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GB/T 44741-2024: Determination methods of soil bioavailable arsenic at the origin of agricultural products
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GB/T 44741-2024: Determination methods of soil bioavailable arsenic at the origin of agricultural products

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National Standard of the People's Republic of China ICS 13.080.99CCS B 10 Determination of available arsenic in soil of agricultural product production areas Determination methods of soil bioavailable arsenic at the origin of agricultural products Released on October 26, 2024 2025-02-01 Implementation State Administration for Market Regulation The National Standardization Administration issued

Table of Contents

Preface Ⅲ 1 Scope...1 2 Normative references 1 3 Terms and Definitions 1 4 Method Principle 1 5 Reagents and Materials 1 6 Instruments and Equipment 2 7 Soil sample collection and pretreatment 2 8 Steps 2 9 Result calculation and presentation 3 10 Precision 3 Appendix A (Informative) Reference Working Conditions for Hydride Generation Atomic Fluorescence Spectrometer 4 References 5 Preface This document is in accordance with the provisions of GB/T 1.1-2020 "Guidelines for standardization work Part 1.Structure and drafting rules for standardization documents" Drafting is required. Please note that some of the contents of this document may involve patents. The issuing organization of this document does not assume the responsibility for identifying patents. This document is proposed by the Ministry of Agriculture and Rural Affairs of the People's Republic of China. This document is under the jurisdiction of the National Technical Committee on Soil Quality Standardization (SAC/TC 404). This document was drafted by. Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Institute of Eco-Environmental Sciences and Soil Sciences, Guangdong Academy of Sciences, Tianjin Renewable Resources Research Institute of the Supply and Marketing Cooperatives, Hebei Agricultural University, Nanjing Institute of Soil Science, Chinese Academy of Sciences, Jiangsu Provincial Quality and Standardization Administration Research Institute, Institute of Agricultural Resources and Agricultural Regional Planning, Chinese Academy of Agricultural Sciences, and Shandong University. The main drafters of this document are. Duan Guilan, Wang Zewen, Zhu Yongguan, Li Man, Yuan Yuzhen, Liu Wenju, Zhao Bin, Li Fangbai, Yang Yuping, Duan Zengqiang, Chen Meijun, Hou Yueli, Chen Shibao, Cui Zhaojie, Li Man, Chen Peng, Yao Baomin, Jin Chunxiao, Fang Liping, and Yang Haoyu. Determination of available arsenic in soil of agricultural product production areas

1 Scope

This document describes a method for determining the available arsenic content in soils from agricultural product production areas using atomic fluorescence spectrometry. This document is applicable to the determination of available arsenic in cultivated land (dry land, irrigated land and paddy field) soil. The detection limit of the method in this document is 0.5 mg/kg. 2 Normative references The contents of the following documents constitute the essential clauses of this document through normative references in this document. For referenced documents without a date, only the version corresponding to that date applies to this document; for referenced documents without a date, the latest version (including all amendments) applies to This document. GB/T 36197 Soil quality - Guide to soil sampling techniques 3 Terms and Definitions The following terms and definitions apply to this document. 3.1 soil bioavailable arsenic Arsenic in farmland soil can be absorbed by plants and pose a risk to agricultural product safety. 4 Principles of the Method The phosphate ions in the ammonium dihydrogen phosphate solution were used to replace the arsenate ions in the dryland and irrigated land soil samples, and the effective Arsenic; or use dilute nitric acid solution to dissolve and extract the available arsenic in paddy field soil samples. Add thiourea to the leaching solution to reduce pentavalent arsenic to trivalent arsenic. The valence arsenic is then reduced to arsenic by adding potassium borohydride, which is then introduced into a quartz atomizer for atomization and decomposition into atomic arsenic. The arsenic hollow cathode lamp produces atomic fluorescence under the excitation of the emission light. The intensity of the fluorescence is proportional to the content of the measured arsenic element in the extract. By comparing with the standard series, the arsenic content in the extract was obtained, and the available arsenic content in the soil was calculated. 5 Reagents and Materials Unless otherwise stated, only reagents of confirmed analytical grade and distilled or deionized water or water of equivalent purity were used in the analyses. 5.1 Ammonium dihydrogen phosphate extractant [c(NH4H2PO4)=0.05 mol/L]. Weigh 5.75 g of ammonium dihydrogen phosphate into a beaker and add 800 mL Transfer all the liquid in the beaker to a 1000 mL volumetric flask, dilute to the mark, and shake well. 5.2 Dilute nitric acid extraction agent [c(HNO3)=0.43 mol/L]. Take 30 mL of nitric acid and slowly pour it into a beaker containing 100 mL of water. Stir well. Transfer all the liquid in the beaker to a 1000 mL volumetric flask, dilute to the mark, and shake well. 5.3 2% potassium borohydride (KBH4) 0.35% potassium hydroxide (KOH) solution. Weigh 0.35 g of potassium hydroxide into a beaker and add 10 mL Dissolve in water, weigh 2.00 g of potassium borohydride and put it into potassium hydroxide solution, stir until completely dissolved, and transfer all the liquid in the beaker to 100 mL Add to a volumetric flask, bring to volume, and shake well. Prepare immediately before use. Note. This is a reducing agent solution. 5.4 (19) Hydrochloric acid (HCl) solution. Take 100 mL of hydrochloric acid and slowly pour it into a beaker containing 100 mL of water. Stir well and add 100 mL of water to the beaker. ...