2009 Greenhouse Gas Savings Study Report - Alberta Used Oil ...

2009 GREENHOUSE GAS (GHG) SAVINGS STUDY 

REPORT 

Prepared For: 

British Columbia Used Oil Management Association (BCUOMA) 

9 – 45905 Yale Road, Suite #125 

Chilliwack, British Columbia, V2P 8E6 

AUGUST 2010 

REF. NO. 071620(2) 

Prepared by: 

Conestoga-Rovers 

& Associates 

110-3851 Shell Road 

Richmond, British Columbia 

Canada V6X 2W2 

Office: (604) 214-0510 

Fax: (604) 214-0525 

web: http:\\www.CRAworld.com 

Worldwide Engineering, Environmental, Construction, and IT Services

TABLE OF CONTENTS 

1.0 INTRODUCTION ...................................................................................................................1 

1.1 BACKGROUND AND SCOPE OF STUDY .....................................................1 

1.1.1 IDENTIFICATION OF PROJECT SCENARIO................................................1 

1.1.2 IDENTIFICATION OF BASELINE SCENARIO .............................................2 

1.2 ORGANIZATION OF THE REPORT...............................................................3 

2.0 INPUT DATA ..........................................................................................................................4 

2.1 DATA COLLECTION.........................................................................................4 

2.2 EMISSION FACTORS.........................................................................................5 

3.0 METHODOLOGY.................................................................................................................10 

3.1 MATERIALS COLLECTION ...........................................................................10 

3.2 TRANSPORTATION DISTANCES.................................................................12 

3.2.1 BASELINE SCENARIO ....................................................................................12 

3.2.2 PROJECT SCENARIO.......................................................................................12 

3.2.3 DETERMINATION OF TOTAL DISTANCES ..............................................15 

3.3 TRANSPORTATION GHG EMISSIONS .......................................................16 

3.4 BASELINE EMISSIONS (EXCLUDING TRANSPORTATION) .................16 

3.4.1 OIL PRODUCTS EMISSIONS..........................................................................17 

3.4.2 OIL FILTER EMISSIONS..................................................................................17 

3.4.3 OIL CONTAINER EMISSIONS.......................................................................18 

3.5 PROJECT EMISSIONS (EXCLUDING TRANSPORTATION)....................18 

4.0 RESULTS OF THE STUDY ..................................................................................................20 

5.0 REFERENCES........................................................................................................................21 

071620 (2) CONESTOGA-ROVERS & ASSOCIATES 

Page

LIST OF FIGURES 

(Following Text) 

FIGURE 3.1 BCUOMA COLLECTION ZONE MAP 

FIGURE 3.2 BRITISH COLUMBIA REGIONAL DISTRICTS MAP 

LIST OF TABLES 

(Following Text) 

TABLE 1.1 PROJECT AND BASELINE ELEMENTS 

TABLE 2.1 MATERIAL QUANTITIES COLLECTED IN 2009 

TABLE 2.2 EMISSION FACTORS (GLOBAL WARMING POTENTIAL) 

TABLE 3.1 USED OIL, FILTER, AND CONTAINER COLLECTION AND RECYCLING 

BY CENSUS DIVISION 

TABLE 3.2 TRANSPORTATION COMPONENTS OF USED OIL, FILTERS AND 

CONTAINERS 

TABLE 3.3 PROJECT – DESTINATION DISTANCES 

TABLE 4.1 RESULTS OF THE GHG SAVINGS STUDY 

LIST OF APPENDICES 

APPENDIX A RAW PROCESSING FACILITY COLLECTION DATA 

APPENDIX B DATA CALCULATIONS 

APPENDIX C RAW EMISSION FACTOR DATA (GLOBAL WARMING POTENTIAL) 

LIST OF ATTACHMENTS 

ATTACHMENT 1 MICROSOFT EXCEL WORKBOOK MODEL 

071620 (2) CONESTOGA-ROVERS & ASSOCIATES

LIST OF CONVERSIONS, SYMBOLS AND ACRONYMS 

0.0283 conversion factor from cubic foot to cubic metre 

3.785 conversion factor from gallon to litre 

BC British Columbia 

BCUOMA British Columbia Used Oil Management Association 

BTU British thermal unit 

CO2 carbon dioxide 

Collector Registered Collector 

CRA Conestoga-Rovers & Associates 

ft3 cubic foot 

Generator used oil materials generator 

GHG greenhouse gases 

GRVD Greater Vancouver Regional District 

HDPE high-density polyethylene 

kg kilogram 

km kilometre 

L litre 

m3 cubic metre 

Processor Registered Processing Facility 

RD Regional District 

Report 2009 Greenhouse Gas Savings Study Final Report 

Return Facility Registered Return Collection Facility 

Study 2009 Greenhouse Gas Savings Study 

yd3 cubic yard 

071620 (2) CONESTOGA-ROVERS & ASSOCIATES

1.0 INTRODUCTION 

This 2009 Greenhouse Gas Savings Study (Study) Final Report (Report) has been 

prepared by Conestoga-Rovers & Associates (CRA) on behalf of the British Columbia 

Used Oil Management Association (BCUOMA), to determine the reduction in GHG 

emissions that occurred as a result of BCUOMA's collection and recycling programs in 

2009. 

1.1 BACKGROUND AND SCOPE OF STUDY 

The BCUOMA is a not-for-profit Society composed of 193 producer members in the 

province of British Columbia (BC), and is responsible for the operation of a 

province-wide collection and recycling program for used lubricating oil, oil filters and 

used oil containers sold through the producer members' retail and wholesale facilities, 

as mandated by the province. 

This Study involved the analysis of the 2009 GHG emissions savings from the operation 

of BCUOMA's robust collection and recycling program. Total 2009 GHG savings 

realized were identified for the following three functional units: 

1. Per litre of oil that is collected and re-refined or used as a fuel 

2. Per filter that is collected and recycled in a steel mill 

3. Per kilogram (kg) of oil container that is collected and processed for sale as 

high-density polyethylene (HDPE) pellets 

These savings were determined by calculating the difference between the GHG 

emissions created by the BCUOMA's program, called the Project scenario, and the 

emissions that would be created in the absence of the BCUOMA program, called the 

Baseline scenario. The Project and Baseline scenarios were divided into various 

Elements, which represent specific and unique processes that generate emissions, such 

as transportation and materials processing. 

1.1.1 IDENTIFICATION OF PROJECT SCENARIO 

The BCUOMA recycling program consists of a network of over 4,000 used oil material 

generators (Generators), of which about 500 of them are Return Collection Facilities 

(Return Facilities) for the do-it-yourselfers. The Generators consist mainly of auto 

service and repair centers and industrial operations throughout British Columbia (BC). 

071620 (2) 1 CONESTOGA-ROVERS & ASSOCIATES

BCUOMA Registered Collectors (Collectors) regularly pick up the used oil materials 

from the Generators and deliver them to BCUOMA Registered Processing Facilities 

(Processors) in BC, Alberta (AB), and Washington State (WA). 

Almost half of the used oil is shipped directly from Collectors to pulp mills in WA and 

asphalt plants in BC and AB. The component of used oil recycled for re-refining 

purposes yields new consumer lubricating oil products that are shipped to retailers 

across the province. For oil filters, processing yields crushed paper and metal, and 

reclaimed oil. A small fraction of the crushed paper filters is sent to the Burnaby 

waste-to-energy facility for incineration. The remainder of the paper filters and all metal 

filters are sent to metal brokers and subsequently steel mills in BC and AB for processing 

into new steel products (paper is burned as part of the steel making operation). For oil 

containers, processing yields HDPE pellets and reclaimed oil. The HDPE pellets are sent 

to manufacturers of plastics to be turned into various products. 

It is noted that oil is recovered from the collected oil filters and containers, and this 

volume of oil recovered has been included in the total oil collected. It is not known how 

much of the total oil collected was recovered from the filters and containers, and 

therefore, the GHG savings from recovering this oil have been allocated to the recycled 

oil component of this Study. It is also noted that this oil would have been landfilled and 

therefore the calculations for the production of oil from raw materials for the recycled oil 

Baseline may be slightly skewed high. 

The individual Project Elements for each of the three materials are presented in 

Table 1.1. 

1.1.2 IDENTIFICATION OF BASELINE SCENARIO 

Previously oil was combusted at the Generators, sprayed on roads as a dust 

suppressant, or disposed of to the environment. As spraying oil on the roads is no 

longer exercised and the majority of used oil is collected and not disposed of to the 

environment, the Baseline scenario of combusting at the Generators is applicable. As the 

oil is re-refined or used as a fuel in the Project scenario, the Baseline for the oil analysis 

would also include the production of heating oil from raw materials. 

For the oil filters and containers Baseline scenario, these materials were transported to 

landfill for final disposal or disposed of to the environment without the operation of the 

BCUOMA program. For this Study, it was assumed that all materials were landfilled. 

Transportation thus consists of common municipal refuse trucks transporting the filters 


and containers from the Generators to the closest municipal/district landfills. As the oil 

filters and containers are recycled and reused (or incinerated, in the case of some of the 

paper filters) in the Project scenario, the Baseline also includes the production of steel 

and HDPE from raw materials, and the decomposition of the paper filters in a municipal 

landfill. 

The individual Baseline Elements for each of the three materials are presented in 

Table 1.1. 

1.2 ORGANIZATION OF THE REPORT 

This Report has been organized into the following sections: 

• Section 1.0 Introduction: presents an introduction and background to the Study 

• Section 2.0 Input Data: presents the input data for the Study provided by BCUOMA, 

Processors, and additional resources 

• Section 3.0 Methodology: discusses in detail the methodology utilized in calculating 

the GHG savings 

• Section 4.0 Results of the Study: presents the results of the Study 

• Section 5.0 References: provides a list of references utilized to complete the Study 


2.0 INPUT DATA 

2.1 DATA COLLECTION 

CRA was provided with the amount of materials collected (used oil in litres [L], oil 

filters in kg, and oil containers in kg) in each Zone (as specified by BCUOMA) for the 

2009 year. This data is presented in Table 2.1, along with total 2009 sales of materials 

and additional recovery and rejection estimates for the three materials. All the original 

data provided by BCUOMA is highlighted blue. These values in the Microsoft Excel 

model file (Attachment 1) can be updated annually to analyze the GHG savings for 

subsequent years. As the antifreeze containers will become part of the BCUOMA 

program in 2011, a blank row was provided within this table, to be filled in when 

appropriate. 

2006 Census population data for each of BC's census subdivisions was used to represent 

the geographic distribution of materials collection to aid in the estimation of 

transportation distances. This data was obtained from a Microsoft Excel data 

spreadsheet provided on the BC Stats website (Statistics Canada, 2006). 

The locations of Return Facilities, Collectors, and Processors are provided on the 

BCUOMA website. Additionally, the materials that each Return Facility accepts, each 

Collector collects and each Processor processes are indicated. The locations of pulp 

mills, asphalt plants, steel mills, and plastics manufacturers (end users) were found 

through industry association websites and associated research. Where possible, larger 

facilities and facilities in or near BC were selected. 

All transportation distances were estimated using Google Maps or Google Earth 

software (Google, 2010). 

M&R Environmental provided 2009 collection data for used oil, filters, and containers, 

and Merlin Plastics Supply provided 2009 collection data for containers. The raw data is 

presented in Appendix A. 

Safety-Kleen Systems, Inc. (Safety-Kleen) also provided 2009 collection data for total 

used oil and used oil from BC. 

Data specific to the Project was utilized to form the data required for the Baseline for 

comparison purposes. 


Appendix B contains all the relevant calculations performed to obtain proper values to 

multiply with the emission factors to obtain GHG emissions for each Element. 

2.2 EMISSION FACTORS 

Appendix C contains all the raw emission factor data utilized in this analysis. Table 2.2 

presents a summary of the emission factors utilized for each Project and Baseline 

Element. BC-specific emission factors were used where available, if not, Canadian- or 

North American-specific emission factors were used. In the event where emission 

factors were not available for North America, emission factors were taken from other 

locations around the world in order to evaluate each Element within this Study. 

Transportation 

The emission factors for the diesel consumption of trucks for the transportation of 

materials from all Generators to Collectors, Processors, and end users (i.e., asphalt plant, 

pulp mill, steel mill) were taken from the Energy Mobile Combustion Sources – Road 

Transport section of the Environment Canada document, National Inventory Report, 

Greenhouse Gas Source and Sinks in Canada, 1990-2008 (Environment Canada, 2009). 

Heavy-duty vehicle with moderate control, weighing more than 3,900 kg for both the 

truck and the load was assumed. 

For the transportation of used oil to a re-refinery by rail, emission factors for a diesel 

train were used from the above-noted Environment Canada document. 

Recycled Oil 

Safety-Kleen provided the results of a life cycle analysis report to CRA to be utilized in 

this Study. The report entitled, "Safety-Kleen Product Carbon Footprint for Re-refined 

Base Oil", prepared by ENVIRON International Corporation in October 2009, includes 

relevant emissions data for the oil re-refinery process used by Safety-Kleen. The 

following components of oil re-refining and associated calculated emission factors were 

utilized in this Study: 

• Re-refinery input materials 

• Re-refinery diesel 

• Re-refinery electricity 

• Re-refinery natural gas 


• Re-refinery fuel (co-products consumed on-site) 

• Waste (including energy recovery) 

• Co-products recovery (offsetting production from raw materials) 

The process of oil re-refining consumes about 14 percent of the used oil re-refined. This 

percentage has been accounted for within the Baseline scenario by reducing the amount 

of oil to be produced from raw materials by 14 percent. 

The production of oil for the Baseline scenario included emission factors for the 

extraction of crude oil, transportation of crude oil to the refinery, and the refining of 

crude oil into oil products. 

The emission factors for the production of crude oil were taken from Pembina Institute's 

emission factor database (Pembina, ND) for the production of light and medium, and 

heavy crude oil. These emission factors include the emissions associated with initial oil 

well development, which includes exploratory drilling, development drilling and 

production. These emission factors are Canadian-specific. As the actual breakdown of 

light, medium and heavy oils was not available, it was assumed that the ratio between 

the three different types is equal. A weighted emission factor was calculated to account 

for this divide. 

The emission factors for the transportation of crude oil were taken from Pembina 

Institute's emission factor database (Pembina, ND) for crude oil transmission. These 

emission factors assume the piping of crude oil using diesel generators, using US data 

from 1991. These emission factors are based on volume of crude oil and transmission 

distance. A distance of 1,000 km was assumed to account for the distance from the oil 

sands in Athabasca, AB to the Chevron Corporation Refinery in Burnaby, BC. 

The Ecoinvent Life Cycle Inventory Database (Ecoinvent, 2009) was used to obtain 

emission factors for the refinery of crude oil. These emission factors include all 

processes on the refinery site from a survey of European refineries, excluding the 

emissions from combustion facilities, including waste water treatment, process 

emissions and direct discharges to rivers. 

The emission factors for the combustion of oil for heat at the Generators in the Baseline 

scenario were taken from the Environment Canada, 2009 document for heavy oil 

combustion in an industrial setting. The same emission factors were used for the 

combustion of used oil in asphalt plants and pulp mills in the Project scenario. 


Recycled Oil Filters (Metal) 

M&R Environmental provided annual energy usage data for their facility in 2007 and 

2008 which included: office and plant electricity requirements; natural gas for heating 

and distillation (85 percent used for antifreeze distillation which is outside the scope of 

this Study); diesel, biodiesel, and gasoline requirements for the transportation 

(collection) component; and, propane to operate fork lifts within the plant. An average 

between the two years was taken, as 2009 data was not available and the actual 

quantities of materials processed in 2007 and 2008 were not known. Annual quantities 

of each type of energy were calculated for the Project scenario based on the weight of 

materials recycled at M&R Environmental. M&R Environmental processes recycled oil 

filters (both metal and paper) and containers, and minimal effort is done on-site to 

handle and transport collected oil to the Processors. Based on discussions with M&R 

Environmental, the energy requirements for oil handling on-site is minimal, and 

therefore was assumed negligible. The actual energy breakdown for metal filters, paper 

filters, and containers is unknown and therefore assumptions were made as follows. 

M&R Environmental's diesel, biodiesel, and gasoline usages were not used as the 

transportation component of this Study was completed as a whole for the entire 

BCUOMA program. The 15 percent of natural gas remaining after distillation 

requirements was removed, was divided between metal filters, paper filters, and 

containers based on weight recycled at M&R Environmental. The same divide was 

made with the propane used in the fork lifts. 

Electricity requirements for metal filter, paper filter, and container processing was 

calculated based on equipment similar to what is actually used. The energy 

requirements for a commercial filter crusher were used, and the electricity requirements 

to crush the metal and paper filters processed at M&R Environmental were calculated. 

It was assumed that 20 percent of the total electricity was used in the office. Therefore, 

the total electricity minus the electricity calculated to crush the metal and paper filters 

and to operate the office was assumed to be the electricity required to process the 

containers. The electricity used in the office was divided between the metal filters, 

paper filters, and containers based on weight processed. 

The emission factor for electricity generation in BC was taken from the Environment 

Canada document, National Inventory Report, Greenhouse Gas Source and Sinks in 

Canada, 1990-2008 (Environment Canada, 2009), Table A13-11. 

The emission factors for natural gas production, processing, and distributing were taken 

from the Canadian Association of Petroleum Producers 2005 report, A National 


Inventory of Greenhouse Gas, Criteria Air Contaminant (CAC) and Hydrogen Sulphide 

(H2S) Emissions by the Upstream Oil and Gas Industry, Volume 1, Overview of the 

GHG Emissions Inventory (Canadian Association of Petroleum Producers, 2005). The 

emission factors for natural gas combustion for heat were taken from the Environmental 

Protection Agency 1998 document, AP42, Fifth Edition, Volume 1, Chapter 1: External 

Combustion Sources, 1.4 Natural Gas Combustion (US EPA, 1998). 

The emission factor for the production of liquid propane gas was taken from the 

Government of Canada, Technology Early Action Measures, Emission Factor Database. 

The emission factors for the combustion of propane as a fuel were taken from 

Environment Canada, 2009, Table A8-11. 

Please refer to Appendix B for a further description of the assumptions made for the 

energy requirements and emission factors used for filter and container processing. 

The emission factors for the production of steel for the Baseline scenario were taken 

from the Pembina Institute's emission factor database (Pembina, ND) for steel 

production. These emission factors represent an average of values taken from sources 

from Canada, Alberta, US, and Switzerland. The boundaries differ for each source 

however the average is considered indicative of the entire life cycle production of steel 

from the raw materials extraction (i.e., iron ore mining activities) to hot stripping and 

cold rolling steel production. The transportation of steel to the steel mill is also included 

in these emission factors. 

Recycled Oil Filters (Paper) 

Refer to the discussion above for the emission factors for recycled metal oil filters for 

information pertaining to the processing of paper oil filters at the Processor for the 

Project scenario. 

The Ecoinvent Life Cycle Inventory Database (Ecoinvent, 2009) was used to obtain 

emission factors for the disposal of paper to a municipal incinerator for the Project. 

These emission factors include waste-specific air emissions from incineration, auxiliary 

material consumption for flue gas cleaning, utilizing technology specific to Switzerland 

in 2000 which is applicable to modern incineration practices in Europe, North America 

and Japan. 

The emissions associated with the decomposition of the paper filters for the Baseline 

scenario were calculated using the Scholl Canyon landfill gas model, assuming 

100 percent paper. The model parameters for the methane generation potential (based 


on material) and methane generation rate (based on precipitation) were taken from the 

Landfill Gas Generation Assessment Procedure Guidance Report, prepared by CRA, 

dated March 2009, for the British Columbia Ministry of Environment. Paper is assumed 

to be moderately decomposable material. 

Recycled Oil Containers 

Refer to the discussion above for the emission factors for recycled metal oil filters for 

information pertaining to the processing of oil containers at the Processor for the Project 

scenario. 

The emission factors for the production of HDPE for the Baseline scenario were taken 

from the Pembina Institute's emission factor database (Pembina, ND) for plastic (HDPE) 

production. These emission factors represent European data from 1993, which has been 

considered fairly current and applicable to North America by the Pembina Institute. 

These emission factors include the emissions associated with the extraction of all raw 

materials up to the final polymerization. The transportation of HDPE to the plastics 

manufacturer is also included in these emission factors. 


3.0 METHODOLOGY 

This Section presents the methodology developed and utilized for this GHG savings 

study. Select equations used during the Study are presented and referenced in this 

section, along with the parameters associated with the equations. Where necessary, 

reasonable assumptions were made and discussed. 

3.1 MATERIALS COLLECTION 

In order to accurately represent the transportation distances traveled by collected 

materials across the province, the collection data was divided by Census Subdivision 

(Subdivision). A Subdivision is generally an incorporated municipality, an electoral 

area, or a grouping of Indian Reserves. In BC, each Subdivision is tied to a Regional 

District (RD), of which there are 28 in the province. Indian Reserve populations were 

excluded, as they are totaled for each RD and thus cannot be linked to specific 

Subdivisions. For the Study, each Subdivision was tied to a specific BCUOMA 

Collection Zone (Zone), based on their locations and mapping provided by BC Stats. 

There are 11 Zones in the province, and Figure 3.1 shows their coverage areas. 

Figure 3.2 shows the coverage of the 28 regional districts. With 2001 and 2006 

populations provided in the data for each Subdivision, an annual population growth 

rate (r) was calculated using the following formula (Equation 1): 

Equation 1: Annual Growth Rate 

( ) n 

r 

P = P ⋅ 1+ 

2006 

2001 

Where, P2006 = 2006 population 

P2001 = 2001 population 

r = annual growth rate 

n = number of years (5) 


With the calculated annual growth rate (r), the 2009 population (P2009) was estimated for 

each Subdivision using the above formula. The amount of materials collected from each 

census Subdivision was then calculated using the following equation (Equation 2): 

Equation 2: Material Amount Collected From a Subdivision 

P 

A = A ⋅ 

SUB 

ZONE 

SUBDIVISION 

071620 (2) 11 CONESTOGA-ROVERS & ASSOCIATES 

P 

ZONE 

Where, ASUB = amount of material collected from the Subdivision (L, #, kg) 

AZONE = amount of material collected from the Zone (L, #, kg) 

PSUBDIVISION = population of the Subdivision 

= population of the Zone 

PZONE 

This calculation was repeated for each Subdivision, resulting in a data table presenting 

the amount of materials collected in each geographic division of the province, as 

presented in Table 3.1. 

The starting point for transportation of materials in the Project and Baseline scenarios 

was assumed to be the Generator. Due to the fact that many of the Generators are auto 

service centers and industrial operations, it is reasonable to assume that even in the 

absence of the BCUOMA program, many materials would accumulate there from the 

servicing of vehicles and other equipment. Thus, under this assumption, all used oil 

materials, including those from do-it-yourselfers and other generators, end up at one of 

these locations for both the Project and Baseline, where they proceed to recycling 

(Project) or end use/disposal (Baseline). 

Considering that there are approximately 5,000 Generators in BC, it was assumed that 

each municipality has at least one Generator within its boundary. Thus, for each 

municipal Subdivision, the starting point for materials is the municipality itself. For 

each regional or electoral district (i.e., Cariboo A) Subdivision, the starting point for 

materials is the closest municipality. As many Generators and Collectors can exist 

within a municipality, transportation distances were calculated based on travel to the 

geographic center of each municipality (as defaulted by Google software). 

3.2 TRANSPORTATION DISTANCES 

This subsection presents the methodology and assumptions employed in calculating the 

transportation distances for moving all materials under the Baseline and Project

scenarios. For more information, please refer to the Microsoft Excel model file 

(Attachment 1). 

3.2.1 BASELINE SCENARIO 

Under the Baseline scenario, used oil is combusted at the Generators, while the oil filters 

and containers are transported to landfill for final disposal. Transportation thus consists 

only of common municipal refuse trucks bringing the filters and containers from the 

Generators to the closest municipal/district landfills. 

For an individual refuse truck, a capacity of 23 cubic metres (m3) (30 cubic yards [yd3]) was assumed. Generally, these trucks have capacities ranging from 20 yd3 (rear-loader) 

to 40 yd3 (front loader), making 30 yd3 a reasonable middle value (Mid-Iowa, 2008). The 

hydraulic compaction ability of refuse trucks was considered negligible. The truck's 

capacity for oil filters was calculated assuming a typical size of filter retrieved from 

FRAM, a major oil filter manufacturer. The truck's capacity for oil containers was 

calculated by assuming the amounts and densities of air and HDPE occupying the space. 

The 1-5 L containers are not compacted, and thus contain a significant portion of air 

(70 percent assumed). The 20 L containers are stacked, reducing the amount of air space 

(5 percent assumed). It was assumed that a truck's volume is equally split between 20 L 

and 1-5 L containers. A fuel consumption value of 0.84 L/kilometre (km) was used 

(Siuru, 2003, p. 1). 

The transportation distances of the new virgin materials (oil, steel, plastic) being 

produced are accounted for in the Emission Factors chosen for the associated processes, 

as they are based on life cycle analyses, as discussed in Section 2.2. Transportation 

distances for moving new lubricating oil from refinery to retailer (Baseline) were 

considered to be similar to distances for moving re-refined lubricating oil from 

re-refinery to retailer (Project) and were thus not accounted for in the calculations. 

3.2.2 PROJECT SCENARIO 

Under the Project scenario, used oil, oil filters, and oil containers are first transported 

from the Generators by the Collectors to the Processors. It was assumed that materials 

from each Generator were transported to the closest Collector accepting the materials. 

Transportation distances from Generators to Collectors that exist within the same 

municipality were calculated as one half of the radius of the geographic area of the 


municipality, as provided in the 2006 census data. This provides a consistent estimation 

method that accounts for the varying sizes of municipalities. 

Transportation of the used oil was assumed to occur in small tank trucks with 

2,700 gallon capacities (Seneca Tank, 2010). Transportation of the filters and containers 

was assumed to occur in small box trucks with 44 m3 (1550 cubic feet [ft3]) capacities 

(ShipNorthAmerica Transportation, 2007). For both small tank and box trucks, a fuel 

consumption value of 0.302 L/km was used (Kodjak, 2004). For routes traversing 

waterways serviced by BC Ferries, it was assumed that the representative fuel 

consumption of the ferries is equivalent to that of the trucks. 

From the Collectors, the used oil, oil filters, and oil containers are transported to various 

Processors as is the case for used oil, pulp mills and asphalt plants as well. Table 3.2 

presents the percentages and amounts of materials traveling to each Processor and end 

use facility specific to each Zone, based on data provided by BCUOMA and Processors 

and assuming that all materials collected under the program end up at one of the 

facilities indicated. M&R Environmental provided 2009 collection data for used oil, 

filters, and containers, and Merlin Plastics Supply provided 2009 collection data for 

containers. The raw data is presented in Appendix C. M&R Environmental is a 

Processor of filters and containers, and thus the collection data for these two materials 

was utilized. However, M&R Environmental is not the final destination (end user) for 

used oil, and only the re-refineries, pulp mills, and asphalt plants (end users) for used oil 

are listed in Table 3.2. Thus, M&R Environmental's used oil collection data was not 

utilized, as doing so would require the addition of another set of percentages for 

amounts of materials traveling to each Collector (prior to an end use facility), which 

would provide little extra accuracy and a significant amount of additional data 

collection. Merlin Plastics provided data for four months only, thus an average was 

taken to gain data for the entire 2009 year. 

Where no indication was provided as to the relative quantities of materials accepted by 

facilities, it was assumed that all facilities of the same type accept equal amounts of 

materials. The specific Processors handling each material were provided by BCUOMA. 

The pulp mills, asphalt plants, steel mills, and plastics manufacturers were chosen based 

on indications provided by BCUOMA as well as reasonable assumptions based on 

facility size and proximity to the province. At least two facilities of each type were 

chosen to achieve representative values for transportation distances and process 

emissions. 


It should be noted that significant data gaps exist in the amounts (percentages) of 

materials going to each facility. Only collection data from M&R Environmental, Merlin 

Plastics, and Safety-Kleen were received, with the remaining percentages having been 

calculated/assumed, applying the assumptions stated above. With more complete data 

from other Processors, better estimates of where the materials were actually transported 

during the year could be calculated. 

Used Oil 

It was assumed that all used oil going from Collector to Processor was transported in 

large tank trucks with 8,000 gallon capacities (Seneca Tank, 2010). For large tank trucks, 

a fuel consumption value of 0.395 L/km was used (NRCan, 2009). The only exception to 

this concerns the railway transportation for used oil that occurs from Safety-Kleen's 

facility in Delta, BC to their re-refinery in Breslau, ON. The transportation distances 

from Collectors to the Delta facility were separated from the distance of rail transport 

from the Delta facility to the Breslau re-refinery, in order to account for the difference in 

fuel consumption between trucks and rail locomotives. For rail transport, a fuel 

consumption value of 0.828 L/km was calculated, based on a value of 

525 gallons/24 hours (Vantuono, 2002, p. 4) and an average speed of 100 km/hour (Via 

Rail, 2010). Due to the variable and large capacity that freight rail can offer, it was 

assumed that all the used oil that went to the Breslau facility in 2009 was accommodated 

in one trip, making the total capacity of the train on this trip equal to 2,450,030 L. With 

tank cars having an average capacity of over 113,563 L (30,000 gallons) (UTLX, 2008), 

this is equivalent to a train with 22 cars. 

Oil Filters 

It was assumed that all oil filters traveling from Collector to Processor and subsequent 

end users were transported in 42 US-gallon oil barrels (barrel height assumed to be 

twice its diameter) in large trailer trucks with 107 m3 (3,800 ft3) capacities 

(ShipNorthAmerica Transportation, 2007). 

For oil filters traveling to Processors, the number of filters that can fit into this volume 

was based on a weight of unprocessed filter per barrel ratio calculated by M&R 

Environmental based on their 2009 collection data. With the ratio between weight and 

number of filters from the BCUOMA 2009 collection data known (Table 2.1), the truck's 

capacity for filters in this arrangement was calculated. Filters are crushed/stripped at 

the Processors, thus allowing increased capacity for filters traveling to the metal brokers 

and steel mills. A percentage reduction in volume of 20 percent was assumed to 

accommodate this fact. 


Approximately 8 percent of the filters collected and recycled are paper. Of the four oil 

filter Processors, however, only M&R Environmental sorts out the paper filters from the 

steel ones. They send the paper filters to the Greater Vancouver Regional District's 

(GVRDs) waste-to-energy facility in Burnaby for incineration. Thus, approximately 

4.6 percent of all filters are incinerated. The other three Processors simply send the 

paper filters along with the steel ones to metal brokers and subsequently, steel mills. 

The total number of filters recycled at a steel mill (for consideration in Project and 

Baseline Elements) does not include the paper filters sent to the steel mills. 

Oil Containers 

It was assumed that all oil containers traveling from Collector to Processor and 

subsequent facility were transported in large trailer trucks with 107 m3 (3,800 ft3) capacities (ShipNorthAmerica Transportation, 2007). 

For oil containers, the container mass that can be fit into a truck's volume capacity was 

estimated by assuming the amounts and densities of air and HDPE occupying the space. 

The 1-5 L containers are not compacted, and thus contain a significant portion of air 

(70 percent assumed). The 20 L containers are stacked, reducing the amount of air space 

(5 percent assumed). It was assumed that a truck's volume is equally split between 20 L 

and 1-5 L containers. Containers are pelletized at the Processor, thus the trucks 

traveling to the plastics manufacturers will be able to hold more HDPE (98 percent 

volume assumed). Additionally, the residual oil present in the intact containers is 

removed at the Processors. Assuming that 10 percent of the weight of the intact 

containers consists of residual oil, then 90 percent of the total weight of containers 

recycled travels to plastics manufacturers. For large trailer trucks, a fuel consumption 

value of 0.395 L/km was used (NRCan, 2009). 

3.2.3 DETERMINATION OF TOTAL DISTANCES 

With the distances from each Collector to Processor, the total distances traveled by 

materials from each Subdivision were calculated. It was assumed that the materials 

collected by each Collector would travel to all applicable Processors, pulp mills, or 

asphalt plants based on the percentages indicated in Table 3.2. Similarly, it was 

assumed that the materials at each Processor would travel to all additional applicable 

facilities based on the percentages indicated in Table 3.2. This permits the calculation of 

a total weighted distance traveled for each transportation element of each material for 


each census Subdivision (see Table 3.3 for more information). This is equal to the sum of 

the weighted distances for all applicable routes, as shown in Equation 3 below: 

Equation 3: Total Weighted Distance 

D wt 

= f ⋅ D + f ⋅ D + f ⋅ D 

1 

1 

2 

071620 (2) 16 CONESTOGA-ROVERS & ASSOCIATES 

2 

3 

3 

+ ... 

Where, DWT = total weighted distance of the transport element (km) 

f1 (f2,,…) = fraction of material in subdivision traveling route 

D1 (D2 ,…) = total distance of route (km) 

3.3 TRANSPORTATION GHG EMISSIONS 

The total volume of diesel fuel consumed for each transportation element of each 

material and each Subdivision for the 2009 year is given by Equation 4 below: 

Equation 4: Transportation Diesel Consumption 

⎛ 

⎜ 

⎝ 

A 

⎞ 

⎟ 

⎠ 

SUB 

VFUEL = 

⎜ 

⋅ DWT 

⋅ 

A ⎟ 

VEHICLE 

C 

FUEL 

Where, VFUEL = total volume of diesel fuel consumed (L) 

ASUB 

AVEHICLE 

= amount of material collected from the Subdivision (L, 

#, kg) 

= capacity of the vehicle (L, #, kg) 

DWT = total weighted distance of transport element (km) 

CFUEL = fuel consumption of the vehicle (L / km) 

This calculation is repeated for each Baseline and Project transportation element for each 

Subdivision. The total GHG emissions released through an individual Baseline or 

Project transportation element is then calculated by multiplying the amount of diesel 

consumed for that Element by the emission factor (EF) for diesel combustion for that 

certain transportation vehicle. 

3.4 BASELINE EMISSIONS (EXCLUDING TRANSPORTATION) 

In addition to transportation, emissions are generated during facility processes, material 

extraction, and disposal. Under the Baseline scenario, GHG emissions will be generated 

during the extraction and processing of raw materials required to produce all virgin oil,

filter, and container products that must replace those recycled under the Project 

scenario. Additionally, emissions will arise out of the end use or final disposal of the 

products, as they are not recycled. 

3.4.1 OIL PRODUCTS EMISSIONS 

Production of virgin oil requires the extraction of crude oil (BE1), transportation of the 

crude oil to refineries (BE2), and the refining of crude oil into lubricating oil products 

(BE3). Using appropriate emission factors for these three elements, the total GHG 

emissions associated with the production of virgin oil products were calculated. To 

correlate the volume of crude oil required to yield the volume of oil product, which is 

equal to the total amount recycled under the Project scenario, a specific lubricating oil to 

crude oil ratio was used. Lubricating oil has a heating value of approximately 8 million 

BTUs/barrel (Harvey, 1977), while crude oil has a heating value of approximately 

5.6 million BTUs/barrel (US DOE, 2008). Lubricating oil's higher heating value reflects 

the additives and processing that are input during its manufacture. Dividing it by the 

heating value of crude oil gives a ratio higher than 1, which suitably reflects the need for 

a higher input, and thus this ratio was used to calculate the volume of crude oil required 

to match the amount of oil recycled to calculate the GHG emissions. 

In the Baseline scenario, the end use of the used oil consists of combustion at the 

Generators for heat energy (BE4), and an appropriate emission factor was used to 

calculate the GHG emissions associated with this Element. 

3.4.2 OIL FILTER EMISSIONS 

Under the Baseline scenario, virgin steel is produced by extracting raw materials, 

transporting the raw materials, and manufacturing steel from the raw materials (Metal 

Oil Filters BE1 and BE2) in order to compensate for the steel filters deposited in landfill 

in the absence of a recycling program. Based on the data provided by BCUOMA, 

approximately 92 percent of the recycled oil filters are steel, which yields the mass of 

virgin steel required. The filters collected contain residual oil, which was assumed to 

amount to 25 percent. Thus, the mass of virgin steel is equal to 75 percent of the total 

mass of the steel containers. Appropriate emission factors were used to calculate GHG 

emissions associated with this Element. 

Final disposal of the filters occurs at municipal landfills. As steel has been considered an 

inert material, only the paper filters degrade in the landfill to produce GHG emissions. 


A landfill gas generation model was performed to determine these emissions, and the 

results of the model are presented in the final results table (Table 4.1). The mass of the 

plastic filters have not been discounted by 20 percent as the total mass of plastic filters is 

only an estimate. 

3.4.3 OIL CONTAINER EMISSIONS 

Under the Baseline scenario, virgin HDPE must be manufactured (BE1) and transported 

to plastics manufacturers (BE2) in order to compensate for the HDPE containers 

deposited in landfill in the absence of a recycling program. The containers collected 

contain residual oil, which was assumed to amount to 10 percent. Thus, the mass of 

virgin HDPE is equal to 90 percent of the total mass of oil containers collected. 

Appropriate emission factors were used to calculate GHG emissions associated with this 

Element. 

Final disposal occurs at municipal landfills, and with the assumption made that plastic 

are an inert material, no emissions are associated with disposal of HDPE containers in 

landfill. 

3.5 PROJECT EMISSIONS (EXCLUDING TRANSPORTATION) 

The GHG emissions from each of the non-transportation Project Elements consist of the 

following: 

• Used oil: re-refining of used oil by Processors and the combustion of used oil at pulp 

mills and asphalt plants (Re-refine and Reuse PE3 and Use as a Fuel PE3) 

• Oil filters: processing of paper and steel oil filters by Processors and incineration of 

paper filters (Metal Filters PE3 and Paper Filters PE3) 

• Oil containers: processing of oil containers by Processors (PE3) 

Facility data was collected from M&R Environmental for oil filters and oil containers, 

and from Safety-Kleen for used oil, which was utilized to calculate the emissions 

associated with the processing of each material. Emission factors for combustion of the 

used oil at the pulp mills and asphalt plants, and of the paper filters at the Burnaby 

waste-to-energy facility were chosen from database resources. See Section 2.2 for more 

information regarding the emission factors selected. 


4.0 RESULTS OF THE STUDY 

Based on the input data and the data analysis resources and methods used during this 

Study, the following presents the results of the 2009 GHG Savings Study. For the 2009 

year, BCUOMA's programs resulted in the following GHG savings (also presented in 

Table 4.1): 


• 2.47 kg CO2 equivalent per liter of used oil that is collected and re-refined or used as 

a fuel 

• 109,931,357 kg CO2 equivalent total GHG savings for 2009 

Recycled Oil Filters 

• 1.09 kg CO2 equivalent per filter that is collected and recycled in a steel mill 



• 2.11 kg CO2 equivalent per kg of oil container that is collected and processed for sale 

as HDPE pellets 


The total GHG savings realized for BCUOMA's program for the year 2009 is estimated 

to be 117,525,027 kg CO2 equivalent, which equates to the following: 

• Powering approximately 549,776 B.C. households for one year 

• Removing approximately 33,761 cars from the road 

Additionally, it should be noted that oil re-refining results in additional GHG savings of 

339 percent when compared to the GHG savings associated with the use of oil in the 

pulp mills and asphalt plants. 

Table 4.1 provides a breakdown of the GHG emissions associated with each Element 

within the Study. Note that the results are subject to the assumptions and limitations 

made throughout this study. 


5.0 REFERENCES 

Canadian Association of Petroleum Producers. 2005. A National Inventory of 

Greenhouse Gas (GHG), Criteria Air Contaminant (CAC) and Hydrogen 

Sulphide (H2S) Emissions by the Upstream Oil and Gas Industry, Volume 1, 

Overview of the GHG Emissions Inventory. 

Retrieved from 

(accessed July 10, 2010). 

Conestoga-Rovers & Associates (March 2009). Landfill Gas Generation Assessment 

Procedure Guidance Report. Prepared for the British Columbia Ministry of 

Environment. 

Dynalab Corporation (2010). High Density Polyethylene Properties Technical 

Information. 


(accessed 

June 21, 2010). 

ENVIRON International Corporation (2009). Safety-Kleen Product Carbon Footprint for 

Re-refined Base Oil. Prepared for Safety-Kleen Systems Inc., October 2009. 

Environment Canada (2010). National Inventory Report, Greenhouse Gas Sources and 

Sinks in Canada, 1990-2008. 

Google (2010). Google Maps web application and Google Earth desktop software. 

Retrieved from (accessed June 1 

– 11, 2010). 

Harvey, D. G. (1977). Testimony, Hearing Before the Subcommittee on Advanced 

Energy Technologies and Energy Conservation Research, Development, and 

Demonstration of the Committee on Science and Technology, U.S. House of 

Representatives, 95th Congress, First Session, December 12, 1977. U.S. 

Government Printing Office, Washington, 1978. Original from the University of 

Michigan. 

Honeywell International Inc. (Honeywell) (2010). FRAM Auto Filters Catalog – Oil 

Filters. 

Retrieved from 

(accessed June 21, 2010). 

Intergovernmental Panel on Climate Change (IPCC) (2007). IPCC Fourth Assessment 

Report (AR4): Climate Change 2007. Retrieved from 

(accessed August 11, 2010). 


Kodjak, D. (2004). "Policy Discussion – Heavy-duty Truck Fuel Economy," in 10th Diesel 

Engine Emissions Reduction Conference (August 29 – September 2, 2004). 



Mid-Iowa Solid Waste Equipment Co. (Mid-Iowa) (2008). Used Equipment List – 

Garbage Trucks. 



Natural Resources Canada (NRCan) (2009). Fuel Efficiency Benchmarking in Canada's 

Trucking Industry. 



Seneca Tank (2010). Tank Truck Info product page. 



ShipNorthAmerica Transportation Inc. (2007). Equipment – Truck, Truck Trailer & Van 

Specifications. 



Siuru, B. (2003). "New study makes strong case for natural gas garbage trucks – 

alternative fuels," in Diesel Progress North American Edition (November 2003). 


 


Statistics Canada (2006). 2006 Census of Canada. Prepared by BC Stats, Ministry of 

Labour and Citizens' Services, Victoria, British Columbia. 

Statistics Canada (2007). Electric Power Generation, Transmission, and Distribution, 

2003-2007 (catalogue no. 57-202-X). 


 

(accessed August 9, 2010). 

Swiss Centre for Life Cycle Inventories. Ecoinvent Centre. Emission Factor Database. 

Available at (Subscription required). 


The Engineering Toolbox (2010). Density and Specific Weight of Air. 


 


The Pembina Institute (1998-2007). Life-Cycle Value Assessment Database. 


(access required). 

Union Tank Car Company (UTLX) (2008). UTLX Tank Car Designs and Descriptions. 

Retrieved from (accessed June 21, 

2010). 

U.S. Department of Energy (US DOE) (2008). "Lower and Higher Heating Values of 

Fuels (excel file)." Hydrogen Properties. Hydrogen Analysis Resource Center. 


(accessed 

June 23, 2010). 

U.S. Environmental Protection Agency. 1998. AP 42, Fifth Edition, Volume 1, Chapter 1: 

External Combustion Sources. 1.4 Natural Gas Combustion. 


(accessed July 10, 2010). 

Vantuono, W. (2002). "Sipping, not slurping: how much fuel efficiency can be squeezed 

out of a locomotive? Railroads and suppliers have devised innovative ways to 

reach what has been an elusive goal," in Railway Age (September 2002). 



Via Rail (2010). Locomotives – P42DC. 


 



071620 (2) 

ATTACHMENT 1 

MICROSOFT EXCEL WORKBOOK MODEL 

(PROVIDED ON A COMPACT DISC)

CRA 071620 (2) 

TABLE 1.1 

PROJECT AND BASELINE ELEMENTS 

2009 GREENHOUSE GAS SAVINGS STUDY 

BCUOMA 


Re-refine and Reuse 

Project PE1 Transportation (from generator to registered collector) 

PE2 Transportation (from registered collector to registered processor) 

PE3 Re-refining of oil at registered processing facilities into new products 

Baseline BE1 Crude oil extraction 

BE2 Transportation of crude oil to refinery 

BE3 Refine crude oil into oil products 

BE4 Combustion of oil for heat at generators 

Use as a Fuel 


PE2 Transportation (from registered collector to asphalt plants and pulp mills) 

PE3 Combustion of the used oil at pulp mills and asphalt plants 






Metal Oil Filters 


PE2 Transportation (from registered collector to registered steel oil filter processor) 

PE3 Processing of steel oil filters (crushed into cubes and cylinders) 

PE4 Transportation of steel to metal broker 

PE5 Transportation of steel to steel mill 

Baseline BE1 Production of steel 

BE2 Transportation of steel to steel mill 

BE3 Transportation of steel filters to disposal facility 

Paper Filters 


PE2 Transportation (from registered collector to registered paper oil filter processor) 

PE3 Processing of paper oil filters (crushed and incinerated) 

Baseline BE1 Transportation of paper filters to landfill 

BE2 Decomposition of paper filters in landfill 



PE2 Transportation (from registered collector to registered oil container processor) 

PE3 Processing of oil containers (shredded, centrifuged, washed and pelletized) 

PE4 Transportation of HDPE pellets to plastics manufacturer 

Baseline BE1 Production of HDPE 

BE2 Transportation of HDPE to plastics manufacturer 

BE3 Transportation of oil containers to disposal facility 

Page 1 of 1

CRA 071620 (2) 

TABLE 2.1 

MATERIAL QUANTITIES COLLECTED IN 2009 


BCUOMA 

Total 1 2 3 4 5 6 7 8 9 10 11 

(1) 

Zone 

Sold 

Oil L 83,600,000.00 -- -- -- -- -- -- -- -- -- -- -- 

Filters kg 4,301,823.65 -- -- -- -- -- -- -- -- -- -- -- 

# 5,740,000.00 -- -- -- -- -- -- -- -- -- -- -- 

Containers 

Consumed 

kg 1,773,000.00 -- -- -- -- -- -- -- -- -- -- -- 


Collected 

% 30.10% -- -- -- -- -- -- -- -- -- -- -- 

Oil L 44,546,000.00 21,033,225.00 2,244,182.00 2,880,386.00 7,031,434.00 1,220,699.00 2,195,175.00 4,356,375.00 2,211,954.00 1,002,184.00 369,796.00 590.00 

% (2) 

76.23% 35.99% 3.84% 4.93% 12.03% 2.09% 3.76% 7.45% 3.79% 1.71% 0.63% 0.00% 

Filters kg 3,889,628.00 1,980,597.00 198,817.00 125,307.00 662,582.00 46,697.00 222,772.00 352,488.00 186,803.00 87,460.00 23,275.00 2,830.00 

# 5,190,000.00 2,642,745.89 265,285.07 167,199.36 884,094.98 62,308.64 297,248.65 470,331.02 249,254.57 116,699.44 31,056.25 3,776.12 

% (2) 

90.42% 46.04% 4.62% 2.91% 15.40% 1.09% 5.18% 8.19% 4.34% 2.03% 0.54% 0.07% 

- (paper portion) % 8.00% 8.00% 8.00% 8.00% 8.00% 8.00% 8.00% 8.00% 8.00% 8.00% 8.00% 8.00% 

- (oil weight) % 25.00% 25.00% 25.00% 25.00% 25.00% 25.00% 25.00% 25.00% 25.00% 25.00% 25.00% 25.00% 

Containers kg 1,433,413.00 716,843.00 92,243.00 60,663.00 252,372.00 10,771.00 71,702.00 118,977.00 71,526.00 28,179.00 6,727.00 3,410.00 

% (2) 

80.85% 40.43% 5.20% 3.42% 14.23% 0.61% 4.04% 6.71% 4.03% 1.59% 0.38% 0.19% 

- 20L pails kg 440,000.00 220,041.90 28,314.88 18,621.10 77,468.03 3,306.26 22,009.62 36,521.14 21,955.60 8,649.82 2,064.92 1,046.73 

% 30.70% 30.70% 30.70% 30.70% 30.70% 30.70% 30.70% 30.70% 30.70% 30.70% 30.70% 30.70% 

- 1-5L containers kg 715,257.36 357,696.79 46,028.24 30,270.17 125,930.86 5,374.61 35,778.51 59,368.22 35,690.69 14,061.01 3,356.70 1,701.55 

% 49.90% 49.90% 49.90% 49.90% 49.90% 49.90% 49.90% 49.90% 49.90% 49.90% 49.90% 49.90% 

- Ineligible kg 278,155.64 139,104.31 17,899.87 11,771.73 48,973.11 2,090.13 13,913.87 23,087.64 13,879.71 5,468.17 1,305.38 661.71 

% 19.41% 19.41% 19.41% 19.41% 19.41% 19.41% 19.41% 19.41% 19.41% 19.41% 19.41% 19.41% 

- Antifreeze (3) 

kg 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 

% 0.00% 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 

- (oil weight) % 10.00% 10.00% 10.00% 10.00% 10.00% 10.00% 10.00% 10.00% 10.00% 10.00% 10.00% 10.00% 

Unrecovered 


% 16.62% -- -- -- -- -- -- -- -- -- -- -- 

Filters kg 412,195.65 -- -- -- -- -- -- -- -- -- -- -- 

# 550,000.00 -- -- -- -- -- -- -- -- -- -- -- 

% 9.58% -- -- -- -- -- -- -- -- -- -- -- 

Containers kg 339,587.00 -- -- -- -- -- -- -- -- -- -- -- 

% 19.15% -- -- -- -- -- -- -- -- -- -- -- 

Notes: (1) To update data for subsequent years, insert amounts sold, percent consumed (oil), and amounts collected (all values highlighted in blue). 

(2) Percentage of total amount of material sold 

(3) Antifreeze will become eligible in the 2011 calendar year. The mass of residual antifreeze in collected containers can be assumed negligible. 

Source: British Columbia Used Oil Management Association, 2010 

Page 1 of 1

TABLE 2.2 

EMISSION FACTORS (GLOBAL WARMING POTENTIAL) 


BCUOMA 

Value 

GWP 100a IPCC 2007 Climate Change kg CO 2 e / UNIT 



Project PE1 Transportation (from generator to registered collector) 2.69 kg CO2e/L diesel 


- transport by truck 2.69 kg CO2e/L diesel 

- transport by rail 2.99 kg CO2e/L diesel 

PE3 Re-refining of oil at registered processing facilities into new products 0.37 kg CO2e/L oil produced 

Baseline BE1 Crude oil extraction 51.91 kg CO2e/1 bbl crude oil 

BE2 Transportation of crude oil to refinery 9.03 kg CO2e/(1x10 6 lkm) 

BE3 Refine crude oil into oil products 0.43 kg CO2e/kg crude oil 

Use as a Fuel 

BE4 Combustion of oil for heat at generators 3.15 kg CO2e/L heavy oil 


PE2 Transportation (from registered collector to asphalt plants and pulp mills) 2.69 kg CO2e/L diesel 

PE3 Combustion of the used oil at pulp mills and asphalt plants 3.15 kg CO2e/L heavy oil 

Baseline BE1 Crude oil extraction 51.91 kg CO2e/1 bbl crude oil 

BE2 Transportation of crude oil to refinery 9.03 kg CO2e/(1x10 6 lkm) 

BE3 Refine crude oil into oil products 0.43 kg CO2e/kg crude oil 

BE4 Combustion of oil for heat at generators 3.15 kg CO2e/L heavy oil 




PE2 Transportation (from registered collector to registered steel oil filter processor) 2.69 kg CO2e/L diesel 


Electricity Production 0.02 kg CO2e/ kWh 

Natural Gas - Production, Processing, and Distributing 11.20 kg CO2e/GJ natural gas 

Natural Gas - Combustion for Heat 62.98 kg CO2e/GJ natural gas 

Propane - Production of Liquid Propane Gas 0.39 kg CO2e/L 

Propane - Combustion for Fuel (forklift) 1.53 kg CO2e/L 

PE4 Transportation of steel to metal broker 2.69 kg CO2e/L diesel 

PE5 Transportation of steel to steel mill 2.69 kg CO2e/L diesel 

Baseline BE1 Production of steel 2,095.61 kg CO2e/1000 kg steel 

BE2 Transportation of steel to steel mill included in BE1 above 

BE3 Transportation of steel filters to disposal facility 2.69 kg CO2e/L diesel 

Paper Filters 


PE2 Transportation (from registered collector to registered paper oil filter processor) 2.69 kg CO2e/L diesel 







Incinerating paper filters 2.40E-02 kg CO2e/kg 

Baseline BE1 Transportation of paper filters to landfill 2.69 kg CO2e/L diesel 

BE2 Decomposition of paper filters in landfill * Modelling completed by CRA and 

not included in this file. 



PE2 Transportation (from registered collector to registered oil container processor) 2.69 kg CO2e/L diesel 







PE4 Transportation of HDPE pellets to plastics manufacturer 2.69 kg CO2e/L diesel 

Baseline BE1 Production of HDPE 2,153.96 kg CO2e/1000 kg HDPE 

BE2 Transportation of HDPE to plastics manufacturer included in BE1 above 

BE3 Transportation of oil containers to disposal facility 2.69 kg CO2e/L diesel 

CRA 071620 (2) 

Page 1 of 1

CRA 071620 (2) 

Enter Study Year: 

Enter Census Year (start): 

Enter Census Year (end): 

2009 

2001 

2006 

TABLE 3.1 

USED OIL, FILTER, AND CONTAINER COLLECTION AND RECYCLING BY CENSUS SUBDIVISION 


BCUOMA 

2001 Pop Annual Estimated 

BCUOMA Regional 2006 2006 Area Using 2006 Growth 2009 Oil Filters Containers Oil Filters Containers 

Zone District (1) 

Name Population (2) 

km 2 

Boundary (3) 

Total Collected - 2009 

Rate Population L # kg L # kg 

- - British Columbia 4,113,487 924,815.43 3,907,738 0.01032 4,242,100 44,546,000.00 5,190,000.00 1,433,413.00 44,546,000.00 5,190,000.00 1,155,257.36 

1 9 Abbotsford 123,864 359.36 115,494 0.01409 129,174 1,108,350.75 139,260.12 37,774.21 1,108,350.75 139,260.12 30,444.08 

1 9 Chilliwack 69,217 260.19 62,567 0.02041 73,542 631,006.67 79,283.62 21,505.63 631,006.67 79,283.62 17,332.43 

1 9 Harrison Hot Springs 1,573 5.47 1,343 0.03212 1,729 14,839.56 1,864.54 505.75 14,839.56 1,864.54 407.61 

1 9 Hope 6,185 41.42 6,184 0.00003 6,186 53,074.09 6,668.56 1,808.84 53,074.09 6,668.56 1,457.83 

1 9 Kent 4,738 166.51 4,926 -0.00775 4,629 39,715.15 4,990.06 1,353.55 39,715.15 4,990.06 1,090.89 

1 9 Mission 34,505 225.78 31,272 0.01987 36,603 314,064.30 39,461.00 10,703.77 314,064.30 39,461.00 8,626.69 

1 9 Fraser Valley B 796 3,089.46 745 0.01333 828 7,106.70 892.93 242.21 7,106.70 892.93 195.21 

1 9 Fraser Valley C 952 3,669.93 716 0.05863 1,129 9,691.08 1,217.65 330.29 9,691.08 1,217.65 266.19 

1 9 Fraser Valley D 1,296 222.05 1,032 0.04661 1,486 12,748.55 1,601.81 434.49 12,748.55 1,601.81 350.18 

1 9 Fraser Valley E 3,481 750.52 3,400 0.00472 3,531 30,292.83 3,806.18 1,032.42 30,292.83 3,806.18 832.08 

1 9 Fraser Valley F 1,339 2,029.70 1,237 0.01597 1,404 12,048.36 1,513.83 410.63 12,048.36 1,513.83 330.94 

1 9 Fraser Valley G 1,914 74.97 1,827 0.00935 1,968 16,887.47 2,121.85 575.55 16,887.47 2,121.85 463.86 

1 9 Fraser Valley H 394 36.86 356 0.02049 419 3,592.73 451.41 122.45 3,592.73 451.41 98.68 

1 15 Anmore 1,785 27.42 1,344 0.05840 2,116 18,158.60 2,281.56 618.87 18,158.60 2,281.56 498.78 

1 15 Belcarra 676 5.46 682 -0.00177 672 5,769.59 724.93 196.64 5,769.59 724.93 158.48 

1 15 Burnaby 202,799 89.12 193,954 0.00896 208,298 1,787,256.00 224,562.02 60,912.29 1,787,256.00 224,562.02 49,092.18 

1 15 Coquitlam 114,565 121.69 112,890 0.00295 115,582 991,723.41 124,606.33 33,799.38 991,723.41 124,606.33 27,240.57 

1 15 Delta 96,723 183.7 96,950 -0.00047 96,587 828,742.55 104,128.40 28,244.76 828,742.55 104,128.40 22,763.82 

1 15 Langley (1) 93,726 306.93 86,896 0.01525 98,079 841,544.28 105,736.89 28,681.06 841,544.28 105,736.89 23,115.46 

1 15 Langley (2) 23,606 10.22 23,643 -0.00031 23,584 202,355.50 25,425.21 6,896.57 202,355.50 25,425.21 5,558.28 

1 15 Lions Bay 1,328 2.55 1,379 -0.00751 1,298 11,139.84 1,399.68 379.66 11,139.84 1,399.68 305.99 

1 15 Maple Ridge 68,949 265.79 63,169 0.01766 72,668 623,509.49 78,341.63 21,250.11 623,509.49 78,341.63 17,126.50 

1 15 New Westminster 58,549 15.41 54,656 0.01386 61,017 523,539.17 65,780.73 17,842.98 523,539.17 65,780.73 14,380.53 

1 15 North Vancouver 82,562 160.67 82,310 0.00061 82,714 709,704.37 89,171.69 24,187.76 709,704.37 89,171.69 19,494.09 

1 15 North Vancouver 45,165 11.85 44,092 0.00482 45,821 393,158.85 49,398.94 13,399.43 393,158.85 49,398.94 10,799.25 

1 15 Pitt Meadows 15,623 85.38 14,670 0.01267 16,224 139,208.49 17,491.03 4,744.43 139,208.49 17,491.03 3,823.77 

1 15 Port Coquitlam 52,687 28.85 51,257 0.00552 53,564 459,594.01 57,746.26 15,663.63 459,594.01 57,746.26 12,624.09 

1 15 Port Moody 27,512 25.62 23,816 0.02927 30,000 257,403.76 32,341.82 8,772.70 257,403.76 32,341.82 7,070.34 

1 15 Richmond 174,461 128.76 164,345 0.01202 180,827 1,551,544.33 194,945.73 52,878.89 1,551,544.33 194,945.73 42,617.68 

1 15 Surrey 394,976 317.19 347,820 0.02575 426,285 3,657,641.32 459,568.92 124,657.75 3,657,641.32 459,568.92 100,467.76 

1 15 Vancouver 578,041 114.71 545,671 0.01159 598,378 5,134,238.27 645,097.80 174,982.33 5,134,238.27 645,097.80 141,026.79 

1 15 West Vancouver 42,131 87.13 41,421 0.00340 42,563 365,200.36 45,886.06 12,446.56 365,200.36 45,886.06 10,031.29 

1 15 White Rock 18,755 5.16 18,250 0.00547 19,065 163,580.04 20,553.22 5,575.05 163,580.04 20,553.22 4,493.20 

1 15 Greater Vancouver A 11,050 818.62 8,034 0.06583 13,379 114,794.55 14,423.50 3,912.37 114,794.55 14,423.50 3,153.17 

2 51 Vanderhoof 4,064 54.85 4,390 -0.01531 3,880 76,385.96 9,029.59 3,139.71 76,385.96 9,029.59 2,530.44 

2 51 Bulkley-Nechako F 3,137 5,397.05 3,384 -0.01504 2,998 59,010.78 6,975.67 2,425.53 59,010.78 6,975.67 1,954.85 

2 41 Quesnel 9,326 35.34 10,044 -0.01472 8,920 175,604.22 20,758.20 7,217.89 175,604.22 20,758.20 5,817.25 

2 41 Wells 236 159.15 235 0.00085 237 4,657.84 550.60 191.45 4,657.84 550.60 154.30 

2 41 Cariboo A 5,859 783.36 6,428 -0.01837 5,542 109,103.43 12,897.13 4,484.50 109,103.43 12,897.13 3,614.27 

2 41 Cariboo B 3,858 1,419.74 4,338 -0.02318 3,596 70,790.04 8,368.10 2,909.70 70,790.04 8,368.10 2,345.07 

2 41 Cariboo C 1,164 7,392.10 1,323 -0.02528 1,078 21,220.48 2,508.48 872.23 21,220.48 2,508.48 702.97 

2 41 Cariboo I 1,661 11,942.85 1,773 -0.01297 1,597 31,443.62 3,716.95 1,292.43 31,443.62 3,716.95 1,041.63 

2 53 McBride 660 4.43 711 -0.01478 631 12,425.53 1,468.82 510.73 12,425.53 1,468.82 411.62 

2 53 Prince George 70,981 316 72,406 -0.00397 70,139 1,380,794.24 163,223.88 56,755.02 1,380,794.24 163,223.88 45,741.64 

2 53 Valemount 1,018 4.96 1,243 -0.03915 903 17,777.88 2,101.53 730.73 17,777.88 2,101.53 588.93 

2 53 Fraser-Fort George A 3,275 1,379.17 3,406 -0.00781 3,199 62,973.47 7,444.10 2,588.41 62,973.47 7,444.10 2,086.13 

2 53 Fraser-Fort George C 3,217 2,818.61 3,178 0.00244 3,241 63,796.33 7,541.37 2,622.23 63,796.33 7,541.37 2,113.38 

2 53 Fraser-Fort George D 4,361 669.19 4,527 -0.00744 4,264 83,949.43 9,923.67 3,450.59 83,949.43 9,923.67 2,781.00 

2 53 Fraser-Fort George E 502 617.91 564 -0.02302 468 9,215.63 1,089.38 378.79 9,215.63 1,089.38 305.29 

2 53 Fraser-Fort George F 1,284 12,541.44 1,412 -0.01883 1,213 23,876.44 2,822.44 981.40 23,876.44 2,822.44 790.96 

2 53 Fraser-Fort George G 349 17,200.43 479 -0.06136 289 5,681.80 671.65 233.54 5,681.80 671.65 188.22 

(4) 

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2 53 Fraser-Fort George H 1,877 14,978.96 2,009 -0.01350 1,802 35,474.90 4,193.49 1,458.13 35,474.90 4,193.49 1,175.18 

3 53 Mackenzie 4,539 159.09 5,206 -0.02705 4,181 189,254.93 10,985.79 3,985.84 189,254.93 10,985.79 3,212.39 

3 55 Chetwynd 2,633 64.32 2,591 0.00322 2,659 120,352.28 6,986.16 2,534.71 120,352.28 6,986.16 2,042.84 

3 55 Dawson Creek 10,994 22.32 10,754 0.00442 11,141 504,336.68 29,275.51 10,621.69 504,336.68 29,275.51 8,560.54 

3 55 Fort St. John 17,402 22.74 16,051 0.01629 18,267 826,933.92 48,001.49 17,415.82 826,933.92 48,001.49 14,036.26 

3 55 Hudson's Hope 1,012 869.43 1,039 -0.00525 996 45,095.47 2,617.68 949.74 45,095.47 2,617.68 765.44 

3 55 Ingenika Point 0 5.43 0 0.00000 0 0.00 0.00 0.00 0.00 0.00 0.00 

3 55 Pouce Coupe 739 2.06 833 -0.02366 688 31,135.62 1,807.35 655.74 31,135.62 1,807.35 528.49 

3 55 Taylor 1,384 16.61 1,143 0.03901 1,552 70,275.41 4,079.32 1,480.05 70,275.41 4,079.32 1,192.84 

3 55 Tumbler Ridge 2,454 1,574.45 1,851 0.05802 2,906 131,573.63 7,637.53 2,771.04 131,573.63 7,637.53 2,233.31 

3 55 Peace River B 5,538 86,211.91 4,997 0.02077 5,890 266,656.71 15,478.77 5,615.98 266,656.71 15,478.77 4,526.19 

3 55 Peace River C 6,350 582.49 5,813 0.01783 6,696 303,117.61 17,595.24 6,383.87 303,117.61 17,595.24 5,145.08 

3 55 Peace River D 5,749 11,670.10 5,857 -0.00372 5,685 257,368.84 14,939.63 5,420.37 257,368.84 14,939.63 4,368.54 

3 55 Peace River E 3,031 16,593.72 3,142 -0.00717 2,966 134,284.90 7,794.91 2,828.14 134,284.90 7,794.91 2,279.33 

4 9 Fraser Valley A 478 2,335.28 596 -0.04317 419 5,165.41 649.47 185.40 5,165.41 649.47 149.42 

4 41 100 Hundred Mile House 1,885 51.34 1,739 0.01625 1,978 24,405.43 3,068.61 875.96 24,405.43 3,068.61 705.98 

4 41 Williams Lake 10,744 33.11 11,153 -0.00744 10,506 129,598.07 16,294.97 4,651.53 129,598.07 16,294.97 3,748.89 

4 41 Cariboo D 3,073 856.15 3,296 -0.01391 2,947 36,347.60 4,570.15 1,304.59 36,347.60 4,570.15 1,051.43 

4 41 Cariboo E 4,336 1,744.06 4,668 -0.01465 4,148 51,171.99 6,434.09 1,836.66 51,171.99 6,434.09 1,480.26 

4 41 Cariboo F 4,384 9,775.63 4,961 -0.02443 4,071 50,213.36 6,313.56 1,802.26 50,213.36 6,313.56 1,452.53 

4 41 Cariboo G 4,974 2,678.81 5,001 -0.00108 4,958 61,159.38 7,689.85 2,195.13 61,159.38 7,689.85 1,769.16 

4 41 Cariboo H 1,744 2,603.71 1,834 -0.01001 1,692 20,873.86 2,624.57 749.20 20,873.86 2,624.57 603.82 

4 41 Cariboo K 552 13,650.75 674 -0.03915 490 6,040.52 759.50 216.81 6,040.52 759.50 174.73 

4 41 Cariboo L 4,316 1,268.42 4,254 0.00290 4,354 53,705.62 6,752.66 1,927.60 53,705.62 6,752.66 1,553.55 

4 35 Kelowna 106,707 211.69 96,288 0.02076 113,492 1,400,017.03 176,030.67 50,249.37 1,400,017.03 176,030.67 40,498.41 

4 35 Lake Country 9,606 122.16 9,267 0.00721 9,815 121,080.05 15,223.96 4,345.80 121,080.05 15,223.96 3,502.49 

4 35 Peachland 4,883 15.98 4,654 0.00965 5,026 61,997.03 7,795.18 2,225.20 61,997.03 7,795.18 1,793.39 

4 35 Central Okanagan 3,978 1,244.16 3,672 0.01614 4,174 51,486.10 6,473.59 1,847.94 51,486.10 6,473.59 1,489.34 

4 35 Central Okanagan J 28,972 1,297.81 26,001 0.02187 30,915 381,363.83 47,950.65 13,687.90 381,363.83 47,950.65 11,031.74 

4 39 Salmon Arm 16,012 155.36 15,210 0.01033 16,513 203,705.79 25,612.88 7,311.40 203,705.79 25,612.88 5,892.61 

4 39 Sicamous 2,676 14.68 2,720 -0.00326 2,650 32,689.21 4,110.17 1,173.28 32,689.21 4,110.17 945.60 

4 39 Columbia-Shuswap C 7,695 506.33 6,762 0.02619 8,316 102,578.58 12,897.68 3,681.75 102,578.58 12,897.68 2,967.30 

4 39 Columbia-Shuswap D 3,899 694.53 3,904 -0.00026 3,896 48,060.39 6,042.86 1,724.98 48,060.39 6,042.86 1,390.25 

4 39 Columbia-Shuswap E 1,528 1,542.18 1,491 0.00491 1,551 19,128.40 2,405.10 686.56 19,128.40 2,405.10 553.33 

4 39 Columbia-Shuswap F 2,731 2,662.29 2,126 0.05136 3,174 39,151.17 4,922.66 1,405.21 39,151.17 4,922.66 1,132.53 

4 37 Armstrong 4,241 5.24 4,256 -0.00071 4,232 52,205.50 6,564.04 1,873.76 52,205.50 6,564.04 1,510.15 

4 37 Coldstream 9,471 67.25 9,106 0.00789 9,697 119,620.25 15,040.41 4,293.41 119,620.25 15,040.41 3,460.27 

4 37 Enderby 2,828 4.23 2,818 0.00071 2,834 34,959.92 4,395.67 1,254.78 34,959.92 4,395.67 1,011.29 

4 37 Lumby 1,634 5.27 1,618 0.00197 1,644 20,276.09 2,549.41 727.75 20,276.09 2,549.41 586.53 

4 37 Spallumcheen 4,960 254.9 5,134 -0.00687 4,858 59,932.88 7,535.64 2,151.11 59,932.88 7,535.64 1,733.68 

4 37 Vernon 35,944 94.2 33,542 0.01393 37,467 462,186.06 58,112.81 16,588.77 462,186.06 58,112.81 13,369.70 

4 37 North Okanagan B 3,211 489.15 3,034 0.01140 3,322 40,981.05 5,152.74 1,470.89 40,981.05 5,152.74 1,185.46 

4 37 North Okanagan C 3,947 301.12 3,612 0.01790 4,163 51,350.74 6,456.57 1,843.08 51,350.74 6,456.57 1,485.43 

4 37 North Okanagan D 2,837 1,797.09 2,840 -0.00021 2,835 34,974.53 4,397.51 1,255.30 34,974.53 4,397.51 1,011.71 

4 37 North Okanagan F 4,091 1,766.90 3,855 0.01195 4,239 52,297.45 6,575.60 1,877.06 52,297.45 6,575.60 1,512.81 

4 7 Keremeos 1,289 2.11 1,197 0.01492 1,348 16,623.26 2,090.12 596.64 16,623.26 2,090.12 480.86 

4 7 Oliver 4,370 4.95 4,224 0.00682 4,460 55,017.89 6,917.66 1,974.70 55,017.89 6,917.66 1,591.51 

4 7 Osoyoos 4,752 8.76 4,295 0.02043 5,049 62,286.27 7,831.54 2,235.58 62,286.27 7,831.54 1,801.76 

4 7 Penticton 31,909 42.02 30,985 0.00589 32,477 400,625.12 50,372.46 14,379.22 400,625.12 50,372.46 11,588.92 

4 7 Princeton 2,677 10.25 2,610 0.00508 2,718 33,529.03 4,215.76 1,203.42 33,529.03 4,215.76 969.90 

4 7 Summerland 10,828 73.88 10,723 0.00195 10,891 134,355.48 16,893.14 4,822.28 134,355.48 16,893.14 3,886.51 

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4 7 Okanagan-Similkameen A 1,921 259.39 1,897 0.00252 1,936 23,876.54 3,002.11 856.98 23,876.54 3,002.11 690.68 

4 7 Okanagan-Similkameen B 1,082 238.75 1,122 -0.00723 1,059 13,059.78 1,642.07 468.74 13,059.78 1,642.07 377.78 

4 7 Okanagan-Similkameen C 3,899 444.1 4,154 -0.01259 3,754 46,303.44 5,821.95 1,661.92 46,303.44 5,821.95 1,339.42 

4 7 Okanagan-Similkameen D 5,913 916.99 5,703 0.00726 6,043 74,541.57 9,372.46 2,675.44 74,541.57 9,372.46 2,156.27 

4 7 Okanagan-Similkameen E 2,010 491.13 1,996 0.00140 2,018 24,899.20 3,130.69 893.68 24,899.20 3,130.69 720.26 

4 7 Okanagan-Similkameen F 2,011 568.12 1,979 0.00321 2,030 25,047.24 3,149.31 898.99 25,047.24 3,149.31 724.54 

4 7 Okanagan-Similkameen G 2,308 2,119.89 2,052 0.02379 2,477 30,551.94 3,841.44 1,096.57 30,551.94 3,841.44 883.78 

4 7 Okanagan-Similkameen H 2,208 4,815.07 1,969 0.02318 2,365 29,175.55 3,668.38 1,047.17 29,175.55 3,668.38 843.96 

4 31 Lillooet 2,324 27.83 2,741 -0.03247 2,105 25,965.72 3,264.79 931.96 25,965.72 3,264.79 751.11 

4 31 Pemberton 2,192 4.45 1,642 0.05948 2,607 32,157.99 4,043.37 1,154.21 32,157.99 4,043.37 930.24 

4 31 Squamish 14,949 106.11 14,247 0.00967 15,387 189,807.49 23,865.38 6,812.56 189,807.49 23,865.38 5,490.58 

4 31 Whistler 9,248 161.71 8,896 0.00779 9,466 116,769.01 14,681.91 4,191.07 116,769.01 14,681.91 3,377.79 

4 31 Squamish-Lillooet A 207 3,726.67 223 -0.01478 198 2,441.95 307.04 87.65 2,441.95 307.04 70.64 

4 31 Squamish-Lillooet B 575 3,460.19 423 0.06332 691 8,527.71 1,072.23 306.08 8,527.71 1,072.23 246.68 

4 31 Squamish-Lillooet C 1,887 5,606.94 1,499 0.04711 2,166 26,725.27 3,360.29 959.22 26,725.27 3,360.29 773.08 

4 31 Squamish-Lillooet D 839 3,117.56 750 0.02268 897 11,070.07 1,391.89 397.33 11,070.07 1,391.89 320.22 

4 29 Gibsons 4,182 4.33 3,906 0.01375 4,357 53,745.62 6,757.69 1,929.04 53,745.62 6,757.69 1,554.70 

4 29 Sechelt 8,454 39.71 7,775 0.01689 8,890 109,659.77 13,788.03 3,935.90 109,659.77 13,788.03 3,172.14 

4 29 Sechelt (Part) 827 10.71 795 0.00792 847 10,446.16 1,313.44 374.93 10,446.16 1,313.44 302.18 

4 29 Sunshine Coast A 2,624 1,901.61 2,374 0.02023 2,786 34,373.33 4,321.92 1,233.73 34,373.33 4,321.92 994.32 

4 29 Sunshine Coast B 2,558 1,275.86 2,353 0.01685 2,689 33,176.89 4,171.49 1,190.78 33,176.89 4,171.49 959.71 

4 29 Sunshine Coast D 3,307 143.59 3,090 0.01367 3,444 42,490.08 5,342.48 1,525.05 42,490.08 5,342.48 1,229.11 

4 29 Sunshine Coast E 3,552 21.32 3,311 0.01415 3,705 45,703.47 5,746.51 1,640.39 45,703.47 5,746.51 1,322.07 

4 29 Sunshine Coast F 2,235 380.82 1,971 0.02546 2,410 29,730.35 3,738.14 1,067.08 29,730.35 3,738.14 860.01 

4 33 Ashcroft 1,664 51.45 1,814 -0.01711 1,580 19,490.86 2,450.68 699.57 19,490.86 2,450.68 563.81 

4 33 Cache Creek 1,037 10.57 1,056 -0.00362 1,026 12,653.64 1,591.00 454.16 12,653.64 1,591.00 366.03 

4 33 Chase 2,409 3.75 2,470 -0.00499 2,373 29,274.45 3,680.81 1,050.72 29,274.45 3,680.81 846.82 

4 33 Clinton 578 4.36 631 -0.01739 548 6,764.49 850.53 242.79 6,764.49 850.53 195.68 

4 33 Kamloops 80,376 297.3 77,281 0.00788 82,292 1,015,141.42 127,638.46 36,435.42 1,015,141.42 127,638.46 29,365.08 

4 33 Logan Lake 2,162 325.4 2,185 -0.00211 2,148 26,501.24 3,332.12 951.18 26,501.24 3,332.12 766.60 

4 33 Lytton 235 6.71 319 -0.05929 196 2,413.25 303.43 86.62 2,413.25 303.43 69.81 

4 33 Merritt 

Thompson-Nicola A (Wells 

6,998 24.94 7,088 -0.00255 6,945 85,666.70 10,771.27 3,074.75 85,666.70 10,771.27 2,478.09 

4 33 Gray Country) 

Thompson-Nicola B 

3,897 7,165.26 4,399 -0.02394 3,624 44,701.72 5,620.56 1,604.43 44,701.72 5,620.56 1,293.09 

4 33 (Thompson Headwaters) 

Thompson-Nicola E 

269 5,137.36 368 -0.06075 223 2,749.56 345.71 98.69 2,749.56 345.71 79.54 

4 33 (Bonaparte Plateau) 

Thompson-Nicola I (Blue 

1,404 6,654.33 1,297 0.01598 1,472 18,163.16 2,283.74 651.91 18,163.16 2,283.74 525.41 

4 33 Sky Country) 

Thompson-Nicola J (Copper 

1,320 5,740.21 1,276 0.00680 1,347 16,617.89 2,089.44 596.45 16,617.89 2,089.44 480.71 

4 33 Desert Country) 1,609 3,297.75 1,509 0.01292 1,672 20,627.38 2,593.58 740.36 20,627.38 2,593.58 596.69 

4 33 Thompson-Nicola L 2,981 1,912.79 2,860 0.00832 3,056 37,698.80 4,740.05 1,353.08 37,698.80 4,740.05 1,090.52 

4 33 Thompson-Nicola M 1,797 3,837.02 1,793 0.00045 1,799 22,197.12 2,790.95 796.70 22,197.12 2,790.95 642.10 

4 33 Thompson-Nicola N 

Thompson-Nicola O (Lower 

839 2,346.04 707 0.03483 930 11,469.26 1,442.08 411.65 11,469.26 1,442.08 331.77 

4 33 North Thompson) 

Thompson-Nicola P (Rivers 

2,978 5,420.16 3,257 -0.01775 2,822 34,814.23 4,377.36 1,249.55 34,814.23 4,377.36 1,007.07 

4 33 and the Peaks) 4,081 1,591.67 3,736 0.01782 4,303 53,082.38 6,674.30 1,905.23 53,082.38 6,674.30 1,535.52 

5 49 New Aiyansh 806 2.64 716 0.02396 865 129,947.71 6,632.97 1,146.61 129,947.71 6,632.97 924.11 

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5 49 Stewart 496 571.5 661 -0.05582 417 62,694.61 3,200.15 553.19 62,694.61 3,200.15 445.85 

5 49 Kitimat-Stikine A 46 25,398.73 81 -0.10699 33 4,919.28 251.10 43.41 4,919.28 251.10 34.98 

5 49 Kitimat-Stikine D 91 28,288.47 88 0.00673 93 13,943.02 711.70 123.03 13,943.02 711.70 99.15 

5 59 Fort Nelson 4,514 13.26 4,188 0.01511 4,722 709,046.73 36,192.16 6,256.37 709,046.73 36,192.16 5,042.31 

5 59 Northern Rockies A 1,079 50,349.58 937 0.02862 1,174 176,348.16 9,001.41 1,556.03 176,348.16 9,001.41 1,254.08 

5 59 Northern Rockies B 109 34,693.45 100 0.01738 115 17,237.04 879.84 152.09 17,237.04 879.84 122.58 

5 57 Good Hope Lake 32 0.65 75 -0.15663 19 2,882.59 147.14 25.43 2,882.59 147.14 20.50 

5 57 Lower Post 113 0.18 28 0.32186 261 39,193.23 2,000.56 345.83 39,193.23 2,000.56 278.72 

5 57 Stikine Region 574 132,456.37 931 -0.09220 429 64,486.62 3,291.62 569.01 64,486.62 3,291.62 458.59 

6 3 Castlegar 7,259 19.8 7,585 -0.00875 7,070 99,899.25 13,527.36 3,263.05 99,899.25 13,527.36 2,629.85 

6 3 Creston 4,826 8.48 4,795 0.00129 4,845 68,454.06 9,269.36 2,235.95 68,454.06 9,269.36 1,802.06 

6 3 Kaslo 1,072 2.8 1,032 0.00763 1,097 15,496.60 2,098.40 506.17 15,496.60 2,098.40 407.95 

6 3 Nakusp 1,524 8 1,698 -0.02139 1,428 20,181.16 2,732.73 659.19 20,181.16 2,732.73 531.27 

6 3 Nelson 9,258 11.72 9,318 -0.00129 9,222 130,306.64 17,644.82 4,256.27 130,306.64 17,644.82 3,430.33 

6 3 New Denver 512 1.1 538 -0.00986 497 7,022.56 950.92 229.38 7,022.56 950.92 184.87 

6 3 Salmo 1,007 2.38 1,120 -0.02105 945 13,349.01 1,807.59 436.02 13,349.01 1,807.59 351.41 

6 3 Silverton 185 0.44 222 -0.03581 166 2,343.13 317.28 76.53 2,343.13 317.28 61.68 

6 3 Slocan 314 0.75 336 -0.01345 301 4,260.07 576.86 139.15 4,260.07 576.86 112.15 

6 3 Central Kootenay A 2,041 1,704.08 2,125 -0.00803 1,992 28,149.21 3,811.68 919.45 28,149.21 3,811.68 741.03 

6 3 Central Kootenay B 4,575 1,620.91 4,742 -0.00714 4,478 63,267.62 8,567.07 2,066.54 63,267.62 8,567.07 1,665.52 

6 3 Central Kootenay C 1,284 733.29 1,287 -0.00047 1,282 18,117.14 2,453.24 591.77 18,117.14 2,453.24 476.93 

6 3 Central Kootenay D 1,525 5,788.48 1,500 0.00331 1,540 21,762.55 2,946.87 710.84 21,762.55 2,946.87 572.90 

6 3 Central Kootenay E 3,716 812.61 3,521 0.01084 3,838 54,231.82 7,343.53 1,771.40 54,231.82 7,343.53 1,427.66 

6 3 Central Kootenay F 3,730 402.62 3,907 -0.00923 3,628 51,257.90 6,940.83 1,674.26 51,257.90 6,940.83 1,349.37 

6 3 Central Kootenay G 1,605 1,510.61 1,354 0.03460 1,777 25,114.33 3,400.73 820.32 25,114.33 3,400.73 661.14 

6 3 Central Kootenay H 4,319 3,293.57 4,472 -0.00694 4,230 59,764.70 8,092.74 1,952.12 59,764.70 8,092.74 1,573.31 

6 3 Central Kootenay I 2,415 109.47 2,436 -0.00173 2,402 33,946.40 4,596.68 1,108.81 33,946.40 4,596.68 893.64 

6 3 Central Kootenay J 2,792 1,701.37 2,930 -0.00960 2,712 38,324.52 5,189.52 1,251.81 38,324.52 5,189.52 1,008.90 

6 3 Central Kootenay K 1,800 4,390.45 1,979 -0.01878 1,700 24,027.09 3,253.51 784.81 24,027.09 3,253.51 632.51 

6 39 Golden 3,811 11.02 4,020 -0.01062 3,691 52,150.61 7,061.71 1,703.42 52,150.61 7,061.71 1,372.87 

6 39 Revelstoke 7,230 31.9 7,500 -0.00731 7,073 99,934.91 13,532.19 3,264.22 99,934.91 13,532.19 2,630.79 

6 39 Columbia-Shuswap A 3,097 13,514.74 3,135 -0.00244 3,074 43,440.63 5,882.30 1,418.92 43,440.63 5,882.30 1,143.58 

6 39 Columbia-Shuswap B 706 9,786.38 625 0.02467 760 10,732.29 1,453.26 350.55 10,732.29 1,453.26 282.53 

6 1 Canal Flats 700 10.84 754 -0.01475 669 9,459.47 1,280.91 308.98 9,459.47 1,280.91 249.02 

6 1 Cranbrook 18,267 25.14 18,517 -0.00271 18,119 256,010.56 34,666.39 8,362.19 256,010.56 34,666.39 6,739.50 

6 1 Elkford 2,463 101.59 2,589 -0.00993 2,390 33,775.09 4,573.49 1,103.21 33,775.09 4,573.49 889.13 

6 1 Fernie 4,217 16.05 4,611 -0.01771 3,997 56,475.67 7,647.37 1,844.69 56,475.67 7,647.37 1,486.73 

6 1 Invermere 3,002 10.18 2,858 0.00988 3,092 43,687.02 5,915.66 1,426.97 43,687.02 5,915.66 1,150.06 

6 1 Kimberley 6,139 58.31 6,484 -0.01088 5,941 83,942.73 11,366.69 2,741.86 83,942.73 11,366.69 2,209.80 

6 1 Radium Hot Springs 735 6.31 583 0.04743 845 11,934.14 1,616.00 389.81 11,934.14 1,616.00 314.17 

6 1 Sparwood 3,618 177.71 3,812 -0.01039 3,506 49,543.95 6,708.75 1,618.28 49,543.95 6,708.75 1,304.25 

6 1 East Kootenay A 1,873 4,653.72 1,837 0.00389 1,895 26,774.89 3,625.59 874.56 26,774.89 3,625.59 704.85 

6 1 East Kootenay B 1,819 2,791.55 1,838 -0.00208 1,808 25,542.16 3,458.66 834.30 25,542.16 3,458.66 672.40 

6 1 East Kootenay C 5,866 4,519.23 5,753 0.00390 5,935 83,857.78 11,355.18 2,739.08 83,857.78 11,355.18 2,207.56 

6 1 East Kootenay E 1,731 4,266.98 1,824 -0.01041 1,677 23,702.44 3,209.55 774.20 23,702.44 3,209.55 623.97 

6 1 East Kootenay F 2,939 6,102.84 2,602 0.02466 3,162 44,675.32 6,049.48 1,459.25 44,675.32 6,049.48 1,176.08 

6 1 East Kootenay G 1,563 4,654.72 1,635 -0.00897 1,521 21,495.94 2,910.77 702.13 21,495.94 2,910.77 565.88 

6 5 Fruitvale 1,952 2.66 2,025 -0.00732 1,909 26,980.21 3,653.39 881.27 26,980.21 3,653.39 710.26 

6 5 Grand Forks 4,036 10.44 4,054 -0.00089 4,025 56,875.38 7,701.50 1,857.75 56,875.38 7,701.50 1,497.25 

6 5 Greenwood 625 2.52 666 -0.01263 602 8,500.73 1,151.08 277.66 8,500.73 1,151.08 223.78 

6 5 Midway 621 12.16 638 -0.00539 611 8,633.50 1,169.06 282.00 8,633.50 1,169.06 227.28 

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6 5 Montrose 1,012 1.53 1,067 -0.01053 980 13,852.33 1,875.74 452.46 13,852.33 1,875.74 364.66 

6 5 Rossland 3,278 57.97 3,646 -0.02105 3,075 43,452.72 5,883.93 1,419.32 43,452.72 5,883.93 1,143.90 

6 5 Trail 7,237 34.78 7,575 -0.00909 7,041 99,493.98 13,472.48 3,249.82 99,493.98 13,472.48 2,619.19 

6 5 Warfield 1,729 1.9 1,739 -0.00115 1,723 24,345.85 3,296.67 795.22 24,345.85 3,296.67 640.91 

6 5 Kootenay Boundary A 1,989 238.52 1,984 0.00050 1,992 28,146.43 3,811.31 919.36 28,146.43 3,811.31 740.96 

6 5 Kootenay Boundary B 1,418 778.61 1,583 -0.02177 1,327 18,755.39 2,539.67 612.62 18,755.39 2,539.67 493.74 

6 5 Kootenay Boundary C 1,435 530.61 1,456 -0.00290 1,423 20,100.13 2,721.76 656.54 20,100.13 2,721.76 529.14 

6 5 Kootenay Boundary D 3,176 2,116.43 3,241 -0.00404 3,138 44,333.71 6,003.23 1,448.09 44,333.71 6,003.23 1,167.09 

6 5 Kootenay Boundary E 2,234 4,307.49 2,169 0.00592 2,274 32,129.95 4,350.72 1,049.48 32,129.95 4,350.72 845.82 

6 37 North Okanagan E 934 2,613.15 938 -0.00085 932 13,163.34 1,782.45 429.96 13,163.34 1,782.45 346.53 

7 17 Central Saanich 15,745 41.42 15,348 0.00512 15,988 132,513.43 14,306.66 3,619.08 132,513.43 14,306.66 2,916.79 

7 17 Colwood 14,687 17.76 13,745 0.01335 15,283 126,668.55 13,675.62 3,459.45 126,668.55 13,675.62 2,788.14 

7 17 Esquimalt 16,840 7.04 16,127 0.00869 17,283 143,244.48 15,465.23 3,912.15 143,244.48 15,465.23 3,152.99 

7 17 Highlands 1,903 37.87 1,674 0.02597 2,055 17,033.80 1,839.03 465.21 17,033.80 1,839.03 374.94 

7 17 Langford 22,459 39.55 18,840 0.03577 24,956 206,842.05 22,331.46 5,649.07 206,842.05 22,331.46 4,552.86 

7 17 Metchosin 4,795 71.32 4,857 -0.00257 4,758 39,436.98 4,257.77 1,077.06 39,436.98 4,257.77 868.06 

7 17 North Saanich 10,823 37.14 10,436 0.00731 11,062 91,685.05 9,898.67 2,504.01 91,685.05 9,898.67 2,018.10 

7 17 Oak Bay 17,908 10.38 17,798 0.00123 17,974 148,975.66 16,083.99 4,068.68 148,975.66 16,083.99 3,279.14 

7 17 Saanich 108,265 103.44 103,654 0.00874 111,129 921,068.62 99,442.12 25,155.31 921,068.62 99,442.12 20,273.89 

7 17 Sidney 11,315 5.04 10,929 0.00697 11,553 95,755.06 10,338.09 2,615.17 95,755.06 10,338.09 2,107.69 

7 17 Sooke 9,704 50.01 8,735 0.02126 10,336 85,669.50 9,249.21 2,339.72 85,669.50 9,249.21 1,885.69 

7 17 Victoria 78,057 19.68 74,125 0.01039 80,516 667,333.37 72,047.88 18,225.55 667,333.37 72,047.88 14,688.86 

7 17 View Royal 8,768 14.48 7,271 0.03815 9,810 81,310.58 8,778.60 2,220.67 81,310.58 8,778.60 1,789.75 

7 17 Capital F 9,640 182.23 9,279 0.00766 9,863 81,749.53 8,825.99 2,232.66 81,749.53 8,825.99 1,799.41 

7 17 Capital G 5,101 187.46 4,307 0.03442 5,646 46,795.74 5,052.25 1,278.04 46,795.74 5,052.25 1,030.03 

7 17 Capital H (Part 1) 4,250 228.08 3,801 0.02258 4,544 37,665.72 4,066.54 1,028.69 37,665.72 4,066.54 829.07 

7 17 Capital H (Part 2) 234 1,272.66 161 0.07765 293 2,427.24 262.05 66.29 2,427.24 262.05 53.43 

7 19 Duncan 4,986 2.05 4,699 0.01193 5,167 42,821.62 4,623.19 1,169.50 42,821.62 4,623.19 942.56 

7 19 Ladysmith 7,538 12.18 6,811 0.02049 8,011 66,396.62 7,168.44 1,813.36 66,396.62 7,168.44 1,461.47 

7 19 Lake Cowichan 2,948 8.25 2,827 0.00842 3,023 25,055.97 2,705.14 684.30 25,055.97 2,705.14 551.51 

7 19 North Cowichan 27,557 193.66 26,138 0.01063 28,445 235,760.14 25,453.57 6,438.85 235,760.14 25,453.57 5,189.38 

7 19 Cowichan Valley A 4,073 49.43 3,416 0.03581 4,526 37,515.87 4,050.36 1,024.60 37,515.87 4,050.36 825.77 

7 19 Cowichan Valley B 7,562 306.23 7,081 0.01323 7,866 65,196.55 7,038.87 1,780.58 65,196.55 7,038.87 1,435.06 

7 19 Cowichan Valley C 4,530 22.64 4,525 0.00022 4,533 37,570.65 4,056.27 1,026.09 37,570.65 4,056.27 826.98 

7 19 Cowichan Valley D 2,823 15.48 2,689 0.00977 2,907 24,090.49 2,600.90 657.94 24,090.49 2,600.90 530.26 

7 19 Cowichan Valley E 3,878 134.87 3,785 0.00487 3,935 32,613.37 3,521.06 890.70 32,613.37 3,521.06 717.86 

7 19 Cowichan Valley F 1,744 1,792.90 1,763 -0.00216 1,733 14,361.03 1,550.47 392.21 14,361.03 1,550.47 316.10 

7 19 Cowichan Valley G 2,249 284.3 2,199 0.00451 2,280 18,893.42 2,039.81 516.00 18,893.42 2,039.81 415.87 

7 19 Cowichan Valley H 2,274 83.02 2,185 0.00802 2,329 19,304.41 2,084.18 527.22 19,304.41 2,084.18 424.91 

7 19 Cowichan Valley I 1,176 507.87 1,149 0.00466 1,193 9,883.76 1,067.09 269.94 9,883.76 1,067.09 217.55 

7 21 Nanaimo 78,692 89.3 73,000 0.01513 82,318 682,272.58 73,660.78 18,633.55 682,272.58 73,660.78 15,017.69 

7 21 Nanaimo A 6,751 60.11 6,423 0.01001 6,956 57,651.28 6,224.25 1,574.51 57,651.28 6,224.25 1,268.98 

7 21 Nanaimo B 4,050 57.6 3,522 0.02833 4,404 36,502.04 3,940.90 996.91 36,502.04 3,940.90 803.46 

7 21 Nanaimo C 2,508 1,098.49 1,932 0.05357 2,933 24,309.86 2,624.59 663.93 24,309.86 2,624.59 535.09 

8 23 Port Alberni 17,548 19.92 17,748 -0.00226 17,429 200,424.22 22,584.85 6,480.94 200,424.22 22,584.85 5,223.31 

8 23 Tofino 1,655 10.54 1,466 0.02455 1,780 20,467.84 2,306.42 661.85 20,467.84 2,306.42 533.42 

8 23 Ucluelet 1,487 6.55 1,559 -0.00941 1,445 16,621.32 1,872.98 537.47 16,621.32 1,872.98 433.17 

8 23 Alberni-Clayoquot A 303 1,621.71 285 0.01232 314 3,614.74 407.33 116.89 3,614.74 407.33 94.20 

8 23 Alberni-Clayoquot B 476 92.53 502 -0.01058 461 5,301.81 597.44 171.44 5,301.81 597.44 138.17 

8 23 Alberni-Clayoquot C 401 3,210.02 369 0.01677 422 4,847.20 546.21 156.74 4,847.20 546.21 126.32 

8 23 Alberni-Clayoquot D 2,027 1,403.82 2,016 0.00109 2,034 23,385.54 2,635.20 756.20 23,385.54 2,635.20 609.46 

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8 23 Alberni-Clayoquot E 2,822 22.01 2,779 0.00308 2,848 32,751.69 3,690.63 1,059.06 32,751.69 3,690.63 853.55 

8 23 Alberni-Clayoquot F 1,882 186.55 1,892 -0.00106 1,876 21,573.19 2,430.98 697.59 21,573.19 2,430.98 562.22 

8 25 Campbell River 29,572 143.48 28,276 0.00900 30,378 349,328.47 39,364.16 11,295.93 349,328.47 39,364.16 9,103.94 

8 25 Comox 12,136 15.16 11,391 0.01275 12,606 144,963.76 16,335.28 4,687.56 144,963.76 16,335.28 3,777.94 

8 25 Courtenay 21,940 26.68 19,166 0.02740 23,794 273,612.13 30,832.05 8,847.55 273,612.13 30,832.05 7,130.67 

8 25 Cumberland 2,762 29.13 2,633 0.00961 2,842 32,686.09 3,683.24 1,056.94 32,686.09 3,683.24 851.84 

8 25 Gold River 1,362 10.51 1,359 0.00044 1,364 15,682.94 1,767.24 507.13 15,682.94 1,767.24 408.72 

8 25 Sayward 341 4.72 379 -0.02091 320 3,680.43 414.73 119.01 3,680.43 414.73 95.92 

8 25 Tahsis 366 5.73 600 -0.09413 272 3,128.63 352.55 101.17 3,128.63 352.55 81.54 

8 25 Zeballos 189 1.45 224 -0.03341 171 1,962.75 221.17 63.47 1,962.75 221.17 51.15 

8 25 Comox-Strathcona A 4,885 413.64 4,748 0.00571 4,969 57,141.62 6,439.02 1,847.74 57,141.62 6,439.02 1,489.18 

8 25 Comox-Strathcona B 7,219 57.66 7,013 0.00581 7,345 84,468.86 9,518.39 2,731.39 84,468.86 9,518.39 2,201.36 

8 25 Comox-Strathcona C 7,441 1,058.83 7,448 -0.00019 7,437 85,518.87 9,636.71 2,765.35 85,518.87 9,636.71 2,228.73 

8 25 Comox-Strathcona D 4,984 1,611.81 4,920 0.00259 5,023 57,759.24 6,508.61 1,867.71 57,759.24 6,508.61 1,505.28 

8 25 Comox-Strathcona G 74 5,104.75 66 0.02315 79 911.42 102.70 29.47 911.42 102.70 23.75 

8 25 Comox-Strathcona H 755 2,024.49 785 -0.00776 738 8,481.43 955.73 274.26 8,481.43 955.73 221.04 

8 25 Comox-Strathcona I 1,042 135.44 938 0.02125 1,110 12,762.69 1,438.17 412.70 12,762.69 1,438.17 332.61 

8 25 Comox-Strathcona J 2,472 9,271.11 2,548 -0.00604 2,427 27,914.74 3,145.58 902.65 27,914.74 3,145.58 727.49 

8 25 Comox-Strathcona K 2,169 80.95 1,982 0.01820 2,290 26,328.66 2,966.85 851.37 26,328.66 2,966.85 686.16 

8 15 Bowen Island 3,362 49.94 2,957 0.02600 3,631 41,756.22 4,705.31 1,350.23 41,756.22 4,705.31 1,088.22 

8 43 Alert Bay 556 1.78 583 -0.00944 540 6,214.33 700.26 200.95 6,214.33 700.26 161.95 

8 43 Port Alice 821 7.65 1,126 -0.06123 679 7,810.91 880.17 252.57 7,810.91 880.17 203.56 

8 43 Port Hardy 3,822 40.81 4,574 -0.03529 3,432 39,460.54 4,446.62 1,276.00 39,460.54 4,446.62 1,028.39 

8 43 Port McNeill 2,623 7.74 2,821 -0.01445 2,511 28,874.27 3,253.70 933.68 28,874.27 3,253.70 752.50 

8 43 Mount Waddington B 150 2,593.54 169 -0.02357 140 1,605.79 180.95 51.93 1,605.79 180.95 41.85 

8 43 Mount Waddington C 736 1,509.91 829 -0.02352 685 7,880.38 888.00 254.82 7,880.38 888.00 205.37 

8 43 Mount Waddington D 304 3,343.23 401 -0.05388 257 2,960.65 333.62 95.74 2,960.65 333.62 77.16 

8 21 Lantzville 3,661 27.87 3,653 0.00044 3,666 42,154.64 4,750.21 1,363.12 42,154.64 4,750.21 1,098.60 

8 21 Parksville 10,993 14.6 10,323 0.01266 11,416 131,273.80 14,792.62 4,244.88 131,273.80 14,792.62 3,421.16 

8 21 Qualicum Beach 8,502 18 7,849 0.01611 8,920 102,570.11 11,558.14 3,316.72 102,570.11 11,558.14 2,673.11 

8 21 Nanaimo E 5,462 75.11 4,820 0.02532 5,888 67,703.35 7,629.17 2,189.26 67,703.35 7,629.17 1,764.43 

8 21 Nanaimo F 6,680 263.44 5,546 0.03791 7,469 85,887.52 9,678.26 2,777.27 85,887.52 9,678.26 2,238.34 

8 21 Nanaimo G 7,023 48.88 6,113 0.02814 7,633 87,772.66 9,890.68 2,838.23 87,772.66 9,890.68 2,287.47 

8 21 Nanaimo H 3,474 277.52 3,108 0.02252 3,714 42,708.54 4,812.62 1,381.03 42,708.54 4,812.62 1,113.04 

9 51 Burns Lake 2,107 7.17 1,947 0.01592 2,209 32,433.11 3,776.68 911.94 32,433.11 3,776.68 734.98 

9 51 Fort St. James 1,355 22.1 1,927 -0.06801 1,097 16,103.44 1,875.17 452.79 16,103.44 1,875.17 364.93 

9 51 Fraser Lake 1,113 3.9 1,268 -0.02574 1,029 15,110.04 1,759.49 424.86 15,110.04 1,759.49 342.41 

9 51 Granisle 364 40.21 353 0.00616 371 5,443.05 633.82 153.05 5,443.05 633.82 123.35 

9 51 Houston 3,163 72.83 3,577 -0.02430 2,938 43,131.27 5,022.43 1,212.75 43,131.27 5,022.43 977.41 

9 51 Smithers 5,217 15.69 5,414 -0.00739 5,102 74,904.39 8,722.25 2,106.13 74,904.39 8,722.25 1,697.43 

9 51 Telkwa 1,295 6.56 1,371 -0.01134 1,251 18,371.90 2,139.32 516.57 18,371.90 2,139.32 416.33 

9 51 Bulkley-Nechako A 5,290 3,688.00 5,696 -0.01468 5,060 74,290.28 8,650.74 2,088.86 74,290.28 8,650.74 1,683.52 

9 51 Bulkley-Nechako B 2,154 3,628.08 2,277 -0.01104 2,083 30,585.83 3,561.57 860.00 30,585.83 3,561.57 693.12 

9 51 Bulkley-Nechako C 1,355 25,663.24 1,688 -0.04300 1,188 17,435.09 2,030.23 490.23 17,435.09 2,030.23 395.10 

9 51 Bulkley-Nechako D 1,665 4,382.94 1,715 -0.00590 1,636 24,013.15 2,796.21 675.19 24,013.15 2,796.21 544.17 

9 51 Bulkley-Nechako E 1,788 15,912.95 1,750 0.00431 1,811 26,589.50 3,096.22 747.63 26,589.50 3,096.22 602.55 

9 51 Bulkley-Nechako G 1,059 14,439.62 1,099 -0.00739 1,036 15,204.77 1,770.52 427.52 15,204.77 1,770.52 344.56 

9 49 Aiyansh (Kitladamas) 1 0 13.37 0 0.00000 0 0.00 0.00 0.00 0.00 0.00 0.00 

9 49 Gingolx 341 5.26 339 0.00118 342 5,023.80 585.00 141.26 5,023.80 585.00 113.85 

9 49 Gitwinksihlkw 201 3.01 212 -0.01060 195 2,857.97 332.80 80.36 2,857.97 332.80 64.77 

9 49 Hazelton 293 2.85 345 -0.03215 266 3,899.79 454.11 109.65 3,899.79 454.11 88.37 

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9 49 Kitimat 8,987 242.63 10,285 -0.02662 8,288 121,676.28 14,168.61 3,421.24 121,676.28 14,168.61 2,757.35 

9 49 Laxgalts'ap 474 17.62 467 0.00298 478 7,021.02 817.56 197.41 7,021.02 817.56 159.11 

9 49 New Hazelton 627 25.64 750 -0.03519 563 8,266.78 962.63 232.44 8,266.78 962.63 187.34 

9 49 Nisga'a 97 1,946.27 85 0.02676 105 1,541.45 179.49 43.34 1,541.45 179.49 34.93 

9 49 Terrace 11,320 41.52 12,109 -0.01339 10,871 159,600.49 18,584.70 4,487.58 159,600.49 18,584.70 3,616.76 

9 49 Kitimat-Stikine B 1,618 7,464.34 1,948 -0.03644 1,447 21,249.91 2,474.45 597.50 21,249.91 2,474.45 481.55 

9 49 Kitimat-Stikine C (Part 1) 2,822 9,679.06 2,998 -0.01203 2,721 39,951.87 4,652.20 1,123.35 39,951.87 4,652.20 905.36 

9 49 Kitimat-Stikine C (Part 2) 5 18,101.81 10 -0.12945 3 48.43 5.64 1.36 48.43 5.64 1.10 

9 49 Kitimat-Stikine E 4,002 16.39 4,475 -0.02209 3,743 54,943.01 6,397.84 1,544.86 54,943.01 6,397.84 1,245.08 

9 47 Port Edward 577 168.12 659 -0.02623 533 7,821.59 910.79 219.92 7,821.59 910.79 177.25 

9 47 Prince Rupert 12,815 54.9 14,643 -0.02632 11,830 173,666.74 20,222.64 4,883.09 173,666.74 20,222.64 3,935.52 

9 47 Skeena-Queen Charlotte A 52 2,930.73 91 -0.10589 37 545.66 63.54 15.34 545.66 63.54 12.37 

9 47 Skeena-Queen Charlotte C 37 6,514.17 50 -0.05844 31 453.40 52.80 12.75 453.40 52.80 10.27 

10 41 Cariboo J 808 25,948.44 880 -0.01693 768 12,981.37 1,090.20 236.15 12,981.37 1,090.20 190.32 

10 45 Central Coast A 138 19,876.88 143 -0.00709 135 2,284.32 191.84 41.55 2,284.32 191.84 33.49 

10 45 Central Coast C 556 3,987.48 697 -0.04420 485 8,209.79 689.48 149.35 8,209.79 689.48 120.36 

10 45 Central Coast D 421 304.14 516 -0.03988 373 6,301.06 529.18 114.62 6,301.06 529.18 92.38 

10 45 Central Coast E 135 360.18 167 -0.04165 119 2,009.35 168.75 36.55 2,009.35 168.75 29.46 

10 43 Mount Waddington A 1,051 12,737.46 886 0.03475 1,164 19,690.47 1,653.65 358.19 19,690.47 1,653.65 288.68 

10 27 Powell River 12,957 29.77 12,983 -0.00040 12,941 218,843.69 18,378.95 3,981.01 218,843.69 18,378.95 3,208.49 

10 27 Sechelt (Part) 17 0.24 36 -0.13934 11 183.27 15.39 3.33 183.27 15.39 2.69 

10 27 Powell River A 914 3,898.07 988 -0.01545 872 14,750.67 1,238.79 268.33 14,750.67 1,238.79 216.26 

10 27 Powell River B 1,489 130.52 1,450 0.00532 1,513 25,583.66 2,148.57 465.40 25,583.66 2,148.57 375.08 

10 27 Powell River C 2,074 642.34 2,135 -0.00578 2,038 34,467.30 2,894.64 627.00 34,467.30 2,894.64 505.33 

10 27 Powell River D 1,107 300.44 1,129 -0.00393 1,094 18,500.00 1,553.67 336.54 18,500.00 1,553.67 271.23 

10 27 Powell River E 359 73.57 367 -0.00440 354 5,991.06 503.14 108.98 5,991.06 503.14 87.84 

11 47 Masset 940 19.45 926 0.00301 949 171.35 1,096.68 990.35 171.35 1,096.68 798.17 

11 47 Port Clements 440 13.59 516 -0.03136 400 72.24 462.35 417.53 72.24 462.35 336.51 

11 47 Queen Charlotte 948 37.28 1,045 -0.01929 894 161.54 1,033.87 933.63 161.54 1,033.87 752.46 

11 47 Skeena-Queen Charlotte D 607 6,534.37 538 0.02443 653 117.89 754.52 681.37 117.89 754.52 549.15 

11 47 Skeena-Queen Charlotte E 402 3,432.42 460 -0.02659 371 66.98 428.69 387.13 66.98 428.69 312.01 

Notes: (1) Strathcona and Comox Valley RDs were combined for 2006 census, named 'Comox-Strathcona RD'. Comox Valley RD (25) used. 

(2) Upon publication of 2011 census data on the Statistics Canada website, retrieve and insert 2011 population data in this column. 

(3) Upon publication of 2011 census data on the Statistics Canada website, retrieve and insert 2006 population data in this column. 

(4) Includes containers ineligible for recycling collected under the program. As antifreeze containers become eligible in 2011, there will be less containers ineligible for recycling 

Source: 2006 Census, Statistics Canada, Ottawa 

Prepared by: BC Stats, Ministry of Labour and Citizens' Services, Victoria 

Page 7 of 7

CRA 071620 (2) 

TABLE 3.2 

TRANSPORTATION COMPONENTS OF USED OIL, FILTERS, AND CONTAINERS 


BCUOMA 

1 2 3 4 5 6 7 8 9 10 11 

Zone 


Destination % (1) 

Amount (L) Company Address City Prov./State % (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

Reference Sheet 

Registered Re-refinery 55.00% 24,500,300.00 Newalta 130 Forester Street North Vancouver BC 43.37% 43.37% 43.37% 43.37% 43.37% 43.37% 43.37% 43.37% 43.37% 43.37% 43.37% 'Processor, Pulp, Asph. Dist.' 

(1st trip) Safety Kleen 230-300 Regional Road 17 Breslau ON 11.63% 11.63% 11.63% 11.63% 11.63% 11.63% 11.63% 11.63% 11.63% 11.63% 11.63% 'Processor, Pulp, Asph. Dist.' 

Pulp Mill 22.50% 10,022,850.00 Domtar 2005 Mission Flats Road Kamloops BC 4.28% 4.28% 4.28% 4.28% 4.28% 4.28% 4.28% 4.28% 4.28% 4.28% 4.28% 'Processor, Pulp, Asph. Dist.' 

(1st trip) Georgia Pacific NE 4th and Adams Camas WA 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 'Processor, Pulp, Asph. Dist.' 

Weyerhaueser 3401 Industrial Way Longview WA 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 'Processor, Pulp, Asph. Dist.' 

Simpson 801 Portland Avenue Tacoma WA 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 6.08% 'Processor, Pulp, Asph. Dist.' 

Asphalt Plant 22.50% 10,022,850.00 Lafarge 6757 Otway Road Prince George BC 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 'Processor, Pulp, Asph. Dist.' 

(1st trip) Lafarge 13340 Mitchell Road Richmond BC 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 'Processor, Pulp, Asph. Dist.' 


South Rock 3800-4294 Box Springs Rd NW Medicine Hat AB 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 7.50% 'Processor, Pulp, Asph. Dist.' 


Amount (#) Company Address City Prov./State % (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 


Registered Processor 100.00% 5,190,000.00 M&R Environmental 4623 Byrne Road Burnaby BC 54.07% 0.00% 0.00% 3.68% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 'Processor, Pulp, Asph. Dist.' 

(1st trip) Clean Harbors Canada Inc. 7842 Progress Way Delta BC 15.31% 33.33% 33.33% 32.11% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 'Processor, Pulp, Asph. Dist.' 

Heatherington Industries Ltd. 4715 Roger Street Port Alberni BC 15.31% 33.33% 33.33% 32.11% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 'Processor, Pulp, Asph. Dist.' 

Enviro West 4208 - 84th Avenue NW Edmonton AB 15.31% 33.33% 33.33% 32.11% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 'Processor, Pulp, Asph. Dist.' 

Steel Broker 95.38% 4,950,216.03 ABC Recycling 8081 Meadow Avenue Burnaby BC 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 'Steel, Plastics, Incin. Dist.' 

(2nd trip) General Recycling Industries 4120 – 84 Avenue Edmonton AB 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 'Steel, Plastics, Incin. Dist.' 

Steel Mill 95.38% 4,950,216.03 Alta Steel 9401 - 34 Street Edmonton AB 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 'Steel, Plastics, Incin. Dist.' 

(3rd trip) Tenaris Prudential Steel Ltd. 8919 Barlow Trail S. E. Calgary AB 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 47.69% 'Steel, Plastics, Incin. Dist.' 

Incinerator 

(2nd trip) 


4.62% 239,783.97 Metro Vancouver (GRVD) 5279 Thorn St Burnaby BC 4.33% 0.00% 0.00% 0.29% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 'Steel, Plastics, Incin. Dist.' 


Amount (kg) Company Address City Prov./State % (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

% (2) 

Facility 


Registered Processor 100.00% 1,155,257.36 M&R Environmental 4623 Byrne Road Burnaby BC 79.61% 0.00% 0.00% 4.32% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 0.00% 'Processor, Pulp, Asph. Dist.' 

(1st trip) Merlin Plastics Supply Inc. #9 - 7483 Progress Way Burnaby BC 21.59% 100.00% 26.98% 62.25% 0.00% 0.00% 50.54% 30.77% 62.31% 0.00% 0.00% 'Processor, Pulp, Asph. Dist.' 

Precision Plastics 9620-27 Avenue Edmonton AB 0.00% 0.00% 73.02% 33.43% 100.00% 100.00% 49.46% 69.23% 37.69% 100.00% 100.00% 'Processor, Pulp, Asph. Dist.' 

Plastics Manufacturer 100.00% 1,155,257.36 Newton Industries 20215 - 102 Ave. Langley BC 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 'Steel, Plastics, Incin. Dist.' 

(2nd trip) Advance Plastics Inc. #2-7315 Meadow Ave. Burnaby BC 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 'Steel, Plastics, Incin. Dist.' 

PlasticsPlus Ltd. 12948 - 148 Street Edmonton AB 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 33.33% 'Steel, Plastics, Incin. Dist.' 

Notes: 

(1) Percentage of total amount of material going to particular type of processor. Based on figures provided by BCUOMA, and assuming all materials end up at one of the destinations indicated. Percentages can be updated as necessary, and must add up to 100% for each Zone. Refer to note (3) 

regarding the addition of another facility. 

(2) Percentage of total amount of material going to particular facility. Based on figures provided by BCUOMA, and assuming even distribution to facilities of the same type, and that all materials end up at one of the destinations indicated. Percentages can be updated as necessary, and must add up 

to 100% for each Zone. Refer to note (3) regarding the addition of another facility. 

(3) To add a facility, the following steps must be taken: 

- insert facility information as a new row, grouped with appropriate similar facilities 

- update percentages in columns H-R accordingly, to sum up to 100% down each column for all facilities of the same type. 

- insert the facility into the appropriate distances sheet (ie. if it is a Registered Processor (1st trip), add into the "1st Trip Facility Dist." table.) 

- determine the distances to the new facility and insert in appropriate cells in the distances sheet. 

- update the "Distances" for each affected Registered Processor/Facility route column in the "Destination Distances" sheet. This must be done by inserting another set of product formulae (including HLOOKUP functions) with the appropriate cells called. 

- update the row numbers in the new HLOOKUP functions so that the appropriate facilities are called for each calculation. 

Page 1 of 1

TABLE 3.3 

PROJECT - DESTINATION DISTANCES 


BCUOMA 

BCUOMA Regional 2006 Area Generator Distance Diesel Distance Diesel Distance Diesel Distance Diesel Distance Diesel Distance Diesel Distance Diesel Distance Diesel Distance Diesel Distance Diesel Distance Diesel Distance Diesel 


Name km 2 

Location (2) 

Zone RD Location (3) 

(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed (L) (km) (5) 

Consumed 

(L) Zone RD Location (3) 

(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 




Registered Collector Registered Processor Pulp Mills & Asphalt Plants Rail Travel Registered Collector 

Registered Processor Steel Broker Steel Mill 

Incinerator Registered Collector 

Registered Processor Plastics Manufacturer 

Consumed 

(L) 

1 9 Abbotsford 359.36 Abbotsford 1 15 Surrey 57.5 1883.1 20.2 292.7 235.3 3402.0 503.8 89.2 1 15 Surrey 57.5 68.5 224.3 143.5 583.5 311.2 560.3 298.8 0.2 0.1 1 15 Surrey 57.5 20.2 22.5 4.2 397.6 43.2 

1 9 Chilliwack 260.19 Chilliwack 1 15 Surrey 83.6 1558.7 20.2 166.6 235.3 1936.8 503.8 50.8 1 15 Surrey 83.6 56.7 224.3 81.7 583.5 177.2 560.3 170.1 0.2 0.1 1 15 Surrey 83.6 16.7 22.5 2.4 397.6 24.6 

1 9 Harrison Hot Springs 5.47 Harrison Hot Springs 1 15 Surrey 109.0 47.8 20.2 3.9 235.3 45.5 503.8 1.2 1 15 Surrey 109.0 1.7 224.3 1.9 583.5 4.2 560.3 4.0 0.2 0.0 1 15 Surrey 109.0 0.5 22.5 0.1 397.6 0.6 

1 9 Hope41.42 Hope 1 15 Surrey 139.0 218.0 20.2 14.0 235.3 162.9 503.8 4.3 1 15 Surrey 139.0 7.9 224.3 6.9 583.5 14.9 560.3 14.3 0.2 0.0 1 15 Surrey 139.0 2.3 22.5 0.2 397.6 2.1 

1 9 Kent 166.51 Kent 1 15 Surrey 104.0 122.0 20.2 10.5 235.3 121.9 503.8 3.2 1 15 Surrey 104.0 4.4 224.3 5.1 583.5 11.2 560.3 10.7 0.2 0.0 1 15 Surrey 104.0 1.3 22.5 0.2 397.6 1.5 

1 9 Mission 225.78 Mission 1 15 Surrey 54.2 503.0 20.2 82.9 235.3 964.0 503.8 25.3 1 15 Surrey 54.2 18.3 224.3 40.7 583.5 88.2 560.3 84.7 0.2 0.0 1 15 Surrey 54.2 5.4 22.5 1.2 397.6 12.2 

1 9 Fraser Valley B 3,089.46 Hope 1 15 Surrey 139.0 29.2 20.2 1.9 235.3 21.8 503.8 0.6 1 15 Surrey 139.0 1.1 224.3 0.9 583.5 2.0 560.3 1.9 0.2 0.0 1 15 Surrey 139.0 0.3 22.5 0.0 397.6 0.3 

1 9 Fraser Valley C 3,669.93 Kent 1 15 Surrey 104.0 29.8 20.2 2.6 235.3 29.7 503.8 0.8 1 15 Surrey 104.0 1.1 224.3 1.3 583.5 2.7 560.3 2.6 0.2 0.0 1 15 Surrey 104.0 0.3 22.5 0.0 397.6 0.4 

1 9 Fraser Valley D 222.05 Kent 1 15 Surrey 104.0 39.2 20.2 3.4 235.3 39.1 503.8 1.0 1 15 Surrey 104.0 1.4 224.3 1.7 583.5 3.6 560.3 3.4 0.2 0.0 1 15 Surrey 104.0 0.4 22.5 0.0 397.6 0.5 

1 9 Fraser Valley E 750.52 Chilliwack 1 15 Surrey 83.6 74.8 20.2 8.0 235.3 93.0 503.8 2.4 1 15 Surrey 83.6 2.7 224.3 3.9 583.5 8.5 560.3 8.2 0.2 0.0 1 15 Surrey 83.6 0.8 22.5 0.1 397.6 1.2 

1 9 Fraser Valley F 2,029.70 Mission 1 15 Surrey 54.2 19.3 20.2 3.2 235.3 37.0 503.8 1.0 1 15 Surrey 54.2 0.7 224.3 1.6 583.5 3.4 560.3 3.2 0.2 0.0 1 15 Surrey 54.2 0.2 22.5 0.0 397.6 0.5 

1 9 Fraser Valley G 74.97 Mission 1 15 Surrey 54.2 27.0 20.2 4.5 235.3 51.8 503.8 1.4 1 15 Surrey 54.2 1.0 224.3 2.2 583.5 4.7 560.3 4.6 0.2 0.0 1 15 Surrey 54.2 0.3 22.5 0.1 397.6 0.7 

1 9 Fraser Valley H 36.86 Abbotsford 1 15 Surrey 57.5 6.1 20.2 0.9 235.3 11.0 503.8 0.3 1 15 Surrey 57.5 0.2 224.3 0.5 583.5 1.0 560.3 1.0 0.2 0.0 1 15 Surrey 57.5 0.1 22.5 0.0 397.6 0.1 

1 15 Anmore 27.42 Anmore 1 15 Burnaby 22.4 12.0 8.9 2.1 239.9 56.8 503.8 1.5 1 15 Burnaby 22.4 0.4 209.1 2.2 583.5 5.1 560.3 4.9 0.2 0.0 1 15 Burnaby 22.4 0.1 2.1 0.0 397.6 0.7 

1 15 Belcarra 5.46 Belcarra 1 15 Burnaby 26.5 4.5 8.9 0.7 239.9 18.1 503.8 0.5 1 15 Burnaby 26.5 0.2 209.1 0.7 583.5 1.6 560.3 1.6 0.2 0.0 1 15 Burnaby 26.5 0.0 2.1 0.0 397.6 0.2 

1 15 Burnaby 89.12 Burnaby 1 15 Burnaby 2.7 140.6 8.9 208.2 239.9 5592.1 503.8 143.9 1 15 Burnaby 2.7 5.1 209.1 215.7 583.5 501.9 560.3 481.9 0.2 0.2 1 15 Burnaby 2.7 1.5 2.1 0.6 397.6 69.7 

1 15 Coquitlam 121.69 Coquitlam 1 15 Burnaby 24.0 703.3 8.9 115.5 239.9 3103.0 503.8 79.8 1 15 Burnaby 24.0 25.6 209.1 119.7 583.5 278.5 560.3 267.4 0.2 0.1 1 15 Burnaby 24.0 7.6 2.1 0.4 397.6 38.7 

1 15 Delta 183.70 Delta 1 15 Delta 3.8 93.6 14.6 158.0 240.7 2601.6 503.8 66.7 1 15 Delta 3.8 3.4 218.4 104.5 583.5 232.7 560.3 223.4 0.2 0.1 1 15 Surrey 5.0 1.3 22.5 3.2 397.6 32.3 

1 15 Langley (1) 306.93 Langley (1) 1 15 Surrey 20.0 497.3 20.2 222.2 235.3 2583.0 503.8 67.8 1 15 Surrey 20.0 18.1 224.3 109.0 583.5 236.3 560.3 226.9 0.2 0.1 1 15 Surrey 20.0 5.3 22.5 3.2 397.6 32.8 

1 15 Langley (2) 10.22 Langley (2) 1 15 Surrey 20.0 119.6 20.2 53.4 235.3 621.1 503.8 16.3 1 15 Surrey 20.0 4.3 224.3 26.2 583.5 56.8 560.3 54.6 0.2 0.0 1 15 Surrey 20.0 1.3 22.5 0.8 397.6 7.9 

1 15 Lions Bay 2.55 Lions Bay 1 15 North Vancouver 29.8 9.8 5.9 0.9 240.3 34.9 503.8 0.9 1 15 Burnaby 42.7 0.5 209.1 1.3 583.5 3.1 560.3 3.0 0.2 0.0 1 15 Burnaby 42.7 0.2 2.1 0.0 397.6 0.4 

1 15 Maple Ridge 265.79 Maple Ridge 1 15 Surrey 22.5 414.5 20.2 164.7 235.3 1913.8 503.8 50.2 1 15 Surrey 22.5 15.1 224.3 80.8 583.5 175.1 560.3 168.1 0.2 0.1 1 15 Burnaby 19.6 3.9 2.1 0.2 397.6 24.3 

1 15 New Westminster 15.41 New Westminster 1 15 Burnaby 8.3 128.4 8.9 61.0 239.9 1638.1 503.8 42.1 1 15 Burnaby 8.3 4.7 209.1 63.2 583.5 147.0 560.3 141.2 0.2 0.1 1 15 Burnaby 17.0 2.8 2.1 0.2 397.6 20.4 

1 15 North Vancouver 160.67 North Vancouver 1 15 North Vancouver 3.6 75.0 5.9 54.7 240.3 2224.5 503.8 57.1 1 15 Burnaby 19.6 14.9 209.1 85.7 583.5 199.3 560.3 191.4 0.2 0.1 1 15 Burnaby 19.6 4.4 2.1 0.3 397.6 27.7 

1 15 North Vancouver 11.85 North Vancouver 1 15 North Vancouver 1.0 11.3 5.9 30.3 240.3 1232.3 503.8 31.7 1 15 Burnaby 17.0 7.2 209.1 47.5 583.5 110.4 560.3 106.0 0.2 0.0 1 15 Burnaby 17.0 2.1 2.1 0.1 397.6 15.3 

1 15 Pitt Meadows 85.38 Pitt Meadows 1 15 Surrey 25.8 106.1 20.2 36.8 235.3 427.3 503.8 11.2 1 15 Surrey 25.8 3.9 224.3 18.0 583.5 39.1 560.3 37.5 0.2 0.0 1 15 Surrey 25.8 1.1 22.5 0.5 397.6 5.4 

1 15 Port Coquitlam 28.85 Port Coquitlam 1 15 Burnaby 23.0 312.3 8.9 53.5 239.9 1438.0 503.8 37.0 1 15 Burnaby 23.0 11.4 209.1 55.5 583.5 129.1 560.3 123.9 0.2 0.0 1 15 Burnaby 23.0 3.4 2.1 0.2 397.6 17.9 

1 15 Port Moody 25.62 Port Moody 1 15 Burnaby 17.4 132.3 8.9 30.0 239.9 805.4 503.8 20.7 1 15 Burnaby 17.4 4.8 209.1 31.1 583.5 72.3 560.3 69.4 0.2 0.0 1 15 Burnaby 17.4 1.4 2.1 0.1 397.6 10.0 

1 15 Richmond 128.76 Richmond 1 15 Burnaby 23.6 1081.9 8.9 180.7 239.9 4854.6 503.8 124.9 1 15 Burnaby 23.6 39.3 209.1 187.3 583.5 435.7 560.3 418.3 0.2 0.2 1 15 Burnaby 23.6 11.6 2.1 0.6 397.6 60.5 

1 15 Surrey 317.19 Surrey 1 15 Surrey 5.0 543.0 20.2 965.9 235.3 11226.7 503.8 294.5 1 15 Surrey 5.0 19.7 224.3 473.7 583.5 1027.0 560.3 986.2 0.2 0.4 1 15 Surrey 5.0 5.8 22.5 14.0 397.6 142.6 

1 15 Vancouver 114.71 Vancouver 1 15 North Vancouver 15.0 2275.6 5.9 396.1 240.3 16092.7 503.8 413.3 1 15 Burnaby 31.0 171.0 209.1 619.8 583.5 1441.7 560.3 1384.3 0.2 0.5 1 15 Burnaby 31.0 50.5 2.1 1.8 397.6 200.1 

1 15 West Vancouver 87.13 West Vancouver 1 15 North Vancouver 22.1 238.5 5.9 28.2 240.3 1144.7 503.8 29.4 1 15 Burnaby 38.1 14.9 209.1 44.1 583.5 102.5 560.3 98.5 0.2 0.0 1 15 Burnaby 38.1 4.4 2.1 0.1 397.6 14.2 

1 15 White Rock 5.16 White Rock 1 15 Surrey 16.0 77.3 20.2 43.2 235.3 502.1 503.8 13.2 1 15 Surrey 16.0 2.8 224.3 21.2 583.5 45.9 560.3 44.1 0.2 0.0 1 15 Surrey 16.0 0.8 22.5 0.6 397.6 6.4 

1 15 Greater Vancouver A 818.62 Vancouver 1 15 North Vancouver 22.1 75.0 5.9 8.9 240.3 359.8 503.8 9.2 1 15 Burnaby 38.1 4.7 209.1 13.9 583.5 32.2 560.3 31.0 0.2 0.0 1 15 Burnaby 38.1 1.4 2.1 0.0 397.6 4.5 

2 51 Vanderhoof 54.85 Vanderhoof 2 53 Prince George 110.0 248.3 407.8 406.3 365.9 364.6 503.8 6.1 2 53 Prince George 110.0 8.5 796.7 33.1 613.1 21.2 560.3 19.4 0.0 0.0 1 15 Prince George 110.0 3.2 788.8 12.4 397.6 3.6 

2 51 Bulkley-Nechako F 5,397.05 Vanderhoof 2 53 Prince George 110.0 191.8 407.8 313.8 365.9 281.7 503.8 4.8 2 53 Prince George 110.0 6.6 796.7 25.5 613.1 16.4 560.3 15.0 0.0 0.0 1 15 Prince George 110.0 2.5 788.8 9.6 397.6 2.8 

2 41 Quesnel 35.34 Quesnel 2 53 Quesnel 1.7 8.7 341.8 782.8 346.8 794.4 503.8 14.1 2 53 Quesnel 1.7 0.3 752.3 71.8 613.1 48.7 560.3 44.5 0.0 0.0 1 15 Quesnel 1.7 0.1 667.4 24.1 397.6 8.3 

2 41 Wells 159.15 Wells 2 53 Prince George 184.0 25.3 407.8 24.8 365.9 22.2 503.8 0.4 2 53 Prince George 184.0 0.9 796.7 2.0 613.1 1.3 560.3 1.2 0.0 0.0 1 15 Prince George 184.0 0.3 788.8 0.8 397.6 0.2 

2 41 Cariboo A 783.36 Quesnel 2 53 Quesnel 7.9 25.5 341.8 486.3 346.8 493.6 503.8 8.8 2 53 Quesnel 7.9 0.9 752.3 44.6 613.1 30.3 560.3 27.7 0.0 0.0 1 15 Quesnel 7.9 0.3 667.4 15.0 397.6 5.1 

2 41 Cariboo B 1,419.74 Quesnel 2 53 Quesnel 10.6 22.2 341.8 315.6 346.8 320.3 503.8 5.7 2 53 Quesnel 10.6 0.8 752.3 28.9 613.1 19.6 560.3 18.0 0.0 0.0 1 15 Quesnel 10.6 0.3 667.4 9.7 397.6 3.3 

2 41 Cariboo C 7,392.10 Quesnel 2 53 Quesnel 24.3 15.2 341.8 94.6 346.8 96.0 503.8 1.7 2 53 Quesnel 24.3 0.5 752.3 8.7 613.1 5.9 560.3 5.4 0.0 0.0 2 53 Quesnel 24.3 0.2 661.0 2.9 395.0 1.0 

2 41 Cariboo I 11,942.85 Quesnel 2 53 Quesnel 30.8 28.6 341.8 140.2 346.8 142.3 503.8 2.5 2 53 Quesnel 30.8 1.0 752.3 12.9 613.1 8.7 560.3 8.0 0.0 0.0 2 53 Quesnel 30.8 0.4 661.0 4.3 395.0 1.5 

2 53 McBride 4.43 McBride 2 53 Prince George 211.0 77.5 407.8 66.1 365.9 59.3 503.8 1.0 2 53 Prince George 211.0 2.6 796.7 5.4 613.1 3.4 560.3 3.2 0.0 0.0 2 53 Prince George 211.0 1.0 781.0 2.0 395.0 0.6 

2 53 Prince George 316.00 Prince George 2 53 Prince George 5.0 204.6 407.8 7343.7 365.9 6590.5 503.8 111.2 2 53 Prince George 5.0 7.0 796.7 597.6 613.1 383.2 560.3 350.3 0.0 0.0 2 53 Prince George 5.0 2.6 781.0 221.9 395.0 64.5 

2 53 Valemount 4.96 Valemount 2 53 Prince George 295.0 155.0 407.8 94.6 365.9 84.9 503.8 1.4 2 53 Prince George 295.0 5.3 796.7 7.7 613.1 4.9 560.3 4.5 0.0 0.0 2 53 Prince George 295.0 2.0 781.0 2.9 395.0 0.8 

2 53 Fraser-Fort George A 1,379.17 Prince George 2 53 Prince George 10.5 19.5 407.8 334.9 365.9 300.6 503.8 5.1 2 53 Prince George 10.5 0.7 796.7 27.3 613.1 17.5 560.3 16.0 0.0 0.0 2 53 Prince George 10.5 0.3 781.0 10.1 395.0 2.9 

2 53 Fraser-Fort George C 2,818.61 Prince George 2 53 Prince George 15.0 28.2 407.8 339.3 365.9 304.5 503.8 5.1 2 53 Prince George 15.0 1.0 796.7 27.6 613.1 17.7 560.3 16.2 0.0 0.0 2 53 Prince George 15.0 0.4 781.0 10.3 395.0 3.0 

2 53 Fraser-Fort George D 669.19 Prince George 2 53 Prince George 7.3 18.1 407.8 446.5 365.9 400.7 503.8 6.8 2 53 Prince George 7.3 0.6 796.7 36.3 613.1 23.3 560.3 21.3 0.0 0.0 2 53 Prince George 7.3 0.2 781.0 13.5 395.0 3.9 

2 53 Fraser-Fort George E 617.91 Prince George 2 53 Prince George 7.0 1.9 407.8 49.0 365.9 44.0 503.8 0.7 2 53 Prince George 7.0 0.1 796.7 4.0 613.1 2.6 560.3 2.3 0.0 0.0 2 53 Prince George 7.0 0.0 781.0 1.5 395.0 0.4 

2 53 Fraser-Fort George F 12,541.44 Prince George 2 53 Prince George 31.6 22.3 407.8 127.0 365.9 114.0 503.8 1.9 2 53 Prince George 31.6 0.8 796.7 10.3 613.1 6.6 560.3 6.1 0.0 0.0 2 53 Prince George 31.6 0.3 781.0 3.8 395.0 1.1 

2 53 Fraser-Fort George G 17,200.43 Mackenzie 2 53 Prince George 182.0 30.6 407.8 30.2 365.9 27.1 503.8 0.5 2 53 Prince George 182.0 1.0 796.7 2.5 613.1 1.6 560.3 1.4 0.0 0.0 2 53 Prince George 182.0 0.4 781.0 0.9 395.0 0.3 

2 53 Fraser-Fort George H 14,978.96 McBride 2 53 Prince George 211.0 221.2 407.8 188.7 365.9 169.3 503.8 2.9 2 53 Prince George 211.0 7.6 796.7 15.4 613.1 9.8 560.3 9.0 0.0 0.0 2 53 Prince George 211.0 2.9 781.0 5.7 395.0 1.7 

3 53 Mackenzie 159.09 Mackenzie 2 53 Prince George 182.0 1017.8 407.8 1006.5 365.9 903.3 503.8 15.2 2 53 Prince George 182.0 17.1 796.7 40.2 613.1 25.8 560.3 23.6 0.0 0.0 2 53 Prince George 182.0 6.8 781.0 15.6 395.0 4.5 

3 55 Chetwynd 64.32 Chetwynd 3 55 Fort St. John 135.0 480.1 647.0 1015.7 541.1 849.5 503.8 9.7 3 55 Fort St. John 135.0 8.1 1,061.0 34.1 613.1 16.4 560.3 15.0 0.0 0.0 3 55 Fort St. John 135.0 3.2 820.5 10.4 669.4 4.9 

3 55 Dawson Creek 22.32 Dawson Creek 3 55 Fort St. John 75.4 1123.6 647.0 4256.2 541.1 3559.7 503.8 40.6 3 55 Fort St. John 75.4 18.9 1,061.0 142.7 613.1 68.7 560.3 62.8 0.0 0.0 3 55 Fort St. John 75.4 7.5 820.5 43.6 669.4 20.5 

3 55 Fort St. John 22.74 Fort St. John 3 55 Fort St. John 1.3 32.9 647.0 6978.6 541.1 5836.6 503.8 66.6 3 55 Fort St. John 1.3 0.6 1,061.0 234.1 613.1 112.7 560.3 103.0 0.0 0.0 3 55 Fort St. John 1.3 0.2 820.5 71.5 669.4 33.5 

3 55 Hudson's Hope 869.43 Hudson's Hope 3 55 Fort St. John 88.0 117.3 647.0 380.6 541.1 318.3 503.8 3.6 3 55 Fort St. John 88.0 2.0 1,061.0 12.8 613.1 6.1 560.3 5.6 0.0 0.0 3 55 Fort St. John 88.0 0.8 820.5 3.9 669.4 1.8 

3 55 Ingenika Point 5.43 Prince George 2 53 Prince George 0.7 0.0 407.8 0.0 365.9 0.0 503.8 0.0 2 53 Prince George 0.7 0.0 796.7 0.0 613.1 0.0 560.3 0.0 0.0 0.0 2 53 Prince George 0.7 0.0 781.0 0.0 395.0 0.0 

3 55 Pouce Coupe 2.06 Pouce Coupe 3 55 Fort St. John 85.4 78.6 647.0 262.8 541.1 219.8 503.8 2.5 3 55 Fort St. John 85.4 1.3 1,061.0 8.8 613.1 4.2 560.3 3.9 0.0 0.0 3 55 Fort St. John 85.4 0.5 820.5 2.7 669.4 1.3 

3 55 Taylor 16.61 Taylor 3 55 Fort St. John 17.3 35.9 647.0 593.1 541.1 496.0 503.8 5.7 3 55 Fort St. John 17.3 0.6 1,061.0 19.9 613.1 9.6 560.3 8.8 0.0 0.0 3 55 Fort St. John 17.3 0.2 820.5 6.1 669.4 2.8 

3 55 Tumbler Ridge 1,574.45 Tumbler Ridge 3 55 Fort St. John 169.0 657.0 647.0 1110.4 541.1 928.7 503.8 10.6 3 55 Fort St. John 169.0 11.0 1,061.0 37.2 613.1 17.9 560.3 16.4 0.0 0.0 3 55 Fort St. John 169.0 4.4 820.5 11.4 669.4 5.3 

3 55 Peace River B 86,211.91 Fort St. John 3 55 Fort St. John 82.8 652.6 647.0 2250.4 541.1 1882.1 503.8 21.5 3 55 Fort St. John 82.8 11.0 1,061.0 75.5 613.1 36.3 560.3 33.2 0.0 0.0 3 55 Fort St. John 82.8 4.3 820.5 23.1 669.4 10.8 

3 55 Peace River C 582.49 Fort St. John 3 55 Fort St. John 6.8 61.0 647.0 2558.1 541.1 2139.5 503.8 24.4 3 55 Fort St. John 6.8 1.0 1,061.0 85.8 613.1 41.3 560.3 37.8 0.0 0.0 3 55 Fort St. John 6.8 0.4 820.5 26.2 669.4 12.3 

3 55 Peace River D 11,670.10 Dawson Creek 3 55 Fort St. John 75.4 573.4 647.0 2172.0 541.1 1816.6 503.8 20.7 3 55 Fort St. John 75.4 9.6 1,061.0 72.8 613.1 35.1 560.3 32.1 0.0 0.0 3 55 Fort St. John 75.4 3.8 820.5 22.3 669.4 10.4 

3 55 Peace River E 16,593.72 Dawson Creek 3 55 Fort St. John 75.4 299.2 647.0 1133.2 541.1 947.8 503.8 10.8 3 55 Fort St. John 75.4 5.0 1,061.0 38.0 613.1 18.3 560.3 16.7 0.0 0.0 3 55 Fort St. John 75.4 2.0 820.5 11.6 669.4 5.4 

CRA 071620 (2) 

Page 1 of 6

TABLE 3.3 



BCUOMA 



Name km 2 

Location (2) 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 


Consumed 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 








Consumed 

(L) 

CRA 071620 (2) 

4 9 Fraser Valley A 2,335.28 Lytton 4 33 Kamloops 169.0 25.8 195.0 13.1 260.7 17.6 503.8 0.4 4 33 Kamloops 169.0 0.9 555.8 1.7 611.1 1.5 560.3 1.4 0.0 0.0 4 33 Kamloops 169.0 0.3 505.7 0.5 520.5 0.3 

4 41 100 Mile House 51.34 100 Mile House 2 53 Prince George 332.0 239.4 407.8 129.8 365.9 116.5 503.8 2.0 2 53 Prince George 332.0 8.7 796.7 11.2 613.1 7.2 560.3 6.6 0.0 0.0 2 53 Prince George 332.0 2.7 781.0 3.4 395.0 1.0 

4 41 Williams Lake 33.11 Williams Lake 2 53 Prince George 242.0 926.7 407.8 689.3 365.9 618.6 503.8 10.4 2 53 Prince George 242.0 33.7 796.7 59.7 613.1 38.3 560.3 35.0 0.0 0.0 2 53 Prince George 242.0 10.5 781.0 18.2 395.0 5.3 

4 41 Cariboo D 856.15 Williams Lake 2 53 Prince George 242.0 259.9 407.8 193.3 365.9 173.5 503.8 2.9 2 53 Prince George 242.0 9.5 796.7 16.7 613.1 10.7 560.3 9.8 0.0 0.0 2 53 Prince George 242.0 2.9 781.0 5.1 395.0 1.5 

4 41 Cariboo E 1,744.06 Williams Lake 2 53 Prince George 242.0 365.9 407.8 272.2 365.9 244.2 503.8 4.1 2 53 Prince George 242.0 13.3 796.7 23.6 613.1 15.1 560.3 13.8 0.0 0.0 2 53 Prince George 242.0 4.1 781.0 7.2 395.0 2.1 

4 41 Cariboo F 9,775.63 Williams Lake 2 53 Prince George 242.0 359.1 407.8 267.1 365.9 239.7 503.8 4.0 2 53 Prince George 242.0 13.1 796.7 23.1 613.1 14.8 560.3 13.5 0.0 0.0 2 53 Prince George 242.0 4.1 781.0 7.0 395.0 2.0 

4 41 Cariboo G 2,678.81 100 Mile House 2 53 Prince George 332.0 600.0 407.8 325.3 365.9 291.9 503.8 4.9 2 53 Prince George 332.0 21.8 796.7 28.2 613.1 18.1 560.3 16.5 0.0 0.0 2 53 Prince George 332.0 6.8 781.0 8.6 395.0 2.5 

4 41 Cariboo H 2,603.71 100 Mile House 2 53 Prince George 332.0 204.8 407.8 111.0 365.9 99.6 503.8 1.7 2 53 Prince George 332.0 7.4 796.7 9.6 613.1 6.2 560.3 5.6 0.0 0.0 2 53 Prince George 332.0 2.3 781.0 2.9 395.0 0.9 

4 41 Cariboo K 13,650.75 Williams Lake 2 53 Prince George 242.0 43.2 407.8 32.1 365.9 28.8 503.8 0.5 2 53 Prince George 242.0 1.6 796.7 2.8 613.1 1.8 560.3 1.6 0.0 0.0 2 53 Prince George 242.0 0.5 781.0 0.8 395.0 0.2 

4 41 Cariboo L 1,268.42 100 Mile House 2 53 Prince George 332.0 526.9 407.8 285.6 365.9 256.3 503.8 4.3 2 53 Prince George 332.0 19.2 796.7 24.7 613.1 15.9 560.3 14.5 0.0 0.0 2 53 Prince George 332.0 6.0 781.0 7.5 395.0 2.2 

4 35 Kelowna 211.69 Kelowna 4 35 Kelowna 4.1 169.8 214.4 3914.3 289.0 5276.8 503.8 112.7 4 35 Kelowna 4.1 6.2 604.9 489.4 611.1 412.0 560.3 377.7 0.0 0.0 4 35 Kelowna 4.1 1.9 552.8 139.1 520.5 75.2 

4 35 Lake Country 122.16 Lake Country 4 35 Winfield 8.2 29.3 224.7 354.8 288.4 455.5 503.8 9.7 4 35 Winfield 8.2 1.1 611.7 42.8 611.1 35.6 560.3 32.7 0.0 0.0 4 35 Winfield 8.2 0.3 565.7 12.3 520.5 6.5 

4 35 Peachland 15.98 Peachland 4 35 Kelowna 28.2 51.7 214.4 173.3 289.0 233.7 503.8 5.0 4 35 Kelowna 28.2 1.9 604.9 21.7 611.1 18.2 560.3 16.7 0.0 0.0 4 35 Kelowna 28.2 0.6 552.8 6.2 520.5 3.3 

4 35 Central Okanagan 1,244.16 Kelowna 4 35 Kelowna 10.0 15.1 214.4 143.9 289.0 194.1 503.8 4.1 4 35 Kelowna 10.0 0.6 604.9 18.0 611.1 15.1 560.3 13.9 0.0 0.0 4 35 Kelowna 10.0 0.2 552.8 5.1 520.5 2.8 

4 35 Central Okanagan J 1,297.81 Kelowna 4 35 Kelowna 10.2 114.5 214.4 1066.3 289.0 1437.4 503.8 30.7 4 35 Kelowna 10.2 4.2 604.9 133.3 611.1 112.2 560.3 102.9 0.0 0.0 4 35 Kelowna 10.2 1.3 552.8 37.9 520.5 20.5 

4 39 Salmon Arm 155.36 Salmon Arm 4 33 Kamloops 110.0 662.1 195.0 518.1 260.7 692.8 503.8 16.4 4 33 Kamloops 110.0 24.1 555.8 65.4 611.1 59.9 560.3 55.0 0.0 0.0 4 33 Kamloops 110.0 7.5 505.7 18.5 520.5 10.9 

4 39 Sicamous 14.68 Sicamous 4 33 Kamloops 150.0 144.9 195.0 83.1 260.7 111.2 503.8 2.6 4 33 Kamloops 150.0 5.3 555.8 10.5 611.1 9.6 560.3 8.8 0.0 0.0 4 33 Kamloops 150.0 1.6 505.7 3.0 520.5 1.8 

4 39 Columbia-Shuswap C 506.33 Salmon Arm 4 33 Kamloops 110.0 333.4 195.0 260.9 260.7 348.9 503.8 8.3 4 33 Kamloops 110.0 12.1 555.8 32.9 611.1 30.2 560.3 27.7 0.0 0.0 4 33 Kamloops 110.0 3.8 505.7 9.3 520.5 5.5 

4 39 Columbia-Shuswap D 694.53 Salmon Arm 4 33 Kamloops 110.0 156.2 195.0 122.2 260.7 163.5 503.8 3.9 4 33 Kamloops 110.0 5.7 555.8 15.4 611.1 14.1 560.3 13.0 0.0 0.0 4 33 Kamloops 110.0 1.8 505.7 4.4 520.5 2.6 

4 39 Columbia-Shuswap E 1,542.18 Sicamous 4 33 Kamloops 150.0 84.8 195.0 48.6 260.7 65.1 503.8 1.5 4 33 Kamloops 150.0 3.1 555.8 6.1 611.1 5.6 560.3 5.2 0.0 0.0 4 33 Kamloops 150.0 1.0 505.7 1.7 520.5 1.0 

4 39 Columbia-Shuswap F 2,662.29 Chase 4 33 Kamloops 58.2 67.3 195.0 99.6 260.7 133.2 503.8 3.2 4 33 Kamloops 58.2 2.4 555.8 12.6 611.1 11.5 560.3 10.6 0.0 0.0 4 33 Kamloops 58.2 0.8 505.7 3.6 520.5 2.1 

4 37 Armstrong 5.24 Armstrong 4 35 Winfield 54.5 84.1 224.7 153.0 288.4 196.4 503.8 4.2 4 35 Winfield 54.5 3.1 611.7 18.5 611.1 15.4 560.3 14.1 0.0 0.0 4 35 Winfield 54.5 1.0 565.7 5.3 520.5 2.8 

4 37 Coldstream 67.25 Coldstream 4 35 Winfield 33.5 118.4 224.7 350.6 288.4 450.1 503.8 9.6 4 35 Winfield 33.5 4.3 611.7 42.3 611.1 35.2 560.3 32.3 0.0 0.0 4 35 Winfield 33.5 1.3 565.7 12.2 520.5 6.4 

4 37 Enderby 4.23 Enderby 4 33 Winfield 67.3 69.5 224.7 102.5 288.4 131.5 503.8 2.8 4 33 Winfield 67.3 2.5 611.7 12.4 611.1 10.3 560.3 9.4 0.0 0.0 4 33 Winfield 67.3 0.8 565.7 3.6 520.5 1.9 

4 37 Lumby 5.27 Lumby 4 35 Winfield 54.6 32.7 224.7 59.4 288.4 76.3 503.8 1.6 4 35 Winfield 54.6 1.2 611.7 7.2 611.1 6.0 560.3 5.5 0.0 0.0 4 35 Winfield 54.6 0.4 565.7 2.1 520.5 1.1 

4 37 Spallumcheen 254.90 Spallumcheen 4 35 Winfield 53.4 94.6 224.7 175.6 288.4 225.5 503.8 4.8 4 35 Winfield 53.4 3.4 611.7 21.2 611.1 17.6 560.3 16.2 0.0 0.0 4 35 Winfield 53.4 1.1 565.7 6.1 520.5 3.2 

4 37 Vernon 94.20 Vernon 4 35 Winfield 31.3 427.5 224.7 1354.5 288.4 1738.9 503.8 37.2 4 35 Winfield 31.3 15.6 611.7 163.4 611.1 136.0 560.3 124.7 0.0 0.0 4 35 Winfield 31.3 4.8 565.7 47.0 520.5 24.8 

4 37 North Okanagan B 489.15 Vernon 4 35 Winfield 31.3 37.9 224.7 120.1 288.4 154.2 503.8 3.3 4 35 Winfield 31.3 1.4 611.7 14.5 611.1 12.1 560.3 11.1 0.0 0.0 4 35 Winfield 31.3 0.4 565.7 4.2 520.5 2.2 

4 37 North Okanagan C 301.12 Vernon 4 35 Winfield 31.3 47.5 224.7 150.5 288.4 193.2 503.8 4.1 4 35 Winfield 31.3 1.7 611.7 18.2 611.1 15.1 560.3 13.9 0.0 0.0 4 35 Winfield 31.3 0.5 565.7 5.2 520.5 2.8 

4 37 North Okanagan D 1,797.09 Vernon 4 35 Winfield 31.3 32.3 224.7 102.5 288.4 131.6 503.8 2.8 4 35 Winfield 31.3 1.2 611.7 12.4 611.1 10.3 560.3 9.4 0.0 0.0 4 35 Winfield 31.3 0.4 565.7 3.6 520.5 1.9 

4 37 North Okanagan F 1,766.90 Vernon 4 35 Winfield 31.3 48.4 224.7 153.3 288.4 196.8 503.8 4.2 4 35 Winfield 31.3 1.8 611.7 18.5 611.1 15.4 560.3 14.1 0.0 0.0 4 35 Winfield 31.3 0.5 565.7 5.3 520.5 2.8 

4 7 Keremeos 2.11 Keremeos 4 35 Kelowna 115.0 56.5 214.4 46.5 289.0 62.7 503.8 1.3 4 35 Kelowna 115.0 2.1 604.9 5.8 611.1 4.9 560.3 4.5 0.0 0.0 4 35 Kelowna 115.0 0.6 552.8 1.7 520.5 0.9 

4 7 Oliver 4.95 Oliver 4 35 Kelowna 110.0 178.8 214.4 153.8 289.0 207.4 503.8 4.4 4 35 Kelowna 110.0 6.5 604.9 19.2 611.1 16.2 560.3 14.8 0.0 0.0 4 35 Kelowna 110.0 2.0 552.8 5.5 520.5 3.0 

4 7 Osoyoos 8.76 Osoyoos 4 35 Kelowna 131.0 241.1 214.4 174.1 289.0 234.8 503.8 5.0 4 35 Kelowna 131.0 8.8 604.9 21.8 611.1 18.3 560.3 16.8 0.0 0.0 4 35 Kelowna 131.0 2.7 552.8 6.2 520.5 3.3 

4 7 Penticton 42.02 Penticton 4 35 Kelowna 72.0 852.3 214.4 1120.1 289.0 1510.0 503.8 32.3 4 35 Kelowna 72.0 31.0 604.9 140.0 611.1 117.9 560.3 108.1 0.0 0.0 4 35 Kelowna 72.0 9.6 552.8 39.8 520.5 21.5 

4 7 Princeton 10.25 Princeton 4 35 Kelowna 165.0 163.5 214.4 93.7 289.0 126.4 503.8 2.7 4 35 Kelowna 165.0 5.9 604.9 11.7 611.1 9.9 560.3 9.0 0.0 0.0 4 35 Kelowna 165.0 1.8 552.8 3.3 520.5 1.8 

4 7 Summerland 73.88 Summerland 4 35 Kelowna 49.1 194.9 214.4 375.6 289.0 506.4 503.8 10.8 4 35 Kelowna 49.1 7.1 604.9 47.0 611.1 39.5 560.3 36.3 0.0 0.0 4 35 Kelowna 49.1 2.2 552.8 13.3 520.5 7.2 

4 7 Okanagan-Similkameen A 259.39 Osoyoos 4 35 Kelowna 131.0 92.4 214.4 66.8 289.0 90.0 503.8 1.9 4 35 Kelowna 131.0 3.4 604.9 8.3 611.1 7.0 560.3 6.4 0.0 0.0 4 35 Kelowna 131.0 1.0 552.8 2.4 520.5 1.3 

4 7 Okanagan-Similkameen B 238.75 Keremeos 4 35 Kelowna 115.0 44.4 214.4 36.5 289.0 49.2 503.8 1.1 4 35 Kelowna 115.0 1.6 604.9 4.6 611.1 3.8 560.3 3.5 0.0 0.0 4 35 Kelowna 115.0 0.5 552.8 1.3 520.5 0.7 

4 7 Okanagan-Similkameen C 444.10 Oliver 4 35 Kelowna 110.0 150.5 214.4 129.5 289.0 174.5 503.8 3.7 4 35 Kelowna 110.0 5.5 604.9 16.2 611.1 13.6 560.3 12.5 0.0 0.0 4 35 Kelowna 110.0 1.7 552.8 4.6 520.5 2.5 

4 7 Okanagan-Similkameen D 916.99 Penticton 4 35 Kelowna 72.0 158.6 214.4 208.4 289.0 281.0 503.8 6.0 4 35 Kelowna 72.0 5.8 604.9 26.1 611.1 21.9 560.3 20.1 0.0 0.0 4 35 Kelowna 72.0 1.8 552.8 7.4 520.5 4.0 

4 7 Okanagan-Similkameen E 491.13 Penticton 4 35 Kelowna 72.0 53.0 214.4 69.6 289.0 93.8 503.8 2.0 4 35 Kelowna 72.0 1.9 604.9 8.7 611.1 7.3 560.3 6.7 0.0 0.0 4 35 Kelowna 72.0 0.6 552.8 2.5 520.5 1.3 

4 7 Okanagan-Similkameen F 568.12 Penticton 4 35 Kelowna 72.0 53.3 214.4 70.0 289.0 94.4 503.8 2.0 4 35 Kelowna 72.0 1.9 604.9 8.8 611.1 7.4 560.3 6.8 0.0 0.0 4 35 Kelowna 72.0 0.6 552.8 2.5 520.5 1.3 

4 7 Okanagan-Similkameen G 2,119.89 Keremeos 4 35 Kelowna 115.0 103.8 214.4 85.4 289.0 115.2 503.8 2.5 4 35 Kelowna 115.0 3.8 604.9 10.7 611.1 9.0 560.3 8.2 0.0 0.0 4 35 Kelowna 115.0 1.2 552.8 3.0 520.5 1.6 

4 7 Okanagan-Similkameen H 4,815.07 Keremeos 4 35 Kelowna 115.0 99.1 214.4 81.6 289.0 110.0 503.8 2.3 4 35 Kelowna 115.0 3.6 604.9 10.2 611.1 8.6 560.3 7.9 0.0 0.0 4 35 Kelowna 115.0 1.1 552.8 2.9 520.5 1.6 

4 31 Lillooet 27.83 Lillooet 4 33 Kamloops 166.0 127.4 195.0 66.0 260.7 88.3 503.8 2.1 4 33 Kamloops 166.0 4.6 555.8 8.3 611.1 7.6 560.3 7.0 0.0 0.0 4 33 Kamloops 166.0 1.4 505.7 2.4 520.5 1.4 

4 31 Pemberton 4.45 Pemberton 1 15 North Vancouver 156.0 148.2 5.9 2.5 240.3 100.8 503.8 2.6 1 15 Burnaby 172.0 5.9 209.1 3.9 583.5 9.0 560.3 8.7 0.2 0.0 1 15 Burnaby 172.0 1.8 2.1 0.0 397.6 1.3 

4 31 Squamish 106.11 Squamish 1 15 North Vancouver 67.3 377.4 5.9 14.6 240.3 594.9 503.8 15.3 1 15 Burnaby 83.3 17.0 209.1 22.9 583.5 53.3 560.3 51.2 0.2 0.0 1 28 Burnaby 83.3 5.3 2.1 0.1 397.6 7.8 

4 31 Whistler 161.71 Whistler 1 15 North Vancouver 124.0 427.8 5.9 9.0 240.3 366.0 503.8 9.4 1 15 Burnaby 140.0 17.6 209.1 14.1 583.5 32.8 560.3 31.5 0.2 0.0 1 28 Burnaby 140.0 5.5 2.1 0.0 397.6 4.8 

4 31 Squamish-Lillooet A 3,726.67 Lillooet 4 33 Kamloops 166.0 12.0 195.0 6.2 260.7 8.3 503.8 0.2 4 33 Kamloops 166.0 0.4 555.8 0.8 611.1 0.7 560.3 0.7 0.0 0.0 4 28 Kamloops 166.0 0.1 505.7 0.2 520.5 0.1 

4 31 Squamish-Lillooet B 3,460.19 Lillooet 4 33 Kamloops 166.0 41.8 195.0 21.7 260.7 29.0 503.8 0.7 4 33 Kamloops 166.0 1.5 555.8 2.7 611.1 2.5 560.3 2.3 0.0 0.0 4 28 Kamloops 166.0 0.5 505.7 0.8 520.5 0.5 

4 31 Squamish-Lillooet C 5,606.94 Pemberton 1 15 North Vancouver 156.0 123.2 5.9 2.1 240.3 83.8 503.8 2.2 1 15 Burnaby 172.0 4.9 209.1 3.2 583.5 7.5 560.3 7.2 0.2 0.0 1 15 Burnaby 172.0 1.5 2.1 0.0 397.6 1.1 

4 31 Squamish-Lillooet D 3,117.56 Squamish 1 15 North Vancouver 67.3 22.0 5.9 0.9 240.3 34.7 503.8 0.9 1 15 Burnaby 83.3 1.0 209.1 1.3 583.5 3.1 560.3 3.0 0.2 0.0 1 15 Burnaby 83.3 0.3 2.1 0.0 397.6 0.5 

4 29 Gibsons 4.33 Roberts Creek 1 15 North Vancouver 43.1 68.4 5.9 4.1 240.3 168.5 503.8 4.3 1 15 Burnaby 60.7 3.5 209.1 6.5 583.5 15.1 560.3 14.5 0.2 0.0 1 15 Burnaby 60.7 1.1 2.1 0.0 397.6 2.2 

4 29 Sechelt 39.71 Roberts Creek 1 15 North Vancouver 59.1 191.5 5.9 8.5 240.3 343.7 503.8 8.8 1 15 Burnaby 75.1 8.9 209.1 13.2 583.5 30.8 560.3 29.6 0.2 0.0 1 15 Burnaby 75.1 2.8 2.1 0.0 397.6 4.5 

4 29 Sechelt (Part) 10.71 Roberts Creek 1 15 North Vancouver 59.1 18.2 5.9 0.8 240.3 32.7 503.8 0.8 1 15 Burnaby 75.1 0.8 209.1 1.3 583.5 2.9 560.3 2.8 0.2 0.0 1 15 Burnaby 75.1 0.3 2.1 0.0 397.6 0.4 

4 29 Sunshine Coast A 1,901.61 Roberts Creek 1 15 North Vancouver 59.1 60.0 5.9 2.7 240.3 107.7 503.8 2.8 1 15 Burnaby 75.1 2.8 209.1 4.2 583.5 9.7 560.3 9.3 0.2 0.0 1 15 Burnaby 75.1 0.9 2.1 0.0 397.6 1.4 

4 29 Sunshine Coast B 1,275.86 Roberts Creek 1 15 North Vancouver 59.1 57.9 5.9 2.6 240.3 104.0 503.8 2.7 1 15 Burnaby 75.1 2.7 209.1 4.0 583.5 9.3 560.3 9.0 0.2 0.0 1 15 Burnaby 75.1 0.8 2.1 0.0 397.6 1.4 

4 29 Sunshine Coast D 143.59 Roberts Creek 1 15 North Vancouver 59.1 74.2 5.9 3.3 240.3 133.2 503.8 3.4 1 15 Burnaby 75.1 3.4 209.1 5.1 583.5 11.9 560.3 11.5 0.2 0.0 1 15 Burnaby 75.1 1.1 2.1 0.0 397.6 1.7 

4 29 Sunshine Coast E 21.32 Roberts Creek 1 15 North Vancouver 59.1 79.8 5.9 3.5 240.3 143.3 503.8 3.7 1 15 Burnaby 75.1 3.7 209.1 5.5 583.5 12.8 560.3 12.3 0.2 0.0 1 15 Burnaby 75.1 1.1 2.1 0.0 397.6 1.9 

4 29 Sunshine Coast F 380.82 Roberts Creek 1 15 North Vancouver 59.1 51.9 5.9 2.3 240.3 93.2 503.8 2.4 1 15 Burnaby 75.1 2.4 209.1 3.6 583.5 8.4 560.3 8.0 0.2 0.0 1 15 Burnaby 75.1 0.7 2.1 0.0 397.6 1.2 

4 33 Ashcroft 51.45 Ashcroft 4 33 Kamloops 100.0 57.6 195.0 49.6 260.7 66.3 503.8 1.6 4 33 Kamloops 100.0 2.1 555.8 6.3 611.1 5.7 560.3 5.3 0.0 0.0 4 33 Kamloops 100.0 0.7 505.7 1.8 520.5 1.0 

4 33 Cache Creek 10.57 Cache Creek 4 33 Kamloops 84.0 31.4 195.0 32.2 260.7 43.0 503.8 1.0 4 33 Kamloops 84.0 1.1 555.8 4.1 611.1 3.7 560.3 3.4 0.0 0.0 4 33 Kamloops 84.0 0.4 505.7 1.1 520.5 0.7 

4 33 Chase 3.75 Chase 4 33 Kamloops 58.2 50.3 195.0 74.5 260.7 99.6 503.8 2.4 4 33 Kamloops 58.2 1.8 555.8 9.4 611.1 8.6 560.3 7.9 0.0 0.0 4 33 Kamloops 58.2 0.6 505.7 2.7 520.5 1.6 

4 33 Clinton 4.36 Clinton 4 33 Kamloops 124.0 24.8 195.0 17.2 260.7 23.0 503.8 0.5 4 33 Kamloops 124.0 0.9 555.8 2.2 611.1 2.0 560.3 1.8 0.0 0.0 4 33 Kamloops 124.0 0.3 505.7 0.6 520.5 0.4 

4 33 Kamloops 297.30 Kamloops 4 33 Kamloops 4.9 145.9 195.0 2581.8 260.7 3452.6 503.8 81.7 4 33 Kamloops 4.9 5.3 555.8 326.0 611.1 298.7 560.3 273.9 0.0 0.0 4 33 Kamloops 4.9 1.6 505.7 92.3 520.5 54.5 

4 33 Logan Lake 325.40 Logan Lake 4 33 Kamloops 58.0 45.4 195.0 67.4 260.7 90.1 503.8 2.1 4 33 Kamloops 58.0 1.7 555.8 8.5 611.1 7.8 560.3 7.2 0.0 0.0 4 33 Kamloops 58.0 0.5 505.7 2.4 520.5 1.4 

4 33 Lytton 6.71 Lytton 4 33 Kamloops 169.0 12.1 195.0 6.1 260.7 8.2 503.8 0.2 4 33 Kamloops 169.0 0.4 555.8 0.8 611.1 0.7 560.3 0.7 0.0 0.0 4 33 Kamloops 169.0 0.1 505.7 0.2 520.5 0.1 

4 33 Merritt 24.94 Merritt 4 33 Kamloops 93.3 236.2 195.0 217.9 260.7 291.4 503.8 6.9 4 33 Kamloops 93.3 8.6 555.8 27.5 611.1 25.2 560.3 23.1 0.0 0.0 4 33 Kamloops 93.3 2.7 505.7 7.8 520.5 4.6 

Page 2 of 6

TABLE 3.3 



BCUOMA 



Name km 2 

Location (2) 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 


Consumed 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 








Consumed 

(L) 

CRA 071620 (2) 

4 33 Thompson-Nicola A 7,165.26 Kamloops 4 33 Kamloops 23.9 31.5 195.0 113.7 260.7 152.0 503.8 3.6 4 33 Kamloops 23.9 1.1 555.8 14.4 611.1 13.2 560.3 12.1 0.0 0.0 4 33 Kamloops 23.9 0.4 505.7 4.1 520.5 2.4 

4 33 Thompson-Nicola B 5,137.36 Kamloops 4 33 Kamloops 20.2 1.6 195.0 7.0 260.7 9.4 503.8 0.2 4 33 Kamloops 20.2 0.1 555.8 0.9 611.1 0.8 560.3 0.7 0.0 0.0 4 33 Kamloops 20.2 0.0 505.7 0.2 520.5 0.1 

4 33 Thompson-Nicola E 6,654.33 Ashcroft 4 33 Kamloops 100.0 53.7 195.0 46.2 260.7 61.8 503.8 1.5 4 33 Kamloops 100.0 2.0 555.8 5.8 611.1 5.3 560.3 4.9 0.0 0.0 4 33 Kamloops 100.0 0.6 505.7 1.7 520.5 1.0 

4 33 Thompson-Nicola I 5,740.21 Logan Lake 4 33 Kamloops 58.0 28.5 195.0 42.3 260.7 56.5 503.8 1.3 4 33 Kamloops 58.0 1.0 555.8 5.3 611.1 4.9 560.3 4.5 0.0 0.0 4 33 Kamloops 58.0 0.3 505.7 1.5 520.5 0.9 

4 33 Thompson-Nicola J 3,297.75 Kamloops 4 33 Kamloops 16.2 9.9 195.0 52.5 260.7 70.2 503.8 1.7 4 33 Kamloops 16.2 0.4 555.8 6.6 611.1 6.1 560.3 5.6 0.0 0.0 4 33 Kamloops 16.2 0.1 505.7 1.9 520.5 1.1 

4 33 Thompson-Nicola L 1,912.79 Kamloops 4 33 Kamloops 12.3 13.7 195.0 95.9 260.7 128.2 503.8 3.0 4 33 Kamloops 12.3 0.5 555.8 12.1 611.1 11.1 560.3 10.2 0.0 0.0 4 33 Kamloops 12.3 0.2 505.7 3.4 520.5 2.0 

4 33 Thompson-Nicola M 3,837.02 Merritt 4 33 Kamloops 93.3 61.2 195.0 56.5 260.7 75.5 503.8 1.8 4 33 Kamloops 93.3 2.2 555.8 7.1 611.1 6.5 560.3 6.0 0.0 0.0 4 33 Kamloops 93.3 0.7 505.7 2.0 520.5 1.2 

4 33 Thompson-Nicola N 2,346.04 Merritt 4 33 Kamloops 93.3 31.6 195.0 29.2 260.7 39.0 503.8 0.9 4 33 Kamloops 93.3 1.2 555.8 3.7 611.1 3.4 560.3 3.1 0.0 0.0 4 33 Kamloops 93.3 0.4 505.7 1.0 520.5 0.6 

4 33 Thompson-Nicola O 5,420.16 Kamloops 4 33 Kamloops 20.8 21.4 195.0 88.5 260.7 118.4 503.8 2.8 4 33 Kamloops 20.8 0.8 555.8 11.2 611.1 10.2 560.3 9.4 0.0 0.0 4 33 Kamloops 20.8 0.2 505.7 3.2 520.5 1.9 

4 33 Thompson-Nicola P 1,591.67 Kamloops 4 33 Kamloops 11.3 17.7 195.0 135.0 260.7 180.5 503.8 4.3 4 33 Kamloops 11.3 0.6 555.8 17.0 611.1 15.6 560.3 14.3 0.0 0.0 4 33 Kamloops 11.3 0.2 505.7 4.8 520.5 2.9 

5 49 New Aiyansh 2.64 New Aiyansh 2 53 Prince George 616.0 2365.3 407.8 691.1 365.9 620.2 503.8 10.5 2 53 Prince George 616.0 34.9 796.7 24.3 613.1 15.6 560.3 14.2 0.0 0.0 2 53 Prince George 616.0 6.6 781.0 4.5 395.0 1.3 

5 49 Stewart 571.50 Stewart 2 53 Prince George 695.0 1287.5 407.8 333.4 365.9 299.2 503.8 5.0 2 53 Prince George 695.0 19.0 796.7 11.7 613.1 7.5 560.3 6.9 0.0 0.0 2 53 Prince George 695.0 3.6 781.0 2.2 395.0 0.6 

5 49 Kitimat-Stikine A 25,398.73 Stewart 2 53 Prince George 695.0 101.0 407.8 26.2 365.9 23.5 503.8 0.4 2 53 Prince George 695.0 1.5 796.7 0.9 613.1 0.6 560.3 0.5 0.0 0.0 2 53 Prince George 695.0 0.3 781.0 0.2 395.0 0.0 

5 49 Kitimat-Stikine D 28,288.47 Stewart 2 53 Prince George 695.0 286.3 407.8 74.2 365.9 66.5 503.8 1.1 2 53 Prince George 695.0 4.2 796.7 2.6 613.1 1.7 560.3 1.5 0.0 0.0 2 53 Prince George 695.0 0.8 781.0 0.5 395.0 0.1 

5 59 Fort Nelson 13.26 Fort Nelson 3 59 Fort St. John 380.0 7961.4 647.0 5983.7 541.1 5004.6 503.8 57.1 3 59 Fort St. John 380.0 117.6 1,061.0 176.5 613.1 85.0 560.3 77.7 0.0 0.0 3 59 Fort St. John 380.0 22.1 820.5 25.7 669.4 12.0 

5 59 Northern Rockies A 50,349.58 Fort Nelson 3 59 Fort St. John 380.0 1980.1 647.0 1488.2 541.1 1244.7 503.8 14.2 3 59 Fort St. John 380.0 29.2 1,061.0 43.9 613.1 21.1 560.3 19.3 0.0 0.0 3 59 Fort St. John 380.0 5.5 820.5 6.4 669.4 3.0 

5 59 Northern Rockies B 34,693.45 Fort Nelson 3 59 Fort St. John 380.0 193.5 647.0 145.5 541.1 121.7 503.8 1.4 3 59 Fort St. John 380.0 2.9 1,061.0 4.3 613.1 2.1 560.3 1.9 0.0 0.0 3 59 Fort St. John 380.0 0.5 820.5 0.6 669.4 0.3 

5 57 Good Hope Lake 0.65 Terrace 2 53 Prince George 1119.0 95.3 407.8 15.3 365.9 13.8 503.8 0.2 2 53 Prince George 1119.0 1.4 796.7 0.5 613.1 0.3 560.3 0.3 0.0 0.0 2 53 Prince George 1119.0 0.3 781.0 0.1 395.0 0.0 

5 57 Lower Post 0.18 Lower Post 2 59 Fort St. John 874.0 1012.2 647.0 330.8 541.1 276.6 503.8 3.2 2 59 Fort St. John 874.0 14.9 1,061.0 9.8 613.1 4.7 560.3 4.3 0.0 0.0 2 59 Fort St. John 874.0 2.8 1217.0 2.1 395.0 0.4 

5 57 Stikine Region 132,456.37 Smithers 2 53 Prince George 371.0 706.9 407.8 343.0 365.9 307.8 503.8 5.2 2 53 Prince George 371.0 10.4 796.7 12.1 613.1 7.7 560.3 7.1 0.0 0.0 2 53 Prince George 371.0 2.0 781.0 2.2 395.0 0.6 

6 3 Castlegar 19.80 Castlegar 6 1 Cranbrook 230.0 678.9 463.2 603.5 344.7 449.1 503.8 8.0 6 1 Cranbrook 230.0 26.6 844.0 52.5 613.1 31.8 560.3 29.0 0.0 0.0 6 1 Cranbrook 230.0 7.0 670.0 10.9 770.8 7.2 

6 3 Creston 8.48 Creston 6 1 Cranbrook 109.0 220.5 463.2 413.6 344.7 307.8 503.8 5.5 6 1 Cranbrook 109.0 8.6 844.0 36.0 613.1 21.8 560.3 19.9 0.0 0.0 6 1 Cranbrook 109.0 2.3 670.0 7.5 770.8 5.0 

6 3 Kaslo 2.80 Kaslo 6 1 Cranbrook 230.0 105.3 463.2 93.6 344.7 69.7 503.8 1.2 6 1 Cranbrook 230.0 4.1 844.0 8.1 613.1 4.9 560.3 4.5 0.0 0.0 6 1 Cranbrook 230.0 1.1 670.0 1.7 770.8 1.1 

6 3 Nakusp 8.00 Nakusp 6 1 Winfield 222.0 132.4 224.7 59.1 288.4 75.9 503.8 1.6 6 1 Winfield 222.0 5.2 619.7 7.8 613.1 6.4 560.3 5.9 0.0 0.0 6 1 Winfield 222.0 1.4 886.0 2.9 770.8 1.5 

6 3 Nelson 11.72 Nelson 6 1 Cranbrook 233.0 897.1 463.2 787.3 344.7 585.8 503.8 10.5 6 1 Cranbrook 233.0 35.1 844.0 68.4 613.1 41.4 560.3 37.9 0.0 0.0 6 1 Cranbrook 233.0 9.2 670.0 14.3 770.8 9.4 

6 3 New Denver 1.10 New Denver 6 1 Winfield 267.0 55.4 224.7 20.6 288.4 26.4 503.8 0.6 6 1 Winfield 267.0 2.2 619.7 2.7 613.1 2.2 560.3 2.0 0.0 0.0 6 1 Winfield 267.0 0.6 886.0 1.0 770.8 0.5 

6 3 Salmo 2.38 Salmo 6 1 Cranbrook 189.0 74.5 463.2 80.6 344.7 60.0 503.8 1.1 6 1 Cranbrook 189.0 2.9 844.0 7.0 613.1 4.2 560.3 3.9 0.0 0.0 6 1 Cranbrook 189.0 0.8 670.0 1.5 770.8 1.0 

6 3 Silverton 0.44 Silverton 6 1 Winfield 272.0 18.8 224.7 6.9 288.4 8.8 503.8 0.2 6 1 Winfield 272.0 0.7 619.7 0.9 613.1 0.7 560.3 0.7 0.0 0.0 6 1 Winfield 272.0 0.2 886.0 0.3 770.8 0.2 

6 3 Slocan 0.75 Slocan Park 6 1 Cranbrook 256.0 32.2 463.2 25.7 344.7 19.2 503.8 0.3 6 1 Cranbrook 256.0 1.3 844.0 2.2 613.1 1.4 560.3 1.2 0.0 0.0 6 1 Cranbrook 256.0 0.3 670.0 0.5 770.8 0.3 

6 3 Central Kootenay A 1,704.08 Nelson 6 1 Cranbrook 233.0 193.8 463.2 170.1 344.7 126.6 503.8 2.3 6 1 Cranbrook 233.0 7.6 844.0 14.8 613.1 8.9 560.3 8.2 0.0 0.0 6 1 Cranbrook 233.0 2.0 670.0 3.1 770.8 2.0 

6 3 Central Kootenay B 1,620.91 Creston 6 1 Cranbrook 109.0 203.8 463.2 382.2 344.7 284.4 503.8 5.1 6 1 Cranbrook 109.0 8.0 844.0 33.2 613.1 20.1 560.3 18.4 0.0 0.0 6 1 Cranbrook 109.0 2.1 670.0 6.9 770.8 4.6 

6 3 Central Kootenay C 733.29 Creston 6 1 Cranbrook 109.0 58.4 463.2 109.5 344.7 81.5 503.8 1.5 6 1 Cranbrook 109.0 2.3 844.0 9.5 613.1 5.8 560.3 5.3 0.0 0.0 6 1 Cranbrook 109.0 0.6 670.0 2.0 770.8 1.3 

6 3 Central Kootenay D 5,788.48 Kaslo 6 1 Cranbrook 150.0 96.5 463.2 131.5 344.7 97.8 503.8 1.8 6 1 Cranbrook 150.0 3.8 844.0 11.4 613.1 6.9 560.3 6.3 0.0 0.0 6 1 Cranbrook 150.0 1.0 670.0 2.4 770.8 1.6 

6 3 Central Kootenay E 812.61 Nelson 6 1 Cranbrook 233.0 373.4 463.2 327.6 344.7 243.8 503.8 4.4 6 1 Cranbrook 233.0 14.6 844.0 28.5 613.1 17.2 560.3 15.8 0.0 0.0 6 1 Cranbrook 233.0 3.8 670.0 5.9 770.8 3.9 

6 3 Central Kootenay F 402.62 Nelson 6 1 Cranbrook 233.0 352.9 463.2 309.7 344.7 230.4 503.8 4.1 6 1 Cranbrook 233.0 13.8 844.0 26.9 613.1 16.3 560.3 14.9 0.0 0.0 6 1 Cranbrook 233.0 3.6 670.0 5.6 770.8 3.7 

6 3 Central Kootenay G 1,510.61 Castlegar 6 1 Cranbrook 230.0 170.7 463.2 151.7 344.7 112.9 503.8 2.0 6 1 Cranbrook 230.0 6.7 844.0 13.2 613.1 8.0 560.3 7.3 0.0 0.0 6 1 Cranbrook 230.0 1.8 670.0 2.8 770.8 1.8 

6 3 Central Kootenay H 3,293.57 Kaslo 6 1 Cranbrook 150.0 264.9 463.2 361.1 344.7 268.7 503.8 4.8 6 1 Cranbrook 150.0 10.4 844.0 31.4 613.1 19.0 560.3 17.4 0.0 0.0 6 1 Cranbrook 150.0 2.7 670.0 6.5 770.8 4.3 

6 3 Central Kootenay I 109.47 Castlegar 6 1 Cranbrook 230.0 230.7 463.2 205.1 344.7 152.6 503.8 2.7 6 1 Cranbrook 230.0 9.0 844.0 17.8 613.1 10.8 560.3 9.9 0.0 0.0 6 1 Cranbrook 230.0 2.4 670.0 3.7 770.8 2.5 

6 3 Central Kootenay J 1,701.37 Castlegar 6 1 Cranbrook 230.0 260.5 463.2 231.5 344.7 172.3 503.8 3.1 6 1 Cranbrook 230.0 10.2 844.0 20.1 613.1 12.2 560.3 11.1 0.0 0.0 6 1 Cranbrook 230.0 2.7 670.0 4.2 770.8 2.8 

6 3 Central Kootenay K 4,390.45 Kaslo 6 1 Cranbrook 150.0 106.5 463.2 145.2 344.7 108.0 503.8 1.9 6 1 Cranbrook 150.0 4.2 844.0 12.6 613.1 7.6 560.3 7.0 0.0 0.0 6 1 Cranbrook 150.0 1.1 670.0 2.6 770.8 1.7 

6 39 Golden 11.02 Golden 4 33 Kamloops 361.0 556.3 195.0 132.6 260.7 177.4 503.8 4.2 4 33 Kamloops 361.0 21.8 555.8 18.0 611.1 16.5 560.3 15.2 0.0 0.0 4 33 Kamloops 361.0 5.7 505.7 4.3 520.5 2.6 

6 39 Revelstoke 31.90 Revelstoke 4 33 Kamloops 213.0 629.0 195.0 254.2 260.7 339.9 503.8 8.0 4 33 Kamloops 213.0 24.6 555.8 34.6 611.1 31.7 560.3 29.0 0.0 0.0 4 33 Kamloops 213.0 6.5 505.7 8.3 520.5 4.9 

6 39 Columbia-Shuswap A 13,514.74 Golden 4 33 Kamloops 361.0 463.4 195.0 110.5 260.7 147.7 503.8 3.5 4 33 Kamloops 361.0 18.2 555.8 15.0 611.1 13.8 560.3 12.6 0.0 0.0 4 33 Kamloops 361.0 4.8 505.7 3.6 520.5 2.1 

6 39 Columbia-Shuswap B 9,786.38 Revelstoke 4 33 Kamloops 213.0 67.5 195.0 27.3 260.7 36.5 503.8 0.9 4 33 Kamloops 213.0 2.6 555.8 3.7 611.1 3.4 560.3 3.1 0.0 0.0 4 33 Kamloops 213.0 0.7 505.7 0.9 520.5 0.5 

6 1 Canal Flats 10.84 Canal Flats 6 1 Cranbrook 82.7 23.1 463.2 57.1 344.7 42.5 503.8 0.8 6 1 Cranbrook 82.7 0.9 844.0 5.0 613.1 3.0 560.3 2.7 0.0 0.0 6 1 Cranbrook 82.7 0.2 670.0 1.0 770.8 0.7 

6 1 Cranbrook 25.14 Cranbrook 6 1 Cranbrook 1.4 10.7 463.2 1546.7 344.7 1151.0 503.8 20.6 6 1 Cranbrook 1.4 0.4 844.0 134.5 613.1 81.4 560.3 74.4 0.0 0.0 6 1 Cranbrook 1.4 0.1 670.0 28.1 770.8 18.5 

6 1 Elkford 101.59 Elkford 6 1 Cranbrook 65.2 65.1 463.2 204.1 344.7 151.8 503.8 2.7 6 1 Cranbrook 65.2 2.5 844.0 17.7 613.1 10.7 560.3 9.8 0.0 0.0 6 1 Cranbrook 65.2 0.7 670.0 3.7 770.8 2.4 

6 1 Fernie 16.05 Fernie 6 1 Cranbrook 94.1 157.0 463.2 341.2 344.7 253.9 503.8 4.5 6 1 Cranbrook 94.1 6.2 844.0 29.7 613.1 18.0 560.3 16.4 0.0 0.0 6 1 Cranbrook 94.1 1.6 670.0 6.2 770.8 4.1 

6 1 Invermere 10.18 Invermere 6 1 Cranbrook 128.0 165.2 463.2 263.9 344.7 196.4 503.8 3.5 6 1 Cranbrook 128.0 6.5 844.0 22.9 613.1 13.9 560.3 12.7 0.0 0.0 6 1 Cranbrook 128.0 1.7 670.0 4.8 770.8 3.2 

6 1 Kimberley 58.31 Kimberley 6 1 Cranbrook 28.8 71.4 463.2 507.1 344.7 377.4 503.8 6.8 6 1 Cranbrook 28.8 2.8 844.0 44.1 613.1 26.7 560.3 24.4 0.0 0.0 6 1 Cranbrook 28.8 0.7 670.0 9.2 770.8 6.1 

6 1 Radium Hot Springs 6.31 Radium Hot Springs 6 1 Cranbrook 142.0 50.1 463.2 72.1 344.7 53.7 503.8 1.0 6 1 Cranbrook 142.0 2.0 844.0 6.3 613.1 3.8 560.3 3.5 0.0 0.0 6 1 Cranbrook 142.0 0.5 670.0 1.3 770.8 0.9 

6 1 Sparwood 177.71 Sparwood 6 1 Cranbrook 126.0 184.5 463.2 299.3 344.7 222.7 503.8 4.0 6 1 Cranbrook 126.0 7.2 844.0 26.0 613.1 15.8 560.3 14.4 0.0 0.0 6 1 Cranbrook 126.0 1.9 670.0 5.4 770.8 3.6 

6 1 East Kootenay A 4,653.72 Fernie 6 1 Cranbrook 94.1 74.4 463.2 161.8 344.7 120.4 503.8 2.2 6 1 Cranbrook 94.1 2.9 844.0 14.1 613.1 8.5 560.3 7.8 0.0 0.0 6 1 Cranbrook 94.1 0.8 670.0 2.9 770.8 1.9 

6 1 East Kootenay B 2,791.55 Fernie 6 1 Cranbrook 94.1 71.0 463.2 154.3 344.7 114.8 503.8 2.1 6 1 Cranbrook 94.1 2.8 844.0 13.4 613.1 8.1 560.3 7.4 0.0 0.0 6 1 Cranbrook 94.1 0.7 670.0 2.8 770.8 1.8 

6 1 East Kootenay C 4,519.23 Cranbrook 6 1 Cranbrook 19.0 47.0 463.2 506.6 344.7 377.0 503.8 6.8 6 1 Cranbrook 19.0 1.8 844.0 44.0 613.1 26.7 560.3 24.4 0.0 0.0 6 1 Cranbrook 19.0 0.5 670.0 9.2 770.8 6.1 

6 1 East Kootenay E 4,266.98 Cranbrook 6 1 Cranbrook 18.4 12.9 463.2 143.2 344.7 106.6 503.8 1.9 6 1 Cranbrook 18.4 0.5 844.0 12.4 613.1 7.5 560.3 6.9 0.0 0.0 6 1 Cranbrook 18.4 0.1 670.0 2.6 770.8 1.7 

6 1 East Kootenay F 6,102.84 Invermere 6 1 Cranbrook 128.0 169.0 463.2 269.9 344.7 200.9 503.8 3.6 6 1 Cranbrook 128.0 6.6 844.0 23.5 613.1 14.2 560.3 13.0 0.0 0.0 6 1 Cranbrook 128.0 1.7 670.0 4.9 770.8 3.2 

6 1 East Kootenay G 4,654.72 Radium Hot Springs 6 1 Cranbrook 142.0 90.2 463.2 129.9 344.7 96.6 503.8 1.7 6 1 Cranbrook 142.0 3.5 844.0 11.3 613.1 6.8 560.3 6.2 0.0 0.0 6 1 Cranbrook 142.0 0.9 670.0 2.4 770.8 1.6 

6 5 Fruitvale 2.66 Fruitvale 6 1 Cranbrook 214.0 170.6 463.2 163.0 344.7 121.3 503.8 2.2 6 1 Cranbrook 214.0 6.7 844.0 14.2 613.1 8.6 560.3 7.8 0.0 0.0 6 1 Cranbrook 214.0 1.8 670.0 3.0 770.8 2.0 

6 5 Grand Forks 10.44 Grand Forks 4 35 Kelowna 206.0 346.2 214.4 159.0 289.0 214.4 503.8 4.6 4 35 Kelowna 206.0 13.6 604.9 21.4 611.1 18.0 560.3 16.5 0.0 0.0 4 35 Kelowna 206.0 3.6 552.8 5.1 520.5 2.8 

6 5 Greenwood 2.52 Greenwood 4 35 Kelowna 161.0 40.4 214.4 23.8 289.0 32.0 503.8 0.7 4 35 Kelowna 161.0 1.6 604.9 3.2 611.1 2.7 560.3 2.5 0.0 0.0 4 35 Kelowna 161.0 0.4 552.8 0.8 520.5 0.4 

6 5 Midway 12.16 Midway 4 35 Kelowna 150.0 38.3 214.4 24.1 289.0 32.5 503.8 0.7 4 35 Kelowna 150.0 1.5 604.9 3.3 611.1 2.7 560.3 2.5 0.0 0.0 4 35 Kelowna 150.0 0.4 552.8 0.8 520.5 0.4 

6 5 Montrose 1.53 Montrose 6 1 Cranbrook 219.0 89.6 463.2 83.7 344.7 62.3 503.8 1.1 6 1 Cranbrook 219.0 3.5 844.0 7.3 613.1 4.4 560.3 4.0 0.0 0.0 6 1 Cranbrook 219.0 0.9 670.0 1.5 770.8 1.0 

6 5 Rossland 57.97 Rossland 6 1 Cranbrook 242.0 310.7 463.2 262.5 344.7 195.4 503.8 3.5 6 1 Cranbrook 242.0 12.2 844.0 22.8 613.1 13.8 560.3 12.6 0.0 0.0 6 1 Cranbrook 242.0 3.2 670.0 4.8 770.8 3.1 

6 5 Trail 34.78 Trail 6 1 Cranbrook 232.0 682.0 463.2 601.1 344.7 447.3 503.8 8.0 6 1 Cranbrook 232.0 26.7 844.0 52.3 613.1 31.6 560.3 28.9 0.0 0.0 6 1 Cranbrook 232.0 7.0 670.0 10.9 770.8 7.2 

6 5 Warfield 1.90 Warfield 6 1 Cranbrook 236.0 169.8 463.2 147.1 344.7 109.5 503.8 2.0 6 1 Cranbrook 236.0 6.7 844.0 12.8 613.1 7.7 560.3 7.1 0.0 0.0 6 1 Cranbrook 236.0 1.7 670.0 2.7 770.8 1.8 

6 5 Kootenay Boundary A 238.52 Trail 6 1 Cranbrook 232.0 192.9 463.2 170.0 344.7 126.5 503.8 2.3 6 1 Cranbrook 232.0 7.6 844.0 14.8 613.1 8.9 560.3 8.2 0.0 0.0 6 1 Cranbrook 232.0 2.0 670.0 3.1 770.8 2.0 

6 5 Kootenay Boundary B 778.61 Rossland 6 1 Cranbrook 242.0 134.1 463.2 113.3 344.7 84.3 503.8 1.5 6 1 Cranbrook 242.0 5.3 844.0 9.9 613.1 6.0 560.3 5.4 0.0 0.0 6 1 Cranbrook 242.0 1.4 670.0 2.1 770.8 1.4 

6 5 Kootenay Boundary C 530.61 Christina Lake 4 35 Kelowna 223.0 132.4 214.4 56.2 289.0 75.8 503.8 1.6 4 35 Kelowna 223.0 5.2 604.9 7.6 611.1 6.4 560.3 5.8 0.0 0.0 4 35 Kelowna 223.0 1.4 552.8 1.8 520.5 1.0 

6 5 Kootenay Boundary D 2,116.43 Christina Lake 4 35 Kelowna 223.0 292.1 214.4 124.0 289.0 167.1 503.8 3.6 4 35 Kelowna 223.0 11.4 604.9 16.7 611.1 14.0 560.3 12.9 0.0 0.0 4 35 Kelowna 223.0 3.0 552.8 4.0 520.5 2.2 

6 5 Kootenay Boundary E 4,307.49 Greenwood 4 35 Kelowna 161.0 152.9 214.4 89.8 289.0 121.1 503.8 2.6 4 35 Kelowna 161.0 6.0 604.9 12.1 611.1 10.2 560.3 9.3 0.0 0.0 4 35 Kelowna 161.0 1.6 552.8 2.9 520.5 1.6 

6 37 North Okanagan E 2,613.15 Vernon 4 35 Winfield 31.3 12.2 224.7 38.6 288.4 49.5 503.8 1.1 4 35 Winfield 31.3 0.5 611.7 5.0 611.1 4.2 560.3 3.8 0.0 0.0 4 35 Winfield 31.3 0.1 565.7 1.2 520.5 0.6 

Page 3 of 6

TABLE 3.3 



BCUOMA 



Name km 2 

Location (2) 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 


Consumed 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 








Consumed 

(L) 

CRA 071620 (2) 

7 17 Central Saanich 41.42 Central Saanich 7 21 Nanaimo 111.0 434.6 53.0 91.6 266.1 459.9 503.8 10.7 7 21 Nanaimo 111.0 13.6 486.3 32.0 613.1 33.6 560.3 30.7 0.0 0.0 7 21 Nanaimo 111.0 3.7 678.2 12.3 580.9 6.0 

7 17 Colwood 17.76 Colwood 7 21 Nanaimo 101.0 378.0 53.0 87.6 266.1 439.6 503.8 10.2 7 21 Nanaimo 101.0 11.8 486.3 30.6 613.1 32.1 560.3 29.3 0.0 0.0 7 21 Nanaimo 101.0 3.3 678.2 11.7 580.9 5.8 

7 17 Esquimalt 7.04 Esquimalt 7 21 Nanaimo 108.0 457.1 53.0 99.1 266.1 497.1 503.8 11.5 7 21 Nanaimo 108.0 14.3 486.3 34.6 613.1 36.3 560.3 33.2 0.0 0.0 7 21 Nanaimo 108.0 3.9 678.2 13.3 580.9 6.5 

7 17 Highlands 37.87 Highlands 7 21 Nanaimo 97.3 49.0 53.0 11.8 266.1 59.1 503.8 1.4 7 21 Nanaimo 97.3 1.5 486.3 4.1 613.1 4.3 560.3 3.9 0.0 0.0 7 21 Nanaimo 97.3 0.4 678.2 1.6 580.9 0.8 

7 17 Langford 39.55 Langford 7 21 Nanaimo 96.0 586.7 53.0 143.1 266.1 717.8 503.8 16.7 7 21 Nanaimo 96.0 18.3 486.3 49.9 613.1 52.4 560.3 47.9 0.0 0.0 7 21 Nanaimo 96.0 5.0 678.2 19.2 580.9 9.4 

7 17 Metchosin 71.32 Metchosin 7 21 Nanaimo 105.0 122.4 53.0 27.3 266.1 136.9 503.8 3.2 7 21 Nanaimo 105.0 3.8 486.3 9.5 613.1 10.0 560.3 9.1 0.0 0.0 7 21 Nanaimo 105.0 1.1 678.2 3.7 580.9 1.8 

7 17 North Saanich 37.14 North Saanich 7 21 Nanaimo 123.0 333.2 53.0 63.4 266.1 318.2 503.8 7.4 7 21 Nanaimo 123.0 10.4 486.3 22.1 613.1 23.2 560.3 21.2 0.0 0.0 7 21 Nanaimo 123.0 2.9 678.2 8.5 580.9 4.2 

7 17 Oak Bay 10.38 Oak Bay 7 21 Nanaimo 112.0 493.0 53.0 103.0 266.1 517.0 503.8 12.0 7 21 Nanaimo 112.0 15.4 486.3 35.9 613.1 37.8 560.3 34.5 0.0 0.0 7 21 Nanaimo 112.0 4.2 678.2 13.8 580.9 6.8 

7 17 Saanich 103.44 Saanich 7 21 Nanaimo 109.0 2966.5 53.0 637.0 266.1 3196.3 503.8 74.2 7 21 Nanaimo 109.0 92.7 486.3 222.2 613.1 233.5 560.3 213.4 0.0 0.0 7 21 Nanaimo 109.0 25.5 678.2 85.4 580.9 42.0 

7 17 Sidney 5.04 Sidney 7 21 Nanaimo 127.0 359.3 53.0 66.2 266.1 332.3 503.8 7.7 7 21 Nanaimo 127.0 11.2 486.3 23.1 613.1 24.3 560.3 22.2 0.0 0.0 7 21 Nanaimo 127.0 3.1 678.2 8.9 580.9 4.4 

7 17 Sooke 50.01 Sooke 7 21 Nanaimo 116.0 293.6 53.0 59.2 266.1 297.3 503.8 6.9 7 21 Nanaimo 116.0 9.2 486.3 20.7 613.1 21.7 560.3 19.8 0.0 0.0 7 21 Nanaimo 116.0 2.5 678.2 7.9 580.9 3.9 

7 17 Victoria 19.68 Victoria 7 21 Nanaimo 109.0 2149.3 53.0 461.5 266.1 2315.8 503.8 53.7 7 21 Nanaimo 109.0 67.1 486.3 161.0 613.1 169.2 560.3 154.6 0.0 0.0 7 21 Nanaimo 109.0 18.5 678.2 61.9 580.9 30.4 

7 17 View Royal 14.48 View Royal 7 21 Nanaimo 102.0 245.1 53.0 56.2 266.1 282.2 503.8 6.5 7 21 Nanaimo 102.0 7.7 486.3 19.6 613.1 20.6 560.3 18.8 0.0 0.0 7 21 Nanaimo 102.0 2.1 678.2 7.5 580.9 3.7 

7 17 Capital F 182.23 Sidney 7 21 Nanaimo 127.0 306.8 53.0 56.5 266.1 283.7 503.8 6.6 7 21 Nanaimo 127.0 9.6 486.3 19.7 613.1 20.7 560.3 18.9 0.0 0.0 7 21 Nanaimo 127.0 2.6 678.2 7.6 580.9 3.7 

7 17 Capital G 187.46 Sidney 7 21 Nanaimo 127.0 175.6 53.0 32.4 266.1 162.4 503.8 3.8 7 21 Nanaimo 127.0 5.5 486.3 11.3 613.1 11.9 560.3 10.8 0.0 0.0 7 21 Nanaimo 127.0 1.5 678.2 4.3 580.9 2.1 

7 17 Capital H (Part 1) 228.08 Victoria 7 21 Nanaimo 109.0 121.3 53.0 26.0 266.1 130.7 503.8 3.0 7 21 Nanaimo 109.0 3.8 486.3 9.1 613.1 9.5 560.3 8.7 0.0 0.0 7 21 Nanaimo 109.0 1.0 678.2 3.5 580.9 1.7 

7 17 Capital H (Part 2) 1,272.66 Victoria 7 21 Nanaimo 109.0 7.8 53.0 1.7 266.1 8.4 503.8 0.2 7 21 Nanaimo 109.0 0.2 486.3 0.6 613.1 0.6 560.3 0.6 0.0 0.0 7 21 Nanaimo 109.0 0.1 678.2 0.2 580.9 0.1 

7 19 Duncan 2.05 Duncan 7 21 Nanaimo 48.0 60.7 53.0 29.6 266.1 148.6 503.8 3.4 7 21 Nanaimo 48.0 1.9 486.3 10.3 613.1 10.9 560.3 9.9 0.0 0.0 7 21 Nanaimo 48.0 0.5 678.2 4.0 580.9 2.0 

7 19 Ladysmith 12.18 Ladysmith 7 21 Nanaimo 21.0 41.2 53.0 45.9 266.1 230.4 503.8 5.3 7 21 Nanaimo 21.0 1.3 486.3 16.0 613.1 16.8 560.3 15.4 0.0 0.0 7 21 Nanaimo 21.0 0.4 678.2 6.2 580.9 3.0 

7 19 Lake Cowichan 8.25 Lake Cowichan 7 21 Nanaimo 70.5 52.2 53.0 17.3 266.1 86.9 503.8 2.0 7 21 Nanaimo 70.5 1.6 486.3 6.0 613.1 6.4 560.3 5.8 0.0 0.0 7 21 Nanaimo 70.5 0.4 678.2 2.3 580.9 1.1 

7 19 North Cowichan 193.66 North Cowichan 7 21 Nanaimo 43.1 300.2 53.0 163.1 266.1 818.1 503.8 19.0 7 21 Nanaimo 43.1 9.4 486.3 56.9 613.1 59.8 560.3 54.6 0.0 0.0 7 21 Nanaimo 43.1 2.6 678.2 21.9 580.9 10.8 

7 19 Cowichan Valley A 49.43 Sidney 7 21 Nanaimo 127.0 140.8 53.0 25.9 266.1 130.2 503.8 3.0 7 21 Nanaimo 127.0 4.4 486.3 9.1 613.1 9.5 560.3 8.7 0.0 0.0 7 21 Nanaimo 127.0 1.2 678.2 3.5 580.9 1.7 

7 19 Cowichan Valley B 306.23 Sidney 7 21 Nanaimo 127.0 244.7 53.0 45.1 266.1 226.2 503.8 5.2 7 21 Nanaimo 127.0 7.6 486.3 15.7 613.1 16.5 560.3 15.1 0.0 0.0 7 21 Nanaimo 127.0 2.1 678.2 6.0 580.9 3.0 

7 19 Cowichan Valley C 22.64 Sidney 7 21 Nanaimo 127.0 141.0 53.0 26.0 266.1 130.4 503.8 3.0 7 21 Nanaimo 127.0 4.4 486.3 9.1 613.1 9.5 560.3 8.7 0.0 0.0 7 21 Nanaimo 127.0 1.2 678.2 3.5 580.9 1.7 

7 19 Cowichan Valley D 15.48 Duncan 7 21 Nanaimo 48.0 34.2 53.0 16.7 266.1 83.6 503.8 1.9 7 21 Nanaimo 48.0 1.1 486.3 5.8 613.1 6.1 560.3 5.6 0.0 0.0 7 21 Nanaimo 48.0 0.3 678.2 2.2 580.9 1.1 

7 19 Cowichan Valley E 134.87 Duncan 7 21 Nanaimo 48.0 46.3 53.0 22.6 266.1 113.2 503.8 2.6 7 21 Nanaimo 48.0 1.4 486.3 7.9 613.1 8.3 560.3 7.6 0.0 0.0 7 21 Nanaimo 48.0 0.4 678.2 3.0 580.9 1.5 

7 19 Cowichan Valley F 1,792.90 Lake Cowichan 7 21 Nanaimo 70.5 29.9 53.0 9.9 266.1 49.8 503.8 1.2 7 21 Nanaimo 70.5 0.9 486.3 3.5 613.1 3.6 560.3 3.3 0.0 0.0 7 21 Nanaimo 70.5 0.3 678.2 1.3 580.9 0.7 

7 19 Cowichan Valley G 284.30 Ladysmith 7 21 Nanaimo 21.0 11.7 53.0 13.1 266.1 65.6 503.8 1.5 7 21 Nanaimo 21.0 0.4 486.3 4.6 613.1 4.8 560.3 4.4 0.0 0.0 7 21 Nanaimo 21.0 0.1 678.2 1.8 580.9 0.9 

7 19 Cowichan Valley H 83.02 Ladysmith 7 21 Nanaimo 21.0 12.0 53.0 13.4 266.1 67.0 503.8 1.6 7 21 Nanaimo 21.0 0.4 486.3 4.7 613.1 4.9 560.3 4.5 0.0 0.0 7 21 Nanaimo 21.0 0.1 678.2 1.8 580.9 0.9 

7 19 Cowichan Valley I 507.87 Lake Cowichan 7 21 Nanaimo 70.5 20.6 53.0 6.8 266.1 34.3 503.8 0.8 7 21 Nanaimo 70.5 0.6 486.3 2.4 613.1 2.5 560.3 2.3 0.0 0.0 7 21 Nanaimo 70.5 0.2 678.2 0.9 580.9 0.5 

7 21 Nanaimo 89.30 Nanaimo 7 21 Nanaimo 2.7 53.7 53.0 471.9 266.1 2367.6 503.8 54.9 7 21 Nanaimo 2.7 1.7 486.3 164.6 613.1 173.0 560.3 158.1 0.0 0.0 7 21 Nanaimo 2.7 0.5 678.2 63.3 580.9 31.1 

Page 4 of 6

TABLE 3.3 



BCUOMA 



Name km 2 

Location (2) 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 


Consumed 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 








Consumed 

(L) 

CRA 071620 (2) 

7 21 Nanaimo A 60.11 Nanaimo 7 21 Nanaimo 2.2 3.7 53.0 39.9 266.1 200.1 503.8 4.6 7 21 Nanaimo 2.2 0.1 486.3 13.9 613.1 14.6 560.3 13.4 0.0 0.0 7 21 Nanaimo 2.2 0.0 678.2 5.3 580.9 2.6 

7 21 Nanaimo B 57.60 Nanaimo 7 21 Nanaimo 2.1 2.3 53.0 25.2 266.1 126.7 503.8 2.9 7 21 Nanaimo 2.1 0.1 486.3 8.8 613.1 9.3 560.3 8.5 0.0 0.0 7 21 Nanaimo 2.1 0.0 678.2 3.4 580.9 1.7 

7 21 Nanaimo C 1,098.49 Nanaimo 7 21 Nanaimo 9.3 6.7 53.0 16.8 266.1 84.4 503.8 2.0 7 21 Nanaimo 9.3 0.2 486.3 5.9 613.1 6.2 560.3 5.6 0.0 0.0 7 21 Nanaimo 9.3 0.1 678.2 2.3 580.9 1.1 

8 23 Port Alberni 19.92 Port Alberni 8 23 Port Alberni 1.3 7.5 93.7 244.8 302.3 790.2 503.8 16.1 8 23 Port Alberni 1.3 0.2 509.3 52.9 613.1 53.0 560.3 48.5 0.0 0.0 8 23 Port Alberni 1.3 0.1 977.6 31.7 655.2 12.2 

8 23 Tofino 10.54 Tofino 8 23 Port Alberni 124.0 75.0 93.7 25.0 302.3 80.7 503.8 1.6 8 23 Port Alberni 124.0 2.4 509.3 5.4 613.1 5.4 560.3 4.9 0.0 0.0 8 23 Port Alberni 124.0 0.8 977.6 3.2 655.2 1.2 

8 23 Ucluelet 6.55 Ucluelet 8 23 Port Alberni 100.0 49.1 93.7 20.3 302.3 65.5 503.8 1.3 8 23 Port Alberni 100.0 1.6 509.3 4.4 613.1 4.4 560.3 4.0 0.0 0.0 8 23 Port Alberni 100.0 0.5 977.6 2.6 655.2 1.0 

8 23 Alberni-Clayoquot A 1,621.71 Port Alberni 8 23 Port Alberni 11.4 1.2 93.7 4.4 302.3 14.3 503.8 0.3 8 23 Port Alberni 11.4 0.0 509.3 1.0 613.1 1.0 560.3 0.9 0.0 0.0 8 23 Port Alberni 11.4 0.0 977.6 0.6 655.2 0.2 

8 23 Alberni-Clayoquot B 92.53 Port Alberni 8 23 Port Alberni 2.7 0.4 93.7 6.5 302.3 20.9 503.8 0.4 8 23 Port Alberni 2.7 0.0 509.3 1.4 613.1 1.4 560.3 1.3 0.0 0.0 8 23 Port Alberni 2.7 0.0 977.6 0.8 655.2 0.3 

8 23 Alberni-Clayoquot C 3,210.02 Ucluelet 8 23 Port Alberni 100.0 14.3 93.7 5.9 302.3 19.1 503.8 0.4 8 23 Port Alberni 100.0 0.5 509.3 1.3 613.1 1.3 560.3 1.2 0.0 0.0 8 23 Port Alberni 100.0 0.1 977.6 0.8 655.2 0.3 

8 23 Alberni-Clayoquot D 1,403.82 Port Alberni 8 23 Port Alberni 10.6 7.3 93.7 28.6 302.3 92.2 503.8 1.9 8 23 Port Alberni 10.6 0.2 509.3 6.2 613.1 6.2 560.3 5.7 0.0 0.0 8 23 Port Alberni 10.6 0.1 977.6 3.7 655.2 1.4 

8 23 Alberni-Clayoquot E 22.01 Port Alberni 8 23 Port Alberni 1.3 1.3 93.7 40.0 302.3 129.1 503.8 2.6 8 23 Port Alberni 1.3 0.0 509.3 8.6 613.1 8.7 560.3 7.9 0.0 0.0 8 23 Port Alberni 1.3 0.0 977.6 5.2 655.2 2.0 

8 23 Alberni-Clayoquot F 186.55 Port Alberni 8 23 Port Alberni 3.9 2.5 93.7 26.4 302.3 85.1 503.8 1.7 8 23 Port Alberni 3.9 0.1 509.3 5.7 613.1 5.7 560.3 5.2 0.0 0.0 8 23 Port Alberni 3.9 0.0 977.6 3.4 655.2 1.3 

8 25 Campbell River 143.48 Campbell River 7 21 Nanaimo 166.0 1713.5 53.0 241.6 266.1 1212.2 503.8 28.1 7 21 Nanaimo 166.0 55.9 486.3 88.0 613.1 92.4 560.3 84.5 0.0 0.0 7 21 Nanaimo 166.0 17.5 678.2 38.4 580.9 18.9 

8 25 Comox 15.16 Comox 7 21 Nanaimo 124.0 531.1 53.0 100.3 266.1 503.1 503.8 11.7 7 21 Nanaimo 124.0 17.3 486.3 36.5 613.1 38.4 560.3 35.1 0.0 0.0 7 21 Nanaimo 124.0 5.4 678.2 15.9 580.9 7.8 

8 25 Courtenay 26.68 Courtenay 7 21 Nanaimo 119.0 962.1 53.0 189.2 266.1 949.5 503.8 22.0 7 21 Nanaimo 119.0 31.4 486.3 68.9 613.1 72.4 560.3 66.2 0.0 0.0 7 21 Nanaimo 119.0 9.8 678.2 30.0 580.9 14.8 

8 25 Cumberland 29.13 Cumberland 7 21 Nanaimo 116.0 112.0 53.0 22.6 266.1 113.4 503.8 2.6 7 21 Nanaimo 116.0 3.7 486.3 8.2 613.1 8.6 560.3 7.9 0.0 0.0 7 21 Nanaimo 116.0 1.1 678.2 3.6 580.9 1.8 

8 25 Gold River 10.51 Gold River 7 21 Nanaimo 254.0 117.7 53.0 10.8 266.1 54.4 503.8 1.3 7 21 Nanaimo 254.0 3.8 486.3 3.9 613.1 4.1 560.3 3.8 0.0 0.0 7 21 Nanaimo 254.0 1.2 678.2 1.7 580.9 0.8 

8 25 Sayward 4.72 Sayward 7 21 Nanaimo 239.0 26.0 53.0 2.5 266.1 12.8 503.8 0.3 7 21 Nanaimo 239.0 0.8 486.3 0.9 613.1 1.0 560.3 0.9 0.0 0.0 7 21 Nanaimo 239.0 0.3 678.2 0.4 580.9 0.2 

8 25 Tahsis 5.73 Tahsis 7 21 Nanaimo 318.0 29.4 53.0 2.2 266.1 10.9 503.8 0.3 7 21 Nanaimo 318.0 1.0 486.3 0.8 613.1 0.8 560.3 0.8 0.0 0.0 7 21 Nanaimo 318.0 0.3 678.2 0.3 580.9 0.2 

8 25 Zeballos 1.45 Zeballos 7 21 Nanaimo 358.0 20.8 53.0 1.4 266.1 6.8 503.8 0.2 7 21 Nanaimo 358.0 0.7 486.3 0.5 613.1 0.5 560.3 0.5 0.0 0.0 7 21 Nanaimo 358.0 0.2 678.2 0.2 580.9 0.1 

8 25 Comox-Strathcona A 413.64 Courtenay 7 21 Nanaimo 119.0 200.9 53.0 39.5 266.1 198.3 503.8 4.6 7 21 Nanaimo 119.0 6.6 486.3 14.4 613.1 15.1 560.3 13.8 0.0 0.0 7 21 Nanaimo 119.0 2.0 678.2 6.3 580.9 3.1 

8 25 Comox-Strathcona B 57.66 Courtenay 7 21 Nanaimo 119.0 297.0 53.0 58.4 266.1 293.1 503.8 6.8 7 21 Nanaimo 119.0 9.7 486.3 21.3 613.1 22.3 560.3 20.4 0.0 0.0 7 21 Nanaimo 119.0 3.0 678.2 9.3 580.9 4.6 

8 25 Comox-Strathcona C 1,058.83 Courtenay 7 21 Nanaimo 119.0 300.7 53.0 59.1 266.1 296.8 503.8 6.9 7 21 Nanaimo 119.0 9.8 486.3 21.5 613.1 22.6 560.3 20.7 0.0 0.0 7 21 Nanaimo 119.0 3.1 678.2 9.4 580.9 4.6 

8 25 Comox-Strathcona D 1,611.81 Campbell River 7 21 Nanaimo 166.0 283.3 53.0 39.9 266.1 200.4 503.8 4.7 7 21 Nanaimo 166.0 9.2 486.3 14.5 613.1 15.3 560.3 14.0 0.0 0.0 7 21 Nanaimo 166.0 2.9 678.2 6.3 580.9 3.1 

8 25 Comox-Strathcona G 5,104.75 Gold River 7 21 Nanaimo 254.0 6.8 53.0 0.6 266.1 3.2 503.8 0.1 7 21 Nanaimo 254.0 0.2 486.3 0.2 613.1 0.2 560.3 0.2 0.0 0.0 7 21 Nanaimo 254.0 0.1 678.2 0.1 580.9 0.0 

8 25 Comox-Strathcona H 2,024.49 Campbell River 7 21 Nanaimo 166.0 41.6 53.0 5.9 266.1 29.4 503.8 0.7 7 21 Nanaimo 166.0 1.4 486.3 2.1 613.1 2.2 560.3 2.1 0.0 0.0 7 21 Nanaimo 166.0 0.4 678.2 0.9 580.9 0.5 

8 25 Comox-Strathcona I 135.44 Campbell River 7 21 Nanaimo 166.0 62.6 53.0 8.8 266.1 44.3 503.8 1.0 7 21 Nanaimo 166.0 2.0 486.3 3.2 613.1 3.4 560.3 3.1 0.0 0.0 7 21 Nanaimo 166.0 0.6 678.2 1.4 580.9 0.7 

8 25 Comox-Strathcona J 9,271.11 Campbell River 7 21 Nanaimo 166.0 136.9 53.0 19.3 266.1 96.9 503.8 2.2 7 21 Nanaimo 166.0 4.5 486.3 7.0 613.1 7.4 560.3 6.8 0.0 0.0 7 21 Nanaimo 166.0 1.4 678.2 3.1 580.9 1.5 

8 25 Comox-Strathcona K 80.95 Campbell River 7 21 Nanaimo 166.0 129.1 53.0 18.2 266.1 91.4 503.8 2.1 7 21 Nanaimo 166.0 4.2 486.3 6.6 613.1 7.0 560.3 6.4 0.0 0.0 7 21 Nanaimo 166.0 1.3 678.2 2.9 580.9 1.4 

8 15 Bowen Island 49.94 Bowen Island 1 15 North Vancouver 34.9 43.1 5.9 3.2 240.3 130.9 503.8 3.4 1 15 Burnaby 48.0 1.9 209.1 4.5 583.5 10.5 560.3 10.1 0.2 0.0 1 15 Burnaby 48.0 0.6 2.1 0.0 397.6 1.5 

8 43 Alert Bay 1.78 Alert Bay 8 21 Nanaimo 374.0 68.7 53.0 4.3 266.1 21.6 503.8 0.5 8 21 Nanaimo 374.0 2.2 486.3 1.6 613.1 1.6 560.3 1.5 0.0 0.0 8 21 Nanaimo 374.0 0.7 907.0 0.9 655.2 0.4 

8 43 Port Alice 7.65 Port Alice 8 21 Nanaimo 411.0 94.9 53.0 5.4 266.1 27.1 503.8 0.6 8 21 Nanaimo 411.0 3.1 486.3 2.0 613.1 2.1 560.3 1.9 0.0 0.0 8 21 Nanaimo 411.0 1.0 907.0 1.1 655.2 0.5 

8 43 Port Hardy 40.81 Port Hardy 8 21 Nanaimo 399.0 465.2 53.0 27.3 266.1 136.9 503.8 3.2 8 21 Nanaimo 399.0 15.2 486.3 9.9 613.1 10.4 560.3 9.5 0.0 0.0 8 21 Nanaimo 399.0 4.7 907.0 5.8 655.2 2.4 

8 43 Port McNeill 7.74 Port McNeill 8 21 Nanaimo 362.0 308.9 53.0 20.0 266.1 100.2 503.8 2.3 8 21 Nanaimo 362.0 10.1 486.3 7.3 613.1 7.6 560.3 7.0 0.0 0.0 8 21 Nanaimo 362.0 3.1 907.0 4.2 655.2 1.8 

8 43 Mount Waddington B 2,593.54 Port Hardy 8 21 Nanaimo 399.0 18.9 53.0 1.1 266.1 5.6 503.8 0.1 8 21 Nanaimo 399.0 0.6 486.3 0.4 613.1 0.4 560.3 0.4 0.0 0.0 8 21 Nanaimo 399.0 0.2 907.0 0.2 655.2 0.1 

8 43 Mount Waddington C 1,509.91 Port McNeill 8 21 Nanaimo 362.0 84.3 53.0 5.5 266.1 27.3 503.8 0.6 8 21 Nanaimo 362.0 2.7 486.3 2.0 613.1 2.1 560.3 1.9 0.0 0.0 8 21 Nanaimo 362.0 0.9 907.0 1.2 655.2 0.5 

8 43 Mount Waddington D 3,343.23 Port McNeill 8 21 Nanaimo 362.0 31.7 53.0 2.0 266.1 10.3 503.8 0.2 8 21 Nanaimo 362.0 1.0 486.3 0.7 613.1 0.8 560.3 0.7 0.0 0.0 8 21 Nanaimo 362.0 0.3 907.0 0.4 655.2 0.2 

8 21 Lantzville 27.87 Lantzville 7 21 Nanaimo 28.3 35.3 53.0 29.2 266.1 146.3 503.8 3.4 7 21 Nanaimo 28.3 1.1 486.3 10.6 613.1 11.2 560.3 10.2 0.0 0.0 7 21 Nanaimo 28.3 0.4 678.2 4.6 580.9 2.3 

8 21 Parksville 14.60 Parksville 7 21 Nanaimo 50.0 193.9 53.0 90.8 266.1 455.5 503.8 10.6 7 21 Nanaimo 50.0 6.3 486.3 33.1 613.1 34.7 560.3 31.7 0.0 0.0 7 21 Nanaimo 50.0 2.0 678.2 14.4 580.9 7.1 

8 21 Qualicum Beach 18.00 Qualicum Beach 7 21 Nanaimo 61.0 184.9 53.0 70.9 266.1 355.9 503.8 8.3 7 21 Nanaimo 61.0 6.0 486.3 25.8 613.1 27.1 560.3 24.8 0.0 0.0 7 21 Nanaimo 61.0 1.9 678.2 11.3 580.9 5.5 

8 21 Nanaimo E 75.11 Parksville 7 21 Nanaimo 50.0 100.0 53.0 46.8 266.1 234.9 503.8 5.5 7 21 Nanaimo 50.0 3.3 486.3 17.0 613.1 17.9 560.3 16.4 0.0 0.0 7 21 Nanaimo 50.0 1.0 678.2 7.4 580.9 3.7 

8 21 Nanaimo F 263.44 Parksville 7 21 Nanaimo 50.0 126.9 53.0 59.4 266.1 298.0 503.8 6.9 7 21 Nanaimo 50.0 4.1 486.3 21.6 613.1 22.7 560.3 20.8 0.0 0.0 7 21 Nanaimo 50.0 1.3 678.2 9.4 580.9 4.6 

8 21 Nanaimo G 48.88 Parksville 7 21 Nanaimo 50.0 129.7 53.0 60.7 266.1 304.6 503.8 7.1 7 21 Nanaimo 50.0 4.2 486.3 22.1 613.1 23.2 560.3 21.2 0.0 0.0 7 21 Nanaimo 50.0 1.3 678.2 9.6 580.9 4.7 

8 21 Nanaimo H 277.52 Parksville 7 21 Nanaimo 50.0 63.1 53.0 29.5 266.1 148.2 503.8 3.4 7 21 Nanaimo 50.0 2.1 486.3 10.8 613.1 11.3 560.3 10.3 0.0 0.0 7 21 Nanaimo 50.0 0.6 678.2 4.7 580.9 2.3 

Page 5 of 6

TABLE 3.3 



BCUOMA 



Name km 2 

Location (2) 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 


Consumed 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 

Consumed 


(km) (4) 

Consumed 

(L) (km) (5) 

Consumed 

(L) (km) (5) 








Consumed 

(L) 

9 51 Burns Lake 7.17 Burns Lake 2 53 Prince George 228.0 218.5 407.8 172.5 365.9 154.8 503.8 2.6 2 53 Prince George 228.0 7.4 796.7 13.8 613.1 8.9 560.3 8.1 0.0 0.0 2 53 Prince George 228.0 1.9 781.0 3.6 395.0 1.0 

9 51 Fort St. James 22.10 Fort St. James 2 53 Prince George 161.0 76.6 407.8 85.6 365.9 76.9 503.8 1.3 2 53 Prince George 161.0 2.6 796.7 6.9 613.1 4.4 560.3 4.0 0.0 0.0 2 53 Prince George 161.0 0.7 781.0 1.8 395.0 0.5 

9 51 Fraser Lake 3.90 Fraser Lake 2 53 Prince George 158.0 70.5 407.8 80.4 365.9 72.1 503.8 1.2 2 53 Prince George 158.0 2.4 796.7 6.4 613.1 4.1 560.3 3.8 0.0 0.0 2 53 Prince George 158.0 0.6 781.0 1.7 395.0 0.5 

9 51 Granisle 40.21 Granisle 2 53 Prince George 327.0 52.6 407.8 28.9 365.9 26.0 503.8 0.4 2 53 Prince George 327.0 1.8 796.7 2.3 613.1 1.5 560.3 1.4 0.0 0.0 2 53 Prince George 327.0 0.5 781.0 0.6 395.0 0.2 

9 51 Houston 72.83 Houston 2 53 Prince George 308.0 392.5 407.8 229.4 365.9 205.9 503.8 3.5 2 53 Prince George 308.0 13.2 796.7 18.4 613.1 11.8 560.3 10.8 0.0 0.0 2 53 Prince George 308.0 3.5 781.0 4.7 395.0 1.4 

9 51 Smithers 15.69 Smithers 2 53 Prince George 371.0 821.1 407.8 398.4 365.9 357.5 503.8 6.0 2 53 Prince George 371.0 27.7 796.7 31.9 613.1 20.5 560.3 18.7 0.0 0.0 2 53 Prince George 371.0 7.3 781.0 8.2 395.0 2.4 

9 51 Telkwa 6.56 Telkwa 2 53 Prince George 357.0 193.8 407.8 97.7 365.9 87.7 503.8 1.5 2 53 Prince George 357.0 6.5 796.7 7.8 613.1 5.0 560.3 4.6 0.0 0.0 2 53 Prince George 357.0 1.7 781.0 2.0 395.0 0.6 

9 51 Bulkley-Nechako A 3,688.00 Smithers 2 53 Prince George 371.0 814.4 407.8 395.1 365.9 354.6 503.8 6.0 2 53 Prince George 371.0 27.4 796.7 31.7 613.1 20.3 560.3 18.6 0.0 0.0 2 53 Prince George 371.0 7.2 781.0 8.2 395.0 2.4 

9 51 Bulkley-Nechako B 3,628.08 Burns Lake 2 53 Prince George 228.0 206.1 407.8 162.7 365.9 146.0 503.8 2.5 2 53 Prince George 228.0 6.9 796.7 13.0 613.1 8.4 560.3 7.6 0.0 0.0 2 53 Prince George 228.0 1.8 781.0 3.4 395.0 1.0 

9 51 Bulkley-Nechako C 25,663.24 Fort St. James 2 53 Prince George 161.0 82.9 407.8 92.7 365.9 83.2 503.8 1.4 2 53 Prince George 161.0 2.8 796.7 7.4 613.1 4.8 560.3 4.4 0.0 0.0 2 53 Prince George 161.0 0.7 781.0 1.9 395.0 0.6 

9 51 Bulkley-Nechako D 4,382.94 Fraser Lake 2 53 Prince George 158.0 112.1 407.8 127.7 365.9 114.6 503.8 1.9 2 53 Prince George 158.0 3.8 796.7 10.2 613.1 6.6 560.3 6.0 0.0 0.0 2 53 Prince George 158.0 1.0 781.0 2.6 395.0 0.8 

9 51 Bulkley-Nechako E 15,912.95 Burns Lake 2 53 Prince George 228.0 179.1 407.8 141.4 365.9 126.9 503.8 2.1 2 53 Prince George 228.0 6.0 796.7 11.3 613.1 7.3 560.3 6.6 0.0 0.0 2 53 Prince George 228.0 1.6 781.0 2.9 395.0 0.8 

9 51 Bulkley-Nechako G 14,439.62 Houston 2 53 Prince George 320.0 143.8 407.8 80.9 365.9 72.6 503.8 1.2 2 53 Prince George 320.0 4.8 796.7 6.5 613.1 4.2 560.3 3.8 0.0 0.0 2 53 Prince George 320.0 1.3 781.0 1.7 395.0 0.5 

9 49 Aiyansh (Kitladamas) 1 13.37 Aiyansh (Kitladamas) 1 2 53 Prince George 616.0 0.0 407.8 0.0 365.9 0.0 503.8 0.0 2 53 Prince George 616.0 0.0 796.7 0.0 613.1 0.0 560.3 0.0 0.0 0.0 2 53 Prince George 616.0 0.0 781.0 0.0 395.0 0.0 

9 49 Gingolx 5.26 Gingolx 2 53 Prince George 693.0 102.9 407.8 26.7 365.9 24.0 503.8 0.4 2 53 Prince George 693.0 3.5 796.7 2.1 613.1 1.4 560.3 1.3 0.0 0.0 2 53 Prince George 693.0 0.9 781.0 0.6 395.0 0.2 

9 49 Gitwinksihlkw 3.01 Gitwinksihlkw 2 53 Prince George 629.0 53.1 407.8 15.2 365.9 13.6 503.8 0.2 2 53 Prince George 629.0 1.8 796.7 1.2 613.1 0.8 560.3 0.7 0.0 0.0 2 53 Prince George 629.0 0.5 781.0 0.3 395.0 0.1 

9 49 Hazelton 2.85 Hazelton 2 53 Prince George 444.0 51.2 407.8 20.7 365.9 18.6 503.8 0.3 2 53 Prince George 444.0 1.7 796.7 1.7 613.1 1.1 560.3 1.0 0.0 0.0 2 53 Prince George 444.0 0.5 781.0 0.4 395.0 0.1 

9 49 Kitimat 242.63 Kitimat 2 53 Prince George 632.0 2272.2 407.8 647.1 365.9 580.8 503.8 9.8 2 53 Prince George 632.0 76.6 796.7 51.9 613.1 33.3 560.3 30.4 0.0 0.0 2 53 Prince George 632.0 20.1 781.0 13.4 395.0 3.9 

9 49 Laxgalts'ap 17.62 Laxgalts'ap 2 53 Prince George 665.0 138.0 407.8 37.3 365.9 33.5 503.8 0.6 2 53 Prince George 665.0 4.6 796.7 3.0 613.1 1.9 560.3 1.8 0.0 0.0 2 53 Prince George 665.0 1.2 781.0 0.8 395.0 0.2 

9 49 New Hazelton 25.64 New Hazelton 2 53 Prince George 439.0 107.2 407.8 44.0 365.9 39.5 503.8 0.7 2 53 Prince George 439.0 3.6 796.7 3.5 613.1 2.3 560.3 2.1 0.0 0.0 2 53 Prince George 439.0 0.9 781.0 0.9 395.0 0.3 

9 49 Nisga'a 1,946.27 Terrace 2 53 Prince George 576.0 26.2 407.8 8.2 365.9 7.4 503.8 0.1 2 53 Prince George 576.0 0.9 796.7 0.7 613.1 0.4 560.3 0.4 0.0 0.0 2 53 Prince George 576.0 0.2 781.0 0.2 395.0 0.0 

9 49 Terrace 41.52 Terrace 2 53 Prince George 576.0 2716.4 407.8 848.8 365.9 761.8 503.8 12.8 2 53 Prince George 576.0 91.5 796.7 68.0 613.1 43.6 560.3 39.9 0.0 0.0 2 53 Prince George 576.0 24.1 781.0 17.5 395.0 5.1 

9 49 Kitimat-Stikine B 7,464.34 Smithers 2 53 Prince George 371.0 232.9 407.8 113.0 365.9 101.4 503.8 1.7 2 53 Prince George 371.0 7.8 796.7 9.1 613.1 5.8 560.3 5.3 0.0 0.0 2 53 Prince George 371.0 2.1 781.0 2.3 395.0 0.7 

9 49 Kitimat-Stikine C (Part 1) 9,679.06 Kitimat 2 53 Prince George 632.0 746.1 407.8 212.5 365.9 190.7 503.8 3.2 2 53 Prince George 632.0 25.1 796.7 17.0 613.1 10.9 560.3 10.0 0.0 0.0 2 53 Prince George 632.0 6.6 781.0 4.4 395.0 1.3 

9 49 Kitimat-Stikine C (Part 2) 18,101.81 Kitimat 2 53 Prince George 632.0 0.9 407.8 0.3 365.9 0.2 503.8 0.0 2 53 Prince George 632.0 0.0 796.7 0.0 613.1 0.0 560.3 0.0 0.0 0.0 2 53 Prince George 632.0 0.0 781.0 0.0 395.0 0.0 

9 49 Kitimat-Stikine E 16.39 Terrace 2 53 Prince George 576.0 935.1 407.8 292.2 365.9 262.2 503.8 4.4 2 53 Prince George 576.0 31.5 796.7 23.4 613.1 15.0 560.3 13.7 0.0 0.0 2 53 Prince George 576.0 8.3 781.0 6.0 395.0 1.8 

9 47 Port Edward 168.12 Port Edward 2 53 Prince George 710.0 164.1 407.8 41.6 365.9 37.3 503.8 0.6 2 53 Prince George 710.0 5.5 796.7 3.3 613.1 2.1 560.3 2.0 0.0 0.0 2 53 Prince George 710.0 1.5 781.0 0.9 395.0 0.2 

9 47 Prince Rupert 54.90 Prince Rupert 2 53 Prince George 718.0 3684.4 407.8 923.6 365.9 828.9 503.8 14.0 2 53 Prince George 718.0 124.1 796.7 74.0 613.1 47.5 560.3 43.4 0.0 0.0 2 53 Prince George 718.0 32.6 781.0 19.1 395.0 5.5 

9 47 Skeena-Queen Charlotte A 2,930.73 Prince Rupert 2 53 Prince George 718.0 11.6 407.8 2.9 365.9 2.6 503.8 0.0 2 53 Prince George 718.0 0.4 796.7 0.2 613.1 0.1 560.3 0.1 0.0 0.0 2 53 Prince George 718.0 0.1 781.0 0.1 395.0 0.0 

9 47 Skeena-Queen Charlotte C 6,514.17 Prince Rupert 2 53 Prince George 718.0 9.6 407.8 2.4 365.9 2.2 503.8 0.0 2 53 Prince George 718.0 0.3 796.7 0.2 613.1 0.1 560.3 0.1 0.0 0.0 2 53 Prince George 718.0 0.1 781.0 0.0 395.0 0.0 

10 41 Cariboo J 25,948.44 Alexis Creek 2 53 Prince George 353.0 135.4 407.8 69.0 365.9 62.0 503.8 1.0 2 53 Prince George 353.0 3.3 796.7 4.0 613.1 2.6 560.3 2.3 0.0 0.0 2 53 Prince George 353.0 0.8 781.0 0.9 395.0 0.3 

10 45 Central Coast A 19,876.88 Bella Coola 2 53 Prince George 700.0 47.2 407.8 12.1 365.9 10.9 503.8 0.2 2 53 Prince George 700.0 1.1 796.7 0.7 613.1 0.5 560.3 0.4 0.0 0.0 2 53 Prince George 700.0 0.3 781.0 0.2 395.0 0.0 

10 45 Central Coast C 3,987.48 Bella Coola 2 53 Prince George 700.0 169.8 407.8 43.7 365.9 39.2 503.8 0.7 2 53 Prince George 700.0 4.1 796.7 2.5 613.1 1.6 560.3 1.5 0.0 0.0 2 53 Prince George 700.0 1.0 781.0 0.6 395.0 0.2 

10 45 Central Coast D 304.14 Bella Coola 2 53 Prince George 700.0 130.3 407.8 33.5 365.9 30.1 503.8 0.5 2 53 Prince George 700.0 3.2 796.7 1.9 613.1 1.2 560.3 1.1 0.0 0.0 2 53 Prince George 700.0 0.7 781.0 0.4 395.0 0.1 

10 45 Central Coast E 360.18 Bella Coola 2 53 Prince George 700.0 41.6 407.8 10.7 365.9 9.6 503.8 0.2 2 53 Prince George 700.0 1.0 796.7 0.6 613.1 0.4 560.3 0.4 0.0 0.0 2 53 Prince George 700.0 0.2 781.0 0.1 395.0 0.0 

10 43 Mount Waddington A 12,737.46 Port McNeill 8 21 Nanaimo 362.0 210.6 53.0 13.6 266.1 68.3 503.8 1.6 8 21 Nanaimo 362.0 5.1 486.3 3.7 613.1 3.9 560.3 3.5 0.0 0.0 8 21 Nanaimo 362.0 1.2 907.0 1.6 655.2 0.7 

10 27 Powell River 29.77 Powell River 8 21 Nanaimo 169.0 1092.8 53.0 151.4 266.1 759.4 503.8 17.6 8 21 Nanaimo 169.0 26.6 486.3 41.1 613.1 43.2 560.3 39.4 0.0 0.0 8 21 Nanaimo 169.0 6.3 907.0 18.1 655.2 7.5 

10 27 Sechelt (Part) 0.24 Powell River 8 21 Nanaimo 169.0 0.9 53.0 0.1 266.1 0.6 503.8 0.0 8 21 Nanaimo 169.0 0.0 486.3 0.0 613.1 0.0 560.3 0.0 0.0 0.0 8 21 Nanaimo 169.0 0.0 907.0 0.0 655.2 0.0 

10 27 Powell River A 3,898.07 Powell River 8 21 Nanaimo 169.0 73.7 53.0 10.2 266.1 51.2 503.8 1.2 8 21 Nanaimo 169.0 1.8 486.3 2.8 613.1 2.9 560.3 2.7 0.0 0.0 8 21 Nanaimo 169.0 0.4 907.0 1.2 655.2 0.5 

10 27 Powell River B 130.52 Powell River 8 21 Nanaimo 169.0 127.8 53.0 17.7 266.1 88.8 503.8 2.1 8 21 Nanaimo 169.0 3.1 486.3 4.8 613.1 5.0 560.3 4.6 0.0 0.0 8 21 Nanaimo 169.0 0.7 907.0 2.1 655.2 0.9 

10 27 Powell River C 642.34 Powell River 8 21 Nanaimo 169.0 172.1 53.0 23.8 266.1 119.6 503.8 2.8 8 21 Nanaimo 169.0 4.2 486.3 6.5 613.1 6.8 560.3 6.2 0.0 0.0 8 21 Nanaimo 169.0 1.0 907.0 2.8 655.2 1.2 

10 27 Powell River D 300.44 Powell River 8 21 Nanaimo 169.0 92.4 53.0 12.8 266.1 64.2 503.8 1.5 8 21 Nanaimo 169.0 2.2 486.3 3.5 613.1 3.6 560.3 3.3 0.0 0.0 8 21 Nanaimo 169.0 0.5 907.0 1.5 655.2 0.6 

10 27 Powell River E 73.57 Powell River 8 21 Nanaimo 169.0 29.9 53.0 4.1 266.1 20.8 503.8 0.5 8 21 Nanaimo 169.0 0.7 486.3 1.1 613.1 1.2 560.3 1.1 0.0 0.0 8 21 Nanaimo 169.0 0.2 907.0 0.5 655.2 0.2 

11 47 Masset 19.45 Masset 2 53 Prince George 1020.0 5.2 407.8 0.9 365.9 0.8 503.8 0.0 2 53 Prince George 1020.0 9.6 796.7 4.0 613.1 2.6 560.3 2.4 0.0 0.0 2 53 Prince George 1020.0 9.4 781.0 3.9 395.0 1.1 

11 47 Port Clements 13.59 Port Clements 2 53 Prince George 951.0 2.0 407.8 0.4 365.9 0.3 503.8 0.0 2 53 Prince George 951.0 3.8 796.7 1.7 613.1 1.1 560.3 1.0 0.0 0.0 2 53 Prince George 951.0 3.7 781.0 1.6 395.0 0.5 

11 47 Queen Charlotte 37.28 Queen Charlotte 2 53 Prince George 922.0 4.4 407.8 0.9 365.9 0.8 503.8 0.0 2 53 Prince George 922.0 8.1 796.7 3.8 613.1 2.4 560.3 2.2 0.0 0.0 2 53 Prince George 922.0 8.0 781.0 3.7 395.0 1.1 

11 47 Skeena-Queen Charlotte D 6,534.37 Port Clements 2 53 Prince George 951.0 3.3 407.8 0.6 365.9 0.6 503.8 0.0 2 53 Prince George 951.0 6.1 796.7 2.8 613.1 1.8 560.3 1.6 0.0 0.0 2 53 Prince George 951.0 6.0 781.0 2.7 395.0 0.8 

11 47 Skeena-Queen Charlotte E 3,432.42 Port Clements 2 53 Prince George 951.0 1.9 407.8 0.4 365.9 0.3 503.8 0.0 2 53 Prince George 951.0 3.5 796.7 1.6 613.1 1.0 560.3 0.9 0.0 0.0 2 53 Prince George 951.0 3.4 781.0 1.5 395.0 0.4 

Notes: 

(1) Strathcona and Comox Valley RDs were combined for 2006 census, named 'Comox- 

Strathcona RD'. Comox Valley RD (25) used. 

(2) The closest available municipality with a Local Collection Facility was chosen for each 

census subdivision. 

(3) The municipality with a Major Collector closest to the Local Collector for each 

subdivision was chosen. In the case that the Major Collector did not accept one type of 

material, the next closest Major Collector was selected for that material. 

(4) In the case that more than one Local Collector or Major Collector exists in the same 

municipality, the start or end point for calculating the distance was set to Google Maps' 

default center for that particular municipality. 

(5) In the case that more than one Major Collector or Processor exists in the same 

municipality, the start or end point for calculating the distance was set to Google Maps' 

default center for that particular municipality. 

CRA 071620 (2) 

Totals of Diesel Consumed (L) 90,563.3 88,826.3 168,154.0 3,586.3 2,884.3 10,153.8 11,869.8 11,137.1 2.3 833.2 2,357.4 1,938.2 

Page 6 of 6

TABLE 4.1 

RESULTS OF THE GHG SAVINGS STUDY 


BCUOMA 

Total 

Emissions/process 

GWP 100a IPCC 2007 Climate Change kg CO 2 e 



Project PE1 Transportation (from generator to registered collector) 243,700 


- transport by truck 239,026 

- transport by rail 10,739 

PE3 Re-refining of oil at registered processing facilities into new products 8,962,833 

Baseline BE1 Crude oil extraction 9,778,366 

Use as a Fuel 

BE2 Transportation of crude oil to refinery 270,344 

BE3 Refine crude oil into oil products 11,864,278 

BE4 Combustion of oil for heat at generators 77,079,708 

Page 1 of 3 

Project PE1 Transportation (from generator to registered collector) 0 Included in Re-refine/Reuse PE1 

PE2 Transportation (from registered collector to asphalt plants and pulp mills) 452,492 

PE3 Combustion of the used oil at pulp mills and asphalt plants 63,065,215 

Baseline BE1 Crude oil extraction 9,302,885 

CRA 071620 (2) 

BE2 Transportation of crude oil to refinery 257,198 

BE3 Refine crude oil into oil products 11,287,368 

BE4 Combustion of oil for heat at generators 63,065,215

TABLE 4.1 



BCUOMA 

Total 






PE2 Transportation (from registered collector to registered steel oil filter processor) 27,323 


Electricity Production 5,543 

Natural Gas - Production, Processing, and Distributing 18,445 

Natural Gas - Combustion for Heat 103,692 

Propane - Production of Liquid Propane Gas 6,317 

Propane - Combustion for Fuel (forklift) 24,789 

PE4 Transportation of steel to metal broker 31,941 

PE5 Transportation of steel to steel mill 29,969 

Baseline BE1 Production of steel 5,624,291 

Paper Filters 

BE2 Transportation of steel to steel mill 0 Included in BE1 above 

BE3 Transportation of steel filters to disposal facility 33,578 

Page 2 of 3 

Project PE1 Transportation (from generator to registered collector) 0 Included in Metal Filters PE1 

PE2 Transportation (from registered collector to registered paper oil filter processor) 0 Included in Metal Filters PE2 


Electricity Production 731 



Propane - Production of Liquid Propane Gas 549 


Incinerating paper filters 7,474 

Baseline BE1 Transportation of paper filters to landfill 0 Included in Metal Filters BE3 

CRA 071620 (2) 

BE2 Decomposition of paper filters in landfill (20 year time period) 14,813 

(Note: CRA completed landfill gas modelling separate from this file)

TABLE 4.1 



BCUOMA 

Total 





PE2 Transportation (from registered collector to registered oil container processor) 6,344 


Electricity Production 10,072 



Propane - Production of Liquid Propane Gas 2,039 


PE4 Transportation of HDPE pellets to plastics manufacturer 5,216 

Baseline BE1 Production of HDPE 2,239,541 

SUMMARY OF RESULTS 



BE2 Transportation of HDPE to plastics manufacturer 0 Included in BE1 above 

BE3 Transportation of oil containers to disposal facility 32,103 

TOTAL EMISSIONS (Re-refined oil) (Baseline - Project) 89,536,397 kg CO 2e 

Emissions per L of oil that is collected and re-refined (Baseline - Project) 3.65 kg CO 2e/L collected oil 

TOTAL EMISSIONS (Collected Oil Used as Fuel) (Baseline - Project) 20,394,960 kg CO 2e 

Emissions per L of oil that is collected and used as a fuel (Baseline - Project) 1.02 kg CO 2e/L collected oil 

TOTAL EMISSIONS (Re-refined oil and Collected Oil Used as Fuel) (Baseline - Project) 109,931,357 kg CO 2e 

Total Emissions per L of oil that is collected and re-refined or used as a fuel (Baseline - Project) 2.47 kg CO 2e/L collected oil 

TOTAL EMISSIONS (Metal Filters) (Baseline - Project) 5,402,089 kg CO 2e 

TOTAL EMISSIONS (Paper Filters) (Baseline - Project) -6,717 kg CO 2e 

TOTAL EMISSIONS (Metal and Paper Filters) (Baseline - Project) 5,395,372 kg CO 2e 

Emissions per filter that is collected and recycled in a steel mill (Baseline - Project) 1.09 kg CO 2e/recycled filter 

Page 3 of 3 


TOTAL EMISSIONS (Baseline - Project) 2,198,298 kg CO2e Emissions per kg oil container collected and processed for sale as HDPE pellets (Baseline - Project) 2.11 kg CO2e/kg recycled container 

Note: For the summary tables above, positive emissions indicate GHG savings and negative emissions indicate an increase in GHG emissions. 

CRA 071620 (2)

071620 (2) 

APPENDIX A 

RAW PROCESSING FACILITY COLLECTION DATA

071620 (2) 

APPENDIX B 

DATA CALCULATIONS

APPENDIX B 

DATA CALCULATIONS 


BCUOMA 



PE1 Transportation (from generator to registered collector) 

Total diesel required 90,563.26 L diesel use this number to calculate emissions from Re-refine and Reuse PE1 


- transport by truck to Registered Processor 

Total diesel required 

- transport by rail 

88,826.26 L diesel use this number to calculate emissions from Re-refine and Reuse PE2 

Total diesel required 3,586.31 L diesel use this number to calculate emissions from Re-refine and Reuse PE2 


Total oil recycled for re-refining in project 24,500,300.00 L use this number to calculate emissions from Re-refine and Reuse PE3 

BE1 Crude oil extraction 

Total oil recycled for re-refining in project 24,500,300.00 L 

Total oil re-refined (14% loss rate as per Safety-Kleen operation) 21,070,258.00 L 

Crude oil required for heavy oil production 1.42 BTU heavy oil / 

BTU crude oil References: (1) Heating value of lube oil: Harvey, D.G., 1977, p. 10; 

(2) Heating value of crude oil: US DOE, 2008 

Total crude oil required 29,948,380.54 L 

Total crude oil per barrel 159.00 L/bbl Reference: The Quiet Road. Carbon dioxide emissions per barrel of crude. 

Available at: http://numero57.net/?p=255 

Total barrels of crude oil 188,354.59 bbl use this number to calculate emissions from Re-refine and Reuse BE1 



Estimated distance to transport crude (from Alberta to BC) 1,000.00 km (Assumed straight line from oil sands in Athabasca, Alberta to Chevron Corporation 

refinery in Burnaby, BC) 

Total Lkm (crude oil) 29,948.38 1x10 6 Lkm use this number to calculate emissions from Re-refine and Reuse BE2 



Density of crude oil 920 kg/m 3 

Reference: SIMetric.co.uk. Average for California, Texas, and Mexico assumed. 

Available at: http://www.simetric.co.uk/si_liquids.htm 

Total weight of crude required 27,562,492.89 kg use this number to calculate emissions from Re-refine and Reuse BE4 


Total oil recycled for re-refining in project 24,500,300.00 L use this number to calculate emissions from Re-refine and Reuse BE4 

Use as a Fuel 


Total diesel required 0 

(Included in Re-refine/Reuse PE1) 

L diesel use this number to calculate emissions from Use as a Fuel PE1 


Total diesel required 168,153.96 L diesel use this number to calculate emissions from Use as a Fuel PE2 


Total oil combusted in pulp mills and asphalt plants 20,045,700.00 L use this number to calculate emissions from Use as a Fuel PE3 

CRA 071620 (2) 

Page 1 of 6

APPENDIX B 



BCUOMA 

BE1 Crude oil extraction 

Total oil sent for fuel use in project 20,045,700.00 L 

Crude oil required for heavy oil production 1.42 BTU heavy oil / 

BTU crude oil References: (1) Heating value of lube oil: Harvey, D.G., 1977, p. 10; 

(2) Heating value of crude oil: US DOE, 2008 


Total crude oil per barrel 159 L/bbl Reference: The Quiet Road. Carbon dioxide emissions per barrel of crude. 

Available at: http://numero57.net/?p=255 

Total barrels of crude oil 179,195.70 bbl use this number to calculate emissions from Use as a Fuel BE1 



Estimated distance to transport crude (from Alberta to BC) 1,000.00 km (Assumed straight line from oil sands in Athabasca, Alberta to Chevron Corporation 

refinery in Burnaby, BC) 

Total Lkm (crude oil) 28,492.12 1x10 6 Lkm use this number to calculate emissions from Use as a Fuel BE2 



Density of crude oil 920 kg/m 3 

Reference: SIMetric.co.uk. Average for California, Texas, and Mexico assumed. 

Available at: http://www.simetric.co.uk/si_liquids.htm 

Total weight of crude required 26,222,244.82 kg use this number to calculate emissions from Use as a Fuel BE3 


Total oil sent for fuel use in project 20,045,700.00 L use this number to calculate emissions from Use as a Fuel BE4 




Total diesel required 2,884.29 L diesel use this number to calculate emissions from Metal Oil Filters PE1 

PE2 Transportation (from registered collector to registered steel oil filter processor) 



CRA 071620 (2) 

Energy requirements for M&R Environmental Reference: Provided by Rahmet Vefghi from M&R Environmental via email on July 14, 201 

2007 2008 Average Usages 

Electricity (kWh) 245,412 339,943 292,678 Office and plant requirements 

Natural gas (GJ) 4,490 5,104 720 Heating for plant and distillation (approx. 85% used in distillation unit for antifreeze - assum 

Diesel (L) 112,840 132,946 not applicable Transportation (collection) 

Bio-diesel (L) 84,883 104,264 not applicable Transportation (collection) 

Gasoline (L) 31,524 37,615 not applicable Transportation (employees, sales reps, etc.) 

Propane (L) 6,342 7,781 7,062 Fork lifts in plant 

Notes: 

15% natural gas to be distributed between steel filters, paper filters and containers based on weight recycled. 

Fork lift energy usage to be divided between steel filters, paper filters, and containers based on weight recycled. 

Electrical energy requirements for steel filter, paper filter, and container processing to be calculated based on industrial equipment similar to what is used. 

Energy requirements for oil at M&R Environmental is minimal. Oil is collected in pumper truck, which is pumped to tanks by an electrical pump then sent to customer for reuse or re-refining. 

Energy requirements assumed negligible. 

Amount of materials recycled by M&R not available for 2007 or 2008, therefore, average energy requirements for each year assumed and amounts of recycled material used for 2009. 

Page 2 of 6

CRA 071620 (2) 

Amount processed by M & R Environmental (2009) 

Total Filters 1,095,342 kg 

Steel Filters 1,007,714 kg 

Paper Filters 87,627 kg 

Oil Containers 468,752 kg 

Electricity 

APPENDIX B 



BCUOMA 

Filter Crusher 

Notes: 

1. Actual plant data for electricity requirements of filter crusher unavailable. Assumed requirements similar to another filter crusher found (Filtermatic) 

2. Once the electricity requirements are estimated for crushing all the filters (steel and paper), the remaining electricity will be assumed for the processing of oil containers. 

3. 20% of the total electricity requirements has been assumed for the office, which will be distributed between the steel filters, paper filters, and containers by weight. 

Filtermatic 

Voltage (outlet) 110 Volts Reference: Email from Zach Arnold, Arnold Machine Inc., Filtermatic Distributor, July 26, 2 

Current (at full load) 15 Amps Reference: Email from Zach Arnold, Arnold Machine Inc., Filtermatic Distributor, July 26, 2 

Hydraulic pump motor will run idle for around 60 seconds without filters then automatically shut off and restart when more filters are added. 

Assumed crusher runs continuously throughout the day, therefore idle energy usage is minimal. 

The crusher will process 50 - 60 filters per hour. Assume 55 per hour. Reference: Email from Zach Arnold, Arnold Machine Inc., Filtermatic Distributor, July 26, 2 

55 filters/hr 

P (watts) = V (volts) * I (amps) 1,650 Watts 

M & R Environmental 

Total steel filters to crush in 2009 1,344,611.12 steel filters 

Total paper filters to crush in 2009 116,922.71 paper filters 

Total time required to crush steel filters 24,447.47 hours 

2,037.29 days (at 12 hrs per day) 

Electricity required to crush steel filters 40,338,333.68 Wh 

Electricity required for crusher (steel filters) 40,338.33 kWh 

Total time required to crush paper filters 4,251.73 hours (paper filters are crushed twice at M&R to remove more oil) 

354.31 days (at 12 hrs per day) 

Electricity required to crush paper filters 7,015,362.38 Wh 

Electricity required for crusher (paper filters) 7,015.36 kWh 

Office Electricity Requirements (assumed 20% of total) 

Office electricity requirements 58,535.50 kWh 

Steel Filters 37,713.26 kWh (Divided based on weight) 

Paper Filters 3,279.41 kWh 

Oil Containers 17,542.83 kWh 

Page 3 of 6

Oil Container Processing 

APPENDIX B 



BCUOMA 

Assumed electricity requirements for oil container processing are the total electricity requirements for M & R minus electricity requirements to crush filters and requirements for office. 

Electricity required to process oil containers 186,788.30 kWh 

Steel Filters 78,051.59 kWh for M & R 

Paper Filters 10,294.78 kWh for M & R 

0.077 kWh/kg 

277,166.19 kWh (total) use this number to calculate emissions from Metal Oil Filters PE3 (electricity) 

0.117 kWh/kg 

Oil Containers 204,331.13 kWh for M & R 

Natural Gas 

36,557.41 kWh (total) use this number to calculate emissions from Paper Oil Filters PE3 (electricity) 

0.436 kWh/kg 

503,582.10 kWh (total) use this number to calculate emissions from Oil Containers PE3 (electricity) 

Steel Filters 463.61 GJ for M & R 

4.60E-04 GJ/kg 

1,646.30 GJ (total) use this number to calculate emissions from Metal Oil Filters PE3 (natural gas) 

Paper Filters 40.31 GJ for M & R 

4.60E-04 GJ/kg 

Oil Containers 215.65 GJ for M & R 

Propane 

143.16 GJ (total) use this number to calculate emissions from Paper Oil Filters PE3 (natural gas) 

4.60E-04 GJ/kg 

531.48 GJ (total) use this number to calculate emissions from Oil Containers PE3 (natural gas) 

Steel Filters 4,549.58 L for M & R 

4.51E-03 L/kg 

16,155.86 L (total) use this number to calculate emissions from Metal Oil Filters PE3 (propane) 

Paper Filters 395.62 L for M & R 

4.51E-03 L/kg 

1,404.86 L (total) use this number to calculate emissions from Paper Oil Filters PE3 (propane) 

Oil Containers 2,116.30 L for M & R 

4.51E-03 L/kg 

5,215.70 L (total) use this number to calculate emissions from Oil Containers PE3 (propane) 





BE1 Production of steel 

Total number of steel filters recycled 4,774,800.00 steel filters 

Total weight of steel filters 2,683,843.32 kg 

Divided by 1000 2,683.84 1000 kg use this number to calculate emissions from Metal Oil Filters BE1 

CRA 071620 (2) 

Page 4 of 6

APPENDIX B 



BCUOMA 



(Included in BE1 above) 

L diesel use this number to calculate emissions from Metal Oil Filters BE2 

BE3 Transportation of steel filters to landfill 


(metal assumed inert material - no LFG production) 

12,478.33 L diesel use this number to calculate emissions from Metal Oil Filters BE3 

Paper Oil Filters 



(Included in Metal Filters PE1) 

L diesel use this number to calculate emissions from Paper Oil Filters PE1 



(Included in Metal Filters PE2) 

L diesel use this number to calculate emissions from Paper Oil Filters PE2 


Total electricity required 36,557.41 kWh use this number to calculate emissions from Paper Oil Filters PE3 (electricity) 

Total natural gas required 143.16 GJ use this number to calculate emissions from Paper Oil Filters PE3 (natural gas) 

Total propane required 1,404.86 L use this number to calculate emissions from Paper Oil Filters PE3 (propane) 

Total mass of paper filters incinerated 311,170.24 kg use this number to calculate emissions from Paper Oil Filters PE3 (incineration) 

BE1 Transportation of paper filters to landfill 


(Included in Metal Filters BE3) 

L diesel use this number to calculate emissions from Paper Oil Filters BE1 


*CRA completed landfill gas modelling separate from this file 



Total diesel required 833.25 L diesel use this number to calculate emissions from Recycled Oil Containers PE1 


Total diesel required 2,357.37 L diesel use this number to calculate emissions from Recycled Oil Containers PE2 


Total electricity required 503,582.10 kWh use this number to calculate emissions from Oil Containers PE3 (electricity) 

Total natural gas required 531.48 GJ use this number to calculate emissions from Oil Containers PE3 (natural gas) 

Total propane required 5,215.70 L use this number to calculate emissions from Oil Containers PE3 (propane) 


Total diesel required 1,938.18 L diesel use this number to calculate emissions from Recycled Oil Containers PE4 

CRA 071620 (2) 

Page 5 of 6

APPENDIX B 



BCUOMA 

BE1 Production of HDPE 

Total weight of plastic containers 1,039,731.62 kg 

Divided by 1000 1,039.73 1000 kg use this number to calculate emissions from Recycled Oil Containers BE1 



(Included in BE1 above) 

L diesel use this number to calculate emissions from Recycled Oil Containers BE2 



(plastics are assumed inert material - no LFG production) 

11,929.99 L diesel use this number to calculate emissions from Recycled Oil Containers BE3 

back to top 

CRA 071620 (2) 

Page 6 of 6

071620 (2) 

APPENDIX C 

RAW EMISSION FACTOR DATA (GLOBAL WARMING POTENTIAL)

Emission Factor (GHG) Data Per Element 










Use as a Fuel 











PE2 Transportation (from regstered collector to registered steel oil filter processor) 




Baseline BE1 Production of steel 


BE3 Transportation of steel filters to disposal facility 

Paper Filters 




Baseline BE1 Transportation of paper filters to landfill 







Baseline BE1 Production of HDPE 



CRA 071620 (2) 

APPENDIX C 

RAW EMISSION FACTOR DATA (GLOBAL WARMING POTENTIAL) 


BCUOMA 

Page 1 of 11


APPENDIX C 



BCUOMA 


PE1 Transportation (from generator to registered collector) (re-refine and reuse) 

back to top Energy Mobile Combustion Sources - Road Transport Environment Canada, National Inventory Report, Greenhouse Gas Sources and Sinks in Canada, 1990-2008. Ta 

Heavy Duty Diesel Vehicles (Moderate Control) (weight of truck and load greater than 3900 kg) 

kg CO 2e 

Emission 

kg CO 2e/unit 

Carbon dioxide 2663 g CO 2/L 1 2.663 

Methane 0.14 g CH 4/L 25 0.004 

Nitrous oxide 0.082 g N 2O/L 298 0.024 

PE2 Transportation (from registered collector to registered processor) (rerefine and reuse) See Recycled Oil, Re‐refine and Reuse, PE1, Transportation (from generator to registered collector) 

back to top For transport by truck 

Transport to Breslau, Ontario by rail Environment Canada, National Inventory Report, Greenhouse Gas Sources and Sinks in Canada, 1990-2008. Ta 

Diesel Train 

kg CO 2e 

Emission 

kg CO 2e/unit 


Methane 0.15 g CH 4/L 25 0.004 



back to top Emission factors from the report, "Safety-Kleen Product Carbon Footprint for Re-refined Base Oil", prepared for Safety-Kleen Systems, Inc., 

prepared by ENVIRON International Corporation, dated October 2009. 

CRA 071620 (2) 

Table 3-2 Emissions 

Re-refinery input materials 90 g CO 2e/gal base oil produced (assumes 14% loss rate) 

re-refinery diesel 3 g CO 2e/gal base oil produced (assumes 14% loss rate) 

re-refinery electricity 202 g CO 2e/gal base oil produced (assumes 14% loss rate) 

re-refinery natural gas 732 g CO 2e/gal base oil produced (assumes 14% loss rate) 

re-refinery fuel (co-products consumed on-site) 536 g CO 2e/gal base oil produced (assumes 14% loss rate) 

Waste (including energy recovery) 2.8 g CO 2e/gal base oil produced (assumes 14% loss rate) 

Co-products -181 g CO 2e/gal base oil produced (assumes 14% loss rate) (offsetting the production of other materials) 

Used Oil Input (virgin embodied) 14% loss rate is accounted for in the baseline - baseline oil quantity decreased by 14% 

Total emissions 1,384.80 g CO 2e/gal base oil produced 

0.37 kg CO 2e/L oil produced 

Page 2 of 11

APPENDIX C 



BCUOMA 

BE1 Crude oil extraction (re-refine and reuse) 

back to top Produce Heavy Crude Oil 

Air emissions associated with initial oil well 

development, including exploratory drilling, 

development drilling and production. 

Canadian-based data. Does not include transmission of oil. 

Pembina Institute, Produce Crude Oil (Heavy crude oil) 

Carbon dioxide equivalents (unit = 1 bbl crude oil) 96.814 kg CO 2e/unit 

Produce Light and Medium Crude Oil Pembina Institute, Produce Crude Oil (Light and medium crude oil) 

Air emissions associated with initial oil well 

development, including exploratory drilling, 

development drilling and production. 

Canadian-based data. Does not include transmission of oil. 

Carbon dioxide equivalents (unit = 1 bbl crude oil) 29.465 kg CO 2e/unit 

Breakdown of light, medium, and heavy oil not provided; assumed 30% of each 

Therefore, weighted emission factor 51.91 kg CO 2e/unit 

BE2 Transportation of crude oil to refinery (re-refine and reuse) 

back to top Crude Oil Transmission Pembina Institute, Transmit Crude Oil 

The piping of crude oil using diesel generators 

US data, 1991. Only CO2 emissions. Fugitive emissions not accounted for. 

CRA 071620 (2) 

Carbon dioxide emissions (unit = 1x10 6 lkm) 9.026986 kg CO 2e/unit 

Page 3 of 11

APPENDIX C 



BCUOMA 

BE3 Refine crude oil into oil products (re-refine and reuse) 

back to top Bitumen, at refinery Ecoinvent Database 

Survey of Eurpoean refineries for 1 kg crude oil through refinery. 

All processes in the refinery site excluding the emissions from combustion facilities, including waste water treatment, process emissions and direct discharges to rivers. 

Description of all flows of materials and energy due to the throughput of 1kg crude oil in the refinery. 

CRA 071620 (2) 

Name Unit Category kg CO 2e Subcategory 

Mean Value 

kg/unit 

Emission 

kg CO 2e/unit 

Carbon dioxide, fossil kg air 1 high population density 0.17648 0.17648 

Carbon dioxide, fossil kg air 1 low population density 0.18956 0.18956 

Carbon dioxide, fossil kg air 1 lower stratosphere + upper troposphere 1.2762E-08 1.2762E-08 

Carbon dioxide, fossil kg air 1 unspecified 0.015976 0.015976 

Carbon dioxide, land transformation kg air 1 low population density 0.00001408 0.00001408 

Carbon monoxide, fossil kg air 1.5714 high population density 0.000042 6.59988E-05 

Carbon monoxide, fossil kg air 1.5714 low population density 0.00037319 0.000586431 

Carbon monoxide, fossil kg air 1.5714 lower stratosphere + upper troposphere 1.499E-11 2.35553E-11 

Carbon monoxide, fossil kg air 1.5714 unspecified 0.00022698 0.000356676 

Chloroform kg air 30 high population density 2.5462E-11 7.6386E-10 

Chloroform kg air 30 low population density 9.1182E-13 2.73546E-11 

Chloroform kg air 30 unspecified 8.7759E-20 2.63277E-18 

Dinitrogen monoxide kg air 298 high population density 2.7376E-06 0.000815805 

Dinitrogen monoxide kg air 298 low population density 3.8701E-06 0.00115329 

Dinitrogen monoxide kg air 298 lower stratosphere + upper troposphere 1.2154E-13 3.62189E-11 

Dinitrogen monoxide kg air 298 unspecified 0.000001045 0.00031141 

Ethane, 1,1,1,2-tetrafluoro-, HFC-134a kg air 1430 high population density 6.5154E-13 9.31702E-10 

Ethane, 1,1,1,2-tetrafluoro-, HFC-134a kg air 1430 low population density 4.7994E-11 6.86314E-08 

Ethane, 1,1,1,2-tetrafluoro-, HFC-134a kg air 1430 unspecified 2.4861E-09 3.55512E-06 

Ethane, 1,1,2-trichloro-1,2,2-trifluoro-, CFC-113 kg air 6130 high population density 1.5215E-13 9.3268E-10 

Ethane, 1,1,2-trichloro-1,2,2-trifluoro-, CFC-113 kg air 6130 unspecified 0 

Ethane, 1,1-difluoro-, HFC-152a kg air 124 high population density 6.2333E-11 7.72929E-09 

Ethane, 1,1-difluoro-, HFC-152a kg air 124 low population density 0 

Ethane, 1,2-dichloro-1,1,2,2-tetrafluoro-, CFC-114 kg air 10000 low population density 8.2924E-10 8.2924E-06 

Ethane, 2-chloro-1,1,1,2-tetrafluoro-, HCFC-124 kg air 609 unspecified 0 

Ethane, hexafluoro-, HFC-116 kg air 12200 high population density 1.2022E-11 1.46668E-07 

Ethane, hexafluoro-, HFC-116 kg air 12200 unspecified 4.0057E-10 4.88695E-06 

Methane, biogenic kg air 25 high population density 3.4875E-08 8.71875E-07 

Methane, biogenic kg air 25 low population density 1.2844E-06 0.00003211 

Methane, bromo-, Halon 1001 kg air 25 unspecified 9.4034E-07 2.35085E-05 

Methane, bromochlorodifluoro-, Halon 1211 kg air 1890 low population density 5.9096E-10 1.11691E-06 

Methane, bromotrifluoro-, Halon 1301 kg air 7140 high population density 1.5838E-16 1.13083E-12 

Methane, bromotrifluoro-, Halon 1301 kg air 7140 low population density 3.6366E-08 0.000259653 

Methane, chlorodifluoro-, HCFC-22 kg air 1810 high population density 1.1057E-11 2.00132E-08 

Methane, chlorodifluoro-, HCFC-22 kg air 1810 low population density 2.3112E-09 4.18327E-06 

Methane, chlorotrifluoro-, CFC-13 kg air 14000 unspecified 0 

Methane, dichloro-, HCC-30 kg air 8.7 high population density 3.549E-12 3.08763E-11 

Methane, dichloro-, HCC-30 kg air 8.7 low population density 2.6986E-12 2.34778E-11 

Page 4 of 11

APPENDIX C 



BCUOMA 

Page 5 of 11 

Methane, dichlorodifluoro-, CFC-12 kg air 10900 high population density 1.2761E-12 1.39095E-08 

Methane, dichlorodifluoro-, CFC-12 kg air 10900 low population density 4.7836E-12 5.21412E-08 

Methane, dichlorodifluoro-, CFC-12 kg air 10900 unspecified 1.5816E-19 1.72394E-15 

Methane, dichlorofluoro-, HCFC-21 kg air 210 high population density 1.8537E-15 3.89277E-13 

Methane, fossil kg air 25 high population density 0.000068837 0.001720925 

Methane, fossil kg air 25 low population density 0.0017109 0.0427725 

Methane, fossil kg air 25 lower stratosphere + upper troposphere 2.0257E-13 5.06425E-12 

Methane, fossil kg air 25 unspecified 1.0025E-06 2.50625E-05 

Methane, monochloro-, R-40 kg air 13 high population density 4.4155E-14 5.74015E-13 

Methane, monochloro-, R-40 kg air 13 low population density 4.9275E-12 6.40575E-11 

Methane, tetrachloro-, R-10 kg air 1400 high population density 5.6656E-10 7.93184E-07 

Methane, tetrachloro-, R-10 kg air 1400 unspecified 7.0721E-17 9.90094E-14 

Methane, tetrafluoro-, R-14 kg air 7390 high population density 3.2059E-12 2.36916E-08 

Methane, tetrafluoro-, R-14 kg air 7390 unspecified 3.6052E-09 2.66424E-05 

Methane, trichlorofluoro-, CFC-11 kg air 4750 high population density 3.0093E-15 1.42942E-11 

Methane, trifluoro-, HFC-23 kg air 14800 high population density 5.8981E-13 8.72919E-09 

Nitrogen fluoride kg air 17200 high population density 0 

Sulfur hexafluoride kg air 22800 high population density 0 

Sulfur hexafluoride kg air 22800 low population density 3.9467E-12 8.99848E-08 

Sulfur hexafluoride kg air 22800 unspecified 1.0784E-08 0.000245875 

0.430450114 Total emissions for 1 k 

crude oil through refi 

BE4 Combustion of oil for heat at generators (re-refine and reuse) 

back to top Heavy Oil Combustion (Industrial) Environment Canada, National Inventory Report, Greenhouse Gas Sources and Sinks in Canada, 1990-2008 

kg CO 2e 

Emission 

kg CO 2e/unit 


Methane 0.12 g CH 4/L 25 0.003 


Use as a Fuel 

PE1 Transportation (from generator to registered collector) (use as a fuel) See Recycled Oil, Re‐refine and Reuse, PE1, Transportation (from generator to registered collector) 

back to top 

PE2 Transportation (from registered collector to asphalt plants and pulp mills) See Recycled Oil, Re‐refine and Reuse, PE1, Transportation (from generator to registered collector) 

back to top 

PE3 Combustion of the used oil at pulp mills and asphalt plants See Recycled Oil, Re‐refine and Reuse, BE4, Combustion of oil for heat at generators 

back to top 

BE1 Crude oil extraction (use as a fuel) See Recycled Oil, Re-refine and Reuse, BE1, Crude oil extraction (re-refine and reuse) 

back to top 

BE2 Transportation of crude oil to refinery (use as a fuel) See Recycled Oil, Re-refine and Reuse, BE2, Transportation of crude oil (re-refine and reuse) 

back to top 

CRA 071620 (2)

APPENDIX C 



BCUOMA 

BE3 Refine crude oil into oil products (use as a fuel) See Recycled Oil, Re-refine and Reuse, BE3, Refine crude oil into pil products (re-refine and reuse) 

back to top 

BE4 Combustion of oil for heat at generators (use as a fuel) See Recycled Oil, Re‐refine and Reuse, BE4, Combustion of oil for heat at generators 

back to top 



PE1 Transportation (from generator to registered collector) (metal oil filters) See Recycled Oil, Re‐refine and Reuse, PE1, Transportation (from generator to registered collector) 

back to top 

PE2 Transportation (from registered collector to registered steel oil filter processor) See Recycled Oil, Re‐refine and Reuse, PE1, Transportation (from generator to registered collector) 

back to top 


back to top 

Electricity Production 

CRA 071620 (2) 

Electricity generation intensity for British Columbia 0.02 kg CO 2e/ 

kWh 

Natural Gas - Production, Processing, and Distributing 

Page 6 of 11 

Environment Canada, National Inventory Report, Greenhouse Gas Sources and Sinks in Canada, 1990-2008. Ta 

Natural Gas Production (Canada - 2000) 2.18E+11 m 3 /year Canadian Association of Petroleum Producers. 2005. A National Inventory of Greenhouse Gas (GHG), 

Emissions - Upstream NG (Produce, Process, Transport) CO 2 44,866 kt/year Criteria Air Contaminant (CAC) and Hydrogen Sulphide (H2S) Emissions by the Upstream Oil and Gas Industr 

Emissions - Upstream NG (Produce, Process, Transport) CH 4 1,849 kt/year Volume 1, Overview of the GHG Emissions Inventory, 

Emissions - Upstream NG (Produce, Process, Transport) NO x 2.13 kt/year http://www.capp.ca/library/publications/climateChange/Pages/default.aspx 

Energy content of natural gas 37.63 MJ/m 3 

Energy Density of Natural Gas. Average value taken. Available at: http://hypertextbook.com/facts/2004/Jess 

kg/ m 3 

natural gas kg CO 2e/GJ natural gas kg CO 2e 

Emission 

kg CO 2e/unit 

Carbon dioxide 0.21 kg CO 2 5.48 1 5.48 

Methane 8.50E-03 kg CH 4 0.23 25 5.65 

Nitrous oxide 9.79E-06 kg N 2O 2.60E-04 298 7.75E-02 

Natural Gas - Combustion for Heat 

Environmental Protection Agency. 1998. AP 42, Fifth Edition, Volume I Chapter 1: External Combustion Source 

1.4 Natural Gas Combustion, http://www.epa.gov/ttn/chief/ap42/ch01/index.html. 

kg/10 6 m 3 

natural gas kg CO 2e/GJ natural gas kg CO 2e 

Emission 

kg CO 2e/unit 

Carbon dioxide 1,920,000 kg CO 2 51.02 1 51.02 

Carbon monoxide 640 kg CO 1.70E-02 1.57 2.67E-02 

Methane 37 kg CH 4 9.78E-04 25 2.44E-02 

Nitrous oxide 1,504 kg N 2O 4.00E-02 298 1.19E+01

Propane - Production of Liquid Propane Gas 

APPENDIX C 



BCUOMA 

Carbon dioxide equivalents 0.391 kg CO 2e/L 

Government of Canada. Technology Early Action Measures. Emission Factor Database. 

Page 7 of 11 

Propane - Combustion for Fuel (forklift) 

Energy Mobile Combustion Sources - Road Transport Environment Canada, National Inventory Report, Greenhouse Gas Sources and Sinks in Canada, 1990-2008. Ta 

Propane Vehicles 

kg CO 2e 

Emission 

kg CO 2e/unit 


Methane 0.64 g CH 4/L 25 0.016 


PE4 Transportation of steel to metal broker See Recycled Oil, Re‐refine and Reuse, PE1, Transportation (from generator to registered collector) 

back to top 

PE5 Transportation of steel to steel mill (project) See Recycled Oil, Re‐refine and Reuse, PE1, Transportation (from generator to registered collector) 

back to top 

BE1 Production of steel 

back to top Steel Production Pembina Institute, Produce Steel 

Sources from Canada, Alberta, US, and Switzerland. Average taken (using a T-distribution statistical analysis). 

Boundaries differ for each source however the average is considered indicative of the entire lfe cycle production of steel from the raw materials extraction to the hot stripping 

and cold rolling steel production. 

kg/ 1000 kg 

steel kg CO 2e 

Emission 

kg CO 2e/unit 

Carbon dioxide 1822.75 kg CO 2 1 1822.75 

Methane 10.8 kg CH 4 25 270.00 

Nitrous oxide 0.0096 kg N 2O 298 2.86 

BE2 Transportation of steel to steel mill (baseline) Included in BE1, Production of Steel above 

back to top 

BE3 Transportation of steel filters to disposal facility See Recycled Oil, Re‐refine and Reuse, PE1, Transportation (from generator to registered collector) 

back to top 

CRA 071620 (2)

APPENDIX C 



BCUOMA 

Paper Oil Filters 

PE1 Transportation (from generator to registered collector) (paper filters) See Recycled Oil, Re‐refine and Reuse, PE1, Transportation (from generator to registered collector) 

back to top 

PE2 Transportation (from registered collector to registered paper oil filter processor) See Recycled Oil, Re‐refine and Reuse, PE1, Transportation (from generator to registered collector) 

back to top 

PE3 Processing of paper oil filters (crushed and incinerated) See Processing of Steel Oil Filters (crushed into cubes and cylinders), PE3 

back to top For electricty, natural gas and propane emission factors 

CRA 071620 (2) 

Paper filters are sent to the Greater Vancouver Regional District’s (GVRDs) waste-to-energy facility in Burnaby for incineration. 

Disposal, paper, 11.2% water, to municipal incinerator Ecoinvent Database 

Waste-specific air and water emissions from incineration, auxiliary material consumption for flue gas cleaning. Process energy demands for MSWI. 

Specific to the technology mix encountered in Switzerland in 2000. Well applicable to modern incineration practices in Europe, North America or Japan. 

Average Swiss MSWI plants in 2000 with electrostatic precipitator for fly ash (ESP), wet flue gas scrubber. 

Due to the throughput of 1 kg of paper into MSWI. 

Name Unit Category kg CO2e Subcategory 

Mean Value 

kg/unit 

Emission 

kg CO2e/unit 

Carbon dioxide, fossil kg air 1 high population density 0.0075581 0.0075581 

Carbon dioxide, fossil kg air 1 low population density 0.0032392 0.0032392 

Carbon dioxide, fossil kg air 1 lower stratosphere + upper troposphere 1.5731E-09 1.5731E-09 

Carbon dioxide, fossil kg air 1 unspecified 0.0073281 0.0073281 

Carbon dioxide, land transformation kg air 1 low population density 2.887E-07 2.887E-07 

Carbon monoxide, fossil kg air 1.5714 high population density 2.4322E-06 3.82196E-06 

Carbon monoxide, fossil kg air 1.5714 low population density 0.000004185 6.57631E-06 

Carbon monoxide, fossil kg air 1.5714 lower stratosphere + upper troposphere 1.8478E-12 2.90363E-12 

Carbon monoxide, fossil kg air 1.5714 unspecified 0.000033158 5.21045E-05 

Chloroform kg air 30 high population density 3.7125E-12 1.11375E-10 

Chloroform kg air 30 low population density 5.1997E-14 1.55991E-12 

Chloroform kg air 30 unspecified 1.9827E-20 5.9481E-19 

Dinitrogen monoxide kg air 298 high population density 0.000015987 0.004764126 

Dinitrogen monoxide kg air 298 low population density 4.7598E-08 1.41842E-05 

Dinitrogen monoxide kg air 298 lower stratosphere + upper troposphere 1.4982E-14 4.46464E-12 

Dinitrogen monoxide kg air 298 unspecified 7.7763E-08 2.31734E-05 

Ethane, 1,1,1,2-tetrafluoro-, HFC-134a kg air 1430 high population density 3.2427E-13 4.63706E-10 

Ethane, 1,1,1,2-tetrafluoro-, HFC-134a kg air 1430 low population density 2.4672E-12 3.5281E-09 

Ethane, 1,1,1,2-tetrafluoro-, HFC-134a kg air 1430 unspecified 4.3705E-09 6.24982E-06 

Ethane, 1,1,2-trichloro-1,2,2-trifluoro-, CFC-113 kg air 6130 high population density 1.3548E-13 8.30492E-10 

Ethane, 1,1,2-trichloro-1,2,2-trifluoro-, CFC-113 kg air 6130 unspecified 0 

Ethane, 1,1-difluoro-, HFC-152a kg air 124 high population density 2.8113E-12 3.48601E-10 

Ethane, 1,1-difluoro-, HFC-152a kg air 124 low population density 0 

Ethane, 1,2-dichloro-1,1,2,2-tetrafluoro-, CFC-114 kg air 10000 low population density 4.3904E-11 4.3904E-07 

Ethane, 2-chloro-1,1,1,2-tetrafluoro-, HCFC-124 kg air 609 unspecified 0 

Ethane, hexafluoro-, HFC-116 kg air 12200 high population density 9.4061E-12 1.14754E-07 

Ethane, hexafluoro-, HFC-116 kg air 12200 unspecified 1.0864E-10 1.32541E-06 

Methane, biogenic kg air 25 high population density 6.3894E-06 0.000159735 

Methane, biogenic kg air 25 low population density 5.9554E-08 1.48885E-06 

Methane, biogenic kg air 25 unspecified 4.0603E-08 

Methane, bromo-, Halon 1001 kg air 25 unspecified 5.3742E-20 1.34355E-18 

Page 8 of 11

APPENDIX C 



BCUOMA 

Page 9 of 11 

Methane, bromochlorodifluoro-, Halon 1211 kg air 1890 low population density 1.5025E-10 2.83973E-07 

Methane, bromotrifluoro-, Halon 1301 kg air 7140 high population density 7.3698E-17 5.26204E-13 

Methane, bromotrifluoro-, Halon 1301 kg air 7140 low population density 8.5505E-11 6.10506E-07 

Methane, chlorodifluoro-, HCFC-22 kg air 1810 high population density 5.0685E-12 9.17399E-09 

Methane, chlorodifluoro-, HCFC-22 kg air 1810 low population density 5.3825E-10 9.74233E-07 

Methane, chlorotrifluoro-, CFC-13 kg air 14000 unspecified 0 

Methane, dichloro-, HCC-30 kg air 8.7 high population density 1.6223E-13 1.4114E-12 

Methane, dichloro-, HCC-30 kg air 8.7 low population density 1.5389E-13 1.33884E-12 

Methane, dichlorodifluoro-, CFC-12 kg air 10900 high population density 6.8318E-13 7.44666E-09 

Methane, dichlorodifluoro-, CFC-12 kg air 10900 low population density 5.1289E-13 5.5905E-09 

Methane, dichlorodifluoro-, CFC-12 kg air 10900 unspecified 3.5731E-20 3.89468E-16 

Methane, dichlorofluoro-, HCFC-21 kg air 210 high population density 9.2258E-16 1.93742E-13 

Methane, fossil kg air 25 high population density 1.1812E-06 0.00002953 

Methane, fossil kg air 25 low population density 0.000032308 0.0008077 

Methane, fossil kg air 25 lower stratosphere + upper troposphere 2.497E-14 6.2425E-13 

Methane, fossil kg air 25 unspecified 1.0495E-07 2.62375E-06 

Methane, monochloro-, R-40 kg air 13 high population density 4.7735E-15 6.20555E-14 

Methane, monochloro-, R-40 kg air 13 low population density 2.81E-13 3.653E-12 

Methane, tetrachloro-, R-10 kg air 1400 high population density 7.4786E-11 1.047E-07 

Methane, tetrachloro-, R-10 kg air 1400 unspecified 1.5977E-17 2.23678E-14 

Methane, tetrafluoro-, R-14 kg air 7390 high population density 1.4458E-13 1.06845E-09 

Methane, tetrafluoro-, R-14 kg air 7390 unspecified 9.7775E-10 7.22557E-06 

Methane, trichlorofluoro-, CFC-11 kg air 4750 high population density 1.4978E-15 7.11455E-12 

Methane, trifluoro-, HFC-23 kg air 14800 high population density 2.9355E-13 4.34454E-09 

Nitrogen fluoride kg air 17200 high population density 0 

Sulfur hexafluoride kg air 22800 high population density 0 

Sulfur hexafluoride kg air 22800 low population density 3.3619E-13 7.66513E-09 

Sulfur hexafluoride kg air 22800 unspecified 4.7119E-10 1.07431E-05 

0.024018866 Total emissions for 1 k 

paper through inciner 

BE1 Transportation of paper filters to landfill See Recycled Oil, Re‐refine and Reuse, PE1, Transportation (from generator to registered collector) 

back to top 

CRA 071620 (2)

APPENDIX C 



BCUOMA 


back to top LFG Model 

Lo (methane generation potential) 

Scholl Canyon LFG Model 

Model parameters from "Landfill Gas Generation Assessment Procedure Guidance Report" by CRA 

dated March 2009, prepared for the British Columbia Ministry of Enviornment. 

Moderately Decomposable 120 m 3 k (Methane Generation rate) 

Moderately Decomposable 

Annual Precipitation 

methane/tonne waste 

250 to 500 to 1,000 to 2,000 to 3,000mm 0.08 yr -1 

CRA 071620 (2) 

Note: Modelling was conducted by CRA and the results only have been included in this analysis. 

Page 10 of 11


APPENDIX C 



BCUOMA 

PE1 Transportation (from generator to registered collector) (containers) See Recycled Oil, Re‐refine and Reuse, PE1, Transportation (from generator to registered collector) 

back to top 

PE2 Transportation (from registered collector to registered oil container processor) See Recycled Oil, Re‐refine and Reuse, PE1, Transportation (from generator to registered collector) 

back to top 

PE3 Processing of oil containers (shredded, centrifuged, washed and pelletized) See Processing of Steel Oil Filters (crushed into cubes and cylinders), PE3 

back to top For electricty, natural gas and propane emission factors 

PE4 Transportation of HDPE pellets to plastics manufacturer See Recycled Oil, Re‐refine and Reuse, PE1, Transportation (from generator to registered collector) 

back to top 

BE1 Production of HDPE 

back to top Plastic (HDPE) Production Pembina Institute, Produce Plastic (HDPE) 

Source from Europe (1993), data considered fairly current and applicable to North America 

kg / 1000kg 

HDPE kg CO 2e 

Emission 

kg CO 2e/unit 

Carbon dioxide 2060 kg CO 2 1 2060.00 

Methane 3.7 kg CH 4 25 92.50 

Nitrous oxide 0.0049 kg N 2O 298 1.46 

BE2 Transportation of HDPE to plastics manufacturer Included in BE1, Production of HDPE above 

back to top 

BE3 Transportation of oil containers to disposal facility See Recycled Oil, Re‐refine and Reuse, PE1, Transportation (from generator to registered collector) 

back to top 

END OF WORKSHEET 

CRA 071620 (2) 

Page 11 of 11

2009 Greenhouse Gas Savings Study Report - Alberta Used Oil ...

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