TWI746638B - 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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TWI746638B
TWI746638B TW106131604A TW106131604A TWI746638B TW I746638 B TWI746638 B TW I746638B TW 106131604 A TW106131604 A TW 106131604A TW 106131604 A TW106131604 A TW 106131604A TW I746638 B TWI746638 B TW I746638B
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water
polymer flocculant
purifying agent
plant powder
aforementioned
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TW201822861A (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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  • 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

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Description

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

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-derived water purification agent used for water purification of industrial discharge water and the like, and a discharge water treatment method 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 number of waste liquids containing environmentally hazardous substances such as metal ions or fluoride ions have been generated. On the other hand, the emission regulations for these inorganic ions have gradually become stricter. In order to comply with these emission regulations, the present inventors seek a method for removing inorganic ions that can efficiently remove inorganic ions from the discharged water containing inorganic ions and implement it in a simple and low-cost manner as much as possible. As far as methods for removing impurity particles such as water discharged from factories are concerned, some people have proposed agglomeration precipitation method, ion exchange method, adsorption method using adsorbents such as activated carbon, electrosorption method, and magnetic adsorption method.

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, with regard to the agglomeration precipitation method, a method has been proposed, which includes: adding alkali to the discharged water in which heavy metal ions are dissolved, and making the discharged water alkaline, and then insolubilizing at least a part of the heavy metal ions , And then the step of forming a suspended solid; adding an inorganic flocculant to the discharged water to make the suspended solid coagulate and settle; and let the discharged water pass through leafy vegetables such as jute (mulukhiya) and komatsuna (komatsuna) The adsorption step of the adsorption layer of the cation exchanger (for example, refer to Patent Document 1). At the same time, some people have also proposed an agglutination method, which is to mix or use a polymer flocculant with a flocculant containing at least any one of jute cabbage, its dried product, or its extract, and then aggregate the fine particles in the 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 increases, the amount of unnecessary substances contained in the discharged water increases, or the types of unnecessary substances contained in the discharged water increase, it is desirable to construct a type of discharged water. A system that automatically puts the necessary purifying agent in the purification process. In addition to performing high-speed and stable purification processing, the automation of the device is an important issue, and in addition to providing an automatic purification device exhibiting stable purification performance, it is also desired to provide a water purifier suitable for the automatic purification device. However, the methods described in Patent Document 1 and Patent Document 2 are completely unaware of automated devices for purifying wastewater, and the water purifiers described in these documents are not suitable for supplying to automated system devices. Therefore, a water purifying agent made of particles containing a mixture of plant powder and a polymer flocculant has been proposed as a water purifying agent that can be suitably used in an automated 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 Document] [Patent Document] [Patent Document 1] Japanese Patent Application Publication No. 2011-194385 [Patent Document 2] Japanese Patent Application Publication No. 11-114313 [Patent Document 3] Japanese Patent Application Publication 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。[Problem to be solved by the invention] However, when the automatic purification device is enlarged, 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. As far as purification performance is concerned, we understand that the water purification agent described in Patent Document 3 is insufficient. Therefore, the present inventors desire to provide a water purifier, which can also be applied to a water purifier when the size of a drain tank is used in a large automatic purification device, and which is low-cost and stable with no change every 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 multiple problems in the past, and aims to achieve the following objects as a subject. That is, the object of the present invention is to provide a water purifier, which can also be applied to the water purifier when the size of the discharge water tank is used in a large automatic purification device, and it is low-cost and can display unchanged every time The 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 made of particles containing plant powder and a polymer flocculant, which includes: a kneading step, mixing plant powder with high Molecular coagulant kneading; wherein, in the aforementioned kneading step, the hardness of the kneaded product obtained through the aforementioned kneading step is kneaded so that the stress is 3N/mm 2 ~ 100N/mm 2 under the following measurement conditions Plant powder and polymer agglutinant; Measurement conditions: For the aforementioned kneaded material, use a stress-controlled rheometer (viscosity measuring device) to measure when a probe with a diameter of 16mm is pushed in at a speed of 30mm/min, and the amount is pushed into Stress at 5mm. <2> The method for producing a water purifying agent as described in the above <1>, which meets any one of the following (a1), the following (a2), and the following (b): (a1): First In the kneading step, water is mixed with the polymer flocculant to knead the polymer flocculant and water; after that, the second kneading step is performed to mix the plant powder with the kneaded polymer flocculant to knead the plant Powder and polymer flocculant; wherein, in the first kneading step, the total amount (mass) of water mixing relative to the solid content (mass) in the water purifying agent is 1.5 to 8 times; (a2): In the first kneading step, water is mixed with the polymer flocculant to knead the polymer flocculant and water; after that, the second kneading step is performed to mix the plant powder and water to the kneaded polymer flocculant, The plant powder and the polymer flocculant are kneaded; wherein, in the first kneading step and the second kneading step, the total amount (mass) of the water mixed with respect to the solid content (mass) in the water purifying agent is 1.5 times to 8 times; and (b): mixing step, mixing plant powder with polymer flocculant and water to knead them; wherein, in the aforementioned mixing step, relative to the solid content (mass ), the total amount (mass) of water mixing is 1.5 to 8 times. <3> The method for producing a water purifier as described in the above <1>, which includes: a first kneading step, mixing water with the polymer flocculant to knead the polymer flocculant and water; In the second kneading step, the plant powder is mixed with the kneaded polymer flocculant to knead the plant powder and the polymer flocculant. <4> The method for producing a water purifier as described in any one of the above <1> to <3>, wherein the total value of the kneading time at the time of 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 as described in any one of the aforementioned <1> to <4>, wherein the plant powder is selected from changshuohuangma, jute, small pine cabbage, and celery , Japanese turnip and any one of the group consisting of Bocai. <6> The method for producing a water purifying agent as described in the above <5>, wherein the plant powder is Changshuo jute. <7> The manufacturing method of the water purifier as described in the above <6>, wherein the Changshuo jute is "Zhonghuang Ma No. 4" under the identification number 2013 of the Bast Fiber Research Institute of the Chinese Academy of Agricultural Sciences. <8> The method for producing a water purifying agent according to any one of the aforementioned <1> to <7>, wherein the median diameter of the water purifying agent is 150 μm or more. <9> The method for producing a water purifying agent according to any one of the aforementioned <1> to <8>, wherein the polymer flocculant is polyacrylamide. <10> The method for producing a water purifying agent as described in any one of the aforementioned <1> to <9>, which comprises: a forming step, forming a molded body with a kneaded product obtained through the aforementioned kneading step; drying Step, drying the aforementioned shaped body; and pulverizing step, pulverizing the dried shaped body. <11> A discharge water treatment method, which is to dissolve the water purifier obtained by the method of manufacturing the water purifier described in any one of the above <1> to <10> in water to obtain a plant powder and high The dispersion liquid of the molecular coagulant is then supplied to the discharged water containing the inorganic waste to remove the inorganic waste in the discharged water. <12> The discharged water treatment method as described in the aforementioned <11>, wherein the discharged water system has at least one selected from the group consisting of nickel, fluorine, iron, copper, zinc, chromium, arsenic, cadmium, and lead Inorganic waste. <13> The discharge water treatment method described in the above <11> or <12>, wherein the conductivity of the 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, it is possible to solve multiple problems in the past and achieve the aforementioned objects, and to provide a water purifier, which can also be applied to the size of a discharge tank for use in a large automated purification device The water purifier is low-cost and can show 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 purifying agent) The water purifying agent manufactured by the manufacturing method of the water purifying agent of the present invention (hereinafter also referred to as the manufacturing method of the present invention) is made of particles containing plant powder and a polymer coagulant. The manufacturing method of the present invention includes a kneading step of kneading a plant powder and a polymer flocculant, and, if necessary, includes other steps such as a forming step, a drying step, and a crushing step. The manufacturing method of the present invention is characterized in that, in the aforementioned kneading step, the hardness of the kneaded product obtained through the aforementioned kneading step is such that the stress is 3N/mm 2 to 100 N/mm 2 under the following measurement conditions. , To mix plant powder and polymer flocculant. Measurement conditions: For the aforementioned mixture, use a stress-controlled rheometer (viscosity measuring device) to measure the stress when a probe with a diameter of 16 mm is pushed in at a speed of 30 mm/min, and the amount of pressure is 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 obtaining the above-mentioned kneaded product with the desired hardness, the following manufacturing method is more preferable. The production method of the present invention defines the total amount (mass) of water mixing when kneading the polymer flocculant and water, or when kneading the plant powder and the polymer flocculant. The total amount (mass) of the water mixing relative to the solid content (mass) in the aforementioned water purification agent is 1.5 to 8 times. In addition, the production method of the present invention defines a kneading step of mixing water with a polymer flocculant and kneading the polymer flocculant and water before the kneading step of kneading the plant powder and the polymer flocculant. The water purifier system manufactured by the manufacturing method of the present invention that satisfies the above requirements can be applied to the water purifier when the size of the drain tank is used in a large automatic purification device, and it is low-cost and can display unchanged every time Water purifier 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 purifier is used to purify the discharged water, the method of adding the water purifier can include the method of directly adding the discharged water to the water purifier, and the method of first dissolving the water purifier in water to obtain plant powder and A method of dispersing the polymer flocculant into the drain water, etc. However, if the automatic purification device is enlarged, especially when the size of the drain tank becomes larger, in the case of a granular water purifier, it will form a stable and uniform dispersion state every time and maintain constant water purification performance. , This system becomes difficult. Therefore, in an automated purification device in which the size of the drain water tank is large, it becomes necessary to use a purification method of the drain water using a dispersion liquid. Therefore, the inventors of the present invention conducted repeated studies on the purification treatment of the discharged water using the dispersion, and found that the viscosity of the dispersion changes when the plant powder and the polymer flocculant are dissolved according to the type of water in the dispersion. Next, the inventors obtained the following insights: the difference in the viscosity of the dispersion liquid will affect the purification performance of the discharged water, and in order to obtain good purification performance, it is effective to increase the viscosity of the dispersion liquid to some extent. Specifically, although tap water and underground water systems are typically cheaper, when using water with high conductivity due to the influence of ions contained in it to obtain a dispersion, if the dispersion is added to the drain water , The viscosity of the discharged water decreases, and solid components such as plant powders settle in a short time. As a result, sufficient inorganic ion adsorption performance cannot be obtained. On the other hand, as an alternative to tap water and groundwater, if distilled water with low conductivity is used, such problems will not occur. However, distilled water is expensive, and its cost becomes a huge burden in semiconductor factories and electroplating factories that process a large amount of discharged water every day. Therefore, when the present inventors conducted further research, they found a water purifier that 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 relatively inexpensive, as a dispersion. The concentration is lower than the concentration.

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 present inventors realized that even the dispersion of tap water and groundwater can increase its viscosity. This is due to the adjustment of kneaded plant powder and polymer flocculant in the production method of the water purifier. The hardness of the obtained mixture is effective. Here, the hardness of the kneaded product can be obtained using the AR-G2 hardness measurement mode manufactured by TA Instruments, which is a stress control type rheometer (viscosity measuring device). Specifically, approximately 7.5 g of the kneaded material is filled in a polypropylene cylindrical container with an inner diameter of 22 mm in diameter and 11 mm in depth, and a probe with a diameter of 16 mm is used to measure when it is pushed at a pushing speed of 30 mm/min. The stress when the pushing amount is 5mm. In the present invention, the stress measured under this condition is called "hardness". As a result, the hardness of the kneaded product is preferably in the range of 3N/mm 2 to 100 N/mm 2 . Next, the present inventors discovered that in order to obtain the desired hardness of the kneaded product, it is important to perform the steps shown in (i) or (ii) below. (I) In the method of manufacturing a water purifier, when a polymer flocculant and water are kneaded, or when a plant powder and a polymer flocculant are kneaded, relative to the solid content (mass) in the water purifier, the water is mixed The total amount (quality) is 1.5 times to 8 times. (Ii) In the method of manufacturing the water purifier, before the kneading step of kneading the plant powder and the polymer flocculant, a kneading step of mixing water with the polymer flocculant and kneading the polymer flocculant 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 a step of adding a large amount of water to the polymer flocculant and kneading is performed, or a step of kneading the polymer flocculant and water in advance is performed before kneading with the plant powder, a kneaded product with the desired hardness can be formed. In addition, the water purifier produced by such a mixture can increase the viscosity of the dispersion in which the water purifier is dispersed, and increase the viscosity of the discharged water after the dispersion is injected. Although the reason is not clear, it can be considered as follows: Under these conditions, whether the agglutination of the molecular chains of the polymer flocculant is solved to some extent by kneading and the improvement of its solubility with water is done. 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。Hereinafter, the specific structure of the water purifying agent manufacturing method is divided into (A) the first aspect and (B) the second aspect, and the detailed description will be given.

<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; The first aspect of the method of producing a water purifier> In the method of producing the water purifier, when the polymer flocculant and water are kneaded, or when the plant powder and the polymer flocculant are kneaded, relative to the water The total amount (mass) of the solid content (mass) in the purifier is 1.5 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 step of plant powder and polymer flocculant>> Although the production method of the aforementioned water purifying agent includes the step of kneading the plant powder and the polymer flocculant, the kneading step specifically includes, for example, the following The steps defined in (a1), (a2) and (b) can be listed in the following three aspects (a1), (a2) and (b). (A1): In the first mixing step, water is mixed with the polymer flocculant to knead the polymer flocculant and water; after that, the second mixing step is performed to mix the plant powder into the kneaded polymer flocculant, To knead the aforementioned plant powder and polymer flocculant. In the above (a1), when the plant powder and the polymer flocculant are kneaded, water may be mixed. In this case, it becomes the following (a2). (A2): In the first mixing step, water is mixed with the polymer flocculant to knead the polymer flocculant and water; after that, the second mixing step is performed to mix the plant powder and water until the kneaded polymer agglomerates Agent to knead the aforementioned plant powder and polymer flocculant. (B): Mixing step, mixing plant powder with polymer flocculant and water for mixing.

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。In terms of the total amount (mass) of the aforementioned water mixing, in the above (a1), it is called the amount of water mixed in the first kneading step; in the above (a2), it is called the The amount of water mixed in the first kneading step and the amount of water mixed in the second kneading step, the total amount of the two; in the above (b), it is said to be in the kneading step of plant powder and polymer flocculant , The amount of water mixed together when the plant powder and the polymer flocculant are mixed. The total amount (mass) of water mixing is preferably 1.5 times to 8 times relative to the solid content (mass) in the water purifier. Also, in the case of (a2) above, although the total amount of water mixed during the first kneading and the second kneading may be 1.5 to 8 times, the amount of water during the first kneading is relative to the solid content (mass) described above. The mixing amount is preferably at least 1 time or more. In addition, although the solid content in the above water purifier refers to the combination of plant powder and polymer flocculant, if the water purifier also includes the following other than plant powder and polymer flocculant In the case of additives, the solid content in the water purification agent also includes these additives, and the solid content in the water purification agent refers to the combination of all solid components in the water purification 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。The mixing method 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 mixing machine that can obtain a certain mixing effect, it can be selected. 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。Regarding the rotation speed of the kneader at the time of kneading, it is preferable to perform, for example, in the range of 10 rpm to 180 rpm. Also, for example, under the condition of the rotation speed of 80 rpm to 150 rpm, the total value of the kneading time at the time of kneading is preferably 15 minutes or more and 30 minutes or less. If it is less than 15 minutes, the effect of increasing the viscosity when supplied to the drain water is insufficient. In addition, if it exceeds 30 minutes, the effect of increasing the viscosity when supplied to the drain water also becomes insufficient. If the mixing time is too long, it may be considered that the molecular chain of the polymer flocculant 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 for the aforementioned plants, any plant that can agglutinate and separate wastes (nickel, copper, fluorine, etc.) in the discharged water is not particularly limited and can be used. For example, for plants having a cation exchange function, for example, changshuohuangma (changshuohuangma), jute (molokheiya), Komatsu cabbage, duck parsley, Japanese turnip, and bok choy are mentioned. Regarding the part of the plant, a part of any one of leaves, stems, and roots can be used. Among the plants, Changshuo jute and jute vegetable are preferred, and more preferably, 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, Changshuo Jute Zhongtejia is "Zhonghuang Ma No. 4" under the identification number 2013 of the Bast Fiber Research Institute of the Chinese Academy of Agricultural Sciences. "Zhonghuang Ma No. 4" has the following characteristics: Type of crop: 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 flocculant>> The polymer flocculant is the same as the above-mentioned plant part, and it is not particularly limited as long as it has the effect of removing the aforementioned inorganic waste in the discharged water. Examples include polyacrylamide (PAM), partially hydrolyzed salt of polyacrylamide, sodium alginate, sodium polyacrylate, sodium carboxymethyl cellulose (CMC, Carboxymethyl Cellulose) and the like. Among these, it is preferable to use polyacrylamide. For this polyacrylamide, for example, commercially available products Flopan AN 995SH, FA 920SH, FO 4490, AN 923, AN 956 (manufactured by SNF Co., Ltd.), etc. 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 purifying agent. In addition, for the purpose of improving the solubility of the kneading component and water, a small amount of liquid such as alcohol may be contained. In addition, other additives may be added when the polymer flocculant is kneaded, or other additives may be added when the plant powder and the polymer flocculant 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 flocculant>> The mixing ratio of the plant powder particles and the polymer flocculant is preferably in the range of 10:90 to 90:10 by mass ratio. On the surface of the particles obtained by kneading the aforementioned plant powder and the aforementioned polymer flocculant, it is preferable to include a covered part of the plant powder present on the particle surface covered by the polymer flocculant, and a non-coated part that is not covered by the polymer flocculant. part. The median diameter of the aforementioned particles is preferably 150 μm or more, more preferably 150 μm or more and 850 μm or less. If the median diameter of the aforementioned particles is 150 μm or more, the sedimentation of the purification active ingredient is delayed, and the adsorption time of the purification active ingredient can be prolonged. Here, the median diameter (also referred to as d50) refers to the particle size when the particle size of the aforementioned particles is plotted, and the particle size is 50% of the total number in the figure (the larger particle size is compared with the particle size). The smaller diameter side is divided into the same particle size). 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 above-mentioned kneading step, the production method of the present invention may also include other steps such as a forming step, a drying step, and a crushing step. Specifically, the particles defined in the present invention are manufactured by a manufacturing method including the following steps: a forming step, forming a shaped body with a kneaded product obtained through the above-mentioned kneading step; and a drying step, forming the aforementioned shaped body Drying; and pulverizing step, pulverizing the dried shaped body. Then, after the aforementioned pulverization step, a classification step may also be included, which is to classify the particles through 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 shaping step, for example, the aforementioned kneaded product can be shaped by any shaping method to form a shaped 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 foregoing drying step, it is preferable to use a multi-stage hot air dryer to dry the obtained molded body at a temperature of 80°C to 150°C and conditions of 2 hours to 12 hours. Preferably, the aforementioned molded body is dried and supplied to the pulverization step. In addition, although the preferable aspect of the aforementioned drying step is to apply the sequence of "drying the molded body obtained in the forming step, and then pulverizing the dried molded body", it is also possible to perform the procedure of "drying the molded body obtained in the forming step". After pulverization, the drying step is performed to obtain particles" in the order. A pulverizer is used in the foregoing pulverization step, for example, a jet type ultrafine pulverizer is used to pulverize particles. In the foregoing classification step, a classifier is used, preferably, for example, a vibrating screen or an air ratio classifier is used to classify the pulverized powder so that the median diameter of the particles is within the desired range. It is better to set the median diameter in the range of 150μm~850μm, so the sieve will only select particles with a particle size in the range of 150μm~850μm, and the powder smaller than 150μm or more than 850μm will be taken out by the sieve and removed (sieved out).

<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; The second aspect of the method for producing a water purifier> In the method for producing a water purifier, before the kneading step of kneading the plant powder and the polymer flocculant, it further includes mixing water with the polymer flocculant and mixing the high The step of mixing the molecular coagulant 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 flocculant>> The kneading step in the second aspect is specifically the same as described in (a1) and (a2) above in the first aspect, For example, it includes the steps defined in (a1) and (a2) below, and the following two aspects (a1) and (a2) can be cited. (A1): In the first mixing step, water is mixed with the polymer flocculant to knead the polymer flocculant and water; after that, the second mixing step is performed to mix the plant powder into the kneaded polymer flocculant, To knead the aforementioned plant powder and polymer flocculant. In the above (a1), when the plant powder and the polymer flocculant are kneaded, water may be mixed. In this case, it becomes the following (a2). (A2): In the first mixing step, water is mixed with the polymer flocculant to knead the polymer flocculant and water; after that, the second mixing step is performed to mix the plant powder and water until the kneaded polymer agglomerates Agent to knead the aforementioned plant powder and polymer flocculant.

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, pre-kneading the polymer flocculant with water before kneading with the plant powder is effective for obtaining a kneaded system with the desired hardness. At this time, the total amount (mass) of water added during kneading is not particularly limited. For example, the amount of water mixed with respect to the solid content (mass) in the water purifier is 1 time to At 9 times, the water purifying agent for achieving the purpose of the present invention can be obtained. However, as defined in the first aspect, at the time of kneading, the total amount (mass) of water mixing relative to the solid content (mass) in the water purifier is more preferably in the range of 1.5 times to 8 times. Regarding the requirements other than the above-mentioned requirements defined in the kneading step, the content described in the above-mentioned 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。Regarding the second aspect of <<Plant powder>>, <<High polymer flocculant>>, <<Other additives>>, <<Plant powder and polymer flocculant granules>>, <<Other steps>> etc. The 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 dissolves the water purifying agent obtained by the above-mentioned production method of the present invention in water to obtain a dispersion liquid containing plant powder and a polymer flocculant. Next, by supplying the dispersion liquid to the discharged water containing inorganic wastes, the inorganic wastes in the discharged water are removed. The aforementioned inorganic waste includes, for example, inorganic waste having at least one selected from the group consisting of nickel, fluorine, iron, copper, zinc, chromium, arsenic, cadmium, and lead. As for the aforementioned dispersion, in addition to pure water (distilled water), water with a conductivity of 30 μS/cm or more can be used. In this way, cheaper tap water and underground water can be used. Even if tap water and underground water are used for the dispersion, the concentration of inorganic ions in the discharged water can be reduced to a concentration below the desired concentration, and it exhibits excellent water purification performance. The water purifier obtained by the production method of the present invention is used to prepare a dispersion.

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 discharge water treatment method of the present invention will be specifically described. For example, alkali can also be added to the discharged water to make the discharged water alkaline to insolubilize at least a part of the aforementioned heavy metal ions, and after the insolubilization step of forming a suspended solid, add the manufacturing method of the present invention The obtained water purifying agent. Furthermore, after separately adding a polymer flocculant such as amine, the water purifying agent obtained by the production method of the present invention may be added. 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 drain water. By supplying the dispersion to the discharged water, the inorganic wastes are aggregated and settled, and the sediment separated by the sedimentation is 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 produced, which was used as the discharge water (hypothetical discharge water) used in the experiment. Next, sodium hydroxide was supplied to the above-mentioned drain water so that the pH value became 10, and stirred to insolubilize nickel. The nickel ion concentration of the supernatant liquid of the discharged water was 2 mg/L. <Water Purifier> Furthermore, "Concentrated Spinach from Maebashi, Gunma Prefecture" is used as the plant, and polypropylene amide (PAM) is used as the polymer flocculant. The pellet 1 is obtained by the manufacturing method shown below, and this pellet 1 is used as the water purifying 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 for manufacturing water purifier>> Add 5 times the mass of water to the mass of the total solid content of the plant powder and polymer flocculant to obtain a kneaded product (plant powder + polymer flocculant + water = 30kg), The kneaded product was put into a planetary mixer (manufactured by Aikosha Manufacturing Co., Ltd., mixer ACM-110, capacity 110L), and kneaded by applying shear stress under mixing conditions of 150 rpm and 20 minutes. The obtained kneaded product is shaped, and a shaped body is produced. Using a multi-stage hot air dryer (a rack oven device manufactured by Shichiyo Manufacturing Co., Ltd.), the molded product was dried at 120°C for 3 hours, and then at 150°C for 2 hours. Next, the dried flakes were pulverized with an airflow type ultrafine pulverizer (Ceren Miller manufactured by Masuko Sangyo Co., Ltd.) so that the median diameter was 400 μm. Furthermore, the median diameter was measured by mastersizer2000 (manufactured by Malvern Instrument). Use a classifier (vibrating sieving machine manufactured by Mikasa Co., Ltd.) and set it to only siev the powder with a particle size in the range of 150μm~850μm. The particles with a particle size of less than 150μm or a particle size of more than 850μm are sieved. Take out and remove (sieve out). In this way, particles 1 are obtained and used as water purifiers 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> To the particles, water with a conductivity of 110 μS/cm (tap water from Kanuma City, Tochigi Prefecture) was added and stirred so that the solid content became 0.1% by mass to obtain a dispersion liquid 1.

<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 above-mentioned drain water, and the solid content was adjusted to 7 mg/L, and it stirred. Here, the "solid content" measurement method can be obtained by measuring the slurry concentration of the discharged water using a moisture meter and deducing the solid content. The drain water to which the dispersion liquid 1 was added was transferred to a sedimentation tank, and after that, it was allowed to stand, and the state was visually confirmed every 1 hour. The time at which two layers of the supernatant clear liquid and the sediment were confirmed to be clearly separated was measured as the settling time. In addition, the supernatant liquid was taken out and the ion concentration was measured with Lambda (Λ)9000 (manufactured by Kyoritsu Rikaki Lab). The following criteria were used to evaluate the water purification performance of the results. [Evaluation criteria for water purification performance] ◎: Less than 1.0 mg/L (below the 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 result of the dispersion viscosity 50 (mPa‧sec) measured by the B-type viscosity agent. In addition, with regard to the hardness of the kneaded product obtained in the process of manufacturing the pellets, the measurement result in the AR-G2 hardness measurement mode manufactured by TA Instruments is also displayed according to the above-mentioned method. In addition, the above-mentioned viscosity measurement was measured with a Toki Sangyo TVC-7 viscometer (B-type viscometer) at a room temperature of 23°C using a No. 1 rotor. In addition, in Table 1-1, plant powder 1 refers to “concentrated spinach produced in Maebashi, Gunma Prefecture”, and PAM refers to polyacrylamide (the same applies to Table 1-2 to Table 1-3, and Table 2).

(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 Changshuo jute (produced in Guangzhou, China) and the rotation speed of the mixer in the kneading step was changed to 80 rpm. Using the water purifying agent 2 made of pellets 2, and in the same manner as in Example 1, the characteristics of the water purifying agent were evaluated. The evaluation results of Example 2 are shown in Table 1-1. In addition, 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, "Zhonghuang Ma No. 4" of the ID No. 2013 of the Chinese Academy of Agricultural Sciences Bast Research Institute of Changshuo Jute was used. Except for this, pellets 3 were produced in the same manner as in Example 2. Using the water purifying agent 3 made of pellets 3, and in the same manner as in Example 1, the characteristics of the water purifying agent were evaluated. The evaluation results of Example 3 are shown in Table 1-1. In addition, the plant powder 3 in Table 1-1 refers to "Zhonghuang Ma 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 pellet 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. Using the water purifying agent 4 made of pellets 4, and in the same manner as in Example 1, the characteristics of the water purifying agent were evaluated. 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 pellet 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. Using the water purifying agent 5 made of the pellets 5, and in the same manner as in Example 1, the characteristics of the water purifying agent were evaluated. 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) 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. Using the water purifying agent 6 made of pellets 6, and in the same manner as in Example 1, the characteristics of the water purifying agent were evaluated. 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) 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. Using the water purifying agent 7 made of pellets 7, and in the same manner as in Example 1, the characteristics of the water purifying agent were evaluated. 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) The pellet 8 was produced in the same manner as in Example 3 except that the water as the dispersion in Example 3 was changed to water with a conductivity of 198 μS/cm (tap water in Kanuma City, Tochigi Prefecture). Using the water purifying agent 8 made of pellets 8, and in the same manner as in Example 1, the characteristics of the water purifying agent were evaluated. 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 as the dispersion in Example 3 was changed to water with a conductivity of 30 μS/cm obtained by mixing appropriate amounts of Kanuma City, Tochigi Prefecture tap water and distilled water. Using the water purifying agent 9 made of pellets 9, and in the same manner as in Example 1, the characteristics of the water purifying agent were evaluated. 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. Using the water purifying agent 10 made of pellets 10, and in the same manner as in Example 1, the characteristics of the water purifying agent were evaluated. 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 flocculant of Example 3 was changed to polyamine. Using the water purifying agent 11 made of pellets 11, and in the same manner as in Example 1, the characteristics of the water purifying agent were evaluated. 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 produced, which was used as drain water for experiments (hypothetical drain water). Next, 8.6 mg/L of calcium chloride was added to the above-mentioned drain water, and sodium hydroxide was added to make the pH value 7.5 to 9.0, and while stirring, the fluorine was insolubilized. By this operation, the supernatant liquid containing the micro-flock in the fluorine aqueous solution is separated from the sediment. At this point, the ion concentration of the upper clear liquid of the discharged water was 10 mg/L. Except for using the above-mentioned discharged water, in the same manner as in Example 3, the water purifying agent 3 made of pellets 3 was used, and the characteristics of the water purifying agent were evaluated. The evaluation results of Example 12 are shown in Table 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) The 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 drain water (hypothetical drain water) used in the experiment. Furthermore, while adding sodium hydroxide to the above-mentioned drain water to make the pH value 6.5 to 9.0, stirring was carried out to insolubilize iron. At this point, the ion concentration of the upper clear liquid of the discharged water was 2 mg/L. Except for using the above-mentioned discharged water, in the same manner as in Example 3, the water purifying agent 3 made of pellets 3 was used, and the characteristics of the water purifying agent were evaluated. The evaluation results of Example 13 are shown in Table 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) The copper sulfate pentahydrate was dissolved in pure water, and 800 g of an aqueous solution containing 100 mg/L of copper ions was produced, which was used as the discharge water (hypothetical discharge water) used in the experiment. Furthermore, while adding sodium hydroxide to the drain water to have a pH of 7.0 to 8.0, stirring was carried out to insolubilize copper. At this point, the ion concentration of the upper clear liquid of the discharged water was 2 mg/L. Except for using the above-mentioned discharged water, in the same manner as in Example 3, the water purifying agent 3 made of pellets 3 was used, and the characteristics of the water purifying agent were evaluated. The evaluation results of Example 14 are shown in Table 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 produced, which was used as the discharge water for the experiment (hypothetical discharge water). Furthermore, while adding sodium hydroxide to the drain water to have a pH of 9.0 to 9.5, stirring was performed to insolubilize zinc. At this point, the ion concentration of the upper clear liquid of the discharged water was 5 mg/L. Except for using the above-mentioned discharged water, in the same manner as in Example 3, the water purifying agent 3 made of pellets 3 was used, and the characteristics of the water purifying agent were evaluated. The evaluation results of Example 15 are shown in Table 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 made, which was used as drain water for the experiment (hypothetical drain water). Furthermore, while adding sodium hydroxide to the drain water to have a pH of 6.0 to 7.5, it was stirred to insolubilize chromium. At this point, the ion concentration of the upper clear liquid of the discharged water was 5 mg/L. Except for using the above-mentioned discharged water, in the same manner as in Example 3, the water purifying agent 3 made of pellets 3 was used, and the characteristics of the water purifying agent were evaluated. The evaluation results of Example 16 are shown in Table 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 made, which was used as drain water for experiments (hypothetical drain water). Next, 65 mg/L of iron chloride and 354 mg/L of calcium chloride were added to the drain water, and then sodium hydroxide was added to make the pH value 8.0 to 9.5, and while stirring, the arsenic was insolubilized. At this point, the ion concentration of the upper clear liquid of the discharged water was 0.05 mg/L. Except for using the above-mentioned discharged water, in the same manner as in Example 3, the water purifying agent 3 made of pellets 3 was used, and the characteristics of the water purifying agent were evaluated. The evaluation results of Example 17 are shown in Table 1-3. However, in Example 17, after the sedimentation time was measured in the same manner as in Example 3, the supernatant liquid was taken out and the volume was concentrated to 1/100 by an evaporator, and the ion concentration was measured. Regarding arsenic ions, if the ion concentration is judged to be a good result of 0.01 mg/L or less, the result is evaluated as ⓞ.

[表1-1]

Figure 106131604-A0304-0001
[Table 1-1]
Figure 106131604-A0304-0001

[表1-2]

Figure 106131604-A0304-0002
[Table 1-2]
Figure 106131604-A0304-0002

[表1-3]

Figure 106131604-A0304-0003
[Table 1-3]
Figure 106131604-A0304-0003

(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) Regarding the water purifiers 3, 4, and 5 obtained in Examples 3, 4, and 5, the same method as in Examples 3, 4, and 5 was used to replace the water in the dispersion with conductivity. Evaluation of the characteristics of water purifiers with 1μS/cm of water (distilled water). The evaluation results when using distilled water as the water of the dispersion of the water purifiers 3, 4, and 5 are the same as the water with conductivity of 110 μS/cm (tap water from Kanuma City, Tochigi Prefecture) performed in Examples 3, 4, and 5 above. The evaluation results at the time of use of the dispersion are shown in Table 2 together.

(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, except that the amount of water added to the solid content (polymer aggregate + plant powder) was changed to 0.8 times and 9 times, the same procedure as in Example 3 was carried out to produce comparative particles 1 ~2. Using comparative water purifiers 1 and 2 made of comparative particles 1 and 2, and the same as in Example 3 and Example 18, when using water with a conductivity of 110 μS/cm (tap water in Kanuma City, Tochigi Prefecture) as the dispersion liquid, And when using distilled water with a conductivity of 1 μS/cm as the dispersion liquid, the water purification performance of the discharged water was evaluated. Table 2 shows the evaluation results of Comparative Examples 1-2. In addition, with respect to the comparative particles 1 used in Comparative Example 1, although it is also intended to measure the hardness of the kneaded material obtained in the manufacturing process by the same method as in Example 1, it is because the kneaded material has no stickiness. It disintegrates into pieces and does not form lumps, so it cannot be measured with a hardness meter.

[表2]

Figure 106131604-A0304-0004
[Table 2]
Figure 106131604-A0304-0004

(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 as in Example 3, the experiment for evaluating the purification performance of discharged water in Example 3 was performed 30 times. On the other hand, using the water purifying agent 3 obtained in Example 3, instead of using a dispersion liquid, 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 addition amount of the water purifying agent 3 is an amount such that the solid content becomes 7 mg/L with respect to the discharged water. The variability of purification performance was evaluated based on the results of each experiment. In the case of using the dispersion, the result was ⊚, and it was confirmed that the purification result with little fluctuation was obtained every time. On the other hand, when the water purifier is directly put into the discharged water, although there are cases where good results are shown as ◎, there are cases where the same results are not shown (when there are results of ○ or ○△), but because it is used The experiment is carried out in the same way, so the experimental results are subject to variability.

(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) The 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. Using the water purifying agent 20 made of particles 20, and in the same manner as in Example 3, the characteristics of the water purifying agent were evaluated. <Kneading step> The amount of water shown in Table 3 below was added to the polymer flocculant, and the polymer flocculant and water were kneaded for 10 minutes. After that, the plant powder is mixed with the kneaded polymer flocculant, and the plant powder and the polymer flocculant are kneaded for 10 minutes. Furthermore, using the water purifying agent 20 obtained by the above-mentioned method, as shown in Example 18, the characteristics of the water purifying agent when the water of the dispersion was changed to water with a conductivity of 1 μS/cm (distilled water) were evaluated. Table 3 shows the results of the evaluation using the water purifier 20.

(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 21-23) Except having changed the water purifier 20 to the conditions shown in the following Table 3, the water purifier 21-23 was produced by the same method. 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]

Figure 106131604-A0304-0005
[table 3]
Figure 106131604-A0304-0005

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 purifier system manufactured by the manufacturing method of the present invention can be applied to the water purifier when the size of the drain tank is used in a large automatic purification device. , And it is low-cost and shows stable purification performance unchanged every time.

none

無。none.

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 producing a water purifying agent, which is a method for producing a water purifying agent made of particles containing plant powder and a polymer flocculant, which comprises: a kneading step of kneading the plant powder and the polymer flocculant; wherein In the aforementioned kneading step, the hardness of the kneaded product obtained through the aforementioned kneading step is to knead the plant powder and polymer agglomeration in such a way that the stress is 3N/mm 2 ~ 100N/mm 2 under the following measurement conditions Measurement conditions: For the aforementioned mixture, use a stress-controlled rheometer (viscosity measuring device) to measure the stress when a probe with a diameter of 16mm is pushed in at a speed of 30mm/min and a pushing amount is 5mm. 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 purifier according to claim 1, wherein any of the following (a1), the following (a2), and the following (b) are met: (a1): the first kneading step, Water is mixed with the polymer flocculant to knead the polymer flocculant and water; after that, the second mixing step is performed to mix the plant powder with the kneaded polymer flocculant to knead the plant powder and the polymer A flocculant; wherein, in the first kneading step, the total amount (mass) of water mixing relative to the solid content (mass) in the water purifying agent is 1.5 to 8 times; (a2): the first kneading step , Water is mixed with the aforementioned polymer flocculant to knead the aforementioned polymer flocculant and water; after that, a second mixing step is carried out, the aforementioned plant powder and water are mixed into the aforementioned polymer flocculant to knead the aforementioned plant Powder and polymer flocculant; wherein, in the first kneading step and the second kneading step, the total amount (mass) of water mixed with respect to the solid content (mass) in the water purifier is 1.5 times to 8 And (b): mixing step, mixing plant powder with polymer flocculant and water to knead it; wherein, in the aforementioned mixing step, the water is mixed with respect to the solid content (mass) in the aforementioned water purifying agent The total amount (quality) is 1.5 times 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 producing a water purifying agent according to claim 1, which comprises: a first kneading step, mixing water with the polymer flocculant to knead the polymer flocculant and water; then, performing a second kneading step , Mixing the plant powder with the kneaded polymer flocculant to knead the plant powder and the polymer flocculant. 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 purifier according to claim 1, wherein the total value of the kneading time during the kneading is 15 minutes or more and within 30 minutes 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 selected from any one of the group consisting of Changshu jute, jute, Komatsu cabbage, Japanese celery, Japanese turnip, and bok choy. 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 Changshuo jute is "Zhonghuang Ma No. 4" under the identification number 2013 of the Bast Fiber Research Institute 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 purifying agent according to claim 1, wherein the median diameter of the water purifying 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 purifying agent according to claim 1, wherein the polymer flocculant is polyacrylamide. 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, which comprises: a forming step of forming a shaped body with a kneaded product obtained through the aforementioned kneading step; a drying step of drying the aforementioned shaped body; and a pulverizing step, The dried shaped body is 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 dissolves the water purifier obtained by the method for producing a water purifier as set forth in any one of claims 1 to 10 in water to obtain a plant powder and a polymer coagulant Then, by supplying the dispersion liquid to the discharged water containing inorganic wastes, the inorganic wastes in the discharged water are removed. 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 discharge water treatment method according to claim 11, wherein the discharge water system has at least one inorganic waste 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 the water in the dispersion liquid is 30 μS/cm or more.
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