CN106248604A - A kind of measure the method for laccase activity in soil - Google Patents

A kind of measure the method for laccase activity in soil Download PDF

Info

Publication number
CN106248604A
CN106248604A CN201610528833.4A CN201610528833A CN106248604A CN 106248604 A CN106248604 A CN 106248604A CN 201610528833 A CN201610528833 A CN 201610528833A CN 106248604 A CN106248604 A CN 106248604A
Authority
CN
China
Prior art keywords
laccase
solution
soil
abts
absorbance
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.)
Granted
Application number
CN201610528833.4A
Other languages
Chinese (zh)
Other versions
CN106248604B (en
Inventor
任大军
何小勇
张淑琴
郭舒悦
刘海
龚洁
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.)
Wuhan University of Science and Engineering WUSE
Wuhan University of Science and Technology WHUST
Original Assignee
Wuhan University of Science and Engineering WUSE
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 Wuhan University of Science and Engineering WUSE filed Critical Wuhan University of Science and Engineering WUSE
Priority to CN201610528833.4A priority Critical patent/CN106248604B/en
Publication of CN106248604A publication Critical patent/CN106248604A/en
Application granted granted Critical
Publication of CN106248604B publication Critical patent/CN106248604B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/17Systems in which incident light is modified in accordance with the properties of the material investigated
    • G01N21/25Colour; Spectral properties, i.e. comparison of effect of material on the light at two or more different wavelengths or wavelength bands
    • G01N21/31Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry
    • G01N21/33Investigating relative effect of material at wavelengths characteristic of specific elements or molecules, e.g. atomic absorption spectrometry using ultraviolet light
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N1/00Sampling; Preparing specimens for investigation
    • G01N1/28Preparing specimens for investigation including physical details of (bio-)chemical methods covered elsewhere, e.g. G01N33/50, C12Q
    • G01N1/34Purifying; Cleaning
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/75Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N21/00Investigating or analysing materials by the use of optical means, i.e. using sub-millimetre waves, infrared, visible or ultraviolet light
    • G01N21/75Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated
    • G01N21/77Systems in which material is subjected to a chemical reaction, the progress or the result of the reaction being investigated by observing the effect on a chemical indicator
    • G01N2021/7769Measurement method of reaction-produced change in sensor

Landscapes

  • Physics & Mathematics (AREA)
  • Health & Medical Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Pathology (AREA)
  • Analytical Chemistry (AREA)
  • Biochemistry (AREA)
  • General Health & Medical Sciences (AREA)
  • General Physics & Mathematics (AREA)
  • Immunology (AREA)
  • Engineering & Computer Science (AREA)
  • Spectroscopy & Molecular Physics (AREA)
  • Plasma & Fusion (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Biomedical Technology (AREA)
  • Molecular Biology (AREA)
  • Measuring Or Testing Involving Enzymes Or Micro-Organisms (AREA)

Abstract

The invention belongs to agrology and environmental science, be specifically related to a kind of measure the method for laccase activity in soil, it is characterised in that it comprises the following steps: the pretreatment of (1) soil;(2) preparation of reverse micelle system;(3) ABTS number of free radical and the linear equation of absorbance relation are solved;(4) ABTS colorimetric method for determining laccase activity.The present invention uses reverse micelle to extract the laccase in soil, reverse micelle is suitable for the purification of biomacromolecule, and in when laccase contacts with reverse micelle, laccase can enter reverse micelle " pond ", can effectively ensure that the activity of laccase during extraction, present invention laccase in acetic acid sodium-acetate buffer back extraction reverse micelle, buffer solution can make laccase be maintained in a metastable environment and make the enzyme of laccase live to reach optimum degree, in addition the laccase activity detection technique inverse micellar solution that is easy to be quick and that use that the present invention uses can be reused, it is suitable for batch detection.

Description

A kind of measure the method for laccase activity in soil
Technical field
The invention belongs to agrology and environmental science, be specifically related to a kind of measure the method for laccase activity in soil.
Background technology
Laccase is a kind of protein being combined with multiple copper ion, belongs to covellite oxidase, and laccase utilizes molecular oxygen catalysis The by-product of oxidation reaction is water, belongs to environment-friendly type enzyme, and owing to the catalysis organic substrates of laccase is relatively broad so that paint Enzyme has become a kind of multifunctional enzyme with many-sided good characteristic, and its application relates to multiple subjects such as biology, chemistry and environment Field, has had increasing scholar to start with laccase treatment by the soil of Organic Pollution, and the enzyme of laccase has been lived It is the key factor affecting Organic substance disposal ability, therefore measures the Changing Pattern of laccase activity in soil and seem and be even more important.
Reverse micelle is a kind of direction micelle that surfactant is formed in organic solvent, and surfactant is at organic solvent Middle can form the hydrophilic group hydrophobic group polarity kernel with multimolecules reaction model outwardly inwardly, in the polarity of reverse micelle " pond " phenomenon can be formed, due to the existence of " pond " phenomenon so that reverse micelle can be the most molten after karyolysis suitable quantity of water Solve some biological substances, such as protein, nucleic acid and aminoacid etc., due between these biological substance and organic solvents across anti-glue Group so that biological substance directly will not contact with organic solvent, simultaneously the activity of the biological substance that the microenvironment in pond is protected again. Using reverse micelle extraction biological substance, not only extraction yield is high, and extraction has selectivity, additionally it is possible to keep biological substance in extraction process Activity.
Summary of the invention
It is an object of the invention to provide and a kind of can effectively measure the method for laccase activity in soil.
For achieving the above object, the present invention adopts the technical scheme that, a kind of measures the method for laccase activity in soil, its It is characterised by that it comprises the following steps:
(1) pretreatment of soil:
After pedotheque to be measured is fetched, put in fume hood and air-dry, then by after air-dried ground 20 mesh sieves of soil Standby;
(2) preparation of reverse micelle system:
Surfactant AOT is dissolved in isobutyltrimethylmethane., is made into the AOT/ isobutyltrimethylmethane. that concentration is 0.05~0.08g/mL and mixes Close liquid, in AOT/ isobutyltrimethylmethane. mixed liquor, then add KCl and Acetic acid-sodium acetate buffer, then mixed liquor is carried out ultrasonic, Until surfactant AOT is completely dissolved, and mixed solution clear, prepare reverse micelle system;
(3) ABTS number of free radical and the linear equation of absorbance relation are solved:
The ABTS being separately added into 0mL, 0.5mL, 1mL, 1.5mL, 2mL, 2.5mL in the color-comparison tube of 6 25mL is molten Liquid, the concentration of ABTS solution is 4mmol/L, then 6 equipped with the color-comparison tube of ABTS solution in each to add 1mL laccase molten Liquid, the enzyme of laccase solution is lived as 1U/mL, then all adds distilled water in 6 color-comparison tubes to 25mL scale, then by 6 Color-comparison tube is placed one hour after all shaking up, and after placing one hour, use ultraviolet spectrophotometer is under the wavelength of 420nm Measure the absorbance of solution in 6 color-comparison tubes and draw standard curve, obtain in color-comparison tube mixed solution A BTS from By base concentration and the linear equation of absorbance relation:
Y=aX+b,
In formula: Y is the concentration (μm ol/L) of ABTS free radical;X is absorbance (A);A, b are constant to be asked;
(4) ABTS colorimetric method for determining laccase activity:
Soil after grinding weighs 1.0~3.0g and puts in centrifuge tube, and adds 10mL reverse micelle body in centrifuge tube System, is then put into centrifuge tube shaking table concussion 1~2 hours, after having shaken, is placed on by centrifuge tube on centrifuge with 4000r/ The centrifugation 15~30min of min, puts in the cleanest centrifuge tube standby by the solution taking-up being in upper strata after being centrifuged With, the reverse micelle system that the soil being in lower floor continuously adds 10mL repeats above-mentioned concussion and centrifugally operated, repeats two Secondary, and each sample does three parallel samples;
Add isopyknic Acetic acid-sodium acetate buffer to being in the solution on upper strata of taking-up, and shake 15~20 points Clock, is then placed in a centrifuge mixed solution, with the centrifugation 30 of 4000r/min~40 minutes, takes out after centrifugal layering Be in the laccase solution of lower floor, it is achieved the back extraction of laccase, add in cuvette the laccase solution after 1.5mL back extraction and The ABTS solution of 1.5mL, wherein the concentration of ABTS solution is 0.5mmol/L, then utilizes ultraviolet spectrophotometer 420nm's Under wavelength, in 2 minutes, measure the absorbance of mixed solution in a cuvette every 15s, obtain mixed solution in cuvette Absorbance and the linear equation of time relationship:
S=cT+d,
In formula: S is absorbance (A);T is time (min);C, d are constant to be asked;
The computing formula of soil laccase activity to be measured is as follows:
In formula: e is ABTS free radical and the slope of the linear equation of absorbance relation, i.e. e is equal to trying to achieve in step (3) Constant a;F is the slope of absorbance and the linear equation of time relationship, i.e. f is equal to the constant c tried to achieve in step (4);V1For instead The volume (mL) of laccase solution after extraction;V2For joining the volume (mL) of laccase solution after back extraction in cuvette;M is soil Quality (g);V3For adding the volume (mL) of ABTS solution in cuvette.
Further, the concentration of the KCl solution of described addition is 0.1mol/L, and addition is that the AOT/ isobutyltrimethylmethane. of every 10mL mixes Close the KCl solution adding 0.5~0.8ml in liquid.
Further, the pH of the Acetic acid-sodium acetate buffer of described addition is 2.0~6.0, and concentration is 0.1mol/L.
The present invention compared with prior art, has the following advantages and effect:
1, the present invention uses reverse micelle to extract the laccase in soil, and reverse micelle is suitable for the purification of biomacromolecule, works as laccase In when contacting with reverse micelle, laccase can enter reverse micelle " pond ", it is possible to the activity of laccase during effective guarantee extraction.
2, present invention laccase in Acetic acid-sodium acetate buffer back extraction reverse micelle, buffer solution can make laccase protect Hold in a metastable environment and make the enzyme of laccase live and reach optimum degree.
3, the laccase activity detection technique that the present invention uses inverse micellar solution that is easy to be quick and that use can be reused, It is suitable for batch detection.
Accompanying drawing explanation
Fig. 1 is ABTS free radical and the linear relationship chart of absorbance relation in embodiment 1;
Fig. 2 is the linear relationship chart in embodiment 1 for absorbance with time relationship;
Fig. 3 is ABTS free radical and the linear relationship chart of absorbance relation in embodiment 2;
Fig. 4 is absorbance and the linear relationship chart of time relationship in embodiment 2;
Wherein, R2For linear correlation index.
Detailed description of the invention
Below in conjunction with detailed description of the invention, the inventive method is further described, not the limit to its protection domain System.
Embodiment 1
A kind of measure the method for laccase activity in soil, it is characterised in that it comprises the following steps:
(1) pretreatment of soil:
Gather brown calcareous soil topsoil and put in fume hood air-dried, then by after air-dried ground 20 mesh sieves of soil Standby;
(2) preparation of reverse micelle system:
Surfactant AOT is dissolved in isobutyltrimethylmethane., is made into the AOT/ isobutyltrimethylmethane. mixed liquor that concentration is 0.05g/mL, so After in AOT/ isobutyltrimethylmethane. mixed liquor, add KCl and Acetic acid-sodium acetate buffer, then mixed liquor is carried out ultrasonic, until table Face activating agent AOT is completely dissolved, and mixed solution clear, prepares reverse micelle system;
(3) ABTS number of free radical and the linear equation of absorbance relation are solved:
The ABTS being separately added into 0mL, 0.5mL, 1mL, 1.5mL, 2mL, 2.5mL in the color-comparison tube of 6 25mL is molten Liquid, the concentration of ABTS solution is 4mmol/L, then 6 equipped with the color-comparison tube of ABTS solution in each to add 1mL laccase molten Liquid, the enzyme of laccase solution is lived as 1U/mL, then all adds distilled water in 6 color-comparison tubes to 25mL scale, then by 6 Color-comparison tube is placed one hour after all shaking up, and after placing one hour, use ultraviolet spectrophotometer is under the wavelength of 420nm Measure the absorbance of solution in 6 color-comparison tubes and draw standard curve (see Fig. 1), obtaining mixed solution in color-comparison tube ABTS number of free radical and the linear equation of absorbance relation:
Y=aX+b,
In formula: Y is the concentration (μm ol/L) of ABTS free radical;X is absorbance (A);A, b are the constant tried to achieve, and a= 192.1, b=2.950, linear correlation index R2=0.998;
(4) ABTS colorimetric method for determining laccase activity:
Soil after grinding weighs 1.0g and puts in centrifuge tube, and adds 10mL reverse micelle system in centrifuge tube, so After centrifuge tube be put into shaking table shake 1 hour, after having shaken, centrifuge tube is placed on centrifuge the speed with 4000r/min The centrifugal 15min of degree, puts in the cleanest centrifuge tube standby by the solution taking-up being in upper strata after being centrifuged, will be in down The soil of layer continuously adds the reverse micelle system of 10mL and repeats above-mentioned concussion and centrifugally operated, is repeated twice, and each Sample does three parallel samples;
It is in the solution on upper strata adds isopyknic Acetic acid-sodium acetate buffer to take out, and shake 15 minutes, so After mixed solution is placed in a centrifuge, with the centrifugation 30 minutes of 4000r/min, take out after centrifugal layering and be in lower floor Laccase solution, it is achieved the back extraction of laccase, adds the laccase solution after 1.5mL back extraction and the ABTS of 1.5mL in cuvette Solution, wherein the concentration of ABTS solution is 0.5mmol/L, then utilize ultraviolet spectrophotometer under the wavelength of 420nm, 2 Measuring the absorbance of mixed solution in a cuvette every 15s in minute, with absorbance as vertical coordinate, the time is that abscissa is painted Absorption curve processed (Fig. 2), obtains the linear equation of mixed solution absorbance and time relationship in cuvette:
S=cT+d,
In formula: S is absorbance (A);T is time (min);C, d are the constant tried to achieve, and c=0.358, d=0.058, line Property index of correlation R2=0.999;
In soil, the enzyme of laccase is lived and is calculated as follows:
In formula: e is ABTS free radical and the slope of the linear equation of absorbance relation, i.e. e is equal to trying to achieve in step (3) Constant a, e=192.1;F is the slope of absorbance and the linear equation of time relationship, i.e. f is equal to the constant tried to achieve in step (4) C, f=0.358;V1For the volume (mL) of laccase solution, V after back extraction1=30mL;V2For joining in cuvette after back extraction The volume (mL) of laccase solution, V2=1.5mL;M is soil quality (g), m=1g;V3For adding as ABTS solution in cuvette Volume (mL), V3=1.5mL.
Further, the concentration of the KCl solution of described addition is 0.1mol/L, and addition is that the AOT/ isobutyltrimethylmethane. of every 10mL mixes Close the KCl solution adding 0.5~0.8ml in liquid.
Further, the pH of the Acetic acid-sodium acetate buffer of described addition is 2.0~6.0, and concentration is 0.1mol/L.
Embodiment 2
A kind of measure the method for laccase activity in soil, it is characterised in that it comprises the following steps:
(1) pretreatment of soil:
Air-dry the Subtropical Red Soil topsoil gathered, and soil is ground air-dry after cross after 20 mesh sieves standby;
(2) preparation of reverse micelle system:
Surfactant AOT is dissolved in isobutyltrimethylmethane., is made into the AOT/ isobutyltrimethylmethane. mixed liquor that concentration is 0.08g/mL, so After in AOT/ isobutyltrimethylmethane. mixed liquor, add KCl and Acetic acid-sodium acetate buffer, then mixed liquor is carried out ultrasonic, until table Face activating agent AOT is completely dissolved, and mixed solution clear, prepares reverse micelle system;
(3) ABTS number of free radical and the linear equation of absorbance relation are solved:
The ABTS being separately added into 0mL, 0.5mL, 1mL, 1.5mL, 2mL, 2.5mL in the color-comparison tube of 6 25mL is molten Liquid, the concentration of ABTS solution is 4mmol/L, then 6 equipped with the color-comparison tube of ABTS solution in each to add 1mL laccase molten Liquid, the enzyme of laccase solution is lived as 1U/mL, then all adds distilled water in 6 color-comparison tubes to 25mL scale, then by 6 Color-comparison tube is placed one hour after all shaking up, and after placing one hour, use ultraviolet spectrophotometer is under the wavelength of 420nm Measure the absorbance of solution in 6 color-comparison tubes and draw standard curve (see Fig. 3), obtaining mixed solution in color-comparison tube ABTS number of free radical and the linear equation of absorbance relation:
Y=aX+b,
In formula: Y is the concentration (μm ol/L) of ABTS free radical;X is absorbance (A);A, b are the constant tried to achieve, and a= 193.7, b=0.105, linear correlation index R2=0.999;
(4) ABTS colorimetric method for determining laccase activity:
Soil after grinding weighs 2.0g and puts in centrifuge tube, and adds 10mL reverse micelle system in centrifuge tube, so After centrifuge tube be put into shaking table shake 2 hours, after having shaken, centrifuge tube is placed on centrifuge the speed with 4000r/min The centrifugal 30min of degree, puts in the cleanest centrifuge tube standby by the solution taking-up being in upper strata after being centrifuged, will be in down The soil of layer continuously adds the reverse micelle system of 10mL and repeats above-mentioned concussion and centrifugally operated, is repeated twice, and each Sample does three parallel samples;
It is in the solution on upper strata adds isopyknic Acetic acid-sodium acetate buffer to take out, and shake 20 minutes, so After mixed solution is placed in a centrifuge, with the centrifugation 40 minutes of 4000r/min, take out after centrifugal layering and be in lower floor Laccase solution, it is achieved the back extraction of laccase, adds the laccase solution after 1.5mL back extraction and the ABTS of 1.5mL in cuvette Solution, wherein the concentration of ABTS solution is 0.5mmol/L, then utilize ultraviolet spectrophotometer under the wavelength of 420nm, 2 Measuring the absorbance of mixed solution in a cuvette every 15s in minute, with absorbance as vertical coordinate, the time is that abscissa is painted Absorption curve processed (Fig. 4), obtains the linear equation of mixed solution absorbance and time relationship in cuvette:
S=cT+d,
In formula: S is absorbance (A);T is time (min);C, d are the constant tried to achieve, and c=0.666, d=0.107, line Property index of correlation R2=0.999;
In soil, the enzyme of laccase is lived and is calculated as follows:
In formula: e is ABTS free radical and the slope of the linear equation of absorbance relation, i.e. e is equal to trying to achieve in step (3) Constant a, e=193.7;F is the slope of absorbance and the linear equation of time relationship, i.e. f is equal to the constant tried to achieve in step (4) C, f=0.666;V1For the volume (mL) of laccase solution, V after back extraction1=30mL;V2For joining in cuvette after back extraction The volume (mL) of laccase solution, V2=1.5mL;M is soil quality (g), m=2g;V3For adding as ABTS solution in cuvette Volume (mL), V3=1.5mL.
Further, the concentration of the KCl solution of described addition is 0.1mol/L, and addition is that the AOT/ isobutyltrimethylmethane. of every 10mL mixes Close the KCl solution adding 0.5~0.8ml in liquid.
Further, the pH of the Acetic acid-sodium acetate buffer of described addition is 2.0~6.0, and concentration is 0.1mol/L.

Claims (3)

1. one kind measures the method for laccase activity in soil, it is characterised in that it comprises the following steps:
(1) pretreatment of soil:
After pedotheque to be measured is fetched, put in fume hood and air-dry, then by standby after air-dried ground 20 mesh sieves of soil;
(2) preparation of reverse micelle system:
Surfactant AOT is dissolved in isobutyltrimethylmethane., is made into the AOT/ isobutyltrimethylmethane. mixed liquor that concentration is 0.05~0.08g/mL, Then in AOT/ isobutyltrimethylmethane. mixed liquor, add KCl and Acetic acid-sodium acetate buffer, then mixed liquor is carried out ultrasonic, until Surfactant AOT is completely dissolved, and mixed solution clear, prepares reverse micelle system;
(3) ABTS number of free radical and the linear equation of absorbance relation are solved:
The ABTS solution of 0mL, 0.5mL, 1mL, 1.5mL, 2mL, 2.5mL it is separately added in the color-comparison tube of 6 25mL, The concentration of ABTS solution is 4mmol/L, then 6 equipped with the color-comparison tube of ABTS solution in each add 1mL laccase solution, The enzyme of laccase solution is lived as 1U/mL, then all adds distilled water in 6 color-comparison tubes to 25mL scale, then by 6 tools Plug color comparison tube is placed one hour after all shaking up, and measures 6 with ultraviolet spectrophotometer after placing one hour under the wavelength of 420nm The absorbance of solution draw standard curve in color-comparison tube, obtains mixed solution A BTS free radical in color-comparison tube dense The linear equation of degree and absorbance relation:
Y=aX+b,
In formula: Y is the concentration (μm ol/L) of ABTS free radical;X is absorbance (A);A, b are constant to be asked;
(4) ABTS colorimetric method for determining laccase activity:
Soil after grinding weighs 1.0~3.0g and puts in centrifuge tube, and adds 10mL reverse micelle system in centrifuge tube, so After centrifuge tube is put into shaking table concussion 1~2 hours, after having shaken, centrifuge tube is placed on centrifuge with 4000r/min's Centrifugation 15~30min, puts in the cleanest centrifuge tube standby by the solution taking-up being in upper strata after being centrifuged, will It is in the soil of lower floor to continuously add the reverse micelle system of 10mL and repeat above-mentioned concussion and centrifugally operated, is repeated twice, and And each sample does three parallel samples;
It is in the solution on upper strata adds isopyknic Acetic acid-sodium acetate buffer to take out, and shake 15~20 minutes, so After mixed solution is placed in a centrifuge, with the centrifugation 30 of 4000r/min~40 minutes, take out after centrifugal layering and be in down The laccase solution of layer, it is achieved the back extraction of laccase, adds the laccase solution after 1.5mL back extraction and 1.5mL in cuvette ABTS solution, wherein the concentration of ABTS solution is 0.5mmol/L, then utilize ultraviolet spectrophotometer under the wavelength of 420nm, In 2 minutes, measure the absorbance of mixed solution in a cuvette every 15s, obtain in cuvette mixed solution absorbance with The linear equation of time relationship:
S=cT+d,
In formula: S is absorbance (A);T is time (min);C, d are constant to be asked;
The computing formula of soil laccase activity to be measured is as follows:
In formula: e is the slope of ABTS free radical and the linear equation of absorbance relation, i.e. e is equal to the constant tried to achieve in step (3) a;F is the slope of absorbance and the linear equation of time relationship, i.e. f is equal to the constant c tried to achieve in step (4);V1For back extraction The volume (mL) of rear laccase solution;V2For joining the volume (mL) of laccase solution after back extraction in cuvette;M is soil quality (g);V3For adding the volume (mL) of ABTS solution in cuvette.
The most according to claim 1 a kind of measure the method for laccase activity in soil, it is characterised in that the KCl of described addition The concentration of solution is 0.1mol/L, addition be every 10mL AOT/ isobutyltrimethylmethane. mixed liquor in add 0.5~0.8ml KCl molten Liquid.
The pH of the Acetic acid-sodium acetate buffer added the most according to claim 1 is 2.0~6.0, and concentration is 0.1mol/L.
CN201610528833.4A 2016-06-25 2016-06-25 Method for determining laccase enzyme activity in soil Active CN106248604B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610528833.4A CN106248604B (en) 2016-06-25 2016-06-25 Method for determining laccase enzyme activity in soil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610528833.4A CN106248604B (en) 2016-06-25 2016-06-25 Method for determining laccase enzyme activity in soil

Publications (2)

Publication Number Publication Date
CN106248604A true CN106248604A (en) 2016-12-21
CN106248604B CN106248604B (en) 2020-03-10

Family

ID=57613722

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610528833.4A Active CN106248604B (en) 2016-06-25 2016-06-25 Method for determining laccase enzyme activity in soil

Country Status (1)

Country Link
CN (1) CN106248604B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112345413A (en) * 2020-09-18 2021-02-09 武汉大学 Method for testing global distribution of infiltration water and inorganic solute under micro-spray irrigation condition

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1996038577A1 (en) * 1995-06-01 1996-12-05 Biotechnology Research And Development Corp. Enzyme catalysis in organic solutions
CN101270385A (en) * 2007-03-21 2008-09-24 中国科学院沈阳应用生态研究所 Analysis method for testing soil denitrification enzyme liveness
CN102533688A (en) * 2012-03-07 2012-07-04 湖南大学 Method for extracting and purifying lignin peroxidase by using reverse micelles

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1996038577A1 (en) * 1995-06-01 1996-12-05 Biotechnology Research And Development Corp. Enzyme catalysis in organic solutions
CN101270385A (en) * 2007-03-21 2008-09-24 中国科学院沈阳应用生态研究所 Analysis method for testing soil denitrification enzyme liveness
CN102533688A (en) * 2012-03-07 2012-07-04 湖南大学 Method for extracting and purifying lignin peroxidase by using reverse micelles

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
XIN PENG ET AL.: "Extraction and purification of laccase by employing a novel rhamnolipid reversed micellar system", 《PROCESS BIOCHEMISTRY》 *
张鹏: "以ABTS为底物测定漆酶活力的方法", 《印染助剂》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112345413A (en) * 2020-09-18 2021-02-09 武汉大学 Method for testing global distribution of infiltration water and inorganic solute under micro-spray irrigation condition
CN112345413B (en) * 2020-09-18 2021-12-17 武汉大学 Method for testing global distribution of infiltration water and inorganic solute under micro-spray irrigation condition

Also Published As

Publication number Publication date
CN106248604B (en) 2020-03-10

Similar Documents

Publication Publication Date Title
Williams et al. Radiocarbon in dissolved organic matter in the central North Pacific Ocean
Gibson et al. Requirement for Bicarbonate in Fatty Acid Synthesis1
CN107638814B (en) A kind of preparation method and applications of GO/PVDF molecularly imprinted composite membrane
CN102928528A (en) High performance liquid chromatography mass spectrometry detecting method of 16 fat soluble saxitoxins in shellfish meet
CN105749876B (en) A kind of preparation method of chitosan-modified graphene oxide quantum dot sorbing material
CN105548429A (en) Method for simultaneously detecting organic arsenic and inorganic arsenic in aquatic feed
CN102206630B (en) Method and kit for extracting total DNA of soil and sediment
CN107576704A (en) Microcysin LR molecular engram optical electro-chemistry sensor and its preparation and application
CN1773287A (en) Organic phosphorus pesticide bionic identification test reagent kit
CN100501370C (en) Monoamine oxidase activity fluorescent detecting method
CN106248604A (en) A kind of measure the method for laccase activity in soil
CN107828775A (en) The method that a kind of graphene oxide and chitosan microball fix difunctional acid urease
CN103951673B (en) A kind of reagent and the application in mercaptan detects thereof
CN102735512B (en) Method for extracting biotin from Antarctic krill and high-efficiency thin layer scanning analysis method
CN107643347A (en) The immobilon-p extraction gaschromatographic mass spectrometry detection method of phthalate compound in a kind of water body
Majak et al. Photosynthesis in algae: I. Accumulation products in the rhodophyceae
CN100339703C (en) Biosensor electrode used for detecting aflatoxin and variegated aspergillin and its preparation method
CN104697831B (en) The extracting method of membrane protein matter and the preparation method of electrophoresis Sample
CN103739762A (en) Preparation method of near-ultraviolet polystyrene copolymerization fluorescence microsphere
EP2022858A1 (en) Two-Step Gram Staining Method
CN102798656B (en) Method for separating 3-hydroxyl glutaric acid monoester enantiomer by high-performance capillary electrophoresis
CN103901139A (en) Pretreatment method for analyzing tetrabromobisphenol A in biologic urine
Lozada et al. Microbial communities associated with kelp detritus in temperate and subantarctic intertidal sediments
CN104407085B (en) Application liquid matter-matter combined instrument measures the method for chloromycetin in freshwater bed mud
Han Capillary electrophoresis with chemiluminescence detection of rutin and chlorogenic acid based on its enhancing effect for the luminol-ferricyanide system

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
EE01 Entry into force of recordation of patent licensing contract

Application publication date: 20161221

Assignee: Wuhan University of science and Technology Business Incubator Co., Ltd

Assignor: WUHAN University OF SCIENCE AND TECHNOLOGY

Contract record no.: X2020420000008

Denomination of invention: A method for determination of laccase activity in soil

Granted publication date: 20200310

License type: Common License

Record date: 20201022

EE01 Entry into force of recordation of patent licensing contract