TWI745018B - Method of processing mswi fly ash with multiple washing operations - Google Patents
Method of processing mswi fly ash with multiple washing operations Download PDFInfo
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本發明係有關於一種焚化飛灰處理方法,特別是一種多級擦洗焚化飛灰之處理方法。The present invention relates to a treatment method of incineration fly ash, in particular to a treatment method of multi-stage scrubbing incineration fly ash.
一般廢棄物經焚化焚燒過程中,所產生的焚化飛灰收集於煙氣管道、煙氣淨化、分離器和除塵器裝置等處的容重較輕、粒徑細小的粉體物質,其成分複雜、毒性大:飛灰中不僅含有大量的Cd、Cr、Cu、Ni、Pb和Zn等重金屬無機有害物,還富集了高濃度的具有最強毒性的二噁英等有機致癌物,是國家指定的危險廢物,因此,必須透過穩定化或無害化處理後,才能進行資源再利用或最終處置;而現有焚化飛灰多以固化、穩定化進行中間處理,而固化作法則是以固化劑(例如水泥、矽酸鈉、石灰或黏土等)加入該焚化飛灰中而形成固體硬塊物質,使有害物質不易溶出,而固化處理雖有操作簡便、設置費用低廉、無廢氣、廢水處理問題的優點,但固化後的體積、重量均會增加,且浪費固化劑及自然資源,又須分區掩埋處理降低掩埋年限,同時焚化飛灰中含有高濃度氯鹽,影響固化體的耐久性,長期放置重金屬仍有融出的疑慮。In the process of incineration of general waste, the incineration fly ash produced is collected in the flue gas pipeline, flue gas purification, separator and dust collector device, etc. The powder material has a lighter bulk density and a small particle size, and its composition is complex. Very toxic: fly ash not only contains a large amount of heavy metal inorganic harmful substances such as Cd, Cr, Cu, Ni, Pb and Zn, but also contains a high concentration of organic carcinogens such as dioxins with the strongest toxicity, which is designated by the state Hazardous wastes, therefore, must be stabilized or treated in a harmless manner before they can be reused or finally disposed of. The existing incineration fly ash is mostly solidified and stabilized for intermediate treatment, while the solidification method is based on curing agents (such as cement). , Sodium silicate, lime or clay, etc.) are added to the incineration fly ash to form a solid lumpy substance, which makes the harmful substances difficult to dissolve. Although the solidification treatment has the advantages of simple operation, low installation cost, no waste gas and wastewater treatment problems, but After curing, the volume and weight will increase, and the curing agent and natural resources will be wasted. The burial treatment must be divided into sections to reduce the burial period. At the same time, the incineration fly ash contains high concentration of chloride salts, which affects the durability of the solidified body, and heavy metals can still be stored for a long time. Melt out doubts.
此外,垃圾焚燒廠飛灰中可溶性物質主要有鉀、鈉、氯離子等,約占飛灰量的20%,去除氯鹽後,可製成工業二級鉀、鈉鹽,不可溶物質主要包含鈣、矽、鋁、鐵等,約占飛灰量的80%,其成分接近優質石灰石,可作為水泥原料用來生產水泥熟料,但由於飛灰中易揮發的氯鹽,在水泥窯內燒結過程中,會造成水泥窯腐蝕、結皮等情況,因此,該飛灰無論欲後續處理成工業二級鉀、鈉鹽,或者欲作為生產水泥熟料之原料,皆必須先去除該飛灰中的氯鹽。In addition, the soluble substances in fly ash from waste incineration plants mainly include potassium, sodium, chloride ions, etc., accounting for about 20% of the fly ash. After the chlorine salt is removed, it can be made into industrial secondary potassium and sodium salt. Insoluble substances mainly include Calcium, silicon, aluminum, iron, etc., account for about 80% of the fly ash. Its composition is close to high-quality limestone. It can be used as a cement raw material to produce cement clinker. However, due to the volatile chloride salt in the fly ash, it is used in cement kilns. During the sintering process, cement kiln corrosion and skinning will be caused. Therefore, whether the fly ash is to be processed into industrial secondary potassium or sodium salt or used as a raw material for the production of cement clinker, the fly ash must be removed first In the chlorine salt.
而現有主要是利用水洗方式去除大部分的氯鹽,但目前係利用2至8倍重量比的水混合飛灰,攪拌擦洗後進行固液分離,使部分之重金屬及氯鹽由該水帶走,而降低殘留於該飛灰中的重金屬及氯鹽成分;然而,一般擦洗主要採一次性擦洗,且每次都是使用清水進行擦洗,當對擦洗後飛灰中的重金屬或氯鹽要求更高時,更需要使用更高倍數的水進行混合,除需消耗大量的水資源,且單獨利用清水洗採用一次性擦洗,其無法有效進行擦洗外,所產生之大量之廢水也容易造成水資源之浪費,實須改善。The existing method mainly uses water washing to remove most of the chloride salt, but currently uses 2 to 8 times the weight ratio of water to mix fly ash, stir and scrub the solid-liquid separation, so that part of the heavy metals and chloride salts are taken away by the water , And reduce the heavy metals and chloride salts remaining in the fly ash; however, the general scrubbing is mainly a one-time scrub, and clean water is used for scrubbing each time. When the heavy metals or chloride salts in the fly ash after scrubbing are more demanding When it is high, it is more necessary to use higher multiples of water for mixing. In addition to consuming a lot of water resources, and using clean water alone to use one-time scrubbing, it cannot be effectively scrubbed. The large amount of waste water produced can also easily cause water resources. The waste must be improved.
因此,本發明之目的,是在提供一種多級擦洗焚化飛灰之處理方法,其可降低水資源之浪費外,同時又可有效降低該回收飛灰中的氯鹽成分,使該回收飛灰能再進行後續利用。Therefore, the object of the present invention is to provide a multi-stage scrubbing and incineration fly ash treatment method, which can reduce the waste of water resources, and at the same time can effectively reduce the chlorine salt content in the recovered fly ash, so that the recovered fly ash Can be used again.
於是,本發明多級擦洗焚化飛灰之處理方法,其包含有準備步驟、初洗步驟、初脫步驟、精洗步驟及精脫步驟;其中,該準備步驟備置有欲處理之焚化飛灰,以及一清水及一回收水,而該初洗步驟中係利用該回收水與焚化飛灰混合後,進行攪拌擦洗,使該焚化飛灰中部份之重金屬與氯鹽受到該回收水帶走,而後透過該初脫步驟進行脫水處理,以將該回收水與該焚化飛灰分離,使該回收水形成較高溶度之廢水,另該焚化飛灰則形成含重金屬及氯鹽較低含量之初洗飛灰再經由該精洗步驟中,將該初洗飛灰及清水進行攪拌擦洗後,再經該精脫步驟,以分別得到回收水及回收飛灰,故透過該回收水係提供該初洗步驟中所使用,能有效降低水資源之浪費外,同時又可有效降低該回收飛灰中的氯鹽成分,使該回收飛灰能再進行後續利用。Therefore, the multi-stage scrubbing and incineration fly ash treatment method of the present invention includes a preparation step, an initial washing step, an initial removal step, a fine washing step, and a fine removal step; wherein the preparation step prepares the incineration fly ash to be treated, And a clean water and a recycled water. In the initial washing step, the recycled water is mixed with the incineration fly ash, and then stirred and scrubbed, so that part of the heavy metals and chloride salts in the incineration fly ash are taken away by the recycled water. Then through the initial removal step, dehydration treatment is carried out to separate the recovered water from the incineration fly ash, so that the recovered water will form wastewater with a higher solubility, and the incineration fly ash will form a lower content of heavy metals and chloride salts. The first-washed fly ash is then passed through the fine washing step, the first-washed fly ash and clean water are stirred and scrubbed, and then subjected to the fine removal step to obtain recycled water and recycled fly ash, respectively. Therefore, the recycled water system provides the The use in the initial washing step can effectively reduce the waste of water resources, and at the same time can effectively reduce the chloride salt component in the recovered fly ash, so that the recovered fly ash can be reused again.
有關本發明之前述及其他技術內容、特點與功效,在以下配合參考圖式之較佳實施例的詳細說明中,將可清楚地明白。The foregoing and other technical contents, features, and effects of the present invention will be clearly understood in the following detailed description of the preferred embodiment with reference to the drawings.
參閱圖1,本發明第一較佳實施例,本發明焚化飛灰處理方法包含一備置有焚化飛灰、清水及回收水之準備步驟,一將該焚化飛灰與回收水混合擦洗之初洗步驟,一將該初洗步驟之焚化飛灰與回收水進行壓濾分離之初脫步驟,一將該初脫步驟所得之初洗飛灰與清水混合擦洗之精洗步驟,以及一將該精洗步驟中初洗飛灰與清水進行壓濾分離之精脫步驟;其中,該焚化飛灰可為垃圾焚化廠空污防治設備集收後所得,而該清水可為自來水、蒸餾水或經軟水處理之水,而該回收水則是經過擦洗該焚化飛灰後經壓濾分離焚化飛灰後所得之水。Referring to Fig. 1, the first preferred embodiment of the present invention. The incineration fly ash treatment method of the present invention includes a preparation step of preparing incineration fly ash, clean water and recovered water, and a preliminary washing by mixing the incineration fly ash and the recovered water for scrubbing Steps: a step of removing the incineration fly ash and the recovered water from the preliminary washing step by pressure filtration; In the washing step, the first washing fly ash is separated from the clean water by pressure filtration; the incineration fly ash can be collected from the air pollution control equipment of the garbage incineration plant, and the clean water can be tap water, distilled water or soft water treatment The recovered water is the water obtained after scrubbing the incineration fly ash and then separating the incineration fly ash by pressure filtration.
仍續前述,該初洗步驟係將該焚化飛灰與回收水進行攪拌,且該焚化飛灰:回收水以重量比1:2-5混合後進行攪拌擦洗,而最佳之狀況下則是該焚化飛灰:回收水以重量比1:3,例如當100公斤的焚化飛灰,則以至少300公斤的回收水進行混合後,並依據所使用的設備大小及擦洗狀態而調整攪拌時間,使該焚化飛灰與該回收水攪拌均勻後,由於該焚化飛灰中含有較高濃度之氯鹽,故當該焚化飛灰及回收水輸入一第一壓濾脫水設備中,透過該第一壓濾脫水設備壓濾過濾後,將產生較高氯鹽濃度之廢水,以及氯鹽濃度降低之初洗飛灰,而該廢水則可經輸入一廢水槽內,以進行後續處理,而經初洗飛灰可壓濾成至少含水率低於38%以下,以便於後續進行處理。 Continuing the foregoing, the initial washing step is to stir the incineration fly ash and the recovered water, and the incineration fly ash: the recovered water is mixed in a weight ratio of 1:2-5 and then stirred and scrubbed. In the best condition, it is The incineration fly ash: the weight ratio of recycled water is 1:3. For example, when 100 kilograms of incineration fly ash is mixed with at least 300 kilograms of recycled water, the mixing time is adjusted according to the size of the equipment used and the scrubbing state. After the incineration fly ash and the recovered water are evenly stirred, since the incineration fly ash contains a higher concentration of chloride salts, when the incineration fly ash and the recovered water are input into a first filter press and dehydration device, the first After the filter press and dehydration equipment, the wastewater with higher chloride salt concentration and the initial washing fly ash with lower chloride salt concentration will be produced after the filter press. The wastewater can be fed into a waste water tank for subsequent treatment. The washed fly ash can be press filtered to at least the moisture content below 38%, so as to facilitate subsequent processing.
仍續前述,該精洗步驟係將前述氯鹽含量較低之初洗飛灰,再利用一清水混合,該初洗飛灰:清水以重量比1:2-5之比例混合,而最佳之狀況下則是該初洗飛灰:回收水以重量比1:3,即利用當100公斤的初洗飛灰,則利用300公斤的清水進行混拌,可依據所使用的設備大小及擦洗狀態而調整攪拌時間,使該初洗飛灰與該清水攪拌均勻後,由於該初洗飛灰其中所含的氯鹽較低,因此當該精脫步驟針對前段之精洗飛灰輸入一第二壓濾脫水設備進行壓濾脫水時,將可產生較低含量氯鹽之回收水,以及產生氯鹽含量極低之回收飛灰,該回收水可供該初洗步驟進行使用,而該回收飛灰成份內其所含的氯鹽為2%重量百分比以下,將可作為後續處理成工業二及鉀、鈉鹽,甚至當該回收飛灰其所含的氯鹽為1%重量百分比以下時,亦可作為水泥原料以用來生產水泥熟料等,使該回收飛灰能再進行後續利用。 As mentioned above, the fine washing step is to mix the first-washed fly ash with the lower chlorine salt content, and then mix it with a clean water. The first-washed fly ash: clean water is mixed in a weight ratio of 1:2-5, and the best In this situation, it is the initial washing fly ash: the weight ratio of the recycled water is 1:3, that is, if 100 kg of the first washing fly ash is used, 300 kg of clean water is used for mixing, which can be based on the size of the equipment used and the scrubbing. Adjust the mixing time to make the first clean fly ash and the clean water evenly stirred, because the first clean fly ash contains less chloride salt, so when the fine removal step is input for the first clean fly ash in the previous stage When the second filter press dehydration equipment performs filter press dehydration, it will produce recycled water with a lower content of chloride salts and recycled fly ash with a very low content of chloride salts. The recycled water can be used for the initial washing step, and the recovery The chlorine salt contained in the fly ash component is less than 2% by weight, and it can be used as a follow-up treatment to industrial di-potassium and sodium salt, even when the recycled fly ash contains less than 1% by weight of the chloride salt It can also be used as a cement raw material to produce cement clinker, etc., so that the recovered fly ash can be reused.
因此,本發明利用該焚化飛灰以重量比1:3重量比的回收水進行水洗,脫水所得初洗飛灰後再利用1:3重量比的清水進行水洗,而後壓濾後所得之各數值如下(重量百分比):
如前所述,經過初洗步驟及精洗步驟且搭配回收水及清水使用狀態下,其擦洗兩次所需僅消耗該焚化飛灰相對重量的3倍清水,就能將該焚化飛灰所含氯鹽成分降低至1%以內。As mentioned above, after the initial washing step and the fine washing step and the use of recycled water and clean water, the two scrubbing only consumes 3 times the relative weight of the incineration fly ash, and the incineration fly ash can be used. The content of chloride salt is reduced to less than 1%.
因此,本發明將該焚化飛灰分成至少初洗步驟與精洗步驟多重式擦洗,即利用精洗步驟中所產生回收水,用來作為初洗步驟中含有較高氯鹽成分之焚化飛灰的擦洗使用,而當該焚化飛灰經過該初洗步驟中擦洗後將產生較低含氯鹽成分之初洗飛灰, 再利用清水對該初洗飛灰進行擦洗,如此利用該回收水擦洗氯鹽濃度較高之焚化飛灰,而後形成含氯鹽成分較低之初洗飛灰,再利用清水進行擦洗,能有效降低水資源之浪費外,同時又可確保該焚化飛灰擦洗後之品質,達到降低水洗成本及提高水洗效率之功效。Therefore, the present invention divides the incineration fly ash into multiple scrubbing at least the initial washing step and the fine washing step, that is, the recovered water generated in the fine washing step is used as the incineration fly ash containing higher chloride salt content in the preliminary washing step. When the incineration fly ash is scrubbed in the initial washing step, it will produce the initial washing fly ash with a lower chlorine salt content, and then use clean water to scrub the initial washing fly ash, so that the recycled water is used for scrubbing The incineration fly ash with a higher concentration of chloride salt will then form the initial washing fly ash with a lower content of chloride salt, and then use clean water for scrubbing, which can effectively reduce the waste of water resources and at the same time ensure that the incineration fly ash is scrubbed after scrubbing. Quality, achieve the effect of reducing washing cost and improving washing efficiency.
參閱圖2,本發明多級擦洗焚化飛灰之處理方法的第二較佳實施例,本實施例中仍包含有準備步驟、初洗步驟、初脫步驟、精洗步驟及精脫步驟等,而前述步驟所欲達成之功效皆與第一實施例相同,恕不詳述,特別是:本實施例中,該初脫步驟與該精洗步驟間依序增設有至少一次洗步驟及至少一次脫步驟,其中,該次洗步驟其將該精脫後所得之回收水用以擦洗,而該次洗步驟中該初洗飛灰與回收水重量比為1:2-5,最佳比例為該初洗飛灰與回收水為1:3;另,該次脫步驟則是將壓濾產生回收水及次洗飛灰,以將該回收水提供至該初洗步驟中使用,而所得之次洗飛灰則進入下階段的次洗步驟或精洗步驟中處理;是以,透過該次洗步驟、次脫步驟之設計,可依據該精脫步驟後之回收飛灰內所含氯鹽狀況,調整是否增加該次洗步驟與該次脫步驟,進而依序進行分級清洗,且每一脫水後所產生之回收水將可供前一步驟之擦洗所使用,藉以達到濃水洗濃灰,清水洗淨灰之概念,故實現了水的高效利用率,從而做到用最少的水,就能擦洗出最乾淨的回收飛灰,達到降低水洗成本及提高水洗效率之功效。Referring to Fig. 2, the second preferred embodiment of the multi-stage scrubbing incineration fly ash processing method of the present invention, this embodiment still includes a preparation step, a preliminary washing step, a preliminary removal step, a fine washing step, a fine removal step, etc., The effects to be achieved by the foregoing steps are the same as those in the first embodiment, and will not be described in detail. In particular, in this embodiment, at least one washing step and at least one washing step are sequentially added between the initial removal step and the fine washing step. In this washing step, the recovered water obtained after the fine washing is used for scrubbing, and the weight ratio of the first washing fly ash to the recovered water in this washing step is 1:2-5, and the best ratio is The ratio of the primary washing fly ash and the recovered water is 1:3; in addition, the secondary desorption step is to generate recovered water and secondary washing fly ash from the press filter, so as to provide the recovered water for use in the primary washing step, and the resultant The secondary washing fly ash is processed in the next stage of secondary washing step or fine washing step; therefore, through the design of this secondary washing step and secondary removal step, the chlorine salt contained in the recovered fly ash after the fine removal step can be used. Condition, adjust whether to add this washing step and this degassing step, and then carry out graded cleaning in order, and the recovered water generated after each dehydration will be used for the scrubbing in the previous step, so as to achieve thick water washing and thick ash. The concept of washing the ash with clean water realizes the efficient utilization of water, so that the cleanest recycled fly ash can be scrubbed with the least water, so as to reduce the washing cost and improve the washing efficiency.
歸納前述,本發明多級擦洗焚化飛灰之處理方法,其包含有準備步驟、初洗步驟、初脫步驟、精洗步驟及精脫步驟,其利用脫水後所產生之回收水將可供前一步驟之擦洗所使用,且僅有初脫步驟後才會產生廢水,其廢水的濃度將可更濃,能有效降低水資源之浪費外,同時又可有效降低該回收飛灰中的氯鹽成分,使該回收飛灰能再進行後續利用,達到降低水洗成本及提高水洗效率之功效。In summary, the multi-stage scrubbing and incineration fly ash treatment method of the present invention includes a preparation step, a preliminary washing step, a preliminary removal step, a fine washing step, and a fine removal step. It is used for one-step scrubbing, and waste water is only produced after the initial removal step. The concentration of the waste water will be more concentrated, which can effectively reduce the waste of water resources, and at the same time can effectively reduce the chlorine salt in the recycled fly ash. The components enable the recovered fly ash to be reused again, achieving the effect of reducing washing costs and improving washing efficiency.
惟以上所述者,僅為說明本發明之較佳實施例而已,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書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, what has been described above is only to illustrate the preferred embodiments of the present invention, and should not be used to limit the scope of implementation of the present invention, that is, simple equivalent changes and modifications made according to the scope of the patent application of the present invention and the content of the description of the invention. , Should still fall within the scope of the invention patent.
無without
圖1為本發明第一實施例之流程方塊圖。 圖2為本發明第二實施例之流程方塊圖 Fig. 1 is a flow block diagram of the first embodiment of the present invention. Figure 2 is a flow block diagram of the second embodiment of the present invention
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WO2015006799A1 (en) * | 2013-07-15 | 2015-01-22 | Relivit Pty Ltd | Recovery of super absorbent polymers |
CN106391663A (en) * | 2016-11-03 | 2017-02-15 | 湖州森诺环境科技有限公司 | Flying ash harmless treatment resource recycling utilization device and treatment method |
TWI629082B (en) * | 2017-09-05 | 2018-07-11 | 蘇鈺荃 | Method for stabilizing mswi fly ash |
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WO2015006799A1 (en) * | 2013-07-15 | 2015-01-22 | Relivit Pty Ltd | Recovery of super absorbent polymers |
CN106391663A (en) * | 2016-11-03 | 2017-02-15 | 湖州森诺环境科技有限公司 | Flying ash harmless treatment resource recycling utilization device and treatment method |
TWI629082B (en) * | 2017-09-05 | 2018-07-11 | 蘇鈺荃 | Method for stabilizing mswi fly ash |
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