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BPVC.V-2025: Section V, Nondestructive Examination

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1241

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BPVC.I-2025: Section I, Rules for Construction of Power Boilers

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1074

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BPVC.VII-2025: Section VII, Recommended Guidelines for the Care of Power Boilers

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653

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BPVC.IV-2025: Section IV, Rules for Construction of Heating Boilers

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1098

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BPVC.VI-2025: Section VI, Recommended Rules for the Care and Operation of Heating Boilers

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653

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BPVC.CC.BPV.S1-2025: 2025 ASME BPVC Code Cases: Boilers and Pressure Vessels, Supplement 1

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BPVC.X-2025: Section X, Fiber-Reinforced Plastic Pressure Vessels

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979

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BPVC.I-2023: Section I, Rules for Construction of Power Boilers (Previous Edition)

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963

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BPVC.IV-2023: Section IV, Rules for Construction of Heating Boilers (Previous Edition)

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979

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API PUBL 347

API PUBL 347: Hazardous Air Pollutant Emissions from Gasoline Loading Operations at Bulk Gasoline Te

CDN $178.00

Hazardous Air Pollutant Emissions from Gasoline Loading Operations at Bulk Gasoline Te

SKU: f1ddf3ed600b Category:

Description

HAP emission testing was conducted at 33 bulk gasoline terminals across the United States. Emissions were measured from the loading of gasoline cargo tanks at facilities with a vapor control system. Emission tests from 23 carbon adsorption units, 8 thermal oxidizers, and 2 refrigeration units were included. Control efficiencies for eight HAP compounds were derived for the carbon adsorption units and thermal oxidizers; no control efficiencies were reported from the refrigeration units due to the limited data collected. The HAP control efficiencies presented in this report have been used to develop HAP emission factors that can be used to determine HAP emissions based on the volume of gasoline loaded at a facility.

Edition

1998

Published Date

1998-10-01

Status

Current

Pages

128

Language Detail Icon

English

Format Secure Icon

Secure PDF

Abstract

HAP emission testing was conducted at 33 bulk gasoline terminals across the United States. Emissions were measured from the loading of gasoline cargo tanks at facilities with a vapor control system. Emission tests from 23 carbon adsorption units, 8 thermal oxidizers, and 2 refrigeration units were included. Control efficiencies for eight HAP compounds were derived for the carbon adsorption units and thermal oxidizers; no control efficiencies were reported from the refrigeration units due to the limited data collected. The HAP control efficiencies presented in this report have been used to develop HAP emission factors that can be used to determine HAP emissions based on the volume of gasoline loaded at a facility.

Previous Editions

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