API TR 2574-2016 Field Testing Protocol for Characterization of Total Gaseous Nonmethane Organics (TGNMO) Methane and Ethane in Air CVapor Mixture During Filling of a Cargo Vessel .pdf

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1、Field Testing Protocol for Characterization of Total Gaseous Nonmethane Organics (TGNMO), Methane, and Ethane in AirVapor Mixture During Filling of a Cargo Vessel with Crude OilAPI TECHNICAL REPORT 2574 FIRST EDITION, AUGUST 2016Special NotesAPI publications necessarily address problems of a general

2、 nature. With respect to particular circumstances, local, state, and federal laws and regulations should be reviewed.Neither API nor any of APIs employees, subcontractors, consultants, committees, or other assignees make any warranty or representation, either express or implied, with respect to the

3、accuracy, completeness, or usefulness of the information contained herein, or assume any liability or responsibility for any use, or the results of such use, of any information or process disclosed in this publication. Neither API nor any of APIs employees, subcontractors, consultants, or other assi

4、gnees represent that use of this publication would not infringe upon privately owned rights.API publications may be used by anyone desiring to do so. Every effort has been made by the Institute to assure the accuracy and reliability of the data contained in them; however, the Institute makes no repr

5、esentation, warranty, or guarantee in connection with this publication and hereby expressly disclaims any liability or responsibility for loss or damage resulting from its use or for the violation of any authorities having jurisdiction with which this publication may conflict.API publications are pu

6、blished to facilitate the broad availability of proven, sound engineering and operating practices. These publications are not intended to obviate the need for applying sound engineering judgment regarding when and where these publications should be utilized. The formulation and publication of API pu

7、blications is not intended in any way to inhibit anyone from using any other practices.Any manufacturer marking equipment or materials in conformance with the marking requirements of an API standard is solely responsible for complying with all the applicable requirements of that standard. API does n

8、ot represent, warrant, or guarantee that such products do in fact conform to the applicable API standard.Classified areas may vary depending on the location, conditions, equipment, and substances involved in any given situation. Users of this Technical Report should consult with the appropriate auth

9、orities having jurisdiction.Users of this Technical Report should not rely exclusively on the information contained in this document. Sound business, scientific, engineering, and safety judgment should be used in employing the information contained herein.API is not undertaking to meet the duties of

10、 employers, manufacturers, or suppliers to warn and properly train and equip their employees, and others exposed, concerning health and safety risks and precautions, nor undertaking their obligations to comply with authorities having jurisdiction.Information concerning safety and health risks and pr

11、oper precautions with respect to particular materials and condi-tions should be obtained from the employer, the manufacturer or supplier of that material, or the material safety data sheet.All rights reserved. No part of this work may be reproduced, translated, stored in a retrieval system, or trans

12、mitted by any means, electronic, mechanical, photocopying, recording, or otherwise, without prior written permission from the publisher. Contact the Publisher, API Publishing Services, 1220 L Street, NW, Washington, DC 20005.Copyright 2016 American Petroleum InstituteForewordNothing contained in any

13、 API publication is to be construed as granting any right, by implication or otherwise, for the manufacture, sale, or use of any method, apparatus, or product covered by letters patent. Neither should anything contained in the publication be construed as insuring anyone against liability for infring

14、ement of letters patent.Suggested revisions are invited and should be submitted to the Standards Department, API, 1220 L Street, NW, Washington, DC 20005, standardsapi.org.iiiContentsPage1 Scope . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

15、 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 11.1 Applicability . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 11.2 Principle . . . . . . . . . . . . . . . . . . . . . . . . . . .

16、 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12 Field Sampling Apparatus . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 22.1 General . . . . . . . . . . .

17、. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 22.2 Sampling Probe . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

18、. . . . 22.3 Water Condensate Trap . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 32.4 VOC Condensate Trap . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

19、. . . . . . . . . . . . . . . 32.5 Metering Valve and Rate Meter . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 42.6 Sample Canister . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

20、. . . . . . . . . . . . . . . . . . . . . . . . . . . 42.7 Mercury Manometer or Absolute Pressure Gauge . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 52.8 Vacuum Pump . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

21、 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 53 Sampling Reagents . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 54 Time-Integrated Field Sampling Procedure . . . . . . . . . . . . . . . .

22、. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 54.1 Sampling Train Assembly. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 54.2 Sample Train Operation . . . . . . . . . . . . . . . . . . . . .

23、. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 124.3 Sample Train Recovery. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 135 Instantaneous Field Sampling Procedure . . .

24、. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 145.1 Sampling Train Preparation . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 145.2 Sampling Train Operation. . . . . . . .

25、 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 145.3 Sampling Train Recovery . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 146 Nomenclature and Calc

26、ulations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 146.1 General . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

27、 146.2 Nomenclature. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 156.3 Calculations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

28、. . . . . . . . . . . . . . . . . . . . 16Annex A (informative) Federal Reference Method 25 (FRM 25) Determination of Total Gaseous Nonmethane Organic Emissions as Carbon (Abridged and Modified) . . . . . . . . . . . . . . . . . . . . . . . . . . . 18Annex B (informative) Protocol for Sampling and A

29、nalysis of Vapors from Marine Loading of Crude Oil: Field Testing for Proof-of-Principle . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 34Annex C (informative) Analytical Sample Canister Identification . . . . . . . . . . . . . . . . . . . . . . . . . .

30、 . . . . . . . . . . 45Annex D (informative) Laboratory Analytical Results . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 46Bibliography . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

31、. . . . . . . . . . . . . . . . . . . . . 48Figures1 Analytical Diagram of Gas Chromatograph (CG), Oxidizing and Reducing Catalysts, and Flame Ionization Detector (FID) Specified in FRM 25 Analysis . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 22 Analytical Chromatogram Assoc

32、iated With FRM 25 Analysis for Quantifying TGNMO, Methane, and Ethane Emissions in an AirVapor Mixture . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 33 Typical Time-Integrated Sampling Train Used for Measuring TGNMO, Methane, and Ethane in AirVapor Mixture During Fillin

33、g of a Cargo Vessel with Crude Oil . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 44 Close-up View of Water Condensate Trap and VOC Condensate Trap . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5B.1 Meteorological Data: New Orleans Lakefront, LA . . . . . . . . . . . . . . .

34、 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 36B.2 Meteorological Data: Baton Rouge, LA . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 36B.1 Barge Hatch with Sampling Probes . . . . . . . . . . . . . . . . . . . . . . . . . .

35、 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 37vPageB.2 TGNMOC Concentration (ppm) vs Time (hours) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 39B.3 Methane Concentration (ppm) vs Time (hours) . . . . . . . . . . . . . . . . . . . . . .

36、 . . . . . . . . . . . . . . . . . . . . . . . . 39B.4 Ethane Concentration (ppm) vs Time (hours) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 40Tables1 Various Project Activities to be Completed by Host Facility and Testing Contractor. . . . . . .

37、. . . . . . . . . . 62 Various Project (Sampling) Activities to be Completed by Host Facility and Testing Contractor . . . . . . 83 Various Project (Clean up) Activities to be Completed by Host Facility and Testing Contractor . . . . . . . 84 QC Checklist Associated with Sampling and Analytical Even

38、t . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 95 QC Checklist for Equipment and Reagents . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 106 Field Test Data Sheet (FTDS) . . . . . . . . . . . . . . . . . . . . . . . . . .

39、. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 11B.1 Results for Only Location at Which Both Grab Samples and a Valid Integrated Sample Were Obtained . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .

40、 . . . . . . . . . 40B.2 Results From Other Sample Locations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 41B.3 Summary of Data Comparing Grab Sample Average Results to All Integrated Sample Results Average . . . . . . . . . . . . . . . .

41、. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 41B.4 Barge A . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 43B.5 Barge B .

42、. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 44vi1Field Testing Protocol for Characterization of Total Gaseous Nonmethane Organics (TGNMO), Methane, and Ethane in airvapor Mixture During Fi

43、lling of a Cargo Vessel with Crude Oil1 Scope1.1 ApplicabilityThis method applies to the measurement of volatile organic compounds (VOC) as total gaseous nonmethane organics (TGNMO), methane and ethane from the airvapor mixture that is expelled during filling of a cargo vessel with crude oil. This p

44、rotocol utilizes a modified version of U.S. EPA Federal Reference Method 25 (FRM 25) entitled: “Determination of Total Gaseous Nonmethane Organic Emissions as Carbon.” Annex A contains an abridged and modified version of FRM 25 to meet specific project quality objectives (PQOs).While the field testi

45、ng in support of this protocol (see Annex B, Annex C, and Annex D) was performed only for the loading of crude oil into barges, the method could be suitable for loading of any volatile organic liquid into any type of vessel or compartment from which vapors are exhausted through a single vent opening

46、 where the field sampling can take place.The objective of this field testing protocol is to provide standardized testing methodology for quantifying TGNMO, methane and ethane emissions in the airvapor mixture that is expelled from cargo compartments during filling with crude oil.The characteristics

47、and composition of the airvapor mixture expelled from a cargo vessel into the atmosphere during filling with crude oil is dependent upon the characteristics of the crude oil, including such variables as volatility, temperature, etc. The changing characteristics of the exhausted airvapor mixture can

48、affect the application of FRM 25 in quantifying the concentration of TGNMO, methane, and ethane in the airvapor mixture. This field testing protocol provides guidance on utilizing various configurations of FRM 25 in the characterization process. They are: Time-Integrated Sampling: The traditional FR

49、M 25 sampling train configuration is used but modified by adding a water condensate trap in front of the volatile organic compound (VOC) condensate trap to drop out the water content found in the airvapor mixture. The water condensate trap prevents freezing of the VOC condensate trap by the water molecules which would lead to reduced gas flow through the sampling system. Instantaneous Sample: In this configuration, the FRM 25 condensate trap(s) i.e. water and VOC traps are removed from the sampling train and instantaneous samples of the airvapor mixture are acquired period

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