CN104502298B - A kind of measure cadmium and the method for micro lead in iron ore - Google Patents

A kind of measure cadmium and the method for micro lead in iron ore Download PDF

Info

Publication number
CN104502298B
CN104502298B CN201410813789.2A CN201410813789A CN104502298B CN 104502298 B CN104502298 B CN 104502298B CN 201410813789 A CN201410813789 A CN 201410813789A CN 104502298 B CN104502298 B CN 104502298B
Authority
CN
China
Prior art keywords
iron ore
sample
cadmium
lead
time
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.)
Expired - Fee Related
Application number
CN201410813789.2A
Other languages
Chinese (zh)
Other versions
CN104502298A (en
Inventor
黎香荣
韦彦强
李小琴
陈永欣
韦新红
何龙凉
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.)
FANGCHENGGANG ENTRY-EXIST INSPECTION AND QUARANTINE BUREAU OF PEOPLE'S REPUBLIC OF CHINA
Original Assignee
FANGCHENGGANG ENTRY-EXIST INSPECTION AND QUARANTINE BUREAU OF PEOPLE'S REPUBLIC OF CHINA
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 FANGCHENGGANG ENTRY-EXIST INSPECTION AND QUARANTINE BUREAU OF PEOPLE'S REPUBLIC OF CHINA filed Critical FANGCHENGGANG ENTRY-EXIST INSPECTION AND QUARANTINE BUREAU OF PEOPLE'S REPUBLIC OF CHINA
Priority to CN201410813789.2A priority Critical patent/CN104502298B/en
Publication of CN104502298A publication Critical patent/CN104502298A/en
Application granted granted Critical
Publication of CN104502298B publication Critical patent/CN104502298B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Abstract

The present invention discloses and a kind of measures cadmium and the method for micro lead in iron ore, clears up iron ore sample including with microwave dissolver, then uses graphite furnace atomic absorption spectrophotometer to measure test solution.The process of micro-wave digestion is: is placed in politef counteracting tank by the iron ore sample of drying, uses deionized water moistening, be subsequently adding chloroazotic acid, after vigorous reaction stops, putting in microwave dissolver furnace chamber, set digestion condition as 190 DEG C, the heating-up time is 20min, clearing up the retention time is 20min, it is cooled to room temperature after having cleared up, takes out counteracting tank, after sample in tank is taken out, add water constant volume, i.e. obtains sample liquid to be measured.Sample can be cleared up by present invention Microwave Digestion completely, and in the case of not adding matrix modifier, testing result is consistent with the testing result of additive method, has simply, advantage fast and accurately, it is adaptable to micro lead and Cadmium detrmination in iron ore in batches.

Description

A kind of measure cadmium and the method for micro lead in iron ore
Technical field
The invention belongs to physical and chemical inspection technical field, a kind of measure cadmium and the method for micro lead in iron ore.
Background technology
Iron ore is as the basic material of steel and iron industry, and mineral composition is various, complex chemical composition, either trade relations Or metallurgical requirements is all the most deeply concerned to its component.The poisonous and harmful element not only shadow such as lead, arsenic, cadmium, hydrargyrum, fluorine and chlorine in iron ore Ring smelting equipment and product quality, also can pollute surrounding enviroment simultaneously, threaten health of human body.Based on environmental conservation and smelting enterprise The factors such as industry protection smelting equipment, iron and steel industry industry standard formulated the limitation mark of harmful elements in iron ore in 2014 Accurate.In iron ore, the examination criteria of the element such as lead, arsenic is more, mainly has atomic fluorescence spectrometry, inductively coupled plasma to send out Penetrate spectrographic method, flame atomic absorption spectrometry, volumetric method, spectrophotography, inductively coupled plasma mass spectrometry method etc..Iron mine In stone, the examination criteria method of cadmium compares shortage, mainly has atomic fluorescence method and ICP-MS method.The iron ore of other document report Middle cadmium element method for measuring also has inductively coupled plasma emission spectrography, voltammetry, atomic absorption spectrography (AAS), inductance coupling Close ICP-MS etc..In these methods, ICP-MS method is expensive, and the expense using process to produce is too high, at home Produce, detection enterprise popularizes difficulty.Although flame atomic absorption method and inductive coupling plasma emission spectrum method instrumentation Simply, but the cadmium content ratio in iron ore is relatively low, uses both approaches sensitivity not reach requirement.Zhang Li etc. use hydrogenation Thing Generation-Atomic Fluorescence Spectrometry measures, although detection limit ratio is relatively low, but preparing of Sulfhydryl Cotton is cumbersome, and process is complicated. At present, the report of cadmium in graphite furnace atomic absorption spectrometry iron ore is not the most found.
GFAAS is the atomizer utilizing graphite material to make the shapes such as pipe, cup, adds with electric current Hot atom carries out the method for atomic absorption analysis.Due to sample full entry atomization, and avoid atomic concentration at fire Dilution in flame gas, sensitivity for analysis has obtained significant raising, and detection limit can reach 10-6~10-4, better than ICP-AES method 1~2 order of magnitude.For measuring trace metal element, better than other many methods in performance, and a small amount of sample can be used for Analyze and solid sample direct analysis.Compared with atomic emission spectrum and atomic fluorescence spectrometry technology, spectral interference is few, right Have more preferable selectivity in tested unit, thus its application is quite varied.
Summary of the invention
It is an object of the invention to provide one and have employed micro-wave digestion GFAAS to measure ferrum Cadmium and the method for micro lead in Ore.
For reaching above-mentioned purpose, the technical solution used in the present invention is:
A kind of measure cadmium and the method for micro lead in iron ore, clear up iron ore sample, then including with microwave dissolver Use the step that graphite furnace atomic absorption spectrophotometer measures.
In technique scheme:
Described microwave dissolver clears up the process of iron ore:
The solution iron ore sample of drying is placed in politef counteracting tank, uses deionized water moistening, be subsequently adding king Water, after vigorous reaction stops, putting in microwave dissolver furnace chamber, sets digestion condition as 190 DEG C, and the heating-up time is 20min, Clearing up the retention time is 20min, is cooled to room temperature after having cleared up, and takes out counteracting tank, and after being taken out by sample in tank, add water constant volume, I.e. obtain sample liquid to be measured.
Further, if silicone content is higher in ironstone sample, described vigorous reaction adds a small amount of Fluohydric acid. after stopping.
Further, described iron ore sample is preferably dried under the conditions of 105 DEG C.
The process that described graphite furnace atomic absorption spectrophotometer measures is:
Concentration is 1000 μ L/mL lead, cadmium Standard Stock solutions, is diluted to the lead mark that concentration is multiple numerical value respectively Quasi-working solution and cadmium standard working solution, utilize graphite furnace atomic absorption spectrophotometer mensuration lead, cadmium standard working solution to obtain Calibration curve, recycling graphite furnace atomic absorption spectrophotometer measures the iron ore sample after micro-wave digestion, passes through comparison calibration Curve obtains cadmium and the content of lead in iron ore.
Preferably, a series of concentration values of described lead standard working solution are: 0mg/L, 2mg/L, 4mg/L, 6mg/L, 8mg/L.A series of concentration values of described cadmium standard working solution are: 0 μ g/L, 0.5 μ g/L, 1 μ g/L, 2 μ g/L, 4 μ g/L.
Preferably, instrument parameter when described graphite furnace atomic absorption spectrophotometer is measured is:
Cadmium: wavelength 228.8nm, slit 0.7nm, lamp current 4.0mA;Baking temperature 85~120 DEG C, drying time 25s;Ash Change temperature 500 DEG C, ashing time 20s;Atomization temperature 1500 DEG C, atomization time 5s;Burn residual temperature 2450 DEG C, burn the residual time 3s;Zeeman correcting background, measures peak area;With high-purity argon gas for graphite furnace protective gas, flow 1.8L/min;Sample size then with 20 μ L are optimal;
Lead: wavelength 217.0nm, slit 0.7nm, lamp current 2.0mA;Baking temperature 85~130 DEG C, drying time 25s;Ash Change temperature 650 DEG C, ashing time 25s;Atomization temperature 1500 DEG C, atomization time 5s;Burn residual temperature 2450 DEG C, burn the residual time 3s;Zeeman correcting background, measures peak area;With high-purity argon gas for graphite furnace protective gas, flow 1.8L/min;Sample size also with 20 μ L are optimal.
Compared to the prior art, the invention have the advantages that
1, the pre-treatment of ironstone sample uses microwave digestion technology, has gathered the property of high-pressure digestion and microwave fast heating Can, there is sample and decompose quick, complete, simple to operate, volatile element loss is little, and reagent consumption is few, pollutes few, and blank is low, The distinguishing features such as analysis cost is low;
Have employed GFAAS when 2, measuring cadmium and lead, sensitivity for analysis is high, and amount of samples is few, operation Simply, compared with atomic emission spectrum and atomic fluorescence spectrometry technology, spectral interference is few, have preferably for tested unit Selectivity.
Detailed description of the invention
Embodiment 1
1.1 key instrument
AA240Z type graphite furnace atomic absorption spectrophotometer (Varian company of the U.S.);PSD120 graphite furnace automatic sampler (Varian company of the U.S.);O2E-05 type cadmium hollow cathode lamp;WB24A type lead hollow cathode lamp.ETHOS A type microwave dissolver (LabTech company of the U.S.), is equipped with 12 100mL high-pressure digestion tanks.Milli-Q Advantage A10 ultrapure water system is (beautiful Millipore Corp. of state): resistivity 18.2M Ω cm.
1.2 main agents
Lead, cadmium Standard Stock solutions (ferrous materials test center of country): be 1000 μ g/mL, be diluted to as required Different concentration standard working solution (being shown in Table 1).
The concentration of Pb and Cd in table 1 standard working solution
1.3 experimental technique
Weigh 0.5g 105 DEG C dry iron ore samples, be placed in 100mL politef counteracting tank, with go on a small quantity from Sub-water-wet, adds 10mL chloroazotic acid, (if silicone content is higher in sample, drip 1mL Fluohydric acid .) after vigorous reaction stops, adding Lid set, is placed in rotating disk, puts in furnace chamber, connects temperature, pressure transducer.Setting digestion condition as 190 DEG C, the heating-up time is 20min, clearing up the retention time is 20min.It is cooled to room temperature after having cleared up, takes out counteracting tank, by whole for Specimen eliminating liquid in tank It is transferred in 100mL plastics volumetric flask, is diluted with water to scale, shakes up, stand.In company with doing blank experiment.Then graphite furnace is used Atomic absorption spectrography (AAS) measures lead cadmium in solution under the conditions of selected instrument parameter.
The process that graphite furnace atomic absorption spectrophotometer measures is: it is molten that concentration is 1000 μ L/mL lead, cadmium standard inventory Liquid, is diluted to lead standard working solution and cadmium standard working solution (being shown in Table 1) that concentration is multiple numerical value respectively, utilizes graphite furnace Atomic absorption spectrometry lead, cadmium standard working solution obtain calibration curve, and recycling graphite furnace atomic absorption spectrophotometer is surveyed Fixed iron ore sample after micro-wave digestion, obtains cadmium and the content of lead in iron ore by comparison calibration curve.
Instrument parameter when graphite furnace atomic absorption spectrophotometer is measured is:
Cadmium: wavelength 228.8nm, slit 0.7nm, lamp current 4.0mA;Baking temperature 85~120 DEG C, drying time 25s;Ash Change temperature 500 DEG C, ashing time 20s;Atomization temperature 1500 DEG C, atomization time 5s;Burn residual temperature 2450 DEG C, burn the residual time 3s;Zeeman correcting background, measures peak area;With high-purity argon gas for graphite furnace protective gas, flow 1.8L/min;Sample size 20 μ L;
Lead: wavelength 217.0nm, slit 0.7nm, lamp current 2.0mA;Baking temperature 85~130 DEG C, drying time 25s;Ash Change temperature 650 DEG C, ashing time 25s;Atomization temperature 1500 DEG C, atomization time 5s;Burn residual temperature 2450 DEG C, burn the residual time 3s;Zeeman correcting background, measures peak area;With high-purity argon gas for graphite furnace protective gas, flow 1.8L/min;Sample size 20 μ L。
1.4 method detection limits, precision, accuracy and the response rate
Under above-mentioned instrument working condition, draw calibration curve, to blank solution replication 11 times, take measurement result 3 times of standard deviation (s) are as detection limit, 10 times of Determination Limit as method.The detection limit of lead and cadmium is respectively 0.25 μ g/ G (Pb) and 0.072 μ g/g (Cd).Lead and Cadmium detrmination lower limit are respectively 0.83 μ g/g (Pb) and 0.24 μ g/g (Cd).
According to above-mentioned experimental technique, for same sample ore METHOD FOR CONTINUOUS DETERMINATION 11 times, investigate method precision.Lead, cadmium are relative Standard deviation (RSD, n=11) is respectively 0.8% (Pb) and 2.6% (Cd) (being shown in Table 2);Select two different iron ores, adopt Measure by this method, from the point of view of table 2 result, consistent with additive method measured value.Sample ore is separately added into isocyatic to be measured Element, is measured after clearing up process by 1.4 joint experimental techniques, and the method response rate is respectively 96.0% (Pb) and 107.3% (Cd) (being shown in Table 3), result is more satisfactory.
Table 2 preci-sion and accuracy is tested
Note: the cooperative experiment sample that same Fe-1, Fe-2 provide for Tianjin Entry-Exit Inspection and Quarantine Bureau, reference value is collaborative Experiment median.
The response rate of table 3 method
Test result indicate that, sample can be cleared up completely with microwave dissolver, and do not adding the feelings of matrix modifier Under condition, the method is consistent to the testing result of actual sample and the testing result of additive method.This method is simple, quick, accurate, Lead and Cadmium detrmination be applicable to batch iron ore.

Claims (4)

1. one kind measures cadmium and the method for micro lead in iron ore, it is characterised in that: include clearing up instrument iron ore with micro-wave digestion Sample, then uses the step that graphite furnace atomic absorption spectrophotometer measures;
The process of described micro-wave digestion iron ore sample is: dried under the conditions of 105 DEG C by iron ore sample, the iron ore of drying Sample is placed in politef counteracting tank, uses deionized water moistening, is subsequently adding chloroazotic acid, after vigorous reaction stops, putting into In microwave dissolver furnace chamber, setting digestion condition as 190 DEG C, the heating-up time is 20min, and clearing up the retention time is 20min, clears up Being cooled to room temperature after completing, take out counteracting tank, after being taken out by sample in tank, add water constant volume, i.e. obtains sample liquid to be measured;
The process that described graphite furnace atomic absorption spectrophotometer measures is: it is molten that concentration is 1000 μ L/mL lead, cadmium standard inventory Liquid, is diluted to lead standard working solution and cadmium standard working solution that concentration is multiple numerical value respectively, utilizes sampling Graphite Furnace Atomic to inhale Receive spectrophotometer lead, cadmium standard working solution obtains calibration curve, and recycling graphite furnace atomic absorption spectrophotometer measures through micro- Ripple clear up after iron ore sample, obtain cadmium and the content of lead in iron ore by comparison calibration curve.
Method the most according to claim 1, it is characterised in that: described vigorous reaction adds Fluohydric acid. after stopping.
Method the most according to claim 1, it is characterised in that:
A series of concentration values of described lead standard working solution are: 0mg/L, 2mg/L, 4mg/L, 6mg/L, 8mg/L;
A series of concentration values of described cadmium standard working solution are: 0 μ g/L, 0.5 μ g/L, 1 μ g/L, 2 μ g/L, 4 μ g/L.
4. according to the method described in claim 1 or 3, it is characterised in that described graphite furnace atomic absorption spectrophotometer is measured Time instrument parameter be:
Cadmium: wavelength 228.8nm, slit 0.7nm, lamp current 4.0mA;Baking temperature 85~120 DEG C, drying time 25s;Ashing temperature Spend 500 DEG C, ashing time 20s;Atomization temperature 1500 DEG C, atomization time 5s;Burn residual temperature 2450 DEG C, burn residual time 3s; Zeeman correcting background, measures peak area;With high-purity argon gas for graphite furnace protective gas, flow 1.8L/min;
Lead: wavelength 217.0nm, slit 0.7nm, lamp current 2.0mA;Baking temperature 85~130 DEG C, drying time 25s;Ashing temperature Spend 650 DEG C, ashing time 25s;Atomization temperature 1500 DEG C, atomization time 5s;Burn residual temperature 2450 DEG C, burn residual time 3s; Zeeman correcting background, measures peak area;With high-purity argon gas for graphite furnace protective gas, flow 1.8L/min.
CN201410813789.2A 2014-12-23 2014-12-23 A kind of measure cadmium and the method for micro lead in iron ore Expired - Fee Related CN104502298B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410813789.2A CN104502298B (en) 2014-12-23 2014-12-23 A kind of measure cadmium and the method for micro lead in iron ore

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410813789.2A CN104502298B (en) 2014-12-23 2014-12-23 A kind of measure cadmium and the method for micro lead in iron ore

Publications (2)

Publication Number Publication Date
CN104502298A CN104502298A (en) 2015-04-08
CN104502298B true CN104502298B (en) 2016-12-28

Family

ID=52943716

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410813789.2A Expired - Fee Related CN104502298B (en) 2014-12-23 2014-12-23 A kind of measure cadmium and the method for micro lead in iron ore

Country Status (1)

Country Link
CN (1) CN104502298B (en)

Families Citing this family (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105300908A (en) * 2015-11-10 2016-02-03 合肥通用机械研究院 Method for determining trace element lead in centrifugal casting furnace tube and matrix modifier applied thereto
CN105548331A (en) * 2015-12-10 2016-05-04 内蒙古包钢钢联股份有限公司 Method for simultaneous determination of multiple trace elements in iron ore
CN106290194A (en) * 2016-08-22 2017-01-04 常州大学 A kind of method of cadmium content in direct mensuration electron level diethylene glycol dimethyl ether
CN109297914A (en) * 2018-11-16 2019-02-01 阿拉山口出入境检验检疫局综合技术服务中心 A method of using the Zn-ef ficiency content in graphite resolution-atomic absorption spectrometry sulphur
CN110161017B (en) * 2019-06-04 2022-08-23 深圳市环保科技集团股份有限公司 Method for establishing mathematical model of spectral interference coefficient of iron in cadmium determination by ICP-OES method
CN111537328A (en) * 2020-04-20 2020-08-14 湛江海关技术中心 Pretreatment method for chromium ore by microwave digestion acid melting method and chromium production method
CN114280222A (en) * 2021-12-14 2022-04-05 万宝矿产有限公司 Method for batch processing of copper ore samples

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101793830B (en) * 2010-03-16 2011-11-16 武汉钢铁(集团)公司 Method for measuring sulfur content in iron ore
CN102565176A (en) * 2010-12-17 2012-07-11 鞍钢股份有限公司 Method for simultaneously determining harmful elements in iron ore
CN102854238A (en) * 2012-08-10 2013-01-02 同济大学 Method for determination analysis of multiple heavy metals in environmental medium or biological sample

Also Published As

Publication number Publication date
CN104502298A (en) 2015-04-08

Similar Documents

Publication Publication Date Title
CN104502298B (en) A kind of measure cadmium and the method for micro lead in iron ore
CN105699361B (en) The method for detecting Al, Cu, Mn, P and Si content in ferrotianium simultaneously using inductive coupling plasma emission spectrograph
CN101846629B (en) Method for measuring boric acid and borate in cosmetics by microwave digestion -ICP-OES
CN101846651A (en) Method for measuring boric acid and borate in cosmetics by microwave digestion -ICP-MS
CN102998303A (en) Detection method for determining contents of niobium and tantalum in steel by applying microwave digestion-ICP-AES (Inductively Coupled Plasma-Atomic Emission Spectrometry)
CN104931330A (en) Digestion method of detection of heavy metals in soil
CN106290317A (en) Potassium, lead and Direct spectrophotometry method in iron ore, slag and ion dust mud contaning
CN101187629A (en) Tobacco and tobacco product arsenic content determination method
CN104062284A (en) Method for determining tungsten content in ferroniobium
CN106153605A (en) Measure the method for ferro-aluminum silicon slicker solder Fe content in aluminium copper simultaneously
CN109163958A (en) A kind of Methods of Soil Digestion and a kind of detection method for measuring various heavy in soil simultaneously
CN106290180A (en) A kind of Pb in food, chromium, cadmium and the detection method of copper content
CN103837396B (en) The digestion procedure of a kind of crystal glass and the assay method of crystal glass lead content
CN104215627A (en) Method for microwave digestion-inductively coupled plasma mass spectrometer (ICP-MS) determination of metal ions such as lead, arsenic, cadmium and chromium in cigarette case
CN103954677A (en) Detection method for measuring trace Cr in tobacco and tobacco products
CN108593692A (en) EU REACH Legislation height pays close attention to the leather standard sample and preparation method of substance X fluorescence spectrum standard measure screening
CN108020541A (en) The method of sulfur content in inductively coupled plasma emission spectrography measure ferrosilicon
CN104359751B (en) Trace uranium in micro-wave digestion Soil by Flurescence
CN103969320A (en) Anodic stripping voltammetric detection method for cadmium in rice
CN110095419A (en) The detection method of lead, cadmium in automotive material
CN105223147B (en) The assay method of content of 6-valence Cr ions in chromium type high iron ore
CN104880454B (en) A kind of method of measuring metal element content in Merlon
CN105277532A (en) Determination method for indium content
CN103969323A (en) Method for determining As content in tobacco and tobacco product by utilizing <75>AS<16>O<+>
CN110186909B (en) Microwave digestion and ICP-OES (inductively coupled plasma-optical emission spectrometry) test of heavy metal elements in leather product

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20161228

Termination date: 20181223

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