CN108164005A - A kind of method using Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol - Google Patents

A kind of method using Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol Download PDF

Info

Publication number
CN108164005A
CN108164005A CN201810037097.1A CN201810037097A CN108164005A CN 108164005 A CN108164005 A CN 108164005A CN 201810037097 A CN201810037097 A CN 201810037097A CN 108164005 A CN108164005 A CN 108164005A
Authority
CN
China
Prior art keywords
magnoliae officinalis
cortex magnoliae
crude enzyme
enzyme liquid
degradation
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201810037097.1A
Other languages
Chinese (zh)
Inventor
肖强
周秀梅
王雨雪
蒲圩
唐密
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Hubei University for Nationalities
Original Assignee
Hubei University for Nationalities
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Hubei University for Nationalities filed Critical Hubei University for Nationalities
Priority to CN201810037097.1A priority Critical patent/CN108164005A/en
Publication of CN108164005A publication Critical patent/CN108164005A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • C02F3/342Biological treatment of water, waste water, or sewage characterised by the microorganisms used characterised by the enzymes used
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • C02F2101/345Phenols

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Microbiology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Preparation Of Compounds By Using Micro-Organisms (AREA)

Abstract

The invention belongs to organic pollution processing technology fields, disclose a kind of method using Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol, the present invention is according to Phenols Catalyzed by Peroxidase in Nonaqueous Media class substance oxidation reaction principle, oxidants hydrogen peroxide is added in using artificial, organic matter NP is removed by Catalyzed Synthesis By Peroxidase, proposes a kind of method using Cortex Magnoliae Officinalis blade crude enzyme liquid degradation NP.Cortex Magnoliae Officinalis is transplanted as the medicinal plant of Chinese tradition extensively in Chinese Mountainous Region of Southwest Hubei, resourceful, and blade is easier to obtain;Enzymatic reaction has the characteristics that high catalytic efficiency, reaction condition be mild, controllability, the effect of decomposition NP can be greatly improved by decomposing NP using Cortex Magnoliae Officinalis blade crude enzyme liquid, it also has extraordinary elimination effect for some other phenolic compounds simultaneously, has at low cost, green, safe and pollution-free characteristic.

Description

A kind of method using Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol
Technical field
The invention belongs to organic pollution processing technology field more particularly to a kind of utilization Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyls The method of base phenol.
Background technology
Nonyl phenol (Nonylphenol), abbreviation NP.It is a kind of persistence organic pollutant, belongs in typical phenols and divide Chaff interferent is secreted, there is toxicity, refractory organics, bioconcentration and estrogenic activity, is the drop of nonyl phenol ethoxylate (NPE) Solve one of product.NPE is highly important nonionic surface active agent, and the textile industries process such as be widely used in printing and dyeing, clean. And except textile industry, NPE is also used as surfactant, detergent, is the environmental hormone that the whole world is generally acknowledged, such surface Activating agent is once entered in environment, ethyoxyl will be gone to react rapidly, resolves into the stronger environmental hormone-NP of toxicity. In recent years, to the demand cumulative year after year of NPE, incident is the discharge of a large amount of NP pollutants in China.NP has that " sperm kills The title of hand " can be absorbed by the body by skin so as to the endocrine, reproduction and immune system of interfering human and animal, can Promote Cells Proliferation of Human Breast Cancer, it seriously can be carcinogenic.Research shows that cell survival rate is notable in high dose NP and their mixture Declining, cell is more sensitive to NP in breeding, even if concentration is very low in environment, also great harmfulness.In recent years, NP existed In water body concentrations have year by year it is increased become Potential.Therefore, how to handle NP in water environment becomes urgent need to solve the problem.It is thick Piao, the purple Piao of alias, purple oil Piao, warm Piao etc., is Magnoliaceae, magnolia, is planted extensively as the medicinal plant of Chinese tradition It plants in Chinese Mountainous Region of Southwest Hubei.Traditional Cortex Magnoliae Officinalis planting industry mainly extracts pharmaceutically acceptable ingredient magnolol therein using Magnolia bark And honokiol.Magnolol and honokiol are the principal active components of Cortex Magnoliae Officinalis, are primarily present in bark, have it is anti-oxidant, The pharmacological actions such as anti-inflammatory, antitumor and antibacterial.Under normal circumstances, Cortex Magnoliae Officinalis, which is grown 15 years or more, can just strip dry hide and branch skin, add Work is into available Chinese medicine, and during long term growth, a large amount of Cortex Magnoliae Officinalis blades are not utilized effectively, and inventor passes through survey Fixed to confirm, peroxidase activity occupy forefront in Magnoliacea plant in Leaf of Magnolia officinalis.At present, the processing method of NP generally with Physical, chemical method, bioanalysis be representative three big treatment technologies, including burning method, active carbon adsorption, chemical method, Solvent extraction, microbial degradation method etc..It is a kind of relatively effective processing method using powder electroless plating, but drawback exists It is not thorough in removing, it can only be as the emergency method of sudden water pollution.In addition, Ti/SnO2—Sb2O5Electrode Electrocatalysis Degradation Method power consumption is big, complex procedures, economic benefit are low.O3 catalytic oxidation is a kind of place for effectively removing Organic Pollutants in Wastewater Reason method has synthesized a series of oxidation manganese material of different-shapes, phase, valence state and composition, applied to catalysis ozone at present Oxidative degradation phenolic comp ' ds pollution, but this method often brings secondary pollution, because of inherently a kind of noxious material of ozone, It is and expensive, it is difficult to promote the use of on a large scale.In recent years, the microbial method in bioanalysis is with its density height, processing equipment The features such as simple, is used widely, although this method safety, practical Sewage Environment is quite severe, and microorganism is to existence Condition has very big requirement, once in rugged environment, survival ability is necessarily restricted, and utilizes microbial degradation Phenols wastewater then needs large-scale culture microorganism and time-consuming, space is big, while phenol wastewater has murder by poisoning to microorganism and makees With.
In conclusion problem of the existing technology is:The processing method of NP is not thorough in the presence of removing at present, power consumption Greatly, complex procedures, economic benefit are low, expensive, it is difficult to which large-scale promotion uses;It is then needed using microbial degradation phenols wastewater It wants large-scale culture microorganism and time-consuming, space is big, while there are toxic actions to microorganism for phenol wastewater;Microbe survival Ability is necessarily restricted, it is difficult to realize the efficient process to a large amount of phenols wastewaters.And the biological Enzymology method for passing through plant source Phenol wastewater is removed, then it is possible to prevente effectively from these above-mentioned drawbacks.
Invention content
In view of the problems of the existing technology, Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol is utilized the present invention provides a kind of Method.
The invention is realized in this way a kind of method using Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol, described using thick The method of plain blade crude enzyme liquid degradation nonyl phenol includes:
Step 1 weighs ripe Cortex Magnoliae Officinalis leaf, according to 1:5 solid-liquid ratios are added in containing 2% polyvinylpyrrolidone and 2mmol/L The citrate phosphate buffer of ethylenediamine tetra-acetic acid, 4 DEG C of homogenate, 4 layers of filtered through gauze, filtrate is at 4 DEG C, 12000g centrifugations 20min abandons precipitation, retains supernatant;
Step 2 adds in ammonium sulfate in supernatant, reaches 20% saturation degree, precipitates overnight, and centrifugation discards precipitation, takes Supernatant continuously adds ammonium sulfate, takes the precipitation of 60%~90% saturation degree part, is thick enzyme after being dissolved with appropriate pure water Liquid;
Step 3 pipettes buffer solution, and control temperature of reaction system is 10~50 DEG C, and pH value is 3~11, adds in appropriate thick Enzyme solution makes a concentration of 10~20 μm of ol/L of NP in reaction system, adds in the H that molar concentration is NP10~100 times2O2Start reaction, Reaction time is 180min;Start 1min, 3min, 5min, 15min, 45min, 90min, 120min, 180min from upper in reaction It states and 1ml is sampled in reaction system, add in 2mL methanol and terminate reaction, realize degradation of the Cortex Magnoliae Officinalis blade crude enzyme liquid to NP;It is anti-terminating It answers and appropriate alum is added in liquid, shake up, 5000g centrifuges 10min after overnight precipitation;Supernatant after centrifugation crosses 0.22 μm of filter membrane Afterwards, it is detected using liquid chromatogram-mass spectrometer, mobile phase is 80% methanol/water, and Mass Spectrometer Method quasi-molecular ion peak corresponds to Relative molecular mass be 219.18.
Further, to there is the lemon of polyvinylpyrrolidone, ethylenediamine tetra-acetic acid in the step 1 Cortex Magnoliae Officinalis leaf extract Acid-phosphate buffer.
Further, the step 1 buffer solution for acetic acid-sodium acetate buffer, borax buffer solution, citric acid- Any one of phosphate buffer.
Further, the pH value is 7.
Further, the NP initial concentrations are 10~20 μm of ol/L.
Further, the temperature is room temperature.
Further, the reaction time is 180min.
Further, the enzyme addition is 10%.
The present invention adds in oxidant peroxidating according to Phenols Catalyzed by Peroxidase in Nonaqueous Media class substance oxidation reaction principle using artificial Hydrogen removes organic matter NP by Catalyzed Synthesis By Peroxidase, proposes a kind of method using Cortex Magnoliae Officinalis blade crude enzyme liquid degradation NP.Cortex Magnoliae Officinalis is made For Chinese tradition medicinal plant and transplanted extensively in Chinese Mountainous Region of Southwest Hubei, resourceful, blade is easier to obtain;Enzyme Promoting reaction has the characteristics that high catalytic efficiency, reaction condition be mild, controllability, can be with using Cortex Magnoliae Officinalis blade crude enzyme liquid decomposition NP The effect for decomposing NP is greatly improved, while it also has extraordinary elimination effect for some other phenolic compounds, has The characteristics such as at low cost, green, safe and pollution-free.This method is using plant peroxidases catalytic oxidation degradation NP, drop Solve efficient, and used raw material Cortex Magnoliae Officinalis blade easily obtains, have the advantages that efficiently, green, contaminate without two pollutions;And it can fill Divide using the Cortex Magnoliae Officinalis blade largely abandoned generated in Cortex Magnoliae Officinalis production link, provided for vast Cortex Magnoliae Officinalis farmer new Income source improves the overall economic efficiency of Cortex Magnoliae Officinalis plantation.
Description of the drawings
Fig. 1 is the method flow diagram provided in an embodiment of the present invention using Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol.
Fig. 2 is the removing situation schematic diagram of NP under different enzyme concentrations provided in an embodiment of the present invention.
Fig. 3 is NP NP surplus ratios schematic diagrames in 3 hours under condition of different temperatures provided in an embodiment of the present invention.
Fig. 4 is NP surplus ratio schematic diagrames in 3 hours under condition of different pH provided in an embodiment of the present invention.
Fig. 5 is that difference NP provided in an embodiment of the present invention and NP under the conditions of hydrogen peroxide molar concentration rate was remained in 3 hours Remaining rate schematic diagram.
Fig. 6 is NP surplus ratio schematic diagrames in 3 hours under the conditions of various concentration FA provided in an embodiment of the present invention.
Specific embodiment
In order to make the purpose , technical scheme and advantage of the present invention be clearer, with reference to embodiments, to the present invention It is further elaborated.It should be appreciated that the specific embodiments described herein are merely illustrative of the present invention, it is not used to Limit the present invention.
The application principle of the present invention is explained in detail below in conjunction with the accompanying drawings.
As shown in Figure 1, it is provided in an embodiment of the present invention using Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol method include with Lower step:
S101:Ripe Cortex Magnoliae Officinalis leaf is weighed, according to 1:5 solid-liquid ratios add in containing 2% polyvinylpyrrolidone (PVP-K30) and The citrate phosphate buffer (50mmol/L, pH 7.0) of 2mmol/L ethylenediamine tetra-acetic acids (EDTA), 4 DEG C of homogenate, 4 layers of gauze Filtering, at 4 DEG C, 12000g centrifugation 20min abandon precipitation, retain supernatant, as Cortex Magnoliae Officinalis blade zyme extract filtrate;
S102:Ammonium sulfate is added in above-mentioned supernatant, reaches 20% saturation degree, precipitates overnight, centrifugation (at 4 DEG C, 12000g centrifuges 15min), precipitation is discarded, takes supernatant, continuously adds ammonium sulfate, takes the heavy of 60%~90% saturation degree part It forms sediment, is Cortex Magnoliae Officinalis blade crude enzyme liquid after being dissolved with appropriate pure water.It is spare to measure enzymatic activity, the assay method of enzyme activity:Using more wound Wooden phenol method.It adds in 0.1ml enzyme solutions and starts reaction, the variation of OD values is recorded at wavelength 470nm, 30 DEG C.1 enzyme unit (U) definition For the enzyme amount needed for OD470 variations 0.1 per minute under determination condition;
S103:Buffer solution is pipetted, control temperature of reaction system is 10~50 DEG C, and pH value is 3~11, adds in appropriate thick enzyme Liquid makes a concentration of 10~20 μm of ol/L of NP in reaction system, adds in the H that molar concentration is 10~100 times of NP2O2Start reaction, Reaction time is 180min.Start 1min, 3min, 5min, 15min, 45min, 90min, 120min, 180min from upper in reaction It states and 1ml is sampled in reaction system, add in 2mL methanol and terminate reaction, that is, realize degradation of the Cortex Magnoliae Officinalis blade crude enzyme liquid to NP.It is terminating Appropriate alum is added in reaction solution, is shaken up, 5000g centrifuges 10min after overnight precipitation.Supernatant after centrifugation crosses 0.22 μm of filter membrane Afterwards, it is detected using liquid chromatogram-mass spectrometer, mobile phase is 80% methanol/water, and Mass Spectrometer Method quasi-molecular ion peak corresponds to Relative molecular mass be 219.18.
The application principle of the present invention is further described with reference to specific embodiment.
The influence that 1 Cortex Magnoliae Officinalis blade crude enzyme liquid difference enzyme concentration of embodiment degrades to NP.
Each reaction system is respectively placed in the reagent bottle of 6 numbers, in total 6 reagent bottles, is added in each reagent bottle Enter pH value be 7 phosphoric acid-citrate buffer solution, add a concentration of 22mg/L 40 μ L of NP solution, be then respectively adding enzyme solution 100U, 200U, 500U, 800U, 1200U, the common 20mL of reaction system take 1mL samples to add in 2mL methanol as blank control, Xiang Qi It is middle to add in clean magnetic stir bar.Reagent bottle is respectively placed in thermostat water bath under room temperature and is stirred, according to NP moles it is dense Degree is than being 20:1 add in hydrogenperoxide steam generator reaction 180min, in reaction 1min, 3min, 5min, 15min, 45min, 90min, 120min, 180min take 1mL reaction mixtures, add in 2mL methanol and terminate reaction, that is, realize drop of the Cortex Magnoliae Officinalis blade crude enzyme liquid to NP Solution.Appropriate alum is added in reaction solution terminating, is shaken up, 5000g centrifuges 10min after overnight precipitation.Supernatant sample after centrifugation Product detected after taking out 0.22 μm of film in liquid phase-mass spectrometer, ultraviolet detection wavelength be 220nm, Mass Spectrometer Method peak pair The relative molecular mass answered is about 219.18, and mobile phase is 80% methanol/water.Obtained concrete outcome is as shown in Fig. 2, from figure As can be seen that when reaction system enzyme concentration is 60U/ml, NP degradation rate highests are 100%, cannot be complete less than this enzyme concentration Clear all.
Influence of 2 condition of different temperatures of embodiment to Cortex Magnoliae Officinalis blade crude enzyme liquid degradation NP.
6 reagent bottles are taken, phosphoric acid-appropriate citrate buffer solution that pH value is 7 is added in each reagent bottle, adds NP Solution, make final concentration of 22mg/L then add in enzyme solution, make total volume for 20mL (insufficient section, using pH value as 7 phosphoric acid- Citrate buffer solution supplements), mixing takes 1mL mixed liquors, adds in 2mL methanol as blank control, magnetic force is added in mixed liquor Stirrer.Reagent bottle is respectively placed in water temperature as 10 DEG C, 20 DEG C, 25 DEG C, 30 DEG C, 40 DEG C, 50 DEG C of temperature constant magnetic stirring water-bath It is stirred in pot, is 20 according to NP molar concentration rates:1 add in hydrogenperoxide steam generator, react 180min, in reaction 1min, 3min, 5min, 15min, 45min, 90min, 120min, 180min take 1mL reaction mixtures respectively from reaction mixture, add in 2mL Methanol terminates reaction, that is, realizes degradation of the Cortex Magnoliae Officinalis blade crude enzyme liquid to NP.Obtained concrete outcome is as shown in figure 3, can from Fig. 3 To find out, when temperature is in 10 DEG C~50 DEG C of ranges, reacted by 3 hours, NP is completely removed, this shows that the clearance technique exists In the annual overwhelming majority time, it can achieve the effect that fully erased NP at room temperature, there is good Acclimation temperature range.
Influences of the embodiment 3pH to Cortex Magnoliae Officinalis blade crude enzyme liquid degradation NP.
Each reaction system is respectively placed in the reagent bottles of 9 numbers, in total 9 reagent bottles, with acetic acid-sodium acetate, Phosphoric acid-citric acid, borate buffer solution control pH value of reaction system for 3,4,5,6,7,8,9,10,11, add a concentration of The NP solution of 22mg/L and then enzyme solution being added in, common 20mL takes 1mL reaction mixtures addition 2mL methanol as blank control, to Wherein add in clean magnetic stir bar.Reagent bottle is respectively placed in magnetic stirring apparatus and is reacted at normal temperatures, according to NP molar concentration rates are 20:1 add in hydrogen peroxide start reaction, in reaction 1min, 3min, 5min, 15min, 45min, 90min, 120min, 180min take 1mL reaction mixtures, add in 2mL methanol and terminate reaction, that is, realize Cortex Magnoliae Officinalis blade crude enzyme liquid pair The degradation of NP.Obtained result is specific as shown in figure 4, it can be seen from the figure that almost can be by for 3~11, NP in pH value Fully erased, wherein pH more low reactions are rapider, it can be seen that, Cortex Magnoliae Officinalis peroxidase has very wide pH threshold values, at sewage Reason downstream is easy to apply.
4 difference NP of embodiment and NP surplus ratios in 3 hours under the conditions of hydrogen peroxide molar concentration rate.
Each reaction system is respectively placed in the reagent bottle of 5 numbers, in total 5 reagent bottles, is added in each reagent bottle Enter pH value be 7 phosphoric acid-citrate buffer solution, add a concentration of 22mg/L NP solution then add in enzyme solution, common 20mL, 1mL reaction mixtures is taken to add in 2mL methanol as blank control, add in clean magnetic stir bar thereto.It rubs according to NP Your concentration ratio is 2:1、5:1、10:1、20:1、30:1 adds in hydrogenperoxide steam generator, reacts 180min under room temperature, in reaction 1min, 3min, 5min, 15min, 45min, 90min, 120min, 180min take reaction mixture 1mL, add in 2mL methanol and terminate reaction, Realize degradation of the Cortex Magnoliae Officinalis blade crude enzyme liquid to NP.Obtained concrete outcome as shown in figure 5, it can be seen from the figure that when NP with Hydrogen peroxide molar concentration rate is 1:When 20, NP degradation rates it is most fast and can basically reach it is fully erased, although other concentration ratios Degradation rate is slightly slow, but as a child can also basically reach 3 fully erased.
NP surplus ratios in 3 hours under the conditions of 5 various concentration humic acid (FA) of embodiment.
Each reaction system is respectively placed in the reagent bottle of 5 numbers, in total 5 reagent bottles, is added in each reagent bottle Enter phosphoric acid-citrate buffer solution that pH value is 7, the NP solution for adding a concentration of 22mg/L, then add in enzyme solution and FA is molten Liquid, FA concentration is respectively 0mg/L, 2mg/L, 5mg/L, 10mg/L, 50mg/L in reaction system, and common 20mL takes 1mL reaction mixing Liquid adds in 2mL methanol as blank control, adds in clean magnetic stir bar thereto.It is 20 according to NP molar concentration rates:1 Add in hydrogenperoxide steam generator, react 180min under room temperature, in reaction 1min, 3min, 5min, 15min, 45min, 90min, 120min, 180min take 1mL reaction mixtures, add in 2mL methanol and terminate reaction, that is, realize drop of the Cortex Magnoliae Officinalis blade crude enzyme liquid to NP Solution.Obtained concrete outcome is as shown in fig. 6, it can be seen from the figure that the FA solution of various concentration has the rate for removing NP It influences, reaction rate is slack-off, but remains to after 180min to reach basic removing, illustrates that Cortex Magnoliae Officinalis peroxidase is more stable, clearly It is not very big that division result is influenced by the organic matter FA of 50mg/L.
The foregoing is merely illustrative of the preferred embodiments of the present invention, is not intended to limit the invention, all essences in the present invention All any modification, equivalent and improvement made within refreshing and principle etc., should all be included in the protection scope of the present invention.

Claims (8)

  1. A kind of 1. method using Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol, which is characterized in that described to utilize the thick enzyme of Cortex Magnoliae Officinalis blade The method of liquid degradation nonyl phenol includes:
    Step 1 weighs ripe Cortex Magnoliae Officinalis leaf, according to 1:5 solid-liquid ratios are added in containing 2% polyvinylpyrrolidone and 2mmol/L second two The citrate phosphate buffer of amine tetraacethyl, 4 DEG C of homogenate, 4 layers of filtered through gauze, filtrate is at 4 DEG C, 12000g centrifugation 20min, Precipitation is abandoned, retains supernatant;
    Step 2 adds in ammonium sulfate in supernatant, reaches 20% saturation degree, precipitates overnight, and centrifugation discards precipitation, takes supernatant Liquid continuously adds ammonium sulfate, takes the precipitation of 60%~90% saturation degree part, is crude enzyme liquid after being dissolved with appropriate pure water;
    Step 3 pipettes buffer solution, and control temperature of reaction system is 10~50 DEG C, and pH value is 3~11, adds in appropriate thick enzyme Liquid makes a concentration of 10~20 μm of ol/L of NP in reaction system, adds in the H that molar concentration is NP10~100 times2O2Start reaction, instead It is 180min between seasonable;Start 1min, 3min, 5min, 15min, 45min, 90min, 120min, 180min from above-mentioned in reaction 1ml is sampled in reaction system, 2mL methanol is added in and terminates reaction, realizes degradation of the Cortex Magnoliae Officinalis blade crude enzyme liquid to NP;It is reacted terminating Appropriate alum is added in liquid, is shaken up, 5000g centrifuges 10min after overnight precipitation;After supernatant after centrifugation crosses 0.22 μm of filter membrane, It is detected using liquid chromatography mass combined instrument, mobile phase is 80% methanol/water, and Mass Spectrometer Method quasi-molecular ion peak is corresponding opposite Molecular mass is 219.18.
  2. 2. the method for Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol is utilized as described in claim 1, which is characterized in that the step It is citric acid-the phosphate buffer for having polyvinylpyrrolidone, ethylenediamine tetra-acetic acid in one Cortex Magnoliae Officinalis leaf extract.
  3. 3. the method for Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol is utilized as described in claim 1, which is characterized in that the step One buffer solution is any one of acetic acid-sodium acetate buffer, borax buffer solution, citric acid-phosphate buffer.
  4. 4. the method for Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol is utilized as described in claim 1, which is characterized in that the pH value It is 7.
  5. 5. the method for Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol is utilized as described in claim 1, which is characterized in that at the beginning of the NP Begin a concentration of 10~20 μm of ol/L.
  6. 6. the method for Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol is utilized as described in claim 1, which is characterized in that the temperature For room temperature.
  7. 7. the method for Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol is utilized as described in claim 1, which is characterized in that the reaction Time is 180min.
  8. 8. the method for Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol is utilized as described in claim 1, which is characterized in that the enzyme adds Enter amount for 60U/ml.
CN201810037097.1A 2018-01-15 2018-01-15 A kind of method using Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol Pending CN108164005A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810037097.1A CN108164005A (en) 2018-01-15 2018-01-15 A kind of method using Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810037097.1A CN108164005A (en) 2018-01-15 2018-01-15 A kind of method using Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol

Publications (1)

Publication Number Publication Date
CN108164005A true CN108164005A (en) 2018-06-15

Family

ID=62514462

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810037097.1A Pending CN108164005A (en) 2018-01-15 2018-01-15 A kind of method using Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol

Country Status (1)

Country Link
CN (1) CN108164005A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109234353A (en) * 2018-09-14 2019-01-18 暨南大学 Microalgae is effectively degraded the experimental method of nonyl phenol

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH01222778A (en) * 1988-03-02 1989-09-06 Nitto Denko Corp Peroxidase and production thereof
JP2002018480A (en) * 2000-07-10 2002-01-22 Idemitsu Kosan Co Ltd Method for cleaning water contaminated by refractory material
CN103055464A (en) * 2012-12-14 2013-04-24 南京林业大学 Method for degrading octyl phenol by utilizing laccase
CN104017783A (en) * 2014-05-13 2014-09-03 安徽味仙食品有限公司 Method for extracting catalase from crop
CN106006994A (en) * 2016-05-20 2016-10-12 佛山市聚成生化技术研发有限公司 Method for degrading bisphenol A by virtue of crude enzyme liquid of lentinula edodes

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH01222778A (en) * 1988-03-02 1989-09-06 Nitto Denko Corp Peroxidase and production thereof
JP2002018480A (en) * 2000-07-10 2002-01-22 Idemitsu Kosan Co Ltd Method for cleaning water contaminated by refractory material
CN103055464A (en) * 2012-12-14 2013-04-24 南京林业大学 Method for degrading octyl phenol by utilizing laccase
CN104017783A (en) * 2014-05-13 2014-09-03 安徽味仙食品有限公司 Method for extracting catalase from crop
CN106006994A (en) * 2016-05-20 2016-10-12 佛山市聚成生化技术研发有限公司 Method for degrading bisphenol A by virtue of crude enzyme liquid of lentinula edodes

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
李鱼等: "《表层沉积物中重金属与雌激素的污染控制研究》", 30 June 2009, 辽宁教育出版社 *
洪健等: "厚朴过氧化物酶的纯化、性质及清除双酚A特性研究 ", 《天然产物研究与开发》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109234353A (en) * 2018-09-14 2019-01-18 暨南大学 Microalgae is effectively degraded the experimental method of nonyl phenol
CN109234353B (en) * 2018-09-14 2021-10-29 暨南大学 Experimental method for effectively degrading nonyl phenol by microalgae

Similar Documents

Publication Publication Date Title
Yang et al. Degradation and detoxification of the triphenylmethane dye malachite green catalyzed by crude manganese peroxidase from Irpex lacteus F17
Zhang et al. Degradation of chlorophenols catalyzed by laccase
AU2011268480B2 (en) Method for rapid treatment of waste water and a composition thereof
Lu et al. Simultaneously enhanced removal of PAHs and nitrogen driven by Fe2+/Fe3+ cycle in constructed wetland through automatic tidal operation
Shi et al. Denitrification during composting: Biochemistry, implication and perspective
Sha et al. Minerals loaded with oxygen nanobubbles mitigate arsenic translocation from paddy soils to rice
Mei et al. A novel membrane-aerated biofilter for the enhanced treatment of nitroaniline wastewater: Nitroaniline biodegradation performance and its influencing factors
CN112047491A (en) Method for removing phenolic substances in phenol aqueous solution by tyrosinase-metal organic framework compound
CN103638545B (en) A kind of microbial deodorant and preparation method thereof
Razaviarani et al. Denitrification of nitric oxide using hollow fiber membrane bioreactor; effect of nitrate and nitric oxide loadings on the reactor performance and microbiology
CN108002511A (en) A kind of method for treating water that single persulfate oxidation degradable organic pollutant is catalyzed using manganese sand
Zhu et al. Biodegradation of lincomycin in wastewater by two-level bio-treatment using chloroperoxidase and activated sludge: degradation route and eco-toxicity evaluation
CN108164005A (en) A kind of method using Cortex Magnoliae Officinalis blade crude enzyme liquid degradation nonyl phenol
Gao et al. Deciphering microbial syntrophic mechanisms for simultaneous removal of nitrate and Cr (VI) by Mn@ Corn cob immobilized bioreactor: performance, enhancement mechanisms and community assembly
Cao et al. The application of post-denitrification fixed biofilm reactor for polishing secondary effluent: Nitrate removal, soluble microbial products and micropollutants biotransformation
Jiang et al. Pilot-scale and mechanistic study of the degradation of typical odors and organic compounds in drinking water by a combined UV/H2O2-BAC process
Borraccino et al. Abiotic transformation of catechol and 1-naphthol in aqueous solution—Influence of environmental factors
Liu et al. Application of the sulfur-siderite composite filler: A case study of augmented performance and synergistic mechanism for low C/N wastewater treatment in constructed wetland
Zhao et al. Biotransformation of hydroxylaminobenzene and aminophenol by Pseudomonas putida 2NP8 cells grown in the presence of 3-nitrophenol
Xing et al. Removal of organic phosphorus and formaldehyde in glyphosate wastewater by CWO and the lime-catalyzed formose reaction
CN108164004A (en) A kind of method that bisphenol-A is removed using Michelia maudiae leaf crude enzyme liquid
CN104761043B (en) The method of quinones catalysis potassium permanganate degraded organic pollutants
Colarieti et al. Toxicity attenuation of olive mill wastewater in soil slurries
CN103130318A (en) Method of preparing synthesis gas by phenolic wastewater
Wang et al. Mechanism and process optimization for H2S removal by plant-derived deodorant

Legal Events

Date Code Title Description
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20180615