TW201408602A - Full resource recycling treatment technique for waste cutting oil - Google Patents

Full resource recycling treatment technique for waste cutting oil Download PDF

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TW201408602A
TW201408602A TW101129664A TW101129664A TW201408602A TW 201408602 A TW201408602 A TW 201408602A TW 101129664 A TW101129664 A TW 101129664A TW 101129664 A TW101129664 A TW 101129664A TW 201408602 A TW201408602 A TW 201408602A
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flotation
slurry
cutting oil
oil
particles
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TW101129664A
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TWI481569B (en
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Ya-Min Hsieh
Mei-Fang Wu
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Ya-Min Hsieh
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Abstract

The present invention provides a full resource recycling treatment technique for waste cutting oil, which can recover three products: oil product, silicon micro-particles and silicon carbide micro-particles. The principle of the full resource recycling technique is described as follows: firstly, according to the oil being liquid, carrying out a solid-liquid separation of the waste cutting oil to separate oil from sludge, wherein the oil can be degraded to carry out secondary industrial utilization or can be incinerated to recover heat value, and the sludge is treated with a floating selection and contains silicon and silicon carbide as main components thereof; then according to the hydrophobic property of the surface of silicon particle and under the condition of controlled acidic pH value of coagulating silicon carbide particles, using a floating selection method to separate two solid components; extracting silicon from the floated ore and extracting silicon carbide from the precipitated ore; and using multiple fining selections to purify the floated ore and the precipitated ore step by step for obtaining two products: silicon having a grade of 99% and silicon carbide having a grade of 99.0%, thereby capable of being used in ceramic raw material or secondary industrial utilization of the same purpose.

Description

廢切削油的全量資源化處理技術 Full-scale resource processing technology for waste cutting oil

本發明係有關於一種廢切削油的全量資源化處理技術。 The invention relates to a full-scale resource treatment technology for waste cutting oil.

「矽晶圓」(Silicon Wafer)就是積體電路製造業使用之矽晶片,因為其形狀為圓形,故稱為矽晶圓,矽晶圓經加工製作成各種電路元件結構,而成為有特定電性功能之積體電路(Integrated Circuit,IC)產品,如:矽晶圓片經過沈澱、蝕刻、加溫、光阻處理、塗佈、顯影等數百道加工程序,製成數十到數百顆的積體電路(IC),經半導體封裝與測試工廠完成測試、切割及封裝後,產生半導體成品,再交由電腦、主機板以及行動電話等各種不同產業之製造業者,生產各種消費型電子產品,矽晶圓製造業是影響我國積體電路產業最重要的一個環節,民國89年以後,台灣的矽晶圓材料自給率已逐步提高,包括:中德電子、台灣信越、台灣小松、合晶科技、中美矽晶、漢磊、嘉晶、昇陽科技、金敏晶研及尚志半導體等十家,主要供應8吋與6吋之磊晶片、拋光片、研磨片與再生矽晶圓片為主。 "Silicon Wafer" is a silicon wafer used in the integrated circuit manufacturing industry. Because it has a circular shape, it is called a germanium wafer. The germanium wafer is processed into various circuit component structures to become specific. Electrically integrated circuit (IC) products, such as: 矽 wafers after centrifugation, etching, heating, photoresist processing, coating, development and other hundreds of processing procedures, made dozens to several Hundreds of integrated circuits (ICs), after being tested, cut and packaged by semiconductor packaging and test factories, produce finished semiconductor products, and then handed them to manufacturers in various industries such as computers, motherboards and mobile phones to produce various consumer types. Electronic products, silicon wafer manufacturing is the most important part of China's integrated circuit industry. After the Republic of China, the self-sufficiency rate of silicon wafer materials in Taiwan has gradually increased, including: Sino-German Electronics, Taiwan Shin-Etsu, Taiwan Komatsu, Hejing Technology, Zhongmei Jingjing, Hanlei, Jiajing, Shengyang Technology, Jinmin Jingyan and Shangzhi Semiconductor, etc., mainly supply 8吋 and 6吋 of the wafer, polished, polished and regenerated矽 Wafer-based.

晶圓加工製程之切片作業在於將矽單晶棒切成矽晶圓薄片,切片厚度一般在600~800μm(少數400~600及800~1000μm),而太陽能切片厚度則為200~300μm,晶圓切割過程係利用線切割機(Wire Saw)在晶棒裁切與晶圓切 片過程須加入由切削粉(碳化矽SiC)與切削油(Epoxy、Glycol)混合之切削劑作為冷卻用途,用以帶走切割過程產生的熱,以提高產品良率,其中Wire Saw所使用的SiC粉粒度為#1000及#1200(相當於10~15μm),因此切片生產單元產生廢切削油的成分為以下四種:10~15μm碳化矽顆粒、切削油(Epoxy、Glycol)、矽屑、線鋸溶出的微量鐵離子。 The wafer processing process is to slice the tantalum single crystal rod into a silicon wafer. The thickness of the slice is generally 600~800μm (a few 400~600 and 800~1000μm), while the thickness of the solar slice is 200~300μm. The cutting process uses wire saws (Wire Saw) for ingot cutting and wafer cutting The chip process must be added with a cutting agent mixed with cutting powder (SiC) and cutting oil (Epoxy, Glycol) for cooling purposes to take away the heat generated by the cutting process to improve product yield, which Wire Saw uses. The particle size of SiC powder is #1000 and #1200 (equivalent to 10~15μm), so the components of waste cutting oil produced by the slicing production unit are the following four types: 10~15μm niobium carbide particles, cutting oil (Epoxy, Glycol), antimony chips, Trace iron ions eluted from the wire saw.

矽晶圓製造業使用的切削油則屬於磨料切削用之水溶性切削油,廢棄的水溶性切削油,需先採取生物處理、酸化分離、化學混凝分離、熱解分離、電解浮除分離、超過濾濃縮分離或冷凍分離等處理方法,再進行二級生物處理。 The cutting oil used in the wafer manufacturing industry is a water-soluble cutting oil for abrasive cutting. The waste water-soluble cutting oil needs to be biologically treated, acidified, chemically coagulated, pyrolyzed, and electrolyzed. Treatment methods such as ultrafiltration, concentration separation or freeze separation, followed by secondary biological treatment.

由於廢棄切削油污染濃度非常高,直接排入廢水處理場,將造成廢水處理系統負荷大增,影響處理水水質,多數工廠會將廢液予以單獨收集貯存或委託廢棄物代處理業處理,有些工廠採用蒸發濃縮後再委外處理方式,可將切削油濃縮至原有體積的1/10以下。 Due to the high concentration of waste cutting oil, direct discharge into the wastewater treatment plant will increase the load on the wastewater treatment system and affect the quality of the treated water. Most factories will collect and store the waste liquid separately or entrust the waste treatment industry. Some The factory adopts evaporation and concentration and then external treatment, which can concentrate the cutting oil to less than 1/10 of the original volume.

一般將去除切削油的金屬粉屑、油脂及其他雜質之處理技術稱為「過濾」,但事實上應細分為「過濾」和「分離」兩種不同的處理技術,廢切削油過濾與分離之設備,分離技術是利用欲分離物的物理特性(如比重不同),來去除切削油中的雜質,過濾技術則是利用濾材來濾除切削油的固態雜質,分離 技術中最簡易的方法,乃是利用收集切削油的貯存槽做為固體雜質之沉澱槽,讓經加工機器流出含粉屑的切削油,在未被重複流回機器前,在貯存槽中利用靜置沉澱方式,讓切削油中大顆粒的粉屑沉澱於槽底,再以人工方式剷除,或利用貯槽內置放可提式濾網收集籃以收集清除沉澱之粉屑,但仍有些較細小的粉塵屑會落在收集籃外,尚需進一步以人工方式剷除,如欲徹底清除粉塵屑則需關閉機器,先排空槽內的切削油,方可進行粉屑的清除,相當耗費人力及時間,並會影響機械設備的生產力。 Generally, the treatment technology for removing metal dust, grease and other impurities from cutting oil is called "filtration", but in fact it should be subdivided into two different treatment technologies: "filtration" and "separation". Waste cutting oil filtration and separation Equipment, separation technology is to use the physical properties of the separation object (such as different specific gravity) to remove impurities in the cutting oil, the filtration technology is to use the filter material to filter the solid impurities of the cutting oil, separation The easiest way to do this is to use a storage tank that collects cutting oil as a sedimentation tank for solid impurities, allowing the processing machine to flow out the cutting oil containing the dust, and use it in the storage tank before it is repeatedly returned to the machine. The sedimentation method is allowed to settle the large particles of the cutting oil in the bottom of the tank, and then manually removed, or the detachable filter collection basket is built in the storage tank to collect the powder for removing the sediment, but still some small. The dust will fall outside the collection basket and need to be further removed manually. If you want to completely remove the dust, you need to turn off the machine and empty the cutting oil before you can remove the dust. It is very labor-intensive. Time and will affect the productivity of mechanical equipment.

由於切削油中含有氣泡、油滴及其他化學物質使得粉屑的沉降速度減緩,一般孔徑大於15微米的粒子在7~10分鐘可以沉降,但是小於15微米的金屬粉屑則需更長的時間才能沉降,甚至無法利用自然重力沉澱去除,因此,現有水力分離器(Hydro-cyclons)、遠心分離機(Screw Decanter Centrifuge)及磁力分離機等設備,水力分離器乃是利用離心力,使比重較大的粉屑等物質從比重較小的切削油中分離去除,藉由切削油流入分離機時的流速產生旋轉渦流,使切削油中的金屬粒子因離心力作用被拋移到裝置外緣,且外緣的渦流方向向下,使得金屬粒子被引減至分離機底部,潔淨的切削油則會由分離機的中央部份向頂部湧出,因分離機的渦流速度取決於切削油進流速度,所以進流速 度愈快則分離效果愈佳,遠心分離機是用來分離二種以上的不同粉屑,同樣利用比重不同的性質進行不同轉速的分離,產生的離心力,就可以將固體與液體分離出來。 Due to the inclusion of bubbles, oil droplets and other chemicals in the cutting oil, the sedimentation speed of the dust is slowed down. Generally, particles with a pore diameter of more than 15 microns can settle in 7 to 10 minutes, but metal dust of less than 15 microns takes longer. It can be settled or even removed by natural gravity sedimentation. Therefore, existing hydraulic separators (Hydro-cyclons), telecentric separators (Screw Decanter Centrifuge) and magnetic separators, etc., hydraulic separators use centrifugal force to make the specific gravity larger. The powder and the like are separated and removed from the cutting oil having a small specific gravity, and the swirling vortex is generated by the flow velocity when the cutting oil flows into the separator, so that the metal particles in the cutting oil are thrown to the outer edge of the device by the centrifugal force, and The vortex direction of the edge is downward, so that the metal particles are led to the bottom of the separator, and the clean cutting oil will flow from the central part of the separator to the top, because the vortex speed of the separator depends on the cutting oil inflow speed, so Inlet velocity The faster the degree, the better the separation effect. The telecentric separator is used to separate two or more different kinds of dust. The same speed is used to separate the different speeds, and the centrifugal force generated can separate the solid and the liquid.

矽晶圓片製造業所產生的無機污泥雖然含有Si及SiC,但目前國內再利用實績屬萌芽階段,幾乎業者均委由清除處理機構採掩埋處理。 Although the inorganic sludge produced by the wafer manufacturing industry contains Si and SiC, the current domestic recycling performance is in its infancy, and almost all of them are disposed of by the cleaning and processing institutions.

學術研究方面對於含Si及SiC污泥,建議使用以下一般無機污泥資源化方式來處理。 For academic research, it is recommended to use the following general inorganic sludge recycling method for Si and SiC sludge.

A.再利用於水泥原料 A. Reuse in cement raw materials

純的Si可分成無定形體及結晶體,前者可在空氣中燃燒,而後者的熔點在1410℃,沸點2480℃,SiC則在2210℃分解,由於從矽晶圓片製造產生的Si及SiC含有相當多的雜質,而且又在含氧量豐富的水泥窯中燃燒,理應會和氧作用而形成SiO2,SiO2是水泥的主成分,因此Si及SiC污泥可做為水泥原料使用。 Pure Si can be divided into amorphous and crystalline, the former can be burned in air, while the latter has a melting point of 1410 ° C, a boiling point of 2480 ° C, and SiC is decomposed at 2210 ° C, due to the formation of Si and SiC from the manufacture of tantalum wafers. Quite a lot of impurities, but also in the oxygen-rich cement kiln burning, should be combined with oxygen to form SiO 2 , SiO 2 is the main component of cement, so Si and SiC sludge can be used as cement raw materials.

B.再利用於燒製陶瓷時之柵板 B. reused in the grid when firing ceramics

柵板是在燒陶瓷時放置坯體的耐火板,這種耐火板的特性是要耐高溫、熱傳導快及不易變形等要素,以前都用謨萊石(Mullite),現在都改用SiC板,Si及SiC污泥也含有Al2O3及SiO2、ZrO2均為耐火的材料,因此也可做成柵板使用。 The grid plate is a refractory plate in which the body is placed when the ceramic is fired. The characteristics of the refractory plate are high temperature resistance, fast heat conduction and deformation resistance. Previously, the mullite was used, and now the SiC plate is used. Si and SiC sludges also contain Al 2 O 3 , SiO 2 , and ZrO 2 which are both refractory materials. Therefore, they can also be used as grid plates.

C.再利用於磚塊原物料 C. Reuse of brick raw materials

由於無機性污泥主要成分與製磚原料土相似,因此 可取代部分的原料,其再利用方式係使用污泥摻配於製磚用土中作為資源再利用的方法。 Since the main components of inorganic sludge are similar to brick raw materials, A part of the raw material can be replaced, and the recycling method is a method in which the sludge is blended into the soil for brick making as a resource.

D.再利用於人工骨材原物料 D. Reuse of artificial aggregate raw materials

再利用機構係將廢棄物再生成人工骨材,為了使非有害性污泥易與水泥結合,並在最短的時間內達到抗壓強度之原理,乃是於製造過程中,視狀況加水成流動性污泥後,加入專利污泥固化劑,此使內部含水成結晶水狀態而非揮發,並加速污泥內部水份劇減,濕潤污泥改質污泥粒子期間的表面張力,使水泥易與污泥結合而達到固化的目的。 The recycling mechanism regenerates the waste into artificial aggregates. In order to make the non-harmful sludge easy to bond with the cement and achieve the compressive strength in the shortest time, it is in the manufacturing process, depending on the situation, the water is added to the flow. After the sludge is added, the patented sludge solidifying agent is added, which makes the internal water into a state of crystallization water instead of volatilization, and accelerates the drastic reduction of the internal moisture of the sludge, and the surface tension during the process of modifying the sludge particles by the wet sludge makes the cement easy Combined with sludge to achieve the purpose of curing.

本發明之主要目的係在提供一種廢切削油的全量資源化處理技術,可以回收油產品、以及微細顆粒矽與碳化矽等三種產品,可以作為燃油、陶瓷原料等,或二次工業利用。 The main object of the present invention is to provide a full-scale resource treatment technology for waste cutting oil, which can recover oil products, micro-particles and tantalum carbide, and can be used as fuel oil, ceramic raw materials, etc., or secondary industrial utilization.

本發明之廢切削油的全量資源化處理技術,係將廢切削油經過固液分離,使油與污泥分離,油可降階進行二次工業利用,或焚化回收熱值,而污泥以浮選處理,從浮礦取出產物矽,沉礦取出產物碳化矽,可以做為二次陶瓷原料使用。 The full-scale resource treatment technology of the waste cutting oil of the invention is that the waste cutting oil is separated by solid-liquid separation to separate the oil from the sludge, the oil can be reduced to the secondary industrial utilization, or the incineration is used to recover the calorific value, and the sludge is Flotation treatment, the product is taken out from the floating ore, and the product carbonized bismuth is taken out from the sinking ore, which can be used as a secondary ceramic raw material.

本發明之固液分離是以取出含油量30%以下的污泥為目的,避免過量油妨礙碳化矽與矽的浮選分離,固液分離的方式可以為靜置沉澱、壓濾、加熱乾燥。 The solid-liquid separation of the present invention is for the purpose of taking out sludge having an oil content of 30% or less, and avoids excessive oil from interfering with the flotation separation of niobium carbide and niobium. The solid-liquid separation method may be static precipitation, pressure filtration, or heat drying.

本發明之該浮選處理包含擦洗處理、礦漿調整、多次精選等先後處理步驟。 The flotation treatment of the present invention comprises sequential treatment steps such as scrubbing treatment, slurry adjustment, and multiple selection.

本發明之該擦洗處理是將污泥置入擦洗槽,加少量水至擦洗葉片可作用高度即可,以高轉速擦洗,使污泥顆粒與顆粒之間充分磨擦,此作用可以將顆粒表面的油污擦除,裸露出顆粒表面,來與浮選藥劑發生反應,以1500rpm轉速下擦洗時間至少5分鐘以上。 The scrubbing treatment of the present invention is to put the sludge into the scrubbing tank, add a small amount of water to the scrubbing blade to work at a height, scrub at a high speed, and fully rub the sludge particles and the particles, which can act on the surface of the particle. The oil is wiped off, the surface of the particles is exposed to react with the flotation reagent, and the scrubbing time is at least 1500 rpm for at least 5 minutes.

本發明之該礦漿調整是將擦洗後的礦漿依序加入少量的調整劑、捕集劑煤油、起泡劑、水,使矽顆粒的表面與調整劑反應,強化表面疏水性,利於煤油捕集,同時利用調整劑控制礦漿pH值於2-3,利於碳化矽凝聚沉降,調整劑可以為氟酸或鹽酸混合酸,適量添加以調整pH,煤油添加量以0.2ml/100g礦石為佳,水添加量視礦漿濃度而定,礦漿濃度以10-30%為佳。 The slurry adjustment of the present invention is to sequentially add a small amount of adjusting agent, collector kerosene, foaming agent and water to the scrubbed pulp, so that the surface of the cerium particles reacts with the adjusting agent to strengthen the surface hydrophobicity, which is favorable for kerosene capturing. At the same time, the adjusting agent is used to control the pH value of the slurry to 2-3, which is beneficial to the coagulation and sedimentation of the niobium carbide. The adjusting agent can be a mixed acid of hydrofluoric acid or hydrochloric acid, and the appropriate amount is added to adjust the pH. The amount of kerosene added is preferably 0.2 ml/100 g ore. The amount of addition depends on the concentration of the slurry, and the concentration of the slurry is preferably 10-30%.

本發明之該多次精選是將浮選後的浮礦或沉礦,再投入浮選槽,每次調整礦漿使礦漿達到前述較佳條件,再次浮選,利用多次精選可以逐步提高品位,浮礦在三次精選後可以獲得較佳的產物,矽品位98.5-99%,沉礦在三次精選後可以獲得較佳的產物,碳化矽品位98-99%。 The plurality of selections of the present invention are to put the flotation or sedimentation after flotation into the flotation tank, and adjust the slurry to make the slurry reach the above-mentioned better conditions, and then float again, and the selection can be gradually improved by using multiple selections. After three times of selection, the flotation can obtain a better product, the grade of 98.5-99%, and the better selection of the precipitate after three times of selection, the grade of niobium carbide is 98-99%.

本發明之該多次精選由於多次浮選操作的礦漿用水含有浮選藥劑,將浮礦漿或沉礦漿,可以循環 水使用,節省藥劑及用水,浮礦漿的顆粒微細僅數個微米,比較不易過濾,可以控制較佳脫水條件在pH2-3間,加入PVA(聚乙烯醇)200ppm以上進行混凝,有利於其過濾脫水操作效率,沉礦漿的顆粒大小約十多微米,浮選條件已適合其凝聚,直接可以快速過濾脫水。 The plurality of selections of the slurry for the multiple flotation operation include a flotation agent for the water, and the floating slurry or the slurry can be recycled. Water use, saving chemicals and water. The particles of floating pulp are only a few micrometers, which is relatively difficult to filter. It can control the better dehydration conditions. It can be mixed with PVA (polyvinyl alcohol) more than 200ppm for coagulation under pH 2-3, which is beneficial to its use. Filtration dewatering operation efficiency, the particle size of the slurry is about ten micron, the flotation condition is suitable for its coagulation, and it can directly filter and dehydrate.

有關本發明為達上述之使用目的與功效,所採用之技術手段,茲舉出較佳可行之實施例,並配合圖式所示,詳述如下:本發明係在提供一種廢切削油的全量資源化處理技術,可以回收油產品、以及微細顆粒矽與碳化矽等三種產品,全量資源化處理技術原理說明如下,如圖1所示,首先依據油是液體,將廢切削油經過固液分離,使油與污泥分離,油可降階進行二次工業利用,或焚化回收熱值,而污泥方面再進行浮選處理,污泥組成物以碳化矽與矽為主,依據矽顆粒表面的疏水性質、以及在控制碳化矽顆粒凝聚的酸性pH值下,以浮選法分離兩種固體成分(~1微米的矽顆粒、~15微米的碳化矽顆粒),從浮礦中取出矽,從沉礦中取出碳化矽等產品,利用多次精選逐步純化浮礦與沉礦,分別可以獲得矽品位99%,以及碳化矽品位99.0%的兩種產品,可以作為陶瓷原料及二次工業利用。 The present invention is directed to a preferred embodiment of the present invention in order to achieve the above-mentioned objects of use and efficacy. The present invention is described in detail with reference to the drawings. The present invention provides a full amount of waste cutting oil. Recycling technology can recover oil products, as well as fine particles and tantalum carbide. The principle of full-scale resource treatment technology is as follows. As shown in Figure 1, the waste cutting oil is firstly separated by solid-liquid separation according to the oil being liquid. To separate the oil from the sludge, the oil can be reduced to secondary industrial utilization, or incinerated to recover the calorific value, and the sludge is further subjected to flotation treatment. The sludge composition is mainly composed of niobium carbide and niobium. The hydrophobic properties, and the acidic pH at which the cerium carbide particles are controlled, the two solid components (~1 micron cerium particles, ~15 micron cerium carbide particles) are separated by flotation, and the hydrazine is taken out from the floating ore. The products such as tantalum carbide are taken out from the sinking ore, and the floatation and sedimentation are gradually purified by multiple selections, and two products of 99% of tantalum grade and 99.0% of grade of tantalum carbide can be obtained respectively, which can be used as ceramic raw materials and Sub industrial use.

依據廢切削油組成物質全量化驗結果,得知廢切削油組成物質(如表1),由於廢切削液是高科技 產業的廢棄物,所以主要成分種類很單純,以揮發分(油)、碳化矽、矽為主,三者含量超過99%以上,其餘微量的鐵、鉀、鈣、銅、鋅等總計在1%以下,將廢切削油乾燥後殘渣進行固體物質分析,以王水及濃氟酸將矽溶解後分析碳化矽的外觀(如圖2A、圖2B所示)以及粒徑分布(雷射粒徑分析),獲知碳化矽的顆粒d50:10-15微米,d25-d75:10~17微米性質,另外從廢切削油乾燥的殘渣中以電子顯微鏡(SEM/EDS)證實矽顆粒約數個微米大小,從廢切削油上層液的濾渣中取出矽,其粒徑分布:d50:1-3微米,d25-d75:0.1~5微米。 According to the full quantitative test results of waste cutting oil constituent materials, the composition of waste cutting oil is known (Table 1). Since waste cutting fluid is waste of high-tech industry, the main components are very simple, with volatile matter (oil) and carbonization. The content of the three is more than 99%, and the remaining traces of iron, potassium, calcium, copper, zinc, etc. are less than 1%. The solid waste material is analyzed after the waste cutting oil is dried, with aqua regia and concentrated. Fluoric acid is used to analyze the appearance of tantalum carbide (as shown in Fig. 2A, Fig. 2B) and particle size distribution (laser particle size analysis) after dissolving bismuth, and it is known that particles of ruthenium carbide d 50 : 10-15 μm, d 25 -d 75 : 10 to 17 micron in nature. In addition, from the residue of the waste cutting oil drying, it was confirmed by electron microscopy (SEM/EDS) that the cerium particles were several micrometers in size, and the cerium was taken out from the slag of the upper layer of the waste cutting oil. d 50 : 1-3 μm, d 25 -d 75 : 0.1 to 5 μm.

由於碳化矽與矽都是很微細,使顆粒表面性質 更顯著,十分適合浮選技術進行分選,將碳化矽與矽投入煤油中,發現矽的表面親油性比碳化矽強,以及文獻指出碳化矽的表面等電點約在pH2-3之間,又根據(表2)碳化矽的沉降實驗發現pH2.57時,沉降時間最短,酸性環境有利於碳化矽的凝聚。 Since the tantalum carbide and niobium are very fine, the surface properties of the particles More significant, it is very suitable for flotation technology for sorting. The tantalum carbide and niobium are put into kerosene, and the surface lipophilicity of niobium is found to be stronger than that of carbonization. The literature indicates that the surface isoelectric point of niobium carbide is about pH2-3. According to the sedimentation experiment of the niobium carbide (Table 2), the sedimentation time is the shortest at pH 2.57, and the acidic environment is conducive to the coagulation of niobium carbide.

將廢切削油靜置數日後,從底部取出底泥(含油量~25%)作為浮選實驗的起始原料,根據浮選條件實驗結果(如圖3A、圖3B、圖3C、圖3D),獲得較佳的浮選條件為:擦洗時間>5min、礦漿濃度10~30wt%、捕集劑<0.2ml/100g礦石、調整劑<2ml/100g,根據表3的浮選實驗結果,利用調整劑氟酸鹽酸混合酸,適量調整至pH~2.3,以捕集劑煤油與起泡劑松節油進行浮選,獲得較佳分選結果:沉礦中碳化矽品位87%、碳化矽回收率85%,浮礦中碳化矽品位18.8%、碳化矽回收率15%(即矽品位81.2%、矽回收率84%)。 After the waste cutting oil was allowed to stand for several days, the sediment (oil content ~25%) was taken out from the bottom as the starting material for the flotation experiment, and the experimental results were based on the flotation conditions (Fig. 3A, Fig. 3B, Fig. 3C, Fig. 3D). The preferred flotation conditions are: scrubbing time>5min, pulp concentration 10~30wt%, collector<0.2ml/100g ore, adjusting agent<2ml/100g, according to the results of flotation experiment in Table 3, using adjustment The ferric acid mixed acid is adjusted to pH~2.3, and the flocculant kerosene and the foaming agent turpentine are floated to obtain better sorting results: 87% of the niobium carbide grade in the sedimentation, and the recovery rate of the niobium carbide is 85. %, the grade of tantalum carbide in the floating ore is 18.8%, and the recovery rate of tantalum carbide is 15% (ie, the grade of tantalum is 81.2%, and the recovery rate of tantalum is 84%).

表3:各pH下浮選實驗結果 條件:起始污泥140g(含油量~25%,乾基污泥重~100g)、SiC~56wt%(乾基含量);煤油0.5ml/100g、松節油0.1ml/100g、調整劑:氟酸鹽酸混合酸、氫氧化鈉。 Table 3: Results of flotation experiments at various pH Conditions: starting sludge 140g (oil content ~25%, dry sludge weight ~100g), SiC~56wt% (dry basis content); kerosene 0.5ml/100g, turpentine 0.1ml/100g, adjusting agent: hydrofluoric acid Hydrochloric acid is mixed with acid and sodium hydroxide.

依據上述浮選條件進行多次精選實驗,結果如表4、表5,經過三次精選就可以從沉礦中獲得碳化矽品位高達98%的產物、回收率99%,另外也將浮礦經過三次精選,獲得純化後的矽產物,矽品位99.3%、回收率98%。 According to the above flotation conditions, a number of selective experiments were carried out. The results are shown in Table 4 and Table 5. After three selections, the product with a tantalum carbide grade of up to 98% can be obtained from the sinking ore, the recovery rate is 99%, and the floating mine is also passed three times. Selected, the purified hydrazine product was obtained, the 矽 grade was 99.3%, and the recovery rate was 98%.

條件:每次起始礦石均為100g,多次浮選而數量不足時重複流程補足起始量,調整pH~2.5(精選實驗流程示意如圖4所示) Condition: Each starting ore is 100g, repeated flotation and the amount is insufficient, repeat the process to make up the initial amount, adjust the pH~2.5 (the selected experimental flow is shown in Figure 4)

條件:每次起始礦石均為100g,多次浮選而數量不足 時重複流程補足起始量,調整pH~2.5(精選實驗流程示意如圖5所示) Condition: Each starting ore is 100g, repeated flotation and the amount is insufficient, repeat the process to make up the initial amount, adjust the pH~2.5 (the selected experimental flow is shown in Figure 5)

(例一) (Example 1)

請參閱圖6所示,將廢切削油經過板框過濾,取出瀝乾污泥120g,其含油量13%、(乾基)碳化矽含量61%、矽39%,經過1500rpm擦洗處理5分鐘使擠壓結成的團聚顆粒充分解開,再調整礦漿至浮選狀態,以浮選條件:礦漿濃度20%、煤油0.2ml/100g礦石、氫氟酸2ml/100g礦石、松節油0.05ml/100g礦石、pH~2.4等進行三次浮選精選,取出浮礦漿經過添加混凝劑200ppm以及在pH<2.5下,利用抽氣過濾脫水,乾燥後獲得矽產物,品位98.5%,精選三次的沉礦漿直接抽氣過濾脫水,乾燥後獲得碳化矽產物,品位99.0%。 Referring to Fig. 6, the waste cutting oil is filtered through the plate frame, and 120 g of the drained sludge is taken out, and the oil content is 13%, (dry basis) strontium carbide content is 61%, 矽 39%, and scrubbed at 1500 rpm for 5 minutes. The agglomerated particles formed by extrusion are fully unwrapped, and the slurry is adjusted to the flotation state for flotation conditions: slurry concentration 20%, kerosene 0.2 ml/100 g ore, hydrofluoric acid 2 ml/100 g ore, turpentine 0.05 ml/100 g ore, Three times flotation selection was carried out at pH~2.4, and the float slurry was taken out by adding 200 ppm of coagulant and at pH <2.5, and dehydrated by suction filtration. After drying, the product was obtained, the grade was 98.5%, and the selected three times of the slurry was directly pumped. The mixture was dehydrated by filtration, and dried to obtain a niobium carbide product with a grade of 99.0%.

(例二) (Example 2)

請參閱圖7所示,將廢切削油底泥經過105度熱風乾燥24hr,取出乾燥污泥粉100g,含油量<0.1%,碳化矽含量55%、矽45%,經過1500rpm擦洗處理10分鐘使污泥顆粒與顆粒之間充分磨擦,以將顆粒表面的油污擦除,裸露出顆粒表面後,再調整礦漿至浮選狀態,以浮選條件:礦漿濃度20%、煤油0.2ml/100g礦石、氫氟酸2ml/100g礦石、松節油0.05ml/100g礦石、pH~2.4等進行三次浮選精選,取出浮礦漿經過添加混凝劑200ppm以及在pH2.3,利用 抽氣過濾脫水,乾燥後獲得矽產物,品位99.1%,精選三次的沉礦漿直接抽氣過濾脫水,乾燥後獲得碳化矽產物,品位98.9%。 Referring to Figure 7, the waste cutting oil sludge is dried by 105 degree hot air for 24 hr, and 100 g of dry sludge powder is taken out, the oil content is <0.1%, the strontium carbide content is 55%, 矽45%, and the rinsing treatment is performed at 1500 rpm for 10 minutes. The sludge particles and the particles are fully rubbed to wipe off the oil on the surface of the particles, and after the surface of the particles is exposed, the slurry is adjusted to a flotation state to float conditions: slurry concentration 20%, kerosene 0.2 ml/100 g ore, Hydrofluoric acid 2ml/100g ore, turpentine 0.05ml/100g ore, pH~2.4, etc., three times flotation selection, take out the floating slurry through the addition of coagulant 200ppm and at pH2.3, use The mixture was dehydrated by suction filtration, and the product was obtained after drying, and the grade was 99.1%. The selected three times of the slurry was directly subjected to air filtration and dehydration, and after drying, the product of niobium carbide was obtained, and the grade was 98.9%.

綜上所述,本發明確實已達到所預期之使用目的與功效,且更較習知者為之理想、實用,惟,上述實施例僅係針對本發明之較佳實施例進行具體說明而已,該實施例並非用以限定本發明之申請專利範圍,舉凡其他未脫離本發明所揭示之技術手段下所完成之均等變化與修飾,均應包含於本發明所涵蓋之申請專利範圍中。 In view of the above, the present invention has achieved the intended use and efficacy, and is more desirable and practical than the prior art, but the above embodiments are only specifically described for the preferred embodiment of the present invention. The present invention is not intended to limit the scope of the invention, and all other equivalents and modifications may be included in the scope of the invention covered by the invention.

圖1所示係為本發明廢切削油的全量資源化處理技術之流程圖。 Figure 1 is a flow chart showing the full-scale resource processing technology of the waste cutting oil of the present invention.

圖2A所示係為碳化矽SEM照片。 Figure 2A shows a SEM photo of ruthenium carbide.

圖2B所示係為廢切削油乾燥殘渣照片(表面附著的顆粒是矽)。 Figure 2B shows a photograph of the dry residue of the waste cutting oil (the surface-attached particles are ruthenium).

圖3A所示係為浮選條件(擦洗時間)下沉礦的碳化矽品位。 Figure 3A shows the grade of tantalum carbide for the sinking of the flotation conditions (scrubbing time).

圖3B所示係為浮選條件(礦漿濃度)下沉礦的碳化矽品位。 Figure 3B shows the grade of tantalum carbide as a sinking condition for flotation conditions (slurry concentration).

圖3C所示係為浮選條件(煤油劑量)下沉礦的碳化矽品位。 Figure 3C shows the grade of tantalum carbide as a sinking condition for flotation conditions (kerosene dosage).

圖3D所示係為浮選條件(調整劑量)下沉礦的碳化矽品位。 Figure 3D shows the grade of tantalum carbide for the sinking condition of the flotation condition (adjusted dose).

圖4所示係為本發明沉礦多次精選實驗之流程示意圖。 Figure 4 is a schematic flow chart of the multiple selection experiments of the sedimentation of the present invention.

圖5所示係為本發明浮礦多次精選實驗之流程示意圖。 Figure 5 is a schematic flow chart showing the multiple selection experiments of the floating ore in the present invention.

圖6所示係為本發明例一之實驗流程示意圖。 Figure 6 is a schematic diagram showing the experimental flow of the first embodiment of the present invention.

圖7所示係為本發明例二之實驗流程示意圖。 Figure 7 is a schematic diagram showing the experimental flow of the second embodiment of the present invention.

Claims (7)

一種廢切削油的全量資源化處理技術,將廢切削油經過固液分離,使油與污泥分離,油可降階進行二次工業利用,或焚化回收熱值,而污泥以浮選處理,從浮礦取出產物矽,沉礦取出產物碳化矽,可以做為陶瓷原料使用或原用途二次利用。 A full-scale resource treatment technology for waste cutting oil, the waste cutting oil is separated by solid-liquid separation, the oil is separated from the sludge, the oil can be reduced to secondary industrial utilization, or the incineration is used to recover the calorific value, and the sludge is treated by flotation The product is taken out from the floating ore and the product is taken out from the ore deposit, which can be used as a ceramic raw material or secondary use for the original purpose. 如申請專利範圍第1項所述之廢切削油的全量資源化處理技術,其中,該固液分離是以取出含油量30%以下的污泥為目的,避免過量油妨礙碳化矽與矽的浮選分離,固液分離的方式可以為靜置沉澱、壓濾、加熱乾燥。 The full-scale resource treatment technology of the waste cutting oil according to the first aspect of the invention, wherein the solid-liquid separation is for the purpose of taking out sludge having an oil content of 30% or less, and avoiding excessive oil hindering the floating of the tantalum carbide and the crucible. Separation and separation can be carried out by static precipitation, pressure filtration and heat drying. 如申請專利範圍第1項所述之廢切削油的全量資源化處理技術,其中,該浮選處理包含擦洗處理、礦漿調整、多次精選等先後處理步驟。 The full-scale resource processing technology of the waste cutting oil according to the first aspect of the invention, wherein the flotation treatment comprises sequential processing steps such as scrubbing treatment, slurry adjustment, and multiple selection. 如申請專利範圍第3項所述之廢切削油的全量資源化處理技術,其中,該擦洗處理是將污泥置入擦洗槽,加少量水至擦洗葉片可作用高度即可,以高轉速擦洗,使污泥顆粒與顆粒之間充分磨擦,此作用可以將顆粒表面的油污擦除,裸露出顆粒表面,來與浮選藥劑發生反應,以1500rpm轉速下擦洗時間至少5分鐘以上。 The full-scale resource processing technology of the waste cutting oil according to claim 3, wherein the scrubbing treatment is to put the sludge into the scrubbing tank, and add a small amount of water to the scrubbing blade to work at a height, and scrub at a high speed. To fully rub the sludge particles and particles, this effect can wipe the oil on the surface of the particles, expose the surface of the particles to react with the flotation reagent, and scrub at 1500 rpm for at least 5 minutes. 如申請專利範圍第3項所述之廢切削油的全量資源化處理技術,其中,該礦漿調整是將擦洗後的礦漿依序加入調整劑、捕集劑煤油、起泡劑、水 ,使矽顆粒的表面與調整劑反應,強化表面疏水性,利於煤油捕集劑,同時利用調整劑控制礦漿pH值於2-3,利於碳化矽凝聚沉降,調整劑可以為氟酸或鹽酸混合酸,適量添加調整pH,煤油添加量以0.2ml/100g礦石為佳,水添加量視礦漿濃度而定,礦漿濃度以10-30%為佳。 The full-scale resource treatment technology of the waste cutting oil according to the third aspect of the patent application, wherein the slurry adjustment is to sequentially add the scrubbed slurry to the adjusting agent, the collector kerosene, the foaming agent, and the water. The surface of the cerium particles is reacted with the adjusting agent to strengthen the surface hydrophobicity, which is beneficial to the kerosene collector, and the adjusting agent is used to control the pH value of the slurry to 2-3, which is favorable for the condensed sedimentation of the cerium carbide, and the adjusting agent may be a mixture of hydrofluoric acid or hydrochloric acid. The acid is added in an appropriate amount to adjust the pH. The amount of kerosene added is preferably 0.2 ml/100 g ore. The amount of water added depends on the concentration of the slurry, and the concentration of the slurry is preferably 10-30%. 如申請專利範圍第3項所述之廢切削油的全量資源化處理技術,其中,該多次精選是將浮選後的浮礦或沉礦,個別再投入浮選槽,重新調整礦漿使礦漿達到前述較佳條件,再次浮選,利用多次精選可以逐步提高品位,浮礦在三次精選後可以獲得較佳的產物,矽品位98.5-99%,沉礦在三次精選後可以獲得較佳的產物,碳化矽品位98-99%。 For example, the full-scale resource treatment technology of the waste cutting oil described in claim 3, wherein the plurality of selections are flotation or sedimentation after flotation, and are separately put into the flotation tank to re-adjust the slurry to make the slurry. To achieve the above-mentioned better conditions, re-flotation, the use of multiple selections can gradually improve the grade, the floating ore can obtain better products after three selections, the grade of 98.5-99%, the sinking can be better after three selections. The product, tantalum carbide grade 98-99%. 如申請專利範圍第6項所述之廢切削油的全量資源化處理技術,其中,該多次精選由於多次浮選操作的礦漿用水含有浮選藥劑,將浮礦漿或沉礦漿脫水,可以循環水使用,節省藥劑及用水,浮礦漿的顆粒微細僅數個微米,比較不易過濾,可以控制較佳脫水條件在pH2-3間,加入PVA(聚乙烯醇)200ppm以上進行混凝,有利於其過濾脫水操作效率,沉礦漿的顆粒大小約十多微米,浮選條件已適合其凝聚,直接可以快速過濾脫水。 The full-scale resource treatment technology of the waste cutting oil according to the sixth aspect of the patent application, wherein the plurality of selected slurry waters containing the flotation operation have a flotation agent, and the floating pulp or the sediment slurry is dehydrated and can be recycled. Water use, saving chemicals and water. The particles of floating pulp are only a few micrometers, which is relatively difficult to filter. It can control the better dehydration conditions. It can be mixed with PVA (polyvinyl alcohol) more than 200ppm for coagulation under pH 2-3, which is beneficial to its use. Filtration dewatering operation efficiency, the particle size of the slurry is about ten micron, the flotation condition is suitable for its coagulation, and it can directly filter and dehydrate.
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Publication number Priority date Publication date Assignee Title
TWI579441B (en) * 2014-10-13 2017-04-21 波斯可公司 Method for producing briquettes and briquettes produced using the same
CN108383353A (en) * 2018-04-23 2018-08-10 宁波联清环保设备有限公司 A kind of useless sludge treatment technology of oil-containing grinding

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TW200827305A (en) * 2006-12-29 2008-07-01 Chung-Wen Lan The recycling method of silicon sludge after slicing
US8231006B2 (en) * 2008-12-31 2012-07-31 Memc Singapore Pte. Ltd. Methods to recover and purify silicon particles from saw kerf

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI579441B (en) * 2014-10-13 2017-04-21 波斯可公司 Method for producing briquettes and briquettes produced using the same
CN108383353A (en) * 2018-04-23 2018-08-10 宁波联清环保设备有限公司 A kind of useless sludge treatment technology of oil-containing grinding

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