ms质谱检测标准ms质谱-中析研究所检测

(CMA)

(CNAS)

(ISO)

(高新技术企业)

ms质谱相关标准参考信息

GB/T 37185-2018 气体分析室内挥发性有害有机物的测定 “SUMMA罐-硅烷化管”采样气相色谱/质谱联用（GC/MS）法
简介：
信息：ICS：71.040.40 CCS：G86 发布：2018-12-28 00:00:00.0 实施：2019-11-01 00:00:00.0

ASTM D7979-20 通过液相色谱串联质谱法（LC/MS/MS）测定水污泥流入物流出物和废水中的全氟烷基物质的标准测试方法
简介：
信息：ICS：13.060.50 CCS：发布：2020-08-15 实施：

ASTM D8024-16 通过多重反应监测液相色谱/质谱（LC/MS/MS）测定水中（三正丁基） - 十四烷基氯化鏻（TTPC）的标准试验方法
简介：
信息：ICS：13.060.50 CCS：发布：2016-06-01 实施：

ASTM D8399-22 使用液相色谱-串联质谱法（LC-MS/MS）对干大麻和大麻原料中农药的多残留分析的标准试验方法
简介：
信息：ICS： CCS：发布：2022-07-01 实施：

ASTM D8310-20 用多重反应监测液相色谱/质谱法（LC/MS/MS）分析土壤中目标酚（TPs）的标准试验方法
简介：
信息：ICS：13.080.10 CCS：发布：2020-02-01 实施：

ASTM E2787-11(2016) 使用加压流体萃取法测定土壤中硫二甘醇的标准测试方法随后采用单反应监测液相色谱/串联质谱（LC/MS/MS）
简介：
信息：ICS：13.080.10 CCS：发布：2016-06-01 实施：

ASTM D8456-22 用液相色谱-串联质谱法（LC-MS/MS）测定水中亚硝胺的标准试验方法
简介：
信息：ICS： CCS：发布：2022-05-01 实施：

ASTM D8018-15(2020) 通过多重反应监测液相色谱/质谱法（LC/MS/MS）测定土壤中（三正丁基） - 正十四烷基氯化鏻（TTPC）的标准试验方法
简介：
信息：ICS：13.080.10 CCS：发布：2020-02-01 实施：

ASTM D7979-16 通过液相色谱串联质谱（LC/MS/MS）测定水污泥流入物流出物和废水中全氟化合物的标准测试方法
简介：
信息：ICS：13.060.50 CCS：发布：2016-06-01 实施：

ASTM D8421-22 用共溶剂化和液相色谱串联质谱法（LC/MS/MS）测定水基质中全氟和多氟烷基物质（PFA）的标准试验方法
简介：
信息：ICS：71.040.50 CCS：发布：2022-05-01 实施：

ASTM D7979-19 通过液相色谱串联质谱法（LC/MS/MS）测定水污泥流入物流出物和废水中的全氟烷基物质的标准测试方法
简介：
信息：ICS：13.060.50 CCS：发布：2019-11-01 实施：

ASTM E2838-11(2016) 通过液相色谱/串联质谱法（LC/MS/MS）通过溶剂萃取测定湿巾上硫二甘醇的标准测试方法
简介：
信息：ICS：97.080 CCS：发布：2016-06-01 实施：

ASTM D8421-21 液相色谱-串联质谱法（LC/MS/MS）后用共溶剂化法测定水基质中全氟和多氟烷基物质（PFA）的标准试验方法
简介：
信息：ICS： CCS：发布：2021-11-01 实施：

ISO 21675-2019 水质.水中全氟烷基和多氟烷基物质（PFAS）的测定.固相萃取和液相色谱-串联质谱法（LC-MS/MS）
简介：
信息：ICS：13.060.50 CCS：发布：2019-10-26 实施：

NF V03-189-2016 婴儿配方奶粉和成人营养品. 采用超高液相色谱和串联质谱法 (UHPLC-MS/MS) 测定泛酸
简介：
信息：ICS：67.050;67.230 CCS：X16 发布：2016-03-03 实施：2016-03-03

ISO 11916-3:2021 土壤质量.选定炸药和相关化合物的测定.第3部分:液相色谱-串联质谱法（LC-MS/MS）
简介：
信息：ICS：13.080.10 CCS：发布：2021-09-17 实施：

ISO 21676:2018 水质.水和处理废水中选定活性药物成分、转化产物和其他有机物质的溶解分数的测定.直接注射后使用高效液相色谱和质谱检测（HPLC-MS/MS或-HRMS）的方法
简介：
信息：ICS：13.060.50 CCS：发布：2018-10-15 实施：

ASTM D7645-16 通过液相色谱/串联质谱法（LC/MS/MS）测定水中涕灭威涕灭威砜涕灭威亚砜呋喃呋喃甲氧基氧杂甲基和硫氧化物的标准测试方法
简介：
信息：ICS：13.060.50 CCS：发布：2016-02-01 实施：

ISO 23970:2021 牛奶、奶制品和婴儿配方奶粉.用液相色谱和串联质谱法（LC-MS/MS）测定三聚氰胺和三聚氰酸
简介：
信息：ICS：67.100.10 CCS：发布：2021-09-16 实施：

ISO 23702-1-2018 皮革.有机氟.第1部分:用液相色谱/串联质谱检测器（LC-MS/MS）萃取法测定非挥发性化合物含量
简介：
信息：ICS：59.140.30 CCS：发布：2018-10-09 实施：

ASTM D7644-16 通过液相色谱/串联质谱（LC/MS/MS）测定水中的溴马醇 Brodifacoum Diphacinone和华法林的标准测试方法
简介：
信息：ICS：13.060.50 CCS：发布：2016-02-01 实施：

IEC 62321-3-3:2021 电工产品中某些物质的测定.第3-3部分:筛选.使用热解/热脱附附件（Py/TD？GC？MS）通过气相色谱-质谱法测定聚合物中的多溴联苯、多溴二苯醚和邻苯二甲酸酯
简介：
信息：ICS：43.040.10 CCS：发布：2021-09-14 实施：

ASTM D7731-17 液相色谱/串联质谱法（LC/MS/MS）测定海水中二丙二醇单丁醚和乙二醇单丁醚的标准试验方法
简介：
信息：ICS：13.060.50 CCS：发布：2017-12-15 实施：

ASTM D7599-16 用单反应监测液相色谱/串联质谱法（LC/MS/MS）测定水中二乙醇胺、三乙醇胺、甲基二乙醇胺和乙基二乙醇胺的标准试验方法
简介：
信息：ICS：13.060.50 CCS：发布：2016-02-01 实施：

IEC 62321-3-3-2021 电工产品中某些物质的测定.第3-3部分:筛选.使用热解/热脱附附件（Py/TD？GC？MS）通过气相色谱-质谱法测定聚合物中的多溴联苯、多溴二苯醚和邻苯二甲酸酯
简介：
信息：ICS：43.040.10 CCS：发布：2021-09-14 实施：

ASTM D7742-17 壬基酚聚氧乙烯酯（NPnEO 3&x2264；n&x2264；18）和辛基酚聚氧乙烯酯（OPnEO 2&x2264；n&x2264；12）通过单反应监测（SRM）液相色谱/串联质谱（LC/MS/MS）测定水中
简介：
信息：ICS：71.100.40 CCS：发布：2017-12-15 实施：

ASTM D7597-2016 采用液相色谱法/串联质谱法 (LC/MS/MS) 测定水中二异丙基甲基磷酸酯, 乙基氢氨基磷酸盐, 乙基甲基膦酸, 异丙基甲基膦酸, 甲基膦酸和吡呐基甲基膦酸的标准试验方法
简介：5.1x00a0;Organophosphate pesticides affect the nervous system by disrupting the enzyme that regulates acetylcholine, a neurotransmitter. They were developed during the early 19th century, but their effects on insects, which are similar to their effects on humans, were discovered in 1932. Some are poisonous and were used as chemical weapon agents. Organophosphate pesticides are usually not persistent in the environment.4, 5 5.2x00a0;This test method is for the analysis of selected organophosphorous-based chemical weapon agent degradation products from Sarin (GB), Soman (GD), Tabun (GA) and VX. This method has been investigated for use with reagent and surface water. 1.1x00a0;This procedure covers the determination of diisopropyl methylphosphonate (DIMP), ethyl hydrogen dimethylamidophosphate (EHDMAP), ethyl methylphosphonic acid (EMPA), isopropyl methylphosphonic acid (IMPA), methylphosphonic acid (MPA) and pinacolyl methylphosphonic acid (PMPA) (referred to collectively as organophosphonates in this test method) in surface water by direct injection using liquid chromatography (LC) and detected with tandem mass spectrometry (MS/MS) using electrospray ionization (ESI). These analytes are qualitatively and quantitatively determined by this method. This method adheres to single reaction monitoring (SRM) mass spectrometry. 1.2x00a0;This test method has been developed by US EPA Region 5 Chicago Regional Laboratory (CRL). 1.3x00a0;The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 1.4x00a0;The detection verification level (DVL) and reporting range for the organophosphonates are listed in Table 1. 1.4.1x00a0;The DVL is required to be at a concentration at least three times below the reporting limit (RL) and have a signal/noise ratio greater than 3:1. Fig. 1 displays the signal/noise ratios at the DVLs for the organophosphonates in the ESI positive mode and Fig. 2 in the ESI negative mode.RSD (%) DIMP Pos 5
信息：ICS：13.060.50 CCS：发布：2016 实施：

ISO 22104:2021 水质.微囊藻毒素的测定.液相色谱法和串联质谱法（LC-MS/MS）
简介：
信息：ICS：13.060.50 CCS：发布：2021-07-01 实施：

ASTM D7730-17 通过液相色谱/串联质谱法测定海水中二辛基磺基琥珀酸盐的标准测试方法（LC/MS/MS）
简介：
信息：ICS：71.060.50 CCS：发布：2017-12-15 实施：

ASTM D7644-2016 采用液相色谱法/串联质谱法 (LC/MS/MS) 测定水中溴敌隆, 溴鼠灵, 敌鼠和杀鼠灵的标准试验方法
简介：5.1x00a0;This test method has been developed by U.S. EPA Region 5 Chicago Regional Laboratory (CRL). 5.2x00a0;Bromadiolone, brodifacoum, diphacinone and warfarin are rodenticides for controlling mice, rats, and other rodents that pose a threat to public health, critical habitats, native plants and animals, crops, food and water supplies. These rodenticides also present human and environmental safety concerns. Warfarin and diphacinone are first-generation anticoagulants, while bromadiolone and brodifacoum are second-generation. The anticoagulants interfere with blood clotting, and death can result from excessive bleeding. The second-generation anticoagulants are especially hazardous for several reasons. They are highly toxic and persist a long time in body tissues. The second-generation anticoagulants are designed to be toxic in a single feeding, but time-to-death occurs in several days. This allows rodents to feed multiple times before death, leading to carcasses containing residues that may be many times the lethal dose.4 5.3x00a0;This test method has been investigated for use with reagent, surface, and drinking water for the selected rodenticides. 1.1x00a0;This procedure covers the determination of bromadiolone, brodifacoum, diphacinone and warfarin (referred to collectively as rodenticides in this test method) in water by direct injection using liquid chromatography (LC) and detected with tandem mass spectrometry (MS/MS). These analytes are qualitatively and quantitatively determined by this test method. This test method adheres to multiple reaction monitoring (MRM) mass spectrometry. 1.2x00a0;The Detection Verification Level (DVL) and Reporting Range for the rodenticides are listed in Table 1. 1.2.1x00a0;The DVL is required to be at a concentration at least 3 times below the Reporting Limit (RL) and have a signal/noise ratio greater than 3:1. Fig. 1 displays the signal/noise ratios of the primary single reaction monitoring (SRM) transitions, and Fig. 2 displays the confirmatory SRM transitions at the DVLs for the rodenticides. 1.2.2x00a0;The reporting limit was calculated from the concentration of the Level 1 calibration standard, as shown in Table 4, accounting for the dilution of a 40 mL water sample up to a final volume of 50 mL with methanol to ensure analyte solubility. 1.3x00a0;Unitsx2014;The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 1.4x00a0;This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use.
信息：ICS：13.060.50 CCS：发布：2016 实施：

ASTM E2838-21 通过液相色谱/串联质谱法（LC/MS/MS）通过溶剂萃取测定湿巾上硫二甘醇的标准测试方法
简介：
信息：ICS：97.080 CCS：发布：2021-05-01 实施：

ASTM D7968-17a 通过液相色谱串联质谱法（LC/MS/MS）测定土壤中多氟化合物的标准测试方法
简介：
信息：ICS：13.080.10 CCS：发布：2017-09-01 实施：

ASTM D7645-2016 采用液相色谱法/串联质谱法 (LC/MS/MS) 测定水中涕灭威, 涕灭威砜, 涕灭威亚砜, 呋喃丹, 灭多威, 杀线威和久效威的标准试验方法
简介：5.1x00a0;This test method has been developed by U.S. EPA Region 5 Chicago Regional Laboratory (CRL). 5.2x00a0;The N-methyl carbamate (NMC) pesticides: aldicarb, carbofuran, methomyl, oxamyl, and thiofanox have been identified by EPA as working through a common mechanism. These affect the nervous system by reducing the ability of enzymes. Enzyme inhibition was the primary toxicological effect of regulatory concern to EPA in assessing the NMCx2019;s food, drinking water, and residential risks. In most of the country, NMC residues in drinking water sources are at levels that are not likely to contribute substantially to the multi-pathway cumulative exposure. Shallow private wells extending through highly permeable soils into shallow, acidic ground water represent what the EPA believes to be the most vulnerable drinking water. Aldicarb sulfone and aldicarb sulfoxide are breakdown products of aldicarb and should also be monitored due to their toxicological effects.4 5.3x00a0;This test method has been investigated for use with reagent, surface, and drinking water for the selected carbamates: aldicarb, aldicarb sulfone, aldicarb sulfoxide, carbofuran, methomyl, oxamyl, and thiofanox. 1.1x00a0;This procedure covers the determination of aldicarb, aldicarb sulfone, aldicarb sulfoxide, carbofuran, methomyl, oxamyl, and thiofanox (referred to collectively as carbamates in this test method) in water by direct injection using liquid chromatography (LC) and detected with tandem mass spectrometry (MS/MS). These analytes are qualitatively and quantitatively determined by this test method. This test method adheres to multiple reaction monitoring (MRM) mass spectrometry. 1.2x00a0;The Detection Verification Level (DVL) and Reporting Range for the carbamates are listed in Table 1. 1.2.1x00a0;The DVL is required to be at a concentration at least 3 times below the Reporting Limit (RL) and have a signal/noise ratio greater than 3:1. Fig. 1 displays the signal/noise ratios of the primary single reaction monitoring (SRM) transitions, and Fig. 2 displays the confirmatory SRM transitions at the DVLs for the carbamates. 1.2.2x00a0;The reporting limit is the concentration of the Level 1 calibration standard as shown in Table 2 for the carbamates. 1.3x00a0;Unitsx2014;The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 1.4x00a0;This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior ......
信息：ICS：13.060.50 CCS：发布：2016 实施：

ASTM E2787-21 使用加压流体萃取法测定土壤中硫二甘醇的标准测试方法随后采用单反应监测液相色谱/串联质谱（LC/MS/MS）
简介：
信息：ICS：13.080.10 CCS：发布：2021-05-01 实施：

ISO 16000-33-2017 室内空气 - 第33部分:气相色谱/质谱法测定邻苯二甲酸酯（GC/MS）
简介：
信息：ICS：13.040.20 CCS：发布：2017-08-10 实施：

ASTM D7979-2016 使用液相色谱串联质谱法 (LC/MS/MS) 测定水, 污泥, 污水, 污物以及废水中全氟化合物的标准试验方法
简介：5.1x00a0;This test method has been developed by the US EPA Region 5 Chicago Regional Laboratory (CRL). 5.2x00a0;PFCs are widely used in various industrial and commercial products; they are persistent, bio-accumulative, and ubiquitous in the environment. PFCs have been reported to exhibit developmental toxicity, hepatotoxicity, immunotoxicity, and hormone disturbance. A draft Toxicological Profile for Perfluoroalkyls from the U.S. Department of Health and Human Services is available.6 PFCs have been detected in soils, sludges, surface, and drinking waters. Hence, there is a need for quick, easy, and robust method to determine these compounds at trace levels in water matrices for understanding of the sources and pathways of exposure. 5.3x00a0;This method has been investigated for use with reagent, surface, sludge and wastewaters for selected perfluorinated compounds. 1.1x00a0;This procedure covers the determination of selected perfluorinated compounds (PFCs) in a water matrix using liquid chromatography (LC) and detection with tandem mass spectrometry (MS/MS). These analytes are qualitatively and quantitatively determined by this method. This method adheres to multiple reaction monitoring (MRM) mass spectrometry. 1.2x00a0;The Method Detection Limit (MDL)2 and Reporting Range3 for the target analytes are listed in Table 1. (A)x00a0;Acronyms are defined in 3.3. 1.2.1x00a0;The reporting limit in this test method is the minimum value below which data are documented as non-detects. Analyte detections between the method detection limit and the reporting limit are estimated concentrations and are not reported following this test method. In most cases, the reporting limit is the concentration of the Level 1 calibration standard as shown in Table 4 for the perfluorinated compounds after taking into account the 50 % dilution with methanol. It is above the Level 1 calibration concentration for PFOS, PFBS, FHEA and FOEA, these compounds can be identified at the Level 1 concentration but the standard deviation among replicates at this lower spike level resulted in a higher reporting limit. 1.3x00a0;Unitsx2014;The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 1.4x00a0;This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use.
信息：ICS： CCS：发布：2016 实施：

KS M 6905-2021 皮革.用气相色谱-串联质谱（GC-MS/MS）和液相色谱-串联质谱（LC-MS/MS）测定全氟化合物（PFC）
简介：
信息：ICS：97.150 CCS：发布：2021-04-02 实施：

ASTM D7979-17 通过液相色谱串联质谱法（LC/MS/MS）测定水污泥流入物流出物和废水中的全氟烷基物质的标准测试方法
简介：
信息：ICS：13.060.50 CCS：发布：2017-07-15 实施：

ISO 20639:2015 婴幼儿配方和成人营养 - 通过超高效液相色谱和串联质谱法测定泛酸（Uhplc-Ms/Ms）
简介：
信息：ICS：67.050 CCS：发布：2015-11-09 实施：

DIN EN 17411-2021 肥料. 采用液相色谱法和串联质谱检测法(LC-MS/MS)测定矿物肥料中的高氯酸盐
简介：This document specifies a method for the determination of traces of perchlorate by liquid chromatography and tandem mass spectrometry detection (LC-MS/MS). The method is applicable to mineral fertilizers.
信息：ICS： CCS：发布：2021-01-00 实施：

DIN 38407-47-2017 检查水, 废水和污泥的德国标准方法. 连带的可测定物质(F组). 第47部分: 水和废水中选择活性药物成分和其他有机物质的测定. 直接注射(F 47)后采用高效液相色谱和质谱检测法(HPLC-MS/MS或-HRMS)
简介：
信息：ICS：13.060.50 CCS：Z23;P41 发布：2017-07 实施：

ASTM D8018-15 通过多重反应监测液相色谱/质谱法（LC/MS/MS）测定土壤中（三正丁基） - 正十四烷基氯化鏻（TTPC）的标准试验方法
简介：
信息：ICS：13.080.10 CCS：发布：2015-11-01 实施：

KS M ISO 23702-1-2020 皮革.有机氟.第1部分:用液相色谱/串联质谱检测器（LC-MS/MS）萃取法测定非挥发性化合物含量
简介：
信息：ICS：59.140.30 CCS：发布：2020-12-30 实施：

BS EN 16858-2017 食品. 采用液相色谱串联质谱法(LC-MS/MS)测定食品中的三聚氰胺和三聚氰酸
简介：
信息：ICS：67.050 CCS：X04 发布：2017-06-21 实施：2017-06-21

BS PD ISO/TS 16780-2015 水质. 多氯萘 (PCN) 的测定. 气相色谱 (GC) 和质谱法 (MS)
简介：
信息：ICS：13.060.50 CCS：Z16 发布：2015-08-31 实施：2015-08-31

T/CAQI 156-2020 生物样本的单核苷酸多态性（SNP）位点检测—高通量飞行时间质谱法（MALDI-TOF MS）
简介：样品的预处理、核酸提取、PCR反应、SAP消化反应、单碱基延伸、仪器分析条件。
信息：ICS：11.220 CCS：M745 发布：2020-12-18 实施：2020-12-18

ASTM D7599-16(2017) 用单反应监测液相色谱/串联质谱法（LC/MS/MS）测定水中二乙醇胺、三乙醇胺、甲基二乙醇胺和乙基二乙醇胺的标准试验方法
简介：
信息：ICS：13.060.50 CCS：发布：2017-06-15 实施：

BS ISO 18363-1-2015 动植物油脂. 采用气相色谱/质谱联用法 (GC/MS) 测定脂肪酸氯丙醇 (MCPD) 和缩水甘油. 采用快速碱酯交换和测量法测定三氯丙二醇和用差分测量法测定缩水甘油
简介：
信息：ICS：67.200.10 CCS：X14 发布：2015-08-31 实施：2015-08-31

ASTM D8086-20 用质谱法（MS）或火焰离子化检测法（FID）用顶空气相色谱法（GC）测定石油源电绝缘液体中甲醇和乙醇的标准试验方法
简介：
信息：ICS：29.040.10 CCS：发布：2020-12-01 实施：

WS/T 549-2017 尿中总铀和铀-235/铀-238比值分析方法电感耦合等离子体质谱法（ICP—MS）
简介：
信息：ICS：ICS13.280 CCS：C57 发布：2017-05-18 实施：2017-11-01

BS ISO 18363-1-2015 动植物油脂. 采用气相色谱/质谱联用法 (GC/MS) 测定脂肪酸氯丙醇 (MCPD) 和缩水甘油. 采用快速碱酯交换和测量法测定三氯丙二醇和用差分测量法测定缩水甘油
简介：
信息：ICS：67.200.10 CCS：发布：2015-08-31 实施：2015-08-31

NF U42-248-2020 肥料. 用液相色谱法和串联质谱法测定无机肥料中的高氯酸盐(LC-MS/MS)
简介：Domaine d'applicationLe présent document spécifie une méthode de détermination des traces de perchlorate par chromatographie liquide couplée à la spectrométrie de masse (LC-MS/MS) . La méthode est applicable aux engrais minéraux.
信息：ICS： CCS：发布：2020-11-11 实施：2020-12-25

ASTM D7968-17 通过液相色谱串联质谱法（LC/MS/MS）测定土壤中多氟化合物的标准测试方法
简介：
信息：ICS：13.080.10 CCS：发布：2017-05-01 实施：

BS PD ISO/TS 16780-2015 水质. 多氯萘 (PCN) 的测定. 气相色谱 (GC) 和质谱法 (MS)
简介：
信息：ICS：13.060.50 CCS：发布：2015-08-31 实施：2015-08-31

ISO 21470-2020 婴幼儿配方和成人营养 - 通过液相色谱和串联质谱法（LC-MS/MS）测定维生素B1 B2 B3和B6含量
简介：
信息：ICS：67.050 CCS：发布：2020-11-03 实施：

ASTM D7979-2017 采用液相色谱串联质谱法(LC/MS/MS)测定水, 污泥, 流入物, 流出物和废水中全氟烷基和多氟烷基物质的标准试验方法
简介：5.1x00a0;PFASs are widely used in various industrial and commercial products; they are persistent, bio-accumulative, and ubiquitous in the environment. PFASs have been reported to exhibit developmental toxicity, hepatotoxicity, immunotoxicity, and hormone disturbance. A draft Toxicological Profile for Perfluoroalkyls from the U.S. Department of Health and Human Services is available.6 PFASs have been detected in soils, sludges, surface, and drinking waters. Hence, there is a need for quick, easy, and robust method to determine these compounds at trace levels in water matrices for understanding of the sources and pathways of exposure. 5.2x00a0;This method has been investigated for use with reagent, surface, sludge and wastewaters for selected PFASs. This method has not been evaluated on drinking water matrices. 1.1x00a0;This procedure covers the determination of selected per- and polyfluoroalkyl substances (PFASs) in a water matrix using liquid chromatography (LC) and detection with tandem mass spectrometry (MS/MS). These analytes are qualitatively and quantitatively determined by this method. This method adheres to a technique known as selected reaction monitoring (SRM) or sometimes referred to as multiple reaction monitoring (MRM). This is not a drinking water method, performance of this test method has not been evaluated on drinking water matrices. 1.2x00a0;The Method Detection Limit (MDL)2 and Reporting Range3 for the target analytes are listed in Table 1. The target concentration for the reporting limit for this test method was 10 ng/L for most of the target analytes at the time of development. TABLE 1 Method Detection Limit and Reporting Range AnalyteA MDL (ng/L) Reporting Ranges (ng/L) PFTreAB 1.2 10 x2013; 400 PFTriAB
信息：ICS：13.060.50 ; 71.080.20 CCS：C51 发布：2017 实施：

ISO/TS 16780:2015 水质 - 多氯萘（PCN）的测定 - 使用气相色谱（GC）和质谱（MS）的方法
简介：
信息：ICS：13.060.50 CCS：发布：2015-08-14 实施：

ISO 21468-2020 婴幼儿配方和成人营养 - 通过液相色谱和串联质谱（LC-MS/MS）测定总胆碱和肉碱含量
简介：
信息：ICS：67.050 CCS：发布：2020-10-06 实施：

ASTM D7968-2017a 采用液相色谱串联质谱法(LC/MS/MS)测定土壤中多氟化合物的标准试验方法
简介：5.1x00a0;This test method has been developed by the U.S. EPA Region 5 Chicago Regional Laboratory (CRL). 5.2x00a0;PFCs are widely used in various industrial and commercial products; they are persistent, bio-accumulative, and ubiquitous in the environment. PFCs have been reported to exhibit developmental toxicity, hepatotoxicity, immunotoxicity, and hormone disturbance. A draft Toxicological Profile for Perfluoroalkyls from the U.S. Department of Health and Human Services is available.7 PFCs have been detected in soils, sludges, and surface and drinking waters. Hence, there is a need for a quick, easy, and robust method to determine these compounds at trace levels in various soil matrices for understanding of the sources and pathways of exposure. 5.3x00a0;This method has been used to determine selected polyfluorinated compounds in sand (Table 4) and four ASTM reference soils (Table 5). TABLE 4 Single-Laboratory Recovery Data in Ottawa Sand Sample Measured ng/kg from Ottawa Sand P&A Data (400 ng/kg spike for all PFCs except 2000 ng/kg for PFBA and PFPeA and 8000 ng/kg spike for FHEA, FDEA, and FOEA) PFTreA PFTriA PFDoA PFUnA
信息：ICS：13.080.10 CCS：B10 发布：2017 实施：

ISO 18363-1-2015 动植物油脂. 采用气相色谱/质谱联用法 (GC/MS) 测定脂肪酸氯丙醇 (MCPD) 和缩水甘油. 第1部分: 采用快速碱酯交换和测量法测定三氯丙二醇和用差分测量法测定缩水甘油
简介：
信息：ICS：67.200.10 CCS：发布：2015-08 实施：