Air Dispersion Modeling Protocol · 2021. 2. 16. · AIR DISPERSION MODELING PROTOCOL Owens-Brockway Glass Container, Inc. (O-B) INTRODUCTION 1. INTRODUCTION 1.1 Purpose of Protocol

The business of sustainability

Air Dispersion Modeling Protocol Owens-Brockway Glass Container, Inc. (O-B) Portland, Oregon

January 2021

Project No.: 0506432

www.erm.com Version: 3.1 Project No.: 0506432 Owens-Brockway Glass Container, Inc. (O-B) January 2021

Signature Page

January 2021

Air Dispersion Modeling Protocol

Owens-Brockway Glass Container Inc. (O-B)

Jim Dill Partner-in-Charge

Vicki Hoffman Principal Scientist

ERM-West, Inc. 1920 Main Street, Suite 300 Irvine, Ca 92614

T: +1 949-623-4700 F: +1 949-623-4711

© Copyright 2021 by ERM Worldwide Group Ltd and / or its affiliates (“ERM”). All rights reserved. No part of this work may be reproduced or transmitted in any form, or by any means, without the prior written permission of ERM.

www.erm.com Version: 3.1 Project No.: 0506432 Owens-Brockway Glass Container, Inc. (O-B) January 2021 Page 1

AIR DISPERSION MODELING PROTOCOL Owens-Brockway Glass Container, Inc. (O-B)

INTRODUCTION

CONTENTS

1. INTRODUCTION ................................................................................................................................ 3 1.1 Purpose of Protocol .............................................................................................................................. 3 1.2 Facility Description ................................................................................................................................ 3

2. EMISSION ESTIMATES AND MODEL SOURCES ........................................................................... 4 2.1 Batch House - Raw Materials Handling ................................................................................................ 4 2.2 Glass Melting Furnaces ........................................................................................................................ 4 2.3 Bottle Forming ...................................................................................................................................... 5 2.4 Hot End Surface Treatment .................................................................................................................. 5 2.5 Mold Preparation .................................................................................................................................. 5 2.6 Warehouse Operations ......................................................................................................................... 6 2.7 Boiler .................................................................................................................................................... 6 2.8 Miscellaneous Activities ........................................................................................................................ 6

3. MODEL SELECTION AND INPUTS .................................................................................................. 6 3.1 Model Selection .................................................................................................................................... 6 3.2 Meteorological Data .............................................................................................................................. 7 3.3 Receptor Grid ....................................................................................................................................... 9 3.4 Aerodynamic Downwash .................................................................................................................... 14 3.5 Model Source Inputs ........................................................................................................................... 15

4. MODELING ANALYSIS DOCUMENTATION .................................................................................. 24 4.1 Modeling Results ................................................................................................................................ 24 4.2 Submittal ............................................................................................................................................. 24

APPENDIX A SITE LOCATION MAP APPENDIX B GRAPHIC DISPLAY OF RECEPTOR GRID APPENDIX C LAND USE MAP APPENDIX D BUILDING DIMENSIONS APPENDIX E ANNUAL AND DAILY EMISSION RATES

List of Tables Table 3-1 Surface Soil Moisture Condition Assessment ........................................................................ 7 Table 3-2 Assessment of Missing Meteorological Data ......................................................................... 8 Table 3-3 Summary of Statewide Zoning and Exposure Type Classification ........................................ 9 Table 3-4 Sensitive Receptors Locations ............................................................................................. 13 Table 3-5 Emission Sources from Building 1 ....................................................................................... 15 Table 3-6 Proposed Model IDs for Inventory TEUs ............................................................................. 15 Table 3-7 Point Source Release Parameters....................................................................................... 17 Table 3-8 Volume Sources Parameters ............................................................................................... 18 Table 3-9 Line Volume Sources Parameters ....................................................................................... 18



INTRODUCTION

Acronyms and Abbreviations µg/m3 micrograms per cubic meter

AERMIC American Meteorological Society/Environmental Protection Agency Regulatory Model Improvement Committee

BPIP PRIME Building Profile Input Program PRIME

CFR Code of Federal Regulations

DEQ Oregon Department of Environmental Quality

ERM ERM-West, Inc.

K Kelvin

km kilometers

m meters

NED National Elevation Dataset

O-B Owens Brockway Glass Container

TAC toxic air contaminant

TEU toxic emissions unit

USEPA U.S. Environmental Protection Agency

USGS U.S. Geological Survey

UTM Universal Transverse Mercator



INTRODUCTION

1. INTRODUCTION

1.1 Purpose of Protocol Owens-Brockway Glass Container Inc. (O-B) has been called in to comply with the Department of Environmental Quality’s (DEQ) newly promulgated Cleaner Air Oregon (CAO) Regulations (Chapter 340, Division 245) for its facility located at 9710 NE Glass Plant Road in Portland, Oregon. Rule 340-245-0050 defines the requirements for a health risk assessment, air quality modeling, four levels of risk assessment, monitoring plans, and risk reduction plans associated with toxic air contaminant (TAC) emissions from facilities.

On behalf of O-B, ERM-West, Inc. (ERM) has prepared this modeling protocol to conduct an analysis of the TACs for submittal to DEQ for review and approval. This protocol provides the facility description and identifies the model selection, including model inputs, receptor generation, meteorological data, terrain classifications of the area, source locations, and emissions inventory information that will be used for the risk assessment modeling.

1.2 Facility Description O-B owns and operates a glass containers manufacturing plant (Plant No. 21) in Portland, Oregon. Plant No. 21 occupies approximately 78 acres of property located at 9710 NE Glass Plant Road, adjacent to Interstate-205. The facility is located at Universal Transverse Mercator (UTM – NAD 83) Zone 10, 533,810 meters (m) Easting by 5,045,669 m Northing, with an elevation of approximately 36 feet above sea level. An aerial image of the facility location and the property boundary is shown in Appendix A. The area surrounding the facility is a mixture of land-use zoning including residential, mixed-use, commercial and industrial. Appendix C presents the existing land-use zoning surrounding the facility.

Plant No. 21 produces a variety of glass containers from post-consumer recycled glass with other essential raw materials such as sand and limestone. The glass manufacturing process comprises of the following areas of operations: raw material and cullet receiving and storage, materials blending and transport, glass melting furnaces, glass forming, final bottle treatment, and the maintenance and support systems such as boiler and storage tanks.



EMISSION ESTIMATES AND MODEL SOURCES

2. EMISSION ESTIMATES AND MODEL SOURCES

The 2018 emissions inventory report identifies all existing toxic emissions units (TEUs) and activities that emit air toxics, in addition to estimating the source-specific annual and maximum daily TAC emissions. All sources will be evaluated based on the potential to emit (PTE) emissions from the emissions inventory report. Note that the emissions inventory report is in the process of being approved by ODEQ, and final emissions values may result in slight changes to the data submitted here.

The daily and annual TAC emission estimates will be converted to units of grams per second (g/s) for purposes of conducting the Level 3 Risk Assessment as shown in Appendix E. Additional detail regarding how the daily and annual TAC emission rates will be used to complete the Level 3 Risk Assessment will be provided in the Risk Assessment Work Plan.

The TEUs identified in the TAC emissions inventory will be represented in the dispersion model developed to represent the facility. Each TEU included in the dispersion model will be modeled using a unit emission rate equivalent to 1 g/s for all modeled source types except for line volume sources. The emission rate for each line volume source will be determined by dividing the total emission rate equally among the individual volume sources used to represent the roof vents on Building 1.

2.1 Batch House - Raw Materials Handling Railcars and trucks deliver the raw materials (e.g., sand and limestone) to the plant. Raw materials are gravity fed into an unloading pit and the elevators transport the materials to designated storage silos in the batch house. A small baghouse located inside the truck-unloading shed operates when trucks unload raw materials. Individual components are weighed on scales located under each silo and conveyed to the mixer where cullet (i.e., recycled glass) is added. The batch baghouse is the main dust collector that operates continuously to abate particulate-dust generated during the raw materials transport and mixing operations.

Fugitive emissions from the material handling and batch baghouse will be represented in the air dispersion model as a volume source with the model ID “S1”. The proposed release parameters for the volume source can be found in Table 3-8.

2.2 Glass Melting Furnaces The facility operates two glass-melting furnaces "A" and "D" that burn natural gas as their primary fuel. The shells of furnaces "B" and "C" physically occupy the space but they have been permanently shut down. Furnace A has dual side-ports with south and north stacks where the furnace exhaust gases are alternatingly exhausted. Furnace D is an end-port furnace with a single stack. The batch-mixture is charged into each furnace at the same rate as molten-glass is pulled out to achieve steady-state operation.

As required by OAR 340-245-0020(5), emissions from the combustion of natural gas will be segregated into a distinct TEU (or TEUs) and the risk at each exposure location from those TEUs will be determined separately. The two exhaust stacks for furnace A will be represented in the air dispersion model as individual point sources with the model IDs “S2” and “S3” for the southern and northern stack, respectively. The exhaust stack for furnace D will be represented in the air dispersion model as an individual point source with the model ID “S4”. The proposed release parameters for the point sources can be found in Table 3-7.



EMISSION ESTIMATES AND MODEL SOURCES

2.3 Bottle Forming As the pre-mixed batch enters the melting furnace through the batch charger, it initially floats on the top of the molten glass already in the furnace. Raw materials melt and pass through the melter and eventually flow through a "throat" at the bottom of furnace that leads into the refiner. As the molten glass flows through the refiner, the glass temperature decreases and becomes more uniform prior to entering the forehearths. Molten glass flows gravitationally from the refiner through the forehearth, where it is cooled to a uniform temperature and desirable viscosity prior to the forming machines.

Fugitive emissions generated by natural gas-fired combustion from the refiners and forehearths are assumed to be emitted through the nearby vents lined along the glass melting furnace building (Building 1) roof. The emissions will be represented in the air dispersion model as line volume sources with the model ID “S6”. The proposed release parameters for line volume sources can be found in Table 3-9.

2.4 Hot End Surface Treatment Semi-molten glass from the forehearths is sheared (forming gobs), and the gobs travel on delivery chutes to the forming machine molds. Once the glass containers are formed, the hot end surface treatment (HEST) process applies mono-butyl-tin trichloride (MBTT). The HEST process deposits a layer of tin oxide (SnO2) onto the glass surface. The exhaust from the HEST process vents through an abatement device. Ammonia is added to HEST hood exhaust prior to the abatement device so it can react with the excess MBTT to form solid particulate matter (PM) that can be collected in the baghouse. Following the HEST process, the bottles are annealed in the lehr, which is a long oven reheats and cools the containers in a way that relieves stresses in the glass.

Exhaust from the HEST process will be represented in the air dispersion model as a single point source with model ID “S5”. Fugitive emissions generated by natural gas-fired combustion from the lehr are assumed to be emitted through the nearby vents lined along the glass melting furnace building (Building 1) roof. The emissions will be represented in the air dispersion model as line volume sources with the model ID “S6”. The proposed release parameters for point sources and line volume sources can be found in Table 3-7 and 3-9, respectively.

2.5 Mold Preparation Mold preparation is an inherent part of the bottle-forming process. The mold preparation involves cleaning, lubricating, curing and heating molds when they are not being used in the forming machines. (Note: While a mold is in use, the operator periodically swabs molds with a graphite/oil solution as needed. This accounts for the emissions from the forming machines). A defective mold is purged from the production line for maintenance and repair. A purged-mold is cleaned in the burnout ovens and grit blasters, and then solid film lubricant is applied in the mold coating spray booth and cured in the mold curing ovens. The repaired mold's temperature is elevated in the mold heat ovens and quick fire ovens prior to re-entering the bottle forming production line.

Fugitive emissions from the solid film lubrication (SFL) and the emissions generated by natural gas-fired combustion from the mold burnout and curing ovens, mold heat oven, and quick fire oven are assumed to be emitted through the nearby vents lined along the glass melting furnace building (Building 1) roof. The emissions will be represented in the air dispersion model as line volume sources with the model ID “S9” for the solid film lubrication emissions and “S6” for the combustion emissions. The proposed release parameters for line volume sources can be found in Table 3-9.



MODEL SELECTION AND INPUTS

2.6 Warehouse Operations Finally, the finished bottles are coded and packaged for shipping. A bottle coder (ink-jet printer) prints tiny identification numbers on the glass containers as they rapidly move through the conveyor. Methyl ethyl ketone (MEK) is used as cleanup solvent and as the ink (carrier) solvent. MEK emissions are grouped under aggregate insignificant activities.

Roof vents and/or building openings are not located in close proximity to the MEK operations enclosure. The MEK fugitive emissions are dispersed in to the general facility from the ink jet printers when in use and when maintenance is done on the printers. As a result, the emissions from the image printing operation will be represented as a volume source with a model ID “S10”. The proposed release parameters for the volume source can be found in Table 3-8.

2.7 Boiler The facility operates a boiler with the rated capacity of 10.5 million British thermal units per hours (MMBtu/hr). The boiler is fueled by natural gas and is used for space heating and hot water. The exhaust stack for the boiler will be represented in the air dispersion model as an individual point source with the model ID “S7”. The proposed release parameters for the point source can be found in Table 3-7.

2.8 Miscellaneous Activities Maintenance activities include welding operations and minor machining activities that are done sporadically on as-needed basis. Fugitive emissions produced from these activities are controlled by dust collectors and are assumed to be emitted through the nearby vents lined along the glass melting furnace building (Building 1) roof. The emissions will be represented in the air dispersion model as line volume sources with the model ID “S8”. The proposed release parameters for line volume sources can be found in Table 3-9.

3. MODEL SELECTION AND INPUTS

The following procedures will be used to determine the off-site concentration impacts of relevant pollutants resulting from the existing O-B facility operations.

3.1 Model Selection Air quality dispersion modeling will be conducted to simulate the downwind transport of toxic air contaminants emitted by all the existing TEUs at the facility. The analysis will estimate maximum off-site concentrations using the AERMOD air dispersion modeling software (Version 9.6.5) developed by the American Meteorological Society/Environmental Protection Agency Regulatory Model Improvement Committee (AERMIC), which follows the procedure requirements as specified in 40 CFR Part 51, Appendix W, "Guidelines on Air Quality Models (Revised)”. AERMOD incorporates air dispersion for both surface and elevated sources, and accounts for differing terrain (i.e., simple and/or complex). AERMOD includes three components: a meteorological data preprocessor, AERMET; a terrain data preprocessor, AERMAP; and the air dispersion model, AERMOD. The dispersion model will be performed using the following versions for AERMOD and all preprocessors:

AERMOD: 19191

AERMET: 19191

AERMINUTE: 15272

AERMAP: 18081




AERSURFACE: 13016

BPIP: 04274

AERMOD modeling will be performed using regulatory default options, which include stack tip downwash, buoyancy-induced dispersion, upper-bound downwash concentrations, default wind speed profile exponents and vertical potential temperature gradients, and a routine for processing concentration averages during calm winds and when there are missing meteorological data. The effects from local terrain will also be incorporated.

3.2 Meteorological Data In preparation for air dispersion modeling, the following meteorological and terrain data files were obtained: five years of meteorological data (2014 to 2018) from the Portland International Airport (KPDX) meteorological tower surface data (Station #24229) in combination with the upper air data from Salem, Oregon (Station #24232), which can be obtained from National Weather Service. Both met stations represents the closest meteorological stations to the facility location with publicly available data to download.

The surface parameters (surface roughness, Bowen ratio, and albedo) for the Portland International Airport station was determined using AERSURFACE, which accounts for surface moisture conditions on a monthly basis for 12 evenly-spaced sectors. A 30-year moisture analysis for the Portland area was also conducted to determine the wetness condition for each month and is presented in Table 3-1. The months of December to February were assumed as “winter.” March to May were assumed as “spring”, June to August were assumed as “summer”, and September to November were assumed as “autumn”. The data was processed using the AERMET program with the adjust “U*” selected. As shown in Table 3-2, the surface and profile files produced by AERMET are more than 90% complete for each calendar quarter in the meteorological dataset.

Table 3-1 Surface Soil Moisture Condition Assessment

Meteorological Years

2014 2015 2016 2017 2018

Annual Precipitation (in)(a) 40.13 40.41 43.37 45.84 27.31

Soil Moisture Condition(b) Average Average Wet Wet Average (a) Climatological data obtained from National Oceanic and Atmospheric Administration National Climatic Data Center for Portland International Airport (WBAN: 24229). (b) Surface moisture conditions correspond to "Dry", "Average" or "Wet" soil content determined by comparing annual precipitation to 30-year climatological period. This method is consistent with the methodology set forth in the current version of the US EPA AERSURFACE User's Guide dated January 16, 2013. Based on the available 30-year climatological period between 1981 and 2010 data, the lower 30th percentile annual precipitation is 27.16 inches. The upper 70th percentile annual precipitation is 43.31 inches.




Table 3-2 Assessment of Missing Meteorological Data

Quarter

2014 2015 2016 2017 2018

Total Hrs

Missing Hrs

Available(b)

% Total Hrs

Missing Hrs

Available(b)

% Total Hrs

Missing Hrs

Available(b)

% Total Hrs

Missing Hrs

Available(b)

% Total Hrs

Missing Hrs

Available(b)

%

Q1 2,160 0 100.00 2,160 0 100.00 2184 0 100.00 2,160 0 100.00 2,160 11 99.49

Q2 2,184 2 99.91 2,184 2 99.91 2184 19 99.13 2,184 0 100.00 2,184 124 94.32

Q3 2,208 1 99.95 2,208 11 99.50 2208 1 99.95 2,208 4 99.82 2,208 113 94.88

Q4 2,208 17 99.23 2,208 22 99.00 2208 24 98.91 2,208 16 99.28 2,208 16 99.28

(a) Total hours obtained from the surface and profile files generated using AERMET (version 19191) for the period between 2014 through 2018. (b) Available hours (%) = (1 - [{missing hours} / {total hours}]) x (100%).




3.3 Receptor Grid Modeling will be conducted using a sufficient number of receptor locations to ensure that the maximum estimated impacts are identified. Following U.S. Environmental Protection Agency (USEPA) guidelines, receptor locations will be identified with sufficient density and spatial coverage to isolate the area with the highest impacts.

The radius of impact (ROI) receptors will be placed along the fence line of the facility at 25-meter increments to a distance of 200 meters. In addition, ROI receptors will be placed on a grid at 50-meter increments to a distance of 1,000 meters, at 100-meter increments out to a distance of 2,000 meters, at 200 meters to a distance of 5,000 and at 500-meter increments out to a distance of 10,000 meters.

Receptor locations will be provided in the UTM coordinate system. Receptor elevations will be obtained from the USEPA website located at https://www.epa.gov/scram/interim-access-and-process-use-1992-nlcd-and-ned. The U.S. Geological Service national elevation data system (NEDS) is no longer providing the 1992 National Land Cover Dataset (NLCD) or the NED in a format (i.e., GeoTIFF) that can be processed directly with the AERSURFACE and AERMAP programs, respectively. USEPA has provided an interim solution for these changes on its website.

As part of the AERMOD modeling system, AERMAP will be run to calculate terrain maximum heights for each modeled receptor using 1/3-Arc-Second NED elevation data. The results from AERMAP will be used as input to the AERMOD runstream file for each modeling run.

In anticipation of dispersion modeling, the Portland Metro RLIS Discovery and Washington Department of Ecology State Land Use zoning data were reviewed to determine land-use classifications for areas within the modeling domain. The land use surrounding the O-B facility is mostly characterized by the urban land use categories (industrial, commercial, and mixed use residential). Urban coefficients will be used in the modeling analysis. Selection of the urban boundary layer option in AERMOD also requires an estimate of the population of the urban area. For this analysis, a value to 632,309 will be used based on the population in the City of Portland proper. South of the facility, the land use categories include commercial, industrial, residential, parks, and open spaces. Figure 3A in Appendix C presents the existing land-use zoning identified for the modeling domain, and Figure 3B in Appendix C is provided for the area immediately surrounding the facility.

The statewide zoning classifications provide the basis for the initial categorization of exposure classifications (e.g. residential, non-residential worker, non-residential child, or acute), as shown in Table 3-3. Figures 3C and 3D in Appendix C present the corresponding exposure location categorization for the modeling domain and the immediate area surrounding the facility, respectively.

For purposes of this modeling protocol, O-B proposes the preliminary determination of exposure type to establish the receptor locations where ambient concentrations will be modeled. A crosswalk of receptor IDs, UTM coordinates and proposed exposure locations for each receptor has been provided as an electronic file along with this protocol.

Table 3-3 Summary of Statewide Zoning and Exposure Type Classification

Statewide Zoning Description Corresponding Exposure Type

Classification Risk Assessments to be

Performed

Beaches and Dunes Acute-only Acute Noncancer

Coastal Estuarine Acute-only Acute Noncancer

Coastal Shorelands Acute-only Acute Noncancer

https://www.epa.gov/scram/interim-access-and-process-use-1992-nlcd-and-ned

https://www.epa.gov/scram/interim-access-and-process-use-1992-nlcd-and-ned




Statewide Zoning Description Corresponding Exposure Type Classification

Risk Assessments to be Performed

Combo equal emphasis Acute-only Acute Noncancer

Combo with priority emphasis Acute-only Acute Noncancer

Commercial - Central Non-Residential Worker or Child

(if applicable) Cancer, Chronic and Acute

Noncancer

Commercial - General Non-Residential Worker or Child


Noncancer

Commercial - Neighborhood Non-Residential Worker or Child


Noncancer

Commercial - Office Non-Residential Worker or Child


Noncancer

Exclusive Farm Use 160+ Residential for structure, Non-

Residential Worker for property Cancer, Chronic and Acute

Noncancer



Noncancer



Noncancer

Exclusive Farm Use 80 Residential for structure, Non-


Noncancer

Federal Forest Acute-only Acute Noncancer

Federal Range Acute-only Acute Noncancer

Forest Acute-only Acute Noncancer

Future Urban Development Residential Cancer, Chronic and Acute

Noncancer

High-density Res. Residential Cancer, Chronic and Acute

Noncancer

Indian reservation/tribal trust Residential Cancer, Chronic and Acute

Noncancer

Industrial - Heavy Non-Residential Worker Cancer, Chronic and Acute

Noncancer

Industrial - Light Non-Residential Worker Cancer, Chronic and Acute

Noncancer

Industrial Campus Non-Residential Worker Cancer, Chronic and Acute

Noncancer

Industrial Office Non-Residential Worker Cancer, Chronic and Acute

Noncancer






Low-density Res. Residential Cancer, Chronic and Acute

Noncancer

Marginal Farm Land 10+ Non-Residential Worker Cancer, Chronic and Acute

Noncancer

Medium High-density Res. Residential Cancer, Chronic and Acute

Noncancer

Medium Low-density Res. Residential Cancer, Chronic and Acute

Noncancer

Medium-density Res. Residential Cancer, Chronic and Acute

Noncancer

Mineral and Aggregate Non-Residential Worker Cancer, Chronic and Acute

Noncancer

Mixed Farm-Forest 160+ Residential for structure, Non-


Noncancer

Mixed Farm-Forest 20 Residential for structure, Non-


Noncancer



Noncancer



Noncancer

Mixed-Use Com. & Res. Extremely High

Residential Cancer, Chronic and Acute

Noncancer

Mixed-Use Com. & Res. High Residential Cancer, Chronic and Acute

Noncancer

Mixed-Use Com. & Res. Low Residential Cancer, Chronic and Acute

Noncancer

Mixed-Use Com. & Res. Med-high Residential Cancer, Chronic and Acute

Noncancer

Mixed-Use Com. & Res. Medium Residential Cancer, Chronic and Acute

Noncancer

Mixed-Use Com. & Res. V.High Residential Cancer, Chronic and Acute

Noncancer

No Data Acute-only Acute Noncancer

Open Space/Conservation Acute-only Acute Noncancer

Other Acute-only Acute Noncancer






Parks & Open Space Acute-only Acute Noncancer

Prime Forest 80 Acute-only Acute Noncancer

Public & semi-public Uses Non-Residential Worker or Child


Noncancer

Public Facilities Non-Residential Worker or Child


Noncancer

Rural Commercial Non-Residential Worker Cancer, Chronic and Acute

Noncancer

Rural Industrial Non-Residential Worker Cancer, Chronic and Acute

Noncancer

Rural Residential 1 acre Residential Cancer, Chronic and Acute

Noncancer

Rural Residential 10 acres Residential Cancer, Chronic and Acute

Noncancer

Rural Residential 2-4 acres Residential Cancer, Chronic and Acute

Noncancer


Noncancer

Secondary Forest 80 Acute-only Acute Noncancer

UC Rural Commercial Non-Residential Worker Cancer, Chronic and Acute

Noncancer

UC Rural Industrial Non-Residential Worker Cancer, Chronic and Acute

Noncancer

Very High-density Res. Residential Cancer, Chronic and Acute

Noncancer

Very Low-density Res. Residential Cancer, Chronic and Acute

Noncancer

Open Space/Conservation Acute-only Acute Noncancer

Other Acute-only Acute Noncancer

Parks & Open Space Acute-only Acute Noncancer

Prime Forest 80 Acute-only Acute Noncancer

Public & semi-public Uses Non-Residential Worker or Child


Noncancer

Public Facilities Non-Residential Worker or Child


Noncancer






Rural Commercial Non-Residential Worker Cancer, Chronic and Acute

Noncancer

Rural Industrial Non-Residential Worker Cancer, Chronic and Acute

Noncancer

Rural Residential 1 acre Residential Cancer, Chronic and Acute

Noncancer


Noncancer

Rural Residential 2-4 acres Residential Cancer, Chronic and Acute

Noncancer


Noncancer

Secondary Forest 80 Acute-only Acute Noncancer

UC Rural Commercial Non-Residential Worker Cancer, Chronic and Acute

Noncancer

UC Rural Industrial Non-Residential Worker Cancer, Chronic and Acute

Noncancer

Very High-density Res. Residential Cancer, Chronic and Acute

Noncancer

Very Low-density Res. Residential Cancer, Chronic and Acute

Noncancer Reference: Zoning descriptions obtained from State of Oregon Department of Environmental Quality’s “Cleaner Air Oregon State Zoning to Exposure Location Crosswalk”, April 15, 2020 and Portland Metro RLIS Discovery.

Sensitive receptors (e.g., schools) located within approximately 1 kilometer (km) from the facility property boundary were identified and are presented in Table 3-4 below.

Table 3-4 Sensitive Receptors Locations

Receptor UTM Easting (X)

(m) UTM Northing (Y)

(m)

Helensview School 533,218 5,045,383

Prescott Elementary 534,594 5,044,705

Joyful Heart Day School 533,441 5,044,932

Airport Learning Tree 535,990 5,045,873

Discovery Gardens Childcare 532,943 5,044,403 UTM = Universal Transverse Mercator; m = meters




3.4 Aerodynamic Downwash Evaluation of building downwash on the adjacent stack is deemed necessary, since the stack height may be below Good Engineering Practice (GEP) heights. The formula for GEP height estimation is:

Hs = Hb + 1.50Lb

where: Hs = GEP stack height Hb = building height Lb = the lesser building dimension of the height, length, or width

The effects of aerodynamic downwash due to buildings and other structures will be accounted for by using wind direction-specific building parameters calculated by the USEPA-approved Building Parameter Input Program Prime (BPIP-Prime) and the algorithms included in AERMOD. Based on examination of plot plans for the relationship of sources to the location of facility structures, the locations and dimensions of emission sources and facility structures will be input to the BPIP-Prime software package, which calculates the direction-specific building dimensions for input into AERMOD. A downwash analysis will be performed on the emission sources.

The building dimensions evaluated for building downwash for this site can be found in Appendix D.




3.5 Model Source Inputs Emission sources will be categorized into three types: point, volume, or line volume sources. Point sources at the facility include the glass melting furnaces A and D and the natural gas-fueled boiler. Furnace A has side-ports and alternatively exhausts from two stacks (south and north exhaust stacks). Furnace D is an end-port furnace with a single stack. The facility also operates a 10.5 MMBtu/hr boiler with a single stack.

Volume sources at the facility include the fugitive emissions from the raw material handling activities and bottle coder printing operations. The raw material handling at the site consists of the unloading conveyor/elevator, storage silos, and baghouses. A Methyl ethyl ketone (MEK)-based ink is used for the coder printing process, as well as a MEK-based solvent for cleaning the print heads.

Line volume sources at the facility include hot end surface treatment operation, miscellaneous natural gas combustion (i.e., refiners, lehrs, and forehearths), nickel spray welding, and Solid Film Lubricant (SFL) coating. All four activities occur within Building 1 where emissions from these sources are most likely released to the outside from the two roof vents that extend along the length of the building. One roof vent is located on the eastern side of the building and the other one is on the western side. Table 3-5 lists the emission sources discharged to air inside Building 1 and are subsequently vented through the roof vents. Detailed source information can be found in the supplemental and supporting information spreadsheets provided along with the emissions inventory. Table 3-6 provide a crosswalk between the emission inventory TEUs and the proposed modeling source IDs.

Table 3-5 Emission Sources from Building 1

TEU ID Description AERMOD Source ID

EU5 Hot End Surface Treatment (MBTT+NH3) S5

EU6 Miscellaneous natural gas combustion sources

(refiners, foreheaths, lehrs, mold burnout and curing oven, model heat oven, and quick fire oven)

S6

EU10 Fugitive emissions from nickel spray, SMAW,

GMAW, and GTAW welding S8

SFL Fugitive emissions from solid film lubrication S9

Table 3-6 Proposed Model IDs for Inventory TEUs


EU1

Raw material handling activities (sand and limestone) and batch house

S1

EU4 GM1 Southern stack from furnace A (glass emissions)

S2

EU4 GM1 Nat gas Southern stack from furnace A (nat gas emissions)

S2





EU4 GM1 Northern stack from furnace A (amber emissions)

S3

EU4 GM1 Nat gas Northern stack from furnace A (nat gas emissions)

S3

EU4 GM4 Stack from furnace D (green glass and amber glass emissions)

S4

EU4 GM4 Nat gas Stack from furnace D (nat gas emissions) S4

EU5 Hot end surface treatment (MBTT and NH3)

S5

EU6 Fugitive emissions from miscellaneous natural gas fuel burning

S6

EU7 Stack from natural gas boiler S7

EU10 Fugitive emissions from nickel spray, SMAW, GMAW, and GTAW welding

S8

SFL Fugitive emissions from solid film lubrication

S9

Image Fugitive emissions from image printing (MEK solvent, MEK ink and MEK UV)

S10

For the risk assessment, unit emission rates will be used to simulate unitized concentrations for each source. Unit concentrations will be calculated based on the source parameters, receptor grid, and meteorological database. The point sources and volume sources will be modeled using a 1 gram per second (g/s) emission rate. The emission rate for each line volume source will be determined by dividing the total emission rate equally among the individual volume sources used to represent the roof vents on Building 1. Dispersion model source inputs for this site are summarized in Tables 3-7, 3-8 and 3-9.




Table 3-7 Point Source Release Parameters


UTM Easting (X)

(m)

UTM Northing (Y)

(m)

Stack Height (m)

Stack Temperature

(K)

Exit Velocity

(m/s)

Stack Diameter

(m)

Model Emission Rate (g/s)

EU4 GM1

Southern stack from furnace A (glass and nat

gas emissions)

S2 534,043 5,045,531 21.49 391.48 15.58 1.12 1

EU4 GM1

Northern stack from furnace A (amber and nat

gas emissions)

S3 534,047 5,045,543 21.49 380.37 15.94 1.12 1

EU4 GM4

Stack from furnace D (green glass, amber glass

and nat gas emissions)

S4 534,053 5,045,579 31.67 493.71 15.77 0.76 1

EU7 Stack from natural gas boiler

S7 534,080 5,045,570 24.41 773.15 1.72 0.79 1

ID = Identification; UTM = Universal Transverse Mercator; m = meters; K = Kelvin; m/s = meters per second; g/s = grams per second




Table 3-8 Volume Sources Parameters


UTM Easting (X)

(m)

UTM Northing (Y)

(m)

Release Height

(m)

Initial Lateral

Size Y (m)

Initial Vertical

Size Z (m)

Model Emission Rate (g/s)

EU1 Raw material handling activities (sand and limestone) and batch house

S1 534,075 5,045,529 27.15 2.98 12.63 1

Image Fugitive emissions from image printing (MEK solvent, MEK ink and MEK UV)

S10 533,971 5,045,573 9.09 11.63 8.46 1

ID = Identification; UTM = Universal Transverse Mercator; m = meter; K = Kelvin; g/s = grams per second

Table 3-9 Line Volume Sources Parameters


UTM Easting (X)

(m)

UTM Northing (Y)

(m)

Release Height

(m)

Initial Lateral

Size Y (m)

Initial Vertical

Size Z (m)

Model Unit Emission Rate (g/s)

EU5 Hot End Surface Treatment (MBTT+NH3) S5 534,043 5,045,589 30.02 4.57 13.96 0.056














UTM Easting (X)

(m)

UTM Northing (Y)

(m)

Release Height

(m)

Initial Lateral

Size Y (m)

Initial Vertical

Size Z (m)











S6 534,043 5,045,589 30.02 4.57 13.96 0.056


S6 534,041 5,045,582 30.02 4.57 13.96 0.056


S6 534,040 5,045,575 30.02 4.57 13.96 0.056


S6 534,038 5,045,568 30.02 4.57 13.96 0.056


S6 534,036 5,045,561 30.02 4.57 13.96 0.056


S6 534,034 5,045,554 30.02 4.57 13.96 0.056


S6 534,033 5,045,547 30.02 4.57 13.96 0.056





UTM Easting (X)

(m)

UTM Northing (Y)

(m)

Release Height

(m)

Initial Lateral

Size Y (m)

Initial Vertical

Size Z (m)



S6 534,031 5,045,540 30.02 4.57 13.96 0.056


S6 534,029 5,045,533 30.02 4.57 13.96 0.056


S6 534,028 5,045,593 30.02 4.57 13.96 0.056


S6 534,026 5,045,586 30.02 4.57 13.96 0.056


S6 534,024 5,045,579 30.02 4.57 13.96 0.056


S6 534,022 5,045,572 30.02 4.57 13.96 0.056


S6 534,020 5,045,565 30.02 4.57 13.96 0.056


S6 534,019 5,045,558 30.02 4.57 13.96 0.056


S6 534,017 5,045,550 30.02 4.57 13.96 0.056


S6 534,015 5,045,543 30.02 4.57 13.96 0.056


S6 534,013 5,045,536 30.02 4.57 13.96 0.056


S8 534,043 5,045,589 30.02 4.57 13.96 0.056





UTM Easting (X)

(m)

UTM Northing (Y)

(m)

Release Height

(m)

Initial Lateral

Size Y (m)

Initial Vertical

Size Z (m)



S8 534,041 5,045,582 30.02 4.57 13.96 0.056


S8 534,040 5,045,575 30.02 4.57 13.96 0.056


S8 534,038 5,045,568 30.02 4.57 13.96 0.056


S8 534,036 5,045,561 30.02 4.57 13.96 0.056


S8 534,034 5,045,554 30.02 4.57 13.96 0.056


S8 534,033 5,045,547 30.02 4.57 13.96 0.056


S8 534,031 5,045,540 30.02 4.57 13.96 0.056


S8 534,029 5,045,533 30.02 4.57 13.96 0.056


S8 534,028 5,045,593 30.02 4.57 13.96 0.056


S8 534,026 5,045,586 30.02 4.57 13.96 0.056


S8 534,024 5,045,579 30.02 4.57 13.96 0.056


S8 534,022 5,045,572 30.02 4.57 13.96 0.056





UTM Easting (X)

(m)

UTM Northing (Y)

(m)

Release Height

(m)

Initial Lateral

Size Y (m)

Initial Vertical

Size Z (m)



S8 534,020 5,045,565 30.02 4.57 13.96 0.056


S8 534,019 5,045,558 30.02 4.57 13.96 0.056


S8 534,017 5,045,550 30.02 4.57 13.96 0.056


S8 534,015 5,045,543 30.02 4.57 13.96 0.056


S8 534,013 5,045,536 30.02 4.57 13.96 0.056

SFL Fugitive emissions from solid film lubrication S9 534,043 5,045,589 30.02 4.57 13.96 0.056
















UTM Easting (X)

(m)

UTM Northing (Y)

(m)

Release Height

(m)

Initial Lateral

Size Y (m)

Initial Vertical

Size Z (m)







SFL Fugitive emissions from solid film lubrication S9 534,013 5,045,536 30.02 4.57 13.96 0.056 ID = Identification; UTM = Universal Transverse Mercator; m = meter; K = Kelvin; g/s = grams per second



MODELING ANALYSIS DOCUMENTATION

4. MODELING ANALYSIS DOCUMENTATION

The following procedures will be used to report and submit modeling results.

4.1 Modeling Results The modeling methodology and assumptions will be documented in the air quality analysis along with a summary of the results.

The model-predicted concentrations will be used to evaluate health risks based on the toxic air contaminant emissions from the facility. Each TEU will be modeled with a unit emission rate of 1 g/s. The unitized modeled concentrations from each TEU are used to convert the TEU emission rates to exposure concentrations, which are then apportioned by the respective TAC emission rates from that TEU. From these exposure concentrations, an excess cancer risk and/or HI can be calculated at each model receptor from each TAC. The modeled results across the receptor grid will be used to graphically show the spatial distribution of risks and/or concentrations.

4.2 Submittal The air quality analysis submittal will consist of a report and electronic modeling files, which will include:

AERMAP, BPIP, and AERMOD input and output files;

AERSURFACE files;

Plot files;

Downwash files including building heights and locations; and

Meteorological data.


APPENDIX A SITE LOCATION MAP


APPENDIX B GRAPHIC DISPLAY OF RECEPTOR GRID

08/2020 Universal Transverse Mercator Coordinate System

Figure 2Receptor Grid

Owens-Brockway Glass Container Inc.9710 NE Glass Plant Road

Portland, OR

Legend

Proposed Receptor

510,000 515,000 520,000 525,000 530,000 535,000 540,000 545,000 550,000 555,000 560,000

Easting UTM (m)

5,035,000

5,040,000

5,045,000

5,050,000

5,055,000

5,060,000

Nor

thin

g U

TM (m

)


APPENDIX C LAND USE MAP

Site Location

LegendSite LocationCommercialFuture Urban DevelopmentIndustrialMulti FamilyMixed Use ResidentialPublic FacilitiesParks and Open SpacesRuralSingle Family

0 2 4

Miles

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Source: Esri - World Topoographic Map; NAD 1983 StatePlane Oregon North FIPS 3601 FeetERM

Figure 3AExisting Land Use

Zoning ClassificationsOwens-Brockway Glass Container Inc

9710 NE Glass Plant RoadPortland, Oregon

0 1 20.5Miles

¯

Notes:Zoning data downloaded from Portland Metro RLISDiscovery and Washington Department of EcologyState Land use.

Site Location

LegendSite LocationCommercialIndustrialMixed Use ResidentialParks and Open Spaces

RuralSingle Family

0 2,200 4,400

Feet

FILE

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Figure 3BExisting Land Use Zoning

Classifications in the Immediate AreaOwens-Brockway Glass Container Inc


0 0.15 0.30.075Miles

¯

Notes:Zoning data downloaded from Portland Metro RLISDiscovery.

Site Location

LegendSite Location

Child

Worker

Acute

Residential

0 2 4

Miles

FILE

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Figure 3CExposure Categorization

Owens-Brockway Glass Container Inc9710 NE Glass Plant Road

Portland, Oregon

0 1 20.5Miles

¯

Notes:Zoning data downloaded from Portland Metro RLISDiscovery and Washington Department of EcologyState Land use.

Site Location

Head StartSacajawea

Parkrose SD 3

RiglerElementary

Mt. Hood CommunityCollege Head

Start-Thompson SiteRussell

AcademyJason LeeElementary

Rose CityCooperativePreschool

ShaverElementary

MargaretScott

Elementary

Madison High

ArchbishopHoward School

HelensviewHigh

Hand inHand (DART)

SacramentoElementary

OKECHI Village& Health

Center Inc.

Parkrose High

TAG Office atRice School

PortlandSD 1J

ScottElementary

Portland ChristianJunior/Senior High

CommunityTransitional

School

CityChristianSchool

Parkrose High

TrinityLutheran

Parkrose SD 3

RosewayHeights

Elementary

Accessat Rose

City Park

PrescottElementary

ParkroseMiddle

CrossroadsChristian

NAYA EarlyCollege

Academy

LegendSite LocationChild

WorkerAcuteResidential

0 2,200 4,400

Feet

FILE

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Figure 3DExposure Categorization

in the Immediate AreaOwens-Brockway Glass Container Inc


0 10 205Miles

¯

Notes:Zoning data downloaded from Portland Metro RLISDiscovery.


APPENDIX D BUILDING DIMENSIONS


APPENDIX E ANNUAL AND DAILY EMISSION RATES

(lbs/yr) (g/s) (lbs/yr) (g/s) (lbs/yr) (g/s) (lbs/yr) (g/s) (lbs/yr) (g/s) (lbs/yr) (g/s) (lbs/yr) (g/s) (lbs/yr) (g/s)MODEL ID ‐‐‐

7440-38-2 Arsenic and compounds 1.56E+02 2.24E-03 0.00E+00 0.00E+00 2.31E+01 3.33E-04 1.29E+01 1.86E-04 0.00E+00 0.00E+00 5.40E-02 7.77E-07 1.84E-02 2.65E-07 0.00E+00 0.00E+00

7440-41-7 Beryllium and compounds 2.25E-02 3.24E-07 0.00E+00 0.00E+00 4.91E-03 7.06E-08 3.50E-03 5.03E-08 0.00E+00 0.00E+00 3.24E-03 4.66E-08 1.10E-03 1.59E-08 0.00E+00 0.00E+00

7440-43-9 Cadmium and compounds 5.44E+00 7.83E-05 0.00E+00 0.00E+00 2.23E+00 3.21E-05 1.58E+00 2.27E-05 0.00E+00 0.00E+00 2.97E-01 4.27E-06 1.01E-01 1.46E-06 0.00E+00 0.00E+00

18540-29-9 Chromium VI, chromate, and dichromate particulate 1.46E-01 2.10E-06 0.00E+00 0.00E+00 1.12E-02 1.61E-07 1.56E-02 2.25E-07 0.00E+00 0.00E+00 3.78E-01 5.44E-06 1.29E-01 1.85E-06 0.00E+00 0.00E+00

7439-92-1 Lead and compounds 4.00E+02 5.75E-03 0.00E+00 0.00E+00 2.70E+01 3.89E-04 1.70E+02 2.44E-03 0.00E+00 0.00E+00 0.0000 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00

7439-96-5 Manganese and compounds 3.29E+00 4.73E-05 0.00E+00 0.00E+00 6.45E-01 9.27E-06 4.22E-01 6.06E-06 0.00E+00 0.00E+00 1.03E-01 1.48E-06 3.50E-02 5.03E-07 0.00E+00 0.00E+00

7439-97-6 Mercury and compounds 7.52E-01 1.08E-05 0.00E+00 0.00E+00 2.95E-01 4.24E-06 2.96E-01 4.26E-06 0.00E+00 0.00E+00 7.02E-02 1.01E-06 2.39E-02 3.44E-07 0.00E+00 0.00E+00

7440-02-0 Nickel and compounds 6.63E-01 9.54E-06 0.00E+00 0.00E+00 1.10E+00 1.58E-05 6.83E-01 9.82E-06 0.00E+00 0.00E+00 5.67E-01 8.16E-06 1.93E-01 2.78E-06 0.00E+00 0.00E+00

7782-49-2 Selenium and compounds 3.61E+01 5.19E-04 7.87E-03 1.13E-07 1.51E+01 2.17E-04 9.09E+00 1.31E-04 6.24E-03 8.98E-08 6.48E-03 9.32E-08 2.21E-03 3.18E-08 0.00E+00 0.00E+00

7440-36-0 Antimony and compounds 7.53E+00 1.08E-04 0.00E+00 0.00E+00 1.23E+00 1.77E-05 5.26E-01 7.57E-06 0.00E+00 0.00E+00 0.0000 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00

7440-48-4 Cobalt and compounds 6.07E-02 8.72E-07 0.00E+00 0.00E+00 1.95E-02 2.81E-07 3.46E-02 4.98E-07 0.00E+00 0.00E+00 2.27E-02 3.26E-07 7.73E-03 1.11E-07 0.00E+00 0.00E+00

7440-50-8 Copper and compounds 7.61E+00 1.10E-04 0.00E+00 0.00E+00 2.40E+00 3.46E-05 2.87E+00 4.12E-05 0.00E+00 0.00E+00 2.30E-01 3.30E-06 7.82E-02 1.12E-06 0.00E+00 0.00E+00

50-00-0 Formaldehyde 2.28E+01 3.27E-04 0.00E+00 0.00E+00 1.83E+00 2.63E-05 8.50E+00 1.22E-04 0.00E+00 0.00E+00 2.03E+01 2.91E-04 6.90E+00 9.92E-05 0.00E+00 0.00E+00

75-07-0 Acetaldehyde 0.00E+00 0.00E+00 7.02E+00 1.01E-04 0.00E+00 0.00E+00 0.00E+00 0.00E+00 5.56E+00 8.00E-05 5.78E+00 8.31E-05 1.97E+00 2.83E-05 0.00E+00 0.00E+00

107-02-8 Acrolein 0.00E+00 0.00E+00 5.90E-03 8.49E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-03 6.73E-08 0.0000 0.00E+00 1.66E-03 2.38E-08 0.00E+00 0.00E+00

7440-39-3 Barium and compounds 0.00E+00 0.00E+00 1.44E+00 2.08E-05 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.14E+00 1.65E-05 1.19E+00 1.71E-05 4.05E-01 5.82E-06 0.00E+00 0.00E+00

71-43-2 Benzene 0.00E+00 0.00E+00 6.89E-01 9.91E-06 0.00E+00 0.00E+00 0.00E+00 0.00E+00 5.46E-01 7.85E-06 5.67E-01 8.16E-06 1.93E-01 2.78E-06 0.00E+00 0.00E+00

100-41-4 Ethyl benzene 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.0000 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00

110-54-3 Hexane 0.00E+00 0.00E+00 5.90E+02 8.49E-03 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E+02 6.73E-03 4.86E+02 6.99E-03 1.66E+02 2.38E-03 0.00E+00 0.00E+00

1313-27-5 Molybdenum trioxide 0.00E+00 0.00E+00 5.41E-01 7.78E-06 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.29E-01 6.17E-06 4.46E-01 6.41E-06 1.52E-01 2.18E-06 0.00E+00 0.00E+00

83-32-9 Acenaphthene 0.00E+00 0.00E+00 5.90E-04 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-04 6.73E-09 4.86E-04 6.99E-09 1.66E-04 2.38E-09 0.00E+00 0.00E+00

208-96-8 Acenaphthylene 0.00E+00 0.00E+00 5.90E-04 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-04 6.73E-09 4.86E-04 6.99E-09 1.66E-04 2.38E-09 0.00E+00 0.00E+00

120-12-7 Anthracene 0.00E+00 0.00E+00 7.87E-04 1.13E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 6.24E-04 8.98E-09 6.48E-04 9.32E-09 2.21E-04 3.18E-09 0.00E+00 0.00E+00

56-55-3 Benz[a]anthracene 0.00E+00 0.00E+00 5.90E-04 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-04 6.73E-09 4.86E-04 6.99E-09 1.66E-04 2.38E-09 0.00E+00 0.00E+00

50-32-8 Benzo[a]pyrene 0.00E+00 0.00E+00 3.94E-04 5.66E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.12E-04 4.49E-09 3.24E-04 4.66E-09 1.10E-04 1.59E-09 0.00E+00 0.00E+00

205-99-2 Benzo[b]fluoranthene 0.00E+00 0.00E+00 5.90E-04 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-04 6.73E-09 4.86E-04 6.99E-09 1.66E-04 2.38E-09 0.00E+00 0.00E+00

191-24-2 Benzo[g,h,i]perylene 0.00E+00 0.00E+00 3.94E-04 5.66E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.12E-04 4.49E-09 3.24E-04 4.66E-09 1.10E-04 1.59E-09 0.00E+00 0.00E+00

207-08-9 Benzo[k]fluoranthene 0.00E+00 0.00E+00 5.90E-04 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-04 6.73E-09 4.86E-04 6.99E-09 1.66E-04 2.38E-09 0.00E+00 0.00E+00

218-01-9 Chrysene 0.00E+00 0.00E+00 5.90E-04 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-04 6.73E-09 4.86E-04 6.99E-09 1.66E-04 2.38E-09 0.00E+00 0.00E+00

226-36-8 Dibenz[a,h]acridine 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.0000 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00

206-44-0 Fluoranthene 0.00E+00 0.00E+00 9.84E-04 1.42E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.80E-04 1.12E-08 8.10E-04 1.17E-08 2.76E-04 3.97E-09 0.00E+00 0.00E+00

86-73-7 Fluorene 0.00E+00 0.00E+00 9.18E-04 1.32E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.28E-04 1.05E-08 7.56E-04 1.09E-08 2.58E-04 3.71E-09 0.00E+00 0.00E+00

193-39-5 Indeno[1,2,3-cd]pyrene 0.00E+00 0.00E+00 5.90E-04 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-04 6.73E-09 4.86E-04 6.99E-09 1.66E-04 2.38E-09 0.00E+00 0.00E+00

91-57-6 2-Methyl naphthalene 0.00E+00 0.00E+00 7.87E-03 1.13E-07 0.00E+00 0.00E+00 0.00E+00 0.00E+00 6.24E-03 8.98E-08 6.48E-03 9.32E-08 2.21E-03 3.18E-08 0.00E+00 0.00E+00

91-20-3 Naphthalene 0.00E+00 0.00E+00 2.00E-01 2.88E-06 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.59E-01 2.28E-06 1.65E-01 2.37E-06 5.61E-02 8.07E-07 0.00E+00 0.00E+00

85-01-8 Phenanthrene 0.00E+00 0.00E+00 5.58E-03 8.02E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.42E-03 6.36E-08 4.59E-03 6.60E-08 1.56E-03 2.25E-08 0.00E+00 0.00E+00

129-00-0 Pyrene 0.00E+00 0.00E+00 1.64E-03 2.36E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.30E-03 1.87E-08 1.35E-03 1.94E-08 4.60E-04 6.62E-09 0.00E+00 0.00E+00

57-97-6 7,12-Dimethylbenz[a]anthracene 0.00E+00 0.00E+00 5.25E-03 7.55E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.16E-03 5.98E-08 4.32E-03 6.21E-08 1.47E-03 2.12E-08 0.00E+00 0.00E+00

56-49-5 3-Methylcholanthrene 0.00E+00 0.00E+00 5.90E-04 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-04 6.73E-09 4.86E-04 6.99E-09 1.66E-04 2.38E-09 0.00E+00 0.00E+00

108-88-3 Toluene 0.00E+00 0.00E+00 1.12E+00 1.60E-05 0.00E+00 0.00E+00 0.00E+00 0.00E+00 8.84E-01 1.27E-05 9.18E-01 1.32E-05 3.13E-01 4.50E-06 0.00E+00 0.00E+00

7440-62-2 Vanadium (fume or dust) 0.00E+00 0.00E+00 7.54E-01 1.09E-05 0.00E+00 0.00E+00 0.00E+00 0.00E+00 5.98E-01 8.60E-06 6.21E-01 8.93E-06 2.12E-01 3.04E-06 0.00E+00 0.00E+00

1330-20-7Xylene (mixture), including m-xylene, o-xylene, p-xylene

0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.0000 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00

7440-66-6 Zinc and compounds 0.00E+00 0.00E+00 9.51E+00 1.37E-04 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.54E+00 1.08E-04 7.83E+00 1.13E-04 2.67E+00 3.84E-05 0.00E+00 0.00E+00

7664-41-7 Ammonia 0.00E+00 0.00E+00 1.05E+03 1.51E-02 0.00E+00 0.00E+00 0.00E+00 0.00E+00 8.32E+02 1.20E-02 8.64E+02 1.24E-02 2.94E+02 4.23E-03 1.26E+04 1.81E-01

7647-01-0 Hydrochloric acid 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.0000 0.00E+00 0.00E+00 0.00E+00 7.56E+01 1.09E-03

7631-86-9 Silica, crystalline (respirable) 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.0000 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00

71-36-3 n-butyl alcohol 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.0000 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00

1310-73-2 Sodium hydroxide 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.0000 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00

78-93-3 2-Butanone (Methyl ethyl ketone) 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.0000 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00

67-63-0 Isopropyl alcohol 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.0000 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00

108-10-1 Methyl isobutyl ketone (MIBK, Hexone) 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.0000 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00

Appendix EAnnual Emission RatesOwens‐Brockway Glass Container Inc. ‐ Portland

Notes:(a) Emission rate (g/s) = (annual emissions estimate [lb/yr]) x (453.592 g/lb) x (yr/8,760 hrs) x (hr/3,600 s)(b) Emissions estimate obtained from O-I emissions inventory dated May 4, 2020

CAS TACFURNACE A (NORTH & SOUTH STACKS) FURNACE D

FUGITIVE EMISSIONS‐MISC NG

BOILERHOT END SURFACE TREATMENT

(MBTT and NH3)EU4 GM1 EU4 GM1 Nat gas EU4 GM4 green glass EU4 GM4 amber glass EU4 GM4 Nat gas EU6 EU7 EU5

S2, S3 S4 S6 S7 S5

ERM-West, Inc.Appendix E - Annual Emissions Rates_011521.xlsx Page 1 of 2 1/15/21

MODEL ID ‐‐‐

7440-38-2 Arsenic and compounds

7440-41-7 Beryllium and compounds

7440-43-9 Cadmium and compounds

18540-29-9 Chromium VI, chromate, and dichromate particulate

7439-92-1 Lead and compounds

7439-96-5 Manganese and compounds

7439-97-6 Mercury and compounds

7440-02-0 Nickel and compounds

7782-49-2 Selenium and compounds

7440-36-0 Antimony and compounds

7440-48-4 Cobalt and compounds

7440-50-8 Copper and compounds

50-00-0 Formaldehyde

75-07-0 Acetaldehyde

107-02-8 Acrolein

7440-39-3 Barium and compounds

71-43-2 Benzene

100-41-4 Ethyl benzene

110-54-3 Hexane

1313-27-5 Molybdenum trioxide

83-32-9 Acenaphthene

208-96-8 Acenaphthylene

120-12-7 Anthracene

56-55-3 Benz[a]anthracene

50-32-8 Benzo[a]pyrene

205-99-2 Benzo[b]fluoranthene

191-24-2 Benzo[g,h,i]perylene

207-08-9 Benzo[k]fluoranthene

218-01-9 Chrysene

226-36-8 Dibenz[a,h]acridine

206-44-0 Fluoranthene

86-73-7 Fluorene

193-39-5 Indeno[1,2,3-cd]pyrene

91-57-6 2-Methyl naphthalene

91-20-3 Naphthalene

85-01-8 Phenanthrene

129-00-0 Pyrene

57-97-6 7,12-Dimethylbenz[a]anthracene

56-49-5 3-Methylcholanthrene

108-88-3 Toluene

7440-62-2 Vanadium (fume or dust)


7440-66-6 Zinc and compounds

7664-41-7 Ammonia

7647-01-0 Hydrochloric acid

7631-86-9 Silica, crystalline (respirable)

71-36-3 n-butyl alcohol

1310-73-2 Sodium hydroxide

78-93-3 2-Butanone (Methyl ethyl ketone)

67-63-0 Isopropyl alcohol

108-10-1 Methyl isobutyl ketone (MIBK, Hexone)

Appendix EAnnual Emission RatesOwens‐Brockway Glass Container Inc. ‐ Portland

Notes:(a) Emission rate (g/s) = (annual emissions estimate [lb/yr]) x (453.592 g/lb) x (yr/8,760 hrs) x (hr/3,600 s)(b) Emissions estimate obtained from O-I emissions inventory dated May 4, 2020

CAS TAC

(lbs/yr) (g/s) (lbs/yr) (g/s) (lbs/yr) (g/s) (lbs/yr) (g/s) (lbs/yr) (g/s) (lbs/yr) (g/s) (lbs/yr) (g/s) (lbs/yr) (g/s) (lbs/yr) (g/s)‐‐‐ ‐‐‐ ‐‐‐ ‐‐‐ ‐‐‐ ‐‐‐ ‐‐‐ ‐‐‐ ‐‐‐ ‐‐‐

0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.61E+01 5.19E-04

0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 9.51E-03 1.37E-07


1.97E-04 2.83E-09 4.58E-05 6.59E-10 0.00E+00 0.00E+00 6.06E-08 8.72E-13 2.43E-04 3.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.56E-01 2.25E-06


0.00E+00 0.00E+00 1.25E-02 1.80E-07 2.48E-07 3.57E-12 1.52E-07 2.18E-12 1.25E-02 1.80E-07 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.13E+00 1.62E-05


5.08E-01 7.30E-06 2.42E-05 3.49E-10 0.00E+00 0.00E+00 1.21E-06 1.74E-11 5.08E-01 7.30E-06 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2.99E+00 4.30E-05




0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.21E-07 1.74E-12 1.21E-07 1.74E-12 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 5.35E+00 7.69E-05






0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2.26E+00 3.25E-05 0.00E+00 0.00E+00 2.26E+00 3.25E-05












0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00





0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 9.34E-01 1.34E-05 1.35E+00 1.94E-05











0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.07E+02 1.54E-03 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.07E+02 1.54E-03



0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 5.84E+02 8.41E-03 5.84E+02 8.41E-03

0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 9.34E-01 1.34E-05 9.34E-01 1.34E-05

0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 5.54E+00 7.96E-05 5.54E+00 7.96E-05

FUGITIVE EMISSIONS FROM WELDING RAW MATERIAL HANDLING (SAND AND LIMESTONE) AND

FUGITIVE EMISSIONS FROM SOLID FILM

FUGITIVE EMISSIONS FROM IMAGE PRINTING

TOTAL FACILITY ANNUAL EMISSIONS ESTIMATE

WELDING PROCESSES TOTALEU‐10 Nickel Spray EU‐10 SMAW welding EU‐10 GMAW welding EU‐10 GTAW welding EU10 EU1 SFL Image

S8 S1 S9 S10

ERM-West, Inc.Appendix E - Annual Emissions Rates_011521.xlsx Page 2 of 2 1/15/21

(lbs/day) (g/s) (lbs/day) (g/s) (lbs/day) (g/s) (lbs/day) (g/s) (lbs/day) (g/s) (lbs/day) (g/s)MODEL ID ‐‐‐

7440-38-2 Arsenic and compounds 4.27E-01 2.24E-03 0.00E+00 0.00E+00 6.34E-02 3.33E-04 3.54E-02 1.86E-04 0.00E+00 0.00E+00 1.48E-04 7.77E-077440-41-7 Beryllium and compounds 6.16E-05 3.24E-07 0.00E+00 0.00E+00 1.34E-05 7.06E-08 9.58E-06 5.03E-08 0.00E+00 0.00E+00 8.88E-06 4.66E-087440-43-9 Cadmium and compounds 1.49E-02 7.83E-05 0.00E+00 0.00E+00 6.12E-03 3.21E-05 4.32E-03 2.27E-05 0.00E+00 0.00E+00 8.14E-04 4.27E-06

18540-29-9Chromium VI, chromate, and dichromate particulate

4.00E-042.10E-06

0.00E+000.00E+00

3.07E-051.61E-07

4.28E-052.25E-07

0.00E+000.00E+00

1.04E-035.44E-06

7439-92-1 Lead and compounds 1.10E+00 5.75E-03 0.00E+00 0.00E+00 7.41E-02 3.89E-04 4.66E-01 2.44E-03 0.00E+00 0.00E+00 0.00E+00 0.00E+007439-96-5 Manganese and compounds 9.02E-03 4.73E-05 0.00E+00 0.00E+00 1.77E-03 9.27E-06 1.16E-03 6.06E-06 0.00E+00 0.00E+00 2.81E-04 1.48E-067439-97-6 Mercury and compounds 2.06E-03 1.08E-05 0.00E+00 0.00E+00 8.08E-04 4.24E-06 8.12E-04 4.26E-06 0.00E+00 0.00E+00 1.92E-04 1.01E-067440-02-0 Nickel and compounds 1.82E-03 9.54E-06 0.00E+00 0.00E+00 3.01E-03 1.58E-05 1.87E-03 9.82E-06 0.00E+00 0.00E+00 1.55E-03 8.16E-067782-49-2 Selenium and compounds 9.88E-02 5.19E-04 2.16E-05 1.13E-07 4.14E-02 2.17E-04 2.49E-02 1.31E-04 1.71E-05 8.98E-08 1.78E-05 9.32E-087440-36-0 Antimony and compounds 2.06E-02 1.08E-04 0.00E+00 0.00E+00 3.37E-03 1.77E-05 1.44E-03 7.57E-06 0.00E+00 0.00E+00 0.00E+00 0.00E+007440-48-4 Cobalt and compounds 1.66E-04 8.72E-07 0.00E+00 0.00E+00 5.36E-05 2.81E-07 9.49E-05 4.98E-07 0.00E+00 0.00E+00 6.21E-05 3.26E-077440-50-8 Copper and compounds 2.09E-02 1.10E-04 0.00E+00 0.00E+00 6.59E-03 3.46E-05 7.85E-03 4.12E-05 0.00E+00 0.00E+00 6.29E-04 3.30E-0650-00-0 Formaldehyde 6.23E-02 3.27E-04 0.00E+00 0.00E+00 5.01E-03 2.63E-05 2.33E-02 1.22E-04 0.00E+00 0.00E+00 5.55E-02 2.91E-0475-07-0 Acetaldehyde 0.00E+00 0.00E+00 1.92E-02 1.01E-04 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.52E-02 8.00E-05 1.58E-02 8.31E-05107-02-8 Acrolein 0.00E+00 0.00E+00 1.62E-05 8.49E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.28E-05 6.73E-08 0.00E+00 0.00E+007440-39-3 Barium and compounds 0.00E+00 0.00E+00 3.95E-03 2.08E-05 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.13E-03 1.65E-05 3.25E-03 1.71E-0571-43-2 Benzene 0.00E+00 0.00E+00 1.89E-03 9.91E-06 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.50E-03 7.85E-06 1.55E-03 8.16E-06100-41-4 Ethyl benzene 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00110-54-3 Hexane 0.00E+00 0.00E+00 1.62E+00 8.49E-03 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.28E+00 6.73E-03 1.33E+00 6.99E-031313-27-5 Molybdenum trioxide 0.00E+00 0.00E+00 1.48E-03 7.78E-06 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.18E-03 6.17E-06 1.22E-03 6.41E-0683-32-9 Acenaphthene 0.00E+00 0.00E+00 1.62E-06 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.28E-06 6.73E-09 1.33E-06 6.99E-09208-96-8 Acenaphthylene 0.00E+00 0.00E+00 1.62E-06 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.28E-06 6.73E-09 1.33E-06 6.99E-09120-12-7 Anthracene 0.00E+00 0.00E+00 2.16E-06 1.13E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.71E-06 8.98E-09 1.78E-06 9.32E-0956-55-3 Benz[a]anthracene 0.00E+00 0.00E+00 1.62E-06 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.28E-06 6.73E-09 1.33E-06 6.99E-0950-32-8 Benzo[a]pyrene 0.00E+00 0.00E+00 1.08E-06 5.66E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 8.55E-07 4.49E-09 8.88E-07 4.66E-09205-99-2 Benzo[b]fluoranthene 0.00E+00 0.00E+00 1.62E-06 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.28E-06 6.73E-09 1.33E-06 6.99E-09191-24-2 Benzo[g,h,i]perylene 0.00E+00 0.00E+00 1.08E-06 5.66E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 8.55E-07 4.49E-09 8.88E-07 4.66E-09207-08-9 Benzo[k]fluoranthene 0.00E+00 0.00E+00 1.62E-06 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.28E-06 6.73E-09 1.33E-06 6.99E-09218-01-9 Chrysene 0.00E+00 0.00E+00 1.62E-06 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.28E-06 6.73E-09 1.33E-06 6.99E-09226-36-8 Dibenz[a,h]acridine 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00206-44-0 Fluoranthene 0.00E+00 0.00E+00 2.70E-06 1.42E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2.14E-06 1.12E-08 2.22E-06 1.17E-0886-73-7 Fluorene 0.00E+00 0.00E+00 2.52E-06 1.32E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.99E-06 1.05E-08 2.07E-06 1.09E-08193-39-5 Indeno[1,2,3-cd]pyrene 0.00E+00 0.00E+00 1.62E-06 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.28E-06 6.73E-09 1.33E-06 6.99E-0991-57-6 2-Methyl naphthalene 0.00E+00 0.00E+00 2.16E-05 1.13E-07 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.71E-05 8.98E-08 1.78E-05 9.32E-0891-20-3 Naphthalene 0.00E+00 0.00E+00 5.48E-04 2.88E-06 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.35E-04 2.28E-06 4.51E-04 2.37E-0685-01-8 Phenanthrene 0.00E+00 0.00E+00 1.53E-05 8.02E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.21E-05 6.36E-08 1.26E-05 6.60E-08129-00-0 Pyrene 0.00E+00 0.00E+00 4.49E-06 2.36E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.56E-06 1.87E-08 3.70E-06 1.94E-0857-97-6 7,12-Dimethylbenz[a]anthracene 0.00E+00 0.00E+00 1.44E-05 7.55E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.14E-05 5.98E-08 1.18E-05 6.21E-0856-49-5 3-Methylcholanthrene 0.00E+00 0.00E+00 1.62E-06 8.49E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.28E-06 6.73E-09 1.33E-06 6.99E-09108-88-3 Toluene 0.00E+00 0.00E+00 3.06E-03 1.60E-05 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2.42E-03 1.27E-05 2.52E-03 1.32E-057440-62-2 Vanadium (fume or dust) 0.00E+00 0.00E+00 2.07E-03 1.09E-05 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.64E-03 8.60E-06 1.70E-03 8.93E-06


0.00E+000.00E+00

0.00E+000.00E+00

0.00E+000.00E+00

0.00E+000.00E+00

0.00E+000.00E+00

0.00E+000.00E+00

7440-66-6 Zinc and compounds 0.00E+00 0.00E+00 2.61E-02 1.37E-04 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2.07E-02 1.08E-04 2.15E-02 1.13E-047664-41-7 Ammonia 0.00E+00 0.00E+00 2.88E+00 1.51E-02 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2.28E+00 1.20E-02 2.37E+00 1.24E-027647-01-0 Hydrochloric acid 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+007631-86-9 Silica, crystalline (respirable) 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+0071-36-3 n-butyl alcohol 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+001310-73-2 Sodium hydroxide 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+0078-93-3 2-Butanone (Methyl ethyl ketone) 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+0067-63-0 Isopropyl alcohol 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00108-10-1 Methyl isobutyl ketone (MIBK, Hexone) 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00Notes:

Appendix EDaily Emission RatesOwens‐Brockway Glass Container Inc. ‐ Portland

CAS TAC

FURNACE A (NORTH & SOUTH STACKS) FURNACE DFUGITIVE EMISSIONS‐MISC NG

EU4 GM1 EU4 GM1 Nat gas EU4 GM4 green glass EU4 GM4 amber glass EU4 GM4 Nat gas EU6

S2, S3 S4 S6

ERM-West, Inc.Appendix E - Daily Emissions Rates_011521.xlsx Page 1 of 3 1/15/21

MODEL ID ‐‐‐7440-38-2 Arsenic and compounds7440-41-7 Beryllium and compounds7440-43-9 Cadmium and compounds


7439-92-1 Lead and compounds7439-96-5 Manganese and compounds7439-97-6 Mercury and compounds7440-02-0 Nickel and compounds7782-49-2 Selenium and compounds7440-36-0 Antimony and compounds7440-48-4 Cobalt and compounds7440-50-8 Copper and compounds50-00-0 Formaldehyde75-07-0 Acetaldehyde107-02-8 Acrolein7440-39-3 Barium and compounds71-43-2 Benzene100-41-4 Ethyl benzene110-54-3 Hexane1313-27-5 Molybdenum trioxide83-32-9 Acenaphthene208-96-8 Acenaphthylene120-12-7 Anthracene56-55-3 Benz[a]anthracene50-32-8 Benzo[a]pyrene205-99-2 Benzo[b]fluoranthene191-24-2 Benzo[g,h,i]perylene207-08-9 Benzo[k]fluoranthene218-01-9 Chrysene226-36-8 Dibenz[a,h]acridine206-44-0 Fluoranthene86-73-7 Fluorene193-39-5 Indeno[1,2,3-cd]pyrene91-57-6 2-Methyl naphthalene91-20-3 Naphthalene85-01-8 Phenanthrene129-00-0 Pyrene57-97-6 7,12-Dimethylbenz[a]anthracene56-49-5 3-Methylcholanthrene108-88-3 Toluene7440-62-2 Vanadium (fume or dust)


7440-66-6 Zinc and compounds7664-41-7 Ammonia7647-01-0 Hydrochloric acid7631-86-9 Silica, crystalline (respirable)71-36-3 n-butyl alcohol1310-73-2 Sodium hydroxide78-93-3 2-Butanone (Methyl ethyl ketone)67-63-0 Isopropyl alcohol108-10-1 Methyl isobutyl ketone (MIBK, Hexone)Notes:


CAS TAC (lbs/day) (g/s) (lbs/day) (g/s) (lbs/day) (g/s) (lbs/day) (g/s) (lbs/day) (g/s) (lbs/day) (g/s) (lbs/day) (g/s)‐‐‐ ‐‐‐ ‐‐‐ ‐‐‐ ‐‐‐ ‐‐‐ ‐‐‐ ‐‐‐

5.04E-05 2.65E-07 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+003.02E-06 1.59E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+002.77E-04 1.46E-06 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00

3.53E-041.85E-06

0.00E+000.00E+00

5.39E-072.83E-09

1.22E-056.41E-08

0.00E+000.00E+00

1.62E-088.48E-11 1.28E-05 6.71E-08

0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+009.58E-05 5.03E-07 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.33E-03 1.75E-05 6.62E-08 3.48E-10 2.42E-07 1.27E-09 3.33E-03 1.75E-056.55E-05 3.44E-07 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+005.29E-04 2.78E-06 0.00E+00 0.00E+00 1.39E-03 7.30E-06 6.46E-06 3.39E-08 0.00E+00 0.00E+00 3.23E-07 1.70E-09 1.40E-03 7.34E-066.05E-06 3.18E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+000.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+002.12E-05 1.11E-07 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.23E-06 1.70E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.23E-06 1.70E-082.14E-04 1.12E-06 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.23E-08 1.70E-10 3.23E-08 1.70E-101.89E-02 9.92E-05 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+005.39E-03 2.83E-05 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+004.54E-06 2.38E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+001.11E-03 5.82E-06 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+005.29E-04 2.78E-06 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+000.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+004.54E-01 2.38E-03 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+004.16E-04 2.18E-06 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+004.54E-07 2.38E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+004.54E-07 2.38E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+006.05E-07 3.18E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+004.54E-07 2.38E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+003.02E-07 1.59E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+004.54E-07 2.38E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+003.02E-07 1.59E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+004.54E-07 2.38E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+004.54E-07 2.38E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+000.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+007.56E-07 3.97E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+007.06E-07 3.71E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+004.54E-07 2.38E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+006.05E-06 3.18E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+001.54E-04 8.07E-07 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+004.28E-06 2.25E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+001.26E-06 6.62E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+004.03E-06 2.12E-08 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+004.54E-07 2.38E-09 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+008.57E-04 4.50E-06 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+005.80E-04 3.04E-06 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00

0.00E+000.00E+00

0.00E+000.00E+00

0.00E+000.00E+00

0.00E+000.00E+00

0.00E+000.00E+00

0.00E+000.00E+00 0.00E+00 0.00E+00

7.31E-03 3.84E-05 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+008.07E-01 4.23E-03 4.60E+01 2.41E-01 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+000.00E+00 0.00E+00 2.07E-01 1.09E-03 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+000.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+000.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+000.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+000.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+000.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+000.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00

BOILERHOT END SURFACE TREATMENT

(MBTT and NH3)FUGITIVE EMISSIONS FROM WELDING

WELDING PROCESSES TOTALEU7 EU5 EU‐10 Nickel Spray Welding EU‐10 SMAW welding EU‐10 GMAW welding EU‐10 GTAW welding EU10

S8S7 S5


MODEL ID ‐‐‐7440-38-2 Arsenic and compounds7440-41-7 Beryllium and compounds7440-43-9 Cadmium and compounds


7439-92-1 Lead and compounds7439-96-5 Manganese and compounds7439-97-6 Mercury and compounds7440-02-0 Nickel and compounds7782-49-2 Selenium and compounds7440-36-0 Antimony and compounds7440-48-4 Cobalt and compounds7440-50-8 Copper and compounds50-00-0 Formaldehyde75-07-0 Acetaldehyde107-02-8 Acrolein7440-39-3 Barium and compounds71-43-2 Benzene100-41-4 Ethyl benzene110-54-3 Hexane1313-27-5 Molybdenum trioxide83-32-9 Acenaphthene208-96-8 Acenaphthylene120-12-7 Anthracene56-55-3 Benz[a]anthracene50-32-8 Benzo[a]pyrene205-99-2 Benzo[b]fluoranthene191-24-2 Benzo[g,h,i]perylene207-08-9 Benzo[k]fluoranthene218-01-9 Chrysene226-36-8 Dibenz[a,h]acridine206-44-0 Fluoranthene86-73-7 Fluorene193-39-5 Indeno[1,2,3-cd]pyrene91-57-6 2-Methyl naphthalene91-20-3 Naphthalene85-01-8 Phenanthrene129-00-0 Pyrene57-97-6 7,12-Dimethylbenz[a]anthracene56-49-5 3-Methylcholanthrene108-88-3 Toluene7440-62-2 Vanadium (fume or dust)


7440-66-6 Zinc and compounds7664-41-7 Ammonia7647-01-0 Hydrochloric acid7631-86-9 Silica, crystalline (respirable)71-36-3 n-butyl alcohol1310-73-2 Sodium hydroxide78-93-3 2-Butanone (Methyl ethyl ketone)67-63-0 Isopropyl alcohol108-10-1 Methyl isobutyl ketone (MIBK, Hexone)Notes:


CAS TAC (lbs/day) (g/s) (lbs/day) (g/s) (lbs/day) (g/s) (lbs/day) (g/s)‐‐‐ ‐‐‐

0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 5.26E-01 2.76E-030.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 9.66E-05 5.07E-070.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2.65E-02 1.39E-04

0.00E+000.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.89E-03 9.91E-06

0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.64E+00 8.59E-030.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.90E-02 9.96E-050.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.94E-03 2.07E-050.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.16E-02 6.08E-050.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.65E-01 8.67E-040.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2.54E-02 1.34E-040.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.04E-04 2.12E-060.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.61E-02 1.90E-040.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.65E-01 8.66E-040.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 5.57E-02 2.92E-040.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.35E-05 1.76E-070.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.15E-02 6.01E-050.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 5.47E-03 2.87E-050.00E+00 0.00E+00 6.18E-03 3.25E-05 0.00E+00 0.00E+00 6.18E-03 3.25E-050.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E+00 2.46E-020.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.29E-03 2.25E-050.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-06 2.46E-080.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-06 2.46E-080.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 6.25E-06 3.28E-080.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-06 2.46E-080.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.12E-06 1.64E-080.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-06 2.46E-080.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 3.12E-06 1.64E-080.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-06 2.46E-080.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-06 2.46E-080.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+000.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.81E-06 4.10E-080.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.29E-06 3.83E-080.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-06 2.46E-080.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 6.25E-05 3.28E-070.00E+00 0.00E+00 0.00E+00 0.00E+00 2.56E-03 1.34E-05 4.15E-03 2.17E-050.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.42E-05 2.32E-070.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 1.30E-05 6.83E-080.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.16E-05 2.19E-070.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 4.68E-06 2.46E-080.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 8.85E-03 4.65E-050.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 5.99E-03 3.14E-05

0.00E+000.00E+00 2.94E-02 1.54E-04 0.00E+00 0.00E+00 2.94E-02 1.54E-04

0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.55E-02 3.96E-040.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 5.43E+01 2.85E-010.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2.07E-01 1.09E-032.93E-01 1.54E-03 0.00E+00 0.00E+00 0.00E+00 0.00E+00 2.93E-01 1.54E-030.00E+00 0.00E+00 9.12E-02 4.79E-04 0.00E+00 0.00E+00 9.12E-02 4.79E-040.00E+00 0.00E+00 2.87E-03 1.51E-05 0.00E+00 0.00E+00 2.87E-03 1.51E-050.00E+00 0.00E+00 0.00E+00 0.00E+00 1.60E+00 8.41E-03 1.60E+00 8.41E-030.00E+00 0.00E+00 0.00E+00 0.00E+00 2.56E-03 1.34E-05 2.56E-03 1.34E-050.00E+00 0.00E+00 0.00E+00 0.00E+00 1.52E-02 7.96E-05 1.52E-02 7.96E-05

RAW MATERIAL HANDLING (SAND AND LIMESTONE) AND BATCH

FUGITIVE EMISSIONS FROM SOLID FILM LUBRICATION

FUGITIVE EMISSIONS FROM IMAGE PRINTING TOTAL FACILITY DAILY EMISSIONS

ESTIMATEEU1 SFL Image

S1 S9 S10


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Air Dispersion Modeling Protocol · 2021. 2. 16. · AIR DISPERSION MODELING PROTOCOL Owens-Brockway Glass Container, Inc. (O-B) INTRODUCTION 1. INTRODUCTION 1.1 Purpose of Protocol