TWI769639B - Multifunctional adsorption complex, manufacturing method an use thereof - Google Patents

Multifunctional adsorption complex, manufacturing method an use thereof Download PDF

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TWI769639B
TWI769639B TW109146263A TW109146263A TWI769639B TW I769639 B TWI769639 B TW I769639B TW 109146263 A TW109146263 A TW 109146263A TW 109146263 A TW109146263 A TW 109146263A TW I769639 B TWI769639 B TW I769639B
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tannin
complex
ferric
solution
adsorption
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TW202225182A (en
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蔡佩珍
蔡睿宸
詠斯 陳
葉芳好
悅敏 陳
陳俊佑
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國立成功大學
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Abstract

This invention relates to a multifunctional adsorption complex, a manufacturing method and a use thereof. The multifunctional adsorption complex comprises a tannin trivalent iron complex which is manufactured by reaction of a tannic acid material and an iron salt material. The multifunctional adsorption complex can adsorb multiple biological and chemical substances.

Description

多功能吸附錯合物及其製備方法與用途Multifunctional adsorption complex and its preparation method and use

本發明關於一種多功能吸附錯合物及其製備方法與用途,能有效吸附並移除多種生物性物質以及化學性物質。The present invention relates to a multifunctional adsorption complex and its preparation method and application, which can effectively adsorb and remove various biological substances and chemical substances.

目前的水資源中常常會有多種物質汙染,該些汙染物質包含各種的化學性物質或是生物性物質,且這些物質對生物體具有危害,因此目前水資源在使用以及飲用之前,一定要經過適當處理,以將其中的有害物質移除。目前移除水中有害物質的方法包含逆滲透法、曝氣法、消毒法等等,但是該些方法在實施上仍較不便利。近年來也研發出以吸附性材料吸附水中的有害物質並移除,例如中華民國專利第TW 202042884(A)號公開案提供了一種可去除重金屬的吸附材料,係包含鋁矽酸鹽化合物的微粒子化合物與活性碳粒子,其具有吸附鉛離子並避免鋁溶析的功效。又中華民國專利第TW 201934215(A)號公開案也提供一種用於汙染水處理的吸附體,吸附體使用微粒子狀的黏土礦物製成,且黏土礦物可設為水鋁英石或絲狀鋁英石,汙染水處理體。At present, water resources are often polluted by a variety of substances. These pollutants include various chemical substances or biological substances, and these substances are harmful to living organisms. Properly dispose of to remove harmful substances. The current methods for removing harmful substances in water include reverse osmosis, aeration, disinfection, etc., but these methods are still relatively inconvenient in implementation. In recent years, adsorbent materials have also been developed to adsorb and remove harmful substances in water. For example, the Republic of China Patent Publication No. TW 202042884(A) provides an adsorbent material that can remove heavy metals, which is a microparticle containing aluminosilicate compounds. Compound and activated carbon particles, which have the effect of adsorbing lead ions and preventing aluminum from leaching out. The ROC Patent Publication No. TW 201934215(A) also provides an adsorbent for the treatment of polluted water. The adsorbent is made of particulate clay minerals, and the clay minerals can be set to allophane or filamentous aluminum. Stone, polluted water treatment body.

然,現有的吸附材料多是針對單一特性物質而設計,因此若想要移除汙染水中不同物質時,便需要使用多種吸附材料,使用上較耗費時間。However, most of the existing adsorption materials are designed for a single characteristic substance. Therefore, if you want to remove different substances in the polluted water, you need to use a variety of adsorption materials, which is time-consuming.

今,發明人有鑑於現有吸附材料於實際使用時仍有可改進之處,於是乃一本孜孜不倦之精神,並藉由其豐富專業知識及多年之實務經驗所輔佐,而加以改善,並據此研創出本發明。Today, in view of the fact that the existing adsorbent materials still have room for improvement in practical use, the inventor has worked tirelessly to improve them with the help of their rich professional knowledge and years of practical experience. Research and create the present invention.

本發明關於一種多功能吸附錯合物,包含一單寧三價鐵錯合物,且其製備方法是以一單寧酸材料與一鐵鹽材料作用後獲得,且具有吸附生物性物質以及化學性物質的能力。The invention relates to a multifunctional adsorption complex, which comprises a tannin trivalent iron complex, and the preparation method is obtained by the action of a tannic acid material and an iron salt material, and has the functions of adsorbing biological substances and chemical substances. the ability of sexual substances.

本發明亦關於一種多功能吸附錯合物的製備方法,係將一材料與一鐵鹽材料混合均勻,並於一作用溫度反應一作用時間,以獲該多功能吸附錯合物。The present invention also relates to a preparation method of a multifunctional adsorption complex, which comprises mixing a material and an iron salt material uniformly, and reacting at an action temperature for an action time to obtain the multifunctional adsorption complex.

本發明亦關於一種移除生物性物質或化學性物質的方法,係將一多功能吸附錯合物與一溶液作用,以吸附並移除該溶液中含有的生物性物質或化學性物質,其中該多功能吸附錯合物係包含單寧三價鐵錯合物The present invention also relates to a method for removing biological or chemical substances, which is to act on a multifunctional adsorption complex with a solution to adsorb and remove the biological or chemical substances contained in the solution, wherein The multifunctional adsorption complex system comprises tannin trivalent iron complex

於本發明之一實施例中,鐵鹽材料為氯化鐵。In one embodiment of the present invention, the iron salt material is ferric chloride.

於本發明之一實施例中,所吸附的生物性物質包含脂多糖(Lipopolysaccharide)以及微生物毒素。In one embodiment of the present invention, the adsorbed biological substances include lipopolysaccharide (Lipopolysaccharide) and microbial toxins.

於本發明之一實施例中,化學性物質包含抗生素、色素與塑膠微粒。In one embodiment of the present invention, the chemical substances include antibiotics, pigments and plastic particles.

於本發明之一實施例中,抗生素為阿米卡星(Amikacin),頭孢曲松(Ceftriaxone),粘桿菌素(Colistin),去氧羥四環素(Doxycycline),老虎黴素(Tigecycline)及撲菌特(Trimethoprim)其中至少之一。In one embodiment of the present invention, the antibiotics are Amikacin, Ceftriaxone, Colistin, Doxycycline, Tigecycline and Promethazine. Special (Trimethoprim) at least one of them.

於本發明之一實施例中,單寧酸材料與鐵鹽材料的作用溫度為23~28℃,且作用時間為1~10分鐘。In one embodiment of the present invention, the action temperature of the tannic acid material and the iron salt material is 23-28° C., and the action time is 1-10 minutes.

於本發明之一實施例中,係將0.002 M的氯化鐵與0.001 M的單寧酸混合均勻並作用,以獲得該多功能吸附錯合物。In one embodiment of the present invention, 0.002 M ferric chloride and 0.001 M tannic acid are uniformly mixed and acted to obtain the multifunctional adsorption complex.

藉此,本發明之多功能吸附錯合物製備方法簡單,具有吸附多種物質的能力,包含內毒素、微生物毒素、抗生素、色素與塑膠微粒等等,應用範圍也相當廣泛。Therefore, the preparation method of the multifunctional adsorption complex of the present invention is simple, and has the ability to adsorb various substances, including endotoxins, microbial toxins, antibiotics, pigments and plastic particles, etc., and has a wide range of applications.

為令本發明之技術手段其所能達成之效果,能夠有更完整且清楚的揭露,茲詳細說明如下,請一併參閱揭露之圖式。In order to enable a more complete and clear disclosure of the effects that the technical means of the present invention can achieve, the detailed description is as follows, please refer to the disclosed drawings together.

本發明關於一種多功能吸附錯合物及其製造方法,多功能吸附錯合物包含單寧三價鐵錯合物,且其製備方法是將單寧酸材料與鐵鹽材料混合均勻,並於一作用溫度反應一作用時間後所獲得;於本案較佳實施例中,鐵鹽材料為氯化鐵,所製得的單寧三價鐵錯合物可吸附多種生物性以及化學性的物質,包含色素、塑膠粒子、抗生素、內毒素以及微生物毒素等等。The invention relates to a multifunctional adsorption complex and a manufacturing method thereof. The multifunctional adsorption complex comprises a tannin trivalent iron complex, and the preparation method is to mix the tannic acid material and the iron salt material uniformly, and place the It is obtained after one action temperature and one action time; in the preferred embodiment of this case, the iron salt material is ferric chloride, and the prepared tannin trivalent iron complex can adsorb various biological and chemical substances, Contains pigments, plastic particles, antibiotics, endotoxins and microbial toxins, etc.

此外,藉由下述具體實施例,可進一步證明本發明可實際應用之範圍,但不意欲以任何形式限制本發明之範圍。In addition, the following specific examples can further prove the scope of practical application of the present invention, but are not intended to limit the scope of the present invention in any form.

一、單寧三價鐵錯合物製備1. Preparation of tannin trivalent iron complex

分別準備0.002 M的氯化鐵溶液以及0.001 M的單寧酸(tannic acid)溶液,並將二溶液以體積比1:1的比例混合均勻以獲得一混合溶液,將混合溶液於23~28℃作用1~10分鐘,再將混合溶液以2000 rpm之轉速離心5分鐘,先收集上清液以去除大顆粒子;再將上清液以13000 rpm的轉速離心10分鐘,並收集沉澱物,且將沉澱物的體積濃縮到1 mL,以獲得一單寧三價鐵錯合物濃縮液;於此實施例中,氯化鐵與單寧酸溶液係於25℃作用約5分鐘。Prepare 0.002 M ferric chloride solution and 0.001 M tannic acid solution, respectively, and mix the two solutions in a volume ratio of 1:1 to obtain a mixed solution. Act for 1-10 minutes, then centrifuge the mixed solution at 2000 rpm for 5 minutes, first collect the supernatant to remove large particles; then centrifuge the supernatant at 13,000 rpm for 10 minutes, and collect the precipitate, and The volume of the precipitate was concentrated to 1 mL to obtain a tannin ferric complex concentrate; in this example, the ferric chloride and tannic acid solution were reacted at 25° C. for about 5 minutes.

將製得的單寧三價鐵錯合物以傅立葉轉換紅外光譜儀(Fourier-transform infrared spectroscopy,FTIR)進行分析,請參見第一圖(A),與單寧酸與單寧三價鐵錯合物的光譜十分相似,由於單寧酸為水溶性物質,若未與氯化鐵作用,則製備時會存在於上清液中而被移除,但是本案離心後獲得的沉澱物,經分析其FTIR圖譜的結果與十分相似,故可證實單寧酸確實有與氯化鐵作用並形成錯合物。The prepared tannin trivalent iron complex was analyzed by Fourier-transform infrared spectroscopy (FTIR), see the first figure (A), and tannic acid and tannin trivalent iron complex The spectra of the compounds are very similar. Since tannic acid is a water-soluble substance, if it does not interact with ferric chloride, it will be present in the supernatant and removed during preparation. However, the precipitate obtained after centrifugation in this case is analyzed. The results of the FTIR spectrum are very similar, so it can be confirmed that tannic acid does interact with ferric chloride and form a complex.

請再參見第一圖(B),為使用分光光度計(UV-Vis spectra)測量單寧三價鐵錯合物的吸收光圖譜,可觀察到其在575 nm的波長處有一個單一的吸收峰。Please refer to the first figure (B) again, in order to measure the absorption spectrum of the tannin ferric complex using a spectrophotometer (UV-Vis spectra), it can be observed that it has a single absorption at the wavelength of 575 nm peak.

接著使用動態光散射粒徑分析儀(Dynamic Light Scattering/Zeta Potential Analyzer)測量單寧三價鐵錯合物的粒徑以及Zeta電勢(Zeta potential),其中Zeta電勢的絕對值大小代表測量物表面電荷量的高低,Zeta電勢絕對值越大表示測量物表面的電荷量越高、電荷之間的排斥力會防止測量物聚集、代表測量物的結構更穩定;參見第二圖(A),本實施例製備的單寧三價鐵錯合物的粒徑為207 nm,屬於奈米材料的大小;又根據第二圖(B),單寧三價鐵錯合物的Zeta電勢約為-32 mV,屬於Zate電勢絕對值高的材料,表示其結構穩定。Then use Dynamic Light Scattering/Zeta Potential Analyzer to measure the particle size and Zeta potential of tannin trivalent iron complex, where the absolute value of Zeta potential represents the surface charge of the measured object The higher the absolute value of Zeta potential, the higher the amount of charge on the surface of the measurement object, the repulsive force between the charges will prevent the measurement object from gathering, and the structure of the measurement object is more stable; refer to the second figure (A), this implementation The particle size of the tannin trivalent iron complex prepared by example is 207 nm, which belongs to the size of nanomaterials; and according to the second figure (B), the Zeta potential of the tannin trivalent iron complex is about -32 mV , belongs to the material with high absolute value of Zate potential, indicating that its structure is stable.

請再參見第三圖,為本案單寧三價鐵錯合物的穿透式電子顯微鏡(Transmission electron microscope)觀察照片,可得知其呈現一網狀結構。Please refer to the third figure again, which is a transmission electron microscope (Transmission electron microscope) photograph of the tannin trivalent iron complex in this case, and it can be known that it presents a network structure.

二、單寧三價鐵錯合物吸附試驗2. Tannin ferric complex adsorption test

(一)、色素吸附測試(1) Pigment adsorption test

先準備一結晶紫(crystal violet)溶液,在分別與不同濃度的單寧三價鐵錯合物於室溫中作用15分鐘;將結晶紫溶液離心、移除上清液,再使用1 X PBS緩衝液(Phosphate-Buffered Saline)清洗沉澱物,清洗次數為三次,以洗去未被吸附的結晶紫;最後將沉澱物與甲醇作用5分鐘,以將結晶紫自沉澱物中洗脫並獲得一洗脫液,再測量洗脫液於波長595nm的吸光值(簡稱OD595),即可獲得單寧三價鐵錯合物的結晶紫吸收量。請參見第四圖(A),為使用不同濃度單寧三價鐵錯合物進行吸附後、獲得的洗脫液的OD595,隨着所使用的單寧三價鐵錯合物濃度上升,最後洗脫液的OD595也隨之上升,表示單寧三價鐵錯合物對於結晶紫的吸附量具有劑量依存性(dose dependent);第四圖(B)則為吸附後洗脫液的觀察照片,可以看到使用越高劑量的單寧三價鐵錯合物進行吸附,最後獲得的洗脫液顏色越深,表示洗脫液中的結晶紫含量越高。First prepare a crystal violet solution and react it with different concentrations of tannin ferric complexes at room temperature for 15 minutes; centrifuge the crystal violet solution, remove the supernatant, and then use 1 X PBS Buffer (Phosphate-Buffered Saline) washes the precipitate for three times to wash off the unadsorbed crystal violet; finally, the precipitate is reacted with methanol for 5 minutes to elute the crystal violet from the precipitate and obtain a The eluate, and then measure the absorbance of the eluate at a wavelength of 595 nm (OD595 for short), the crystal violet absorption of the tannin ferric complex can be obtained. Please refer to the fourth figure (A), which is the OD595 of the eluate obtained after adsorption with different concentrations of tannin ferric complex. As the concentration of tannin ferric complex used increases, the final The OD595 of the eluate also increased, indicating that the adsorption amount of tannin ferric iron complex to crystal violet was dose-dependent; the fourth figure (B) is the observation photo of the eluate after adsorption , it can be seen that the higher the dosage of tannin ferric complex is used for adsorption, the darker the color of the eluate obtained at the end, indicating that the content of crystal violet in the eluate is higher.

(二)、塑膠微粒吸附測試(2), plastic particle adsorption test

此試驗中,係使用市售茶包袋進行測試,先將茶包袋放入純水中,並加熱煮沸且持續沸騰10分鐘,接著移除茶包袋,所獲得的茶包袋煮沸液中因具有高量塑膠微粒,因此其稱為塑膠微粒組;又,取本案製備的單寧三價鐵錯合物,與茶包袋煮沸液以體積比1:9的比例均勻混合以獲得一混合液,將混合液於室溫作用1小時,再將混合液離心,離心後的上清液稱為樣品一、離心後的沉澱物部分稱為樣品二。將塑膠微粒組、樣品一以及樣品二分別以濾紙進行真空過濾,再將濾紙以尼龍紅染劑於避光的條件下染色30分鐘,最後再以螢光顯微鏡中的TRITC濾鏡或是FITC濾鏡觀察,以偵測塑膠微粒的螢光;請參見第五圖,不論是使用TRITC濾鏡或是FITC濾鏡觀察,塑膠微粒組中都可以觀察到相當多的塑膠微粒光點,而使用單寧三價鐵錯合物處理後獲得的樣品一中,光點數量顯著減少,表示其含有的塑膠微粒量明顯降低;又樣品二中可以觀察到相當大量的光點,表示單寧三價鐵錯合物上確實吸附了大量的塑膠微粒。In this test, commercially available tea bags were used for testing. First, the tea bags were put into pure water, heated and boiled for 10 minutes, and then the tea bags were removed. Because it has a high amount of plastic particles, it is called the plastic particle group; in addition, take the tannin trivalent iron complex prepared in this case, and evenly mix it with the boiling liquid of the tea bag at a volume ratio of 1:9 to obtain a mixed The mixed solution was treated at room temperature for 1 hour, and then the mixed solution was centrifuged. The supernatant after centrifugation was called sample 1, and the sediment part after centrifugation was called sample 2. The plastic particle group, sample 1 and sample 2 were vacuum filtered with filter paper respectively, and then the filter paper was stained with nylon red dye in the dark for 30 minutes, and finally filtered with a TRITC filter or FITC filter in a fluorescence microscope. microscopic observation to detect the fluorescence of plastic particles; please refer to the fifth figure, no matter using a TRITC filter or a FITC filter to observe, a considerable number of plastic particle light spots can be observed in the plastic particle group. In sample 1 obtained after the treatment of ferric iron complex, the number of light spots was significantly reduced, indicating that the amount of plastic particles contained in it was significantly reduced; in the second sample, a considerable amount of light spots could be observed, indicating that tannin ferric iron A large number of plastic particles were indeed adsorbed on the complex.

(三)、抗生素吸附測試(3) Antibiotic adsorption test

先將本案的單寧三價鐵錯合物(後簡稱Fe-TA),以體積比1:9的比例,分別與六種抗生素溶液混合,以獲得一混合液,並將混合液於室溫作用1小時;將作用後的混合液離心,收集離心後的上清液,並與10 5CFU的大腸桿菌混合,並於37℃共同培養24小時,最後於菌液中加入alamarBlue試劑,藉由試劑顏色的變化,做為大腸桿菌生長的指標,以評估與Fe-TA作用後的抗生素對於大腸桿菌生長的影響,若大腸桿菌生長狀況佳,alamarBlue試劑會呈現粉紅色、若大腸桿菌皆沒有存活,試劑會呈現藍色。本試驗中使用的抗生素分別是阿米卡星(Amikacin),頭孢曲松(Ceftriaxone),粘桿菌素(Colistin),去氧羥四環素(Doxycycline),老虎黴素(Tigecycline)以及撲菌特(Trimethoprim),且測試使用的大腸桿菌的ATCC編號為ATCC 25922。請參見第六圖與第七圖,圖中的對照組為沒有與Fe-TA作用的抗生素,而Fe-TA組則是與Fe-TA作用後的抗生素溶液;根據第六圖,阿米卡星、頭孢曲松與粘桿菌素在較高使用濃度的狀況下,都能有效抑制大腸桿菌的生長,因此呈現藍色;但是抗生素與Fe-TA作用後、再與大腸桿菌共同培養的組別中,大腸桿菌的生長情形會恢復,因此與試劑作用後會呈現粉紅色;又請參見第七圖,去氧羥四環素,老虎黴素以及撲菌特同樣也具有抑制大腸桿菌生長的能力,但是與Fe-TA作用後,其抑制細菌生長的能力明顯下降;故,本發明製備的單寧三價鐵錯合物確實具有吸附抗生素的能力。 First, the tannin trivalent iron complex (hereinafter referred to as Fe-TA) of this case was mixed with six kinds of antibiotic solutions in a volume ratio of 1:9 to obtain a mixed solution, and the mixed solution was kept at room temperature. Act for 1 hour; centrifuge the mixed solution after the action, collect the supernatant after centrifugation, mix it with 10 5 CFU of Escherichia coli, and co-cultivate at 37 ° C for 24 hours, and finally add alamarBlue reagent to the bacterial solution. The color change of the reagent is used as an indicator of the growth of E. coli to evaluate the effect of the antibiotics acting on Fe-TA on the growth of E. coli. If the growth of E. coli is in good condition, the alamarBlue reagent will appear pink, and if the E. coli does not survive , the reagent will appear blue. The antibiotics used in this study were Amikacin, Ceftriaxone, Colistin, Doxycycline, Tigecycline and Trimethoprim ), and the ATCC number of E. coli used in the test is ATCC 25922. Please refer to Figure 6 and Figure 7, the control group in the figure is the antibiotic without the action of Fe-TA, while the Fe-TA group is the antibiotic solution after the action with Fe-TA; according to the sixth figure, Amica Star, ceftriaxone and colistin can effectively inhibit the growth of Escherichia coli at higher concentrations, so they appear blue; however, the group that was co-cultured with Escherichia coli after the action of antibiotics and Fe-TA , the growth of E. coli will be restored, so it will appear pink after reacting with the reagent; see also Figure 7, deoxytetracycline, tiger tetracycline, and promethazine also have the ability to inhibit the growth of E. coli, but After acting with Fe-TA, its ability to inhibit bacterial growth is obviously reduced; therefore, the tannin ferric complex prepared by the present invention does have the ability to adsorb antibiotics.

(四)、內毒素吸附測試(4), Endotoxin adsorption test

本實施例係測試單寧三價鐵錯合物(後簡稱Fe-TA)對於內毒素脂多糖(Lipopolysaccharide,LPS)的吸附能力,並使用與LPS作用後會產生凝集反應的鱟魚血萃取物 (Limulus Amebocyte Lysate)進行檢測。將本發明製備的Fe-TA與不同濃度的LPS溶液混合,並於室溫下作用1小時之後,離心並收集上清液,以獲得處理後的LPS溶液;接著將未處理過的LPS溶液(對照組)以及經過Fe-TA處理後的LPS溶液(Fe-TA組),分別與鱟魚血萃取物作用,並觀察鱟魚血萃取物的凝集情形。請參見第八圖,對照組中,加入0.1 μg/mL LPS或是1 μg/mL LPS的組別,鱟魚血萃取物有明顯的凝集情形,會產生呈現不流動狀且聚集於試管底部的濃稠物(圖中紅色圈圈之處);反觀Fe-TA組中,經過Fe-TA處理的LPS,與鱟魚血萃取物作用後,其凝聚情形較不明顯,在試管內的流動性較高,可以在試管內自流動(圖中紅色圈圈之處);此結果顯示,本發明製備的單寧三價鐵錯合物也具有吸附LPS的功效,且能降低LPS誘發的凝集反應。In this example, the adsorption capacity of tannin trivalent iron complex (hereinafter referred to as Fe-TA) to endotoxin lipopolysaccharide (LPS) was tested, and the blood extract of horseshoe crab, which would produce agglutination reaction with LPS, was used (Limulus Amebocyte Lysate) for detection. The Fe-TA prepared by the present invention is mixed with LPS solutions of different concentrations, and after acting at room temperature for 1 hour, the supernatant is centrifuged and collected to obtain the LPS solution after treatment; then the untreated LPS solution ( The control group) and the LPS solution (Fe-TA group) treated with Fe-TA were reacted with the Limulus limulus blood extract respectively, and the agglutination of the Limulus limulus blood extract was observed. Please refer to Figure 8. In the control group, in the group added with 0.1 μg/mL LPS or 1 μg/mL LPS, the Limulus limulus blood extract had obvious agglutination. Thick material (the red circle in the figure); on the contrary, in the Fe-TA group, after the LPS treated with Fe-TA, after the action of the Limulus limulus blood extract, the coagulation situation is less obvious, and the fluidity in the test tube is less obvious. It can flow freely in the test tube (the red circle in the figure); this result shows that the tannin trivalent iron complex prepared by the present invention also has the effect of adsorbing LPS, and can reduce the agglutination reaction induced by LPS .

(五)、微生物毒素吸附測試(5) Microbial toxin adsorption test

本試驗的目的是測試單寧三價鐵錯合物(後簡稱Fe-TA)對於艱難梭狀桿菌( Clostridium difficileVPI10463)生成的毒素B(Toxin B)的吸附能力。 The purpose of this experiment is to test the adsorption capacity of tannin trivalent iron complex (hereinafter referred to as Fe-TA) for toxin B produced by Clostridium difficile VPI10463.

首先,先將艱難梭狀桿菌( Clostridium difficileVPI10463)培養4天,以使其生成毒素B(Toxin B)並將毒素B釋放於培養液中;將細菌菌體過濾、並濃縮培養液,以將毒素B濃縮10倍;將濃縮後的毒素B與不同量的Fe-TA於室溫作用1小時,再以離心的方式去除Fe-TA,並收集作用後的上清液;將上清液以西方點墨法分析,以獲得其中毒素B的含量,其中毒素B的分子量為270 kDa。請參見第九圖,「NC」為不含有毒素B的負對照組,「PC」為含有毒素B的正對照組,「Treated sup.」為與Fe-TA作用並離心後所收集的上清液;根據第九圖,上清液中毒素B的含量,會隨著與之作用的Fe-TA重量的增加而減少,且當使用的Fe-TA重量為0.175 mg以上時,樣本中幾乎為檢測不到毒素B,此結果顯示本發明製備的單寧三價鐵錯合物也能有效吸附毒素B。 First, Clostridium difficile VPI10463 was cultured for 4 days to produce toxin B (Toxin B) and release toxin B in the culture medium; the bacterial cells were filtered and the culture medium was concentrated to Toxin B was concentrated 10 times; the concentrated toxin B was reacted with different amounts of Fe-TA for 1 hour at room temperature, then Fe-TA was removed by centrifugation, and the supernatant after the action was collected; Western blot analysis to obtain the content of toxin B, which has a molecular weight of 270 kDa. Please refer to the ninth figure, "NC" is the negative control group without toxin B, "PC" is the positive control group with toxin B, "Treated sup." is the supernatant collected after interacting with Fe-TA and centrifuging According to the ninth figure, the content of toxin B in the supernatant will decrease with the increase of the weight of Fe-TA acting on it, and when the weight of Fe-TA used is more than 0.175 mg, almost No toxin B can be detected, and this result shows that the tannin trivalent iron complex prepared by the present invention can also effectively adsorb toxin B.

綜上,本發明揭露之多功能吸附錯合物,係包含單寧三價鐵錯合物,具有吸附多種生物性物質與化學性物質的能力,包含吸附色素、塑膠微粒、抗生素、內毒素以及微生物毒素等;此外本發明製備的多功能吸附錯合物,於完成吸附作用後也能輕易將其自作用的溶液中移除,使用上相當方便。To sum up, the multifunctional adsorption complex disclosed by the present invention comprises a tannin ferric complex, which has the ability to adsorb various biological substances and chemical substances, including adsorption of pigments, plastic particles, antibiotics, endotoxins and Microbial toxins, etc.; in addition, the multifunctional adsorption complex prepared by the present invention can also be easily removed from the acting solution after the adsorption is completed, which is quite convenient to use.

綜上所述,本發明多功能吸附錯合物及其製備方法與用途,的確能藉由上述所揭露之實施例,達到所預期之使用功效,且本發明亦未曾公開於申請前,誠已完全符合專利法之規定與要求。爰依法提出發明專利之申請,懇請惠予審查,並賜准專利,則實感德便。To sum up, the multifunctional adsorption complex of the present invention and its preparation method and use can indeed achieve the expected use effect through the above disclosed embodiments, and the present invention has not been disclosed before the application. Fully comply with the provisions and requirements of the Patent Law. It is indeed a virtue to file an application for an invention patent in accordance with the law.

惟,上述所揭之說明,僅為本發明之較佳實施例,非為限定本發明之保護範圍;其;大凡熟悉該項技藝之人士,其所依本發明之特徵範疇,所作之其它等效變化或修飾,皆應視為不脫離本發明之設計範疇。However, the above-mentioned descriptions are only preferred embodiments of the present invention, and are not intended to limit the scope of protection of the present invention; those who are familiar with the art, rely on the characteristic scope of the present invention, do other things, etc. Effective changes or modifications should be regarded as not departing from the design scope of the present invention.

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第一圖:本發明單寧三價鐵錯合物的FTIR與吸光值分析圖。The first figure: the FTIR and absorbance analysis diagram of the tannin trivalent iron complex of the present invention.

第二圖:本發明單寧三價鐵錯合物的粒徑與Zeta電勢分析圖。The second figure: the particle size and Zeta potential analysis diagram of the tannin trivalent iron complex of the present invention.

第三圖:本發明單寧三價鐵錯合物的電子顯微鏡觀察照片。The third figure: the electron microscope observation photograph of the tannin trivalent iron complex of the present invention.

第四圖:本發明單寧三價鐵錯合物吸附色素分析圖。The fourth figure: the analysis diagram of the adsorption pigment of the tannin ferric complex compound of the present invention.

第五圖:本發明單寧三價鐵錯合物吸附塑膠微粒分析圖。The fifth figure: the analysis diagram of the adsorption of plastic particles by the tannin trivalent iron complex of the present invention.

第六圖:本發明單寧三價鐵錯合物吸附抗生素分析圖(一)。Figure 6: Analytical diagram (1) of the adsorption of antibiotics by the tannin trivalent iron complex of the present invention.

第七圖:本發明單寧三價鐵錯合物吸附抗生素分析圖(二)。Figure 7: Analytical diagram (2) of the adsorption of antibiotics by the tannin trivalent iron complex of the present invention.

第八圖:本發明單寧三價鐵錯合物吸附內毒素分析圖。The eighth figure: the analysis diagram of the adsorption of endotoxin by the tannin ferric complex of the present invention.

第九圖:本發明單寧三價鐵錯合物吸附微生物毒素分析圖。The ninth figure: the analysis diagram of the adsorption of microbial toxins by the tannin trivalent iron complex of the present invention.

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Claims (10)

一種以單寧三價鐵錯合物移除生物性物質或化學性物質的方法,係將一單寧三價鐵錯合物與一溶液作用以吸附該溶液中的生物性物質或化學性物質,再將該單寧三價鐵錯合物於該溶液中移除,以移除該溶液中的生物性物質或化學性物質,其中該單寧三價鐵錯合物的製備方法是以一單寧酸材料與一鐵鹽材料作用後獲得,且其中該化學性物質包含抗生素與塑膠微粒。 A method for removing biological or chemical substances with tannin ferric complex, which is to act on a tannin ferric complex with a solution to adsorb biological or chemical substances in the solution , and then remove the tannin ferric complex in the solution to remove biological substances or chemical substances in the solution, wherein the preparation method of the tannin ferric complex is a The tannic acid material is obtained by acting on an iron salt material, and the chemical substance includes antibiotics and plastic particles. 如請求項1所述之方法,其中該鐵鹽材料為氯化鐵。 The method of claim 1, wherein the iron salt material is ferric chloride. 如請求項1所述之方法,其中該生物性物質包含脂多糖(Lipopolysaccharide)。 The method of claim 1, wherein the biological substance comprises lipopolysaccharide. 如請求項1所述之方法,其中該單寧三價鐵錯合物的製備方法中,該單寧酸材料之濃度為0.001M,且該氯化鐵濃度為0.002M。 The method according to claim 1, wherein in the preparation method of the tannin ferric complex, the concentration of the tannic acid material is 0.001M, and the concentration of the ferric chloride is 0.002M. 如請求項1所述之方法,其中該抗生素為阿米卡星(Amikacin),頭孢曲松(Ceftriaxone),粘桿菌素(Colistin),去氧羥四環素(Doxycycline),老虎黴素(Tigecycline)以及撲菌特(Trimethoprim)。 The method of claim 1, wherein the antibiotic is Amikacin, Ceftriaxone, Colistin, Doxycycline, Tigecycline and Trimethoprim. 如請求項1所述之方法,其中該單寧三價鐵錯合物的製備方法,是將該單寧酸材料與該鐵鹽材料混合均勻,於23~28℃作用1~10分鐘,以獲該單寧三價鐵錯合物。 The method according to claim 1, wherein the preparation method of the tannin trivalent iron complex is to mix the tannic acid material and the iron salt material uniformly, and act at 23-28° C. for 1-10 minutes to obtain a The tannin trivalent iron complex was obtained. 如請求項6所述之方法,其中該單寧酸材料與該鐵鹽材料是於25℃作用5分鐘。 The method of claim 6, wherein the tannic acid material and the iron salt material are reacted at 25°C for 5 minutes. 如請求項1所述之方法,其中該生物性物質包含微生物毒素。 The method of claim 1, wherein the biological substance comprises microbial toxins. 如請求項8所述之方法,其中該微生物毒素為艱難梭狀桿菌(Clostridium difficile VpI10463)生成的毒素B(Toxin B)。 The method of claim 8, wherein the microbial toxin is Toxin B produced by Clostridium difficile VpI10463. 如請求項1所述之方法,其中該化學性物質進一步包含結晶紫。 The method of claim 1, wherein the chemical substance further comprises crystal violet.
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CN101342481A (en) * 2008-08-18 2009-01-14 北京思清源生物科技有限公司 Preparation method for iron-tannic acid adsorption agent with high-ctivity dephosphorization and uses thereof
CN109967047A (en) * 2018-11-27 2019-07-05 鲁东大学 One-step synthesis method Fe3+Selective removal pollutant is used for the multi-functional environmentally friendly poly- tannic acid of formaldehyde double cross connection

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101342481A (en) * 2008-08-18 2009-01-14 北京思清源生物科技有限公司 Preparation method for iron-tannic acid adsorption agent with high-ctivity dephosphorization and uses thereof
CN109967047A (en) * 2018-11-27 2019-07-05 鲁东大学 One-step synthesis method Fe3+Selective removal pollutant is used for the multi-functional environmentally friendly poly- tannic acid of formaldehyde double cross connection

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