Second cation exchange resin
13‧‧‧ Wastewater tank
14‧‧‧Drainage trough
15‧‧‧Recycling tank
2‧‧‧Water Heavy Metal Recovery System
21‧‧‧First Heavy Metal Removal Module
211‧‧‧First drainage line
22‧‧‧Second Heavy Metal Removal Module
221‧‧‧Second drain line
23‧‧‧Heavy metal recycling module
231‧‧‧Heavy Metal Recovery Module - Wastewater Tank Pipeline
232‧‧ ‧ sampling point
24‧‧‧ Wastewater tank
25‧‧‧Drainage trough
26‧‧‧Recycling tank
3‧‧‧Water Heavy Metal Recovery System
A‧‧‧First Cation Exchange Resin
B‧‧‧Second cation exchange resin
C‧‧‧ third cation exchange resin
33‧‧‧Heavy metal recycling module
331‧‧‧Heavy Metal Recycling Module - Wastewater Tank Pipeline
332‧‧‧ sampling points
D‧‧‧fourth cation exchange resin
34‧‧‧ Wastewater tank
35‧‧‧Drainage trough
36‧‧‧Recycling tank
37‧‧‧Regenerant tank

【00018】  圖一為習用水中重金屬回收系統之架構示意圖。 【00019】  圖二為本發明第一實施例的水中重金屬回收系統之架構示意圖。 【00020】  圖三A為本發明之第二實施例的水中重金屬回收系統之設置示意圖;圖三B至圖三F為本發明之第二實施例的水中重金屬回收系統運作示意圖。圖中實線表示有液體流動,虛線表示沒有液體流動。[00018] Figure 1 is a schematic diagram of the structure of a heavy metal recovery system in water. [00019] FIG. 2 is a schematic structural view of a heavy metal recovery system in water according to a first embodiment of the present invention. [00020] FIG. 3A is a schematic view showing the arrangement of the heavy metal recovery system in the water according to the second embodiment of the present invention; and FIG. 3B to FIG. 3F are schematic diagrams showing the operation of the heavy metal recovery system in the water according to the second embodiment of the present invention. The solid line in the figure indicates the flow of liquid, and the broken line indicates that there is no liquid flow.

2‧‧‧水中重金屬回收系統 2‧‧‧Water Heavy Metal Recovery System

21‧‧‧第一重金屬清除模組 21‧‧‧First Heavy Metal Removal Module

211‧‧‧第一排水管路 211‧‧‧First drainage line

22‧‧‧第二重金屬清除模組 22‧‧‧Second Heavy Metal Removal Module

221‧‧‧第二排水管路 221‧‧‧Second drain line

23‧‧‧重金屬回收模組 23‧‧‧Heavy metal recycling module

231‧‧‧重金屬回收模組-廢水槽管路 231‧‧‧Heavy Metal Recovery Module - Wastewater Tank Pipeline

232‧‧‧取樣點 232‧‧ ‧ sampling point

24‧‧‧廢水槽 24‧‧‧ Wastewater tank

25‧‧‧排水槽 25‧‧‧Drainage trough

26‧‧‧回收液槽 26‧‧‧Recycling tank

Claims (9)

一種水中重金屬回收系統,包含: 一第一重金屬清除模組、一第二重金屬清除模組、一重金屬回收模組、一廢水槽,以及一回收液槽;且 該第一重金屬清除模組分別與該廢水槽以及該重金屬回收模組以管路連接,且該第一重金屬清除模組具有至少一個陽離子交換樹脂以及一第一排水管路; 該第二重金屬清除模組分別與該廢水槽以及該重金屬回收模組以管路連接,且該第二重金屬清除模組具有至少一個陽離子交換樹脂以及一第二排水管路;以及 該重金屬回收模組分別與該第一重金屬清除模組、該第二重金屬清除模組、該廢水槽、以及該回收液槽以管路連接,且該重金屬回收模組具有至少一個陽離子交換樹脂。A heavy metal recovery system for water, comprising: a first heavy metal removal module, a second heavy metal removal module, a heavy metal recovery module, a wastewater tank, and a recovery liquid tank; and the first heavy metal removal module respectively The waste water tank and the heavy metal recovery module are connected by a pipeline, and the first heavy metal removal module has at least one cation exchange resin and a first drainage pipeline; the second heavy metal removal module and the wastewater tank respectively The heavy metal recovery module is connected by a pipeline, and the second heavy metal removal module has at least one cation exchange resin and a second drainage pipeline; and the heavy metal recovery module and the first heavy metal removal module and the second The heavy metal removal module, the wastewater tank, and the recovery liquid tank are connected by a pipeline, and the heavy metal recovery module has at least one cation exchange resin. 如申請專利範圍第1項所述之水中重金屬回收系統,進一步具有一排水槽,該第一排水管路係連接該第一重金屬清除模組與該排水槽,且該第二排水管路係連接該第二重金屬清除模組與該排水槽。The heavy metal recovery system for water according to claim 1, further comprising a drainage channel connecting the first heavy metal removal module and the drainage channel, and the second drainage pipe is connected The second heavy metal removal module and the drain groove. 如申請專利範圍第1項所述之水中重金屬回收系統,其中該重金屬回收模組與該廢水槽之間連接的重金屬回收模組-廢水槽管路上設有一取樣點。The heavy metal recovery system for water according to claim 1, wherein the heavy metal recovery module and the waste water tank connected to the waste water tank are provided with a sampling point. 一種水中重金屬回收方法,包含: 提供一如申請專利範圍第1項所述之水中重金屬回收系統; 將水自該回收系統的廢水槽流至該回收系統的第一重金屬清除模組進行處理,使水中的重金屬與該第一重金屬清除模組中的陽離子交換樹脂結合,處理後的水由該第一排水管路排出; 在該第一重金屬清除模組中的陽離子交換樹脂尚未飽和時,將該廢水槽中的廢水管線切換至該回收系統的第二重金屬清除模組進行處理,使水中的重金屬與該第二重金屬清除模組中的陽離子交換樹脂結合,處理後的水由該第二排水管路排出; 以陰離子再生劑流洗該第一重金屬清除模組中的陽離子交換樹脂,使重金屬脫離該第一重金屬清除模組中的陽離子交換樹脂,該第一重金屬清除模組中的陽離子交換樹脂可重複使用,並將脫離之重金屬流洗至該重金屬回收模組,使脫離之重金屬與該重金屬回收模組中的陽離子交換樹脂結合; 在該第二重金屬清除模組中的陽離子交換樹脂尚未接近飽和時,將該廢水槽中的廢水管線切換至該第一重金屬清除模組進行處理,並以陰離子再生劑流洗該第二重金屬清除模組中的陽離子交換樹脂,使重金屬脫離該第二重金屬清除模組中的陽離子交換樹脂,該第二重金屬清除模組中的陽離子交換樹脂可再重複使用,並將脫離之重金屬流洗至該重金屬回收模組,使脫離之重金屬與該重金屬回收模組中的陽離子交換樹脂結合;以及 將通過該重金屬回收模組的流洗液經由該重金屬回收模組-廢水槽管路輸入至該廢水槽,當該重金屬回收模組中的陽離子交換樹脂吸附達到飽和時,以陰離子再生劑流洗該重金屬回收模組中的陽離子交換樹脂,使重金屬脫離該重金屬回收模組中的陽離子交換樹脂,並將脫離之重金屬收集至該回收系統的回收液槽,得到高濃度重金屬回收液。A method for recovering heavy metals in water, comprising: providing a heavy metal recovery system in water as described in claim 1; flowing water from a waste water tank of the recovery system to a first heavy metal removal module of the recovery system for processing The heavy metal in the water is combined with the cation exchange resin in the first heavy metal removal module, and the treated water is discharged from the first drainage line; when the cation exchange resin in the first heavy metal removal module is not saturated, The waste water line in the waste water tank is switched to the second heavy metal removal module of the recovery system for processing, the heavy metal in the water is combined with the cation exchange resin in the second heavy metal removal module, and the treated water is drained by the second drain The cation exchange resin in the first heavy metal removal module is washed by an anion regenerant to remove the heavy metal from the cation exchange resin in the first heavy metal removal module, and the cation exchange resin in the first heavy metal removal module Reusable, and the detached heavy metal stream is washed to the heavy metal recovery module to make it detached Is associated with the cation exchange resin in the heavy metal recovery module; when the cation exchange resin in the second heavy metal removal module is not near saturation, the waste water line in the waste water tank is switched to the first heavy metal removal module Treating, and washing the cation exchange resin in the second heavy metal removal module with an anion regenerant to remove heavy metals from the cation exchange resin in the second heavy metal removal module, and the cation exchange resin in the second heavy metal removal module Reusable, and the detached heavy metal stream is washed to the heavy metal recovery module to combine the detached heavy metal with the cation exchange resin in the heavy metal recovery module; and the flow washing liquid passing through the heavy metal recovery module is passed through the The heavy metal recovery module-wastewater tank line is input to the waste water tank, and when the cation exchange resin in the heavy metal recovery module is saturated, the cation exchange resin in the heavy metal recovery module is washed with an anion regenerant to make heavy metal Remove the cation exchange resin from the heavy metal recovery module and remove the weight The metal is collected into the recovery tank of the recovery system to obtain a high concentration heavy metal recovery liquid. 如申請專利範圍第5項所述之水中重金屬回收方法,其中該重金屬回收模組中的陽離子交換樹脂吸附飽和度係透過該重金屬回收模組-廢水槽管路上的取樣點取樣分析流洗液中的重金屬含量而決定。The method for recovering heavy metals in water according to claim 5, wherein the cation exchange resin adsorption saturation in the heavy metal recovery module is sampled and analyzed in the flow washing liquid through the sampling point on the heavy metal recovery module-waste water tank line. The heavy metal content is determined. 一種水中重金屬回收系統,包含: 一第一陽離子交換樹脂、一第二陽離子交換樹脂、一第三陽離子交換樹脂、一重金屬回收模組、一廢水槽、一排水槽,以及一回收液槽;且 該第一陽離子交換樹脂、該第二陽離子交換樹脂、該第三陽離子交換樹脂分別以管路互相串聯,且該第一陽離子交換樹脂、該第二陽離子交換樹脂、該第三陽離子交換樹脂各自分別與該重金屬回收模組、該廢水槽以及該排水槽以管路連接;以及 該重金屬回收模組係為一第四陽離子交換樹脂,且該重金屬回收模組並分別與該廢水槽以及該回收液槽以管路連接。A heavy metal recovery system for water, comprising: a first cation exchange resin, a second cation exchange resin, a third cation exchange resin, a heavy metal recovery module, a waste water tank, a drain tank, and a recovery liquid tank; The first cation exchange resin, the second cation exchange resin, and the third cation exchange resin are respectively connected in series with each other, and the first cation exchange resin, the second cation exchange resin, and the third cation exchange resin are respectively And the heavy metal recovery module, the wastewater tank and the drainage tank are connected by a pipeline; and the heavy metal recovery module is a fourth cation exchange resin, and the heavy metal recovery module is respectively associated with the wastewater tank and the recovery liquid The slots are connected by pipes. 如申請專利範圍第6項所述之水中重金屬回收系統,其中該重金屬回收模組與該廢水槽之間連接的重金屬回收模組-廢水槽管路上設有一取樣點。For example, in the heavy metal recovery system of the water according to claim 6, wherein the heavy metal recovery module and the waste water tank connected to the waste water tank are provided with a sampling point. 一種水中重金屬回收方法,包含: 提供一如申請專利範圍第6項所述之水中重金屬回收系統; 將水自該回收系統的廢水槽流至該第一陽離子交換樹脂進行處理,使水中的重金屬與該第一陽離子交換樹脂結合,處理後的水接著流入該第二陽離子交換樹脂進行處理,使水中殘餘的重金屬與該第二陽離子交換樹脂結合,並將處理後的水經由該排水槽3排出; 在該第一陽離子交換樹脂尚未接近飽和時,將該廢水槽中的廢水管線切換至該第二陽離子交換樹脂進行處理,使水中的重金屬與該第二陽離子交換樹脂結合,處理後的水接著流入該第三陽離子交換樹脂進行處理,使水中殘餘的重金屬與該第三陽離子交換樹脂結合,並將處理後的水經由該排水槽排出,並以陰離子再生劑流洗該第一陽離子交換樹脂,使重金屬脫離該第一陽離子交換樹脂,該第一陽離子交換樹脂可再重複使用,而將脫離之重金屬流洗至該重金屬回收模組,使脫離之重金屬與該第四陽離子交換樹脂結合,並將通過該第四陽離子交換樹脂的流洗液經由該重金屬回收模組-廢水槽管路輸入至該廢水槽; 在該第二陽離子交換樹脂尚未接近飽和時,將該廢水槽中的廢水管線切換至該第三陽離子交換樹脂進行處理,使水中的重金屬與該第三陽離子交換樹脂結合,處理後的水接著流入該再生的第一陽離子交換樹脂進行處理,使水中殘餘的重金屬與該第一陽離子交換樹脂結合,並將處理後的水經由該排水槽排出,並以陰離子再生劑流洗該第二陽離子交換樹脂,使重金屬脫離該第二陽離子交換樹脂,該第二陽離子交換樹脂可再重複使用,而將脫離之重金屬流洗至該重金屬回收模組,使脫離之重金屬與該第四陽離子交換樹脂結合,並將通過該第四陽離子交換樹脂的流洗液經由該重金屬回收模組-廢水槽管路輸入至該廢水槽; 在該第三陽離子交換樹脂尚未接近飽和時,將該廢水槽中的廢水管線切換至該第一陽離子交換樹脂進行處理,使水中的重金屬與該第一陽離子交換樹脂結合,處理後的水接著流入該再生的第二陽離子交換樹脂進行處理,使水中殘餘的重金屬與該第二陽離子交換樹脂結合,並將處理後的水經由該排水槽排出,並以陰離子再生劑流洗該第三陽離子交換樹脂,使重金屬脫離該第三陽離子交換樹脂,該第三陽離子交換樹脂可再重複使用,而將脫離之重金屬流洗至該重金屬回收模組,使脫離之重金屬與該第四陽離子交換樹脂結合,並將通過該第四陽離子交換樹脂的流洗液經由該重金屬回收模組-廢水槽管路輸入至該廢水槽; 當該第四陽離子交換樹脂吸附達到飽和時,以陰離子再生劑流洗該第四陽離子交換樹脂,使重金屬脫離該第四陽離子交換樹脂,並將脫離之重金屬收集至該回收系統的回收液槽,得到高濃度重金屬回收液。A method for recovering heavy metals in water, comprising: providing a heavy metal recovery system in water as described in claim 6; flowing water from the waste water tank of the recovery system to the first cation exchange resin for treatment to make heavy metals in the water The first cation exchange resin is combined, and the treated water is then flowed into the second cation exchange resin for treatment, the residual heavy metal in the water is combined with the second cation exchange resin, and the treated water is discharged through the drain tank 3; When the first cation exchange resin is not near saturation, the waste water line in the waste water tank is switched to the second cation exchange resin for treatment, the heavy metal in the water is combined with the second cation exchange resin, and the treated water is then flowed in. The third cation exchange resin is treated to combine residual heavy metals in the water with the third cation exchange resin, and the treated water is discharged through the drain tank, and the first cation exchange resin is washed with an anion regenerant. Heavy metal is detached from the first cation exchange resin, the first cation exchange The grease can be reused, and the detached heavy metal is washed to the heavy metal recovery module, the detached heavy metal is combined with the fourth cation exchange resin, and the flow washing liquid passing through the fourth cation exchange resin is recovered through the heavy metal. a module-wastewater tank line is input to the waste water tank; when the second cation exchange resin is not nearly saturated, the waste water line in the waste water tank is switched to the third cation exchange resin for treatment, and the heavy metal in the water is The third cation exchange resin is combined, and the treated water is then flowed into the regenerated first cation exchange resin for treatment, the residual heavy metal in the water is combined with the first cation exchange resin, and the treated water is discharged through the drain tank. And washing the second cation exchange resin with an anion regenerant to remove the heavy metal from the second cation exchange resin, the second cation exchange resin can be reused, and the detached heavy metal stream is washed to the heavy metal recovery module, so that The detached heavy metal is combined with the fourth cation exchange resin and will pass through the fourth cation a flow washing liquid of the resin is input to the waste water tank via the heavy metal recovery module-drainage tank line; and when the third cation exchange resin is not near saturation, the waste water line in the waste water tank is switched to the first cation exchange resin Processing to combine heavy metals in the water with the first cation exchange resin, and the treated water is then flowed into the regenerated second cation exchange resin for treatment to combine residual heavy metals in the water with the second cation exchange resin and to treat The water after the drain is discharged through the drain tank, and the third cation exchange resin is washed by an anion regenerant to remove the heavy metal from the third cation exchange resin, and the third cation exchange resin can be reused again, and the heavy metal stream to be detached Washing to the heavy metal recovery module, combining the detached heavy metal with the fourth cation exchange resin, and inputting the flow washing liquid passing through the fourth cation exchange resin to the wastewater tank through the heavy metal recovery module-wastewater tank line When the fourth cation exchange resin is saturated, the anion regenerant is used to wash the first Cation exchange resin, the heavy metal from the fourth cation exchange resin, and collection tank to the recovery of heavy metals from the recovery system to obtain a high concentration of heavy metals recovery solution. 如申請專利範圍第8項所述之水中重金屬回收方法,其中該第四陽離子交換樹脂吸附飽和度係透過該重金屬回收模組-廢水槽管路上的取樣點取樣分析流洗液中的重金屬含量而決定。The method for recovering heavy metals in water according to claim 8, wherein the fourth cation exchange resin adsorption saturation is obtained by sampling the sampling points on the heavy metal recovery module-wastewater tank line to analyze the heavy metal content in the flow washing liquid. Decide.
TW104104078A 2015-02-06 2015-02-06 Heavy metal recovery system and recovery method in water TWI589534B (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110723781A (en) * 2019-11-11 2020-01-24 四川建筑职业技术学院 Sewage treatment device and method for removing heavy metal ions
CN110723781B (en) * 2019-11-11 2024-06-07 四川建筑职业技术学院 Sewage treatment device and treatment method for removing heavy metal ions

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110723781A (en) * 2019-11-11 2020-01-24 四川建筑职业技术学院 Sewage treatment device and method for removing heavy metal ions
CN110723781B (en) * 2019-11-11 2024-06-07 四川建筑职业技术学院 Sewage treatment device and treatment method for removing heavy metal ions

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