TWI267399B - Adsorptive filter media - Google Patents

Adsorptive filter media Download PDF

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TWI267399B
TWI267399B TW93118026A TW93118026A TWI267399B TW I267399 B TWI267399 B TW I267399B TW 93118026 A TW93118026 A TW 93118026A TW 93118026 A TW93118026 A TW 93118026A TW I267399 B TWI267399 B TW I267399B
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Taiwan
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diatomaceous earth
arsenic
filter material
solution
water
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TW93118026A
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Chinese (zh)
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TW200600176A (en
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Chia-Cheng Wu
Tsair-Fuh Lin
Min-Shing Tsai
Chung-Kai Cheng
Yuan-Chang Wang
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Univ Nat Cheng Kung
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  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Water Treatment By Sorption (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

A new adsorptive filter media is invented to treat the with arsenic contaminated water. The GaAs manufacturers, for example, use mostly AsH3 gas as reactant in the surface organic synthesis process. The exhaust gas is treated in a washing tower using hyper chlorite from which the small quantity of waste water with high arsenic concentration is produced. Precipitation/coagulation is the most used method to remove arsenic from water. The arsenic containing sledges have to be transported and treated with high costs. Some new technologies were also developed to solve the arsenic problems in waste water, however with disadvantages such as slow kinetics and high costs. In order to substitute the conventional methods, the inventors have developed a new type of adsorptive filter by modifying the sintered diatomite surface using iron hydroxide. The modification can be achieved by mean of adding diatomite into aqueous solution of ferric chloride followed by the treatment in sodium hydroxide solution. This new type of adsorbent is characterized through its high kinetics and low costs.

Description

12673991267399

本發明係有關於一種吸附性滤材的製備方法,主要是 以石夕藻土為擔體’經過溼式表面處理,於表面上形成具吸 附月b力之氫氧化鐵活性層,如此製備出之吸附性石夕藻土濾 材’特別可供用於處理含砷廢水或是飲用水及礦泉水除砰 淨化之用’且可避免大量含砷污泥產生。 【先前技術】 光電產業在近年來儼然已為多數地區重點發展之產 業。而在光電半導體元件之♦, 「砷化鎵」與傳統之矽元 件相較,具有高頻、雜訊小、抗輻射、體積小、耐高溫等 特性,因此具有更廣闊的發展空間,砷化鎵(GaAs )由於 同時具備多項優點,故於通訊設備及電子器材產業中被廣 泛使用,有逐漸取代傳統矽元件二極體之勢。基於此因只 二有二ί廠商投入大量資金人力,進行研發生I ;據統計 並呈=成化錄產能已高達美金五十-億八千萬, 砷,鎵光電元件生產技術目前均採用 中又以氫化坤(Ash3)氣體進行有機金 ;其 (M0CVD)技術最為廣泛使用;而其產二,曰曰 -般為:利用次氯酸鈉加入洗務塔,將三價毛:處理設施 性之五價砷酸鹽,而後排出高濃度之:麻申虱化為水溶 行廢水處理。❿前述所產生的廢水,在;=,再續之進 的技術,主要以化學混凝沉澱法,即 、’地理含砷廢水 凝劑及尚分子聚合物助凝劑使五價砰形 _ /儿歲劑、混 僅在處理過程中其加藥量是環境上一^ ^泥。惟此法不The invention relates to a method for preparing an adsorbent filter material, which is mainly prepared by using a wet surface treatment to form an active layer of iron hydroxide having an adsorption month b force on the surface by using a wet surface treatment. The adsorbent Shixiazao soil filter material is specially used for treating arsenic-containing wastewater or drinking water and mineral water for purifying and purifying, and can avoid the production of a large amount of arsenic-containing sludge. [Prior Art] In recent years, the optoelectronic industry has been a major development industry in most regions. In the case of optoelectronic semiconductor components, "GaAs" has higher frequency, less noise, radiation resistance, small size, and high temperature resistance compared with conventional germanium components, so it has a broader development space, arsenic. Since gallium (GaAs) has many advantages at the same time, it is widely used in the communication equipment and electronic equipment industry, and gradually replaces the traditional tantalum component diode. Based on this, only two companies have invested a large amount of capital to carry out research and development, and according to statistics, the production capacity of Chenghua Record has reached 50-800 million. The production technology of arsenic and gallium optoelectronic components are currently in use. It is also made of organic gold by hydrogenation (Ash3) gas; its (M0CVD) technology is most widely used; and its production is two, 曰曰-like: using sodium hypochlorite to add to the washing tower, the trivalent hair: processing facilities five prices Arsenate, and then discharge high concentration: Ma Shen is turned into water-soluble wastewater treatment. ❿The above-mentioned wastewater, in the technology of re-continuation, mainly by chemical coagulation precipitation method, ie, 'geographic arsenic-containing wastewater coagulant and molecular molecular coagulant to make the pentavalent shape _ / The ageing agent and the mixing amount are only in the environment during the treatment. But this law is not

第8頁 ------- A員擔,而且會產生 1267399 案號 93Π8026 修正 曰 五、發明說明(2) 大量之含砷污泥,平均處理一噸廢水產生約丨〇 〇公斤之污 泥,且此含砷污泥後續之清理費用一直居高不下,每噸 在新台幣1 2 0 0 0元之譜,處理砷污泥目前僅有固化處理為、 ,一可行之技術,不但附加成本高,又無法實質解決廢 勿問’並造成可利用之石申資源浪費。 , 為彌補化學混凝沉澱法之不足,近來各國專家學者 ,研發各種新技術,以期取代此一技術,其中包括有離 父換法、活性污泥法及吸附法等: Α·在離子交換技術中,目前已發展出數種陰離子交換 除水中含坤’後於氫氧化鈉鹼液中定量解析,將樹 ;2:用2法雖具有去除率高、吸附動力性佳與Ξι 再生荨優點,惟至今仍無法克服高成本之缺陷。 Β·另’活性污泥為利用培養分離出之菌藻共 除:,經植種2氣、沉殿、脫水後可得高濃度含畔活性 ί 2 1 : Ϊ t :地理費用幸交Κ,而活性污泥生物處理技術 :7处理方面較為成熟;但此技術也具備了生物 ^的最大缺點:反應速率低以及產生大量含珅污泥。目前 此-技術尚處於實驗室階段,且並未訂出污泥之最終去 向,故其產業可利用性仍需多方考量。Page 8 ------- A member, and will produce 1267399 Case No. 93Π8026 Amendment 曰5, invention description (2) A large amount of arsenic-containing sludge, the average treatment of one ton of wastewater produces about 丨〇〇 kg of sewage Mud, and the subsequent cleaning costs of this arsenic-containing sludge have remained high, at a rate of NT$1,200 per ton. The treatment of arsenic sludge is currently only cured, and a feasible technology is not only attached. The cost is high, and it is impossible to solve the problem of waste and ask for a waste of resources. In order to make up for the shortcomings of chemical coagulation and sedimentation methods, experts and scholars from various countries have recently developed various new technologies to replace this technology, including the method of separation from the father, activated sludge and adsorption: Α·in ion exchange technology In the present, several kinds of anion exchange have been developed to remove the water in the water, and then quantitatively analyzed in sodium hydroxide lye, the tree; 2: with the 2 method, although it has the advantages of high removal rate, good adsorption power and 荨ι regeneration, However, it still cannot overcome the shortcomings of high cost. Β·The other 'activated sludge is co-extracted by the bacteria isolated from the culture: After planting 2 gas, sinking the temple, dehydration can obtain high concentration of side-effect activity ί 2 1 : Ϊ t : Geographical cost is good, The activated sludge biological treatment technology: 7 treatment is relatively mature; but this technology also has the biggest shortcomings of biological ^: low reaction rate and the production of a large amount of sludge containing sludge. At present, this technology is still in the laboratory stage, and the final destination of sludge has not been set, so its industrial availability still needs to be considered.

第9頁 C·此外,有以各類金屬氧化物為吸附劑之除砷方法, 所採用的包括以乳化錳(㈠n02)及氫氧化鐵為基底之吸 附劑(如爐邊、鋼逢等);例如德國製的GEH以貝塔氮氧 化鐵(/5 FeOOH又名Akaganei te )為主要吸附成分之吸 附劑;目前此類商用吸附劑,雖具有:包括比表面積大、 f晶度低、表面_活性高及平衡吸附量大等特色,可用於去 1267399 案號 五、發明說明(3) 除水中微量重 於成本高,且 水或淡化海水 尚無實務經驗 然而,吸 後進行脫附以 可兼具降低製 發明人有鑑於 附性矽藻土濾 i,另一方面 93118026 金屬、 吸附動 中之除 〇 附劑若 回收石申 程成本 此,特 材’ 一 可大幅 代高成本之舊式除砷 【發明内容】 本發明係以結合 材’製出高效能低成 係採用浸泡與調整酸 於鐵鹽溶液中,令其 調整pH值至2 ± 0. 1, 面’精此以獲得一種 材0 修正一 有巧磷與有機氮等高級處理上;但由 力u,故至今僅應用於飲用水、地下 坤等高級用途,於處理高濃度之廢水 八備良好的脫附特性,可於吸附飽和 ,經濃縮精製而再利用於製程中,即 及減少產生合、- 13坤巧泥之雙重優點;本 &明出以氫氧化鐵進行表面改質之吸 方面除可保持吸附效能於一定水準之 降低生產成本與提高吸附動力,以取 技術。 :附性氫氧化鐵與高透水性矽藻土濾 本之坤吸附性石夕藻土之方法。本發明 鹼兩段式進行之;首先將矽藻土浸泡 :收鐵鹽溶液,再加入氫氧化鈉鹼液 令虱氧化鐵膠羽直接覆膜於碎蕩土表 可供吸附水中砷的吸附性矽藻土滤 :=金'”金屬間,可以+5、+3、0與-3等氧:數 i式存在,一般存在水體中之砷來源有天然及人為污毕兩 種;在工業污染方面除了前述光電產業之外,Page 9 C. In addition, there are arsenic removal methods using various metal oxides as adsorbents, including adsorbents based on emulsified manganese ((i)n02) and iron hydroxide (such as furnace edge, steel slab, etc.) For example, German-made GEH uses beta-iron oxide (/5 FeOOH, also known as Akaganei te) as the main adsorbent component; currently, such commercial adsorbents have: large specific surface area, low f crystal, surface _ Features such as high activity and large amount of equilibrium adsorption, can be used to go to 1267399. Case No. 5. Invention Description (3) There is no practical experience in removing trace amounts of water in water, and there is no practical experience in water or desalinated seawater. However, after desorption, it can be desorbed. Inventors with reduced system in view of the attached diatomaceous earth filter i, on the other hand 93110026 metal, adsorption in the removal of the sputum, if the recovery of the stone application costs, special materials, a large-scale high-cost arsenic removal The present invention is based on the combination of materials to produce a high-performance low-cost system by soaking and adjusting the acid in the iron salt solution, so that the pH is adjusted to 2 ± 0.1, the surface 'fine to obtain a material 0 correction one Clever phosphorus Advanced treatments such as organic nitrogen; but by force u, it has only been used in advanced applications such as drinking water and underground kun. It has good desorption characteristics for the treatment of high-concentration wastewater. It can be saturated and refined. It is used in the process, that is, it can reduce the double advantages of producing the combination, and it can be used to reduce the production cost and increase the adsorption efficiency at a certain level. Adsorb the power to take the technology. : Method of attaching ferric hydroxide and high permeability diatomaceous earth filter. The alkali of the invention is carried out in two stages; firstly, the diatomaceous earth is immersed: the iron salt solution is added, and then the sodium hydroxide alkali solution is added to directly coat the cerium oxide iron feathers on the broken soil surface to adsorb the arsenic in the adsorbed water. Diatomaceous earth filter: = gold '" metal, can be +5, +3, 0 and -3 and other oxygen: number i exists, generally there are two sources of arsenic in water, natural and artificial pollution; in industrial pollution In addition to the aforementioned optoelectronic industry,

本發明人研發所得之吸附性濾材,特別係針對水中砷 兀素,具極佳之吸附效能。砷元素本身乃 1267399 —案5虎 93118026 五、發明說明(4) 飲用水亦危及我們的生活環境,緣此,本發明人結合團隊 之研發精神與心力,經不斷的實驗與試作,遂得出結合吸 附性氯氧化鐵與高透水性矽藻土濾材,進而製出高效能低 成本之神吸附性矽藻土濾材之本發明製備方法。 四於前述之貝塔氫氧化鐵(万-FeOOH )吸附劑,其在水 相ί展境中’由於表面氫氧根離子產生質子化與去質子化作 用’而形成兩性之表面特性,可同時對有機物及無機物產 生吸附作用’以此物為基底而發展出之吸附劑(如德製GEΗ )八,其主要成分為低結晶性之万-FeOOH與Fe(OH)3 (重量百 分比共55% ),粒徑分布在〇· 32-2 mm之間,並具有高比表 面積^:2曰50-30 0 m2/g)、高表面活性等特質;可用於去除 水中微量重金屬、有機磷與有機氮等高級處理上,實際之 3用::也下水、飲用水與淡化海水中之除砷及除有機物 ί二Ϊ管如此,但此吸附劑製作過程繁複,須經過離心及 =墾程序使石—Fe〇〇H成粒狀,而且藥劑成本不低, :?斤售價為新台幣! 32元,且吸附平衡時間長達i 5〇小: 等言2用ί吸附劑目前係僅供使用於飲用水及地下水淨化 冋途;f,操作技術則是以固定床過濾設備為主。 ♦古^ Ϊ,若以吸附劑成分來看,氫氧化鐵係為水中除石Φ 之有效成分。若由製造成本來 ’、申 化鐵來進仃吸附’實為浪費;根據吸附理論 乳 限於吸附劑顆拓主;& ^丄 咐作用僅 以本發明人特以、、轻彳姑淋 γ γ , 笔…、貝馱。是 ^^ ^ 符以屋式技術,將氫氧化鐵覆膜於擔體上, 研發產製吸附性濾材之創新技術。 。體上,以 體方面,除了須考慮成本以及覆膜性外,尚The adsorbent filter material obtained by the present inventors, in particular, is directed to arsenic in water and has excellent adsorption efficiency. The arsenic element itself is 1267399 — case 5 tiger 93118026 V. Invention description (4) Drinking water also endangers our living environment. Therefore, the inventor combined with the research and development spirit and efforts of the team, through continuous experiment and trial work, The invention combines the adsorbed iron oxychloride with the highly permeable diatomaceous earth filter material to prepare a high-efficiency and low-cost god-adsorbing diatomaceous earth filter material. 4. The above-mentioned beta iron hydroxide (Wan-FeOOH) adsorbent, which exhibits the surface characteristics of the amphoteric surface due to the protonation and deprotonation of the surface hydroxide ions in the aqueous phase, can simultaneously Organic and inorganic substances produce an adsorbent that is developed on the basis of this material (such as German GEΗ). Its main components are low crystallinity-FeOOH and Fe(OH)3 (55% by weight) , the particle size distribution is between 〇· 32-2 mm, and has a high specific surface area ^: 2曰50-30 0 m2 / g), high surface activity and other characteristics; can be used to remove traces of heavy metals, organic phosphorus and organic nitrogen in water For advanced treatment, the actual use of 3:: also in the water, drinking water and desalinated seawater in addition to arsenic and organic matter ί Ϊ tube, but the production process of this sorbent is complicated, must be centrifuged and = 垦 procedure to make the stone - Fe〇〇H is granulated, and the cost of the drug is not low. The price of the product is NT$32, and the adsorption equilibrium time is as long as i 5〇: The second ί adsorbent is currently only for use. Drinking water and groundwater purification; f, operating technology is fixed bed filtration The equipment is mainly. ♦ Ancient ^ Ϊ, in terms of adsorbent composition, iron hydroxide is the active ingredient of stone removal Φ in water. If the manufacturing cost comes from ', the application of iron into the sputum adsorption is a waste; according to the adsorption theory, the milk is limited to the sorbent particle extension; & 丄咐 丄咐 仅 本 本 本 本 本 本 本 本 本 本 本γ, pen..., Bellow. It is ^^ ^ that uses the roof-type technology to coat iron hydroxide on the support and develop innovative technology for producing adsorption filter. . Physically, in terms of body, in addition to cost and filming,

第11頁 1267399Page 11 1267399

案號 9311802R 五、發明說明(5 ) 需考”載=透水性及比表面•,以利於過濾。以往有 ϋ用石:◊;、、體,覆膜技術,但因覆膜性不#,成品品 質不穩疋,吸附效能有限而無法繼績推廣。 土為= 条件’本發明係以石夕藻土為擔體。石夕藻 &二: μ、物死亡後埋入地下,經崩解後,由剩餘 ^ ^ 乂边大中空顆粒,平均粒徑約為1 5 // m上下(1 0 ηΓ多孔狀以酸鹽類由二電子顯微鏡下可明 ^ Q見附件一),·由於矽藻土兼具高孔隙 ^’立孔隙率可達8 0%以上)及吸附力等特性,為- i;”過濾材,且可作為人微量元素之來源。石夕藻土 分i食品級與工業…,主要取決於二氧 其他有=1曰二,艮品級矽藻土之結晶度須在3%以下,且無 做為产Iΐ,主要用途除可供食用、飼料添加外,亦可 好了:豐農藥與飲料業過據程序中之助遽齊J,效果十分良 壓及祕勒級矽藻土則具較高之結晶度,主要是因為地殼擠 劑山作用,造成再結晶,其用途在於作為填充 $,别、除濁劑/除臭劑及製作炸藥等。 之吸=^研究指出,矽藻土對有機與無機物皆有一定程度 機物類=f,對蛋白質、醣類、脂肪類及微生物細胞等有 物之吸、吸附’可在飲料業過濾過程中得到證實;在無機 子如金L附方面,則有研究指出,矽藻土對一些重金屬陽離 之主要,、鉻等,均有一定之吸附效果。而含砷廢液中 石夕聲+ ^分即為砷酸根離子(AS〇4 3_),故以表面經改質之 土可達到除砷的較佳成效。 吕’矽藻土可依加工程序分為研磨矽藻土粉及Case No. 9311802R V. Invention Description (5) Need to test "Loading water permeability and specific surface area" to facilitate filtration. In the past, there were stones used in the past: ◊;, body, film coating technology, but due to the filming property not #, The quality of the finished product is unstable, and the adsorption efficiency is limited and cannot be promoted. Soil == Condition 'This invention is based on Shixiazao soil. Shishizao & II: μ, the material is buried underground, collapsed After the solution, the large hollow particles from the remaining ^ ^ 乂 edge, the average particle size is about 1 5 / 4 m up and down (1 0 η Γ porous with acid salts can be seen by two electron microscope ^ Q see Annex I), due to The diatomaceous earth has a high porosity, a porosity of up to 80% or more, and an adsorption force. It is a filter material and can be used as a source of human trace elements. Shiyuezao soil i food grade and industry..., mainly depends on the other oxygen dioxide = 1曰2, the crystallinity of the grade-grade algae soil must be below 3%, and it is not used as the production I. For food and feed, it can be good: the pesticide and beverage industry has been assisted by the process, and the effect is very good, and the scorpion soil has a higher crystallinity, mainly because of the crust. The action of the squeezing mountain causes recrystallization, and its use is as a filling $, a turbidity remover/deodorant, and an explosive. The suction = ^ study pointed out that the diatomaceous earth has a certain degree of organic matter and inorganic matter = f, the absorption and adsorption of proteins, sugars, fats and microbial cells can be filtered in the beverage industry. It has been confirmed; in the case of inorganic substances such as gold L, some studies have pointed out that diatomaceous earth has certain adsorption effects on some heavy metals, such as cations and chromium. In the arsenic-containing waste liquid, Shi Xisheng + ^ points is the arsenate ion (AS〇4 3_), so the surface modified by the surface can achieve better results of arsenic removal. Lu's algae soil can be divided into ground diatomaceous earth powder according to the processing procedure.

一般而+ 1267399 修正 曰 案號 93118026 五、發明說明(6) ^繞矽藻土兩類❹研磨矽藻土粉為一經研磨之粉體,其比 面積約在50 m2/g,鬆密度約為〇 · 5 g/cm3 ;煆燒矽藻土 呈為經6 0 0 C咼溫處理之石夕藻土燒結體,粒徑分布寬廣且 不連續性,比表面積約40 mVg,鬆密度在〇. 6g/cm3上 ,其粒徑分布如第一圖所示。為避免使用於過濾技術時 力損失過大,故於本發明中,採用顆粒較大之燒矽藻 土為吸附劑載體。 ’、 人因此,本發明人將氫氧化鐵及矽藻土之特性加以結 :,利用溼式表面處理製出對砷具吸附性之矽藻土濾材。 發明主要係以煆燒矽藻土為吸附劑擔體,於表面上形 ,別對神酸離子具吸附力之氫氧化鐵活性層,以提供用以 免理含砷廢水,不但可避免含砷污泥產生’並且可大幅 ^吸附劑成本(估算產製成本在每公斤新台幣3〇元以下, ^商用GEH每公斤新台带132元相較,可節省8〇 【實施方式】 有關本發明為達預期之功效及目的, 之實施例詳加說明如下·· 平1 >1订 首先,吻參閱第二圖所示之流程,本發明所提供之吸 :性矽藻土濾材製備方法主要包括調製鐵鹽溶液、混入矽 涂土浸泡、調整酸鹼度、靜置熟化及脫水乾燥等步驟: ()製備鐵鹽溶液·此步驟係以氣化鐵鹽為溶質, 溶於水中後形成鐵、、容淡,鈣越、々、右献制〆 马 ^ 人乳现/合及,鐵鹽溶液配製係將8 j .丨 數 化鐵溶於50 0 rn^l之水巾;由於氣化鐵溶於水中為放熱反、 應’故應先將乳化鐵鹽溶入水中,後再以 度為0. 5 Μ ; 跟General + 1267399 Amendment number 93118026 V. Invention description (6) ^ Two kinds of 矽 矽 矽 algae soil 为 矽 algae soil powder is a ground powder, its specific area is about 50 m2 / g, the bulk density is about 〇· 5 g/cm3 ; 煆 矽 矽 呈 呈 呈 呈 呈 呈 呈 呈 呈 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽 矽The particle size distribution on 6 g/cm3 is shown in the first figure. In order to avoid excessive loss of force when used in the filtration technique, in the present invention, the calcined algae having a larger particle size is used as the adsorbent carrier. Therefore, the present inventors have concluded the characteristics of ferric hydroxide and diatomaceous earth by using a wet surface treatment to produce a diatomaceous earth filter material which adsorbs arsenic. The invention mainly adopts an iron hydroxide active layer which is formed on the surface by using simmered diatomaceous earth as an adsorbent carrier, and is suitable for arsenic-containing waste water to avoid arsenic-containing waste water. Mud production 'and can greatly increase the cost of adsorbent (estimated production cost is less than NT$3 per kilogram, ^ commercial GEH is comparable to 132 yuan per kilogram of new station, saving 8〇 [Embodiment] The expected effect and purpose, the embodiment is described in detail as follows: · 1 1 First, the kiss refers to the flow shown in the second figure, the present invention provides a method for preparing the diatomaceous earth filter material mainly including modulation Iron salt solution, mixing with slag coating, adjusting pH, standing and curing, and dehydration drying: () Preparation of iron salt solution · This step uses gasified iron salt as solute, dissolved in water to form iron, and light , calcium, 々, right 〆 〆 ^ ^ human milk now / combined, iron salt solution preparation system will be 8 j. 丨 number of iron dissolved in 50 0 rn ^ l water towel; because the gasification of iron dissolved in water In order to release the heat, the emulsified iron salt should be dissolved into the water first. 5至Μ ;

第13頁 1267399Page 13 1267399

\一)矽藻土前處理:於此步驟中,首先將工業級煆 燒:藻土過篩分選,取30〜7〇目範圍之顆粒為主原料,進 行β洗處理,為確保清除孔隙内雜質,本發明採用超音波 震盪清洗技術; ^三)浸泡矽藻土 :此步驟係將經步驟(二)前處理 之碎藻土混入步驟(一)所配製的鐵鹽溶液浸泡;為確保 石夕篇土顆粒與溶液之平均接觸,並將孔隙中空氣驅出,浸 泡過程需施以慢速攪拌混合,攪拌速率在7,浸泡時 間最好為二小時; (四) 加入氫氧化鈉溶液調整酸鹼度··於前項溶液中 加入20%之氫氧化鈉鹼液,將pH值調整至1.5至3.0,又其 中pH值在2± 〇·ι反應效果最佳;又為確保反應均勻,並為 避免氫氧化鐵覆膜被沖散,在加入氫氧化鈉鹼液的同時, 需施以慢速攪拌,轉速為70 rpm,反應時間最好為4小 時; (五) 靜置熟化:待攪拌反應完成後,令矽藻土於步 驟(四)之液體中靜f ’使氫氧化鐵吸附層穩定成熟,靜置 時間最好為1 2小時; (六) 固液分離及清洗:因粒狀煆燒石夕藻土之沉降速 度遠高於氫氧化鐵#羽’故於分離前需施以輕微攪拌,令 多餘之氫氧化鐵朦羽懸浮於液體中,經3 0秒等待時間,待 碎藻土沉降後,再以傾析方式進行第一次固液分離,而固 液分離之清洗液又町回流至步驟(一)再利用,又所收集之 矽藻土需再清洗,以去除最後殘留未附著之氫氧化鐵膠羽 與其他雜質;\1) Pretreatment of diatomaceous earth: In this step, the industrial grade simmering: shale is first sieved and sorted, and the granules in the range of 30 to 7 〇 are used as the main raw material, and the β washing is performed to ensure the removal of pores. Intrinsic impurities, the invention adopts ultrasonic oscillating cleaning technology; ^3) immersing diatomaceous earth: this step is to mix the pulverized seaweed pretreated by step (2) into the iron salt solution prepared in step (1); The average contact between the particles of Shixi soil and the solution, and the air in the pores is driven out, the soaking process needs to be mixed with slow stirring, the stirring rate is 7, and the soaking time is preferably two hours; (4) adding sodium hydroxide solution Adjust the pH ● Add 20% sodium hydroxide lye to the solution, adjust the pH to 1.5 to 3.0, and the pH value is 2 ± 〇 · ι. The reaction is optimal; Avoid dissolving the iron hydroxide film. Add sodium hydroxide lye and apply slow stirring at 70 rpm. The reaction time is preferably 4 hours. (5) Static curing: the reaction to be stirred After completion, let the diatomaceous earth in the step ( The liquid in the liquid f 'make the iron hydroxide adsorption layer stable and mature, the standing time is preferably 12 hours; (6) solid-liquid separation and cleaning: due to the sedimentation speed of the granular smoldering stone Ferric hydroxide #羽' Therefore, it needs to be gently stirred before separation, so that the excess iron hydroxide plume is suspended in the liquid, after waiting for 30 seconds, after the sedimentation of the crushed algae, the decantation method is carried out. One solid-liquid separation, and the solid-liquid separation cleaning liquid is returned to the step (1) for reuse, and the collected diatomaceous earth needs to be further cleaned to remove the last remaining unattached iron hydroxide rubber feather and other impurities. ;

1267399 _案號93118026_年月日 修正_ 五、發明說明(8) (七)乾燥:隨後之乾燥程序溫度不宜過高,以防氫氧 化鐵脫水而產生質變,以5 0 ± 2 °C最佳,若乾燥處理至含水 量小於5 %需時約1 2小時(亦可於室溫下自然乾燥,惟需時 甚久較不符經濟效益)。 如上述步驟,經處理而於表面覆蓋鐵鹽之矽藻土,其 含鐵量在1 6 %以上(成份組成如下列表一所示),且所產 製出之以氫氧化鐵覆膜的吸附性矽藻土濾材,特別可供使 用於去除水中之含砷,具有極佳之吸附功效,且覆膜層穩 定,經測試於水態環境中造成之溶鐵現象小於2ppm。1267399 _ Case No. 93118026_年月日日 Revision_ V. Invention description (8) (7) Drying: The subsequent drying procedure temperature should not be too high to prevent dehydration of ferric hydroxide to produce a qualitative change, with a maximum of 50 ± 2 °C Preferably, it takes about 12 hours to dry to a water content of less than 5% (it can also be dried naturally at room temperature, but it takes a long time to be less economical). According to the above steps, the diatomaceous earth covered with iron salt on the surface is treated with iron content of more than 16% (the composition of the composition is shown in the following list 1), and the adsorption of the iron hydroxide film is produced. The diatomaceous earth filter material is especially suitable for removing arsenic in water, has excellent adsorption effect, and the coating layer is stable, and the iron dissolution phenomenon caused by being tested in a water environment is less than 2 ppm.

表一:以氫氧化鐵表面處理後矽藻土之組成成分表 元素 重量百分比[%] 矽Si 26.82 氧〇 45.52 鋁A1 7.59 鐵Fe 16.48 鉀K 1.15 納Na 2.43Table 1: Composition of diatomaceous earth after surface treatment with iron hydroxide Element Weight % [%] 矽Si 26.82 Oxygen 〇 45.52 Aluminum A1 7.59 Iron Fe 16.48 Potassium K 1.15 Na Na 2.43

【處理成效】 本發明人以此法製備出之吸附性矽藻土濾材,進行不 同之吸附測試,吸附測試分為酸鹼度影響實驗及恆溫吸附[Treatment effect] The adsorbent diatomaceous earth filter material prepared by the inventor of the present invention performs different adsorption tests, and the adsorption test is divided into a pH-dependent influence experiment and a constant temperature adsorption.

第15頁 1267399Page 15 1267399

測試兩部分。 首先進行低砷t 珅量為1〇则之配製溶又液;/二吸:與酸鹼度之關係。在含 土濾材,經震i^ β、,| 此入〇· 4 g之吸附性矽藻 如第三圖所示1=出其吸附量對PH值之變化,結果 處理之矽藻土進;^夺對照第四圖所示,其係為未經表面 土用量對吸附實驗結果);而且,不同之梦藻 々一 π Ϊ並無明顯影響。 Τ 由弟 、四圖之對·昭可j | 土對五價石申(砷酸根二::穴經表面覆膜處理之矽藻 酸或鹼性條件下 1 ),、,、月顯之吸附效能,無論於 面處理之石夕簿I 均在3 mg As々上下;反觀經表 為與-般商用ΐ附;::量隨。H值之升高而降低…及附行 1 ·於p Η 2 · 5酸性條件下可逵豆异 曰μ η 2·於中性條件下 達”最大吸附篁40mg As/g ; 3 f 附量亦維持在20mg As“ ; 之两用吸附t,i ’衡所需之時間為38小時,遠低於德國產掣 之商用及附蜊GEH吸附平衡所需之15〇小時。 、 皿吸附測試中’使用不同含坤量之初始溶液 吸附貫…對吸附性石夕藻土之怪溫吸附曲線進行探 始珅濃度分為 3·6、8·2、16·3、44·5、75.4、155 及初 2 6 4ppm。如第五圖所示,其中γ一軸之⑽代表吸附後固體中 (石夕邊土)之珅濃度,單位為㈣As/g矽藻土,χ_軸之Q 代表24小時後液體中之濃度。在中性條件下(pH7 ),經 2 4小時吸附時間後,吸附性矽藻土砷濃度,對水中砷之恆 溫吸附曲線’大略符合F r e n d 1 i c h怪溫吸附模式,於砰初 始濃度為250ppm時’最高吸附量可達63 mg As/g,於低石申Test the two parts. First, the solution of low arsenic t 珅 is 1 〇, and the second solution: the relationship with pH. In the soil-containing filter material, after the shock i ^ β,, | this 〇 · 4 g of the adsorbent diatoms as shown in the third figure 1 = the change in the amount of adsorption to the pH value, the result of the treatment of the algae soil; The fourth figure in the comparison is shown in the figure, which is the result of no adsorption on the surface soil; and the different dreams have no significant effect. Τ By the brother, the four figures of the right · Zhao Ke j | soil to the five-price stone Shen (arsenate II:: the surface of the hole treated by alginic acid or alkaline conditions 1),,,,,,, Efficacy, regardless of the surface treatment of Shi Xi Book I are above 3 mg As々; in contrast, the table is with the general commercial ΐ attached;:: quantity with. Increase in H value and decrease... and appendix 1 · Under p Η 2 · 5 acidic conditions, 逵 曰 iso 曰 μ η 2 · under neutral conditions, "maximum adsorption 篁 40 mg As / g ; 3 f The time required to maintain the adsorption of t, i ' at 20 mg As " is 38 hours, which is much lower than the 15 hours required for the German commercial and the GEH adsorption equilibrium. In the dish adsorption test, the initial solution adsorption of the different concentrations of the sulphate was used to investigate the temperature profile of the adsorbed zephyrite soil. The enthalpy concentration was divided into 3·6, 8·2, 16·3, 44· 5, 75.4, 155 and the initial 2 6 4ppm. As shown in the fifth figure, (10) of γ-axis represents the concentration of lanthanum in the solid after adsorption (Shixiabian soil), the unit is (4) As/g diatomaceous earth, and the Q of χ_axis represents the concentration in the liquid after 24 hours. Under neutral conditions (pH7), after 24 hours of adsorption time, the arsenic concentration of the adsorbed diatomaceous earth and the constant temperature adsorption curve of arsenic in water are roughly in accordance with the F nd id temperature adsorption mode, and the initial concentration of strontium is 250 ppm. At the time of the highest adsorption amount of up to 63 mg As / g, in Shishi Shen

1267399 五1267399 five

L、發明說明(10) 一~^--Ξ----- 漠度時(7ppm),太 附能力。 吸附性矽藻土尚能維持5mg As/g的吸 给从 I -^^3118026^ 論結上述吸附實 吸附性矽藻土, 尸V仔結果,以本發明方法產製出之 發明可提供應梦含砷之去除具有良好之效果,又本 泉水之除砷淨化』匕含產業含砷廢水,以及飲用水、礦 系示JL.戶斤 用目的及功效,ί ί =之實施例確實已能達到所預期之使 具極佳之吸附效益,^明所製備出之吸附性矽藻土濾材, 業或其他工業產生之人^可供用於處理砷化鎵光電元件產 :本案創新的製備J f水、❸用水及礦泉水除砷淨化 ::經濟效益之提昇 :^,且提供產業利用上具 曰賜准提出發明專利已=發明專利之申請 隹專利,則實感德便。之申s月’想請惠予審查,並早L. Description of the invention (10) One ~^--Ξ----- In the case of indifference (7ppm), too attached to the ability. The adsorptive diatomaceous earth can maintain the absorption of 5mg As/g from I-^^3118026^, and the above-mentioned adsorption-adsorbed diatomaceous earth, the result of the corpse V, can be provided by the invention. The arsenic removal of dreams has a good effect, and the arsenic removal of the spring water contains industrial arsenic-containing wastewater, and the drinking water and mineral system show the purpose and efficacy of JL. To achieve the desired adsorption benefit, ^Ming's prepared adsorptive diatomaceous earth filter material, industry or other industrial producers can be used to process gallium arsenide optoelectronic components: the innovative preparation of this case J f Water, hydrazine and mineral water in addition to arsenic purification:: Economic benefits: ^, and provide industrial use of the 曰 曰 提出 提出 提出 提出 提出 提出 提出 = = = = = = = = = 。 发明 发明 。 发明 发明 发明 发明 发明 发明 发明 发明 发明 发明The application of s month ‘I would like to ask for review, and early

苐17頁 1267399 _案號 93118026_年月日__ 圖式簡單說明 【圖式簡單說明】 第一圖所示係為工業級煆燒矽藻土粒徑之重量累積<33分布 圖。 第二圖所示係為本發明之製備流程圖。 第三圖所示係為本發明吸附性矽藻土砷吸附量對pH值之關 係圖。 第四圖所示係為未經處理之矽藻土砷吸附量對pH值之關係 圖。苐17 pages 1267399 _ Case number 93118026_年月日日__ Simple description of the drawing [Simple description of the diagram] The first figure shows the weight accumulation <33 distribution map of the industrial grade 煆 矽 矽 土 粒径 。 The second figure shows the preparation flow chart of the present invention. The third figure shows the relationship between the adsorption amount of arsenic in the adsorbed diatomaceous earth and the pH value. The fourth figure shows the relationship between the arsenic adsorption amount of untreated diatomaceous earth and the pH value.

第五圖所示係為本發明吸附性矽藻土於pH7,24小時之恆 溫吸附曲線圖;其中橫軸為水溶液中砷平衡濃度,縱軸為 砷平衡吸附量。 【附件一】電子顯微鏡下觀察之矽藻土 ·· A. 未經處理之矽藻土粉。 B. 煆燒處理後之矽藻土。The fifth figure shows the adsorption curve of the adsorbent diatomaceous earth of the present invention at pH 7 and 24 hours; wherein the horizontal axis represents the equilibrium concentration of arsenic in the aqueous solution and the vertical axis represents the equilibrium adsorption amount of arsenic. [Annex 1] Algae soil observed under an electron microscope ·· A. Untreated algae powder. B. The algae soil after the simmering treatment.

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Claims (1)

1267399 M3t 9311S09R Λ_Μ 曰 修正 六、申請專利範圍1.本發明係一種吸附性濾材的製備方法,其製備步 為 驟 (一)調製鐵鹽溶液; (一)將锻燒石夕藻土過篩、分選並清洗; (三) 將矽藻土置入鐵鹽溶液中浸泡; (四) 加入氫氧化鈉溶液以調整pH :把氫氧化鈉Λ ,溶液中,將ρΗ值調整至“〜3〇, 乳化鈉加 應,令氫氧化鐵生成; ’幵、,攪拌反 (五) 靜置成熟:將矽藻土於氫氧化鈉溶液中靜 置,使產>生之氫氧化鐵成熟附著於石夕藻土表面及孔洞中; (六) 固液分離:將成熟之矽藻土以過濾及沉澱之 方式與溶液分離,並清浩石夕蘿土 μ w t 其他雜質; Χ β冼矽属土上附者之虱虱化鐵膠羽與 (七) 乾燥··於48t〜52t溫度下使矽藻土乾燥, 即得最終產品。 、2.如申請專利範圍第丨項所述一種吸附性濾材的製備 方法,其中步驟一鐵鹽溶液之配製係將81· lg之 於50〇ml水中’待其完全溶解放熱後,再以水稀釋至 度為0. 5 Μ。 、3·如申請專利範圍第丨項所述一種吸附性濾材的製備 方法,其中步驟二係採用工業級煆燒矽藻土,並取粒徑在 30〜70 mesh之顆粒為原料。 、4 ·如申清專利範圍第1項所述一種吸附性濾材的製備 方法,其中步驟二矽藻土清洗程序以強力攪拌及超音波方1267399 M3t 9311S09R Λ_Μ 曰 Amendment 6. Patent application scope 1. The present invention is a method for preparing an adsorbent filter material, the preparation step is the first step (1) modulating the iron salt solution; (1) sifting the calcined stone Sorting and cleaning; (3) immersing the diatomaceous earth in the iron salt solution; (4) adding sodium hydroxide solution to adjust the pH: Λ sodium hydroxide, solution, adjust the value of ρΗ to “~3〇 , emulsified sodium should be added to make iron hydroxide; '幵,, stirring, reverse (5), standing still: the diatomaceous earth is allowed to stand in the sodium hydroxide solution, so that the ferric hydroxide produced by the > (6) Solid-liquid separation: Separation of the mature diatomaceous earth from the solution by filtration and precipitation, and Qinghaoshi Xiluo soil μ wt other impurities; Χ β冼矽 genus Attached to the bismuth iron powder and (7) Drying · Drying the diatomaceous earth at a temperature of 48t~52t, that is, the final product. 2. An absorbent filter material according to the scope of the patent application. Preparation method, wherein step one is combined with iron salt solution The method for preparing an adsorbent filter material according to the above-mentioned item is as follows: after the heat is dissolved in 50 〇ml of water to be completely dissolved and exothermic, and then diluted with water to a degree of 0.5 Μ. In the second step, the industrial grade simmered diatomaceous earth is used, and the granules having a particle size of 30 to 70 mesh are used as raw materials. 4, and the preparation method of the adsorbent filter material according to the first item of the patent scope of Shenqing, wherein Step 2: The diatomaceous earth cleaning program is strongly stirred and ultrasonic. 第19頁 1267399 案號 93118026 yj /、:申請專利範^ ' ' ' ---复正 式確實將藏於孔隙中之細粉雜質洗出。 5. 如申請專利範圍第1項所述一種吸附 方法,其中步驟三矽藻土浸泡於鐵鹽溶液吐慮材的製備 速為70rpm之慢速攪拌。 寻’需施以轉 6. 如申請專利範圍第5項所述一種吸附 方法,其中矽藻土浸泡於鐵鹽溶液時間為2小=。才的製傷 、7·如申請專利範圍第丨項所述一種吸附性濾材的製備 方法’其中步驟四所加入之氫氧化鈉鹼液濃度為2〇%,並 將pH值調整在1.9〜2.1。 8 ·如申請專利範圍第7項所述一種吸附性濾材的製備 方法,其中步驟四加入之氳氧化鈉鹼液之同時需施以轉速 為70rpm之慢速攪拌。 9 ·如申請專利範圍第7項所述一種吸附性濾材的製備 方法,其中步驟四添加氫氧化鈉鹼液之同時需持續攪拌, 時間為4小時。 I 0 ·如申請專利範圍第1項所述一種吸附性濾材的製備 方法’其中步驟五之靜置時間為1 2小時。 II ·如申請專利範圍第1項所述一種吸附性濾材的製備 方法,其中步驟六之固液分離,利用石夕藻土與膠羽沉降速 度之差異,將溶液稍加攪拌後以傾析方式分離。 1 2 ·如申請專利範圍第1項所述一種吸附性慮材的製備 方法,其中步驟六之固液分離後之液體可回流至步驟一再 利用。Page 19 1267399 Case No. 93118026 yj /,: Applying for a patent ^ ' ' ' --- The complex positive method does wash out the fine powder impurities hidden in the pores. 5. An adsorption method according to claim 1, wherein the step three diatomaceous earth is immersed in the iron salt solution to prepare a slow stirring at a speed of 70 rpm. Seek to need to be transferred. 6. An adsorption method as described in claim 5, wherein the diatomaceous earth is immersed in the iron salt solution for 2 hours =. Injury, 7. The preparation method of an adsorbent filter according to the scope of the patent application, wherein the concentration of sodium hydroxide lye added in step 4 is 2%, and the pH is adjusted to 1.9~2.1. . 8. A method of preparing an adsorptive filter material according to claim 7, wherein the step 4 is carried out by adding a slow stirring at a rotation speed of 70 rpm while adding the bismuth oxide lye. 9. A method for preparing an adsorbent filter according to claim 7, wherein the step 4 is carried out while adding sodium hydroxide lye for a period of 4 hours. I 0 The preparation method of an adsorptive filter material according to the first aspect of the invention is in which the standing time of the step 5 is 12 hours. II. The preparation method of an adsorbent filter material according to the first aspect of the patent application, wherein the solid-liquid separation in step 6 utilizes the difference in the sedimentation speed of the stone and the plume, and the solution is slightly stirred and then decanted. Separation. 1 2 The method for preparing an adsorbent material according to the first aspect of the invention, wherein the liquid after the solid-liquid separation in the step 6 can be refluxed to the step of reuse. 第20頁 1267399Page 20 1267399
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US9994461B2 (en) 2011-12-16 2018-06-12 Helen Of Troy Limited Gravity filter

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US9994461B2 (en) 2011-12-16 2018-06-12 Helen Of Troy Limited Gravity filter

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