CN108717085A - A kind of headspace extraction method for in-situ evaluation metal catalyst reduction performance - Google Patents

A kind of headspace extraction method for in-situ evaluation metal catalyst reduction performance Download PDF

Info

Publication number
CN108717085A
CN108717085A CN201810412758.4A CN201810412758A CN108717085A CN 108717085 A CN108717085 A CN 108717085A CN 201810412758 A CN201810412758 A CN 201810412758A CN 108717085 A CN108717085 A CN 108717085A
Authority
CN
China
Prior art keywords
headspace
metal catalyst
gas
model object
peak area
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
CN201810412758.4A
Other languages
Chinese (zh)
Other versions
CN108717085B (en
Inventor
郭从宝
万小芳
柴欣生
陈广学
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.)
South China University of Technology SCUT
Original Assignee
South China University of Technology SCUT
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 South China University of Technology SCUT filed Critical South China University of Technology SCUT
Priority to CN201810412758.4A priority Critical patent/CN108717085B/en
Publication of CN108717085A publication Critical patent/CN108717085A/en
Application granted granted Critical
Publication of CN108717085B publication Critical patent/CN108717085B/en
Expired - Fee Related 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
    • G01N30/00Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation
    • G01N30/02Column chromatography
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N30/00Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation
    • G01N30/02Column chromatography
    • G01N2030/022Column chromatography characterised by the kind of separation mechanism
    • G01N2030/025Gas chromatography

Landscapes

  • Physics & Mathematics (AREA)
  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Biochemistry (AREA)
  • General Health & Medical Sciences (AREA)
  • General Physics & Mathematics (AREA)
  • Immunology (AREA)
  • Pathology (AREA)
  • Investigating Or Analyzing Non-Biological Materials By The Use Of Chemical Means (AREA)
  • Sampling And Sample Adjustment (AREA)

Abstract

The invention discloses a kind of headspace extraction methods for in-situ evaluation metal catalyst reduction performance;The variation for specifically headspace gas chromatography being utilized quickly to measure reactant and product content in chlorinated aromatic compound catalysis dechlorination reaction process evaluates the technology of the performance of catalyst to establish kinetics relation.Its step is:(1) selected and External standards solutions the preparation of model object, (2) optimization of headspace gas chromatography test parameter, (3) blank control experiment is carried out, (4) headspace gas chromatography is used to carry out the detection of sample, (5) calculating and dynamic analysis of result, the evaluation of (6) catalyst performance.The advantages that this method is better than common gas chromatography and high performance liquid chromatography, has and is not necessarily to sample pretreatment, easy to operate, easy grasp, batch processing is efficient.

Description

A kind of headspace extraction method for in-situ evaluation metal catalyst reduction performance
Technical field
The present invention is to utilize chlorinated aromatic chemical combination in headspace gas chromatography evaluation metallic catalyst catalysis simulated wastewater The treatment effect of object, belongs to environmental analysis detection field, specifically a kind of for in-situ evaluation metal catalyst reduction performance Headspace extraction method.
Background technology
Chlorinated aromatic compound is widely present in the production waste water of a variety of industries such as dyestuff, pesticide, papermaking, petrochemical industry In, with the gradually deflation of environmental protection policy, the discharge standard of waste water is improved constantly, especially to chlorinated aromatic compound Discharge content have the limitation being increasingly stringenter.129 kinds of priority pollutants names that Environmental Protection Agency (EPA) is announced Dan Zhong, the halogenated organic matters based on chlorinated aromatic compound account for more than half.China announce " Chinese environmental preferentially pollutes In object blacklist ", chlorinated aromatic organic matter also accounts for prodigious proportion.In national sewage comprehensive emission standard GB8978- In 1996, the three-level discharge standard of paracide and 2,4,6- trichlorophenols is 1mg/L, and the three-level discharge standard of metacresol is 0.5mg/L。
Organic matter of the chlorinated aromatic compound as difficult for biological degradation, common processing method have catalytic oxidation, change Learn oxidizing process, photochemical oxidation method and electrochemical oxidation process, but oxidation process is there may be the chlorinatedorganic of toxicity bigger, Such as chlorophenol.Since last century the eighties, the reduction dechlorination that zero-valent metal is used as chlorinatedorganic studies the pass for receiving people Note, wherein Zero-valent Iron (ZVI) are widely used due to advantages such as its non-toxic inexpensives.As that studies Zero-valent Iron gradually gos deep into, Nano zero valence iron (nZVI) is gradually developed containing Fe Bimetallic System and immobilization containing Fe Bimetallic System.Currently, this A little metallic catalysts and Bimetallic catalyst system are applied to every field to the reduction dechlorination research of chlorinatedorganic.Meanwhile It filters out cheap metal and substitutes noble metal, reduce application cost and find good support materials and fix metallic catalyst, make It can recycle be current metal catalyst reduction dechlorination research one of hot spot.
Chlorinated aromatic compound and the assay method of corresponding content of degradation products usually have high performance liquid chromatography (HPLC), gas-chromatography (GC), multi-wavelength ultraviolet spectroscopy etc..Wherein HPLC is limited to larger by chromatographic column, and sample is into color It is needed by complicated preprocessor before spectrum column to prevent from blocking, operating process is cumbersome, and cost is higher;Although GC is not by chromatographic column Limitation, but need to extract and pre-concentration process, this process would generally use the organic solvent being more toxic, and repeatedly extraction The loss of test substance can be caused by taking, and lead to experimental error;Multi-wavelength ultraviolet spectroscopy compared to HPLC and GC have it is easy to operate, The advantages of easily grasping, but it is to the more demanding of solution composition, is typically only capable to for analyzing the less mould of contained substance type Quasi- waste water, for more complicated mathematical computations can be encountered when analyzing actual waste water and the more simulated wastewater of contained substance type And resultant error is larger.Therefore, a kind of degradation of efficient detection technique real time on-line monitoring chlorinated aromatic compound is developed Process establishes kinetic model, has realistic meaning for screening highly efficient cheap catalyst.
Invention content
The shortcomings that it is an object of the invention to overcome the above-mentioned prior art and deficiency provide a kind of for in-situ evaluation metal The headspace extraction method of catalyst reduction performance.Overcome the disadvantage present in present analysis chlorinated aromatic compound content method End.Degradation reaction may be implemented using this method and detection is carried out at the same time, be not necessarily to the pre-treatment of sample, it is easy to operate, and can criticize Amount detection, it is efficient, it is highly practical.
The present invention is achieved through the following technical solutions:
A kind of headspace extraction method for in-situ evaluation metal catalyst reduction performance includes the following steps:
Step 1, selected and External standards solutions the preparation of model object
Absolute ethyl alcohol, the model object to be measured of configuration standard concentration and corresponding reduction are previously added in 100mL volumetric flasks Product mother liquor takes the single mother liquor of different volumes ratio to be added in ml headspace bottle, adds deionized water and be diluted to fixed body respectively Product seals ml headspace bottle, rocks uniformly, to be determined;
Step 2, the optimization of headspace gas chromatography test parameter
Solution to be measured in step 1 is placed in head-space sampler, the component in solution reaches gas-liquid point after constant temperature Then gaseous component in ml headspace bottle is blown into gas-chromatography with nitrogen and is analyzed by balancing;By the way that gradient sample introduction is arranged Mouth pressure and chromatogram column temperature, it is ensured that the chromatographic signal peak of all substances will not interfere with each other, and the control of appearance duration is reasonable Range;
Step 3, blank control experiment
It takes prepared model object solution to be measured in step 1 to be diluted to setting concentration, then takes and be quantitatively adding ml headspace bottle In, sealing;
The optimal head space test parameter of step 2 is taken to be analyzed, concrete operations are as follows:By the head space equipped with model object solution Bottle, which is placed in injector furnace box, to be balanced, and then nitrogen purging enters gas chromatographic analysis, and furnace box is back to immediately after purging In balance same time again, and then purging analysis, so recycle (liquid phase extraction) repeatedly, gained gas-chromatography signal peak The logarithm of area can constitute a standard curve with extraction times;
Step 4 carries out the detection of sample using headspace gas chromatography
It takes prepared model object mother liquor to be measured in step 1 to be diluted to the same same concentration of step three-phase, then takes same step 3 Equivalent solution is added in ml headspace bottle, is rapidly added nano-metal particle or nanometer bi-metal catalyst, seals;
It is analyzed according to the identical test parameter of step 3, concrete operations are as follows:By the ml headspace bottle being sealed be placed in into It is balanced in sample device furnace box, then nitrogen purging enters gas chromatographic analysis, is back in furnace box after purging and puts down again immediately Weigh same time, and then purging analysis, so recycles (liquid phase extraction) repeatedly, record gained gas-chromatography signal peak face Product;
Step 5 degrades to model object by the analysis changed over time to the head space balanced gas in same sample bottle Dynamics is studied, and according to multiple headspace extraction theory, the peak area that volatile materials is obtained by extraction in sample bottle meets finger Number decaying, i.e.,:
An=An-1eq=An-2e2q=...=A0enq (1)
ln(An)=nq+ln (A0) (2)
Wherein:A0For the initial peak area of headspace gas, AnWhen being sampled for n-th, obtained peak area, q is the oblique of curve Rate, n are extraction times;For degradation reaction system, the concentration of model object is reduced with the extension in reaction time, can root According to, extrapolate it is adjacent twice extract peak area reduced value
△An=An-1eq-An (3)
By testing obtained peak area A1, A2, A3..., An, corresponding Δ A can be calculated1, Δ A2, Δ A3..., Δ An
The relationship of reaction time and extraction times is indicated with following formula:
T=jn (4)
T is the reaction time, and j is sampling interval time (equilibration time), and n is extraction times;
The relationship of gas-chromatography peak area and concentration C can be indicated with following formula:
C=kA (5)
Wherein k is response coefficient, can be corrected and be obtained by standard curve backstepping;
It can be derived according to formula (3) and formula (5):
△Cn=k (An-1eq-An) (6)
The corresponding peak area of extraction every time that record standard slope of a curve and experiment measure, is brought into formula (6) i.e. The decrement that volatility model object between two sub-samplings can be calculated is converted into the reaction time further according to formula (4) by number is sampled, Kinetics equation can be established, observed rate constant is calculated;
Step 6, the evaluation of catalyst:The performance of catalyst is evaluated according to the calculated observed rate constant of step 5.
Model object in above-mentioned steps one refers to aromatic compound, i.e. chlorobenzene or chlorophenols, the addition of absolute ethyl alcohol Amount is 5-40mL, and the ratio between model object mother liquor volume and corresponding dechlorination product mother liquor volume are 0.1:1-1:0.1.
The thermostat temperature of injector furnace box is 40-80 DEG C in above-mentioned steps two to four;Constant temperature time is 5-30min.
Inlet pressure in above-mentioned steps two is 20-40psi;Chromatogram column temperature is 80-140 DEG C;Inlet pressure ladder Degree is 1-10psi;Chromatogram column temperature gradient is 1-20 DEG C;A length of 1.5-5min when appearance.
A concentration of 40-150mmol/L is set in above-mentioned steps three;Dosage 10-18mL.
It recycles multiple described in above-mentioned steps three and step 4, refer to extraction times is 3~10 times.
Nano-metal particle or nanometer bi-metal catalyst in above-mentioned steps four, for the gold degraded for chlorinatedorganic Belong to, including iron, palladium, nickel or silver.
The present invention compared with the existing technology, has the following advantages and effect:
(1) it is not necessarily to sample pretreatment, easy grasp easy to operate, processing time is short is efficient.
(2) degradation reaction and detection are carried out at the same time, and avoid in conventional detection technology nano metal ion residues in solution In, when sampling carries out sample pretreatment, error caused by the reaction time is extended indirectly.
(3) strong antijamming capability, other substances present in sample will not impact measurement, and can be used for practical useless The processing detection of water.
Description of the drawings
Fig. 1 is the gas-chromatography signal graph of selected model object dichloro-benzenes and corresponding dechlorination product;
Fig. 2 is blank sample and the chromatographic signal peak area logarithm of catalyst sample is added with the variation of extraction times Figure.
Specific implementation mode
The present invention is more specifically described in detail with reference to specific embodiment.
The present invention is more specifically described in detail with reference to specific embodiment, but embodiments of the present invention are unlimited In this.Embodiment is only used for explaining the present invention, is not intended to limit the present invention, and the simple change for being related to the present invention should all belong to this The protection domain of invention.
Embodiment 1
The evaluation of nano-cellulose load iron palladium bimetallic system
(1) selected and External standards solutions the preparation of model object:20mL absolute ethyl alcohols are previously added in 100mL volumetric flasks, Dichloro-benzenes, chlorobenzene and benzene mother liquor 400mmol/L are prepared, the single mother liquor of 1mL dichloro-benzenes, 0.5mL chlorobenzenes and benzene is taken to be added respectively In ml headspace bottle, the dilution of 8mL deionized waters is added, ml headspace bottle is sealed, rocked uniformly, it is to be determined.
(2) optimization of headspace gas chromatography test parameter:Solution to be measured in step (1) is placed in head-space sampler, Then gaseous component in ml headspace bottle is blown into gas-chromatography with nitrogen and is analyzed by solution constant temperature 15min at 40 DEG C.If It is 5psi to set inlet pressure gradient, and chromatogram column temperature gradient is 10 DEG C, gradually rises temperature according to setting gradient, obtains optimal Head space test parameter:230 DEG C, pressure 30psi of injector temperature, 105 DEG C of column temperature, 250 DEG C of detector temperature, appearance duration exists In 2min.
(3) blank control is tested:Prepared 400mmol/L dichloro-benzenes mother liquor in step (1) is taken to be diluted to 40mmol/L, Then 18mL is taken to be added in ml headspace bottle, sealing.The head space test parameter in step (2) is taken to be analyzed, concrete operations are as follows:It will It is placed in 40 DEG C of injector furnace boxes equipped with dichlorobenzene solution ml headspace bottle and balances 15min, then nitrogen purging divides into gas-chromatography It analyses, is back in furnace box immediately after purging and balances 15min again, and then purging analysis, so cycle 6 times, to gained The natural logrithm value of gas-chromatography signal peak area draws out standard curve with extraction times mapping, and standard curve is calculated Regression equation ln (An)=7.215-0.046n, R2=0.997.
(4) headspace gas chromatography is used to carry out the detection of sample:Prepared 400mmol/L dichloro-benzenes mother liquor is taken to be diluted to Then 40mmol/L takes 40mmol/L solution to be added in ml headspace bottle, is rapidly added nano-cellulose load iron palladium bimetallic, close Envelope.Same step (3) same test parameter is taken to be analyzed, concrete operations are as follows:Dichlorobenzene solution and nano-cellulose will be housed The bimetallic ml headspace bottle of load iron palladium is placed in 40 DEG C of injector furnace boxes and balances 15min, and then nitrogen purging enters gas-chromatography It analyzes, is back in furnace box immediately after purging and balances 15min again, and then purging analysis, so cycle 6 times, record Gained gas-chromatography signal peak area is respectively 1299.1,1193.8,860.4,430.8,330.3,138.7.
(5) result of calculation is as shown in table 1:
Table 1:The chromatographic signal peak area of nano-cellulose load iron palladium bimetallic sample and corresponding result of calculation is added
(6) observed rate constant that can be calculated the degradation reaction by fit time and ln (c) is 0.02min-1
Embodiment 2
Carboxymethyl cellulose loads the evaluation of Nanoscale Iron
Step (1), (2), (3) are the same as embodiment 1.
(4) headspace gas chromatography is used to carry out the detection of sample:Prepared 400mmol/L dichloro-benzenes mother liquor is taken to be diluted to Then 40mmol/L takes 40mmol/L solution to be added in ml headspace bottle, be rapidly added the Nanoscale Iron of carboxymethyl cellulose load, close Envelope.Same step (3) same test parameter is taken to be analyzed, concrete operations are as follows:Dichlorobenzene solution and carboxymethyl cellulose will be housed The ml headspace bottle of element load Nanoscale Iron, which is placed in 40 DEG C of injector furnace boxes, balances 15min, and then nitrogen purging divides into gas-chromatography It analyses, is back in furnace box immediately after purging and balances 15min again, and then purging analysis, so cycle 6 times, record institute It is respectively 1268.4,1153.7,1042.5,663.4,554.6,342.1 to obtain gas phase chromatographic signal peak area;
(5) result of calculation is as shown in table 2
Table 2:The chromatographic signal peak area of carboxymethyl cellulose load nanometer iron sample and corresponding result of calculation is added
(6) observed rate constant that can be calculated the degradation reaction by fit time and ln (c) is 0.011min-1, with Embodiment 1 compare, can two kinds of metallic catalysts of Fast Evaluation performance.
The above embodiment is a preferred embodiment of the present invention, but embodiments of the present invention are not by above-described embodiment Limitation, it is other it is any without departing from the spirit and principles of the present invention made by changes, modifications, substitutions, combinations, simplifications, Equivalent substitute mode is should be, is included within the scope of the present invention.

Claims (7)

1. a kind of headspace extraction method for in-situ evaluation metal catalyst reduction performance, it is characterised in that including walking as follows Suddenly:
Step 1, selected and External standards solutions the preparation of model object
Absolute ethyl alcohol, the model object to be measured of configuration standard concentration and corresponding reduzate are previously added in 100mL volumetric flasks Mother liquor takes the single mother liquor of different volumes ratio to be added in ml headspace bottle, adds deionized water and be diluted to fixed volume respectively, close Bind empty bottle, rocks uniformly, to be determined;
Step 2, the optimization of headspace gas chromatography test parameter
Solution to be measured in step 1 is placed in head-space sampler, it is flat that the component in solution reaches gas-liquid distribution after constant temperature Gaseous component in ml headspace bottle, is then blown into gas-chromatography with nitrogen and is analyzed by weighing apparatus;By the way that gradient injection port pressure is arranged Power and chromatogram column temperature, it is ensured that the chromatographic signal peak of all substances will not interfere with each other, and the control of appearance duration is in zone of reasonableness;
Step 3, blank control experiment
It takes prepared model object solution to be measured in step 1 to be diluted to setting concentration, then takes and be quantitatively adding in ml headspace bottle, it is close Envelope;
The optimal head space test parameter of step 2 is taken to be analyzed, concrete operations are as follows:Ml headspace bottle equipped with model object solution is set It is balanced in injector furnace box, then nitrogen purging enters gas chromatographic analysis, is back to immediately in furnace box again after purging Secondary balance same time, and then purging analysis, so cycle are multiple, the logarithm of gained gas-chromatography signal peak area and extraction Number can constitute a standard curve;
Step 4 carries out the detection of sample using headspace gas chromatography
It takes prepared model object mother liquor to be measured in step 1 to be diluted to the same same concentration of step three-phase, then takes the third amount of same step Solution is added in ml headspace bottle, is rapidly added nano-metal particle or nanometer bi-metal catalyst, seals;
It is analyzed according to the identical test parameter of step 3, concrete operations are as follows:The ml headspace bottle being sealed is placed in injector It is balanced in furnace box, then nitrogen purging enters gas chromatographic analysis, is back in furnace box immediately after purging and balances phase again The same time, and then purging analysis, so cycle are multiple, record gained gas-chromatography signal peak area;
Step 5, by the analysis changed over time to the head space balanced gas in same sample bottle, according to multiple headspace extraction Theory, the peak area index of coincidence decaying that volatile materials is obtained by extraction in sample bottle, i.e.,:
An=An-1eq=An-2e2q=...=A0enq (1)
ln(An)=nq+ln (A0) (2)
Wherein:A0For the initial peak area of headspace gas, AnWhen being sampled for n-th, obtained peak area, q is slope of a curve, n For extraction times;For degradation reaction system, the concentration of model object is reduced with the extension in reaction time, can according to, push away Calculate the adjacent reduced value for extracting peak area twice
△An=An-1eq-An (3)
By testing obtained peak area A1, A2, A3..., An, corresponding Δ A can be calculated1, Δ A2, Δ A3..., Δ An
The relationship of reaction time and extraction times is indicated with following formula:
T=jn (4)
T is the reaction time, and j is sampling interval time (equilibration time), and n is extraction times;
The relationship of gas-chromatography peak area and concentration C can be indicated with following formula:
C=kA (5)
Wherein k is response coefficient, can be corrected and be obtained by standard curve backstepping;
It can be derived according to formula (3) and formula (5):
△Cn=k (An-1eq-An) (6)
The corresponding peak area of extraction every time that record standard slope of a curve and experiment measure, being brought into formula (6) can count The decrement for calculating volatility model object between two sub-samplings is converted into the reaction time further according to formula (4) by number is sampled, Kinetics equation is established, observed rate constant is calculated;
Step 6, the evaluation of catalyst:The performance of catalyst is evaluated according to the calculated observed rate constant of step 5.
2. being used for the headspace extraction method of in-situ evaluation metal catalyst reduction performance according to claim 1, feature exists In:Model object in step 1 refers to aromatic compound, i.e. chlorobenzene or chlorophenols, and the addition of absolute ethyl alcohol is 5- 40mL, the ratio between model object mother liquor volume and corresponding dechlorination product mother liquor volume are 0.1:1-1:0.1.
3. being used for the headspace extraction method of in-situ evaluation metal catalyst reduction performance according to claim 1, feature exists In:The thermostat temperature of step 2 to injector furnace box in four is 40-80 DEG C;Constant temperature time is 5-30min.
4. being used for the headspace extraction method of in-situ evaluation metal catalyst reduction performance according to claim 1, feature exists In:Inlet pressure in step 2 is 20-40psi;Chromatogram column temperature is 80-140 DEG C;Inlet pressure gradient is 1- 10psi;Chromatogram column temperature gradient is 1-20 DEG C;A length of 1.5-5min when appearance.
5. being used for the headspace extraction method of in-situ evaluation metal catalyst reduction performance according to claim 1, feature exists In:A concentration of 40-150mmol/L is set in step 3;Dosage 10-18mL.
6. being used for the headspace extraction method of in-situ evaluation metal catalyst reduction performance according to claim 1, feature exists In:It recycles multiple described in step 3 and step 4, refer to extraction times is 3~10 times.
7. being used for the headspace extraction method of in-situ evaluation metal catalyst reduction performance according to claim 1, feature exists In:Nano-metal particle or nanometer bi-metal catalyst in step 4, for the metal degraded for chlorinatedorganic, including iron, Palladium, nickel or silver.
CN201810412758.4A 2018-05-03 2018-05-03 Headspace extraction method for in-situ evaluation of reducing performance of metal catalyst Expired - Fee Related CN108717085B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810412758.4A CN108717085B (en) 2018-05-03 2018-05-03 Headspace extraction method for in-situ evaluation of reducing performance of metal catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810412758.4A CN108717085B (en) 2018-05-03 2018-05-03 Headspace extraction method for in-situ evaluation of reducing performance of metal catalyst

Publications (2)

Publication Number Publication Date
CN108717085A true CN108717085A (en) 2018-10-30
CN108717085B CN108717085B (en) 2021-05-14

Family

ID=63899551

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810412758.4A Expired - Fee Related CN108717085B (en) 2018-05-03 2018-05-03 Headspace extraction method for in-situ evaluation of reducing performance of metal catalyst

Country Status (1)

Country Link
CN (1) CN108717085B (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111024860A (en) * 2019-12-30 2020-04-17 华南理工大学 Method for measuring different forms of moisture in sludge by using headspace gas chromatography
CN114894932A (en) * 2022-05-07 2022-08-12 安徽工程大学 Method for detecting trace amount peculiar smell gas components in automobile textile fabric

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2000037405A1 (en) * 1998-12-18 2000-06-29 Millennium Petrochemicals, Inc. Process control method in acetic acid production
CN104569214A (en) * 2015-01-24 2015-04-29 福州大学 Method for measuring low-concentration p-xylene in metal ion and organism composite wastewater
CN106198427A (en) * 2016-07-26 2016-12-07 华南理工大学 A kind of five length ultraviolet spectrographic techniques evaluating metal catalytic reducing agent reducing property
CN106807448A (en) * 2017-02-28 2017-06-09 华南理工大学 A kind of metallic catalyst of nano-cellulose based aquagel load for trichlorophenol in water body of degrading and preparation method thereof
CN106830259A (en) * 2017-02-28 2017-06-13 华南理工大学 A kind of biodegrading process of chlorinatedorganic

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2000037405A1 (en) * 1998-12-18 2000-06-29 Millennium Petrochemicals, Inc. Process control method in acetic acid production
CN104569214A (en) * 2015-01-24 2015-04-29 福州大学 Method for measuring low-concentration p-xylene in metal ion and organism composite wastewater
CN106198427A (en) * 2016-07-26 2016-12-07 华南理工大学 A kind of five length ultraviolet spectrographic techniques evaluating metal catalytic reducing agent reducing property
CN106807448A (en) * 2017-02-28 2017-06-09 华南理工大学 A kind of metallic catalyst of nano-cellulose based aquagel load for trichlorophenol in water body of degrading and preparation method thereof
CN106830259A (en) * 2017-02-28 2017-06-13 华南理工大学 A kind of biodegrading process of chlorinatedorganic

Non-Patent Citations (6)

* Cited by examiner, † Cited by third party
Title
BAO-WEI ZHU等: "Catalytic Reduction of Chlorobenzenes with Pd/Fe Nanoparticles: Reactive Sites, Catalyst Stability, Particle Aging,and Regeneration", 《ENVIRON. SCI. TECHNOL.》 *
GANG SHEN等: "Headspace Liquid-Phase Microextraction of Chlorobenzenes in Soil with Gas Chromatography-Electron Capture Detection", 《ANAL. CHEM.》 *
JIAN-LIN HUANG等: "A3-Coupling catalyzed by robust Au nanoparticles covalently bonded to HS-functionalized cellulose nanocrystalline films", 《BEILSTEIN J. ORG. CHEM.》 *
SOFIA SÁ等: "Magnetically recyclable magnetite–palladium (Nanocat-Fe–Pd) nanocatalyst for the Buchwald–Hartwig reaction", 《GREEN CHEM.》 *
XINHUA XU等: "Catalytic dechlorination kinetics of p-dichlorobenzene over Pd/Fe catalysts", 《CHEMOSPHERE》 *
徐新华等: "纳米级Pd/Fe双金属体系对水中2,4-二氯苯酚脱氯的催化作用", 《催化学报》 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111024860A (en) * 2019-12-30 2020-04-17 华南理工大学 Method for measuring different forms of moisture in sludge by using headspace gas chromatography
CN111024860B (en) * 2019-12-30 2022-01-18 华南理工大学 Method for measuring different forms of moisture in sludge by using headspace gas chromatography
CN114894932A (en) * 2022-05-07 2022-08-12 安徽工程大学 Method for detecting trace amount peculiar smell gas components in automobile textile fabric
CN114894932B (en) * 2022-05-07 2023-08-01 安徽工程大学 Method for detecting trace odor components in textile fabric for automobile

Also Published As

Publication number Publication date
CN108717085B (en) 2021-05-14

Similar Documents

Publication Publication Date Title
Shade et al. Determination of MeHg in environmental sample matrices using Hg− Thiourea complex ion chromatography with on-line cold vapor generation and atomic fluorescence spectrometric detection
CN104991017B (en) Liquid chromatogram-tandem mass spectrometry method for determining isothiazolinone bactericides contained in water-based adhesive
Asiabi et al. Development of electrochemically controlled packed-in-tube solid phase microextraction method for sensitive analysis of acidic drugs in biological samples
Asiabi et al. On-line electrochemically controlled in-tube solid phase microextraction of inorganic selenium followed by hydride generation atomic absorption spectrometry
Tantra et al. Suitability of analytical methods to measure solubility for the purpose of nanoregulation
Hu et al. Simultaneous determination of palladium, platinum, rhodium and gold by on-line solid phase extraction and high performance liquid chromatography with 5-(2-hydroxy-5-nitrophenylazo) thiorhodanine as pre-column derivatization regents
Hashemi et al. Response surface methodology of pre-concentration of chorophenols from seawater samples by molecularly imprinted stir bar sorptive extraction combined with HPLC: Box–Behnken design
Wuilloud et al. On-line pre-concentration system for vanadium determination in drinking water using flow injection-inductively coupled plasma atomic emission spectrometry
Linhart et al. Mercury speciation in fish by high-performance liquid chromatography (HPLC) and post-column ultraviolet (UV)-photochemical vapor generation (PVG): comparison of conventional line-source and high-resolution continuum source (HR-CS) atomic absorption spectrometry (AAS)
CN108717085A (en) A kind of headspace extraction method for in-situ evaluation metal catalyst reduction performance
Muzikar et al. A preconcentration system using polyamine Metalfix-Chelamine resin for the on-line determination of palladium (II) and platinum (IV) by inductively coupled plasma optical emission spectrometry
Giakisikli et al. Integrated lab-in-syringe platform incorporating a membraneless gas–liquid separator for automatic cold vapor atomic absorption spectrometry
CN109632979A (en) Azanol analysis method when hydroxy amino urea coexists
Pretty et al. Electrochemical sample pretreatment coupled on-line with ICP-MS: analysis of uranium using an anodically conditioned glassy carbon working electrode
Mozo et al. Determination of Nifuroxazide by Flow Injection Linear Adsorptive Stripping Voltammetry on a Screen‐Printed Carbon Nanofiber Modified Electrode
Xiong et al. Total sulfur dioxide determination in red wine by suppressed ion chromatography with in-sample oxidation and SPE
Zarghampour et al. A new microfluidic-chip device followed by sensitive image analysis of smart phone for simultaneous determination of dyes with different acidic–basic properties
Yang et al. Determination of total chromium in seawater by isotope dilution sector field ICPMS using GC sample introduction
Jiang et al. Molecularly imprinted polymers for the selective determination of trace bisphenol A in river water by electrochemiluminescence
Huang et al. Simultaneous determination of peroxydisulfate and conventional inorganic anions by ion chromatography with the column‐switching technique
MacWilliams et al. Polarographic and Spectrophotometric Determination of Acrylamide in Acrylamide Polymers and Copolymers.
CN104569214B (en) The assay method of low concentration xylol in metal ion and Organic substance compound wastewater
CN107543878A (en) A kind of method that 3 kinds of OIT preservatives in cigarette paper are determined using Liquid Chromatography-Tandem Mass Spectrometry
Kononova et al. Sorption preconcentration and determination of molybdenum (VI) by diffuse reflection spectroscopy
CN111189953A (en) Method for determining content of organic peroxide

Legal Events

Date Code Title Description
PB01 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
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20210514

CF01 Termination of patent right due to non-payment of annual fee