TWI504573B - Method and apparatus for recycling and processing of silicon wafer cutting and grinding waste - Google Patents
Method and apparatus for recycling and processing of silicon wafer cutting and grinding waste Download PDFInfo
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- 239000002699 waste material Substances 0.000 title claims description 63
- 238000005520 cutting process Methods 0.000 title claims description 45
- 238000000034 method Methods 0.000 title claims description 43
- 238000004064 recycling Methods 0.000 title claims description 20
- XUIMIQQOPSSXEZ-UHFFFAOYSA-N Silicon Chemical compound [Si] XUIMIQQOPSSXEZ-UHFFFAOYSA-N 0.000 title claims description 17
- 229910052710 silicon Inorganic materials 0.000 title claims description 17
- 239000010703 silicon Substances 0.000 title claims description 17
- 238000000227 grinding Methods 0.000 title claims description 10
- 239000007788 liquid Substances 0.000 claims description 82
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 49
- 239000002202 Polyethylene glycol Substances 0.000 claims description 38
- 229920001223 polyethylene glycol Polymers 0.000 claims description 38
- 239000012065 filter cake Substances 0.000 claims description 26
- 239000012528 membrane Substances 0.000 claims description 24
- 238000000926 separation method Methods 0.000 claims description 24
- 239000010802 sludge Substances 0.000 claims description 21
- 238000001223 reverse osmosis Methods 0.000 claims description 20
- 239000007787 solid Substances 0.000 claims description 18
- 239000003921 oil Substances 0.000 claims description 17
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims description 16
- 229910000420 cerium oxide Inorganic materials 0.000 claims description 15
- BMMGVYCKOGBVEV-UHFFFAOYSA-N oxo(oxoceriooxy)cerium Chemical compound [Ce]=O.O=[Ce]=O BMMGVYCKOGBVEV-UHFFFAOYSA-N 0.000 claims description 15
- 239000001257 hydrogen Substances 0.000 claims description 14
- 229910052739 hydrogen Inorganic materials 0.000 claims description 14
- GUVRBAGPIYLISA-UHFFFAOYSA-N tantalum atom Chemical compound [Ta] GUVRBAGPIYLISA-UHFFFAOYSA-N 0.000 claims description 13
- NFFIWVVINABMKP-UHFFFAOYSA-N methylidynetantalum Chemical compound [Ta]#C NFFIWVVINABMKP-UHFFFAOYSA-N 0.000 claims description 12
- 238000005498 polishing Methods 0.000 claims description 12
- 239000000376 reactant Substances 0.000 claims description 12
- 229910003468 tantalcarbide Inorganic materials 0.000 claims description 11
- 239000007789 gas Substances 0.000 claims description 10
- 230000005484 gravity Effects 0.000 claims description 10
- 238000011084 recovery Methods 0.000 claims description 10
- 239000002173 cutting fluid Substances 0.000 claims description 9
- 238000003860 storage Methods 0.000 claims description 7
- KJTLSVCANCCWHF-UHFFFAOYSA-N Ruthenium Chemical compound [Ru] KJTLSVCANCCWHF-UHFFFAOYSA-N 0.000 claims description 6
- 238000001914 filtration Methods 0.000 claims description 6
- 229910052758 niobium Inorganic materials 0.000 claims description 6
- 239000010955 niobium Substances 0.000 claims description 6
- 238000005086 pumping Methods 0.000 claims description 6
- 229910052707 ruthenium Inorganic materials 0.000 claims description 6
- UNASZPQZIFZUSI-UHFFFAOYSA-N methylidyneniobium Chemical compound [Nb]#C UNASZPQZIFZUSI-UHFFFAOYSA-N 0.000 claims description 5
- GUCVJGMIXFAOAE-UHFFFAOYSA-N niobium atom Chemical compound [Nb] GUCVJGMIXFAOAE-UHFFFAOYSA-N 0.000 claims description 5
- 238000011085 pressure filtration Methods 0.000 claims description 5
- 229910052715 tantalum Inorganic materials 0.000 claims description 5
- 229910004298 SiO 2 Inorganic materials 0.000 claims description 4
- 239000003054 catalyst Substances 0.000 claims description 4
- 230000006835 compression Effects 0.000 claims description 3
- 238000007906 compression Methods 0.000 claims description 3
- 238000004821 distillation Methods 0.000 claims description 3
- 238000005374 membrane filtration Methods 0.000 claims description 3
- 239000002002 slurry Substances 0.000 claims description 3
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 claims 3
- 239000000126 substance Substances 0.000 claims 1
- 235000012431 wafers Nutrition 0.000 description 27
- 239000010408 film Substances 0.000 description 12
- 239000002245 particle Substances 0.000 description 10
- 229910052684 Cerium Inorganic materials 0.000 description 8
- GWXLDORMOJMVQZ-UHFFFAOYSA-N cerium Chemical compound [Ce] GWXLDORMOJMVQZ-UHFFFAOYSA-N 0.000 description 8
- WXANAQMHYPHTGY-UHFFFAOYSA-N cerium;ethyne Chemical compound [Ce].[C-]#[C] WXANAQMHYPHTGY-UHFFFAOYSA-N 0.000 description 8
- 230000008569 process Effects 0.000 description 7
- DNIAPMSPPWPWGF-UHFFFAOYSA-N Propylene glycol Chemical compound CC(O)CO DNIAPMSPPWPWGF-UHFFFAOYSA-N 0.000 description 6
- 230000007613 environmental effect Effects 0.000 description 6
- 239000012535 impurity Substances 0.000 description 5
- 238000004519 manufacturing process Methods 0.000 description 5
- 230000015572 biosynthetic process Effects 0.000 description 3
- 238000001035 drying Methods 0.000 description 3
- 150000002148 esters Chemical class 0.000 description 3
- 150000002431 hydrogen Chemical class 0.000 description 3
- 238000001728 nano-filtration Methods 0.000 description 3
- 239000000047 product Substances 0.000 description 3
- 230000009467 reduction Effects 0.000 description 3
- 238000007790 scraping Methods 0.000 description 3
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- 239000004698 Polyethylene Substances 0.000 description 2
- 238000005273 aeration Methods 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
- 238000009933 burial Methods 0.000 description 2
- CETPSERCERDGAM-UHFFFAOYSA-N ceric oxide Chemical compound O=[Ce]=O CETPSERCERDGAM-UHFFFAOYSA-N 0.000 description 2
- 229910000422 cerium(IV) oxide Inorganic materials 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 239000010730 cutting oil Substances 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 238000003912 environmental pollution Methods 0.000 description 2
- 238000005461 lubrication Methods 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- -1 polyethylene Polymers 0.000 description 2
- 229920000573 polyethylene Polymers 0.000 description 2
- 239000011148 porous material Substances 0.000 description 2
- 239000004576 sand Substances 0.000 description 2
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 229910052797 bismuth Inorganic materials 0.000 description 1
- JCXGWMGPZLAOME-UHFFFAOYSA-N bismuth atom Chemical compound [Bi] JCXGWMGPZLAOME-UHFFFAOYSA-N 0.000 description 1
- 239000011449 brick Substances 0.000 description 1
- 239000004566 building material Substances 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 238000006555 catalytic reaction Methods 0.000 description 1
- 239000002826 coolant Substances 0.000 description 1
- 230000003111 delayed effect Effects 0.000 description 1
- MTHSVFCYNBDYFN-UHFFFAOYSA-N diethylene glycol Chemical compound OCCOCCO MTHSVFCYNBDYFN-UHFFFAOYSA-N 0.000 description 1
- 150000002009 diols Chemical class 0.000 description 1
- 239000004744 fabric Substances 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 239000000295 fuel oil Substances 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- PCHJSUWPFVWCPO-UHFFFAOYSA-N gold Chemical compound [Au] PCHJSUWPFVWCPO-UHFFFAOYSA-N 0.000 description 1
- 229910052737 gold Inorganic materials 0.000 description 1
- 239000010931 gold Substances 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 239000002480 mineral oil Substances 0.000 description 1
- 235000010446 mineral oil Nutrition 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- ZYTNDGXGVOZJBT-UHFFFAOYSA-N niobium Chemical compound [Nb].[Nb].[Nb] ZYTNDGXGVOZJBT-UHFFFAOYSA-N 0.000 description 1
- 238000004806 packaging method and process Methods 0.000 description 1
- 238000005192 partition Methods 0.000 description 1
- 230000010287 polarization Effects 0.000 description 1
- 238000007517 polishing process Methods 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 239000004065 semiconductor Substances 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000010409 thin film Substances 0.000 description 1
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- Separation Using Semi-Permeable Membranes (AREA)
- Grinding-Machine Dressing And Accessory Apparatuses (AREA)
Description
本發明是有關於一種處理矽晶圓廢棄物的方法與裝置,且特別是有關於一種能增加產品附加價值,且能有效地解決環境污染問題的矽晶圓切割研磨廢棄物的回收處理方法及其設備。The present invention relates to a method and a device for processing silicon wafer waste, and particularly relates to a method for recycling and processing a silicon wafer cutting and polishing waste which can increase the added value of the product and can effectively solve the environmental pollution problem. Its equipment.
在製造半導體晶片及太陽能板的產業中,將矽晶棒切割成厚薄均一的矽晶圓(片)已屬於標準流程之一環,其通常使用特殊的金屬線鋸(Wire Saw)為切割刀具,並採用高硬度的碳化矽(SiC,金鋼砂)為研磨料,再輔以混有聚乙二醇(PEG)、二乙二醇(DEG)、丙二醇(PG)等礦物油酯為切削冷卻液,藉此,當金屬線鋸高速往復運行時,就可配合碳化矽為介質來提高線鋸的切削能力,以對矽晶片形成切割作用,且切割同時,係將以聚乙二醇為主成份的切削液對著切割部位噴出,一方面除了作為冷卻及潤滑用途之外,另一方面尚可將切割時所產生的矽粉及雜質帶出切割槽道,使晶圓切割製程能順利且平穩的進行,以利進行後續製程。In the industry of manufacturing semiconductor wafers and solar panels, the cutting of wafers into thin and uniform wafers (sheets) is one of the standard processes, usually using a special wire saw (Wire Saw) as the cutting tool, and Using high hardness tantalum carbide (SiC, gold steel sand) as abrasive, supplemented with mineral oil esters such as polyethylene glycol (PEG), diethylene glycol (DEG), propylene glycol (PG) as cutting coolant Therefore, when the wire saw is reciprocating at high speed, the cutting ability of the wire saw can be improved by using the tantalum carbide as a medium to form a cutting action on the tantalum wafer, and at the same time, the polyethylene glycol is mainly composed. The cutting fluid is sprayed against the cutting part. On the one hand, in addition to being used for cooling and lubrication purposes, on the other hand, the tantalum powder and impurities generated during cutting can be taken out of the cutting channel, so that the wafer cutting process can be smoothly and smoothly. To carry out the follow-up process.
在矽晶圓被切割、研磨的過程中,對切割區所噴出且使用過後的切削液,會挾帶著切削時所產生的矽粉碎屑、雜質與被磨耗的碳化矽,不斷地排出切割區外,進而成為粒子濃度與濁度極高的漿狀廢油泥,以往,國內多數的矽晶圓切割廠商對於這些廢油泥,只能以廢棄物方式來處理,或是以重油進行焚燒後將灰渣掩埋,但是,仍需要支出高昂的費用請廢棄物業者處理,且廢油泥如果以焚化方式處理,也會產生大量的二氧化碳,相當不環保,因此,對於矽晶圓切割研磨後所產生的廢油泥,焚化或掩埋均非理想的處理方法。During the process of cutting and grinding the silicon wafer, the cutting fluid sprayed on the cutting zone and used after cutting will carry out the cutting area continuously with the smashing debris, impurities and the worn carbonized ruthenium generated during cutting. In addition, it has become a slurry-like waste sludge with extremely high particle concentration and turbidity. In the past, most of the domestic silicon wafer cutting manufacturers could only treat these waste sludges as waste, or burn them with heavy oil. The slag is buried, but it still needs to be paid for by the waste industry. If the waste sludge is treated by incineration, it will also generate a lot of carbon dioxide, which is quite environmentally friendly. Therefore, the waste generated after the cutting and polishing of the silicon wafer Sludge, incineration or landfill are not ideal treatment methods.
目前,國外業者已嘗試採用過濾設備來回收廢油泥中的切削油料,其通常利用薄膜技術來進行固液分離,雖然此方式可獲得部份液態再生油,供矽晶圓切割研磨時回收再使用,但此法卻也會產生大量的污泥(濾餅),這些污泥中仍含有可再利用的碳化矽、矽粒與聚乙二醇,但並沒有再予以回收處理,而只視同廢棄物來掩埋,同樣造成嚴重的環保問題,且僅以固液分離方式來進行再生油的回收,其經濟效益並不理想,主因在於廢油泥進行膜過濾時,並沒有獲得良好的前處理,使得膜孔極易污堵,造成膜的操作週期降低,成本增加。At present, foreign companies have tried to use filtration equipment to recover cutting oil in waste sludge, which usually uses thin film technology for solid-liquid separation. Although this method can obtain partial liquid reclaimed oil, it can be recycled when the wafer is cut and ground. It is used, but this method also produces a large amount of sludge (filter cake). These sludges still contain reusable niobium carbide, niobium and polyethylene glycol, but they are not recycled. The same waste causes burial, which also causes serious environmental problems. The recovery of reclaimed oil is only carried out by solid-liquid separation. The economic benefits are not satisfactory. The main reason is that the waste sludge does not obtain good pretreatment. The membrane pores are easily fouled, resulting in a decrease in the operating cycle of the membrane and an increase in cost.
此外,近年來在太陽能產業的強力帶動之下,使得原本作為耗材的碳化矽已嚴重供不應求,連帶讓作為潤滑與冷卻用途的聚乙二醇也隨之大幅提昇用量,且已成了一項頗高的支出,因此,基於成本與環保因素的考量之下,業者除了自廢油泥中回收再生油之外,也勢必須考慮將尚有利用價值的碳化矽、矽粉,自濾餅中進一步地分離回收,以減少廢棄物的生成與總量,俾降低環境污染與處置成本。In addition, in recent years, under the strong driving force of the solar energy industry, the carbonized bismuth originally used as a consumable has been seriously in short supply, and the polyethylene glycol used for lubrication and cooling has also been greatly increased in usage, and has become a considerable High expenditures, therefore, based on the consideration of cost and environmental factors, in addition to the recovery of reclaimed oil from waste sludge, the industry must also consider the use of carbonized niobium and tantalum powder, which is still of value. Separate and recycle to reduce the generation and total amount of waste, and reduce environmental pollution and disposal costs.
因此,如何在回收成本與環保之間達成平衡,至今仍沒有一有效率且符合操作成本的處理方法,使得矽晶圓切割業者在環保改善成本負荷上愈來愈高,故如何積極藉由提高生產品質及污染防治技術來兼顧經濟與環保,降低生產成本,提高產業競爭力,已成為目前相關產業迫切努力之目標。Therefore, how to strike a balance between recycling costs and environmental protection, there is still no efficient and cost-effective treatment method, which makes the wafer cutting industry more and more high in environmental protection and cost load, so how to actively improve Production quality and pollution prevention technologies to balance economic and environmental protection, reduce production costs, and improve industrial competitiveness have become the urgent goals of relevant industries.
本發明之目的,即在提供一種可減少廢棄物生成、相對回收成本低,不僅能有效地解決環保問題,且可自廢棄物中分離出可回收的再生油及碳化矽等副產品的矽晶圓切割研磨廢棄物的回收處理方法。The object of the present invention is to provide a tantalum wafer capable of reducing waste generation, relatively low recovery cost, and not only effectively solving environmental problems, but also separating waste products such as recyclable reclaimed oil and niobium carbide from waste. Recycling method for cutting and grinding waste.
本發明之次要目的,是在提供一種能降低膜堵塞,以延長膜操作壽命,且能增加回收處理效率的矽晶圓切割研磨廢棄物的回收處理設備。A secondary object of the present invention is to provide a recycling processing apparatus for cutting and polishing waste of a silicon wafer which can reduce film clogging, prolong the operation life of the film, and increase the recovery processing efficiency.
根據本發明所提出之一種矽晶圓切割研磨廢棄物的回收處理方法,包含以下步驟:步驟(A):將預先經過脫水後的一濾餅置入一處理槽中,該濾餅是自晶圓切割研磨後所產生的漿狀廢油泥進行壓濾後所生成,並且至少含有矽粉(Si)、碳化矽(SiC)以及由聚乙二醇(PEG)為主所構成的殘留切削液。According to the present invention, a method for recycling a crucible wafer cutting abrasive waste comprises the following steps: Step (A): placing a pre-dehydrated filter cake into a treatment tank, the filter cake being self-crystallized The slurry waste sludge produced after the circular cutting and grinding is produced by pressure filtration, and contains at least tantalum powder (Si), tantalum carbide (SiC), and residual cutting fluid composed mainly of polyethylene glycol (PEG).
步驟(B):在該處理槽內加入一反應劑,使該濾餅被混合稀釋成一工作液體,且可促使工作液體中的矽與該反應劑產生催化反應後,以生成固態的二氧化矽(SiO2 )及氣態的氫氣(H)。Step (B): adding a reactant in the treatment tank, the filter cake is mixed and diluted into a working liquid, and the ruthenium in the working liquid is caused to react with the reactant to form a solid cerium oxide. (SiO 2 ) and gaseous hydrogen (H).
步驟(C):將處理槽內的氫氣抽引入一集氣槽內壓縮儲置。Step (C): pumping the hydrogen in the treatment tank into a gas collection tank for compression storage.
步驟(D):利用比重分離方式在已稀釋污泥濃度後的工作液體之中,更進一步地分離出其內的矽及碳化矽,以便選別回收。Step (D): Separating the ruthenium and ruthenium carbide in the working liquid after the diluted sludge concentration by the specific gravity separation method for sorting and recycling.
步驟(E):將選別出矽及碳化矽的工作液體,再利用膜過濾方式進行固液分離,促使該工作液體能被分離成固態的二氧化矽及液態的水、聚乙二醇等切削液。Step (E): The working liquid of the crucible and the niobium carbide is selected, and the solid-liquid separation is performed by the membrane filtration method, so that the working liquid can be separated into solid ceria and liquid water, polyethylene glycol, etc. liquid.
步驟(F):將液態的水及聚乙二醇再經過逆滲透處理後,而獲得可再利用的水以及以聚乙二醇為主成份的回收切削液。Step (F): The liquid water and the polyethylene glycol are further subjected to reverse osmosis treatment to obtain reusable water and a recycled cutting fluid containing polyethylene glycol as a main component.
依照上述本發明所提出之矽晶圓切割研磨廢棄物的回收處理方法,其中,其中,在步驟(B)時,所加入的反應劑可為水。According to the above method of the present invention, there is provided a process for the recovery of a silicon wafer cutting abrasive waste, wherein, in the step (B), the reactant added may be water.
依照上述本發明所提出之矽晶圓切割研磨廢棄物的回收處理方法,其中,在步驟(E)時,所使用的固液分離是採用圓型平板UF膜來進行分離。According to the above method of the present invention, there is provided a process for recovering a waste cutting waste of a wafer, wherein in the step (E), the solid-liquid separation used is performed by using a round flat UF film.
依照上述本發明所提出之矽晶圓切割研磨廢棄物的回收處理方法,其中,在步驟(F)之後,可將過逆滲透回收後的水,再引回該處理槽中,供步驟(B)之催化劑來使用。According to the above method of the present invention, the method for recovering and processing the silicon wafer cutting and polishing waste, wherein, after the step (F), the water recovered by the reverse osmosis can be returned to the treatment tank for the step (B). ) The catalyst is used.
依照上述本發明所提出之矽晶圓切割研磨廢棄物的回收處理方法,其中,在步驟(F)之後,液態的聚乙二醇可再以蒸餾方式除去其殘留水份及廢油,以形成可供再使用的再生油。According to the above method of the present invention, the method for recycling and processing the waste cutting waste of the wafer, wherein, after the step (F), the liquid polyethylene glycol can be further removed by distillation to remove residual moisture and waste oil to form Recycled oil for reuse.
依照上述本發明所提出之矽晶圓切割研磨廢棄物的回收處理方法,其中,在步驟(F)時,是以RO或NF膜來進行逆滲透處理。According to the above method of the present invention, there is provided a method for recovering and processing a silicon wafer cutting and polishing waste, wherein in the step (F), the reverse osmosis treatment is performed by a RO or NF membrane.
依照上述本發明所提出之矽晶圓切割研磨廢棄物的回收處理方法,其中,在步驟(B)時,尚包含有在該處理槽內打入加壓氣體,以混合成該工作液體。According to the above method of the present invention, there is provided a method for recovering and processing a wafer-cutting and polishing waste, wherein, in the step (B), a pressurized gas is introduced into the treatment tank to be mixed into the working liquid.
依照上述本發明所提出之矽晶圓切割研磨廢棄物的回收處理方法,其中,在步驟(D)之後,更具有將選別後的矽及碳化矽經過乾燥處理,以便包裝回收。According to the above method of the present invention, there is provided a method for recycling and processing a silicon wafer cutting abrasive waste, wherein after the step (D), the selected tantalum and tantalum carbide are further subjected to a drying treatment for packaging recovery.
依照上述本發明所提出之矽晶圓切割研磨廢棄物的回收處理方法,其中,在步驟(E)時,是以負壓吸力方式來抽取工作水體中的水及聚乙二醇。According to the above method of the present invention, there is provided a method for recovering and processing a silicon wafer cutting and polishing waste, wherein in the step (E), water and polyethylene glycol in the working water body are extracted by a vacuum suction method.
因此,本發明先以水為主成份的催化劑來混合濾餅,使濾餅被稀釋成工作液體,進而與矽粉產生催化作用形成二氧化矽與氫氣,然後將氫氣抽引回收,接著,再藉由水來進行比重分離,以選別碳化矽與剩餘的矽粒,繼之,再進行固液分離,使工作液體被分離成固態的二氧化矽與液態的水及聚二乙醇,最後,再來進一步分離出水及聚乙二醇,如此,使得原本回收製程中所產出的廢泥渣,能再回收出有用的矽粒、碳化矽、二氧化矽及聚乙二醇,以減少廢棄物總量,降低廢棄物以掩埋方式的困擾,且更附帶產出具有商業價值的氫氣,使本發明能提昇利用的附加價值,更達成節能減廢的目的。Therefore, the present invention firstly mixes the filter cake with a water-based catalyst, so that the filter cake is diluted into a working liquid, thereby catalyzing the formation of cerium oxide and hydrogen with the cerium powder, and then extracting and recovering the hydrogen gas, and then, The specific gravity is separated by water to select the niobium carbide and the remaining niobium particles, and then the solid-liquid separation is performed to separate the working liquid into solid ceria and liquid water and polydiethanol. Finally, To further separate water and polyethylene glycol, so that the waste sludge produced in the original recycling process can be recycled with useful cerium particles, tantalum carbide, cerium oxide and polyethylene glycol to reduce waste. The total amount, reducing the waste to bury the way, and more with the production of hydrogen with commercial value, so that the invention can enhance the added value of utilization, and achieve the purpose of energy saving and waste reduction.
參照第1圖至第3圖,本發明矽晶圓切割研磨廢棄物的回收處理方法的第一實施例,包含以下步驟:步驟(A):將預先經過壓濾脫水處理後的一濾餅100(Filter Cake)由一投料口210置入一處理槽200中,而該處理槽200係呈密閉狀,該濾餅100是自晶圓切割研磨後所產生的漿狀廢油泥(Wafer Cutting Waste)進行初步的壓濾後所生成,並且至少含有矽粉(Si)、碳化矽(SiC)及聚乙二醇(PEG)為主所構成的殘留切削液。Referring to FIGS. 1 to 3, a first embodiment of the method for recovering a silicon wafer cutting and polishing waste according to the present invention comprises the following steps: Step (A): a filter cake 100 which has been subjected to pressure filtration dewatering treatment in advance (Filter Cake) is placed in a processing tank 200 by a feeding port 210, and the processing tank 200 is sealed. The filter cake 100 is Wafer Cutting Waste which is produced after cutting and grinding from the wafer. It is produced after preliminary pressure filtration, and contains at least a residual cutting fluid composed mainly of tantalum powder (Si), tantalum carbide (SiC), and polyethylene glycol (PEG).
在本實施例中,漿狀廢油泥是採用板框式壓濾機(plate-frame filter press,或稱污泥脫水機)來進行脫水,利用壓濾機的濾布來截留廢油泥中大部份的固形物,再經由高壓空氣之二次壓縮後形成泥渣狀的濾餅,這種濾餅除了含有矽粉(Si)、碳化矽(SiC)及雜質之外,仍殘留少量由聚乙二醇(PEG)為主所構成的切削油酯,本發明即是針對濾餅100中的這些組成物來進行再處理及回收包裝。In this embodiment, the slurry waste sludge is dehydrated by a plate-frame filter press (or a sludge dewatering machine), and the filter cloth of the filter press is used to intercept most of the waste sludge. The solid matter is further compressed by high pressure air to form a sludge-like filter cake. In addition to the powdered silicon (Si), tantalum carbide (SiC) and impurities, the filter cake still has a small amount of polyethylene. The diol (PEG) is mainly a cutting oil ester, and the present invention reprocesses and recycles the package in the filter cake 100.
步驟(B):在該處理槽200內泵送入一反應劑,在本實施例中,該反應劑較佳地是為含有水成份的液體,更進一步地,此液體中並帶有少量的微細氣泡,如此,可使原本呈泥渣狀的濾餅100在被稀釋後,成為帶有氣泡與固形物的工作液體300,而前述的微細氣泡可以採用文氏管原理,將液、氣預先混合後再打入該處理槽200中,一方面可加速水體與濾餅100的攪伴以產生化學反應,另一方面,可將濾餅100中質量較輕的殘餘聚乙二醇等油質及雜質,藉著氣泡的浮力而托昇於液面上層,以利於後續的分離。因此,在預定時間之後,工作液體300中的反應劑與矽粉形成催化反應,並逐漸地生成固態的二氧化矽(SiO2 ,玻璃砂)及氣態的氫氣(H),其化學反應式為:Si+2H2 O → SiO2 (固態)+2H2 (氣態)Step (B): pumping a reactant in the treatment tank 200. In the present embodiment, the reactant is preferably a liquid containing a water component, and further, the liquid has a small amount The fine bubbles, so that the filter cake 100 originally in the form of sludge can be diluted into a working liquid 300 with bubbles and solids, and the aforementioned fine bubbles can be pre-treated by the venturi principle. After mixing, it is driven into the treatment tank 200, on the one hand, the mixing of the water body and the filter cake 100 can be accelerated to generate a chemical reaction, and on the other hand, the oil quality of the light-weight residual polyethylene glycol in the filter cake 100 can be improved. And impurities, by the buoyancy of the bubble lifted to the upper surface of the liquid to facilitate subsequent separation. Therefore, after a predetermined time, the reactant in the working liquid 300 forms a catalytic reaction with the tantalum powder, and gradually forms solid cerium oxide (SiO 2 , glass sand) and gaseous hydrogen (H), and the chemical reaction formula is :Si+2H 2 O → SiO 2 (solid state) + 2H 2 (gaseous state)
在本實施例中,該反應劑是由該處理槽200近底部的一曝氣孔220泵入,此外,上述反應劑中所含有的液體與氣泡量的比例,是以3:1為最佳,且工作液體300的液面高度係略低於該投料口210,以提供氫氣暫存空間。In this embodiment, the reactant is pumped by an aeration hole 220 near the bottom of the treatment tank 200, and the ratio of the liquid to the amount of bubbles contained in the reactant is preferably 3:1. And the liquid level of the working liquid 300 is slightly lower than the feeding port 210 to provide a hydrogen temporary storage space.
步驟(C):在預定時間之後,將處理槽200上層的氫氣自一排氣口230抽引入一集氣槽400內作壓縮儲置,其產生的氫氣可以另外分裝出售,供產生熱源再利用。Step (C): After a predetermined time, the hydrogen in the upper layer of the treatment tank 200 is pumped from a gas outlet 230 into a gas collection tank 400 for compression storage, and the hydrogen gas generated may be separately distributed for sale to generate a heat source. use.
步驟(D):由於矽粒與碳化矽的比重皆高於水(矽比重為2.3,碳化矽比重為3.2),因此,在氫氣(H)被抽引出處理槽200後,便可以利用比重分離方式,在該工作液體300之中更進一步地分離出殘留矽粒及碳化矽,在本實施例中,依序沉降在該處理槽200底部的固態碳化矽及矽粒,可再由底部的一落料口240排出至一篩料桶250中,並經過乾燥處理後,以便各自選別(Sorting)回收。Step (D): Since the specific gravity of the cerium particles and the cerium carbide is higher than that of water (the specific gravity is 2.3 and the specific gravity of the cerium carbide is 3.2), after the hydrogen (H) is extracted from the treatment tank 200, the specific gravity can be separated. In the embodiment, the residual cerium particles and the cerium carbide are further separated in the working liquid 300. In the embodiment, the solid cerium carbide and the cerium particles which are sequentially settled at the bottom of the processing tank 200 can be further removed from the bottom. The blanking port 240 is discharged into a sieve drum 250 and subjected to a drying process for respective sorting recovery.
步驟(E):將選別出矽粒及碳化矽的工作液體300,抽送至一過濾槽500內進行固液分離,在本實施例中,該過濾槽500具有一伸縮管510,該伸縮管510是自外部延伸入該處理槽200內,且底端接設有一圓錐形的吸嘴520,該吸嘴520可隨著工作液體300的液位高度進行活動昇降,且該吸嘴520底端的開孔係設有細微網目(圖未示),用以將工作液體300內的水、二氧化矽及聚乙二醇等液體抽送至該過濾槽內500。Step (E): The working liquid 300 which is selected from the granules and the cerium carbide is pumped into a filter tank 500 for solid-liquid separation. In the embodiment, the filter tank 500 has a telescopic tube 510, and the telescopic tube 510 The bottom end is connected to the processing tank 200, and a conical nozzle 520 is connected to the bottom end. The nozzle 520 can move up and down according to the liquid level of the working liquid 300, and the bottom end of the nozzle 520 is opened. The hole system is provided with a fine mesh (not shown) for pumping liquid such as water, cerium oxide and polyethylene glycol in the working liquid 300 into the filter tank 500.
而且,該過濾槽500內設有半沉降式的一固液分離單元600,該固液分離單元600較佳的是採用圓型平板UF膜,請參第4圖所示,其整體結構是將複數個UF膜610串組於一呈水平且可樞轉的集液管620上,並在該過濾槽500外部以馬達630來帶動UF膜610以集液管620為中心轉動,而另一側則利用一抽油泵640,來唧取透過UF膜610且匯集到該集液管620內的液體,藉著抽油泵630的負壓吸力抽引之下,使工作液體300中呈液態的水、聚乙二醇等切削液,便可以通過UF膜610的過濾而被抽送出該過濾槽500外匯集,而固態的二氧化矽等細小雜質等固形物則被截留在過濾槽500內,且隨著過濾槽500內固形物粒子濃度的不斷提高,就可以將二氧化矽及雜質經過蒸發乾燥處理,以回收作為二級建材再利用(例如作為燒磚、建築隔間材料或步道用地磚…等),藉此,原有的該工作液體300能被分離成固態的二氧化矽及液態的水、聚乙二醇等切削液。Moreover, the filter tank 500 is provided with a semi-settling type solid-liquid separation unit 600. The solid-liquid separation unit 600 preferably uses a round flat UF film, as shown in FIG. 4, the overall structure of which will be A plurality of UF membranes 610 are grouped on a horizontal and pivotable collecting pipe 620, and a UF membrane 610 is driven by the motor 630 outside the filtering tank 500 to rotate around the collecting pipe 620, and the other side Then, using a pump 640, the liquid that has passed through the UF membrane 610 and collected in the header 620 is sucked by the suction of the pump 630 to make the liquid in the working liquid 300 liquid. The cutting fluid such as polyethylene glycol can be pumped out of the filter tank 500 by filtration of the UF membrane 610, and the solid matter such as solid cerium oxide or the like is trapped in the filter tank 500, and As the concentration of solid particles in the filter tank 500 is continuously increased, the cerium oxide and impurities can be subjected to evaporative drying treatment for recycling as a secondary building material (for example, as a brick, a building partition material or a paving floor tile, etc.) ) whereby the original working liquid 300 can be separated into a solid state A cutting fluid such as cerium oxide and liquid water or polyethylene glycol.
在此步驟中,為了延長UF膜的操作周期,每個UF膜610之間可掛置上一刮動元件650,該刮動元件650可以在UF膜610旋轉時,對膜面形成自動刮泥的作用,以防止膜表面積垢、堵塞,進而降低水液濾速。In this step, in order to extend the operation period of the UF film, a scraping member 650 may be suspended between each UF film 610, and the scraping member 650 may form an automatic scraping film on the film surface when the UF film 610 rotates. The role of to prevent membrane surface scale, blockage, and thus reduce the water filtration rate.
步驟(F):將液態的水及聚乙二醇再經過一逆滲透處理單元700的逆滲透處理,該逆滲透處理單元700可採用NF(Nano Filtration)膜或RO(Reverse Osmosis)膜來進行,本實施例是使用RO膜,利用RO膜只允許水分子透析過膜孔的特性,來進一步地分離出水及濃縮的聚乙二醇,而獲得可回收再利用的水及以聚乙二醇為主成份的油酯,其中,回收水可以一迴水管路710抽送到步驟(B)的處理槽200內,以提供作為與矽粉的催化反應劑使用,減少處理槽200所需要的用水量。Step (F): the liquid water and the polyethylene glycol are further subjected to a reverse osmosis treatment of a reverse osmosis treatment unit 700, and the reverse osmosis treatment unit 700 may be performed by using a NF (Nano Filtration) membrane or an RO (Reverse Osmosis) membrane. In this embodiment, the RO membrane is used, and the RO membrane is only allowed to dialyze the pores of the water molecules to further separate the water and the concentrated polyethylene glycol, thereby obtaining recyclable water and polyethylene glycol. An oil ester as a main component, wherein the recovered water can be pumped to the treatment tank 200 of the step (B) in a return water line 710 to provide a catalytic reactant for use with the tantalum powder to reduce the amount of water required for the treatment tank 200. .
步驟(G):前述的液態聚乙二醇可再以蒸餾方式除去其殘留水份及廢油,而濃縮後的聚乙二醇則可以通過濁度計的檢測後,以形成可供回收再利用的再生油,並送至一儲油槽800,再生油可另行包裝後供晶圓切割研磨製程使用。Step (G): the liquid polyethylene glycol can be further removed by distillation to remove residual water and waste oil, and the concentrated polyethylene glycol can be detected by a turbidimeter to form a recyclable product. The used reclaimed oil is sent to an oil storage tank 800, and the reclaimed oil can be separately packaged for use in a wafer cutting and polishing process.
因此,本發明先利用以水為主成份的催化劑來混合經過壓濾脫水處理後的濾餅100(廢泥渣),使濾餅100被稀釋成污泥濃度較低的工作液體300,進而與矽粉產生催化作用形成固態的二氧化矽與氣態的氫氣,然後將氫氣抽引回收,接著,再藉由水來進行比重分離,以選別出工作液體300中的碳化矽與剩餘的矽粒,繼之,再採用UF膜61的來進行固液分離,使工作液體300被分離成固態的二氧化矽與液態的水及聚二乙醇,最後,再以RO膜來進一步分離水及聚乙二醇,如此,使得原本回收製程中所產出的廢泥渣,能再回收出有用的矽粒、碳化矽、二氧化矽及聚乙二醇,以減少廢棄物總量,降低廢棄物以掩埋方式的困擾,且更附帶產出具有商業價值的氫氣,使發明能提昇利用的附加價值,更達成節能減廢的目的。Therefore, the present invention first uses a catalyst containing water as a main component to mix the filter cake 100 (waste sludge) which has been subjected to pressure filtration dewatering treatment, so that the filter cake 100 is diluted into a working liquid 300 having a low sludge concentration, and further The tantalum powder catalyzes the formation of solid cerium oxide and gaseous hydrogen, and then the hydrogen is extracted and recovered, and then the specific gravity is separated by water to select the cerium carbide and the remaining cerium in the working liquid 300. Then, the UF membrane 61 is used for solid-liquid separation, so that the working liquid 300 is separated into solid cerium oxide and liquid water and polydiethanol, and finally, the RO membrane is further separated into water and polyethylene. Alcohol, so that the waste sludge produced in the original recycling process can be recycled with useful niobium grains, tantalum carbide, cerium oxide and polyethylene glycol to reduce the total amount of waste and reduce waste for burial. The dilemma of the method, and more with the production of hydrogen with commercial value, enables the invention to enhance the added value of utilization, and achieve the purpose of energy saving and waste reduction.
如上所述,相較於以往晶圓切割研摩廢棄物處理方法的問題,本發明具有以下功效及優點:As described above, the present invention has the following effects and advantages over the conventional wafer cutting and rubbing waste disposal method:
一、本發明將原本不能再處理的廢棄濾餅100(泥渣),先經過加水以催化出氫氣,再以比重分離選粒出碳化矽與矽粒,並藉由UF膜61與RO膜的設置,來進一步分離工作液體300中的二氧化矽、水及聚乙二醇,最後產出可供回收使用的氫氣、矽粒、碳化矽、二氧化矽、水及聚乙二醇,使本發明能提昇回收利用的附加價值,且處理後剩餘的淤渣等廢棄物量相當少,以達成節能減廢的目的。1. The present invention removes the waste filter cake 100 (sludge) which can not be processed any more, first by adding water to catalyze the hydrogen gas, and then separating and separating the cerium carbide and the cerium particles by the specific gravity, and by using the UF film 61 and the RO membrane. Provided to further separate cerium oxide, water and polyethylene glycol in the working liquid 300, and finally to produce hydrogen, cerium particles, cerium carbide, cerium oxide, water and polyethylene glycol for recycling. The invention can increase the added value of recycling, and the amount of waste such as sludge remaining after the treatment is relatively small, so as to achieve energy saving and waste reduction.
二、本發明在進行固液分離程序前,先以比重分離方式選取出固態的碳化矽及矽粒,來降低工作液體300中固形物的比例,能有效地延緩後續進行固液分離時,UF膜610的積垢堵塞與工作液體300的濃度極化現象,膜的使用周期壽命得以延長,降低作成本。2. Before the solid-liquid separation process is carried out, the solid carbonized niobium and tantalum particles are selected by the specific gravity separation method to reduce the proportion of the solid matter in the working liquid 300, and the UF can be effectively delayed after the subsequent solid-liquid separation. The fouling of the membrane 610 and the concentration polarization of the working liquid 300 increase the life cycle of the membrane and reduce the cost.
三、此外,固液分離所採用的圓型平板UF膜610,利用膜轉動時同步被刮動的效果,可以大幅降低膜面結垢與濾餅的生成,故能提高整體回收處理的效率,並延長膜的操作壽命性,使本發明能兼顧回收效率與成本。3. In addition, the circular flat UF film 610 used for solid-liquid separation can greatly reduce the fouling of the membrane surface and the formation of the filter cake by utilizing the effect of synchronously being scraped when the membrane is rotated, so that the efficiency of the overall recycling treatment can be improved. And prolonging the operational life of the membrane, the invention can balance the recovery efficiency and cost.
惟以上所述者,僅為本發明之一個實施例而已,當不能以此限定本發明實施之範圍,即大凡依本發明申請專利範圍及發明說明內容所作之簡單的等效變化與修飾,皆應仍屬本發明專利涵蓋之範圍內。However, the above is only one embodiment of the present invention, and the scope of the invention is not limited thereto, that is, the simple equivalent changes and modifications made by the scope of the invention and the description of the invention are all It should remain within the scope of this invention.
100...濾餅100. . . Filter cake
200...處理槽200. . . Processing tank
210...投料口210. . . Feeding port
220...曝氣孔220. . . Aeration hole
230...排氣口230. . . exhaust vent
240...落料口240. . . Drop opening
250...篩料桶250. . . Sieve bucket
300...工作液體300. . . Working fluid
400...集氣槽400. . . Gas collecting tank
500...過濾槽500. . . Filter tank
510...伸縮管510. . . flexible tube
520...吸嘴520. . . Nozzle
600...固液分離單元600. . . Solid-liquid separation unit
610...UF膜610. . . UF film
620...集液管620. . . Liquid collection tube
630...馬達630. . . motor
640...抽油泵640. . . Pump
650...刮動元件650. . . Swing element
700...逆滲透處理單元700. . . Reverse osmosis treatment unit
710...迴水管路710. . . Return water pipeline
800...儲油槽800. . . Oil storage tank
第1圖係為一方塊流程圖,說明本發明矽晶圓切割研磨廢棄物的回收處理方法的處理流程。Fig. 1 is a block flow diagram showing the processing flow of the recycling processing method of the wafer cutting and grinding waste of the present invention.
第2圖係為一系統結構圖,說明本發明處理濾餅的回收系統整體配設情形。Fig. 2 is a system structural diagram showing the overall arrangement of the recovery system for treating the filter cake of the present invention.
第3圖係為一局部剖視圖,說明本發明的過濾槽內部結構。Figure 3 is a partial cross-sectional view showing the internal structure of the filter tank of the present invention.
第4圖係為一局部剖視圖,說明本發明的圓型平板UF膜過濾裝置的剖面結構。Figure 4 is a partial cross-sectional view showing the cross-sectional structure of the circular flat UF membrane filtration device of the present invention.
100...濾餅100. . . Filter cake
200...處理槽200. . . Processing tank
250...篩料桶250. . . Sieve bucket
400...集氣槽400. . . Gas collecting tank
500...過濾槽500. . . Filter tank
600...固液分離單元600. . . Solid-liquid separation unit
620...集液管620. . . Liquid collection tube
630...馬達630. . . motor
640...抽油泵640. . . Pump
700...逆滲透處理單元700. . . Reverse osmosis treatment unit
710...迴水管路710. . . Return water pipeline
800...儲油槽800. . . Oil storage tank
Claims (9)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| TW099140939A TWI504573B (en) | 2010-11-26 | 2010-11-26 | Method and apparatus for recycling and processing of silicon wafer cutting and grinding waste |
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| TW099140939A TWI504573B (en) | 2010-11-26 | 2010-11-26 | Method and apparatus for recycling and processing of silicon wafer cutting and grinding waste |
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| TW201221482A TW201221482A (en) | 2012-06-01 |
| TWI504573B true TWI504573B (en) | 2015-10-21 |
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| TW201000399A (en) * | 2008-06-30 | 2010-01-01 | Danen Technology Corp | Method for recycling silicon materials |
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