Valid

HJ 786-2016Solid waste. Determination of Lead, Zinc and Cadmium. Flame atomic absorption spectrometry (English PDF)

固体废物 铅、锌和镉的测定 火焰原子吸收分光光度法

Preview PDF

This is a limited preview

Buy now to download the full PDF (12 pages)

Need quotation for your management?

Get a formal quotation for HJ 786-2016 in 30 minutes.

Issued by

Ministry of Ecology and Environment

Level / Type

National · Mandatory

Issue date

March 29, 2016

Implementation date

May 1, 2016

Scope

HJ 786-2016 is the English-translated version of 固体废物 铅、锌和镉的测定 火焰原子吸收分光光度法.

HJ 786-2016 — This standard specifies the flame atomic absorption spectrophotometric method for the determination of lead, zinc and cadmium in solid waste and solid waste leachate.

This standard applies to the determination of lead, zinc and cadmium in solid waste and solid waste leachate. When the amount of solid waste is 0.5 g and the volume is 25 ml after digestion, the limits of lead, zinc and cadmium 2.0 mg/kg, 2.0 mg/kg and 0.3 mg/kg, respectively.

The lower limit of determination was 8.0 mg/kg, 8.0 mg/kg and 1.2 mg/kg, respectively. when the amount of lead, zinc and cadmium is limited when the volume of solid waste leachate is 50 ml and the volume is 50 ml after digestion.

0.06 mg/L, 0.06 mg/L and 0.05 mg/L, respectively. The lower limit of determination was 0.24 mg/L, 0.24 mg/L and 0.20 mg/L, respectively.

Found what you need?

Document preview — HJ 786-2016

National Standard of the People's Republic of China

Classification
Z 13

Issued by: Ministry of Ecology and Environment

Contents

  • Preface
  • 1 Scope of application
  • 2 Normative reference documents
  • 3 Principle of the method
  • 4 Interference and elimination
  • 5 Reagents and materials
  • 6 Instruments and equipment
  • 7 Samples .4
  • 8 Analysis steps
  • 9 Results calculation and representation
  • 10 Precision and Accuracy
  • 11 Quality assurance and quality control
  • 12 Waste treatment
  • 13 Precautions
  • Appendix A (informative) Standard Addition Act
  • Appendix B (informative) method of precision and accuracy

Foreword

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 the Prevention and Control of Environmental Pollution by Solid Wastes, Protect the environment, protect human health, regulate the determination of lead, zinc and cadmium in solid waste and solid waste leachate.

This standard.

This standard specifies the flame atomic absorption spectrophotometric method for the determination of lead, zinc and cadmium in solid waste and solid waste leachate.

This standard is the first release.

Appendix A and Appendix B of this standard are informative.

This standard is organized by the Ministry of Environmental Protection Science and Technology Standards Division.

The main drafting unit of this standard. Jiangsu Province Environmental Monitoring Center, Environmental Protection Department of Environmental Standards Institute.

The standard verification unit. Nanjing Environmental Monitoring Center Station, Zhejiang Province Environmental Monitoring Center, Shanghai Environmental Monitoring Center, Changzhou City Environmental Monitoring Center Station, Ma On Shan City Environmental Monitoring Center Station, Lianyungang City Environmental Monitoring Center Station.

The environmental protection department of this standard approved on March 29, 2016.

This standard has been implemented since May 1, 2016.

This standard is explained by the Ministry of Environmental Protection.

Solid waste - Determination of lead, zinc and cadmium - Flame atomic absorption spectrophotometric method Warning. nitric acid used in the experiment, perchloric acid with strong oxidizing and corrosive, hydrochloric acid, hydrofluoric acid with strong volatile and corrosive, the operation should be required to wear protective equipment, solution preparation and sample pretreatment process should be in the fume hood into Line operation.

1 Scope of application

This standard specifies the flame atomic absorption spectrophotometric method for the determination of lead, zinc and cadmium in solid waste and solid waste leachate.

This standard applies to the determination of lead, zinc and cadmium in solid waste and solid waste leachate.

When the amount of solid waste is 0.5 g and the volume is 25 ml after digestion, the limits of lead, zinc and cadmium 2.0 mg/kg, 2.0 mg/kg and 0.3 mg/kg, respectively. The lower limit of determination was 8.0 mg/kg, 8.0 mg/kg and 1.2 mg/kg, respectively. when the amount of lead, zinc and cadmium is limited when the volume of solid waste leachate is 50 ml and the volume is 50 ml after digestion.

0.06 mg/L, 0.06 mg/L and 0.05 mg/L, respectively. The lower limit of determination was 0.24 mg/L, 0.24 mg/L and 0.20 mg/L, respectively.

2 Normative reference documents

The contents of this standard refer to the following documents or their terms. Those who do not specify the date of the reference file, the effective version of the appropriate for this standard.

Technical specification for SJ sample preparation for industrial solid waste Technical Specification for Hazardous Waste Identification HJ/T 299 Solid waste leaching toxicity leaching method sulfuric acid nitric acid method HJ/T 300 solid waste leaching toxicity leaching method acetic acid buffer solution method HJ 557 Solid waste leaching toxicity leaching method Horizontal oscillation method

3 Principle of the method

Solid waste or solid waste leachate dissolved by acid, the sample of the test element in the flame atomizer was dissociated into the ground state atom, the ground state of the vapor on the element of the hollow cathode lamp or electrodeless discharge lamp emission characteristics of the radiation line selectivity absorb. In a certain concentration range, the absorption intensity and the sample to be measured in proportion to the mass concentration.

4 Interference and elimination

4.1 When the calcium content is higher than 1000 mg/L, the inhibition of cadmium absorption; calcium content of 2000 mg/L, the signal inhibition of 19%.

Iron content of more than 100 mg/L, inhibition of zinc absorption, adding lanthanum nitrate can eliminate the interference of coexisting components. When the sample is salt A high level of analysis of spectral wavelengths below 350 nm occurs when non-characteristic absorption, such as high concentrations of calcium is generated by background absorption of lead the results of the determination of high.

4.2 When the sample matrix composition is complex or unknown, or spike recovery rate exceeds the scope of the method of control requirements, should be used standard the addition method is used to determine the sample and calculate the results, see Appendix A.

5 Reagents and materials

Unless otherwise stated, analytical reagents conforming to national standards are used in the analysis, and the test water is a newly prepared deionized water.

5.1 sulfuric acid. rho (H2SO4) = 1.84 g/ml, excellent grade pure.

5.2 nitric acid. rho (HNO3) = 1.42 g/ml, excellent grade pure.

5.3 hydrochloric acid. rho (HCl) = 1.19 g/ml, excellent grade pure.

5.4 hydrofluoric acid. rho (HF) = 1.49 g/ml, excellent grade pure.

5.5 perchloric acid. rho (HClO4) = 1.68 g/ml, excellent grade pure.

5.6 Hydrogen peroxide. phi (H2O2) = 30%, excellent grade pure.

5.7 Metal Lead. Spectrum Pure.

5.8 Metal Zinc. Spectrum Pure.

5.9 Cadmium. Spectrum pure.

5.10 lanthanum nitrate [La (NO3) 3 · 6H2O]. excellent grade pure.

5.11 nitric acid solution. 1 9 (v/v), prepared with nitric acid (5.2).

5.12 nitric acid solution. 1 99 (v/v), prepared with nitric acid (5.2).

5.13 hydrochloric acid solution. 1 1 (v/v), prepared with hydrochloric acid (5.3).

5.14 Substrate modifier. lanthanum nitrate solution, [La (NO3) 3 · 6H2O] = 5%.

Accurately weigh 5 g (accurate to 0.01 g) lanthanum nitrate (5.10), dissolve with nitric acid solution (5.12) and set to 100 ml Capacity bottle, spare.

5.15 lead standard stock solution. rho = 1000 mg/L.

Accurately weigh 1.000 g (accurate to 0.0001 g) of metal lead (5.7), add 15 ml of nitric acid (5.2) to dissolve, if necessary can be dissolved by heating. The whole volume into the 1000 ml volumetric flask, the water volume to the mark, shake. Transfer to a polyethylene bottle at 4 ° C Under the cold storage, sealed can be saved for two years. A commercially available standard solution (lead element or lead-containing multi-element mixing standard may also be used Solution).

5.16 zinc standard stock solution. rho = 1000 mg/L.

Accurately weigh 1.000 g (exactly to 0.0001 g) of metal zinc (5.8), add 15 ml of nitric acid (5.2) to dissolve, if necessary can be dissolved by heating. The whole volume into the 1000 ml volumetric flask, the water volume to the mark, shake. Transfer to a polyethylene bottle at 4 ° C Under the cold storage, sealed can be saved for two years. A commercially available standard solution (zinc single element or zinc-containing multi-element mixing standard can also be used Solution).

5.17 cadmium standard stock solution. rho = 1000 mg/L.

Accurately weigh 1.000 g (accurate to 0.0001 g) of metal cadmium (5.9), add 15 ml of nitric acid (5.2) to dissolve, if necessary can be dissolved by heating. The whole volume into the 1000 ml volumetric flask, the water volume to the mark, shake. Transfer to a polyethylene bottle at 4 ° C Under the cold storage, sealed can be saved for two years. A commercially available standard solution (cadmium single element or cadmium-containing multi-element mixing standard) can also be used Solution).

5.18 lead standard use of liquid. rho = 100 mg/L.

Accurate removal of lead standard stock solution (5.15) 10.00 ml in 100 ml volumetric flask, with nitric acid solution (5.12) constant volume to standard Line, shake well. Pro is now available.

5.19 zinc standard use of liquid. rho = 100 mg/L.

Accurate removal of zinc standard stock solution (5.16) 10.00 ml in 100 ml volumetric flask, with nitric acid solution (5.12) constant volume to standard Line, shake well. Pro is now available.

5.20 cadmium standard use of liquid. rho = 100 mg/L.

Accurate removal of cadmium standard stock solution (5.17) 10.00 ml in 100 ml volumetric flask, with nitric acid solution (5.12) constant volume to standard Line, shake well. Pro is now available.

5.21 Acetylene. purity >=99.5%.

5.22 Air. available from air compressor or compressed air cylinders.

6 Instruments and equipment

6.1 flame atomic absorption spectrophotometer.

6.2 lead hollow cathode lamp, zinc hollow cathode lamp, cadmium hollow cathode lamp.

6.3 air compressor, should be equipped with water, degreasing and dust removal device.

6.4 hot plate or graphite digestion. a temperature control function (temperature stability ± 5 °C), the maximum temperature can be set to.200 °C.

6.5 microwave digestion. output power of 1000 W ~ 1600 W. With programmable control function, can be temperature, pressure and time (Heating time and holding time) to monitor the whole; with security features.

6.6 Analytical balance. 0.1 mg accuracy.

6.7 Polytetrafluoroethylene crucible. 50 ml.

6.8 Screen. non-metallic sieve, 100 mesh.

6.9 General laboratory equipment and equipment commonly used.

7 Samples

7.1 Sample collection and storage

The collection and storage of solid waste samples are carried out in accordance with the relevant provisions of HJ/T 20 and HJ/T 298.

7.2 Sample preparation

7.2.1 Solid waste

The preparation of solid waste samples was carried out in accordance with the relevant provisions of HJ/T 20. For solid waste or dry semi-solid waste Product, accurately weighed 10 g (m1, accurate to 0.01 g) sample, naturally air-dried or freeze-dried, weighing again (m2, accurate to 0.01 g), grinding, all over 100 mesh sieve (6.7) standby.

7.2.2 Solid waste leachate

The preparation of solid waste leachate was carried out in accordance with the relevant provisions of HJ/T 299, HJ/T 300 or HJ 557. Leaching solution if not can be timely analysis, should be added nitric acid (5.2) acidification to pH 8 Analysis steps

8.1 Instrument reference conditions

Different models of flame atomic absorption spectrophotometer the best measurement conditions are different, according to the instrument manual Test conditions. The instrument reference measurement conditions are shown in Table 3.

Table 3 Instrument reference measurement conditions

Elemental Lead (Pb) Zinc (Zn) Cadmium (Cd) Determination of wavelength (nm) 283.3 213.9 228.8 Passband width (nm) 0.5 1.0 0.5 Lamp current (mA) 8.0 5.0 5.0 Flame Type Acetylene - Air, Neutral Acetylene - Air, Poor Combustion Acetylene - Air, Lean Burn

8.2 Standard curve drawing

8.2.1 Lead Standard Curve Series

Accurate removal of 0.00 ml, 0.50 ml, 1.00 ml, 2.00 ml, 4.00 ml, 8.00 ml and 10.0 ml lead standards (5.18) in a group of 100 ml volumetric flask, with nitric acid solution (5.12) constant volume to the marking, shake. This standard series contains Lead were 0.00 mg/L, 0.50 mg/L, 1.00 mg/L, 2.00 mg/L, 4.00 mg/L, 8.00 mg/L and 10.0 mg/L, respectively.

According to the instrument reference conditions (8.1), with nitric acid solution (5.12) to adjust the instrument zero, from low concentration to high concentration followed by suction Into the standard series, measuring the corresponding absorbance, with the corresponding absorbance as the ordinate to lead standard series of mass concentration for the abscissa, Establish lead calibration curve.

8.2.2 Zinc Standard Curve Series

Accurately remove 0.00 ml, 0.50 ml, 1.00 ml, 2.00 ml, 3.00 ml, 4.00 ml and 5.00 ml zinc (5.19) in a group of 100 ml volumetric flask, with nitric acid solution (5.12) constant volume to the mark, shake. This standard series contains Zinc were 0.00 mg/L, 0.50 mg/L, 1.00 mg/L, 2.00 mg/L, 3.00 mg/L, 4.00 mg/L and 5.00 mg/L, respectively.

According to the instrument reference conditions (8.1), with nitric acid solution (5.12) to adjust the instrument zero, from low concentration to high concentration followed by suction Into the standard series, measuring the corresponding absorbance, with the corresponding absorbance as the ordinate to zinc standard series of mass concentration for the abscissa, Establish a calibration curve for zinc.

8.2.3 Cadmium standard curve series

Respectively, accurate removal of 0.00 ml, 0.50 ml, 1.00 ml, 2.00 ml, 3.00 ml, 4.00 ml and 5.00 ml cadmium Liquid (5.20) in a group of 100 ml volumetric flask, with nitric acid solution (5.12) constant volume to the mark, shake. This standard series contains Cadmium were 0.00 mg/L, 0.50 mg/L, 1.00 mg/L, 2.00 mg/L, 3.00 mg/L, 4.00 mg/L and 5.00 mg/L, respectively.

According to the instrument reference conditions (8.1), with nitric acid solution (5.12) to adjust the instrument zero, from low concentration to high concentration followed by suction Into the standard series, measuring the corresponding absorbance, with the corresponding absorbance as the ordinate, cadmium standard series of mass concentration for the abscissa, Establish cadmium calibration curve.

8.3 Blank sample determination

Prepare a blank sample (7.3.3) and perform the same conditions as the calibration curve.

8.4 Sample determination

The prepared sample (7.3.1 or 7.3.2) was subjected to the same conditions as the established calibration curve.

9 Results calculation and representation

9.1 Results calculation

9.1.1 Solid waste
9.1.1.1 Solid or dry semi-solid solid waste

The content of the element to be measured in solid waste (mg/kg) Calculated according to formula (1) ( ) x -(1) where. - the content of the element to be measured in the solid waste, mg/kg;

- Check the mass concentration of the element in the sample by the calibration curve, mg/L;

0_1 - Mass concentration in the laboratory blank sample, mg/L;

0V - volume of the sample after digestion, ml;

1m - the amount of solid waste sample weighed before drying, g;

2m - the quality of solid waste samples after drying, g;

3m - the amount of sample to be sintered after grinding, g.

9.1.1.2 Semi-solid solid waste with or without drying

The content of the element to be measured in solid waste (mg/kg) Calc...

......
This preview omits tables, figures, formulas and parts of the technical clauses. The complete document — 12 pages — is available in the English PDF.

Referenced standards

How to Download HJ 786-2016

  1. 1

    Add to cart

    Click "Download PDF" on this page and choose "Buy this standard". You can add more standards before checkout.

  2. 2

    Checkout

    Enter your email and billing details. Payment is processed securely by Stripe (cards or bank transfer). Prefer bank details? Request a quotation (min. order $300).

  3. 3

    Instant delivery (0–9 sec)

    Delivery is automatic: within seconds of payment you'll receive an email with a secure download link. The link stays valid for 72 hours.

  4. 4

    Invoice included

    A tax invoice is attached to the confirmation email. Need a custom invoice? Contact us.

Related Standards

English PDF
12 pages
Instant delivery (0–9 sec)
Invoice included
View Cart

Secure payment via Stripe

Payments accepted

VisaMastercardAmerican ExpressApple PayGoogle PayStripe

HJ 786-2016

$240.00