HJ 490-2009Water quality. Determination of silver. Spectrophotometry with cation 2B (English PDF)
水质 银的测定 镉试剂2B分光光度法
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Issued by
Ministry of Ecology and Environment
Level / Type
National · Mandatory
Issue date
September 27, 2009
Implementation date
November 1, 2009
Scope
HJ 490-2009 is the English-translated version of 水质 银的测定 镉试剂2B分光光度法.
HJ 490-2009 — This standard specifies the gamma reagent 2B spectrophotometric method for the determination of silver in water and wastewater.
This standard is applicable to silver in industrial wastewater from the production of surface water and photosensitive materials contaminated by silver, film printing, silver plating, smelting and other industries.
Determination. When the test volume is 25 ml and the optical path is 10 mm cuvette, the detection limit of this method is 0.01 mg/L, and the lower limit of determination is 0.04 mg/L. The upper limit of determination is 0.8 mg/L.
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Document preview — HJ 490-2009
National Standard of the People's Republic of China
- ICS
- 13.060
- Classification
- Z 16
- Replacing
- GB/T 11908-1989
Issued by: Ministry of Ecology and Environment
Contents
- Foreword
- 1 Scope of application
- 2 Principle of the method
- 3 Reagents and materials
- 3.8 EDTA-2Na solution, rho (EDTA-2Na)=0.05 mol/L. dissolve 1.86 g EDTA-2Na (C10H14N2O3Na2·2H2O)
- 4 Instruments and equipment
- 5 Interference and elimination
- 6 Samples
- 6.1 Acquisition and preservation
- 6.2 Preparation of samples
- 7 Analysis steps
- 7.1 Calibration curve
- 7.2 Sample determination
- 8 Representation of the result
- 9 Precision and accuracy
- 9.1 Repeatability
- 9.2 Reproducibility
- 9.3 Accuracy
Foreword
To protect the environment and protect the human body in order to implement the Environmental Protection Law of the People's Republic of China and the Law of the People's Republic of China on Water Pollution Prevention and Control this standard is developed for the monitoring of health and the regulation of silver in water and wastewater.
This standard specifies the method for determining silver in water and wastewater.
This standard amends the "Measurement of mercury in water, cadmium reagent 2B spectrophotometry" (GB 11908-89), drafted the original standard the unit is China Environmental Monitoring Station, first published in 1989, this is the first revision.
The main revisions are as follows.
-- Increase coexisting ion interference and elimination and adjust and revise the standard text.
From the date of implementation of this standard, the national environmental protection standard "Water" approved and issued by the former National Environmental Protection Agency on December 25, 1989 Determination of steric silver cadmium reagent 2B spectrophotometry (GB 11908-89) abolished.
This standard was formulated by the Science and Technology Standards Department of the Ministry of Environmental Protection.
This standard is mainly drafted by. China Environmental Monitoring Center.
This standard was approved by the Ministry of Environmental Protection on September 27, 2009.
This standard has been implemented since November 1, 2009.
This standard is explained by the Ministry of Environmental Protection.
Determination of mercury in water quality - Cadmium reagent 2B spectrophotometric method
1 Scope of application
This standard specifies the gamma reagent 2B spectrophotometric method for the determination of silver in water and wastewater.
This standard is applicable to silver in industrial wastewater from the production of surface water and photosensitive materials contaminated by silver, film printing, silver plating, smelting and other industries.
Determination.
When the test volume is 25 ml and the optical path is 10 mm cuvette, the detection limit of this method is 0.01 mg/L, and the lower limit of determination is 0.04 mg/L.
The upper limit of determination is 0.8 mg/L.
2 Principle of the method
In the sodium tetraborate buffer medium in the presence of Triton X-100, the complex ratio of cadmium reagent 2B to silver ions is a 4.1 stable magenta complex that is stable for at least 24 h and the color intensity is proportional to the concentration of silver, the complex the maximum absorption wavelength is 554 nm; cadmium reagent 2B is a brown solid powder, which exists in molecular form in a weak acid or alkaline medium.
The agent is yellow with a maximum absorption wavelength of 445 nm.
3 Reagents and materials
The reagents used in this standard are analyzed using analytical reagents in accordance with national standards, unless otherwise stated.
Deionized water or distilled water.
3.1 Nitric acid (HNO3). rho = 1.40 g/ml.
3.2 Sulfuric acid (H2SO4). rho = 1.84 g/ml.
3.3 Perchloric acid (HClO4). rho = 1.68 g/ml.
3.4 Hydrogen peroxide (H2O2). 30%.
3.5 Ethanol (C2H5OH). 95%.
3.6 Nitric acid (HNO3) 1 1 Solution. Add 50 ml of nitric acid (3.1) to 50 ml of water and mix.
3.7 Sodium hydroxide (NaOH) solution, rho (NaOH) = 1 mol/L. Weigh 40 g of sodium hydroxide dissolved in water and dilute to 1 L.
3.8 EDTA-2Na solution, rho (EDTA-2Na)=0.05 mol/L. dissolve 1.86 g EDTA-2Na (C10H14N2O3Na2·2H2O)
In water, and dilute to 100 ml.
3.9 Sodium tetraborate solution, rho (Na2B4O7)=50 g/L. Dissolve 10 g of sodium tetraborate (Na2B4O7·10H2O) in water and dilute to 200 ml.
3.10 Qu Li Tong X-100 solution, rho (Qu Li Tong X-100) = 5% (volume fraction). 5 ml Qu Li Tong X-100 [Triton X-100, (CH3)3CCH2C(CH3)2-C6H4(OCH2CH2)nOHn~10] is dissolved in 95 ml of water and allowed to dissolve by heating.
3.11 Cadmium reagent 2B Ethanol solution, rho (cadmium reagent 2B) = 0.4 g/L. dissolve 0.080 g cadmium reagent 2B (4-nitronaphthyldiazoaminoazo) Benzene, O2NC10H6N. NNHC6H4N. NC6H5) In.200 ml of ethanol (3.5), add 2 drops of sodium hydroxide solution (3.7), use 4 the sand core funnel was filtered to remove insolubles.
3.12 Silver standard stock solution, rho (Ag)=1.00 mg/ml. accurately weigh 0.157 5 g silver nitrate (AgNO3), dissolve in appropriate amount of water, add 2 ml nitric acid solution (3.6). After dissolving, transfer to a 100 ml volumetric flask and dilute to the mark with water. Store in a brown glass bottle, protected from light, at least one month stable.
3.13 Silver standard solution, rho (Ag)=0.100 mg/ml. Transfer 10.00 ml of silver standard stock solution (3.12) to a 100 ml volumetric flask.
Add 2 ml of nitric acid solution (3.6) and dilute to the mark with water. Store in a brown glass bottle protected from light.
3.14 Silver standard solution, rho (Ag)=4.0 µg/ml. Transfer 20.00 ml silver standard solution (3.13) to a 500 ml volumetric flask for use Dilute the water to the mark and prepare it before use.
3.15 methyl orange solution, w (methyl orange) = 10%. Dissolve 0.010 g of methyl orange in water and dilute to 100 ml.
4 Instruments and equipment
4.1 Spectrophotometer and 10 mm quartz cuvette.
4.2 pH meter.
4.3 Volumetric flasks. 50, 100, 500, 1 000 ml.
5 Interference and elimination
Without the masking agent EDTA, under these conditions, Na, B4O72-, PO3- each 100 mg, K, Ca2, Mg2, NH4, NO3-, SO42-, PO43-, citrate 10 mg each, As3, WO42-, MoO42-, ClO4-, BrO3-, IO3-, S2O82- each 1.0 mg and 0.1 mg of Be2, Cr6, SeO32-, TeO32-, VO3- does not interfere with the determination of 10 µg Ag, a small amount of Cd2, Hg2, Zn2, Ni2, There is positive interference in Cu2, etc., but adding 0.5 ml of 0.05 mol/L EDTA-2Na solution can at least mask Cd2, Cu2, Ni2, Zn2, Pb2, 1.0 mg of Mn2, Fe3, Fe2, and La3, and 100 µg of each of Co2, Hg2, Al3, Cr3, Pd2, and Y3. 10 µg Ag Impact.
6 Samples
6.1 Acquisition and preservation
The water sample of silver was measured, collected and stored in a polyethylene bottle, and the water sample was acidified to pH 1-2 with concentrated nitric acid and analyzed as soon as possible.
Wastewater from the production of photosensitive materials, film processing, silver plating, etc., no acid is added after sample collection, and analysis is performed immediately.
Water samples collected should be protected from light.
6.2 Preparation of samples
Unless it is proved that the pretreatment of the sample is unnecessary, the sample may be directly prepared for colorimetry, otherwise the pretreatment should be carried out as follows.
Take 25.0 ml of the homogeneous sample in a 100 ml beaker. If the concentration of silver exceeds 0.8 mg/L, the sample may be appropriately reduced and diluted with water until 25 ml. In the sample, 4 ml of nitric acid (3.1), 1 ml of sulfuric acid (3.2) and 0.5 ml of hydrogen peroxide (3.4) were added in sequence. On the hot plate Heat slowly to white smoke. After removing the cooling, add 1 ml of perchloric acid, cover the watch glass, and continue to heat until near dry. After cooling, add 0.5 ml Nitric acid (3.6), rinse the cup wall with a little water and dissolve the residue slightly. Then, carefully wash into a 25 ml volumetric flask, the volume of the solution should not exceed Over 15 ml.
Samples with precipitates or suspended solids, such as photosensitive materials, printing waste water, etc., should be sampled as evenly as possible.
The sample is complex, contains more organic matter, or precipitates, and can be repeatedly digested with nitric acid. Compared with clean samples, nitric acid and perchloric acid are eliminated.
Just solve it. In the digestion process, it is not suitable to evaporate. Otherwise, silver has a loss.
That is, the water sample is acidified to pH 1-2 using concentrated nitric acid, which is not suitable for storage, and should be analyzed as soon as possible. Especially for printing wastewater, after sample collection, Samples should be prepared for analysis without acid.
7 Analysis steps
7.1 Calibration curve
7.1.1 Add 0.00, 0.50, 1.00, 2.00, 3.00, 4.00, 5.00 ml silver standard solution (3.14) to each of the 7 25 ml volumetric flasks.
7.1.2 Add 0.5 ml of EDTA-2Na solution (3.8) to the above volumetric flask, add 1 drop of methyl orange indicator (3.15), and use hydrogen and oxygen.
The sodium solution (3.7) was adjusted until the indicator just turned yellow. Add 2 ml of sodium tetraborate solution (3.9), 1.0 ml of Triton X-100 solution (3.10) and 1.5 ml cadmium reagent 2B ethanol solution (3.11). Dilute to the mark with water and shake well. After 10 min, use 10 mm colorimetric the dish was measured at 554 nm and the absorbance was measured. The absorbance of the reagent blank (zero concentration) was measured with water as a reference. To subtract the reagent empty the absorbance after white (zero concentration) is plotted against the silver content (µg).
7.2 Sample determination
Accurately pipette 1 to 15 ml of the test sample (depending on the silver content in the water) in a 25 ml volumetric flask, as described below in 7.1.2. From the calibration curve the amount of silver in the sample is determined online or calculated using a regression equation.
8 Representation of the result
The silver mass concentration is calculated as follows.
rho = m
Where. rho - the mass concentration of silver in the sample, mg/L;
m -- the silver content of the sample obtained by the calibration curve or calculated by the regression equation, µg;
V--sample volume taken, ml.
9 Precision and accuracy
Four laboratories analyzed a uniform sample containing 1.00 mg/L of silver in distilled water (sample plus ammonia and cyanogen iodide).
9.1 Repeatability
The relative standard deviation of repeatability was 2.2%.
9.2 Reproducibility
The relative standard deviation of reproducibility was 4.0%.
9.3 Accuracy
The relative error is -0.2%.
......
This preview omits tables, figures, formulas and parts of the technical clauses. The complete document — 7 pages — is available in the English PDF.
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