TW201822861A - Method for producing water-purifying agent and method for treating wastewater - Google Patents

Method for producing water-purifying agent and method for treating wastewater Download PDF

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TW201822861A
TW201822861A TW106131604A TW106131604A TW201822861A TW 201822861 A TW201822861 A TW 201822861A TW 106131604 A TW106131604 A TW 106131604A TW 106131604 A TW106131604 A TW 106131604A TW 201822861 A TW201822861 A TW 201822861A
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water
agent
polymer
plant powder
purifying agent
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TWI746638B (en
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伊東雅彦
島田竜
藤田貴則
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日商迪睿合股份有限公司
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/54Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
    • C02F1/56Macromolecular compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D21/00Separation of suspended solid particles from liquids by sedimentation
    • B01D21/01Separation of suspended solid particles from liquids by sedimentation using flocculating agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/42Treatment of water, waste water, or sewage by ion-exchange

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  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

A production method for a water-purifying agent that comprises a granulated substance that contains a plant powder and a polymer coagulant. The production method is characterized by including a step for mixing and kneading the plant powder and the polymer coagulant such that the hardness of the kneaded mixture obtained by means of the mixing and kneading demonstrates a stress of 3-100 N/mm2 under the following measurement conditions: a stress-controlled rheometer (a viscosity measurement device) is used to measure the stress at a push depth of 5 mm when a probe that has a diameter of 16 mm is pushed into the kneaded mixture at a pushing speed of 30 mm/min.

Description

水淨化劑的製造方法及排放水處理方法Method for manufacturing water purification agent and method for treating discharged water

本發明係關於一種使用於工業排放水等之水淨化的植物來源水淨化劑的製造方法,及使用該水淨化劑的排放水處理方法。The present invention relates to a method for manufacturing a plant-sourced water purification agent used for water purification of industrial discharge water and the like, and a method for treating discharged water using the water purification agent.

近年來,於工廠製造各種產品的過程中,大量產生了包含金屬離子或氟離子等無機離子之環境有害物質的廢液。 另一方面,關於此等無機離子的排放規定亦漸漸變得嚴苛。為了遵守此等排放規定,本發明人們尋求一種能將無機離子自包含無機離子的排放水中有效率地去除,且儘可能地以簡單、低成本的方式實施之無機離子的去除方法。 一直以來,就去除來自工廠排放水等不純物粒子的方法而言,有人提出了凝集沉澱法、離子交換法、使用活性碳等吸附劑之吸附法、電吸附法、及磁吸附法等。In recent years, in the process of manufacturing various products in factories, a large amount of waste liquid containing environmentally harmful substances such as metal ions or inorganic ions has been produced. On the other hand, regulations regarding the emission of these inorganic ions have gradually become stricter. In order to comply with such discharge regulations, the present inventors sought a method for removing inorganic ions that can efficiently remove inorganic ions from the discharged water containing the inorganic ions, and implement it as simply and cost-effectively as possible. Concerning methods for removing impurities such as water discharged from factories, agglutination precipitation methods, ion exchange methods, adsorption methods using adsorbents such as activated carbon, electro-adsorption methods, and magnetic adsorption methods have been proposed.

例如,就凝集沉澱法而言,有人提出了一種方法,該方法包含:將鹼加入溶解有重金屬離子的排放水,並使排放水呈鹼性,接著使至少一部份的重金屬離子不溶解化,進而形成懸濁固狀物的步驟;將無機凝集劑加入排放水,使懸濁固狀物凝結沉降的步驟;及讓排放水通過含有黃麻菜(mulukhiya)、小松菜(komatsuna)等葉菜的陽離子交換體之吸附層的吸附步驟(例如,參照專利文獻1)。 同時,也有人提出一種凝集方法,其係將含有黃麻菜、或其乾燥物、或其抽出物中至少任一者的凝集劑與高分子凝集劑混合或併用,進而使懸濁液中微粒子凝集分離(例如,參照專利文獻2)。For example, in the case of the agglutination precipitation method, a method has been proposed, which comprises adding alkali to the discharged water in which heavy metal ions are dissolved and making the discharged water alkaline, and then insolating at least a part of the heavy metal ions. A step of forming a suspended solid; a step of adding an inorganic agglutinating agent to the discharged water to coagulate and settle the suspended solid; and passing the discharged water through a leafy vegetable containing jute (mulukhiya) and komatsuna An adsorption step of an adsorption layer of a cation exchanger (for example, refer to Patent Document 1). At the same time, an agglutination method has also been proposed, which involves mixing or using agglutinating agents containing at least any one of jute, its dried products, or extracts thereof, and polymer agglutinating agents, thereby aggregating fine particles in suspension Separation (for example, refer to Patent Document 2).

此外,當欲淨化之排放水的量越多、包含於排放水之不必要物質的量越多、或包含於排放水之不必要物質的種類越多時,則期望建構一種於此等排放水的淨化處理中自動地投入必要的淨化劑之系統。 在進行高速且穩定的淨化處理之外,裝置的自動化是重要課題,且在提供顯示有穩定淨化性能的自動化淨化裝置之外,亦期望提供適合該自動化淨化裝置的水淨化劑。 然而,上述專利文獻1與上述專利文獻2所記載的方法完全未意識到排放水淨化處理的自動化裝置,此等文獻所記載的水淨化劑並非適合供給至自動化系統裝置的水淨化劑。 因此,有人提案了由包含植物粉末與高分子凝集劑的混合物之顆粒而成的水淨化劑,作為能夠適當地使用於自動化淨化裝置的水淨化劑(例如,參照專利文獻3)。In addition, when the amount of discharged water to be purified is larger, the amount of unnecessary substances contained in the discharged water is larger, or the types of unnecessary substances contained in the discharged water are more, it is desirable to construct a type of such discharged water A system that automatically puts in necessary purification agents during the purification process. In addition to performing a high-speed and stable purification process, automation of the device is an important issue, and in addition to providing an automatic purification device showing stable purification performance, it is also desirable to provide a water purification agent suitable for the automatic purification device. However, the methods described in the above-mentioned Patent Documents 1 and 2 are not aware of an automatic device for purifying the discharged water, and the water-purifying agents described in these documents are not suitable for supplying water-purifying agents to automated system devices. Therefore, a water purification agent composed of particles of a mixture of a plant powder and a polymer coagulant has been proposed as a water purification agent that can be suitably used in an automatic purification device (for example, refer to Patent Document 3).

[先前技術文獻] [專利文獻] [專利文獻1]日本特開2011-194385號公報 [專利文獻2]日本特開平11-114313號公報 [專利文獻3]日本特開2016-73898號公報[Prior Art Literature] [Patent Literature] [Patent Literature 1] Japanese Patent Laid-Open No. 2011-194385 [Patent Literature 2] Japanese Patent Laid-Open No. 11-114313 [Patent Literature 3] Japanese Patent Laid-Open No. 2016-73898

[發明所欲解決之課題] 然而,就自動化淨化裝置大型化時,特別是排放水槽的尺寸係用於供給至大的自動化淨化裝置時,就低成本且能夠每次都不變動地發揮穩定的淨化性能而言,吾人明白到上述專利文獻3所載之水淨化劑係不夠充分。 因此,本發明人們期望提供一種水淨化劑,其係亦能夠適用於排放水槽的尺寸為用於大的自動化淨化裝置時的水淨化劑,並其係低成本且能夠每次顯示不變動的穩定淨化性能。[Problems to be Solved by the Invention] However, when the size of the automatic purification device is increased, especially when the size of the drain tank is used for supplying to a large automatic purification device, it is low-cost and stable without changing every time. In terms of purification performance, I understand that the water purification agent contained in the above-mentioned Patent Document 3 is insufficient. Therefore, the present inventors desire to provide a water purifying agent which is also applicable to a water purifying agent having a size of a drain tank used in a large automatic purification device, and which is stable at low cost and capable of being displayed without change each time. Purification performance.

本發明解決過去的多個問題,並將達成以下的目的作為課題。亦即,本發明之目的係提供一種水淨化劑,其係亦能夠適用於排放水槽的尺寸為用於大的自動化淨化裝置時的水淨化劑,並其係低成本且能夠每次顯示不變動的穩定淨化性能。The present invention solves a plurality of problems in the past, and has as its object to achieve the following objects. That is, the object of the present invention is to provide a water purifying agent, which can also be applied to a water purifying agent having a size of a drain tank for a large automatic purification device, and is low-cost and can be displayed without changing each time. Stable purification performance.

[用於解決課題之手段] 就解決該課題的手段而言,如下所述。亦即: <1> 一種水淨化劑的製造方法,其係製造由包含植物粉末與高分子凝集劑的顆粒而成之水淨化劑的製造方法,其係包含: 混練步驟,將植物粉末與高分子凝集劑混練;其中, 在前述混練步驟中,經由前述混練步驟而得之混練物的硬度係以在下述測定條件中使其應力顯示為3N/mm2 ~100N/mm2 的方式,來混練植物粉末與高分子凝集劑; 測定條件:針對前述混練物,使用應力控制型流變儀(黏度測定裝置),測定在押入速度為30mm/min下,押入直徑16mm的探針時,押入量為5mm時的應力。 <2> 如前述<1>所述之水淨化劑的製造方法,其中,符合下述(a1)、下述(a2)、及下述(b)中任一者: (a1):第一混練步驟,將水混合至前述高分子凝集劑,以混練前述高分子凝集劑與水;之後,進行第二混練步驟,將前述植物粉末混合至經混練的前述高分子凝集劑,以混練前述植物粉末與高分子凝集劑;其中,在前述第一混練步驟中,相對於前述水淨化劑中的固體成分(質量),水混合的合計量(質量)係1.5倍至8倍; (a2):第一混練步驟,將水混合至前述高分子凝集劑,以混練前述高分子凝集劑與水;之後,進行第二混練步驟,將前述植物粉末與水混合至經混練的前述高分子凝集劑,以混練前述植物粉末與高分子凝集劑;其中,在前述第一混練步驟及前述第二混練步驟中,相對於前述水淨化劑中的固體成分(質量),水混合的合計量(質量)係1.5倍至8倍;及 (b):混練步驟,將植物粉末與高分子凝集劑及水混合,以混練之;其中,在前述混練步驟中,相對於前述水淨化劑中的固體成分(質量),水混合的合計量(質量)係1.5倍至8倍。 <3> 如前述<1>所述之水淨化劑的製造方法,其係包含:第一混練步驟,將水混合至前述高分子凝集劑,以混練前述高分子凝集劑與水;之後,進行第二混練步驟,將前述植物粉末混合至經混練的前述高分子凝集劑,以混練前述植物粉末與高分子凝集劑。 <4> 如前述<1>~<3>中任一者所述之水淨化劑的製造方法,其中,在轉速80rpm~150rpm的條件下,前述混練時之混練時間的合計數值為15分鐘以上且30分鐘以內。 <5> 如前述<1>~<4>中任一者所述之水淨化劑的製造方法,其中,該植物粉末係選自長朔黃麻(changshuohuangma)、黃麻菜、小松菜、鴨兒芹、日本蕪菁及波菜所組成之群中任一者。 <6> 如前述<5>所述之水淨化劑的製造方法,其中,該植物粉末係長朔黃麻。 <7> 如前述<6>所述之水淨化劑的製造方法,其中,該長朔黃麻係中國農業科學院麻類研究所之鑑定編號2013的「中黃麻4號」。 <8> 如前述<1>~<7>中任一者所述之水淨化劑的製造方法,其中,該水淨化劑的中位徑為150μm以上。 <9> 如前述<1>~<8>中任一者所述之水淨化劑的製造方法,其中,該高分子凝集劑係聚丙烯醯胺。 <10> 如前述<1>~<9>中任一者所述之水淨化劑的製造方法,其係包含: 成形步驟,形成經由前述混練步驟所獲得之成形有混練物的成形體; 乾燥步驟,將前述成形體乾燥;及 粉碎步驟,將該乾燥後成形體粉碎。 <11> 一種排放水處理方法,其係將前述<1>~<10>中任一者所述之水淨化劑的製造方法所獲得之水淨化劑溶解於水,進而獲得包含植物粉末與高分子凝集劑的分散液,接著藉由將該分散液供給至含有無機系廢棄物的排放水,以去除排放水中的無機系廢棄物。 <12> 如前述<11>所述之排放水處理方法,其中,該排放水係具有選自鎳、氟、鐵、銅、鋅、鉻、砷、鎘及鉛所組成之群中至少一種的無機系廢棄物。 <13> 如前述<11>或<12>所述之排放水處理方法,其中,前述分散液中水的導電度為30μS/cm以上。[Means for Solving the Problem] The means for solving the problem are as follows. That is: <1> A method for manufacturing a water purifying agent, which is a method for manufacturing a water purifying agent composed of particles of a plant powder and a polymer agglutinating agent, which includes: a kneading step, mixing the plant powder with high Molecular agglutination kneading; wherein, in the kneading step, the hardness of the kneaded material obtained through the kneading step is kneaded in such a manner that the stress is displayed as 3N / mm 2 to 100N / mm 2 under the following measurement conditions. Plant powder and polymer agglutinating agent; Measurement conditions: For the aforementioned kneaded material, a stress-controlled rheometer (viscosity measuring device) is used to measure the insertion amount when a probe with a diameter of 16 mm is inserted at a speed of 30 mm / min. Stress at 5mm. <2> The manufacturing method of the water purification agent as described in said <1> which is compatible with any one of the following (a1), (a2), and (b): (a1): 1st In the kneading step, water is mixed to the aforementioned polymer agglutinating agent to knead the aforementioned polymer agglutinating agent and water; and then, a second kneading step is performed to mix the aforementioned plant powder to the kneaded polymer agglomerating agent to knead the plant Powder and polymer coagulant; wherein, in the first kneading step, the total amount (mass) of water mixing is 1.5 to 8 times the solid content (mass) in the water purifying agent; (a2): A first kneading step, mixing water to the polymer coagulant to knead the polymer coagulant and water; and then performing a second kneading step, mixing the plant powder and water to the kneaded polymer coagulant, The above-mentioned plant powder and polymer agglutinating agent are kneaded; wherein, in the first kneading step and the second kneading step, the total amount of water mixing with respect to the solid content (mass) in the water purifying agent. Mass) is 1.5 times to 8 times; and (b): a kneading step in which the plant powder is mixed with a polymer coagulant and water to knead it; wherein, in the kneading step, compared with the solid in the water purifying agent, The composition (mass) and the total amount (mass) of water mixing are 1.5 to 8 times. <3> The method for producing a water purification agent according to the above <1>, comprising: a first kneading step, mixing water to the polymer agglutinating agent to knead the polymer agglutinating agent and water; and then, performing In a second kneading step, the plant powder is mixed with the kneaded polymer aggregate agent to knead the plant powder and the polymer aggregate agent. <4> The method for producing a water purifying agent according to any one of <1> to <3>, wherein the total value of the kneading time during the kneading is 15 minutes or more under the condition of a rotation speed of 80 rpm to 150 rpm. And within 30 minutes. <5> The method for producing a water purifying agent according to any one of <1> to <4>, wherein the plant powder is selected from the group consisting of changshuohuangma, jute, komatsu, and duck parsley , Japanese turnips and wave dishes. <6> The method for producing a water purifying agent according to the above <5>, wherein the plant powder is Changshuo jute. <7> The method for producing a water purifying agent according to the above <6>, wherein the Changshuo jute is an identification number 2013 of "Medium Jute 4" of the Institute of Hemp Research, Chinese Academy of Agricultural Sciences. <8> The manufacturing method of the water purification agent as described in any one of said <1>-<7> whose median diameter of this water purification agent is 150 micrometers or more. <9> The method for producing a water purification agent according to any one of <1> to <8>, wherein the polymer agglutinating agent is polypropylene amidamine. <10> The method for producing a water purifying agent according to any one of the above <1> to <9>, comprising: a forming step of forming a formed body obtained by forming the kneaded material obtained through the kneading step; drying A step of drying the aforementioned compact; and a crushing step of crushing the dried compact. <11> A method for treating discharged water, which is obtained by dissolving a water purifying agent obtained by the water purifying agent manufacturing method described in any one of the aforementioned <1> to <10> in water, thereby obtaining a plant powder and a high The dispersion liquid of the molecular coagulant is then supplied to the discharged water containing the inorganic waste to remove the inorganic waste from the discharged water. <12> The method for treating discharged water according to the above <11>, wherein the discharged water is at least one selected from the group consisting of nickel, fluorine, iron, copper, zinc, chromium, arsenic, cadmium, and lead. Inorganic waste. <13> The method for treating discharged water according to the above <11> or <12>, wherein the conductivity of water in the dispersion is 30 μS / cm or more.

[發明的效果] 根據本發明,能夠解決過去的多個問題,並能達成前述目的,且能提供一種水淨化劑,其係亦能夠適用於排放水槽的尺寸為用於大的自動化淨化裝置時的水淨化劑,並其係低成本且能夠每次顯示不變動的穩定淨化性能。[Effects of the Invention] According to the present invention, a plurality of problems in the past can be solved and the foregoing objects can be achieved, and a water purification agent can be provided, which can also be applied when the size of the drain tank is used for a large automatic purification device Water purification agent, and it is a low-cost and can display stable purification performance that does not change every time.

(水淨化劑的製造方法) 本發明水淨化劑的製造方法(以下亦稱為本發明的製造方法)所製造之水淨化劑,係由包含植物粉末與高分子凝集劑之顆粒而成。 本發明的製造方法係包含混練植物粉末與高分子凝集劑的混練步驟,且更因應必要,含有成形步驟、乾燥步驟、粉碎步驟等其他步驟。 本發明的製造方法,其特徵在於:在前述混練步驟中,經由前述混練步驟而得之混練物的硬度係以在下述測定條件中使其應力顯示為3N/mm2 ~100N/mm2 的方式,來混練植物粉末與高分子凝集劑。 測定條件:針對前述混練物,使用應力控制型流變儀(黏度測定裝置),測定在押入速度為30mm/min下,押入直徑16mm的探針時,押入量為5mm時的應力。(Manufacturing method of water purification agent) The water purification agent manufactured by the manufacturing method of the water purification agent of this invention (henceforth the manufacturing method of this invention) is a particle | grain containing a plant powder and a polymer aggregating agent. The manufacturing method of the present invention includes a kneading step of kneading a plant powder and a polymer agglutinating agent, and further includes a forming step, a drying step, a pulverizing step, and other steps as necessary. The manufacturing method of the present invention is characterized in that in the kneading step, the hardness of the kneaded material obtained through the kneading step is such that the stress is displayed as 3 N / mm 2 to 100 N / mm 2 under the following measurement conditions. To mix plant powder and polymer agglutinating agent. Measurement conditions: For the aforementioned kneaded material, a stress-controlled rheometer (viscosity measuring device) was used to measure the stress at a pushing speed of 30 mm / min and a probe with a diameter of 16 mm when the pushing amount was 5 mm.

在獲得上述所欲硬度之混練物後,以下的製造方法為更佳。 本發明的製造方法係在混練高分子凝集劑與水時,或在混練植物粉末與高分子凝集劑時,界定水混合的合計量(質量)。相對於前述水淨化劑中的固體成分(質量),該水混合的合計量(質量)係1.5倍至8倍。 又,本發明的製造方法係在混練植物粉末與高分子凝集劑的混練步驟前,界定了進行將水混合於高分子凝集劑且將高分子凝集劑與水混練的混練步驟。 藉由滿足上述要件的本發明製造方法所製造之水淨化劑係能夠適用於排放水槽的尺寸為用於大的自動化淨化裝置時的水淨化劑,並其係低成本且能夠每次顯示不變動的穩定淨化性能的水淨化劑。After the kneaded product having the desired hardness is obtained, the following production method is more preferable. The manufacturing method of the present invention defines a total amount (mass) of water mixing when kneading a polymer coagulant and water, or when kneading a plant powder and a polymer coagulant. The total amount (mass) of the water mixture is 1.5 to 8 times the solid content (mass) in the water purifying agent. In addition, the manufacturing method of the present invention defines a kneading step of mixing water with the polymer agglutinating agent and kneading the polymer agglutinating agent and water before the kneading step of the plant powder and the polymer agglutinating agent. The water purifying agent manufactured by the manufacturing method of the present invention satisfying the above-mentioned requirements can be applied to a water purifying agent having a size of a drain tank for a large automatic purification device, and is low-cost and can be displayed without change every time. Water purification agent with stable purification performance.

在使用水淨化劑進行排放水的淨化時,就水淨化劑的添加方法而言,可舉出於排放水直接投入水淨化劑的方法、以及先將水淨化劑溶於水來獲得植物粉末與高分子凝集劑的分散液,再將該分散液投入排放水的方法等。然而,若自動化淨化裝置大型化,特別是排放水槽的尺寸變大時,在粒狀水淨化劑的情況下,就每次皆形成穩定且均勻的分散狀態並維持不變動地水淨化性能而言,此係變得困難。因此,在排放水槽的尺寸為大的自動化淨化裝置中,變得必須利用使用分散液之排放水的淨化方法。 因此,本發明人們,針對使用分散液之排放水的淨化處理進行反覆研究,發現根據分散液中水的種類,植物粉末與高分子凝集劑溶解時該分散液的黏度會變化。 接著,本發明人們獲得以下見解:分散液黏度的差異會影響排放水的淨化性能,且為了獲得良好的淨化性能,有效的是某種程度地提高分散液的黏度。 具體而言,雖然自來水與地下水係代表性地相較便宜,但在使用由所含離子等影響而造成之導電度大的水,來獲得分散液的情況下,若於排放水添加該分散液,則排放水黏度變小,植物粉末等固體成分在短時間內沉降,結果,無法獲得充分的無機離子吸附性能。另一方面,作為自來水與地下水的替代,若使用導電度小的蒸餾水,則不會產生此種問題。然而,蒸餾水係昂貴的,在每天處理大量排放水的半導體工廠及電鍍工廠等,其成本成為很大的負擔。 因此,本發明人們在進一步進行研究時,發現一種水淨化劑,即使其係使用以相較便宜為代表性之自來水與地下水作為分散液使用,也能夠將排放水中無機離子的濃度減少至所欲濃度以下的濃度為止。When the water purification agent is used to purify the discharged water, the method of adding the water purification agent includes a method of directly pouring the water purification agent into the discharged water, and dissolving the water purification agent in water to obtain plant powder and A method of dispersing a polymer coagulant, and then pouring the dispersion into drained water. However, if the size of the automatic purification device becomes large, especially when the size of the drain tank becomes large, in the case of a granular water purification agent, a stable and uniform dispersion state is formed every time and the water purification performance is maintained without change. This department becomes difficult. Therefore, in an automatic purification apparatus having a large size of a drain tank, it becomes necessary to utilize a purification method of drain water using a dispersion liquid. Therefore, the present inventors conducted repeated researches on the purification treatment of the discharged water using the dispersion liquid, and found that, depending on the type of water in the dispersion liquid, the viscosity of the dispersion liquid changed when the plant powder and the polymer coagulant were dissolved. Then, the present inventors obtained the following insight: the difference in the viscosity of the dispersion liquid will affect the purification performance of the discharged water, and in order to obtain a good purification performance, it is effective to increase the viscosity of the dispersion liquid to some extent. Specifically, although tap water and groundwater are typically cheaper, in the case where a dispersion liquid is obtained by using water having high conductivity due to the influence of ions and the like, if the dispersion liquid is added to the discharged water, , The viscosity of the discharged water becomes small, and the solid components such as plant powder settle in a short time. As a result, sufficient inorganic ion adsorption performance cannot be obtained. On the other hand, as a substitute for tap water and groundwater, such a problem does not occur if distilled water with low conductivity is used. However, distilled water is expensive, and semiconductor factories, electroplating factories, etc., which process a large amount of discharged water every day, have become a heavy burden. Therefore, when the present inventors conducted further research, they found that a water purifying agent can reduce the concentration of inorganic ions in the discharged water to a desired level, even if it uses tap water and groundwater, which are typically cheaper, as a dispersion. Up to the concentration below.

本發明人們遂而認識到,就即使是使用自來水與地下水的分散液亦能夠提高其黏度之效果而言,此係因為在水淨化劑的製造方法中,調整混練植物粉末與高分子凝集劑而獲得之混練物的硬度係有效的。 此處,能夠使用作為應力控制型流變儀(黏度測定裝置)之TA Instruments公司製的AR-G2硬度測定模式,來求得混練物的硬度。具體而言,將約7.5g的混練物填充於內徑的直徑為22mm、深度11mm的聚丙烯製圓筒狀容器,使用直徑16mm的探針,測定在押入速度為30mm/min下押入時,押入量為5mm時的應力。在本發明中,在於此條件下測定的應力稱為「硬度」。 結果,混練物的硬度較佳在3N/mm2 ~100N/mm2 的範圍。 接著,本發明人們發現,為了獲得此所欲硬度的混練物,進行下述(i)或(ii)所示之步驟,係重要的。 (i)在製造水淨化劑的方法中,混練高分子凝集劑與水時,或在混練植物粉末與高分子凝集劑時,相對於水淨化劑中的固體成分(質量),該水混合的合計量(質量)係1.5倍至8倍。 (ii)在製造水淨化劑的方法中,於混練植物粉末與高分子凝集劑的混練步驟前,進行將水混合至高分子凝集劑並混練高分子凝集劑與水之混練步驟。The inventors then realized that the effect of increasing the viscosity even with the dispersion of tap water and groundwater is due to the adjustment and mixing of plant powder and polymer agglutinating agent in the method of manufacturing water purification agents. The hardness of the obtained kneaded material was effective. Here, the hardness of the kneaded material can be determined using the AR-G2 hardness measurement mode made by TA Instruments, which is a stress-controlled rheometer (viscosity measuring device). Specifically, about 7.5 g of the kneaded product was filled in a polypropylene cylindrical container with an inner diameter of 22 mm and a depth of 11 mm. Using a probe with a diameter of 16 mm, it was measured at a pushing speed of 30 mm / min. The stress when the pushing amount is 5mm. In the present invention, the stress measured under these conditions is called "hardness". As a result, the hardness of the kneaded material is preferably in a range of 3 N / mm 2 to 100 N / mm 2 . Next, the present inventors have found that it is important to perform the steps shown in (i) or (ii) below in order to obtain a kneaded product having the desired hardness. (I) In the method for manufacturing a water purifying agent, when the polymer agglutinating agent and water are kneaded, or when the plant powder and the polymer agglutinating agent are kneaded, the water is mixed with respect to the solid content (mass) in the water purifying agent. The total amount (mass) is 1.5 times to 8 times. (Ii) In the method for manufacturing a water purifying agent, before the kneading step of kneading the plant powder and the polymer coagulant, a kneading step of mixing water to the polymer coagulant and kneading the polymer coagulant and water is performed.

如此一來,若進行於高分子凝集劑添加多量水分並混練的步驟,或在與植物粉末混練前,進行預先將高分子凝集劑與水混練的步驟,則能夠形成所欲硬度的混練物,且經過如此之混練物所製造的水淨化劑,係能夠提升分散有該水淨化劑之分散液的黏度、及提升投入該分散液後之排放水的黏度。 雖然理由尚未明瞭,但可被認為係如下所述:在此等條件下,是否藉由混練而某種程度地解開高分子凝集劑分子鏈的凝集,並對提升其與水的溶解性做出有效貢獻。In this way, if the polymer coagulant is added with a large amount of water and kneaded, or the polymer coagulant and water are kneaded in advance before kneading with the plant powder, a kneaded product having a desired hardness can be formed. Moreover, the water purifying agent manufactured through such a kneaded product can increase the viscosity of the dispersion liquid in which the water purifying agent is dispersed and the viscosity of the discharged water after the dispersion liquid is injected. Although the reason is not clear, it can be considered as follows: Under these conditions, whether to agglomerate the molecular chain of the polymer agglutination agent to some extent, and to improve its solubility with water Make effective contributions.

以下,針對水淨化劑製造方法的具體構成,區分成(A)第一態樣及(B)第二態樣,並進行詳細說明。In the following, the specific configuration of the water purification agent manufacturing method is divided into (A) a first aspect and (B) a second aspect and described in detail.

<A;水淨化劑製造方法的第一態樣> 在前述水淨化劑的製造方法中,混練前述高分子凝集劑與水時,或在混練植物粉末與高分子凝集劑時,相對於前述水淨化劑中的固體成分(質量),該水混合的合計量(質量)係1.5倍至8倍。<A; First aspect of the water purifying agent manufacturing method> In the aforementioned water purifying agent manufacturing method, when the polymer agglutinating agent and water are kneaded, or when the plant powder and the polymer agglutinating agent are kneaded, compared with the water, The solid content (mass) in the purifying agent is 1.5 times to 8 times the total amount (mass) of the water mixture.

<<植物粉末與高分子凝集劑的混練步驟>> 雖然前述水淨化劑的製造方法係包含將植物粉末與高分子凝集劑混練的步驟,但就此混練步驟而言,具體來說,例如包含下述(a1)、(a2)及(b)所界定之步驟,可舉出下述(a1)、(a2)及(b)的三個態樣。 (a1):第一混練步驟,將水混合至高分子凝集劑,以混練前述高分子凝集劑與水;之後,進行第二混練步驟,將前述植物粉末混合至經混練的前述高分子凝集劑,以混練前述植物粉末與高分子凝集劑。 上述(a1)中,亦可於混練前述植物粉末與前述高分子凝集劑時,將水混合,此時,成為下述(a2)。 (a2):第一混練步驟,將水混合至高分子凝集劑,以混練前述高分子凝集劑與水;之後,進行第二混練步驟,將前述植物粉末與水混合至經混練的前述高分子凝集劑,以混練前述植物粉末與高分子凝集劑。 (b):混練步驟,將植物粉末與高分子凝集劑及水混合,以混練之。<< Kneading steps of plant powder and polymer agglutinating agent> Although the aforementioned method for producing a water purifying agent includes a step of kneading a plant powder and a polymer agglutinating agent, the kneading step specifically includes, for example, the following The steps defined in (a1), (a2), and (b) can be exemplified by the following three aspects (a1), (a2), and (b). (A1): a first kneading step, mixing water to a polymer coagulant to knead the polymer coagulant and water; and then, performing a second kneading step, mixing the plant powder to the kneaded polymer coagulant, To knead the aforementioned plant powder and polymer agglutinating agent. In the above (a1), when the plant powder and the polymer coagulant are kneaded, water may be mixed, and in this case, the following (a2) is obtained. (A2): the first kneading step, mixing water to the polymer coagulant to knead the polymer coagulant and water; and then, performing the second kneading step, mixing the plant powder and water to the kneaded polymer coagulant Agent to knead the aforementioned plant powder and polymer agglutinating agent. (B): kneading step, mixing plant powder with polymer coagulant and water to knead it.

就前述水混合的合計量(質量)而言,在上述(a1)中,其係被稱為在第一混練步驟中水混合的量;在上述(a2)中,其係被稱為在第一混練步驟中水混合的量與在第二混練步驟中水混合的量,兩者的合計量;在上述(b)中,其係被稱為在植物粉末與高分子凝集劑的混練步驟中,植物粉末與高分子凝集劑混合時一起混合的水的量。 相對於水淨化劑中的固體成分(質量),水混合的合計量(質量)較佳係1.5倍至8倍。 又,在上述(a2)的情況下,雖然第一混練時與第二混練時水混合的合計量係1.5倍至8倍即可,但相對於前述固體成分(質量),第一混練時水混合的量較佳係至少1倍以上。 又,雖然上述水淨化劑中的固體成分指的是植物粉末與高分子凝集劑所合併之物,但若在水淨化劑中還包含除了植物粉末與高分子凝集劑以外之如下所示的其他添加劑時,上述水淨化劑中的固體成分還包含此等添加劑,上述水淨化劑中的固體成分指的是水淨化劑中所有固體成分所合併之物。Regarding the total amount (mass) of the aforementioned water mixing, in the above (a1), it is referred to as the amount of water mixing in the first kneading step; in the above (a2), it is referred to as the first The amount of water mixed in the first kneading step and the amount of water mixed in the second kneading step, the total of the two; in (b) above, it is referred to as the kneading step of the plant powder and the polymer agglutinating agent. The amount of water that is mixed together when the plant powder is mixed with the polymer coagulant. The total amount (mass) of the water mixture is preferably 1.5 to 8 times the solid content (mass) in the water purifying agent. In addition, in the case of (a2), although the total amount of water mixing during the first kneading and the second kneading may be 1.5 times to 8 times, the water content during the first kneading is relative to the solid content (mass). The amount of mixing is preferably at least 1 time or more. In addition, although the solid content in the water purifying agent refers to a combination of a plant powder and a polymer agglutinating agent, if the water purifying agent further includes a plant powder and a polymer agglutinating agent, the following are shown. In the case of additives, the solid ingredients in the water purifying agent also include these additives. The solid ingredients in the water purifying agent refer to a combination of all solid ingredients in the water purifying agent.

就混練手段而言,並未特別限制,能夠因應目的而選擇,例如行星式混合器、捏合器、蝶形攪拌器、擠出器等,只要是能夠獲得一定混練效果的混練機,皆能夠被使用。As for the kneading means, it is not particularly limited and can be selected according to the purpose, such as planetary mixer, kneader, butterfly mixer, extruder, etc. As long as it is a kneading machine that can obtain a certain kneading effect, it can be used. use.

就前述混練時混練機的轉速而言,較佳可例如在10rpm~180rpm的範圍內進行。 又,舉例來說,在轉速80rpm~150rpm的條件下,前述混練時之混練時間的合計數值較佳為15分鐘以上且30分鐘以內。若小於15分鐘,則供給至排放水時提升黏度的效果不充分。又,若超過30分鐘,則供給至排放水時提升黏度的效果也變得不充分。若混練時間過長,則可能被認為是因為高分子凝集劑的分子鏈被切斷,而造成提升黏度效果不充分。The rotation speed of the kneader during the kneading is preferably performed in a range of 10 rpm to 180 rpm, for example. In addition, for example, under the condition that the rotation speed is 80 rpm to 150 rpm, the total value of the kneading time during the kneading is preferably 15 minutes or more and 30 minutes or less. If it is less than 15 minutes, the effect of increasing viscosity when supplied to the drain water is insufficient. If it exceeds 30 minutes, the effect of increasing the viscosity when supplying to the drain water becomes insufficient. If the kneading time is too long, it may be considered that the molecular chain of the polymer agglutinating agent is cut, and the effect of increasing the viscosity is insufficient.

<<植物粉末>> 就前述植物而言,只要是能將排放水中的廢棄物(鎳、銅、氟等)凝集分離的植物,並未特別限制而能夠被使用。舉例來說,就具有陽離子交換功能的植物而言,可舉出例如長朔黃麻(changshuohuangma)、黃麻菜(molokheiya)、小松菜、鴨兒芹、日本蕪菁及波菜等。 就植物的部位而言,可使用葉、莖、根任一者的一部分。 該植物中較佳為長朔黃麻、黃麻菜,且更佳為在下述實施例顯示有良好結果的長朔黃麻。<< Plant powder >> As long as the plant is a plant capable of aggregating and separating wastes (nickel, copper, fluorine, etc.) in the discharged water, it is not particularly limited and can be used. For example, plants having a cation-exchange function include changshuohuangma, molokheiya, komatsu, duck celery, Japanese turnip, and bok choy. Regarding the part of the plant, a part of any of a leaf, a stem, and a root may be used. Among the plants, Changshuo jute and jute are preferred, and Changshuo jute which shows good results in the following examples.

又,長朔黃麻中特佳為中國農業科學院麻類研究所之鑑定編號2013的「中黃麻4號」。 「中黃麻4號」具有以下特性: 農作物種類:黃麻。In addition, Changshu Jute Zhongjia is the "Jute Jute No. 4" with the identification number 2013 of the Institute of Hemp Research, Chinese Academy of Agricultural Sciences. "Zhong Jute No. 4" has the following characteristics: Crop type: Jute.

<<高分子凝集劑>> 就該高分子凝集劑而言,與上述植物的部分相同,只要是具有去除排放水中前述無機系廢棄物的效果之高分子凝集劑,並未特別限制,可舉出例如聚丙烯醯胺(PAM)、聚丙烯醯胺的部份水解鹽、海藻酸鈉、聚丙烯酸鈉、羧甲基纖維素(CMC, Carboxymethyl Cellulose)鈉鹽等。此等當中,較佳係使用聚丙烯醯胺。就該聚丙烯醯胺而言,例如能夠使用市售品Flopan AN 995SH、FA 920SH、FO 4490、AN 923、AN 956(SNF股份有限公司製)等。<< Polymer agglutinating agent >> The polymer agglutinating agent is the same as the above-mentioned plant part, and is not particularly limited as long as it is a polymer agglutinating agent having the effect of removing the aforementioned inorganic wastes in the discharged water. For example, polyacrylamide (PAM), a partially hydrolyzed salt of polyacrylamide, sodium alginate, sodium polyacrylate, sodium salt of carboxymethyl cellulose (CMC, Carboxymethyl Cellulose), and the like are produced. Among these, polyacrylamide is preferably used. As the polypropylene amidamine, commercially available products such as Flopan AN 995SH, FA 920SH, FO 4490, AN 923, AN 956 (manufactured by SNF Co., Ltd.) and the like can be used.

<<其他添加劑>> 作為其他添加劑,亦可在前述水淨化劑中含有例如填料、增黏劑、著色劑、觸變劑等添加物。又,在提升混練成分與水的溶解性之目的下,亦可含有少量的醇等液體。 又,可使其他添加劑於混練高分子凝集劑時添加,或者,亦可使其他添加劑於混練植物粉末與高分子凝集劑時添加。<< Other additives >> As other additives, additives such as fillers, thickeners, colorants, and thixotropic agents may be contained in the water purification agent. In addition, for the purpose of improving the solubility of the kneading component and water, a small amount of a liquid such as an alcohol may be contained. Further, other additives may be added when the polymer coagulant is kneaded, or other additives may be added when the plant powder and the polymer coagulant are kneaded.

<<植物粉末與高分子凝集劑的顆粒>> 前述植物粉末粒子與前述高分子凝集劑的混合比率較佳係在質量比為10:90~90:10的範圍。 在前述植物粉末與前述高分子凝集劑混練所獲得之顆粒表面,較佳係夾雜有存在於顆粒表面之植物粉末被高分子凝集劑被覆的被覆部分,以及未被高分子凝集劑被覆的非被覆部分。 前述顆粒的中位徑較佳為150μm以上,更佳為150μm以上且為850μm以下。若前述顆粒的中位徑在150μm以上,則延遲淨化有效成分的沉降,並能夠延長淨化有效成分的吸附時間。 此處,中位徑(亦稱為d50)係指,以前述顆粒的粒徑大小作圖時,粒徑為圖中全體個數50%位置時的粒徑(將粒徑較大側與粒徑較小側分成等量時的粒徑)。中位徑能夠藉由市售之測定機來測定。<<< particles of plant powder and polymer coagulant> The mixing ratio of the plant powder particles and the polymer coagulant is preferably in a range of 10:90 to 90:10 by mass ratio. The particle surface obtained by kneading the aforementioned plant powder with the aforementioned polymer aggregating agent is preferably mixed with a coating portion of the plant powder existing on the particle surface covered with the polymer agglutinating agent, and an uncoated portion not covered by the polymer agglutinating agent. section. The median diameter of the particles is preferably 150 μm or more, more preferably 150 μm or more and 850 μm or less. When the median diameter of the particles is 150 μm or more, the sedimentation of the purification effective component is delayed, and the adsorption time of the purification effective component can be extended. Here, the median diameter (also referred to as d50) refers to the particle diameter when the particle size of the aforementioned particles is plotted, and the particle diameter is 50% of the total number in the figure (the larger particle diameter side and the particle The smaller diameter side is divided into equal size particle sizes). The median diameter can be measured by a commercially available measuring machine.

<<其他步驟>> 本發明的製造方法除了上述混練步驟之外,亦可包含成形步驟、乾燥步驟、粉碎步驟等其他步驟。 具體而言,本發明所界定之顆粒係以包含下述步驟的製造方法來製造:成形步驟,形成經由如上述混練步驟般所獲得之成形有混練物的成形體;乾燥步驟,將前述成形體乾燥;及粉碎步驟,將乾燥後之成形體粉碎。 接著,在前述粉碎步驟後,亦可包含分級步驟,其係藉由篩子將顆粒分級。<< Other steps >> In addition to the kneading step described above, the production method of the present invention may include other steps such as a forming step, a drying step, and a pulverizing step. Specifically, the granules defined in the present invention are manufactured by a manufacturing method including the following steps: a forming step to form a shaped body obtained by forming a kneaded material obtained by the kneading step described above; and a drying step of forming the aforementioned shaped body Drying; and a pulverizing step, pulverizing the dried compact. Next, after the aforementioned pulverization step, a classification step may be included, which classifies the particles by a sieve.

在前述成形步驟中,舉例來說,可藉由任意的成形方法將前述混練物成形,來形成成形體。In the aforementioned forming step, for example, the aforementioned kneaded material may be formed by an arbitrary forming method to form a formed body.

於前述乾燥步驟中,較佳係使用多階段熱風式乾燥機,以80℃~150℃的溫度與2小時~12小時的條件,對獲得之成形體進行乾燥。 較佳係將前述成形體乾燥,並供給至粉碎步驟。 又,雖然前述乾燥步驟的較佳態樣係適用「將由成形步驟所獲得之成形體乾燥,接著將該乾燥後之成形體粉碎」的順序,但亦可進行「將由成形步驟所獲得之成形體粉碎,之後藉由進行乾燥步驟來獲得顆粒」的順序。 於前述粉碎步驟中使用粉碎機,例如使用氣流式超微粉碎機來粉碎顆粒。 於前述分級步驟使用分級機,較佳係例如使用振動篩分機或風比式分級機將粉碎後之粉末分級,使顆粒的中位徑在所欲的範圍內。較佳係使中位徑成為150μm~850μm的範圍,故篩子只會選取粒徑在150μm~850μm的範圍之顆粒,小於150μm或超過850μm的粉末會被篩子取出並去除(篩除)。In the aforementioned drying step, it is preferred to use a multi-stage hot air dryer to dry the obtained compact at a temperature of 80 ° C. to 150 ° C. and conditions of 2 hours to 12 hours. It is preferable to dry the said compact, and to supply it to a crushing process. In addition, although the preferable aspect of the aforementioned drying step is the order of "drying the formed body obtained in the forming step and then pulverizing the dried formed body", it is also possible to perform "the formed body obtained in the forming step" Crushing, followed by a drying step to obtain particles ". In the aforementioned pulverizing step, a pulverizer is used, for example, an airflow type ultrafine pulverizer is used to pulverize the particles. In the aforementioned classification step, a classifier is used, and it is preferred to classify the pulverized powder using, for example, a vibratory screener or an air ratio classifier, so that the median diameter of the particles is within a desired range. Preferably, the median diameter should be in the range of 150 μm to 850 μm, so the sieve will only select particles with a particle size in the range of 150 μm to 850 μm. Powders smaller than 150 μm or more than 850 μm will be taken out and removed (screened) by the sieve.

<B;水淨化劑製造方法的第二態樣> 在前述水淨化劑的製造方法中,在混練植物粉末與高分子凝集劑的混練步驟前,還包含將水混合至高分子凝集劑且將高分子凝集劑與水混練的步驟。<B; Second aspect of the water purifying agent manufacturing method> In the aforementioned water purifying agent manufacturing method, before the kneading step of kneading the plant powder and the polymer agglutinating agent, the method further includes mixing water to the polymer agglutinating agent and Step of mixing molecular agglutinating agent with water.

<<植物粉末與高分子凝集劑的混練步驟>> 就第二態樣中的混練步驟而言,具體來說,與上述第一態樣中上述(a1)及(a2)所記載的相同,例如包含下述(a1)及(a2)所界定之步驟,可舉出下述(a1)及(a2)的兩個態樣。 (a1):第一混練步驟,將水混合至高分子凝集劑,以混練前述高分子凝集劑與水;之後,進行第二混練步驟,將前述植物粉末混合至經混練的前述高分子凝集劑,以混練前述植物粉末與高分子凝集劑。 上述(a1)中,亦可於混練前述植物粉末與前述高分子凝集劑時,將水混合,此時,成為下述(a2)。 (a2):第一混練步驟,將水混合至高分子凝集劑,以混練前述高分子凝集劑與水;之後,進行第二混練步驟,將前述植物粉末與水混合至經混練的前述高分子凝集劑,以混練前述植物粉末與高分子凝集劑。<< Kneading step of plant powder and polymer agglutinating agent >> The kneading step in the second aspect is specifically the same as that described in (a1) and (a2) in the first aspect, For example, including the steps defined in the following (a1) and (a2), the following two aspects (a1) and (a2) can be cited. (A1): a first kneading step, mixing water to a polymer coagulant to knead the polymer coagulant and water; and then, performing a second kneading step, mixing the plant powder to the kneaded polymer coagulant, To knead the aforementioned plant powder and polymer agglutinating agent. In the above (a1), when the plant powder and the polymer coagulant are kneaded, water may be mixed, and in this case, the following (a2) is obtained. (A2): the first kneading step, mixing water to the polymer coagulant to knead the polymer coagulant and water; and then, performing the second kneading step, mixing the plant powder and water to the kneaded polymer coagulant Agent to knead the aforementioned plant powder and polymer agglutinating agent.

如在第二態樣下的界定般,於與植物粉末混練前,預先將高分子凝集劑與水混練,則對於獲得所欲硬度的混練物係有效的。 此時,就添加於混練時之水的合計量(質量)而言,並未特別限制,舉例來說,相對於水淨化劑中的固體成分(質量),在水混合的量為1倍至9倍時能夠獲得實現本發明目的之水淨化劑。然而,如在第一態樣下的界定般,在混練時,相對於水淨化劑中的固體成分(質量),水混合的合計量(質量)更佳係在1.5倍至8倍的範圍。 就混練步驟所界定之上述要件以外的要件而言,能夠適用上述第一態樣所記載的內容。As defined in the second aspect, prior to kneading with the plant powder, kneading the polymer coagulant with water in advance is effective for obtaining a kneaded system of a desired hardness. At this time, the total amount (mass) of the water added during the kneading is not particularly limited. For example, the amount of water mixed with the solid component (mass) in the water purifying agent is 1 to At 9 times, a water purifying agent that can achieve the object of the present invention can be obtained. However, as defined in the first aspect, when mixing, the total amount (mass) of water mixing is better in the range of 1.5 to 8 times than the solid content (mass) in the water purifying agent. For the requirements other than the above-mentioned requirements defined in the kneading step, the content described in the first aspect can be applied.

第二態樣中關於<<植物粉末>>、<<高分子凝集劑>>、<<其他添加劑>>、<<植物粉末與高分子凝集劑的顆粒>>、<<其他步驟>>等要件,亦能夠適用上述第一態樣所記載的內容。In the second aspect, << plant powder>, << polymer aggregating agent >>, << other additives >>, << particles of plant powder and polymer aggregating agent >>, << other steps >>, etc. Requirements can also be applied to the content described in the first aspect.

(排放水處理方法) 本發明的排放水處理方法,其係藉由將上述之本發明的製造方法所獲得之水淨化劑溶解於水,進而獲得包含植物粉末與高分子凝集劑的分散液,接著藉由將該分散液供給至含有無機系廢棄物的排放水,以去除排放水中的無機系廢棄物。 就前述無機系廢棄物而言,可舉出例如具有選自鎳、氟、鐵、銅、鋅、鉻、砷、鎘及鉛所組成之群中至少一種的無機系廢棄物。 就前述分散液而言,除了純水(蒸餾水)之外,能夠使用導電度為30μS/cm以上的水。藉此,能夠使用較便宜的自來水及地下水。 即使於分散液使用自來水及地下水,也能夠將排放水中的無機離子濃度減少至所欲濃度以下的濃度,且顯示優異的水淨化性能。 使用由本發明的製造方法所獲得之水淨化劑,製作分散液。(Discharge water treatment method) The discharge water treatment method of the present invention is to dissolve the water purifying agent obtained in the above-mentioned production method of the present invention in water, thereby obtaining a dispersion liquid containing a plant powder and a polymer coagulant, Then, the dispersion liquid is supplied to the discharged water containing the inorganic waste to remove the inorganic waste from the discharged water. Examples of the inorganic waste include inorganic waste having at least one selected from the group consisting of nickel, fluorine, iron, copper, zinc, chromium, arsenic, cadmium, and lead. In the aforementioned dispersion liquid, in addition to pure water (distilled water), water having a conductivity of 30 μS / cm or more can be used. This makes it possible to use cheaper tap water and groundwater. Even when tap water and groundwater are used in the dispersion, the concentration of inorganic ions in the discharged water can be reduced to a concentration below a desired concentration, and excellent water purification performance is exhibited. The water purification agent obtained by the manufacturing method of this invention is used, and a dispersion liquid is produced.

針對本發明的排放水處理方法進行具體說明。 舉例來說,亦可於排放水加入鹼,使排放水呈鹼性,使前述重金屬離子的至少一部分不溶解化,並在形成懸濁固形物的不溶解化步驟後,添加由本發明的製造方法所獲得之水淨化劑。再者,亦可在單獨添加胺等高分子凝集劑後,來添加由本發明的製造方法所獲得之水淨化劑。 較佳使用由本發明的製造方法所獲得之水淨化劑,製作分散液,並將此分散液供給至排放水。 藉由將分散液供給至排放水,則使無機系廢棄物凝集沉降,再藉由去除沉降分離之沉澱物,能夠淨化排放水。The discharged water treatment method of the present invention will be specifically described. For example, an alkali may be added to the discharged water to make the discharged water alkaline, so that at least a part of the heavy metal ions are not dissolved, and after the insolubilization step of forming a suspended solid, the manufacturing method of the present invention is added. The water purification agent obtained. Furthermore, the water-purifying agent obtained by the manufacturing method of this invention can also be added after polymer coagulant, such as amine, is added separately. It is preferable to use the water purifying agent obtained by the manufacturing method of the present invention to prepare a dispersion liquid, and supply the dispersion liquid to the discharged water. By supplying the dispersion liquid to the discharged water, the inorganic waste is aggregated and settled, and the precipitate separated and separated can be removed to purify the discharged water.

[實施例] 以下,雖然說明本發明的實施例,但本發明並不限定於此等實施例。[Examples] Hereinafter, although examples of the present invention will be described, the present invention is not limited to these examples.

(實施例1) 將硫酸鎳六水合物溶解於純水,並製作800g之含50mg/L鎳離子的水溶液,以作為實驗使用的排放水(假想排放水)。 接著,將氫氧化鈉供給至上述排放水使其pH值成為10,並攪拌使鎳不溶解化。該排放水的上層澄清液的鎳離子濃度為2mg/L。 <水淨化劑> 再者,使用「群馬縣前橋產 濃縮菠菜」作為植物,且使用聚丙烯醯胺(PAM)作為高分子凝集劑。藉由如下所示的製造方法獲得顆粒1,且將這種顆粒1作為水淨化劑1使用。(Example 1) Nickel sulfate hexahydrate was dissolved in pure water, and 800 g of an aqueous solution containing 50 mg / L of nickel ions was prepared as the discharge water (imaginary discharge water) used in the experiment. Next, sodium hydroxide was supplied to the above-mentioned discharged water so as to have a pH of 10, and the nickel was insolubilized by stirring. The nickel ion concentration of the supernatant liquid of the discharged water was 2 mg / L. <Water Purifying Agent> In addition, "concentrated spinach from Maebashi, Gunma Prefecture" was used as a plant, and polypropylene ammonium (PAM) was used as a polymer agglutinating agent. The granules 1 were obtained by the manufacturing method shown below, and such granules 1 were used as the water purification agent 1.

<<水淨化劑的製造方法>> 相對於植物粉末與高分子凝集劑合計之固體成分的質量,加入5倍質量的水而獲得混練物(植物粉末+高分子凝集劑+水 = 30kg),並將該混練物置入行星式混合器(愛工社製作所股份有限公司製,混合機ACM-110,容量110L),以轉速150rpm、20分鐘的混合條件施加剪應力進行混練。 將獲得之混練物成形,並製作成形體。 使用多階段熱風式乾燥機(七洋製作所股份有限公司製 機架式烘爐裝置)將該成形物,先以120℃、3小時的條件乾燥,再以150℃、2小時的條件乾燥。 接著使用氣流式超微粉碎機(增幸產業股份有限公司製 Ceren Miller)將乾燥後之薄片粉碎,使其中位徑為400μm。 再者,藉由mastersizer2000(Malvern Instrument製)測定中位徑。 使用分級機(Mikasa股份有限公司製 振動篩分機),並將其設定成僅讓粒徑在150μm~850μm範圍內之粉碎後的粉末過篩,粒徑小於150μm或粒徑超過850μm的顆粒自篩子取出並去除(篩除)。 如此一來,獲得顆粒1並作為水淨化劑1。<〈 Method of manufacturing water purification agent 〉> Add 5 times the mass of water to the mass of the solid content of the plant powder and the polymer aggregating agent to obtain a kneaded product (plant powder + polymer aggregating agent + water = 30kg). The kneaded product was placed in a planetary mixer (Mixer ACM-110 manufactured by Aiko Seisakusho Co., Ltd., with a capacity of 110 L), and kneaded by applying shear stress at a mixing speed of 150 rpm for 20 minutes. The obtained kneaded product is formed into a formed body. The formed article was dried using a multi-stage hot air dryer (a rack oven device manufactured by Chiyo Seisakusho Co., Ltd.) at 120 ° C for 3 hours, and then at 150 ° C for 2 hours. Next, the dried flakes were pulverized by using an air-flow type ultrafine pulverizer (Ceren Miller, manufactured by Masano Kogyo Co., Ltd.) to have a median diameter of 400 μm. The median diameter was measured with a mastersizer 2000 (manufactured by Malvern Instrument). Use a classifier (vibration sifter manufactured by Mikasa Co., Ltd.) and set it to sieved only the pulverized powder with a particle size in the range of 150 μm to 850 μm. Remove and remove (sieve out). In this way, the particles 1 are obtained and used as the water purification agent 1.

<分散液> 針對該顆粒,加入導電度110μS/cm的水(栃木縣鹿沼市自來水)並攪拌使固體成分成為0.1質量%,獲得分散液1。<Dispersion liquid> To the particles, water having a conductivity of 110 μS / cm (tap water in Kanuma City, Tochigi Prefecture) was added and stirred to obtain a solid content of 0.1% by mass, and a dispersion liquid 1 was obtained.

<特性評價> 接著,針對上述排放水添加含有水淨化劑1的分散液1,使固體成分成為7mg/L並攪拌。此處,「固體成分」的測定方法係可藉由使用水分計來計測排放水的泥漿濃度並反推出固體成分來求得的。 將添加了分散液1的排放水移送至沉澱槽,之後將其靜置,且每1小時以目視確認狀態。 將確認到明顯分成上層澄清液與沉澱物的兩層之時點測定為沉降時間。 又,取出上層澄清液並藉由Lambda(Λ)9000(共立理化學研究所製)測定離子濃度。 使用下述的基準來評價該結果的水淨化性能。 [水淨化性能的評價基準] ◎:小於1.0mg/L (檢測極限以下) ○:1.0mg/L以上且小於1.4mg/L ○△:1.4mg/L以上且小於1.7mg/L △:1.7mg/L以上且小於2.0mg/L ╳:2.0mg/L以上 將實施例1的評價結果顯示於表1-1。 又,表1-1中,亦顯示藉由B型黏度劑所測定之分散液黏度50(mPa‧sec)的結果。又,就由製造顆粒之過程中所獲得之混練物的硬度而言,亦根據上述方法,顯示在TA Instruments公司製的AR-G2硬度測定模式下的測定結果。 又,上述黏度測定係使用東機產業製TVC-7型黏度計(B型黏度計),於室溫23℃下,使用1號轉子測定的。 又,於表1-1中,植物粉末1係指「群馬縣前橋產 濃縮菠菜」、PAM係指聚丙烯醯胺(表1-2~表1-3、表2亦同)。<Characteristic evaluation> Next, the dispersion liquid 1 containing the water-purifying agent 1 was added to the said discharged water, and the solid content was 7 mg / L, and it stirred. Here, the measurement method of "solid content" can be calculated | required by measuring the density | concentration of the mud of discharged water using a moisture meter, and inferring a solid content. The discharged water to which the dispersion liquid 1 was added was transferred to a sedimentation tank, and thereafter it was left to stand, and the state was visually confirmed every 1 hour. The time at which a clear separation of the upper clear liquid and the precipitate into two layers was confirmed was determined as the settling time. The upper clear solution was taken out and the ion concentration was measured by Lambda (Λ) 9000 (manufactured by Kyoritsu Chemical Research Institute). The following criteria were used to evaluate the water purification performance of this result. [Evaluation criteria for water purification performance] ◎: less than 1.0 mg / L (below detection limit) ○: 1.0 mg / L or more and less than 1.4 mg / L ○ △: 1.4 mg / L or more and less than 1.7 mg / L △: 1.7 mg / L or more and less than 2.0 mg / L ╳: 2.0 mg / L or more The evaluation results of Example 1 are shown in Table 1-1. In addition, Table 1-1 also shows the results of the dispersion viscosity 50 (mPa · sec) measured by the B-type viscosity agent. In addition, the hardness of the kneaded material obtained in the process of producing the pellets also shows the measurement results in the AR-G2 hardness measurement mode made by TA Instruments in accordance with the method described above. In addition, the above-mentioned viscosity measurement was performed using a TVC-7 type viscometer (B-type viscometer) manufactured by Toki Sangyo Co., Ltd. at a room temperature of 23 ° C using a No. 1 spindle. In Table 1-1, plant powder 1 refers to "concentrated spinach from Maebashi, Gunma Prefecture", and PAM refers to polypropylene amide (Table 1-2 to Table 1-3, and Table 2 are the same).

(實施例2) 除了將實施例1使用的植物變更為長朔黃麻(中國‧廣州產)、混練步驟中混合器的轉速變更為80rpm以外,與實施例1相同地製作顆粒2。 使用由顆粒2而成的水淨化劑2,並與實施例1相同,對水淨化劑的特性進行評價。將實施例2的評價結果顯示於表1-1。又,表1-1中植物粉末2係指「長朔黃麻(中國‧廣州產)」。(Example 2) Granules 2 were produced in the same manner as in Example 1 except that the plant used in Example 1 was changed to Changshu Jute (made in China ‧ Guangzhou) and the rotation speed of the mixer in the kneading step was changed to 80 rpm. The characteristics of the water-purifying agent were evaluated in the same manner as in Example 1 using the water-purifying agent 2 composed of the particles 2. The evaluation results of Example 2 are shown in Table 1-1. The plant powder 2 in Table 1-1 refers to "Changshuo Jute (produced in Guangzhou, China)".

(實施例3) 作為實施例2植物的替代,使用研究長朔黃麻之中國農業科學院麻類研究所之鑑定編號2013的「中黃麻4號」。除此之外,與實施例2相同地製作顆粒3。 使用由顆粒3而成的水淨化劑3,並與實施例1相同,對水淨化劑的特性進行評價。將實施例3的評價結果顯示於表1-1。又,表1-1中植物粉末3係指「中黃麻4號」。(Example 3) As an alternative to the plant of Example 2, "Zhong Jute No. 4" which is the identification number of the Institute of Hemp Research of the Chinese Academy of Agricultural Sciences of Changshu Jute, was used. Except for this, particles 3 were produced in the same manner as in Example 2. The characteristics of the water-purifying agent were evaluated in the same manner as in Example 1 using the water-purifying agent 3 composed of the particles 3. The evaluation results of Example 3 are shown in Table 1-1. The plant powder 3 in Table 1-1 refers to "Medium Jute No. 4".

(實施例4) 除了將實施例3中相對於固體成分(高分子凝集+植物粉末)的加水量變更為3倍以外,與實施例3相同地製作顆粒4。 使用由顆粒4而成的水淨化劑4,並與實施例1相同,對水淨化劑的特性進行評價。將實施例4的評價結果顯示於表1-1。(Example 4) A granule 4 was produced in the same manner as in Example 3, except that the amount of water added to the solid content (polymer aggregation + plant powder) in Example 3 was changed to three times. The characteristics of the water-purifying agent were evaluated in the same manner as in Example 1 using the water-purifying agent 4 composed of the particles 4. The evaluation results of Example 4 are shown in Table 1-1.

(實施例5) 除了將實施例3中相對於固體成分(高分子凝集+植物粉末)的加水量變更為8倍以外,與實施例3相同地製作顆粒5。 使用由顆粒5而成的水淨化劑5,並與實施例1相同,對水淨化劑的特性進行評價。將實施例5的評價結果顯示於表1-1。(Example 5) A granule 5 was produced in the same manner as in Example 3, except that the amount of water added to the solid content (polymer aggregation + plant powder) in Example 3 was changed to 8 times. The characteristics of the water-purifying agent were evaluated in the same manner as in Example 1 using a water-purifying agent 5 made of particles 5. The evaluation results of Example 5 are shown in Table 1-1.

(實施例6) 除了將實施例3中混練步驟的混練時間變更為15分鐘以外,與實施例3相同地製作顆粒6。 使用由顆粒6而成的水淨化劑6,並與實施例1相同,對水淨化劑的特性進行評價。將實施例6的評價結果顯示於表1-2。(Example 6) A pellet 6 was produced in the same manner as in Example 3, except that the kneading time of the kneading step in Example 3 was changed to 15 minutes. The characteristics of the water-purifying agent were evaluated in the same manner as in Example 1 using the water-purifying agent 6 composed of the particles 6. The evaluation results of Example 6 are shown in Table 1-2.

(實施例7) 除了將實施例3中混練步驟的混練時間變更為30分鐘以外,與實施例3相同地製作顆粒7。 使用由顆粒7而成的水淨化劑7,並與實施例1相同,對水淨化劑的特性進行評價。將實施例7的評價結果顯示於表1-2。(Example 7) A pellet 7 was produced in the same manner as in Example 3, except that the kneading time of the kneading step in Example 3 was changed to 30 minutes. The characteristics of the water-purifying agent were evaluated in the same manner as in Example 1 using a water-purifying agent 7 made of particles 7. The evaluation results of Example 7 are shown in Table 1-2.

(實施例8) 除了將實施例3中作為分散液的水變更為使用導電度198μS/cm的水(栃木縣鹿沼市自來水)以外,與實施例3相同地製作顆粒8。 使用由顆粒8而成的水淨化劑8,並與實施例1相同,對水淨化劑的特性進行評價。將實施例8的評價結果顯示於表1-2。(Example 8) A pellet 8 was produced in the same manner as in Example 3, except that the water used as the dispersion liquid in Example 3 was changed to water having a conductivity of 198 μS / cm (tapuma city, Tochigi Prefecture). The characteristics of the water-purifying agent were evaluated in the same manner as in Example 1 using a water-purifying agent 8 made of particles 8. The evaluation results of Example 8 are shown in Table 1-2.

(實施例9) 除了將實施例3中作為分散液的水變更為使用栃木縣鹿沼市自來水與蒸餾水適量混合而獲得之導電度30μS/cm的水以外,與實施例3相同地製作顆粒9。 使用由顆粒9而成的水淨化劑9,並與實施例1相同,對水淨化劑的特性進行評價。將實施例9的評價結果顯示於表1-2。(Example 9) Granules 9 were produced in the same manner as in Example 3, except that the water used as the dispersion in Example 3 was changed to water having a conductivity of 30 μS / cm obtained by appropriately mixing tap water and distilled water in Kanuma City, Tochigi Prefecture. The characteristics of the water-purifying agent were evaluated in the same manner as in Example 1 using a water-purifying agent 9 made of particles 9. The evaluation results of Example 9 are shown in Table 1-2.

(實施例10) 除了不進行實施例3的分級步驟以外,與實施例3相同地製作顆粒10。 使用由顆粒10而成的水淨化劑10,並與實施例1相同,對水淨化劑的特性進行評價。將實施例10的評價結果顯示於表1-2。(Example 10) A pellet 10 was produced in the same manner as in Example 3 except that the classification step of Example 3 was not performed. The characteristics of the water-purifying agent were evaluated in the same manner as in Example 1 using a water-purifying agent 10 made of particles 10. The evaluation results of Example 10 are shown in Table 1-2.

(實施例11) 除了將實施例3的高分子凝集劑變更為聚胺以外,與實施例3相同地製作顆粒11。 使用由顆粒11而成的水淨化劑11,並與實施例1相同,對水淨化劑的特性進行評價。將實施例11的評價結果顯示於表1-2。(Example 11) A pellet 11 was produced in the same manner as in Example 3, except that the polymer coagulant of Example 3 was changed to polyamine. The characteristics of the water-purifying agent were evaluated in the same manner as in Example 1 using the water-purifying agent 11 composed of the particles 11. The evaluation results of Example 11 are shown in Table 1-2.

(實施例12) 將氟化鉀溶解於純水,並製作800g之含2,500mg/L氟離子的水溶液,以作為實驗使用的排放水(假想排放水)。 接著,添加氯化鈣8.6mg/L至上述排放水,且一邊添加氫氧化鈉使其pH值為7.5~9.0,並一邊攪拌使氟不溶解化。藉由此操作,使氟水溶液中包含微絮凝物(micro-flock)的上層澄清液與沉澱物分離。 於此時點,該排放水之上層澄清液的離子濃度為10mg/L。 除了使用上述排放水以外,與實施例3相同地,使用由顆粒3而成的水淨化劑3,並對水淨化劑的特性進行評價。將實施例12的評價結果顯示於表1-3。(Example 12) Potassium fluoride was dissolved in pure water, and 800 g of an aqueous solution containing 2,500 mg / L of fluoride ions was prepared as the discharge water (virtual discharge water) used in the experiment. Next, 8.6 mg / L of calcium chloride was added to the above-mentioned discharged water, and sodium hydroxide was added to adjust the pH to 7.5 to 9.0, and the fluorine was not dissolved while stirring. With this operation, the upper clear liquid containing micro-flock in the fluorine aqueous solution was separated from the precipitate. At this point, the ion concentration of the supernatant liquid of the discharged water was 10 mg / L. Except that the above-mentioned discharged water was used, as in Example 3, a water purification agent 3 made of particles 3 was used, and the characteristics of the water purification agent were evaluated. The evaluation results of Example 12 are shown in Tables 1-3.

(實施例13) 將氯化鐵六水合物溶解於純水,並製作800g之含200mg/L鐵離子的水溶液,以作為實驗使用的排放水(假想排放水)。 再者,一邊添加氫氧化鈉至上述排放水使其pH值為6.5~9.0,並一邊攪拌使鐵不溶解化。 於此時點,該排放水之上層澄清液的離子濃度為2mg/L。 除了使用上述排放水以外,與實施例3相同地,使用由顆粒3而成的水淨化劑3,並對水淨化劑的特性進行評價。將實施例13的評價結果顯示於表1-3。(Example 13) Ferric chloride hexahydrate was dissolved in pure water, and 800 g of an aqueous solution containing 200 mg / L of iron ions was prepared as the discharge water (imaginary discharge water) used in the experiment. Furthermore, while adding sodium hydroxide to the above-mentioned discharged water to a pH value of 6.5 to 9.0, the iron was not dissolved while stirring. At this point, the ion concentration of the supernatant liquid of the discharged water was 2 mg / L. Except that the above-mentioned discharged water was used, as in Example 3, a water purification agent 3 made of particles 3 was used, and the characteristics of the water purification agent were evaluated. The evaluation results of Example 13 are shown in Tables 1-3.

(實施例14) 將硫酸銅五水合物溶解於純水,並製作800g之含100mg/L銅離子的水溶液,以作為實驗使用的排放水(假想排放水)。 再者,一邊添加氫氧化鈉至排放水使其pH值為7.0~8.0,並一邊攪拌使銅不溶解化。 於此時點,該排放水之上層澄清液的離子濃度為2mg/L。 除了使用上述排放水以外,與實施例3相同地,使用由顆粒3而成的水淨化劑3,並對水淨化劑的特性進行評價。將實施例14的評價結果顯示於表1-3。(Example 14) Copper sulfate pentahydrate was dissolved in pure water, and 800 g of an aqueous solution containing 100 mg / L of copper ions was prepared as the discharge water (imaginary discharge water) used in the experiment. In addition, while adding sodium hydroxide to the discharged water so that the pH value was 7.0 to 8.0, the copper was not dissolved while stirring. At this point, the ion concentration of the supernatant liquid of the discharged water was 2 mg / L. Except that the above-mentioned discharged water was used, as in Example 3, a water purification agent 3 made of particles 3 was used, and the characteristics of the water purification agent were evaluated. The evaluation results of Example 14 are shown in Tables 1-3.

(實施例15) 將硝酸鋅六水合物溶解於純水,並製作800g之含100mg/L鋅離子的水溶液,以作為實驗使用的排放水(假想排放水)。 再者,一邊添加氫氧化鈉至排放水使其pH值為9.0~9.5,並一邊攪拌使鋅不溶解化。 於此時點,該排放水之上層澄清液的離子濃度為5mg/L。 除了使用上述排放水以外,與實施例3相同地,使用由顆粒3而成的水淨化劑3,並對水淨化劑的特性進行評價。將實施例15的評價結果顯示於表1-3。(Example 15) Zinc nitrate hexahydrate was dissolved in pure water, and 800 g of an aqueous solution containing 100 mg / L of zinc ions was prepared as the discharge water (imaginary discharge water) used in the experiment. In addition, while adding sodium hydroxide to the discharged water to have a pH of 9.0 to 9.5, the zinc was not dissolved while stirring. At this point, the ion concentration of the supernatant liquid of the discharged water was 5 mg / L. Except that the above-mentioned discharged water was used, as in Example 3, a water purification agent 3 made of particles 3 was used, and the characteristics of the water purification agent were evaluated. The evaluation results of Example 15 are shown in Tables 1-3.

(實施例16) 將重鉻酸鉀溶解於純水,並製作800g之含100mg/L鉻離子的水溶液,以作為實驗使用的排放水(假想排放水)。 再者,一邊添加氫氧化鈉至排放水使其pH值為6.0~7.5,並一邊攪拌使鉻不溶解化。 於此時點,該排放水之上層澄清液的離子濃度為5mg/L。 除了使用上述排放水以外,與實施例3相同地,使用由顆粒3而成的水淨化劑3,並對水淨化劑的特性進行評價。將實施例16的評價結果顯示於表1-3。(Example 16) Potassium dichromate was dissolved in pure water, and 800 g of an aqueous solution containing 100 mg / L of chromium ions was prepared as discharge water (imaginary discharge water) used in the experiment. In addition, while adding sodium hydroxide to the discharged water to a pH value of 6.0 to 7.5, the chromium was not dissolved while stirring. At this point, the ion concentration of the supernatant liquid of the discharged water was 5 mg / L. Except that the above-mentioned discharged water was used, as in Example 3, a water purification agent 3 made of particles 3 was used, and the characteristics of the water purification agent were evaluated. The evaluation results of Example 16 are shown in Tables 1-3.

(實施例17) 將三氧化二砷溶解於純水,並製作800g之含10mg/L砷離子的水溶液,以作為實驗使用的排放水(假想排放水)。 接著,添加氯化鐵65mg/L、氯化鈣354mg/L至排放水,接著,一邊添加氫氧化鈉使其pH值為8.0~9.5,並一邊攪拌使砷不溶解化。 於此時點,該排放水之上層澄清液的離子濃度為0.05mg/L。 除了使用上述排放水以外,與實施例3相同地,使用由顆粒3而成的水淨化劑3,並對水淨化劑的特性進行評價。將實施例17的評價結果顯示於表1-3。 然而,實施例17係在與實施例3相同地測定沉降時間後,更包含取出上層澄清液且藉由蒸發器將其體積濃縮至1/100,並測定離子濃度。就砷離子而言,若判斷離子濃度為0.01mg/L以下之較佳結果,則將該結果評價為◎。(Example 17) Arsenic trioxide was dissolved in pure water, and 800 g of an aqueous solution containing 10 mg / L of arsenic ions was prepared as the discharge water (virtual discharge water) used in the experiment. Next, 65 mg / L of ferric chloride and 354 mg / L of calcium chloride were added to the discharged water, and then sodium hydroxide was added to adjust the pH to 8.0 to 9.5, and arsenic was not dissolved while stirring. At this point, the ion concentration of the supernatant liquid of the discharged water was 0.05 mg / L. Except that the above-mentioned discharged water was used, as in Example 3, a water purification agent 3 made of particles 3 was used, and the characteristics of the water purification agent were evaluated. The evaluation results of Example 17 are shown in Tables 1-3. However, in Example 17, after the sedimentation time was measured in the same manner as in Example 3, the upper clear liquid was taken out, and its volume was concentrated to 1/100 by an evaporator, and the ion concentration was measured. As for the arsenic ion, if it is judged that the preferable result of the ion concentration is 0.01 mg / L or less, the result is evaluated as ◎.

[表1-1] [Table 1-1]

[表1-2] [Table 1-2]

[表1-3] [Table 1-3]

(實施例18) 針對實施例3、4及5所獲得之水淨化劑3、4及5,亦各自以與實施例3、4及5相同的方法,進行將分散液的水替換成導電度1μS/cm的水(蒸餾水)時水淨化劑的特性評價。 將蒸餾水作為水淨化劑3、4及5之分散液的水時的評價結果、與在上述實施例3、4及5所進行之將導電度110μS/cm的水(栃木縣鹿沼市自來水)作為分散液使用時的評價結果,一併顯示於表2。(Example 18) The water purification agents 3, 4 and 5 obtained in Examples 3, 4 and 5 were each replaced with the conductivity of the dispersion liquid by the same method as in Examples 3, 4 and 5. Evaluation of the characteristics of a water purifying agent in 1 μS / cm water (distilled water). Evaluation results when distilled water was used as the water of the dispersions of the water purifying agents 3, 4 and 5 and water with a conductivity of 110 μS / cm (tap water in Kanuma City, Tochigi Prefecture) were used as in Examples 3, 4 and 5 described above. The evaluation results at the time of use of the dispersion liquid are also shown in Table 2.

(比較例1~2) 在實施例3中,除了將相對於固體成分(高分子凝集體+植物粉末)的加水量變更成0.8倍及9倍以外,與實施例3相同地製作比較顆粒1~2。 使用由比較顆粒1~2而成的比較水淨化劑1~2,並與實施例3及實施例18相同,針對使用導電度110μS/cm的水(栃木縣鹿沼市自來水)作為分散液時、以及針對使用導電度1μS/cm的蒸餾水作為分散液時,排放水的水淨化性能進行評價。將比較例1~2的評價結果顯示於表2。 又,相對於比較例1所使用之比較顆粒1,雖然亦欲針對在製造過程所獲得之混練物,以與實施例1相同的方法來測定該混練物的硬度,但因為該混練物沒有黏性,四分五裂地崩解且沒有成塊,故無法以硬度計測定。(Comparative Examples 1 to 2) In Example 3, Comparative Particles 1 were produced in the same manner as in Example 3, except that the amount of water added to the solid content (polymer aggregate + plant powder) was changed to 0.8 and 9 times. ~ 2. When using Comparative Water Purification Agents 1 to 2 made of Comparative Particles 1 to 2 and the same as those in Examples 3 and 18, when using water with a conductivity of 110 μS / cm (Takanuma City, Tochigi Prefecture) as the dispersion, And when using distilled water having a conductivity of 1 μS / cm as the dispersion liquid, the water purification performance of the discharged water was evaluated. The evaluation results of Comparative Examples 1 to 2 are shown in Table 2. In addition, compared with the comparative particle 1 used in Comparative Example 1, although it is also intended to measure the hardness of the mixed material obtained in the manufacturing process by the same method as in Example 1, it is because the mixed material is not sticky. It is disintegrated and has no lumps, so it cannot be measured with a hardness meter.

[表2] [Table 2]

(實施例19) 使用如同實施例3的分散液,進行30次在實施例3中之評價排放水淨化性能的實驗。 另一方面,使用在實施例3所獲得之水淨化劑3,而不使用分散液,藉由將該水淨化劑3直接投入上述排水,並進行30次評價排放水淨化性能的實驗。相對於排放水,水淨化劑3的添加量係使固體成分成為7mg/L的量。 針對各實驗結果評價淨化性能的變動性。 於使用分散液的情況下,係為◎的結果,且確認到每次都能夠獲得變動少的淨化結果。 另一方面,將水淨化劑直接投入排放水時,雖然也有顯示為◎的良好結果之情形,不過也有未顯示為相同結果的情形(有○或○△之結果的情形),但因為是用同樣的方法進行實驗,故實驗結果具有變動性。(Example 19) Using the dispersion liquid similar to Example 3, an experiment for evaluating discharge water purification performance in Example 3 was performed 30 times. On the other hand, the water purifying agent 3 obtained in Example 3 was used instead of the dispersion liquid, and the water purifying agent 3 was directly put into the above-mentioned drainage, and an experiment for evaluating the purification performance of the discharged water was performed 30 times. The amount of the water purifying agent 3 added to the discharged water was such that the solid content was 7 mg / L. The variability of the purification performance was evaluated for each experimental result. When a dispersion liquid was used, it was a result of 且, and it was confirmed that a purification result with less fluctuation can be obtained every time. On the other hand, when the water purification agent is directly injected into the discharged water, although a good result may be displayed as ◎, there are also cases where the same result is not displayed (a case where there is a result of ○ or ○ △), but because it is used Experiments are performed in the same way, so the experimental results are variable.

(實施例20) 除了將實施例3中的混練步驟變更為如以下所示以外,與實施例3相同地製造顆粒20。 使用由顆粒20而成的水淨化劑20,並與實施例3相同,對水淨化劑的特性進行評價。 <混練步驟> 將下述表3所示之量的水添加至高分子凝集劑,並混練高分子凝集劑與水10分鐘。之後,將植物粉末混合至混練後之高分子凝集劑,並混練植物粉末與高分子凝集劑10分鐘。 又,使用以上述方法獲得之水淨化劑20,並如實施例18所示,評價將分散液的水變更成導電度為1μS/cm的水(蒸餾水)時水淨化劑的特性。 將使用水淨化劑20的評價結果顯示於表3。(Example 20) A pellet 20 was produced in the same manner as in Example 3, except that the kneading step in Example 3 was changed as shown below. The characteristics of the water-purifying agent were evaluated in the same manner as in Example 3 using a water-purifying agent 20 made of particles 20. <Kneading step> Water of the amount shown in Table 3 below was added to the polymer coagulant, and the polymer coagulant and water were kneaded for 10 minutes. After that, the plant powder is mixed to the polymer agglutinating agent after kneading, and the plant powder and the polymer agglutinating agent are kneaded for 10 minutes. Further, the water purifying agent 20 obtained by the above method was used, and as shown in Example 18, the characteristics of the water purifying agent when the water of the dispersion liquid was changed to water (distilled water) having a conductivity of 1 μS / cm were evaluated. The evaluation result using the water purification agent 20 is shown in Table 3.

(實施例21~23) 除了將水淨化劑20變更成下述表3所示之條件以外,以同樣的方法製作水淨化劑21~23。 在實施例20中,除了將水淨化劑20變更為水淨化劑21~23以外,藉由同樣的方法,評價水淨化劑的特性(實施例21~23)。(Examples 21 to 23) Water purification agents 21 to 23 were produced in the same manner except that the water purification agent 20 was changed to the conditions shown in Table 3 below. In Example 20, the characteristics of the water purification agent were evaluated by the same method except that the water purification agent 20 was changed to the water purification agents 21 to 23 (Examples 21 to 23).

[表3] [table 3]

綜上,從實施例1~23的結果來看,能夠確認到藉由本發明的製造方法所製造之水淨化劑係能夠適用於排放水槽的尺寸為用於大的自動化淨化裝置時的水淨化劑,並其係低成本且每次都不變動地顯示穩定的淨化性能。In summary, from the results of Examples 1 to 23, it can be confirmed that the water purifying agent manufactured by the manufacturing method of the present invention can be applied to a water purifying agent having a size of a drain tank for use in a large automated purification device. And it is a low cost and shows stable purification performance without change every time.

no

Claims (13)

一種水淨化劑的製造方法,其係製造由包含植物粉末與高分子凝集劑的顆粒而成之水淨化劑的製造方法,其係包含: 混練步驟,將植物粉末與高分子凝集劑混練;其中, 在前述混練步驟中,經由前述混練步驟而得之混練物的硬度係以在下述測定條件中使其應力顯示為3N/mm2 ~100N/mm2 的方式,來混練植物粉末與高分子凝集劑; 測定條件:針對前述混練物,使用應力控制型流變儀(黏度測定裝置),測定在押入速度為30mm/min下,押入直徑16mm的探針時,押入量為5mm時的應力。A method for manufacturing a water purifying agent, which is a method for manufacturing a water purifying agent made of particles containing a plant powder and a polymer agglutinating agent, comprising: a kneading step, kneading a plant powder and a polymer agglutinating agent; In the aforementioned kneading step, the hardness of the kneaded material obtained through the aforementioned kneading step is to knead the plant powder and the polymer agglutination in such a manner that the stress is displayed as 3N / mm 2 to 100N / mm 2 under the following measurement conditions. Measurement conditions: For the aforementioned kneaded material, a stress-controlled rheometer (viscosity measuring device) was used to measure the stress at a pushing speed of 30 mm / min and a probe with a diameter of 16 mm when the pushing amount was 5 mm. 如請求項1所述之水淨化劑的製造方法,其中,符合下述(a1)、下述(a2)、及下述(b)中任一者: (a1):第一混練步驟,將水混合至前述高分子凝集劑,以混練前述高分子凝集劑與水;之後,進行第二混練步驟,將前述植物粉末混合至經混練的前述高分子凝集劑,以混練前述植物粉末與高分子凝集劑;其中,在前述第一混練步驟中,相對於前述水淨化劑中的固體成分(質量),水混合的合計量(質量)係1.5倍至8倍; (a2):第一混練步驟,將水混合至前述高分子凝集劑,以混練前述高分子凝集劑與水;之後,進行第二混練步驟,將前述植物粉末與水混合至經混練的前述高分子凝集劑,以混練前述植物粉末與高分子凝集劑;其中,在前述第一混練步驟及前述第二混練步驟中,相對於前述水淨化劑中的固體成分(質量),水混合的合計量(質量)係1.5倍至8倍;及 (b):混練步驟,將植物粉末與高分子凝集劑及水混合,以混練之;其中,在前述混練步驟中,相對於前述水淨化劑中的固體成分(質量),水混合的合計量(質量)係1.5倍至8倍。The method for producing a water purifying agent according to claim 1, which conforms to any one of the following (a1), (a2), and (b): (a1): a first kneading step, Water is mixed with the polymer agglutinant to knead the polymer agglutinant and water; and then, a second kneading step is performed to mix the plant powder to the kneaded polymer agglutinant to knead the plant powder and polymer Agglutinating agent; wherein, in the first kneading step, the total amount (mass) of water mixing is 1.5 to 8 times the solid content (mass) in the water purifying agent; (a2): the first kneading step , Mixing water to the polymer agglutinating agent to knead the polymer agglutinating agent and water; and then, performing a second kneading step, mixing the plant powder and water to the kneaded polymer agglutinating agent to knead the plant Powder and polymer coagulant; wherein, in the first kneading step and the second kneading step, the total amount (mass) of water mixing with respect to the solid content (mass) in the water purifying agent; 1.5 times to 8 times; and (b): a kneading step in which the plant powder is mixed with a polymer coagulant and water to knead it; wherein, in the kneading step, compared with the solid component in the water purifying agent ( Mass), the total amount (mass) of water mixing is 1.5 to 8 times. 如請求項1所述之水淨化劑的製造方法,其係包含:第一混練步驟,將水混合至前述高分子凝集劑,以混練前述高分子凝集劑與水;之後,進行第二混練步驟,將前述植物粉末混合至經混練的前述高分子凝集劑,以混練前述植物粉末與高分子凝集劑。The method for manufacturing a water purifying agent according to claim 1, comprising: a first kneading step, mixing water to the polymer agglutinating agent to knead the polymer agglutinating agent and water; and then performing a second kneading step , Mixing the plant powder to the kneaded polymer coagulant to knead the plant powder and polymer coagulant. 如請求項1所述之水淨化劑的製造方法,其中,在轉速80rpm~150rpm的條件下,前述混練時之混練時間的合計數值為15分鐘以上且30分鐘以內。The method for producing a water purifying agent according to claim 1, wherein the total value of the kneading time during the kneading is 15 minutes or more and 30 minutes or less under the condition of a rotation speed of 80 rpm to 150 rpm. 如請求項1所述之水淨化劑的製造方法,其中,前述植物粉末係選自長朔黃麻、黃麻菜、小松菜、鴨兒芹、日本蕪菁及波菜所組成之群中任一者。The method for producing a water purifying agent according to claim 1, wherein the plant powder is any one selected from the group consisting of Changshuo jute, jute, komatsu, duck celery, Japanese turnip, and seaweed. 如請求項5所述之水淨化劑的製造方法,其中,前述植物粉末係長朔黃麻。The method for producing a water purifying agent according to claim 5, wherein the plant powder is Changshuo jute. 如請求項6所述之水淨化劑的製造方法,其中,前述長朔黃麻係中國農業科學院麻類研究所之鑑定編號2013的「中黃麻4號」。The method for manufacturing a water purifying agent according to claim 6, wherein the aforementioned Changshu jute is an identification number 2013 "Zhong jute 4" of the Institute of Hemp Research of the Chinese Academy of Agricultural Sciences. 如請求項1所述之水淨化劑的製造方法,其中,前述水淨化劑的中位徑為150μm以上且850μm以下。The method for producing a water purification agent according to claim 1, wherein a median diameter of the water purification agent is 150 μm or more and 850 μm or less. 如請求項1所述之水淨化劑的製造方法,其中,該高分子凝集劑係聚丙烯醯胺。The method for producing a water purification agent according to claim 1, wherein the polymer agglutinating agent is polypropylene amidamide. 如請求項1所述之水淨化劑的製造方法,其係包含: 成形步驟,形成經由前述混練步驟所獲得之成形有混練物的成形體; 乾燥步驟,將前述成形體乾燥;及 粉碎步驟,將乾燥後之成形體粉碎。The method for producing a water purifying agent according to claim 1, comprising: a forming step of forming a formed body having a kneaded body obtained through the aforementioned kneading step; a drying step of drying the formed body; and a pulverizing step, The dried compact was pulverized. 一種排放水處理方法,其係將藉由如請求項1~10中任一項所載之水淨化劑的製造方法所獲得之水淨化劑溶解於水,進而獲得包含植物粉末與高分子凝集劑的分散液,接著藉由將該分散液供給至含有無機系廢棄物的排放水,以去除排放水中的無機系廢棄物。A method for treating discharged water, which comprises dissolving a water purifying agent obtained by the method for manufacturing a water purifying agent as set forth in any one of claims 1 to 10 in water, thereby obtaining a plant powder and a polymer agglutinating agent. The dispersion liquid is then supplied to the discharged water containing the inorganic waste to remove the inorganic waste from the discharged water. 如請求項11所述之排放水處理方法,其中,前述排放水係具有選自鎳、氟、鐵、銅、鋅、鉻、砷、鎘及鉛所組成之群中至少一種的無機系廢棄物。The method for treating discharged water according to claim 11, wherein the discharged water is an inorganic waste having at least one selected from the group consisting of nickel, fluorine, iron, copper, zinc, chromium, arsenic, cadmium, and lead. . 如請求項11所述之排放水處理方法,其中,前述分散液中水的導電度為30μS/cm以上。The method for treating discharged water according to claim 11, wherein the conductivity of water in the dispersion liquid is 30 μS / cm or more.
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