CN116764157A - Method for degrading toluene by enzyme oxidation - Google Patents
Method for degrading toluene by enzyme oxidation Download PDFInfo
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- YXFVVABEGXRONW-UHFFFAOYSA-N Toluene Chemical compound CC1=CC=CC=C1 YXFVVABEGXRONW-UHFFFAOYSA-N 0.000 title claims abstract description 228
- 108090000790 Enzymes Proteins 0.000 title claims abstract description 48
- 102000004190 Enzymes Human genes 0.000 title claims abstract description 48
- 238000000034 method Methods 0.000 title claims abstract description 34
- 230000000593 degrading effect Effects 0.000 title claims description 4
- 238000007254 oxidation reaction Methods 0.000 title claims description 4
- 230000003647 oxidation Effects 0.000 title claims description 3
- 108010093096 Immobilized Enzymes Proteins 0.000 claims abstract description 50
- 238000010525 oxidative degradation reaction Methods 0.000 claims abstract description 7
- 230000002255 enzymatic effect Effects 0.000 claims abstract description 3
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims description 41
- 238000006243 chemical reaction Methods 0.000 claims description 40
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 36
- 239000008055 phosphate buffer solution Substances 0.000 claims description 20
- 238000001035 drying Methods 0.000 claims description 19
- 239000007788 liquid Substances 0.000 claims description 18
- 229910052757 nitrogen Inorganic materials 0.000 claims description 18
- 239000006228 supernatant Substances 0.000 claims description 18
- 238000002791 soaking Methods 0.000 claims description 13
- 235000011399 aloe vera Nutrition 0.000 claims description 12
- 244000043261 Hevea brasiliensis Species 0.000 claims description 11
- 244000252337 Epipremnum pinnatum Species 0.000 claims description 9
- 235000002637 Nicotiana tabacum Nutrition 0.000 claims description 9
- 241001116389 Aloe Species 0.000 claims description 7
- 241000196324 Embryophyta Species 0.000 claims description 7
- 239000000243 solution Substances 0.000 claims description 6
- 238000000605 extraction Methods 0.000 claims description 4
- 241000218218 Ficus <angiosperm> Species 0.000 claims 1
- 244000061176 Nicotiana tabacum Species 0.000 claims 1
- 238000001816 cooling Methods 0.000 claims 1
- 238000001914 filtration Methods 0.000 claims 1
- 238000000227 grinding Methods 0.000 claims 1
- 238000010298 pulverizing process Methods 0.000 claims 1
- 239000003054 catalyst Substances 0.000 abstract description 7
- 230000036632 reaction speed Effects 0.000 abstract description 4
- 230000000694 effects Effects 0.000 abstract description 3
- 230000003100 immobilizing effect Effects 0.000 abstract description 2
- 239000007800 oxidant agent Substances 0.000 abstract 1
- 230000001590 oxidative effect Effects 0.000 abstract 1
- 239000011550 stock solution Substances 0.000 description 32
- 238000006731 degradation reaction Methods 0.000 description 21
- 230000015556 catabolic process Effects 0.000 description 20
- 239000008367 deionised water Substances 0.000 description 16
- 229910021641 deionized water Inorganic materials 0.000 description 16
- 239000011521 glass Substances 0.000 description 16
- 239000012535 impurity Substances 0.000 description 16
- 239000000203 mixture Substances 0.000 description 16
- 239000000843 powder Substances 0.000 description 16
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 16
- 241000736019 Sansevieria Species 0.000 description 11
- 241000202847 Allagoptera arenaria Species 0.000 description 9
- 241000202807 Glycyrrhiza Species 0.000 description 8
- 235000001453 Glycyrrhiza echinata Nutrition 0.000 description 8
- 235000006200 Glycyrrhiza glabra Nutrition 0.000 description 8
- 235000017382 Glycyrrhiza lepidota Nutrition 0.000 description 8
- 241000208125 Nicotiana Species 0.000 description 8
- 229940010454 licorice Drugs 0.000 description 8
- 241001133760 Acoelorraphe Species 0.000 description 7
- 239000012855 volatile organic compound Substances 0.000 description 6
- 244000144927 Aloe barbadensis Species 0.000 description 5
- 235000002961 Aloe barbadensis Nutrition 0.000 description 5
- 230000003197 catalytic effect Effects 0.000 description 4
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 3
- 238000006555 catalytic reaction Methods 0.000 description 3
- 238000001000 micrograph Methods 0.000 description 3
- 238000001179 sorption measurement Methods 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 241000894006 Bacteria Species 0.000 description 2
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 description 2
- 238000003795 desorption Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000009826 distribution Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 238000006911 enzymatic reaction Methods 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- 231100000614 poison Toxicity 0.000 description 2
- 239000011148 porous material Substances 0.000 description 2
- 239000003440 toxic substance Substances 0.000 description 2
- 240000003521 Bauhinia purpurea Species 0.000 description 1
- 240000008168 Ficus benjamina Species 0.000 description 1
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 description 1
- 229910000147 aluminium phosphate Inorganic materials 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 238000006065 biodegradation reaction Methods 0.000 description 1
- 239000007853 buffer solution Substances 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 238000005119 centrifugation Methods 0.000 description 1
- 239000002131 composite material Substances 0.000 description 1
- 238000005520 cutting process Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 239000001963 growth medium Substances 0.000 description 1
- 238000005286 illumination Methods 0.000 description 1
- 238000011068 loading method Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 239000008363 phosphate buffer Substances 0.000 description 1
- 239000010970 precious metal Substances 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 229910052709 silver Inorganic materials 0.000 description 1
- 239000004332 silver Substances 0.000 description 1
- 150000003384 small molecules Chemical class 0.000 description 1
- 230000002195 synergetic effect Effects 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 239000002912 waste gas Substances 0.000 description 1
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- Immobilizing And Processing Of Enzymes And Microorganisms (AREA)
Abstract
本发明公开一种酶氧化降解甲苯的方法,包括:从植物中进行复合酶的提取、对获得的酶进行固定化,之后以空气为氧化剂,利用固定化酶对甲苯进行氧化降解。该方法操作简单,条件温和,对设备的要求低,固定化酶催化剂活性高,反应速度快,处理量大,催化剂的使用寿命长,使用1000 h以上固定化酶仍然具有较高的活性。该法能高效降解甲苯,是环境友好型工艺。
The invention discloses a method for enzymatic oxidative degradation of toluene, which includes: extracting complex enzymes from plants, immobilizing the obtained enzymes, and then using air as an oxidant to oxidatively degrade toluene using the immobilized enzymes. This method has simple operation, mild conditions, low requirements for equipment, high activity of the immobilized enzyme catalyst, fast reaction speed, large processing capacity, long service life of the catalyst, and the immobilized enzyme still has high activity after being used for more than 1000 hours. This method can efficiently degrade toluene and is an environmentally friendly process.
Description
技术领域Technical field
本发明属于酶技术领域,具体涉及一种固定化酶催化氧化降解甲苯的方法。The invention belongs to the field of enzyme technology, and specifically relates to a method for catalyzing the oxidative degradation of toluene by an immobilized enzyme.
背景技术Background technique
随着工业技术的不断发展,空气中排放的挥发性有机物越来越多,这对环境和人们的身体健康都造成了极大的危害。因此,人们开始致力于对挥发性有机物的降解处理,目前处理挥发性有机物的方法有物理吸附、生物降解、化学催化等方法,其中能有效降解挥发性有机物的方法主要有微生物和酶法、光催化法、等离子催化法等。专利CN108514886 A公开了一种用于光热协同催化甲苯降解的银基催化剂,该催化剂中采用了贵金属催化剂增加了生产成本。专利CN 109806743 A公开了一种含甲苯废气的处理方法和系统,采用臭氧对甲苯进行氧化降解处理,臭氧会造成二次污染。专利CN 110152670 A公开了一种光热催化降解甲苯的催化剂,甲苯的降解率在91%以上,但光照温度为125 ℃,反应的温度较高,耗能较大,且易产生有毒性的副产物。专利CN 112999845 A公开了一种等离子体电源降解甲苯的方法,该法需要特定的设备,对设备的要求较高,能耗较高,降解过程中生成的臭氧也会造成二次污染;专利CN110079472 A公开了一种分离甲苯降解菌的培养基,培养的甲苯降解菌能高效的降解甲苯,但是微生物处理甲苯反应速度较慢,受环境影响较大。With the continuous development of industrial technology, more and more volatile organic compounds are emitted in the air, which has caused great harm to the environment and people's health. Therefore, people have begun to focus on the degradation of volatile organic compounds. The current methods for treating volatile organic compounds include physical adsorption, biodegradation, chemical catalysis and other methods. Among them, the methods that can effectively degrade volatile organic compounds mainly include microorganisms, enzymatic methods, and light. Catalysis method, plasma catalysis method, etc. Patent CN108514886 A discloses a silver-based catalyst for photothermal synergistic catalytic degradation of toluene. The use of precious metal catalysts in this catalyst increases production costs. Patent CN 109806743 A discloses a method and system for treating toluene-containing waste gas, which uses ozone to oxidatively degrade toluene. Ozone will cause secondary pollution. Patent CN 110152670 A discloses a catalyst for photothermal catalytic degradation of toluene. The degradation rate of toluene is more than 91%, but the illumination temperature is 125°C, the reaction temperature is high, the energy consumption is large, and toxic by-products are easily produced. product. Patent CN 112999845 A discloses a method for degrading toluene using a plasma power source. This method requires specific equipment, has high requirements for equipment, and consumes high energy. The ozone generated during the degradation process will also cause secondary pollution; patent CN110079472 A discloses a culture medium for isolating toluene-degrading bacteria. The cultured toluene-degrading bacteria can efficiently degrade toluene, but the reaction speed of microorganisms in processing toluene is slow and is greatly affected by the environment.
生物酶处理法是利用生物酶的催化氧化反应降解挥发性有机物的一种方法。该法通过酶反应形成游离基,然后游离基打开挥发性有机物中复杂的化学链,最终生成小分子物质。生物酶处理法具有降解效率高,反应条件温和,对设备条件要求低,反应速度快,对温度、浓度和有毒物质适用范围广等优点。Biological enzyme treatment method is a method that uses the catalytic oxidation reaction of biological enzymes to degrade volatile organic compounds. This method uses enzymatic reactions to form free radicals, which then open complex chemical chains in volatile organic compounds, ultimately producing small molecule substances. The biological enzyme treatment method has the advantages of high degradation efficiency, mild reaction conditions, low requirements on equipment conditions, fast reaction speed, and wide application range for temperature, concentration and toxic substances.
发明内容Contents of the invention
针对上述现有技术问题,本发明提供了一种固定化酶氧化降解甲苯的方法,将从植物中提取的复合酶固定化处理后对甲苯进行催化氧化,能够使得甲苯高效氧化降解,降解率达到99.5%。In view of the above existing technical problems, the present invention provides a method for oxidative degradation of toluene with an immobilized enzyme. After immobilizing a complex enzyme extracted from plants, the toluene is catalytically oxidized, which can enable efficient oxidation and degradation of toluene, with a degradation rate of 99.5%.
为实现上述目的,本发明采取如下的技术方案:In order to achieve the above objects, the present invention adopts the following technical solutions:
一种酶氧化降解甲苯的方法,包括如下步骤:A method for enzymatic oxidative degradation of toluene, comprising the following steps:
(1)复合酶的提取:取植物的叶,粉碎后加入磷酸缓冲溶液进行提取,之后离心处理,上清液即为复合酶液;(1) Extraction of complex enzyme: Take the leaves of the plant, crush them and add phosphate buffer solution for extraction, then centrifuge, and the supernatant is the complex enzyme solution;
所述植物为白掌、烟草、甘草、绿萝、芦荟、虎尾兰、矮棕、垂叶榕、橡皮树中的任意两种或两种以上的混合;The plant is any two or a mixture of two or more of white palm, tobacco, licorice, pothos, aloe vera, Sansevieria, dwarf palm, fig, and rubber tree;
(2)酶的固定化:将清洁、干燥的固定化载体在步骤(1)获得的复合酶液中浸泡,之后过滤、烘干,得到固定化酶;(2) Immobilization of enzyme: Soak the clean and dry immobilized carrier in the composite enzyme solution obtained in step (1), then filter and dry to obtain the immobilized enzyme;
(3)甲苯氧化降解:将步骤(2)得到的固定化酶至于反应器中,于20~80℃,通入含有甲苯的空气进行反应。(3) Oxidative degradation of toluene: Place the immobilized enzyme obtained in step (2) into a reactor, and pass in air containing toluene at 20~80°C for reaction.
优选的,步骤(1)中所述的粉碎的方法为:加入液氮冷却后研磨。Preferably, the crushing method described in step (1) is: adding liquid nitrogen to cool and grind.
优选的,步骤(1)中所述的磷酸缓冲溶液的浓度为0.1~0.3 mol/L,pH为5.5~10.5。Preferably, the concentration of the phosphate buffer solution described in step (1) is 0.1~0.3 mol/L, and the pH is 5.5~10.5.
优选的,步骤(1)中所述的植物的叶与磷酸缓冲溶液的质量体积比为1:10(g/mL)。Preferably, the mass-to-volume ratio of the leaves of the plant described in step (1) to the phosphate buffer solution is 1:10 (g/mL).
优选的,步骤(1)中所述的离心的转速为10000rpm。Preferably, the centrifugal speed described in step (1) is 10,000 rpm.
优选的,步骤(1)中所述的离心的时间为10min。Preferably, the centrifugation time described in step (1) is 10 minutes.
优选的,步骤(2)中所述的固定化载体为氧化铝。Preferably, the immobilized carrier described in step (2) is alumina.
优选的,步骤(2)中所述的浸泡的时间为Preferably, the soaking time described in step (2) is
优选的,步骤(2)中所述的烘干的温度为60℃。Preferably, the drying temperature in step (2) is 60°C.
优选的,步骤(3)中所述的含有甲苯的空气中甲苯的浓度为500 ppm~3000 ppm,更优选为500 ppm~2500 ppm,最优选为1000 ppm~2500 ppm。Preferably, the concentration of toluene in the toluene-containing air described in step (3) is 500 ppm~3000 ppm, more preferably 500 ppm~2500 ppm, and most preferably 1000 ppm~2500 ppm.
优选的,步骤(3)中所述的反应,所述含有甲苯的空气的流速为50 mL/min~600mL/min,更优选为100 mL/min~500 mL/min,最优选为100 mL/min~300 mL/min。Preferably, for the reaction described in step (3), the flow rate of the toluene-containing air is 50 mL/min~600 mL/min, more preferably 100 mL/min~500 mL/min, and most preferably 100 mL/min. min~300 mL/min.
优选的,步骤(3)所述的反应的温度为20~60℃,最优选为20~40℃。Preferably, the reaction temperature in step (3) is 20 to 60°C, and most preferably 20 to 40°C.
采用本发明所述的降解甲苯的方法,具有如下优点:The method for degrading toluene of the present invention has the following advantages:
反应条件温和,对设备的要求较低。The reaction conditions are mild and the requirements for equipment are low.
固定化酶的催化活性高,反应速度快,对温度、浓度和有毒物质适用范围广。Immobilized enzymes have high catalytic activity, fast reaction speed, and are applicable to a wide range of temperatures, concentrations, and toxic substances.
(3)处理量大,催化剂的使用寿命长,使用1000 h以上固定化酶仍然具有较高的活性。(3) The processing capacity is large, the catalyst has a long service life, and the immobilized enzyme still has high activity after being used for more than 1000 hours.
(4)该工艺能高效氧化降解甲苯,是环境友好型工艺。(4) This process can efficiently oxidize and degrade toluene and is an environmentally friendly process.
附图说明Description of drawings
图1为为负载前的氧化铝载体的扫描电镜图。Figure 1 is a scanning electron microscope image of the alumina support before loading.
图2为负载固定化酶后的氧化铝的扫描电镜图。Figure 2 is a scanning electron microscope image of alumina loaded with immobilized enzyme.
图3为氧化降解甲苯后的负载固定化酶的氧化铝的扫描电镜图。Figure 3 is a scanning electron microscope image of alumina loaded with immobilized enzyme after oxidative degradation of toluene.
图4为氧化铝载体负载固定化酶前的吸脱附等温线。Figure 4 shows the adsorption and desorption isotherms before the alumina carrier is loaded with immobilized enzyme.
图5为氧化铝载体负载固定化酶后的吸脱附等温线。Figure 5 shows the adsorption and desorption isotherms after the alumina carrier is loaded with immobilized enzyme.
图6为氧化铝载体负载固定化酶前的BJH孔径分布图。Figure 6 shows the BJH pore size distribution diagram before the alumina carrier is loaded with immobilized enzyme.
图7为氧化铝载体负载固定化酶后的BJH孔径分布图。Figure 7 shows the BJH pore size distribution diagram after the alumina carrier is loaded with immobilized enzyme.
图8为固定化酶的元二色谱分析图。Figure 8 shows the metachrotron analysis chart of the immobilized enzyme.
实施方式Implementation
下面将通过实施例更详细地说明本说明,而这些实施例并不试图限制本发明的保护范围。The present description will be explained in more detail below by means of examples, which are not intended to limit the scope of the invention.
实施例Example
取白掌、烟草、甘草、绿萝、芦荟、虎尾兰、矮棕、垂叶榕和橡皮树的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.2mol/L,pH为7.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。Cut and mix the leaves of white palm, tobacco, licorice, pothos, aloe, Sansevieria, dwarf palm, fig and rubber tree, add liquid nitrogen to cool and then grind, then remove 0.1g of powder, add 1mL, 0.2mol/ L, phosphate buffer solution with pH 7.5 for soaking. Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡0.1 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 0.1 h, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为20℃,通入含有甲苯的空气流速为50 mL/min,甲苯初始浓度为,经过一次过柱后,得到甲苯的降解率为62.4%。The immobilized enzyme was filled into a glass reaction tube. The reaction temperature was 20°C. The flow rate of air containing toluene was 50 mL/min. The initial concentration of toluene was. After passing through the column once, the toluene degradation rate was 62.4%. .
实施例Example
取芦荟、虎尾兰和橡皮树的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.1mol/L,pH为6.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。Cut and mix the leaves of aloe vera, Sansevieria orchid and rubber tree, add liquid nitrogen to cool and grind them, then remove 0.1g of powder, add 1mL, 0.1mol/L, phosphate buffer solution with pH 6.5 for soaking. Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡10 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 10 hours, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为20℃,通入含有甲苯的空气流速为200 mL/min,甲苯初始浓度为The immobilized enzyme was filled into a glass reaction tube, the reaction temperature was 20°C, the flow rate of air containing toluene was 200 mL/min, and the initial concentration of toluene was
实施例Example
取白掌、甘草、绿萝、芦荟、矮棕、垂叶榕和橡皮树的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.3mol/L,pH为8.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。Cut and mix the leaves of white palm, licorice, pothos, aloe, dwarf palm, fig and rubber tree, add liquid nitrogen to cool and then grind, then remove 0.1g of powder, add 1mL, 0.3mol/L, pH is 8.5 Soak in phosphate buffer solution. Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡0.5 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 0.5 h, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为25℃,通入含有甲苯的空气流速为150 mL/min,甲苯初始浓度为700 ppm,经过一次过柱后,得到甲苯的降解率为85.0%。The immobilized enzyme was filled into a glass reaction tube. The reaction temperature was 25°C. The flow rate of air containing toluene was 150 mL/min. The initial concentration of toluene was 700 ppm. After passing through the column once, the degradation rate of toluene was obtained. 85.0%.
实施例Example
取烟草、甘草、芦荟、矮棕和垂叶榕的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.1mol/L,pH为10.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。Cut and mix the leaves of tobacco, licorice, aloe vera, dwarf palm and fig, add liquid nitrogen to cool and grind, then remove 0.1g of powder, add 1mL, 0.1mol/L, phosphate buffer solution with pH 10.5 for soaking . Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡1 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 1 hour, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为30 ℃,通入含有甲苯的空气流速为180 mL/min,甲苯初始浓度为10The immobilized enzyme was filled into a glass reaction tube, the reaction temperature was 30°C, the flow rate of air containing toluene was 180 mL/min, and the initial concentration of toluene was 10
实施例Example
取白掌、虎尾兰、垂叶榕和橡皮树的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.2mol/L,pH为5.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。Cut and mix the leaves of white palm, sansevieria, weeping fig and rubber tree, add liquid nitrogen to cool and grind, then remove 0.1g of powder, add 1mL, 0.2mol/L, pH 5.5 phosphate buffer solution for soaking . Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡2 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 2 hours, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为35 ℃,通入含有甲苯的空气流速为200 mL/min,甲苯初始浓度为900 ppm,经过一次过柱后,得到甲苯的降解率为88.5%。The immobilized enzyme was filled into a glass reaction tube. The reaction temperature was 35°C. The flow rate of air containing toluene was 200 mL/min. The initial concentration of toluene was 900 ppm. After passing through the column once, the degradation rate of toluene was obtained. 88.5%.
实施例Example
取白掌、甘草、虎尾兰、矮棕、垂叶榕和橡皮树的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.2mol/L,pH为7.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。Cut and mix the leaves of white palm, licorice, Sansevieria, dwarf palm, fig and rubber tree, add liquid nitrogen to cool and grind, then remove 0.1g of powder, add 1mL, 0.2mol/L, pH 7.5 Soak in phosphate buffer solution. Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡2.5 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 2.5 hours, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为20℃,通入含有甲苯的空气流速为250 mL/min,甲苯初始浓度为1000 ppm,经过一次过柱后,得到甲苯的降解率为91.3%。The immobilized enzyme was filled into a glass reaction tube. The reaction temperature was 20°C. The flow rate of air containing toluene was 250 mL/min. The initial concentration of toluene was 1000 ppm. After passing through the column once, the degradation rate of toluene was obtained. 91.3%.
实施例Example
取烟草、甘草、芦荟、虎尾兰、垂叶榕和橡皮树的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.2mol/L,pH为7.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。Cut and mix the leaves of tobacco, licorice, aloe, sansevieria, fig and rubber tree, add liquid nitrogen to cool and grind, then remove 0.1g of powder, add 1mL, 0.2mol/L, phosphate buffer with pH 7.5 Soak in the solution. Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡3 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 3 hours, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为40℃,通入含有甲苯的空气流速为100甲苯初始浓度为1500 ppm,经过一次过柱后,得到甲苯的降解率为84.8%。The immobilized enzyme was filled into a glass reaction tube, the reaction temperature was 40°C, the flow rate of air containing toluene was 100, and the initial concentration of toluene was 1500 ppm. After passing through the column once, the toluene degradation rate was 84.8%.
实施例Example
取绿萝、芦荟、虎尾兰和橡皮树的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.2mol/L,pH为7.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。Cut and mix the leaves of pothos, aloe, sansevieria and rubber tree, add liquid nitrogen to cool and then grind them, then remove 0.1g of powder, add 1mL, 0.2mol/L, phosphate buffer solution with pH 7.5 for soaking. Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡3.5 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 3.5 hours, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为20℃,通入含有甲苯的空气流速为300 mL/min,甲苯初始浓度为1800 ppm,经过一次过柱后,得到甲苯的降解率为92.6%。The immobilized enzyme was filled into a glass reaction tube. The reaction temperature was 20°C. The flow rate of air containing toluene was 300 mL/min. The initial concentration of toluene was 1800 ppm. After passing through the column once, the degradation rate of toluene was obtained. 92.6%.
实施例Example
取烟草、甘草、虎尾兰、矮棕和橡皮树的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.2mol/L,pH为7.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。Cut and mix the leaves of tobacco, licorice, Sansevieria, dwarf palm and rubber tree, add liquid nitrogen to cool and grind, then remove 0.1g of powder, add 1mL, 0.2mol/L, phosphate buffer solution with pH 7.5. soak. Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡4 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 4 hours, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为45 ℃,通入含有甲苯的空气流速为350 mL/min,甲苯初始浓度为2000 ppm,经过一次过柱后,得到甲苯的降解率为91.3%。The immobilized enzyme was filled into a glass reaction tube. The reaction temperature was 45°C. The flow rate of air containing toluene was 350 mL/min. The initial concentration of toluene was 2000 ppm. After passing through the column once, the degradation rate of toluene was obtained. 91.3%.
实施例Example
取白掌、甘草、芦荟、虎尾兰、矮棕和垂叶榕的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.2mol/L,pH为7.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。Cut and mix the leaves of white palm, licorice, aloe, Sansevieria, dwarf palm and fig. Add liquid nitrogen to cool and then grind. Then remove 0.1g of powder and add 1mL, 0.2mol/L, phosphoric acid with a pH of 7.5. Buffer solution for soaking. Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡4.5 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 4.5 hours, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为50 ℃,通入含有甲苯的空气流速为400 mL/min,甲苯初始浓度为2100 ppm,经过一次过柱后,得到甲苯的降解率为75.5%。The immobilized enzyme was filled into a glass reaction tube. The reaction temperature was 50°C. The flow rate of air containing toluene was 400 mL/min. The initial concentration of toluene was 2100 ppm. After passing through the column once, the degradation rate of toluene was obtained. 75.5%.
实施例Example
取绿萝、芦荟和虎尾兰的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.2mol/L,pH为7.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。Cut and mix the leaves of pothos, aloe vera and Sansevieria, add liquid nitrogen to cool and then grind them, then remove 0.1g of powder, add 1mL, 0.2mol/L, pH 7.5 phosphate buffer solution for soaking. Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡5 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 5 hours, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为55℃,通入含有甲苯的空气流速为500 mL/min,甲苯初始浓度为30Fill the immobilized enzyme into a glass reaction tube, the reaction temperature is 55°C, the flow rate of air containing toluene is 500 mL/min, and the initial concentration of toluene is 30
实施例Example
取绿萝和芦荟的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.2mol/L,pH为7.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。Cut and mix the leaves of pothos and aloe vera, add liquid nitrogen to cool and then grind them. Then remove 0.1g of powder and add 1mL, 0.2mol/L, phosphate buffer solution with a pH of 7.5 for soaking. Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡5.5 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 5.5 hours, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为60℃,通入含有甲苯的空气流速为380 mL/min,甲苯初始浓度为2500 ppm,经过一次过柱后,得到甲苯的降解率为62.1%。The immobilized enzyme was filled into a glass reaction tube. The reaction temperature was 60°C. The flow rate of air containing toluene was 380 mL/min. The initial concentration of toluene was 2500 ppm. After passing through the column once, the degradation rate of toluene was obtained. 62.1%.
实施例Example
取白掌、烟草、绿萝、芦荟、矮棕、垂叶榕和橡皮树的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.2mol/L,pH为7.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。Cut and mix the leaves of white palm, tobacco, pothos, aloe, dwarf palm, fig and rubber tree, add liquid nitrogen to cool and then grind, then remove 0.1g of powder, add 1mL, 0.2mol/L, pH is 7.5 Soak in phosphate buffer solution. Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡6 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 6 hours, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为65℃,通入含有甲苯的空气流速为6甲苯初始浓度为2600 ppm,经过一次过柱后,得到甲苯的降解率为58.7%。The immobilized enzyme was filled into a glass reaction tube. The reaction temperature was 65°C. The flow rate of air containing toluene was 6. The initial concentration of toluene was 2600 ppm. After passing through the column once, the toluene degradation rate was 58.7%.
实施例Example
取烟草、虎尾兰和垂叶榕的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.2mol/L,pH为7.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。Cut and mix the leaves of tobacco, sansevieria and fig. Then add liquid nitrogen to cool and grind them. Then remove 0.1g of powder and add 1mL, 0.2mol/L, phosphate buffer solution with pH 7.5 for soaking. Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡6.5 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 6.5 hours, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为70℃,通入含有甲苯的空气流速为450 mL/min,甲苯初始浓度为2700 ppm,经过一次过柱后,得到甲苯的降解率为49.6%。The immobilized enzyme was filled into a glass reaction tube. The reaction temperature was 70°C. The flow rate of air containing toluene was 450 mL/min. The initial concentration of toluene was 2700 ppm. After passing through the column once, the degradation rate of toluene was obtained. 49.6%.
实施例Example
取白掌和绿萝的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.2mol/L,pH为7.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。After cutting and mixing the leaves of white palm and pothos, add liquid nitrogen to cool and grind, then remove 0.1g of powder, add 1mL, 0.2mol/L, phosphate buffer solution with pH 7.5 for soaking. Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡7 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 7 hours, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为75℃,通入含有甲苯的空气流速为550 mL/min,甲苯初始浓度为2800 ppm,经过一次过柱后,得到甲苯的降解率为43.7%。The immobilized enzyme was filled into a glass reaction tube. The reaction temperature was 75°C. The flow rate of air containing toluene was 550 mL/min. The initial concentration of toluene was 2800 ppm. After passing through the column once, the degradation rate of toluene was obtained. 43.7%.
实施例Example
取烟草和矮棕的叶片剪碎、混合后,加入液氮冷却之后研磨,然后去0.1g粉末,加入1mL、0.2mol/L,pH为7.5的磷酸缓冲溶液进行浸泡。之后10000rpm条件下进行离心10min,取上清液为酶原液。Cut the leaves of tobacco and dwarf palm into pieces, mix them, add liquid nitrogen to cool them and then grind them. Then remove 0.1g of the powder and add 1mL, 0.2mol/L, phosphate buffer solution with a pH of 7.5 for soaking. Then centrifuge at 10,000 rpm for 10 min, and take the supernatant as the enzyme stock solution.
将氧化铝载体用去离子水清洗,并在超声中震荡20min以去除表面杂质,然后在干燥箱中烘干;将预处理后的氧化铝载体完全浸没在酶原液中,浸泡8 h,过滤,之后在60℃下烘干,得到固定化酶。Wash the alumina carrier with deionized water, shake it in ultrasonic for 20 minutes to remove surface impurities, and then dry it in a drying oven; completely immerse the pretreated alumina carrier in the enzyme stock solution, soak for 8 hours, and filter. It was then dried at 60°C to obtain the immobilized enzyme.
将固定化酶填装于玻璃反应管中,反应温度为80℃,通入含有甲苯的空气流速为600 mL/min,甲苯初始浓度为3000 ppm,经过一次过柱后,得到甲苯的降解率为40.1%。The immobilized enzyme was filled into a glass reaction tube. The reaction temperature was 80°C. The flow rate of air containing toluene was 600 mL/min. The initial concentration of toluene was 3000 ppm. After passing through the column once, the degradation rate of toluene was obtained. 40.1%.
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---|---|---|---|---|
US4338398A (en) * | 1979-03-20 | 1982-07-06 | Kabushiki Kaisha Hayashibara Seibutsu Kagaku Kenkyujo | Immobilization of starch degrading enzymes |
CN110093380A (en) * | 2019-04-25 | 2019-08-06 | 苏州凯祥生物科技有限公司 | A kind of resveratrol process for extracting, separating and purifying |
CN110616207A (en) * | 2019-11-11 | 2019-12-27 | 王喜 | Method for extracting superoxide dismutase from plant |
CN112646789A (en) * | 2020-12-31 | 2021-04-13 | 王磊 | Industrial production method for extracting superoxide dismutase from Shenzhou grass |
CN113088512A (en) * | 2021-04-15 | 2021-07-09 | 武汉理工大学 | Complex enzyme, and preparation method, regeneration method and application thereof |
CN114540322A (en) * | 2022-03-01 | 2022-05-27 | 中国海洋大学 | A kind of plant-derived amine oxidase and its extraction method and application |
-
2023
- 2023-01-12 CN CN202310040758.7A patent/CN116764157A/en active Pending
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4338398A (en) * | 1979-03-20 | 1982-07-06 | Kabushiki Kaisha Hayashibara Seibutsu Kagaku Kenkyujo | Immobilization of starch degrading enzymes |
CN110093380A (en) * | 2019-04-25 | 2019-08-06 | 苏州凯祥生物科技有限公司 | A kind of resveratrol process for extracting, separating and purifying |
CN110616207A (en) * | 2019-11-11 | 2019-12-27 | 王喜 | Method for extracting superoxide dismutase from plant |
CN112646789A (en) * | 2020-12-31 | 2021-04-13 | 王磊 | Industrial production method for extracting superoxide dismutase from Shenzhou grass |
CN113088512A (en) * | 2021-04-15 | 2021-07-09 | 武汉理工大学 | Complex enzyme, and preparation method, regeneration method and application thereof |
CN114540322A (en) * | 2022-03-01 | 2022-05-27 | 中国海洋大学 | A kind of plant-derived amine oxidase and its extraction method and application |
Non-Patent Citations (1)
Title |
---|
胡保卫: "《室内装饰用饰面刨花板VOC释放特性的研究》", 31 December 2020, 浙江科学技术出版社, pages: 280 - 281 * |
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