TWI642632B - Gynura decolorized metabolite, the composition and the use for decolorization of dye thereof - Google Patents

Gynura decolorized metabolite, the composition and the use for decolorization of dye thereof Download PDF

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TWI642632B
TWI642632B TW106111488A TW106111488A TWI642632B TW I642632 B TWI642632 B TW I642632B TW 106111488 A TW106111488 A TW 106111488A TW 106111488 A TW106111488 A TW 106111488A TW I642632 B TWI642632 B TW I642632B
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dye
decolorization
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metabolite
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TW201836989A (en
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陳博彥
薛仲娟
許安瑋
廖家輝
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國立宜蘭大學
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Abstract

本發明提供一種紅鳳菜液脫色代謝物、其組合物及其染料脫色之應用,該紅鳳菜液脫色代謝物預先以希瓦氏菌(Shewanella sp.)脫色處理,該組合物包括紅鳳菜液脫色代謝物;該組合物可產生電子梭以及有效促進氧化還原反應,有效地使染料脫色降解。本發明之組合物不包括非自然之化學物質,對於環境友善。 The invention provides a decolorizing metabolite of Hongfengcai liquid, a composition thereof and a dye decolorizing application thereof, wherein the decolorizing metabolite of the red cabbage liquid is preliminarily decolorized by Shewanella sp., and the composition comprises red phoenix. The vegetable liquid decolorizes the metabolite; the composition can generate a electron shuttle and effectively promote the redox reaction, effectively decolorizing and degrading the dye. The compositions of the present invention do not include unnatural chemicals and are environmentally friendly.

Description

一種紅鳳菜液脫色代謝物、其組合物及其染料脫色之應用 Decolorization metabolite of red phoenix liquid, its composition and application of dye decolorization

本發明提供一種紅鳳菜液脫色代謝物、其組合物及其染料脫色之應用,該組合物係包含紅鳳菜液脫色代謝物。 The invention provides a decolorizing metabolite of Hongfengcao liquid, a composition thereof and a dye decolorizing application thereof, the composition comprising a decolorizing metabolite of Hongfengcao liquid.

有色染料製程所排放之廢水中含有10-15%之染料,其中具有大量有機或無機化合物,對環境造成嚴重危害。為使廢水排放符合法規要求,業者多使用漂水添加、氧化還原、活性碳吸附、或電解等方法以達成脫色效果,但經脫色劑、混凝劑或其二者混和後與廢水共同作用,會產生凝聚物質行程汙泥淤積造成二次汙染。 The waste water discharged from the process of colored dyes contains 10-15% of dyes, which have a large amount of organic or inorganic compounds, which cause serious harm to the environment. In order to make the wastewater discharge comply with the regulatory requirements, the industry uses bleaching water addition, redox, activated carbon adsorption, or electrolysis to achieve the decolorization effect, but after the decoloring agent, coagulant or both, it cooperates with the wastewater. Will produce agglomerated material stroke sludge deposition caused by secondary pollution.

染料分子大多為具有芳香族結構之化合物,其發色基團多為偶氮基團(-N=N-),結構穩定,係以共價鍵結的方式,將染料固定於紡織纖維上。部分偶氮染料或其衍生分解物具有毒性及潛在致癌風險。因此染料廢水處理係不容忽視之公共衛生和環境保護要點。 Most of the dye molecules are compounds having an aromatic structure, and the chromophoric groups are mostly azo groups (-N=N-), and the structure is stable, and the dyes are fixed on the textile fibers by covalent bonding. Some azo dyes or their degraded products have toxicity and potential cancer risk. Therefore, dye wastewater treatment is a public health and environmental protection point that cannot be ignored.

先前研究發現化學合成之染料及脫色代謝物可作為電子梭(ES),具有促進電子轉移作用,可於廢水處理時促進生物脫色及產電之能量回收再利用(Chen et al.2013 Int J Hydrogen Energ)。然而在廢水處理上,額外添加非天然之化學合成物質,如孔雀石綠、鄰及對胺基酚(2- aminophenol,2AP及4-aminophenol,4AP)、1-胺基-2萘酚(1A2N)、4-胺基萘酚(4A1N),雖然具有功效,但也會造成二次汙染,不符合永續發展及環保應用法規要求,因此有必要尋找與環境生態相容且具有善性之ES應用,以利用生物刺激策略以進行廢水脫色處理。 Previous studies have found that chemically synthesized dyes and decolorized metabolites can be used as electron shuttles (ES) to promote electron transfer and promote bio-decolorization and energy recovery in wastewater treatment (Chen et al. 2013 Int J Hydrogen) Energ). However, in the wastewater treatment, additional non-natural chemical synthetic substances such as malachite green, o- and p-aminophenol (2- Aminophenol, 2AP and 4-aminophenol, 4AP), 1-amino-2 naphthol (1A2N), 4-aminonaphthol (4A1N), although effective, can cause secondary pollution and is not consistent with sustainable development. As well as environmental protection application regulations, it is necessary to find ES applications that are ecologically compatible and good-natured to utilize bio-stimulation strategies for wastewater decolorization.

本研究的目的係在環境生態友善及相容之前提下,由自然生態中尋找生物合成或是分解轉換所得天然物ES之技術,來進行廢水脫色處理以取代會造成環境二次汙染之化學合成物質。 The purpose of this study is to extract the natural product ES from the natural ecology and to decompose and convert the natural ES produced by the natural environment to replace the chemical synthesis that will cause secondary pollution. substance.

紅鳳菜過去在專利上的應用為萃取液製備或使用其汁液為保健食品之應用,台灣專利(證書號M499072)揭露一種促進甘胺酸亞鐵吸收之含紅鳳菜蔬果粉之食品結構,利用紅鳳菜作為蔬果粉添加物以促進甘胺酸亞鐵吸收;台灣專利(公開號201515655)揭露紅鳳菜極性萃取物及其製備方法與用途,其中紅鳳菜極性萃取物可以增加植物中鐵質汁有效吸收,減少貧血發生率;但目前沒有研究或公開資訊揭露關於紅鳳菜液進行生物轉化做其他環保應用汁技術。 The application of Hongfengcai in the past is the application of the extract preparation or the use of its juice as a health food. The Taiwan patent (certificate No. M499072) discloses a food structure containing red phoenix vegetable and fruit powder which promotes the absorption of ferrous ferrous sulphate. Hongfengcai is used as a vegetable and fruit powder additive to promote the absorption of ferrous ferrous sulphate; Taiwan Patent (Publication No. 201515655) discloses a polar extract of Hongfengcai and its preparation method and use, wherein the polar extract of red phoenix can increase iron in plants The effective absorption of the juice reduces the incidence of anemia; however, there is currently no research or public information to disclose the biotransformation of Hongfengcai liquid for other environmentally friendly application techniques.

本發明之目的係提供一種紅鳳菜液脫色代謝物、其組合物及其染料脫色之應用,達成染料脫色、降解並清除廢水汙染之目的。 The object of the present invention is to provide a decolorizing metabolite of Hongfengcai liquid, a composition thereof and a dye decolorizing application thereof, thereby achieving the purpose of decolorizing, degrading and eliminating waste water pollution.

為達上述之發明目的,本發明提供一種紅鳳菜液脫色代謝物之製備方法,包括:混和希瓦氏菌(Shewanella sp.)及紅鳳菜汁液後進行脫色代謝。 In order to achieve the above object, the present invention provides a method for preparing a decolorizing metabolite of Hongfengcai liquid, which comprises: performing decolorization metabolism after mixing Shewanella sp. and red phoenix juice.

其中,該製備方法進一步包括:混合紅鳳菜液和希瓦氏菌(Shewanella sp.)之菌液後,待其脫色率達90%。 Wherein, the preparation method further comprises: mixing the red phoenix liquid and the bacterium of Shewanella sp., and the decolorization rate thereof is 90%.

其中,該紅鳳菜液之添加體積比例係為該紅鳳菜液脫色代謝物之1%-10%。 Wherein, the added volume ratio of the red phoenix liquid is 1%-10% of the decolorized metabolite of the red phoenix liquid.

其中,該紅鳳菜液之製備方法包括:紅鳳菜加水研磨後離心取出上清液,其中該紅鳳菜與該水之重量比例為10~20%:80~90%;該上清液以濾紙抽氣過濾,取得過濾液;以及該過濾液以孔洞大小0.24μm之濾膜取得該紅鳳菜液。 Wherein, the preparation method of the red phoenix liquid comprises: removing the supernatant from the red phoenix vegetable and water, and extracting the supernatant liquid, wherein the weight ratio of the red phoenix to the water is 10-20%: 80-90%; the supernatant The filtrate was filtered with a filter paper to obtain a filtrate; and the filtrate was obtained by a filter having a pore size of 0.24 μm.

本發明另提供一種用於染料脫色之組合物,其中包括前述之紅鳳菜液脫色代謝物。 The present invention further provides a composition for decolorizing a dye, which comprises the aforementioned decolorizing metabolite of Hongfengcao liquid.

其中,該組合物進一步包括用於增加電子梭之脫色代謝中間物,該脫色代謝中間物係選自孔雀石綠、鄰胺基酚(2AP)、對胺基酚(4AP)、1-胺基2-萘酚(1A2N)、4胺基萘酚(4A1N)所構成之群組。。 Wherein, the composition further comprises a decolorizing metabolic intermediate for increasing the electron shuttle, the decolorizing metabolic intermediate selected from the group consisting of malachite green, o-aminophenol (2AP), p-aminophenol (4AP), 1-amino group. A group consisting of 2-naphthol (1A2N) and 4-aminonaphthol (4A1N). .

本發明另提供一種染料脫色之方法,包括於染料中加入前述之用於染料脫色之組合物。 The invention further provides a method of decolorizing a dye comprising adding to the dye a composition for dye decolorization as described above.

其中,該方法係用於染料廢水之脫色。 Among them, the method is used for decolorization of dye wastewater.

其中,該方法係用於降解偶氮染料。 Among them, the method is for degrading an azo dye.

其中,該方法可用於生物燃料電池,該生物燃料電池可降解染料並產生電子梭。 Among other things, the method can be applied to a biofuel cell that degrades the dye and produces an electron shuttle.

圖1 微生物於紅鳳菜液進行脫色反應之實驗流程;圖2 不同菌株於紅鳳菜水萃取液,進行脫色前與脫色後的循環伏安測 定圖譜;圖3 不同劑量紅鳳菜液經微生物菌株(WLP72)脫色所產生的,進行脫色前與脫色後的循環伏安測定圖譜;圖4 添加脫色後紅鳳菜代謝物(DM)於不同菌株(WLP72、YTL1)對反應性黑色染料五號(RBk5)之脫色及菌體生長之影響。 Fig.1 Experimental procedure of decolorization reaction of microorganisms in Hongfengcai liquid; Fig.2 Cyclic voltammetry of different strains in Hongfengcao water extract before decolorization and after decolorization Figure 3: The cyclic voltammetry of pre-decolorization and decolorization was carried out by different doses of red cabbage solution by decolorization of microbial strain (WLP72); Figure 4: Decolorization of red phoenix metabolites (DM) after discoloration The effect of strain (WLP72, YTL1) on the decolorization and cell growth of reactive black dye No. 5 (RBk5).

圖5 希瓦氏菌(Shewanella sp.)不同菌株於紅鳳菜液,進行脫色前與脫色後的循環伏安測定圖譜分析,使用市面可取得之菌株BCRC 80907培養菌液和紅鳳菜液之組合物,測定其循環伏安圖譜,亦可產生氧化還原反應。 Fig. 5 Cyclic voltammetry analysis of different strains of Shewanella sp. in Hongfengcai liquid before decolorization and after decolorization, using commercially available strain BCRC 80907 culture liquid and red phoenix liquid The composition, which measures the cyclic voltammogram, can also produce a redox reaction.

本說明書中所述之所有技術性及科學術語,除非另外有所定義,皆為該所屬領域具有通常技藝者可共同瞭解的意義。本發明係以下面的實施例予以示範闡明,但僅為例示而非限制,本發明不受下述實施例所限制。除非另有說明,本發明所用之材料皆市售易於取得,下列僅為示例可取得之管道。 All of the technical and scientific terms described in this specification, unless otherwise defined, are intended to be common to those of ordinary skill in the art. The present invention is exemplified by the following examples, which are intended to be illustrative and not restrictive. Unless otherwise indicated, the materials used in the present invention are readily available commercially, and the following are merely examples of available pipelines.

本發明所使用之紅鳳菜萃取液之製備方法,包括將紅鳳菜加水研磨成泥狀;以11,000rpm、23℃高速離心20分鐘;取出上清液並抽氣過濾(5A濾紙(ADVANTEC),孔洞大小0.06毫米)取得過濾液;以孔洞大小0.24微米(μm)之濾膜過濾該過濾液,取得可用於產生電子梭之紅鳳菜萃取液。 The preparation method of the red phoenix extract used in the invention comprises the steps of: grinding the red phoenix with water into a mud; centrifuging at 11,000 rpm and 23 ° C for 20 minutes; taking the supernatant and pumping the air (5A filter paper (ADVANTEC)) The pore size was 0.06 mm. The filtrate was obtained; the filtrate was filtered through a filter having a pore size of 0.24 μm, and a red cabbage extract which can be used for the production of an electron shuttle was obtained.

循環伏安法(cyclic voltammetry,CV)是改變電位以得到氧化還原電流方向之測定,主要是以施加一循環電位的方式來進行,從一起始 化還原電流方向之測定,主要是以施加一循環電位的方式來進行,從一起始電位以固定速率施加到一終點電位,再以相同速率改變回相同起始電位,此為一個循環,但該測定方法可多次循環以達到明確之結果,並繪製一可逆氧化反應物分析所得的電位-電流圖譜。當從低電位往高電位掃瞄時,會使分析物產生氧化電流的氧化峰(anodic peak),可判斷在何種電位時會發生氧化反應。若脫色代謝物液體具有顯著氧化還原峰,即具有可促進染料脫色之特性。 Cyclic voltammetry (CV) is a measure of changing the potential to obtain the direction of the redox current, mainly by applying a cyclic potential, starting from a The measurement of the direction of the reduction current is mainly performed by applying a cyclic potential, applying a potential from a starting potential to an end point potential, and then changing back to the same starting potential at the same rate, which is a cycle, but The method of measurement can be cycled multiple times to achieve a definitive result, and a potential-current map obtained by analysis of a reversible oxidation reaction is plotted. When scanning from a low potential to a high potential, the analyte will generate an anodic peak of the oxidation current, and it can be determined at which potential an oxidation reaction occurs. If the decolorized metabolite liquid has a significant redox peak, it has the property of promoting dye discoloration.

實施例1、WLP72(Shewanella haliotis)具有促進脫色之特性 Example 1. WLP72 ( Shewanella haliotis ) has the property of promoting discoloration

4菌株WLP72(Shewanella haliotis)、K2(Exiguobacterium acetylicum)、YTL1(Aeromonas hydrophila)、KB23(Aeromonas hydrophila)培養於LB培養基,添加1-10%培養基體積之紅鳳菜水萃取液(20g/100ml)進行降解、脫色;待脫色率達90%之後,取已脫色之菌液進行離心(11,000rpm,15分鐘,25℃)分離細菌,並取出上層澄清脫色代謝物液體以進行循環伏安測定,如圖1所示,該循環伏安測定係於掃瞄範圍0.4伏特(V)至-0.6V,掃描速率為每秒10毫伏特(mV‧s-1),掃描圈數為3,比較脫色前、脫色後之循環伏安圖譜,圖2結果顯示,菌株WLP72(圖2A)脫色後有明顯的氧化還原峰,代表脫色代謝物確實可產生促進電子轉移的中間產物,菌株K2((圖2B)、YTL1(圖2C)、KB23(圖2D)脫色後不具有明顯的氧化還原峰,代表相同的天然植物萃取液、同樣的脫色條件下,由於脫色菌株之代謝生理活性不同,其脫色產物不同,因此有不同之促進電子轉移的效果,此4菌株中,只有菌株WLP72可以有效脫色,且循環伏安圖譜具有顯著的氧化還原峰,表示其具有促進染料脫色之特性。上述菌株培養液添加 5%紅鳳菜水萃取液所得之脫色效果最佳。 4 strains WLP72 ( Shewanella haliotis ), K2 ( Exiguobacterium acetylicum ), YTL1 ( Aeromonas hydrophila ), KB23 ( Aeromonas hydrophila ) were cultured in LB medium, and 1-2% medium volume of Hongfengcao water extract (20g/100ml) was added. Degradation and decolorization; after the decolorization rate reaches 90%, the decolorized bacteria solution is centrifuged (11,000 rpm, 15 minutes, 25 ° C) to separate the bacteria, and the upper layer of clear decolorizing metabolite liquid is taken for cyclic voltammetry. As shown in Fig. 1, the cyclic voltammetry is in the scanning range of 0.4 volts (V) to -0.6 V, the scanning rate is 10 millivolts per second (mV ‧ s -1 ), and the number of scanning circles is 3, before the decolorization, The cyclic voltammetry spectrum after decolorization, the results in Figure 2 show that the strain WLP72 (Fig. 2A) has obvious redox peak after decolorization, indicating that the decolorized metabolite can indeed produce an intermediate product that promotes electron transfer, strain K2 (Fig. 2B). YTL1 (Fig. 2C) and KB23 (Fig. 2D) do not have obvious redox peaks after decolorization, which means that the same natural plant extracts and the same decolorization conditions have different decolorization products due to their different metabolic physiological activities. Do you have In promoting the effect of electron transfer, only the strain WLP72 can effectively decolorize, and the cyclic voltammogram has a significant redox peak, indicating that it has the property of promoting dye discoloration. The water extract obtained the best decolorization effect.

實施例2、不同劑量紅鳳菜液培養對WLP72促進染料脫色能力之影響 Example 2, the effect of different doses of Hongfengcao culture on the decolorization ability of WLP72 to promote dye

菌株WLP72(Shewanella haliotis)培養於LB培養基,添加1-10%培養基體積之紅鳳菜水萃取液(高濃度:20g/100ml、低濃度:20g/200ml)進行降解、脫色;待脫色率達90%之後,取已脫色之菌液進行離心(11,000rpm,15分鐘,25℃)分離細菌,並取出上層澄清脫色代謝物液體以進行循環伏安測定,該循環伏安測定係於掃瞄範圍0.4伏特(V)至-0.6V,掃描速率為每秒10毫伏特(mV‧s-1),掃描圈數為3,比較脫色前、脫色後之循環伏安圖譜,圖3結果顯示,高濃度紅鳳菜水萃取液培養之WLP72代謝液體脫色後的氧化還原峰最明顯,表示菌株WLP72促進染料脫色之效果,隨著培養液中紅鳳菜水萃取液之濃度增加而上升。上述菌株培養液添加5%紅鳳菜水萃取液所得之脫色效果最佳。 The strain WLP72 ( Shewanella haliotis ) was cultured in LB medium, and added with 1-10% medium volume of Hongfengcao water extract (high concentration: 20g/100ml, low concentration: 20g/200ml) for degradation and decolorization; After %, the decolorized bacterial liquid was centrifuged (11,000 rpm, 15 minutes, 25 ° C) to separate the bacteria, and the upper clear decolorizing metabolite liquid was taken for cyclic voltammetry, which was in the scanning range of 0.4. Volt (V) to -0.6V, scanning rate is 10 millivolts per second (mV‧s -1 ), scanning circle number is 3, compare the cyclic voltammogram before decolorization, after decolorization, Figure 3 results show that high concentration The redox peak after decolorization of WLP72 metabolic liquid cultured in Hongfengcai water extract was the most obvious, indicating that the effect of strain WLP72 on dye decolorization increased with the increase of the concentration of Hongfengcao water extract in the culture solution. The decolorization effect obtained by adding 5% Hongfengcao water extract to the above culture solution is the best.

實施例3、紅鳳菜脫色代謝物(decolorized metabolites;DM)對菌株脫色能力之影響 Example 3, the effect of decolorized metabolites (DM) on the decolorization ability of strains

為進一步測試紅鳳菜脫色代謝物(decolorized metabolites;DM)對不同菌株促進脫色之影響,本實施例取前述菌株WLP72、YT11,並添加染料反應性黑色染料RBk5進行脫色評估,驗證菌株在含有與不含有紅鳳菜液對脫色代謝之影響。 In order to further test the effect of decolorized metabolites (DM) on the decolorization of different strains, in this example, the above strains WLP72 and YT11 were taken, and the dye-reactive black dye RBk5 was added for decolorization evaluation to verify that the strain contained Does not contain the effect of red cabbage liquid on decolorization metabolism.

培養細菌並加入染料後,於固定時間以分光光度計測量菌體吸收度(波長600nm)與染料吸收度(RBk5最大吸收波長600nm),濃度之測量可以下列方式進行估算決定: 假設未經離心之原含菌液樣品之量測值為OD500nm X-Dye =OD500nm Dye +OD500nm X …(1) After culturing the bacteria and adding the dye, the cell absorbance (wavelength 600 nm) and the dye absorbance (RBk5 maximum absorption wavelength 600 nm) were measured by a spectrophotometer at a fixed time. The concentration measurement can be estimated in the following manner: The measured value of the original bacteria-containing liquid sample is OD 500 nm X-Dye = OD 500 nm Dye + OD 500 nm X ...(1)

經離心後取上層液(假設只含染料)所測得值為OD500nm sup=OD500nm Dye …(2) After centrifugation, the upper layer (assuming only the dye) is measured as OD 500 nm sup = OD 500 nm Dye ... (2)

經離心後取上層液(假設只含染料)所測得值為OD λmax sup=OD λmax Dye …(3) After centrifugation, the upper layer liquid (assuming only the dye) is measured as OD λ max sup = OD λ max Dye ... (3)

將此三式聯立即可決定出染料吸收度(ODλmax Dye)及菌體吸收度OD600nm X,再取定適當稀釋倍數使染料吸收度位於線性範圍內(OD值約<1.0),經濃度校正曲線分別計算出實際濃度。 The triad can immediately determine the dye absorbance (OD λmax Dye ) and the cell absorbance OD 600nm X , and then take appropriate dilution factor to make the dye absorbance in the linear range (OD value about <1.0), the concentration The calibration curve calculates the actual concentration separately.

以每單位菌體濃度計算生長速率和脫色速率,其計算方法如下:生長速率d ln X/dt(1/X)(△(X)/△t) The growth rate and decolorization rate were calculated per unit cell concentration as follows: growth rate d ln X/dt (1/X)(△(X)/△t)

脫色速率SDR=-(1/X)(d[dye]/dt) Decolorization rate SDR=-(1/X)(d[dye]/dt)

X:菌體濃度(ODU) X0:起始菌體濃度(ODU) X: cell concentration (ODU) X 0 : initial cell concentration (ODU)

t:時間(h) t: time (h)

[dye]:染料濃度(mgL-1) [dye]: dye concentration (mgL -1 )

隨著添加紅鳳菜脫色代謝物(decolorized metabolites;DM),可以發現菌株對RBk5之脫色速率(SDR),由快而慢依序為:WLP72-DM(13.85)>WLP72(11.47)>YT11-DM(9.00)>YT11(5.13),可以發現加入紅鳳菜的脫色代謝物(DM)可增加菌株脫色效果,WLP72-DM的脫色速率較WLP72增加20.69%,YT11-DM的脫色速率較YT11增加75.29%,如圖4所示,而脫色雨與電子轉移有關,進一步推知紅鳳菜脫色代謝物有提高電子 轉移能力,可加速還原脫色,有效提升脫色效果。。 With the addition of decolorized metabolites (DM), the decolorization rate (SDR) of RBk5 by strains was found to be fast and slow: WLP72-DM (13.85)>WLP72 (11.47)>YT11- DM(9.00)>YT11(5.13), it can be found that the decolorization metabolite (DM) added to the red phoenix can increase the decolorization effect of the strain. The decolorization rate of WLP72-DM is 20.69% higher than that of WLP72, and the decolorization rate of YT11-DM is higher than that of YT11. 75.29%, as shown in Figure 4, and the decolorization rain is related to electron transfer, further inferring that the decolorized metabolites of Hongfengcai have improved electrons. The transfer ability can accelerate the reduction and decolorization, effectively improving the decolorization effect. .

實施例4 希瓦氏菌(shewanella sp.)具有脫色效果 Example 4 Shewanella sp. has a decolorizing effect

依據前述實施例,WLP72(Shewanella haliotis)具有產生電子梭之能力、可有效脫色之微生物。新竹食品工業發展研究所編號BCRC 80907(Shewanella algae)與WLP72為相同菌屬。本實施例測試WLP72與BCRC 80907是否具有相同功效。 According to the foregoing embodiment, WLP72 ( Shewanella haliotis ) has microorganisms capable of efficiently decolorizing the ability to generate an electron shuttle. Hsinchu Food Industry Development Research Institute No. BCRC 80907 ( Shewanella algae ) is the same genus as WLP72. This example tests whether WLP72 has the same efficacy as BCRC 80907.

菌株WLP72(Shewanella haliotis)、BCRC 80907(Shewanella algae)培養於LB培養基,添加1-10%培養基體積之紅鳳菜水萃取液(20g/100ml)進行降解、脫色;待脫色率達90%之後,取已脫色之菌液進行離心(11,000rpm,15分鐘,25℃)分離細菌,並取出上層澄清脫色代謝物液體以進行循環伏安測定,該循環伏安測定係於掃瞄範圍0.4伏特(V)至-0.6V,掃描速率為每秒10毫伏特(mV‧s-1),掃描圈數為3,比較脫色前、脫色後之循環伏安圖譜,圖5結果顯示,菌株WLP72與BCRC 80907都有明顯的氧化還原峰,代表脫色代謝物確實可產生促進電子轉移的中間產物,表示其具有促進染料脫色之特性。上述菌株培養液添加5%紅鳳菜水萃取液所得之脫色效果最佳。 The strains WLP72 ( Shewanella haliotis ) and BCRC 80907 ( Shewanella algae ) were cultured in LB medium, and the extract of Hongfengcao water (20g/100ml) was added with 1-10% medium volume for degradation and decolorization; after the decolorization rate reached 90%, The decolorized bacterial solution was centrifuged (11,000 rpm, 15 minutes, 25 ° C) to separate the bacteria, and the upper clear decolorizing metabolite liquid was taken for cyclic voltammetry, which was 0.4 volts in the scanning range (V). ) to -0.6V, the scanning rate is 10 millivolts per second (mV‧s -1 ), the number of scanning circles is 3, compared with the cyclic voltammogram before decolorization and after decolorization, the results of Figure 5 show that the strains WLP72 and BCRC 80907 There are obvious redox peaks, which represent that the decolorized metabolite can indeed produce an intermediate product that promotes electron transfer, indicating that it has the property of promoting dye discoloration. The decolorization effect obtained by adding 5% Hongfengcao water extract to the above culture solution is the best.

由前述結果可以推得,由申請人自行分離的WLP72(參考宜蘭大學化材系岳沛林碩士論文,105年6月)與購得之BCRC 80907與紅鳳菜液混合後都具有產生電子梭之能力,可以有效脫色,可以得知,與紅鳳菜液共培養後、令紅鳳菜液產生電子梭之效果係希瓦氏菌(shewanella sp.)所固有之能力,本發明之生物材料屬本發明技術領域具有通常知識者可依據本說明書而獲得與實施。意即該脫色代謝物施加電位差後可產生電子梭以 及氧化還原反應,並且可用於降解染劑達成脫色之功效。 It can be inferred from the above results that the WLP72 separated by the applicant (refer to the Yilan University Chemicals Department Yue Peilin master's thesis, June, 105) and the purchased BCRC 80907 and Hongfengcai liquid have the ability to produce electronic shuttle. It can be effectively decolored, and it can be known that the effect of co-cultivation with red phoenix liquid and the production of a electronic shuttle by the red phoenix liquid is the inherent ability of Shewanella sp. , and the biological material of the present invention belongs to the present invention. Those skilled in the art can obtain and implement the present invention in light of the present specification. That is to say, the potential difference of the decolorizing metabolite can generate a electron shuttle and a redox reaction, and can be used for degrading the dye to achieve the effect of decolorization.

上列詳細說明係針對本發明之一可行實施例之具體說明,惟該實施例並非用以限制本發明之專利範圍,凡未脫離本發明技藝精神所為之等效實施或變更,均應包含於本案之專利範圍中。 The detailed description of the preferred embodiments of the present invention is intended to be limited to the scope of the invention, and is not intended to limit the scope of the invention. The patent scope of this case.

Claims (10)

一種紅鳳菜液脫色代謝物之製備方法,包括:混和希瓦氏菌(Shewanella sp.)培養液及紅鳳菜液後進行脫色代謝。 The invention relates to a method for preparing a decolorizing metabolite of red phoenix liquid, which comprises: decolorizing metabolism after mixing Shewanella sp. culture solution and red phoenix liquid. 如申請專利範圍第1項所述之製備方法,該製備方法進一步包括:混和希瓦氏菌(Shewanella sp.)培養液及紅鳳菜液後,待其脫色率達90%。 The preparation method according to claim 1, wherein the preparation method further comprises: after mixing the Shewanella sp. culture solution and the red phoenix solution, the decolorization rate is 90%. 如申請專利範圍第1項所述之製備方法,該紅鳳菜液之添加體積比例係為該希瓦氏菌培養液之1%-10%。 The preparation method according to the first aspect of the patent application, wherein the ratio of the added volume of the red phoenix liquid is 1% to 10% of the culture medium of the Shewanella. 如申請專利範圍第1項所述之製備方法,該紅鳳菜液之製備方法包括:紅鳳菜研磨後離心取出上清液,其中該紅鳳菜與該水之重量比例為10~20%:80~90%;該上清液以濾紙抽氣過濾,取得過濾液;以及該過濾液以孔洞大小0.24微米(μm)之濾膜取得該紅鳳菜液。 According to the preparation method of the first aspect of the patent application, the preparation method of the red phoenix liquid comprises: removing the supernatant after centrifugation of the red phoenix, wherein the weight ratio of the red phoenix to the water is 10-20%. : 80~90%; the supernatant is filtered by a filter paper to obtain a filtrate; and the filtrate is obtained by a filter having a pore size of 0.24 micrometers (μm). 一種用於染料脫色之組合物,包括申請專利範圍第1項所述之紅鳳菜液脫色代謝物。 A composition for decolorizing a dye, comprising the decolorizing metabolite of Hongfengcao liquid according to claim 1 of the patent application. 如申請專利範圍第5項所述之組合物,該組合物進一步包括用於增加電子梭之脫色代謝中間物,該脫色代謝中間物係選自孔雀石綠、鄰胺基酚(2AP)、對胺基酚(4AP)、1-胺基2-萘酚(1A2N)、4胺基萘酚(4A1N)所構成之群組。 The composition of claim 5, further comprising a decolorizing metabolic intermediate for increasing the electron shuttle, the decolorizing metabolic intermediate selected from the group consisting of malachite green, o-aminophenol (2AP), A group consisting of aminophenol (4AP), 1-amino 2-naphthol (1A2N), and 4-aminonaphthol (4A1N). 一種染料脫色之方法,包括於染料中加入申請專利範圍第5項所述之用於染料脫色之組合物。 A method for decolorizing a dye, comprising adding a composition for dye decolorization as described in claim 5 of the patent to a dye. 如申請專利範圍第7項所述之方法,該方法係用於染料廢水之脫色。 The method of claim 7 is for the decolorization of dye wastewater. 如申請專利範圍第7項所述之方法,該方法係用於降解偶氮染料。 The method of claim 7, wherein the method is for degrading an azo dye. 如申請專利範圍第7項所述之方法,該方法可用於生物燃料電池,該生物燃料電池可降解染料並產生電子梭。 The method of claim 7, wherein the method is applicable to a biofuel cell that degrades the dye and produces an electron shuttle.
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