CN103969201A - Measuring method for total chrome in groundwater - Google Patents

Measuring method for total chrome in groundwater Download PDF

Info

Publication number
CN103969201A
CN103969201A CN201410163661.6A CN201410163661A CN103969201A CN 103969201 A CN103969201 A CN 103969201A CN 201410163661 A CN201410163661 A CN 201410163661A CN 103969201 A CN103969201 A CN 103969201A
Authority
CN
China
Prior art keywords
instrument
sample
standard
samples
measuring method
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201410163661.6A
Other languages
Chinese (zh)
Inventor
李化
马丽娟
宋立伟
董玲
曹新全
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.)
Angang Steel Co Ltd
Original Assignee
Angang Steel Co Ltd
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 Angang Steel Co Ltd filed Critical Angang Steel Co Ltd
Priority to CN201410163661.6A priority Critical patent/CN103969201A/en
Publication of CN103969201A publication Critical patent/CN103969201A/en
Pending legal-status Critical Current

Links

Abstract

The invention relates to a measuring method for total chrome in groundwater. The measuring method comprises the following steps: (1) 0 ug/L, 10 ug/L, 20 ug/L, 30 ug/L and 40 ug/L of a series of standard samples are prepared; (2) samples are the groundwater, the measuring is carried out by absorbing 20 uL of the samples and a series of standard samples; (3) an Agilent atomic absorption spectrophotometer 3511 graphite furnace system is adopted as an experimental instrument, the instrument is adjusted to be in the optimum state, and the experiment is conducted after the instrument is stabilized; (4) an argon gas source and a water source are opened, and the pressure of the argon gas is adjusted to 0.3 MPa; (5) parameters in the experiment are set; (6) at the wavelength of 357.8 nm, the blank zero setting is conducted, the standard curve is drew, the absorbance of the samples is measured, the corresponding chromium content of the samples can be measured from the standard curve, and the unit is ug/L. Compared with the prior art, the measuring method has the benefits as follows: the method detection limit is low, so that the measuring method is more suitable for the monitoring of the total chrome in the groundwater; meanwhile, the detection process is simple, the operation is easy, and the detection accuracy is high, so that the measuring method is suitable for popularization and application.

Description

The assay method of total chromium in a kind of underground water
Technical field
The present invention relates to groundwater monitoring technical field, relate in particular to the assay method of total chromium in a kind of underground water.
Background technology
Total chromium is one of groundwater monitoring index, the detection method national standard using at present has potassium permanganate oxygen--diphenyl carbazide spectrophotometry and ferrous sulphate titrimetry, and its measurement range is respectively concentration limit to be 0.004mg/l and to be greater than being suitable for of 1mg/l.In underground water, total chrome content is atomic, substantially can detect out with chemical determination, therefore needs to study the assay method of total chromium in a kind of more applicable underground water.
Summary of the invention
The present invention overcomes the deficiencies in the prior art, a kind of method that adopts flameless atomic absorption spectrometry to measure total chromium in underground water is provided, has greatly reduced method detection limit (0.003mg/l), easy and simple to handle, accuracy is high, has met the needs of groundwater monitoring.
In order to achieve the above object, the present invention realizes by the following technical solutions:
In underground water, an assay method for total chromium, comprises the steps:
1) draw 1mg/L chromium standard and use solution 0mL, 1.0mL, 2.0mL, 3.0mL, 4.0mL, be placed in 100mL volumetric flask, with volume ratio be 1 part of nitric acid: the salpeter solution of 99 parts of distilled water is diluted to scale, shake up, be mixed with the standard series sample of 0ug/L, 10ug/L, 20ug/L, 30ug/L, 40ug/L;
2) sample is underground water, draws 20uL sample and standard series sample measure with 20ul microsyringe;
3) use Agilent atomic absorption spectrophotometer (AAS) 3511 graphite furnace systemic effect experimental apparatuss, regulate instrument to optimum condition, after instrument stabilizer, test instrument condition of work:
Wavelength: 357.8nm;
Lamp current: 2.0mA;
Slit: 0.2nm;
4) open argon gas source of the gas and water source, argon pressure is adjusted to 0.3MPa;
5) parameters setting in experiment:
Drying stage: 90~100 DEG C of 10~15 minutes retention times 15~20 minute heating-up time of temperature
The ashing stage: 680~720 DEG C of 15~20 minutes retention times 15~20 minute heating-up time of temperature
Atomized stage: 2800~3000 DEG C of 5~6 minutes retention times 1~2 minute heating-up time of temperature
Wash phase: 2900~3100 DEG C of 3~4 minutes retention times 2~3 minute heating-up time of temperature
6), under the best operating condition of instrument, in wavelength 357.8nm place, with blank zeroing, survey its absorbance; Taking measure absorbance as ordinate, corresponding chromium content is horizontal ordinate, drawing standard curve; Press the equal instrument condition of typical curve, with blank zeroing, measure the absorbance of sample, try to achieve the corresponding chromium content of sample, the ug/l of unit from typical curve.
Compared with prior art, the invention has the beneficial effects as follows:
1) method detection limit is low, is more suitable for the monitoring of total chromium in underground water;
2) experimentation is simple, easily operation;
3) inspection accuracy is high, is applicable to applying.
Embodiment
In underground water, an assay method for total chromium, comprises the steps:
1) draw 1mg/L chromium standard and use solution 0mL, 1.0mL, 2.0mL, 3.0mL, 4.0mL, be placed in 100mL volumetric flask, with volume ratio be 1 part of nitric acid: the salpeter solution of 99 parts of distilled water is diluted to scale, shake up, be mixed with the standard series sample of 0ug/L, 10ug/L, 20ug/L, 30ug/L, 40ug/L;
2) sample is underground water, draws 20uL sample and standard series sample measure with 20ul microsyringe;
3) use Agilent atomic absorption spectrophotometer (AAS) 3511 graphite furnace systemic effect experimental apparatuss, regulate instrument to optimum condition, after instrument stabilizer, test instrument condition of work:
Wavelength: 357.8nm;
Lamp current: 2.0mA;
Slit: 0.2nm;
4) open argon gas source of the gas and water source, argon pressure is adjusted to 0.3MPa;
5) parameters setting in experiment:
Drying stage: 90~100 DEG C of 10~15 minutes retention times 15~20 minute heating-up time of temperature
The ashing stage: 680~720 DEG C of 15~20 minutes retention times 15~20 minute heating-up time of temperature
Atomized stage: 2800~3000 DEG C of 5~6 minutes retention times 1~2 minute heating-up time of temperature
Wash phase: 2900~3100 DEG C of 3~4 minutes retention times 2~3 minute heating-up time of temperature
6), under the best operating condition of instrument, in wavelength 357.8nm place, with blank zeroing, survey its absorbance; Taking measure absorbance as ordinate, corresponding chromium content is horizontal ordinate, drawing standard curve; Press the equal instrument condition of typical curve, with blank zeroing, measure the absorbance of sample, try to achieve the corresponding chromium content of sample, the ug/l of unit from typical curve.
Following examples are implemented under taking technical solution of the present invention as prerequisite, provided detailed embodiment and concrete operating process, but protection scope of the present invention are not limited to following embodiment.In following embodiment, method therefor is conventional method if no special instructions.
[embodiment 1] application the method for the invention is measured the underground water of 30 well heads, replicate determination 3 times, and concrete steps are as follows:
1) draw 1mg/L chromium standard and use solution 0mL, 1.0mL, 2.0mL, 3.0mL, 4.0mL, be placed in 100mL volumetric flask, with volume ratio be 1 part of nitric acid: the salpeter solution of 99 parts of distilled water is diluted to scale, shake up, be mixed with the standard series sample of 0ug/L, 10ug/L, 20ug/L, 30ug/L, 40ug/L;
2) measure with 20ul microsyringe absorption 20uL sample and standard series sample;
3) use Agilent atomic absorption spectrophotometer (AAS) 3511 graphite furnace systemic effect experimental apparatuss, regulate instrument to optimum condition, after instrument stabilizer, test instrument condition of work:
Wavelength: 357.8nm;
Lamp current: 2.0mA;
Slit: 0.2nm;
4) open argon gas source of the gas and water source, argon pressure is adjusted to 0.3MPa;
5) parameters setting in experiment:
Drying stage: 90 DEG C of 10 minutes retention times 15 minute heating-up time of temperature
The ashing stage: 700 DEG C of 15 minutes retention times 15 minute heating-up time of temperature
Atomized stage: 2900 DEG C of 5 minutes retention times 1 minute heating-up time of temperature
Wash phase: 3000 DEG C of 3 minutes retention times 2 minute heating-up time of temperature
6), under the best operating condition of instrument, in wavelength 357.8nm place, with blank zeroing, survey its absorbance; Taking measure absorbance as ordinate, corresponding chromium content is horizontal ordinate, drawing standard curve; Press the equal instrument condition of typical curve, with blank zeroing, measure the absorbance of sample, try to achieve the corresponding chromium content of sample, the ug/l of unit from typical curve.
Precision test result is as follows:
The relative standard deviation of above measuring result: 4.0%~10.4%.
Recovery test result is as follows:
Numbering Add scalar (μ g/l) Measured value-background values (μ g/l) Recovery %
1 0.50 0.470 94
2 0.50 0.530 106
3 0.50 0.565 113
4 0.50 0.546 109
5 1.0 0.960 96
6 1.0 1.012 101
7 1.0 0.970 97
8 1.0 1.042 104
Above chromium recovery test recovery of standard addition: 94%~113%.
[embodiment 2] application the method for the invention is measured the underground water of 30 well heads, replicate determination 3 times, and concrete steps are as follows:
1) draw 1mg/L chromium standard and use solution 0mL, 1.0mL, 2.0mL, 3.0mL, 4.0mL, be placed in 100mL volumetric flask, with volume ratio be 1 part of nitric acid: the salpeter solution of 99 parts of distilled water is diluted to scale, shake up, be mixed with the standard series sample of 0ug/L, 10ug/L, 20ug/L, 30ug/L, 40ug/L;
2) measure with 20ul microsyringe absorption 20uL sample and standard series sample;
3) use Agilent atomic absorption spectrophotometer (AAS) 3511 graphite furnace systemic effect experimental apparatuss, regulate instrument to optimum condition, after instrument stabilizer, test instrument condition of work:
Wavelength: 357.8nm;
Lamp current: 2.0mA;
Slit: 0.2nm;
4) open argon gas source of the gas and water source, argon pressure is adjusted to 0.3MPa;
5) parameters setting in experiment:
Drying stage: 100 DEG C of 15 minutes retention times 20 minute heating-up time of temperature
The ashing stage: 720 DEG C of 20 minutes retention times 20 minute heating-up time of temperature
Atomized stage: 3000 DEG C of 6 minutes retention times 2 minute heating-up time of temperature
Wash phase: 3100 DEG C of 4 minutes retention times 3 minute heating-up time of temperature
6), under the best operating condition of instrument, in wavelength 357.8nm place, with blank zeroing, survey its absorbance; Taking measure absorbance as ordinate, corresponding chromium content is horizontal ordinate, drawing standard curve; Press the equal instrument condition of typical curve, with blank zeroing, measure the absorbance of sample, try to achieve the corresponding chromium content of sample, the ug/l of unit from typical curve.
Precision test result is as follows:
The relative standard deviation of above measuring result: 4.1%~10.6%.
Recovery test result is as follows:
Numbering Add scalar (μ g/l) Measured value-background values (μ g/l) Recovery %
1 0.50 0.537 107
2 0.50 0.562 112
3 0.50 0.465 93
4 0.50 0.545 109
5 1.0 0.984 98
6 1.0 1.012 101
7 1.0 1.056 106
8 1.0 0.963 96
Above chromium recovery test recovery of standard addition: 93%~112%.

Claims (1)

1. an assay method for total chromium in underground water, is characterized in that, comprises the steps:
1) draw 1mg/L chromium standard and use solution 0mL, 1.0mL, 2.0mL, 3.0mL, 4.0mL, be placed in 100mL volumetric flask, with volume ratio be 1 part of nitric acid: the salpeter solution of 99 parts of distilled water is diluted to scale, shake up, be mixed with the standard series sample of 0ug/L, 10ug/L, 20ug/L, 30ug/L, 40ug/L;
2) sample is underground water, draws 20uL sample and standard series sample measure with 20ul microsyringe;
3) use Agilent atomic absorption spectrophotometer (AAS) 3511 graphite furnace systemic effect experimental apparatuss, regulate instrument to optimum condition, after instrument stabilizer, test instrument condition of work:
Wavelength: 357.8nm;
Lamp current: 2.0mA;
Slit: 0.2nm;
4) open argon gas source of the gas and water source, argon pressure is adjusted to 0.3MPa;
5) parameters setting in experiment:
Drying stage: 90~100 DEG C of 10~15 minutes retention times 15~20 minute heating-up time of temperature
The ashing stage: 680~720 DEG C of 15~20 minutes retention times 15~20 minute heating-up time of temperature
Atomized stage: 2800~3000 DEG C of 5~6 minutes retention times 1~2 minute heating-up time of temperature
Wash phase: 2900~3100 DEG C of 3~4 minutes retention times 2~3 minute heating-up time of temperature
6), under the best operating condition of instrument, in wavelength 357.8nm place, with blank zeroing, survey its absorbance; Taking measure absorbance as ordinate, corresponding chromium content is horizontal ordinate, drawing standard curve; Press the equal instrument condition of typical curve, with blank zeroing, measure the absorbance of sample, try to achieve the corresponding chromium content of sample, the ug/l of unit from typical curve.
CN201410163661.6A 2014-04-21 2014-04-21 Measuring method for total chrome in groundwater Pending CN103969201A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410163661.6A CN103969201A (en) 2014-04-21 2014-04-21 Measuring method for total chrome in groundwater

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410163661.6A CN103969201A (en) 2014-04-21 2014-04-21 Measuring method for total chrome in groundwater

Publications (1)

Publication Number Publication Date
CN103969201A true CN103969201A (en) 2014-08-06

Family

ID=51238967

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410163661.6A Pending CN103969201A (en) 2014-04-21 2014-04-21 Measuring method for total chrome in groundwater

Country Status (1)

Country Link
CN (1) CN103969201A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105300969B (en) * 2015-02-05 2018-04-24 温州医科大学 Chromium ion field fast detection method in a kind of water for eliminating reagent blank influence
CN113670839A (en) * 2021-08-11 2021-11-19 中国市政工程东北设计研究总院有限公司 Hexavalent chromium detection method

Non-Patent Citations (6)

* Cited by examiner, † Cited by third party
Title
何铭慈: ""石墨炉原子吸收光谱法测定环境水中的铬(Ⅲ)与铬(Ⅵ)"", 《岩矿测试》 *
北京工业大学工业水务中心、中国标准出版社第二编辑室: "《税务管理 法规 标准 规范 全书(水源环境卷)》", 31 December 2003, 中国标准出版社 *
张东霞 等: ""石墨炉原子吸收法直接测定饮用水中铬"", 《油气田地面工程》 *
田佩瑶、刘丽萍: ""石墨炉原子吸收法测定矿泉水中总铬"", 《中国卫生检验杂志》 *
陈万明 等: ""水样中总铬测定方法研究"", 《光谱实验室》 *
高舸 等: ""快速程序升温石墨炉原子吸收光谱法直接测定水中铬和银"", 《中国卫生检验杂质》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105300969B (en) * 2015-02-05 2018-04-24 温州医科大学 Chromium ion field fast detection method in a kind of water for eliminating reagent blank influence
CN113670839A (en) * 2021-08-11 2021-11-19 中国市政工程东北设计研究总院有限公司 Hexavalent chromium detection method

Similar Documents

Publication Publication Date Title
CN105987896B (en) A kind of method that micro-wave digestion-ICP-AES quickly measures hexa-atomic cellulose content in chromite simultaneously
Zhao et al. Determination of heavy metals in leather and fur by microwave plasma-atomic emission spectrometry
CN104122253B (en) The detection method of heavy metal in plastics
CN104502298B (en) A kind of measure cadmium and the method for micro lead in iron ore
CN104062284A (en) Method for determining tungsten content in ferroniobium
CN103499479A (en) Method for detecting content of heavy metal in polymeric material and sample treatment method
CN104297226A (en) Method for detecting content of aluminum and calcium in nodulizing agent by ICP-AES process
CN107525799A (en) The method of chromium content in inductively coupled plasma mass spectrometry measure indium
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
CN103969201A (en) Measuring method for total chrome in groundwater
CN107782719A (en) A kind of method for determining special medicine purposes formula food Mineral Elements in Jadeite Shellfish content
CN103837396A (en) Crystal glass digestion method and method for measuring lead content of crystal glass
CN104132933B (en) A kind of measure the method for free aluminum content in Tercod
CN104406926A (en) Detection method of trace methylmercury in alga
Özer et al. Central composite design for the optimisation of Cd and Pb determination in PVC materials by atomic absorption spectrometry after Kjeldahl digestion
CN104181147A (en) Test method for determining content of sulfur in lubrication oil
CN101639443A (en) Method for rapidly and accurately determining sulphur element content in fluorite
CN104359751B (en) Trace uranium in micro-wave digestion Soil by Flurescence
CN101451951A (en) Method for detecting content of sulfite in water by gas-phase molecular absorption spectrum
CN107367505B (en) ICP-AES method for rapidly and accurately determining content of niobium element in heat-resistant steel
CN105021692A (en) Method for simultaneously determining multiple inorganic elements in cigarette liquid of electronic cigarette
CN103604765A (en) Method for detecting chromium content in steel and iron alloy
CN104165856A (en) Method for testing content of nickel in industrial sulfuric acid by flame atomic absorption spectroscopy method
CN102466582B (en) Pretreatment method of sweetened bean paste for detection of sodium element therein and method for detecting sodium element in sweetened bean paste
CN202929013U (en) Adsorbable organic halide measurement device

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20140806

WD01 Invention patent application deemed withdrawn after publication