TW201119955A - Entrapped mixed microbial cell with cellulose acetate, fabricating method therefor and wastewater treatment system of multi-function employing the same - Google Patents

Entrapped mixed microbial cell with cellulose acetate, fabricating method therefor and wastewater treatment system of multi-function employing the same Download PDF

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TW201119955A
TW201119955A TW98141328A TW98141328A TW201119955A TW 201119955 A TW201119955 A TW 201119955A TW 98141328 A TW98141328 A TW 98141328A TW 98141328 A TW98141328 A TW 98141328A TW 201119955 A TW201119955 A TW 201119955A
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Taiwan
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wastewater
biological
reaction tank
wastewater treatment
treatment system
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TW98141328A
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Chinese (zh)
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Cheng-Fang Lin
Ping-Yi Yang
Karen Lin
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Cheng-Fang Lin
Ping-Yi Yang
Karen Lin
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Priority to TW98141328A priority Critical patent/TW201119955A/en
Publication of TW201119955A publication Critical patent/TW201119955A/en

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  • Activated Sludge Processes (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

A multi-function wastewater treatment system is provided, including a plurality of treating units entrapped with cellulose acetate capable of removing organics and nitrogen compounds from the wastewater simultaneously and at least one membrane module arranged therein for suspended solid filtration. The provided wastewater treatment system is advantageous in the simplified operation, cost-effect and toxicity tolerance. Moreover, the system is capable of removing organics and nitrogen compounds from the wastewater under a controlled aeration mode, and enhancing the efficiency of membrane treatment. The expense for membrane module is thus reduced.

Description

201119955 六、發明說明: 【發明所屬之技術領域】 本發明係關於一種廢水生物處理系統’特別是關於 一種利用活性污泥法之廢水生物處理系統° 【先前技術】 生物處理法係屬於廢水處理程序中之二級處理程序,主要 是用於處理經初級處理沉澱後之廢水,使廢水經生物處理程序 與終沉池處理後予以放流,其係利用微生物之代謝作用’對廢 水中存在之複雜有機化合物進行分解,藉以去除廢水中生化需 氧量(Biochemical Oxygen Demand,BOD )、化學需氧量 (Chemical Oxygen Demand, COD )等有機物質以及氮、碟等化 合物》 廢水生物處理程序一般可分為好氧性處理及厭氧性處理兩 種,其中好氧性處理用於去除水中有機物(碳)及將廢水中有 機氮與氨氮化合物生物氧化成硝酸鹽氮化合物,而厭氧性處理 則可用於進行水中硝酸鹽氮化合物之處理(即脫硝程序)。廢水 生物處理程序中所使用之微生物主要由細菌、真菌類、蒸類、 原生動物等微生物組成,往往需針對不同的廢水源以及欲去除 之物質的種類而分別養成不同組成的微生物群,故其處理效率 之影響因子非常複雜,在操作上高度仰賴經驗的累積、十分不 易。 活性污泥法係一種好氧性生物處理法,其中,經初級處理 201119955 後之廢水係流入曝氣槽而與槽内之活性污泥相混合接觸,並流 入終沉池中予以沉澱分離污泥與清水;部分經分離之污泥連續 迴流至曝氣槽(即所謂之迴流污泥),而另一部份則需排出並進 行進步的處理(即所謂之廢棄污/尼處理)。在實際操作上,除 微生物群之養成外,更必須精確控制停留時間、污泥迴流量、 與曝氣條件等參數,以尋求最佳處理效率之系統操作條件。 由於活性污泥係由懸浮狀的好氧性微生物群所組成,因而 容易自其聚結體剝落,導致水中懸浮物濃度的增加;除增加活 性污泥法之處理負荷外,亦造成操作條件的不易控制。此外, 為達到生物硝化與生物脫硝之目的,由於微生物分解選擇性之 故’現有的生物處理程序必須利用多次污泥迴流與廢水迴流之 設計,重複於不同反應槽内進行兼氣(Anoxic )'厭氧(Anaerobic ) 與好氧(Aerobic)條件控制,在好氧性條件下使氨氮化合物硝 化、並去除廢水中BOD、COD等有機物,輔以在厭氧性條件下 另行脫硝去除硝酸鹽氮化合物(即所謂之A20程序),其程序 複雜’佔用大量處理面積,且處理成本亦較為高昂。 另一方面,薄膜分離系統現已廣泛用於進行廢水處理,其 具有許多優點’且可應用於各種產業和民生廢水的處理及回收 再利用,可謂目前及未來的主流。 目前已有部分技術係針對生物處理結合薄膜過濾而發展, 亦即利用微遽(Microfiltraticm,MF )或超濾(ultrafiltrati〇n,UF ) 微孔薄膜進行反應槽中懸浮生物污泥之分離,以得到水質良好 之出々il水例如薄膜生物反應技術(Membrane bioreactor, MBR)。然因廢水與高濃度污泥的成分複雜,懸浮生物污泥膠羽 201119955 與顆粒常會吸附於膜面上或膜孔中,造成膜孔的阻塞形成結 垢,因此需要經常清洗或更換膜材;由於薄膜膜材壽命與操作 年限較短,需經常更換,且其成本較為高昂,因而造成操作不 便且不符經濟效益,此為目前亟需突破的瓶頸。 申請人已研發出一種「多功能廢水處理系統」並提出專利 申請(申請號第98114342號,申請曰為98年4月30曰),以 改善上述問題,其可減少生物處理後出流水中所含懸浮顆粒 量,大幅降低薄膜模組浸置槽中懸浮污泥與顆粒濃度,以提升 薄膜模組的處理效能及使用年限;更可於同一處理槽中以單一 反應槽控制曝氣模式操作同時去除水中的BOD、COD等有機 物與氮化合物以及懸浮顆粒。 為進一步提升多功能廢水處理系統的處理效率,申請人經 悉心試驗與研究,對多功能廢水處理系統提出了改良設計。藉 由調整多功能廢水處理系統中所含之廢水生物處理單元的組成 種類,進一步提高其處理效果。本發明具有操作簡單、廢棄污 泥量少、除氮除碳效果佳之優勢,且可於短時間内使生物處理 槽達穩定,深具應用價值。 【發明内容】 本發明之第一目的在於提供一種廢水生物處理單 元,其係以醋酸纖維予以塑形,可強化活性污泥聚集效 果並具較佳處理效率。 本發明之第二目的在於提供一種廢水生物處理單元 201119955 藉以製作污泥聚集性佳且處理效率高之廢 本發明之第二Bmi 卢… 目的在於提供-種固定式之活性污泥 處理早元,杳甘處m ,. .....:廢水生物處理槽中進行廢水處理 時不致輕易自污泥平&士辨车丨# 、 聚、·。體剝洛而導致水中懸浮物濃度201119955 VI. INSTRUCTIONS OF THE INVENTION: TECHNICAL FIELD The present invention relates to a wastewater biological treatment system', particularly to a wastewater biological treatment system using an activated sludge method. [Prior Art] The biological treatment system belongs to a wastewater treatment program. The secondary treatment process is mainly used to treat the wastewater after primary treatment and sedimentation, so that the wastewater is discharged after being treated by the biological treatment process and the final settling tank, which utilizes the metabolism of microorganisms to 'complex organic The compound is decomposed to remove biochemical Oxygen Demand (BOD), chemical oxygen demand (COD) and other organic substances, as well as nitrogen, dish and other compounds. Wastewater biological treatment procedures can generally be divided into good Oxygen treatment and anaerobic treatment, in which aerobic treatment is used to remove organic matter (carbon) from water and bio-oxidation of organic nitrogen and ammonia nitrogen compounds in wastewater into nitrate nitrogen compounds, while anaerobic treatment can be used for Treatment of nitrate nitrogen compounds in water (ie denitration procedure). The microorganisms used in the biological treatment process of wastewater are mainly composed of microorganisms such as bacteria, fungi, steaming, protozoa, etc., and it is often necessary to separately cultivate microbial groups of different compositions for different sources of wastewater and the types of substances to be removed. The impact factor of processing efficiency is very complicated, and it is very difficult to rely on the accumulation of experience in operation. The activated sludge process is an aerobic biological treatment method in which the wastewater after the primary treatment 201119955 flows into the aeration tank and is mixed with the activated sludge in the tank, and flows into the final settling tank to precipitate and separate the sludge. With the clean water; part of the separated sludge is continuously refluxed to the aeration tank (so-called return sludge), while the other part is discharged and advanced treatment (so-called waste treatment). In practice, in addition to the development of microbial populations, parameters such as residence time, sludge return flow, and aeration conditions must be precisely controlled to find the optimal operating efficiency of the system operating conditions. Since the activated sludge system is composed of a suspended aerobic microbial population, it is easy to peel off from the agglomerates, resulting in an increase in the concentration of suspended solids in the water; in addition to increasing the processing load of the activated sludge process, it also causes operating conditions. Not easy to control. In addition, in order to achieve the purpose of biological nitrification and biological denitrification, due to the selective decomposition of microorganisms, the existing biological treatment procedures must utilize multiple designs of sludge reflux and wastewater reflux, and repeat the gas in different reaction tanks (Anoxic). 'Anaerobic and Aerobic conditions control, nitrification of ammonia nitrogen compounds under aerobic conditions, and removal of BOD, COD and other organic matter in wastewater, supplemented by additional denitrification to remove nitric acid under anaerobic conditions Salt nitrogen compounds (the so-called A20 program), the complexity of the program 'occupies a large amount of processing area, and the processing cost is also relatively high. On the other hand, membrane separation systems are now widely used for wastewater treatment, which has many advantages, and can be applied to the treatment and recycling of various industries and people's livelihood wastewater, which can be said to be the current and future mainstream. At present, some technologies have been developed for the biological treatment combined with membrane filtration, that is, the separation of suspended biological sludge in the reaction tank by microfilasure (MF) or ultrafiltrati〇n (UF) microporous membrane. A good water quality 々 il water such as Membrane bioreactor (MBR) is obtained. However, due to the complex composition of wastewater and high-concentration sludge, suspended biological sludge rubber feather 201119955 and particles often adsorb on the membrane surface or membrane pores, causing membrane pore blockage to form scale, so it is necessary to clean or replace the membrane frequently; Due to the short life and operating life of the film membrane, it needs to be replaced frequently, and its cost is relatively high, which causes inconvenience in operation and is not economical. This is a bottleneck that needs to be broken. The applicant has developed a "multi-functional wastewater treatment system" and filed a patent application (Application No. 98114342, filed on April 30, 1998) to improve the above problems, which can reduce the water in the discharged water after biological treatment. Containing suspended particles, greatly reducing the concentration of suspended sludge and particles in the membrane module immersion tank to improve the processing efficiency and service life of the membrane module; it can also control the aeration mode operation in a single reaction tank in the same treatment tank. Removal of organic matter such as BOD and COD from water and nitrogen compounds and suspended particles. In order to further improve the processing efficiency of the multifunctional wastewater treatment system, the applicant has carefully improved the design of the multifunctional wastewater treatment system through careful testing and research. The treatment effect is further improved by adjusting the composition of the biological treatment unit of the wastewater contained in the multifunctional wastewater treatment system. The invention has the advantages of simple operation, less waste sludge, good nitrogen removal and carbon removal effect, and can stabilize the biological treatment tank in a short time, and has deep application value. SUMMARY OF THE INVENTION A first object of the present invention is to provide a wastewater biological treatment unit which is shaped by cellulose acetate to enhance the effect of activated sludge aggregation and has a better treatment efficiency. A second object of the present invention is to provide a wastewater biological treatment unit 201119955, which is capable of producing a sludge with good sludge aggregation and high treatment efficiency. The second Bmi of the present invention aims to provide a fixed type of activated sludge treatment early.杳甘处m ,. .....: When the wastewater treatment is carried out in the wastewater biological treatment tank, it is not easy to use the sludge flat & Body stripping results in suspended solids concentration in water

本發明之第四目的在於提供-種廢水生物處理設 備’其設計簡單、易於操作,無須污泥迴流之設計;此 外’所提供之廢水生物處理設備具有啟動時間短、污泥 在短時間内即可達到穩定之優勢。The fourth object of the present invention is to provide a wastewater biological treatment device which is simple in design, easy to operate, and does not require sludge recirculation design. In addition, the wastewater biological treatment equipment provided has a short start-up time and sludge in a short time. Can achieve the advantage of stability.

的製備方法, 水生物處理單 本發明之第五目的在於提供一種廢水處理系統,其 含有以醋酸纖維予以塑形之廢水生物處理單元以去除廢 水中的有機物與氮化合物,並設有薄膜模組以濾除廢水 中所含之懸浮顆粒。本發明之廢水處理系統操作簡單、 成本低、具毒物應變能力、且可於單-反應槽控制曝氣 模式條件下去除水中有機物與氮化合物,並有助於提升 薄臈模組的處理效能,減緩薄膜模組之消耗。 本發明之第六目的在於提供一種廢水處理系統其 可減少生物處理後出流水令所含懸浮顆粒量,藉以提升 薄膜模組的處理效能及使用年限。 本發明之第七目的在於提供一種廢水處理系統,其 可於單一槽體中同時除氮除碳及濾除懸浮微粒,藉以簡 201119955 化處理程序並減少所需之處理面積。 基於上述目的,本發明提出一種廢水生物處理單 生 元,用於去除廢水中之有機物與氮化合物,其包括一 物擔體以及用於支撐及固定該生物擔體之一支撐裝置. 該生物擔體係含有經調製之活性生物污泥以及醋酸纖 維。 ’ 根據上述構想,該支撐裝置係一籠狀結構,該籠狀 結構係由位於不同平面之i少三個環狀結構建構而成。 較佳為’該等環狀結構是由聚乙烯或聚丙烯材料製成。 在-較佳實施例中,該等環狀結構之内徑係介於5毫米 與30¾米之間’且較佳為25毫米。 根據另-構想,該支縣置係含有複數個網孔之— 網板。較佳為’該網板是由聚乙埽或聚丙烯材料製成且 該等網板與網孔之大小係依據廢水氣理負荷與該生物擔 體之組成而設計。 本發明另提出一種用於製作廢水生物處理單元之方 法:所述廢水生物處理單元係用於去除廢水中之有機物 與氮化合物’該方法包今6A ff$< A& / 的步驟為.(a)製備一醋酸纖維 ㈣溶液’其重量百分濃度係實質上為15%:⑻將一定 里之活m與一定量之該醋酸纖維丙嗣溶液混合,以 形成一生物擔體;⑷將該生物擔體填人—域裝置中, 以形成—生物處理單元,·⑷將該生物處理單元浸入^ 7 S3 201119955 /谷液中並予以乾燥;以及(e)於—曝氣條件下清洗經乾燥 之該生物處理單元。 根據上述構想,在步驟(b)中’該活性污泥之固體含 量係實質上為12%,且其實質上係取1〇〇公克。 根據上述構想,在步驟(b)中,該醋酸纖維丙酮溶液 實質上係取300毫升。 根據上述構想,在步驟(c)中,該支撐裝置係由位於 不同平面之至少三個環狀結構建構而成。在另—實施例 中’該支撐裝置係含有複數個網孔之一網板。 根據上述構想,在步驟(d)中,係將該生物處理單元 次入甲苯溶液中實質上達丨分鐘,且乾燥時間實質上為 3至4小時。 根據上述構想,在步驟(d)中,該生物處理單元係於 排氣良好之空間中進行乾燥。 根據上述構想,在步驟中,係以水清洗該生物處 理單元實質上達6小時。 本發明亦提出一種廢水處理設備,用於去除廢水中 之有機物和氮化合物,該廢水處理設備包括一生物反應 槽,其特徵在於該生物反應槽中填有至少一廢水生物處 理單元,且該等廢水生物處理單元各包括一生物擔體與 用於支撐及固定該生物擔體之一支撐裝置,該生物擔體 含有經調製之活性生物污泥以及醋酸纖維。 201119955 本發明提出一種廢水處理系統,其包括:一生物反 應槽,其填有至少一廢水生物處理單元,所述廢水生物 處理單元係各由一生物擔體與用於支撐及固定該生物擔 體之一支撐裝置所構成,其中該生物擔體含有經調製之 活性生物污泥以及醋酸纖維;以及一薄膜反應槽,其含 有至少一薄膜模組,該薄膜反應槽之一進流口係與該生 物反應槽之一出流口流體相通。 根據上述構想,該生物反應槽係一柱狀反應槽與一 矩形反應槽其中之一。 根據上述構想,該矩形反應槽内具有至少一箱籠匣 體’所述箱籠匣體内填有複數個所述廢水生物處理單元。 本發明提出一種可同時除氮除碳及濾除懸浮顆粒之 廢水處理槽,其包括:一反應槽體;至少一廢水生物處 理單元’其配置於該反應槽體内並浸置於該反應槽體内 之廢水中’所述廢水生物處理單元係各由一生物擔體與 用於支撐及固定該生物擔體之一支撐裝置所構成,其中 該生物擔體含有經調製之活性生物污泥以及醋酸纖維; 以及至少一薄膜模組,其係設置在該反應槽體中並與該 反應槽體内之廢水接觸,其中所述廢水生物處理單元係 以生物處理方式去除廢水中的有機物與氮化合物,且廢 水中所含之懸浮顆粒係藉由所述薄膜模組予以渡除。 根據上述構想’該支樓裝置係一籠狀結構,所述廢 201119955 水生物處理單元係藉由該反應槽體内之廢水而以流體化 方式分散於該反應槽體中。 根據上述構想,該反應槽體内包括至少一箱籠匣 體’所述廢水生物處理單元係填置於所述箱籠匣體中。 根據上述構想,所述至少一箱籠匣體與所述至少一 薄膜模組係呈串聯配置。 根據上述構想,該支撐裝置係含有複數個網孔之一 網板。較佳為,所述網板與所述至少一薄膜模組係呈串 聯配置。 本發明得藉由下列圖式及詳細說明’俾得以令讀者 更深入瞭解: 【實施方式】 以下即配合圖式說明本發明之具體實施方式,·然需 瞭解的是,這些圖式中所標示之元件係為說明清晰之 用其並不代表實際的尺寸與比例,且為求圖面簡潔以 利於瞭解,部分圖式中亦省略了習知元件之繪製。 "月參閱第一 Α圖,其係一示意圖,用以說明本發明 之一較佳實施例之廢水生物處理單元。本發明之廢水生 物處理單元1〇A係由一生物擔體12與一支撐裝置"所 擔體12即經調製之活性生物污泥球,其 係由活性污泥與醋酸纖維溶液混合調製而成;而支揮裝 [S] 10 201119955 置14係具有一内部空間之籠壯 > 认 心龍狀結構,該支撐裝置丨4之 蘢狀結構使該生物擔體12徨/Cf u Z诗以保持容置於其内部空間 中。在本實施例中,支撐震置14係由位於不同平面由 聚乙稀(的咖^,PE )所製成之三個環狀結構! 42、 M4與146交錯建構而成。根據本發明,環狀結構μ]、 144與146之内徑係介於5毫米與3〇毫米之間,並藉由 熱炼方式彼此膠合㈣㈣成所需之球㈣狀結構The present invention provides a wastewater treatment system comprising a wastewater biological treatment unit shaped by cellulose acetate to remove organic matter and nitrogen compounds in wastewater, and a membrane module is provided. In order to filter out suspended particles contained in the wastewater. The wastewater treatment system of the invention has simple operation, low cost, toxic strain capability, and can remove organic matter and nitrogen compounds in water under the single-reaction tank controlled aeration mode, and helps to improve the processing efficiency of the thin tantalum module and slow down the film. The consumption of modules. A sixth object of the present invention is to provide a wastewater treatment system which can reduce the amount of suspended particles contained in the water discharge after biological treatment, thereby improving the treatment efficiency and service life of the membrane module. A seventh object of the present invention is to provide a wastewater treatment system which can simultaneously remove nitrogen and carbon and filter out suspended particles in a single tank, thereby reducing the required treatment area by reducing the processing time. Based on the above object, the present invention provides a wastewater biological treatment single unit for removing organic matter and nitrogen compounds in wastewater, which comprises a material carrier and a supporting device for supporting and fixing the biological carrier. The system contains prepared active biological sludge and acetate fibers. According to the above concept, the supporting device is a cage structure which is constructed by three annular structures which are located in different planes. Preferably, the annular structures are made of a polyethylene or polypropylene material. In the preferred embodiment, the annular structures have an inner diameter of between 5 mm and 303⁄4 m and preferably 25 mm. According to another concept, the county has a plurality of meshes - a stencil. Preferably, the stencil is made of polyethylene or polypropylene material and the size of the stencil and mesh is designed according to the effluent load of the wastewater and the composition of the biological support. The present invention further provides a method for producing a wastewater biological treatment unit: the wastewater biological treatment unit is used to remove organic matter and nitrogen compounds in wastewater. The method of the method is 6A ff$<A&/. a) preparing a cellulose acetate (4) solution having a weight percent concentration of substantially 15%: (8) mixing a certain amount of live m with a certain amount of the cellulose acetate hydrazine solution to form a biological support; (4) The biological carrier is filled in a domain device to form a biological treatment unit, (4) the biological treatment unit is immersed in ^ 7 S3 201119955 / gluten solution and dried; and (e) is dried under aeration conditions The biological processing unit. According to the above concept, the solid content of the activated sludge in the step (b) is substantially 12%, and it is substantially 1 gram. According to the above concept, in the step (b), the cellulose acetate acetone solution is substantially taken up to 300 ml. According to the above concept, in the step (c), the supporting device is constructed by at least three annular structures located in different planes. In another embodiment, the support device comprises a web of a plurality of meshes. According to the above concept, in the step (d), the biological treatment unit is sub-into the toluene solution for substantially several minutes, and the drying time is substantially 3 to 4 hours. According to the above concept, in the step (d), the biological treatment unit is dried in a space where the exhaust gas is good. According to the above concept, in the step, the biological treatment unit is washed with water for substantially 6 hours. The invention also provides a wastewater treatment device for removing organic matter and nitrogen compounds in wastewater, the wastewater treatment device comprising a biological reaction tank, characterized in that the biological reaction tank is filled with at least one wastewater biological treatment unit, and the same The wastewater biological treatment unit each includes a biological support and a support device for supporting and immobilizing the biological support, the biological support containing the prepared active biological sludge and acetate fibers. 201119955 The present invention provides a wastewater treatment system comprising: a biological reaction tank filled with at least one wastewater biological treatment unit, each of the biological treatment units of the wastewater being supported by a biological carrier and used for supporting and fixing the biological carrier a support device comprising: the biological carrier comprising the prepared activated biological sludge and the cellulose acetate; and a film reaction tank comprising at least one membrane module, the inlet port of the membrane reaction tank One of the biological reaction tanks is in fluid communication with the outlet. According to the above concept, the biological reaction tank is one of a columnar reaction tank and a rectangular reaction tank. According to the above concept, the rectangular reaction tank has at least one tank body. The tank body is filled with a plurality of the wastewater biological treatment units. The invention provides a wastewater treatment tank capable of simultaneously removing nitrogen and removing carbon and filtering suspended particles, comprising: a reaction tank body; at least one wastewater biological treatment unit disposed in the reaction tank and immersed in the reaction tank In the wastewater in the body, the wastewater biological treatment unit is composed of a biological carrier and a supporting device for supporting and fixing the biological carrier, wherein the biological carrier contains the prepared activated biological sludge and Acetate; and at least one membrane module disposed in the reaction tank and in contact with wastewater in the reaction tank, wherein the wastewater biological treatment unit biologically removes organic matter and nitrogen compounds in the wastewater And the suspended particles contained in the wastewater are removed by the thin film module. According to the above concept, the branch building device is a cage structure, and the waste 201119955 aquatic biological treatment unit is fluidized in the reaction tank body by the waste water in the reaction tank. According to the above concept, the reaction tank body includes at least one tank body. The waste water biological treatment unit is filled in the tank body. According to the above concept, the at least one box cage body and the at least one film module are arranged in series. According to the above concept, the supporting device comprises a mesh plate of a plurality of meshes. Preferably, the stencil and the at least one film module are arranged in series. The present invention can be further understood by the following drawings and detailed descriptions. [Embodiment] The following is a description of the specific embodiments of the present invention, and it is to be understood that The components are used for clarity and do not represent actual dimensions and proportions, and the drawing is simplified for the sake of understanding, and the drawing of the conventional components is omitted in some drawings. "Monthly, reference is made to the first diagram, which is a schematic diagram for illustrating a wastewater biological treatment unit in accordance with a preferred embodiment of the present invention. The wastewater biological treatment unit 1A of the present invention is composed of a biological carrier 12 and a support device, which is a modulated active biological sludge ball, which is prepared by mixing activated sludge and cellulose acetate solution. ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; ; To keep it in its internal space. In this embodiment, the support striking 14 is made up of three ring-shaped structures made of polyethylene (PE) in different planes! 42. M4 and 146 are interlaced. According to the present invention, the inner diameters of the annular structures μ], 144 and 146 are between 5 mm and 3 mm, and are glued to each other by means of heat refining (4) and (4) into a desired spherical (quad) structure.

第一 B圖係本發明另—實施例之廢水生物處理翠元 示意圖。在此實施例中,用於固定生物擔體之支撐裝置 係一聚乙烯或聚丙烯網板14,,其含有複數個網孔MS 以使經調製之生物擔體容置於其中。在本發明中網板 與網孔148的大小與型態係依據實際廢水處理負荷與生 物擔體組成而設計,以輔助生物擔體附著於網板^ 4,上、 且不影響廢水通過其間為要。 如第二圖所示,其為根據本發明一實施例之廢水生 物處理單元實際外觀照片;照片中右側為一支撐生物擔 體用之網板的實際設計型態,而左側為含有生物擔體分 佈附著於其上之廢水生物處理單元。根據本發明之實施 例,除網格大小係經設計外,在網格交會處亦設計有貫 孔22與凸柱24專輔助結構’以利生物擔體容置並附著 於其中。由第二圖左側照片可知,藉由本發明之網板設 計’生物擔體確可緊緻附著於支撐裝置上,減少剝落的 機會。 在本發明中’生物擔體是由取自實際廢水處理廠中 201119955 二級沉澱池底之活性生物污泥養成與調製而成,藉由執 行第三圖所示之程序,調製所需之生物擔體,並將其容 置於支樓結構中,而形成本發明之廢水處理單元。根據 本發明之一實施例,生物擔體的調製程序詳述如下: 利用離心脫水的方式來調整取自沉澱池底之活性生 物污泥的固體含量’使其固體含量介於10%與15〇/〇之 間,如步驟31所示。於65〇毫升之丙酮(Acet〇ne)中 加入100公克之醋酸纖維(Cellulose Acetate),並以攪 拌子擾拌約1 00分鐘’形成濃度約i 5%之醋酸纖維溶液, 如步驟32所示。 此份置配比之醋酸纖維溶液可用以固定約2〇〇公克 的活性生物污泥( 300毫升之醋酸纖維溶液搭配1〇〇公 克、固體含量約12%之活性污泥),當然,丙酮與醋酸纖 維的使用量係依欲固定之活性生物污泥量而定,其呈— 定之比例。 細言之,取300毫升的醋酸纖維溶液加入1〇〇公 克、固體含量經調整為12〇/〇之活性生物污泥中,加以授 拌至呈膠狀,並放入直徑為28 mm (内徑約25 mm)之 PE環’繼續擾拌直到活性生物污泥整個填充於pE環中, 即形成球狀廢水處理單元,分別如步驟33與步驟34所 不。在另一實施例中,膠狀之活性污泥/醋酸纖維混合物 係填入PE或PP網板之網格中,以形成板狀廢水處理單 元’如步驟34,所示。 以曱苯浸洗所形成之污泥球或污泥板約丨分鐘後取 12 201119955 出 於排氣良好之環境令 風乾該污泥球或污泥板達The first B is a schematic diagram of the biological treatment of wastewater in the other embodiment of the present invention. In this embodiment, the support means for securing the biological support is a polyethylene or polypropylene mesh 14, which contains a plurality of meshes MS to accommodate the modulated biological carrier. In the present invention, the size and shape of the stencil and the mesh 148 are designed according to the actual wastewater treatment load and the composition of the biological support, so as to assist the biological support to adhere to the stencil 4, without affecting the passage of waste water therebetween. Want. As shown in the second figure, it is a photograph of the actual appearance of the wastewater biological treatment unit according to an embodiment of the present invention; the right side of the photograph is a practical design form of a mesh plate for supporting the biological support, and the left side is a biological support. A wastewater biological treatment unit attached to it. In accordance with an embodiment of the present invention, in addition to the mesh size design, a through hole 22 and a stud 24 are also provided at the intersection of the mesh to facilitate the attachment and attachment of the biological carrier. As can be seen from the photograph on the left side of the second figure, the stencil design of the present invention can be tightly attached to the support device to reduce the chance of flaking. In the present invention, the biological carrier is formed and prepared from the activated biological sludge taken from the bottom of the second-stage sedimentation tank of the 201119955 in the actual wastewater treatment plant, and the desired organism is prepared by performing the procedure shown in the third figure. The support is housed in a building structure to form the wastewater treatment unit of the present invention. According to an embodiment of the present invention, the preparation procedure of the biological carrier is detailed as follows: The solid content of the activated biological sludge taken from the bottom of the sedimentation tank is adjusted by centrifugal dehydration to make the solid content between 10% and 15〇. Between /〇, as shown in step 31. Add 100 grams of Cellulose Acetate to 65 ml of acetone (Acet〇ne) and mix with a stirrer for about 100 minutes to form a solution of about 5% acetate solution, as shown in step 32. . The ratio of the acetate solution can be used to fix about 2 gram of activated biological sludge (300 ml of acetate solution with 1 gram of activated sludge and about 12% solids of activated sludge). Of course, acetone and The amount of acetate used is determined by the amount of active biological sludge to be fixed, which is in a predetermined ratio. In a nutshell, 300 ml of acetic acid fiber solution was added to 1 gram of activated biological sludge with a solid content adjusted to 12 〇 / 〇, and then mixed into a gel form and placed in a diameter of 28 mm (within The PE ring of about 25 mm) continues to be disturbed until the active biological sludge is completely filled in the pE ring, that is, a spherical wastewater treatment unit is formed, as shown in steps 33 and 34, respectively. In another embodiment, the colloidal activated sludge/acetate blend is filled into a grid of PE or PP screens to form a sheet wastewater treatment unit' as shown in step 34. Take the sludge ball or sludge board formed by the benzene immersion in about 丨 minutes and take it 12 201119955 Out of the well-ventilated environment, air dry the sludge ball or sludge board

小時以使甲苯蒸發, 的環境中以水浸洗污 如步驟35所示;最後,於持續曝氣 泥球或污泥板約6小時,直到污泥 球或污泥板上沒有甲婪& 〇〇 本殘餘’即製成本發明之廢水處理 單元’如步驟36所示。 在本發明中,嚴顆嵌★占 早顆廢水處理單元的大小係依組成支 禮結構的Μ環的内徑而定,較佳係介於5_與3〇醜 之間(下文將進-步說明内徑為25 mm與16 mm之處理 結果)’ PE環的内你勒| ^ k越小’即可形成越小的籠狀結構, 合置於’、所限定之内部空間中的生物擔體即越為緊緻。 換言之,藉由PE援ρ λα τ 尺寸的不同選擇,即可依實際處理條 件來使用不同大小的廢水處理單元。In the environment where the toluene is evaporated, the water is immersed in the environment as shown in step 35; finally, the aerated mud ball or sludge board is continuously aerated for about 6 hours until there is no nails & The residue of the sputum is formed into the wastewater treatment unit of the present invention as shown in step 36. In the present invention, the size of the severely embedded wastewater treatment unit depends on the inner diameter of the ankle ring that constitutes the support structure, preferably between 5 and 3 ugly (hereinafter will be - Steps indicate the results of the treatment of the inner diameter of 25 mm and 16 mm) 'The inner ring of the PE ring| ^ k is smaller, the smaller the cage structure can be formed, and the creatures enclosed in the defined internal space The more compact the body is. In other words, different sizes of wastewater treatment units can be used depending on the actual processing conditions by different choices of PE aids ρ λα τ size.

上述實施例係利用三個ρΕ環來建構廢水處理單元 的支撐結構,然其數量與材質並無一定之限制,其他塑 膠材料、陶竟材料、甚或金屬材料亦屬可行;更甚者, 亦可如用% i兄可分解之材料來製造本發明中所需之支撐 、,’。構,以利曰後此處理單元時之廢棄處理。 本發明亦提出-種廢水處理系統以去除廢水中之有 機物與氮化合物。請參閱第四圖,其係本發明之廢水處 理系統之第-實施方式的配置示意圖。本發明之廢水處 理系統400主要由一生物反應槽410與-薄膜反應槽420 彼此流體相通而組成。生物反應槽410中填置有複數個 廢水生物處理單元415;薄膜反應槽42〇中含有至少一 薄膜模組425。在本發明中’每一個廢水生物處理二元 13 201119955 415即如第一 A圖中所示之由一生物擔體與一支樓裝置 所構成的球狀廢水生物處理單元。 如第四圖所示,待處理之廢水係藉由進流泵43〇的 作用而自進流貯槽440泵送至本發明之生物反應槽41〇 中。在此例中,本發明之生物反應槽41〇係一柱狀反應 槽’其内填置了複數個球形廢水生物處理單元4丨5。待 處理之廢水係自柱狀反應槽底部的進流口 4丨〇 A進入槽 體,於反應槽中進行有機物與氮化合物之去除程序後, 由反應槽上方之出流口 41 0B排出。 在本發明中’生物反應槽410的出流口 41〇b係與 薄膜反應槽420的進流口 420A流體相通。換言之,經本 發明之生物反應槽41 0進行除氮除碳處理後之廢水係經 由進流口 420A而進流至薄膜反應槽42〇内,以藉由設置 於槽中的薄膜模組425進行懸浮顆粒之濾除。經濾除之 渗流水係經泵送而自薄膜反應槽42〇排出至貯槽48〇 中’以達澄清出水之效。 在本發明中’生物處理槽410中廢水生物處理單元 415的填充率可依實際處理需求而加以調整(如:每立 方公分之槽體空間含有0.3立方公分之填充量,即表示 體積填充率為30%),且藉由空壓機或鼓風機450、氣體 調節器(圖中未示)之調整,可提高對槽體之通氣量, 以調整槽體之溶氧條件;並可使生物反應槽41〇形成類 似於完全混合或柱狀流之形式。 請參閱第五圖’其係本發明之廢水處理系統之第二 201119955 實施方式的配置示意圖。本發明之廢水處理系統5 〇 〇主 要由一生物反應槽5 1 0與一薄膜反應槽52〇彼此流體相 通而組成。根據此實施方式,生物反應槽5 1 〇係由一矩 形反應槽體建構而成’其内配置有至少一箱籠g體512。 換言之,在此例中,球狀廢水生物處理單元5丨5係填置 於箱籠匣體512中,再進而配置於生物反應槽51〇内, 以去除廢水中所含之有機物與氮化合物,進行除碳除氮 作用。薄膜反應槽520中含有至少一薄膜模組525。在 本發明中,每一個廢水生物處理單元515是由一支撐結 構以及容置於其中之生物擔體形成為一球形體(參前述 第一 A圖之相關說明)。 如第五圖所示,待處理之廢水係藉由進流泵53〇的 作用而自進流貯槽54〇泵送至本發明之矩形生物反應槽 5 1 0中。待處理之廢水係藉由進流泵53〇的作用而自進 流貯槽540泵送至本發明之反應槽體51〇中,由反應槽 右方之出流口 510B排出。 在本發明中’生物反應槽5 10的出流口 5 1 0B係與 薄膜反應槽520的進流口 52〇A流體相連。換言之,經本 發明之生物反應槽5丨〇進行除氮除碳處理後之廢水係經 由進流口 520A而進流至薄膜反應槽52〇内,以藉由設置 於槽中的薄膜模組525進行懸浮顆粒之濾除。經滤除之 渗流水係經果送而自薄膜反應槽520排出至貯槽58〇 中’以達澄清出水之效。 同樣的’在本發明中,矩形生物處理槽510中球狀 15 201119955 廢水生物處理單元515的填充率可依實際處理需求而加 以調整(如:每立方公分之槽體空間含有0.3立方公分 之填充量,即表示體積填充率為3 0%),且藉由空壓機或 鼓風機55 0、氣體調節器(圖中未示)之調整,可提高 對槽體之通氣量,以調整槽體之溶氧條件;並可使生物 反應槽5 1 〇形成類似於完全混合或柱狀流之形式。 請參閱第六圖,其係本發明之廢水處理系統之第二 貫施方式的配置示意圖。在此實施方式中,本發明之廢 水處理系統600主要由單一反應槽體61〇建置而成複 數個廢水生物處理單元6丨5係以箱籠匣體形式置放於反 應槽體610中,以去除廢水中所含之有機物與氮化合 物進行除石反除氮作用;在反應槽體610中設置至少一 薄膜模組625,其與反應槽體中待處理之廢水接觸,藉 以滤除廢水中所含之懸浮顆粒。在本發明中,每一個廢 水生物處理單元615是由一支推結構與容置於其中之生 物擔體所形成之一球形體(請參前述第一A圖之相關說 明)。 如第六圖所示,待處理之廢水係藉由進流泵63〇的 作用而自進流貯槽640泵送至本發明之反應槽體61〇 中。在本發明中,待處理之廢水係自反應槽體61〇之進 流口 61 0A進入槽體’於反應槽體610中藉由廢水生物處 理單元615的作用而進行有機物與氮化合物之去除程 序’同時藉由設置於槽體中的薄膜模組625進行懸浮顆 粒之渡除。經除碳除氮以及懸浮顆粒濾除之滲流液係經 16 201119955 泵送而自反應槽體6 1 0排出至貯槽680,以達澄清出水 之效。同樣的,藉由空壓機或鼓風機65〇與氣體調節器 (圖中未示)調整,可提高對槽體之通氣量,以調整槽 體之溶氧條件;並可使廢水流體以類似於完全混合或柱 狀流之形式而分散於反應槽體6 1 0中。 閱第七圖’其說明本發明之另一較佳實施方 式在本心明中,廢水生物處理單元74除可藉由待處理In the above embodiment, the three p-rings are used to construct the support structure of the wastewater treatment unit. However, the quantity and material are not limited, and other plastic materials, ceramic materials, or even metal materials are feasible; more importantly, If the material that can be decomposed by the % i brother is used to make the support required in the present invention, '. Structure, in order to facilitate the disposal of this processing unit. The invention also proposes a wastewater treatment system for removing organic matter and nitrogen compounds from wastewater. Please refer to the fourth drawing, which is a schematic view showing the configuration of the first embodiment of the wastewater treatment system of the present invention. The wastewater treatment system 400 of the present invention is mainly composed of a biological reaction tank 410 and a membrane reaction tank 420 in fluid communication with each other. The biological reaction tank 410 is filled with a plurality of wastewater biological treatment units 415; the membrane reaction tank 42 contains at least one membrane module 425. In the present invention, each wastewater biological treatment binary 13 201119955 415 is a spherical wastewater biological treatment unit composed of a biological carrier and a building device as shown in Fig. A. As shown in the fourth figure, the wastewater to be treated is pumped from the inlet sump 440 to the biological reaction tank 41 of the present invention by the action of the inlet pump 43. In this example, the biological reaction tank 41 of the present invention is a columnar reaction tank which is filled with a plurality of spherical wastewater biological treatment units 4丨5. The wastewater to be treated is introduced into the tank from the inlet port 4丨〇 A at the bottom of the column reaction tank, and the removal process of the organic matter and the nitrogen compound is carried out in the reaction tank, and then discharged from the outlet port 41 0B above the reaction tank. In the present invention, the outlet port 41〇b of the biological reaction tank 410 is in fluid communication with the inlet port 420A of the membrane reaction tank 420. In other words, the wastewater subjected to the nitrogen and carbon removal treatment by the biological reaction tank 41 0 of the present invention flows into the membrane reaction tank 42 through the inlet port 420A to be suspended by the membrane module 425 disposed in the tank. Filtration of the particles. The filtered percolating water is pumped and discharged from the membrane reaction tank 42 to the storage tank 48' to achieve the effect of clarifying the water. In the present invention, the filling rate of the wastewater biological treatment unit 415 in the biological treatment tank 410 can be adjusted according to the actual processing demand (for example, the volume of the cubic space per cubic centimeter is 0.3 cubic centimeters, which means that the volume filling rate is 30%), and by adjusting the air compressor or blower 450, gas regulator (not shown), the ventilation of the tank can be increased to adjust the dissolved oxygen condition of the tank; and the biological reaction tank can be 41〇 forms a form similar to a fully mixed or columnar flow. Please refer to the fifth drawing, which is a schematic view of the configuration of the second 201119955 embodiment of the wastewater treatment system of the present invention. The wastewater treatment system 5 of the present invention is mainly composed of a biological reaction tank 510 and a membrane reaction tank 52 流体 in fluid communication with each other. According to this embodiment, the biological reaction tank 5 1 is constructed by a rectangular reaction tank body, and at least one tank g body 512 is disposed therein. In other words, in this example, the spherical wastewater biological treatment unit 5丨5 is placed in the box cage body 512, and further disposed in the biological reaction tank 51〇 to remove the organic matter and nitrogen compounds contained in the wastewater. In addition to carbon and nitrogen. The film reaction tank 520 includes at least one film module 525. In the present invention, each of the wastewater biological treatment units 515 is formed of a support structure and a biological carrier accommodated therein as a spherical body (refer to the related description of the first A diagram). As shown in the fifth figure, the wastewater to be treated is pumped from the inflow sump 54 to the rectangular bioreactor 50 of the present invention by the action of the inflow pump 53A. The wastewater to be treated is pumped from the inlet tank 540 to the reaction tank body 51 of the present invention by the action of the inlet pump 53, and is discharged from the outlet port 510B on the right side of the reaction tank. In the present invention, the outlet port 5 10 B of the biological reaction tank 5 10 is fluidly connected to the inlet port 52A of the membrane reaction tank 520. In other words, the wastewater subjected to the nitrogen and decarburization treatment of the biological reaction tank 5 of the present invention flows into the membrane reaction tank 52 through the inlet port 520A to be carried out by the membrane module 525 disposed in the tank. Filtration of suspended particles. The filtered percolating water is sent from the membrane reaction tank 520 to the sump 58 ’ by filtration to achieve the effect of clarifying the effluent. Similarly, in the present invention, the filling rate of the spherical biological treatment unit 515 in the rectangular biological treatment tank 510 can be adjusted according to the actual processing demand (for example, the cubic space per cubic centimeter contains 0.3 cubic centimeters of filling). The amount, that is, the volume filling rate is 30%), and by adjusting the air compressor or the blower 55 0 and the gas regulator (not shown), the ventilation amount of the tank body can be increased to adjust the tank body. The dissolved oxygen conditions; and the bioreactor tank 5 1 〇 can be formed in a form similar to a fully mixed or columnar stream. Please refer to the sixth drawing, which is a schematic view showing the configuration of the second embodiment of the wastewater treatment system of the present invention. In this embodiment, the wastewater treatment system 600 of the present invention is mainly constructed by a single reaction tank body 61〇, and a plurality of wastewater biological treatment units 6丨5 are placed in the reaction tank body 610 in the form of a box cage body, The organic matter and the nitrogen compound contained in the waste water are removed to perform de-salt and denitrification; at least one thin film module 625 is disposed in the reaction tank body 610, which is in contact with the wastewater to be treated in the reaction tank body, thereby filtering out the waste water. Containing suspended particles. In the present invention, each of the waste water biological treatment units 615 is formed into a spherical body formed by a push structure and a biomass carrier accommodated therein (refer to the related description of Fig. 1A above). As shown in the sixth drawing, the wastewater to be treated is pumped from the inlet sump 640 to the reaction tank body 61 of the present invention by the action of the inlet pump 63. In the present invention, the wastewater to be treated is introduced into the tank body 610 from the inlet port 61 0A of the reaction tank body 61. The organic matter and the nitrogen compound are removed by the action of the wastewater biological treatment unit 615 in the reaction tank body 610. At the same time, the suspended particles are removed by the film module 625 disposed in the tank. The seepage liquid filtered by removing carbon and nitrogen and suspended particles is discharged from the reaction tank body 61 to the storage tank 680 by pumping in 2011, 20115, to achieve the effect of clarifying the water. Similarly, by adjusting the air compressor or the blower 65〇 and the gas regulator (not shown), the ventilation amount of the tank body can be increased to adjust the dissolved oxygen condition of the tank body; and the wastewater fluid can be similar to It is dispersed in the reaction tank body 61 in the form of a completely mixed or columnar stream. Referring to the seventh figure, which illustrates another preferred embodiment of the present invention, in the present invention, the wastewater biological treatment unit 74 can be treated by

廢水而以類似於流體化床之形式分散於槽體中,亦可填 置於含有複數個滲水孔722之—箱㈣體72()内形成 一廢水處理模組72。根據本發明另—實施方式,該廢水 處理模組72可與第六圖所示之薄膜模組625配置於反應 槽體610中’以於單—反應槽控制曝氣模式條件下進行 有機物與氮化合物之去除’達到對廢水同時除後除氮及 滤除懸洋顆粒之效。在此例中,將球狀廢水生物處理單 凡74填置於箱蘢^體720中之設計可使廢水處理模组 72的更換更易於進行。 、” 根據本發明之另一實施例’在第五圖與第六圖之廢 Χ系統中’亦可利用如第二圖中所示之板狀廢水生 物處理單元來取代箱籠㈣512或72(如第七圖所示) 的使用。 M i ; 第八圖說明了本發明嵌 曰 廢水處理系統對於實際廢水 中化千舄軋置(C〇D ),氨氮 虱虱〔NH3_N)與總氮之去除率, 八中廢水處理系統係使用 .^ ^ ^ ^ 仏馮25¾米之支柱籠,其廢 水處理早體於反應槽中 I髖積填充率為30°/。(即每立方 ί S1 17 201119955The waste water is dispersed in the tank in a form similar to a fluidized bed, or may be filled in a tank (four) body 72 () containing a plurality of water seepage holes 722 to form a wastewater treatment module 72. According to another embodiment of the present invention, the wastewater treatment module 72 can be disposed in the reaction tank body 610 with the membrane module 625 shown in FIG. 6 to perform organic matter and nitrogen under the condition of single-reaction tank controlled aeration mode. The removal of the compound 'achieves the effect of removing nitrogen from the wastewater and removing the suspended particles. In this example, the design of the spherical wastewater biological treatment unit 74 in the tank 720 makes the replacement of the wastewater treatment module 72 easier. According to another embodiment of the present invention, 'in the waste system of the fifth and sixth figures', the plate-shaped wastewater biological treatment unit as shown in the second figure may be used instead of the cage (four) 512 or 72 (eg The use of the seventh figure) M i ; The eighth figure illustrates the removal of the actual wastewater from the inlaid wastewater treatment system (C〇D), ammonia nitrogen [NH3_N) and total nitrogen removal. Rate, Bazhong wastewater treatment system is used. ^ ^ ^ ^ 仏 253 253⁄4 m pillar cage, its wastewater treatment in the reaction tank in the I hip filling rate is 30 ° / (ie per cubic ί S1 17 201119955

公分之槽體空間有0.3立方公分之填充量);水力停留時 間(HRT)係依所處理之廢水條件進行調整(Η*小 時)’在本例中’水力停留時間$ 12小時。空氣流量為 每公升之槽體空間通入1L/min,並以開啟一小時通氣、 關閉兩小時⑴2)之條件進行。由實驗結果可知,本 發明之廢水處理系統對於實際廢水之c〇d與氮化合物 係於短時間内即達穩定去除率9〇%以上,對於氨氮之去 除率更達98·99%’而總氮去除率亦穩定成長至91%。 本發明之廢水處理系統可與多種薄膜模組(例如超 遽中空纖維薄膜,UF Holl〇w Fibers ,其薄膜 孔徑為iOOkDa約為Ο. _或微滤平板膜,MFp_ Membrane其薄膜孔徑約為〇 4μη〇結合應用以於除碳 除氮程序中同時濾除廢水中之懸浮微粒;同時,由於本 發明之廢水處理單體中的生物擔體係容置於支撐結構 (支撐籠或支撐網板)中,可避免微生物體自污泥聚結 體剝落,且可增加污泥齡(Sludge Age)讀十至數百口 日,對水中污染物的處理效率較佳,新生污泥量亦相對 較少,可減少廢棄污泥處理之負荷與困擾。 此外,本發明之廢水處理系統操作簡單、成本低、 具毒物應變能力、且可於單一反應槽控制曝氣模式條件 下去除水中有機物與氮化合物,並有助於提升薄膜模組 的處理效能與使用年限,減緩薄膜模組之消耗,實為一 新穎、進步且具產業實用性與競爭性之發明,深具發展 價值。The tank space of the centimeters has a filling capacity of 0.3 cubic centimeters; the hydraulic retention time (HRT) is adjusted according to the treated wastewater conditions (Η*hours). In this example, the hydraulic retention time is $12 hours. The air flow rate is 1 L/min per liter of the tank space, and is carried out under the conditions of opening one hour of ventilation and closing for two hours (1) and 2). It can be seen from the experimental results that the wastewater treatment system of the present invention has a stable removal rate of more than 9〇% for the actual wastewater c〇d and nitrogen compounds in a short period of time, and a removal rate of 98.99% for the ammonia nitrogen. The nitrogen removal rate also steadily increased to 91%. The wastewater treatment system of the present invention can be combined with a variety of membrane modules (for example, ultra-fine hollow fiber membranes, UF Holl〇W Fibers, which has a membrane pore size of iOOkDa of about Ο. _ or a microfiltration flat membrane, and MFp_ Membrane has a membrane pore size of about 〇. The 4μη〇 combination application is used to simultaneously filter the suspended particles in the wastewater in the carbon removal and nitrogen removal process; meanwhile, the bioburden system in the wastewater treatment monomer of the present invention is accommodated in the support structure (support cage or support mesh) It can prevent the microbial body from peeling off from the sludge agglomerate, and can increase the sludge age (Sludge Age) to read for ten to hundreds of days, the treatment efficiency of the pollutants in the water is better, and the amount of new sludge is relatively less. The waste treatment system of the invention can be reduced in operation and troubles. In addition, the wastewater treatment system of the invention has simple operation, low cost, toxic strain resistance, and can remove organic matter and nitrogen compounds in water under a single reaction tank controlled aeration mode, and It is helpful to improve the processing efficiency and service life of the film module, and to slow down the consumption of the film module. It is a novel, progressive and industrially practical and competitive invention. With development value.

18 201119955 其他免选態樣 在本說明書令所揭露的所有特徵都可能與其他方法 結合,本說明書中所揭露的每一個特徵都可能選擇性的 以:同、相等或相似目的特徵所取代,因此,除了特別 顯者的特徵之外,所有的太% 有的本説明書所揭露的特徵僅是相 等或相似特徵中的一個例子。 雖然本發明已以較佳實祐 子又狂π %例揭路如上’然其並非用18 201119955 Other exemptions All features disclosed in this specification may be combined with other methods. Each feature disclosed in this specification may be selectively replaced by features of the same, equal or similar purpose. In addition to the features of the particulars, all of the features disclosed in this specification are only one of the equivalent or similar features. Although the present invention has been exemplified by the better simplification and madness, the above is not the case.

以限定本發明,任何孰寿卜 J…、思此技藝者,在不脫離本發明之 精神和範圍内,當可作各種之更動與潤飾。 【圖式簡單說明】 第一 A圖係一示意圖’用以說明本發明之一較佳實 施例之廢水生物處理單元; 第一 B圖係—示意圖’用以說明本發明之另一較佳 實施例之廢水生物處理單元; 第二圖係根據本發明—實施例之廢水生物處理單元 實際外觀照片; 第三圖係-流程圖’用以說明本發明之廢水生物處 理單元的製作程序; 第四圖係本發明之廢水處理系統之第—實施方式的 配置示意圖; 第五圖係本發明之廢水處理系統之第二實施方式的 配置示意圖; 19 201119955 配置:::係本發明之廢水處理系統之第三實施方式的 第七圖係一結構示意圖 方式’說明置於廢水處理槽 體;以及 ,其根據本發明一較佳實施 中之—廢水處理單體箱籠g 際廢水 第八圖說明了本發明之廢水處理系統對於實 的處理結果。 'In order to limit the present invention, any of the skilled person can make various changes and refinements without departing from the spirit and scope of the present invention. BRIEF DESCRIPTION OF THE DRAWINGS FIG. 1A is a schematic view of a wastewater biological treatment unit for explaining a preferred embodiment of the present invention; FIG. 1B is a schematic view for explaining another preferred embodiment of the present invention. Example of wastewater biological treatment unit; second diagram is a photo of actual appearance of wastewater biological treatment unit according to the present invention - embodiment; third diagram - flow chart ' to explain the preparation procedure of wastewater biological treatment unit of the present invention; BRIEF DESCRIPTION OF THE DRAWINGS FIG. 5 is a schematic view showing the configuration of a second embodiment of the wastewater treatment system of the present invention; and the fifth diagram is a schematic configuration of a second embodiment of the wastewater treatment system of the present invention; 19 201119955 Configuration::: The wastewater treatment system of the present invention The seventh embodiment of the third embodiment is a schematic diagram of the structure of the wastewater treatment tank; and the eighth diagram of the waste water treatment monomer tank cage wastewater according to a preferred embodiment of the present invention illustrates the present invention. The wastewater treatment system is the result of the actual treatment. '

【主要元件符號說明】[Main component symbol description]

10A、10B 12 14 142、144、146 145 148 22 24 31 〜36 400 > 500 ' 600 410 、 510 512 415 、 515 、 615 420 ' 520 廢水生物處理單元 生物擔體 支撐結構 環狀結構 網板 網孔 貫孔 凸柱 步驟 廢水處理系統 生物反應槽 匣體 廢水生物處理單元 薄膜反應槽 20 201119955 425 ' 525 ' 625 薄膜模組 430、530、630 進流泵 440、480、540、580、640 ' 680 貯槽 450、550、650 空壓機或鼓風機 610 反應槽體 410A、420A、510A、520A、610A 進流口10A, 10B 12 14 142, 144, 146 145 148 22 24 31 ~ 36 400 > 500 ' 600 410 , 510 512 415 , 515 , 615 420 ' 520 Wastewater biological treatment unit biological support support structure ring structure stencil Hole through hole step column wastewater treatment system biological reaction tank body water biological treatment unit film reaction tank 20 201119955 425 ' 525 ' 625 membrane module 430, 530, 630 inlet pump 440, 480, 540, 580, 640 '680 storage tank 450 , 550, 650 air compressor or blower 610 reaction tank 410A, 420A, 510A, 520A, 610A inlet

410B 、 520B 72 74 720 722 出流口 廢水處理模組 廢水處理單體 箱籠匣體 渗水孔410B, 520B 72 74 720 722 Outlet Wastewater Treatment Module Wastewater Treatment Unit Box Cage Body Water Infiltration Hole

21twenty one

Claims (1)

201119955 七、申晴專利範圍: 用於去除廢水中之有機物與氮 一種廢水生物處理單元 化合物,其包括: -生物擔體’其含有經調製之活性生物污泥以及萨 酸纖維;以及 曰 一支撐裝置,用於支撐及固定該生物擔體。 2.如申請專利範圍帛1項所述之廢水生物處理單元,其中 該支撐裝置係一籠狀結構,該籠狀結構係由位於不同平 面之至少三個環狀結構建構而成。 3_如申請專利範圍第2項所述之廢水生物處理單元,其中 該等環狀結構是由聚乙烯或聚丙烯材料製成。 4. 如申請專利範圍第2項所述之廢水生物處理單元,其中 該等環狀結構之内徑係介於5毫米與3 〇毫米之間。 5. 如申請專利範圍第2項所述之廢水生物處理單元,其中 該等環狀結構之内徑係25毫米。 6. 如申請專利範圍第丨項所述之廢水生物處理單元,其中 該支撐裝置係含有複數個網孔之一網板。 7. 如申請專利範圍第6項所述之廢水生物處理單元,其中 該網板是由聚乙烯或聚丙烯材料製成。 8·如申請專利範圍第6項所述之廢水生物處理單元,其中 該等網板與網孔之大小係依據廢水處理負荷與該生物 擔體之組成而設計。 9. 一種用於製作廢水生物處理單元之方法,所述廢水生物 [S] 22 201119955 處理單元係用於去除廢水中之有機物與氮化合物,該方 法包括下列步驟: 其重量百分濃度係 (a)製備一醋酸纖維丙酮溶液, 實質上為15% ; 维丙 "生 (b) 將疋量之活性污泥與一定量之該醋酸纖 酮溶液混合,以形成一生物擔體; (c) 將該生物擔體填入一支撐裝置中,以形201119955 VII. Shenqing Patent Range: A biological treatment unit compound for removing organic matter and nitrogen in wastewater, which comprises: - a biological carrier containing modified activated biological sludge and sodium oxalate fiber; A device for supporting and fixing the biological carrier. 2. The wastewater biological treatment unit of claim 1, wherein the support device is a cage structure constructed from at least three annular structures on different planes. The wastewater biological treatment unit of claim 2, wherein the annular structure is made of a polyethylene or polypropylene material. 4. The wastewater biological treatment unit of claim 2, wherein the annular structure has an inner diameter of between 5 mm and 3 mm. 5. The wastewater biological treatment unit of claim 2, wherein the annular structure has an inner diameter of 25 mm. 6. The wastewater biological treatment unit of claim 2, wherein the support device comprises a mesh of a plurality of meshes. 7. The wastewater biological treatment unit of claim 6, wherein the stencil is made of a polyethylene or polypropylene material. 8. The wastewater biological treatment unit of claim 6, wherein the size of the mesh and the mesh are designed according to a wastewater treatment load and a composition of the biological support. 9. A method for producing a wastewater biological treatment unit, the wastewater organism [S] 22 201119955 processing unit for removing organic matter and nitrogen compounds in wastewater, the method comprising the following steps: Preparing a solution of acetic acid fiber acetone, substantially 15%; vitamin C; raw (b) mixing the amount of activated sludge with a certain amount of the cellulose acetate solution to form a biological carrier; (c) Filling the biological carrier into a supporting device to shape 物處理單元; / (d)將該 燥;以及 生物處理單元浸入甲苯溶液中並 予以乾 (e)於 元 10·如申請專利範圍第9項所述 活性污泥之固體含量係實質 100公克。 之方法,其於步驟(b)中,該 上為12%,且其實質上係取/ (d) drying the biological treatment unit; and immersing the biological treatment unit in a toluene solution and drying it. (e) The content of the activated sludge is substantially 100 grams as described in claim 9. The method, in the step (b), the above is 12%, and the method is substantially 11. 如申請專利範圍第10項所述之方法, 該醋酸纖維丙鲷溶液實質上係取300毫升/ (bH 12. 如申請專利範圍第9項所述之方法,其 支樓裝置係由位於不同平面之至少三個^^ 13. 如申請專利範圍第9項所述之方法,並於 支撐裝置係含有複數個網孔之—網板;、/^(C)中,該 14. 如申請專利範圍第9項所述之方法,其於 將該生物處理單元浸入甲苯溶0 4 h中,係 23 201119955 乾燥時間實質上為3至4小時。 15.如申請專利範圍第9項所述之方法,其於步驟⑷中,該 生物處理單元係於排氣良好之空間中進行乾燥。 16·如申請專利範圍第9項所述之方法,其於步驟(e)中,係 以水清洗該生物處理單元實質上達6小時。 17. —種廢水處理設備,用於去除廢水中之有機物和氮化合 物,該廢水處理設備包括一生物反應槽,其特徵在於該 生物反應槽中填有至少一廢水生物處理單元,且該等廢 水生物處理單元各包括一生物擔體與用於支撐及固定 該生物擔體之一支撐裝置,該生物擔體含有經調製之活 性生物污泥以及醋酸纖維。 18. 如申明專利範圍第17項所述之廢水處理設備,其中該 支撐裝置係一籠狀結構,該籠狀結構係由位於不同平面 之至少三個環狀結構建構而成。 19. 如申請專利範圍第18項所述之廢水處理設備,其中該 等環狀結構是由聚乙烯或聚丙烯材料製成。 20. 如申凊專利範圍第18項所述之廢水處理設備,其中該 等環狀結構之内徑係介於5毫米與3〇毫米之間。 21·如申請專利範圍帛18項所述之廢水處理設備,其中該 等環狀結構之内徑係2 5毫米。 22.如申凊專利範圍帛17項所述之廢水處理設備’其中該 支撐裝置係含有複數個網孔之一網板。 23·如申請專利範圍帛22項所述之廢水處理設備,其中該 網板是由聚乙烯或聚丙烯材料製成。 24 201119955 24. 如申請專利範圍第22項所述之廢水處理設備,其中該 等網板與網孔之大小係依據廢水處理負荷與該生物擔 體之組成而設計。 25. —種廢水處理系統,其包括: 一生物反應槽’其填有至少一廢水生物處理單元, 所述廢水生物處理單元係各由一生物擔體與用於支樓 及固定該生物擔體之一支撐裝置所構成,其中該生物擔 體含有經調製之活性生物污泥以及醋酸纖維;以及 一薄膜反應槽’其含有至少一薄膜模組,該薄膜反 應槽之一進流口係與該生物反應槽之一出流口流體相 通。 26. 如申请專利範圍第25項所述之廢水處理系統,其中該 支撐裝置係一籠狀結構,該籠狀結構係由位於不同平面 之至少三個環狀結構建構而成。 27. 如申s青專利範圍第26項所述之廢水處理系統,其中該 等環狀結構是由聚乙烯或聚丙烯材料製成。 28. 如申请專利範圍第26項所述之廢水處理系統,其中該 等環狀結構之内徑係介於5毫米與3〇毫米之間。 29. 如申清專利範圍第26項所述之廢水處理系統,其中該 等環狀結構之内徑係25毫米。 30. 如申請專利範圍第26項所述之廢水處理系統,其中該 生物反應槽係一柱狀反應槽與一矩形反應槽其中之一。 31. 如申请專利範圍第30項所述之廢水處理系統,其中該 矩形反應槽内具有至少一箱籠匣體,所述箱籠匣體内填 25 201119955 有複數個所述廢水生物處理單元。 32. 如申請專利範圍第25項所述之廢水處理系統,其中該 支撑裝置係含有複數個網孔之—網板。 33. 如申請專利範圍第32項所述之廢水處理系統,其中該 網板疋由聚乙稀或聚丙烯材料製成。 34. 如申請專利範圍第32項所述之廢水處理系統,其中該 等網板與網孔之大小係依據廢水處理負荷與該线= 體之組成而設計。 ° 35. —種可同時除氮除碳及濾除懸浮顆粒之廢水處理 包括: S ~ 一反應槽體; 至少一廢水生物處理單元,其配置於該反應槽體内 並次置於該反應槽體内之廢水中,所述廢水生物處理單 兀係各由一生物擔體與用於支撐及固定該生物擔體之 支撑裝置所構成,其中該生物擔體含有經調製之活性 生物污泥以及醋酸纖維;以及 至少一薄膜模組’其係設置在該反應槽體中並與該 反應槽體内之廢水接觸,其中所述廢水生物處理單元係 以生物處理方式去除廢水中的有機物與氮化合物,且廢 水中所含之懸浮顆粒係藉由所述薄膜模組予以濾除。 36. 如申请專利範圍第35項所述之廢水處理槽,其中該支 樓裝置係一籠狀結構,該籠狀結構係由位於不同平面之 至少三個環狀結構建構而成。 37. 如申請專利範圍第36項所述之廢水處理槽,其中該等 [S] 26 201119955 環狀結構是由聚乙烯或聚丙烯材料製成。 38.如申請專利範圍第36項所述之廢水處理系統 統,其中該11. The method according to claim 10, wherein the cellulose acetate solution is substantially 300 ml/(bH 12. The method of claim 9 is provided in the method of claim 9 At least three of the different planes are as described in claim 9 and in the support device comprising a plurality of meshes, a mesh plate, and /^(C), the application is as follows. The method of claim 9, wherein the biological treatment unit is immersed in toluene for 0.4 h, and the drying time of the system 23 201119955 is substantially 3 to 4 hours. 15. As described in claim 9 The method, in the step (4), the biological treatment unit is dried in a space where the exhaust gas is good. The method of claim 9, wherein in the step (e), the water is washed with water. The biological treatment unit is substantially up to 6 hours. 17. A wastewater treatment device for removing organic matter and nitrogen compounds in wastewater, the wastewater treatment device comprising a biological reaction tank, characterized in that the biological reaction tank is filled with at least one wastewater Biological processing unit, Each of the wastewater biological treatment units includes a biological support and a support device for supporting and immobilizing the biological support, the biological support containing the prepared activated biological sludge and acetate fiber. The wastewater treatment apparatus of claim 17, wherein the support device is a cage structure constructed by at least three annular structures located in different planes. 19. As described in claim 18 The waste water treatment device, wherein the annular structure is made of a polyethylene or a polypropylene material. 20. The wastewater treatment device according to claim 18, wherein the inner diameter of the annular structure is Between 5 mm and 3 mm. 21. The wastewater treatment apparatus of claim 18, wherein the annular structure has an inner diameter of 25 mm. 22. If the application scope is 帛17 items The wastewater treatment device of the invention, wherein the support device comprises a stencil of a plurality of meshes. 23. The wastewater treatment device of claim 22, wherein the stencil is made of polyethylene or polypropylene. The invention relates to a waste water treatment device according to claim 22, wherein the size of the mesh plate and the mesh is designed according to the wastewater treatment load and the composition of the biological support. A wastewater treatment system comprising: a biological reaction tank filled with at least one wastewater biological treatment unit, each of the biological treatment units of the wastewater being supported by a biological support and for supporting the building and fixing one of the biological supports The device comprises: the biological carrier comprising the prepared active biological sludge and the cellulose acetate; and a film reaction tank comprising at least one membrane module, the inlet port of the membrane reaction tank and the biological reaction tank One of the outlets is in fluid communication. 26. The wastewater treatment system of claim 25, wherein the support device is a cage structure constructed from at least three annular structures located in different planes. 27. The wastewater treatment system of claim 26, wherein the annular structure is made of a polyethylene or polypropylene material. 28. The wastewater treatment system of claim 26, wherein the annular structure has an inner diameter of between 5 mm and 3 mm. 29. The wastewater treatment system of claim 26, wherein the annular structure has an inner diameter of 25 mm. 30. The wastewater treatment system of claim 26, wherein the biological reaction tank is one of a columnar reaction tank and a rectangular reaction tank. The wastewater treatment system of claim 30, wherein the rectangular reaction tank has at least one tank body, and the tank body is filled with a plurality of the wastewater biological treatment units. 32. The wastewater treatment system of claim 25, wherein the support device comprises a plurality of mesh-network plates. 33. The wastewater treatment system of claim 32, wherein the stencil is made of a polyethylene or polypropylene material. 34. The wastewater treatment system of claim 32, wherein the size of the mesh and the mesh are designed according to a wastewater treatment load and a composition of the wire. ° 35. A wastewater treatment capable of simultaneously removing nitrogen and removing carbon and filtering suspended particles comprises: S ~ a reaction tank; at least one wastewater biological treatment unit disposed in the reaction tank and placed in the reaction tank In the wastewater in the body, the wastewater biological treatment unit is composed of a biological carrier and a supporting device for supporting and fixing the biological carrier, wherein the biological carrier contains the prepared activated biological sludge and Acetate fiber; and at least one film module disposed in the reaction tank and in contact with wastewater in the reaction tank, wherein the wastewater biological treatment unit biologically removes organic matter and nitrogen compounds in the wastewater And the suspended particles contained in the wastewater are filtered by the thin film module. 36. The wastewater treatment tank of claim 35, wherein the building device is a cage structure constructed from at least three annular structures located in different planes. 37. The wastewater treatment tank of claim 36, wherein the [S] 26 201119955 annular structure is made of a polyethylene or polypropylene material. 38. The wastewater treatment system of claim 36, wherein 等環狀結構之内徑係25毫米。The inner diameter of the annular structure is 25 mm. 統,其中所 之廢水而以 流體化方式分散於該反應槽體中。 41.如申請專利範圍第36項所述之廢水處理系統,其中該 反應槽體内包括至少一箱籠g體,所述廢水生物處理單 元係填置於所述箱籠匣體中。 42·如申請專利範圍第41項所述之廢水處理系統,其中所 述至少一箱籠匣體與所述至少一薄膜模組係呈串聯配 置。 43.如申請專利範圍第35項所述之廢水處理系統,其中該 支撐裝置係含有複數個網孔之一網板。 4 4 如申凊專利範圍第4 3項所述之廢水處理系統,其中該 網板是由聚乙烯或聚丙烯材料製成。 45 _如申請專利範圍第43項所述之廢水處理系統,其中該 等網板與網孔之大小係依據廢水處理負荷與該生物擔 體之組成而設計。 46.如申請專利範圍第43項所述之廢水處理系統,其中所 述網板與所述至少一薄膜模組係呈串聯配置。 1 27The wastewater therein is dispersed in the reaction tank body in a fluidized manner. The wastewater treatment system of claim 36, wherein the reaction tank body comprises at least one tank g body, and the wastewater biological treatment unit is filled in the tank body. 42. The wastewater treatment system of claim 41, wherein the at least one cage body is in series with the at least one membrane module. 43. The wastewater treatment system of claim 35, wherein the support device comprises a mesh of a plurality of meshes. 4 4 The wastewater treatment system of claim 4, wherein the stencil is made of a polyethylene or polypropylene material. 45. The wastewater treatment system of claim 43, wherein the size of the mesh and the mesh are designed according to a wastewater treatment load and a composition of the biological support. 46. The wastewater treatment system of claim 43, wherein the screen is in series with the at least one membrane module. 1 27
TW98141328A 2009-12-03 2009-12-03 Entrapped mixed microbial cell with cellulose acetate, fabricating method therefor and wastewater treatment system of multi-function employing the same TW201119955A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110117073A (en) * 2019-06-19 2019-08-13 吴万益 The manufacturing method of rotating biological embedding contact sewage treatment equipment and reaction sphere

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110117073A (en) * 2019-06-19 2019-08-13 吴万益 The manufacturing method of rotating biological embedding contact sewage treatment equipment and reaction sphere

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