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Canada’s Regulatory Framework for Air Emissions:
A Business and Environmental Law Perspective
Elisabeth (Lisa) DeMarco May 9, 2007
The Ontario Bar AssociationWebinar
Overview• General Principles of Emissions Trading• Voluntary versus Compliance Markets• Canadian Emissions Context• The Canadian Framework for Air Emissions• Framework in International ET Context• Considerations for Business and
Environmental Lawyers
Macleod Dixon LLP• Canadian based International law firm established 1912
• 300 lawyers, 420 total staff in 7 global offices
• Focus: natural resource law (oil, gas, electricity, water, carbon and emission products)
• MD Climate Change Team: International Team, lead out of Toronto serving domestic and international clients
• MD Climate Change lawyers at the leading edge of Canadian and international emissions trading policy development since 1996 – more than a decade of proven ET Law experience
• Member of EMA, IETA, IETA CWGCM
• MD Climate Change Team has closed more than 50 MT of carbon transactions
Macleod Dixon’s Offices
Calgary, Toronto
Caracas
Rio de Janeiro
Moscow
Almaty, Atyrau
General Principles of Emissions Trading
Environmental Kuznets Curve
Personal Income
Env
iro.
Deg
rada
tion
I. The Theory: ET 101
30
60
90
120
150
0
30
60
90
120
150
A B C D E
Total emissions of X = 450 tonnes
Current emissions of X
The Theory: ET 101
2754
135 10
8 813
6
9
12
15
0
27
54
81
108
135
162
A B C D E
Total emissions of X = 405 tonnesTotal reductions required - 45 tonnes
Government requires 10% reduction
The Theory: ET 101
A B C D E
$300
$240
$180
$120
$60
0
60
120
180
240
300
A B C D E
If the cost of reducing 1 tonne of X is uniform for all emitters and equal to $20/tonne then, the individual and total costs of reduction are:
Total cost of reducing 45 tonnes of X is $900
The Theory: ET 101
$15
$240
$180
$120
$60
0
60
120
180
240
If the cost of reducing 1 tonne of X is not the same for all emitters and A can make reductions for $1/tonne while B,C.D,E make reductions at $20/tonne. Then, the individual and total costs of reduction are:
Total cost of reducing 45 tonnes of X is $615
The Theory: ET 101
If A can make 42 T of emission reductions at $1/tonne, it can then sell emission reductions at a profit to B,C,D,E at $10/tonne and decrease both individual and total compliance costs.
A: $15 compliance cost, $243 profitB: buys 12T from A = $120 compliance costC: buys 9T from A = $90 compliance costD: buys 6T from A = $60 compliance costE: makes 3T reductions itself = $60 compliance cost___________________________________________45T emission reduction goal achieved at $345 compliance cost
Total cost of reducing Total cost of reducing 45 tonnes of X using ET 45 tonnes of X using ET is $345; without ET is $345; without ET $900$900
Exercise: Compliance Cost Curve
-$20
-$10
$0
$10
$20
$30
$40
$50
$60
110 115 120 125 130 135 140 145 150
Emissions (Mega)tonnes CO2e/year
C$/
tCO
2e Emission Cost Curve
Emission reduction options identified in Upstream Oil & Gas Options Report, 1999
Source Rick Hyndman (CAPP)
Voluntary vs. Compliance Markets
Voluntary vs. Compliance
• The Differences• the nature of the “product/rights” • project-based vs. government allocated• generally* contract-based vs. regulatory regime
• ExamplesCompliance: EU ETS, US RGGI, US SO2, units= allowances, permitsVoluntary: domestic offsets, CDM and JIunits= VERs, offsets, ERs, CERs, ERUs
• Significant difference but both have value
Example: Compliance MarketReg 397/01 2007 NOx Allocations
• OPG – 16993• Kingston Cogen – 383• Transalta Sarnia- 1382• Brighton Beach – 640• Keele Valley LFG Power – 168
• http://www.oetr.on.ca/oetr/index.jsp
Example: Credit Creation Process (Voluntary)
Source: Government of Canada
1
6
8
9
5 7
3
2
4
General Characteristics of an Offset
• Real• Quantifiable• Verifiable (Verified)• Unique (No double counting)• Surplus (Additional)
Direct vs. Indirect CreditsDirect Indirect
CH4 reductions at LFG power plant
NOx, SO2, CO2 offsets from LFG power offsetting higher emission power relative tosystem supply mix
Environmental Attributes
• The “Greenness” of power or a product (ethanol)
• Both quantifiable (# ERs, RECs) and diffuse (all rights, benefits and interest – akin to goodwill)
• Can be sold Bundled/Aggregated or Separately/Disaggregated or partially bundled***
• Quantified units: RECs, TRCs, green tags• Diffuse units: enviro. attributes, benefits
Canadian Emissions Context
Canada’s GHG Emissions
Source: Environment Canada
Emissions by Sector
The Canadian Framework for Air Emissions
The Framework: General Views
• The Framework as the First Step Forward• Theory of the Second Best• Framework vs. Kyoto
• Framework: 150 MT decrease from estimated 2006 GHG levels (780MT) = 630MT by 2020
• Kyoto: 220 MT reduction from estimated 2006 GHG levels (780MT) = 560 MT by 2012
• Framework is not Kyoto: it continues Canada's move toward a "made-in-Canada" approach to climate change
Greenhouse Gas Targets
• Short-term:• Emissions intensity targets• Targeted reductions relative to 2006 emissions• 2010 implementation date
• by 2010:• -18% (combustion & non-fixed process emissions)• 0% (predefined fixed process emissions)
• -2% emission intensity per year (2010-2020)
Goal (2020): 20% absolute emissions reduction
Greenhouse Gas Targets
• Sectorally, basic approach is -18% emission intensity by 2010• Variable goals for fixed process emissions
• New facilities (1st-year operation 2004+)• 3-year grace period to reach normal operating
levels• Initial target based on cleaner fuel standards• -2% annual emissions intensity (to 2020)
GHG Compliance Mechanisms
• Engineered in-house reductions• Energy efficiency and management improvements• Technological advances – e.g., C-capture and storage
• Domestic trading• Between regulated Canadian companies• Bankable credits created by a company exceeding its
intensity target
• Domestic offset system• Regulated purchase from unregulated• Verified Emission Reductions (VERs)
GHG Compliance Mechanisms
• Kyoto Protocol’s Clean Development Mechanism (CDM)• International CDM credits may comprise ≤ 10%
of firm’s total target
• Credit for early action (1992-2006)• One-time allocation of credits for verified
emissions reductions, to max 15 Mt CO2e
GHG Compliance Mechanisms
• Climate Change Technology Fund• Companies may pay for not meeting intensity targets
• 2010-2012: $15/t CO2e
• 2013: $20• 2013-2020: adjusted at growth rate of nominal GDP• Declining %age of total target:
• 70-50% (2010-2014; -5% p.a.)
• 40% (2015)
• 10% (2016-2017), and 0% thereafter
• Purpose funding of emissions reduction technology deployment and related infrastructure
Air Pollution Targets
• Fixed national emission caps (2012-2015)• NOx (600 kt; -40% )• SOx (840 kt; - 55%)• Particulate matter (160 kt; -20%)• Volatile Organic Compounds (360 kt; -
45%)
• Reductions relative to 2006 emissions
Air Pollution Targets
• Other pollutants in specific sectors, e.g.: • Hg from electricity generation• benzene from refineries & natural gas
production/processing
• Fixed sectoral caps (2012 and 2015) to be validated by June 2007
J. Kellerman, Environment Canada. National Energy, Environment and Resources Law Summit, 28 April 2007Montréal, PQ.
AP Compliance Mechanisms
• Domestic emissions trading system• Cap-and-Trade for SOx and NOx
• regions that do not meet national air quality objectives will have limits on use of credits from elsewhere
• On-going discussions with USA on cross-border trading system (SOx & NOx)
• Verification and enforcement under CEPA 1999
Framework in International ET Context
Global Carbon Market• Kyoto came into effect and became international law February
16, 2005 creating binding obligations (Canada must reduce 6% from 1990 by 2012)
• EU pre-compliance market: EU ETS started January 2005• Two main markets: EU ETS and Kyoto Mechanisms with links• Commodities:
• EU allowances, CDM (CERs), JI (ERUs), and AAUs• all generally traded in units of CO2 equivalents
• International Carbon market activity (CDM and JI) has increased dramatically since Fall 2004, related prices also rose very sharply and dropped sharply in April 06 and are rising again
• Prices: EUA @ 19 Euros for 2008 (crash on 2007); Volumes: significant increase in last 12 months
• Current prices and volumes published by a number of emission brokers (Evolution, Natsource, Point Carbon)
Global Performance (based on 2004 inventories)
sourceEnvironment Canada
Market Dynamics: Volumes (2006) * based on volume estimates from Point Carbon, Natsource and extrapolations based on completed
transactions. 2006 Figures significantly higher.
SystemEstimated Total Volume (MT)
Estimated Financial size (million Euros)
EU ETS 1100 25,000
CDM (CERs) 475 5260
JI/AAU 16 141
Other 30 200
Total 1621 30,601
Market Dynamics• Estimated Global Supply
• 250 MT to 350 MT/ year over 2008 to 2012• compliance instruments• other
• Estimated Global Demand • 2.5 BT to 4BT over 2008 to 2012• contingencies
• EU NAPs and Phase II, Canadian commitment and position (300 MT/yr swing); Japan DET
• Second Commitment Period• Asia Pacific Partnership and US position• AAU trading
Pricing Differences
• Prices currently showing an upward trend• Higher prices for compliance-grade commodities• Differences between CER and ERU prices reflect
greater risk in less developed countries (JI projects are in Eastern Europe)
• Other price determinants:• Creditworthiness and experience• Confidence in counterparty and project• Structure of contract• Cost of validation and certification• ER vintage and seniority• Regulatory Risk***• Additional environmental benefits
Market Pricing (January 2005-2006 in US$/tCO2e)
Source: IETA
EUA Prices
Sources: IETA, PowerNext, ECX
International GHG Emissions Trading
Source: State and Trends of the Carbon Market 2007.
Annual volumes (Mt CO2e) of project-based emission reductions transactions
State and Trends of the Carbon Market 2007.
Increases in volumes and values of transactions on the Main International
Allowances Markets
2005 2006Volume
(Mt CO2e)Value
(MUS$)
Volume (Mt CO2e)
Value (MUS$)
EU ETS 321 7,908 1,101 24,357
New South Wales 6 59 20 225
Chicago Climate Exchange 1 3 10 38
UK ETS 0 1 na na
TOTAL 328 7,971 1,131 24,620
Considerations for Business and Environmental Lawyers
Domestic Regulatory• Host of new regulatory obligations for clients
• is facility/corp. a large industrial emitter?• can it create offsets?• what 2006 data/analysis required under s. 71?• what is GHG sector-based intensity target
applicable to facility?• what fixed AP caps apply to sector? facility?
allocation?• what emissions covered (fixed process vs. non-
fixed process? • compliance strategy (short and long term)?• provincial equivalency (AB, ON, QC)• treatment of any emissions book under CEA?• new facility, timing of implementation of GHG
control measures
Domestic Commercial (Emissions Transactions)
• Scenario planning to determine likely market boundaries (provincial? national? US? Mexico?)
• Facility based cost compliance curves• Forward price curves for GHG and AP• Compliance strategy in light of evolution and
integration of Tech Fund• Offset purchasing strategy• Impact on existing ERPAs and future ERPA
language• CDM portfolio (?)• Trading in Tech Fund credits?• Arbitrage on existing CEA book?• Cross border trading? (DeMarco et al. 2002)
International Trade and Treaty• Impacts of CDN Kyoto non-compliance• NAFTA / WTO vs. Kyoto• Product impact (import taxes and duties)• Cross border emissions trading in NOx and SO2 –
extra-territorial incompetence
• Legality of limits on types (jurisdictions?) of CDM projects and interpretation of supplementarity
• Impact on inter-provincial trade and AIT (DeMarco et al. 2004)
• International carbon market impacts (alters 2008 to 2012 demand by at least 250 MT/yr)
• Pricing impacts
Contact Information
Elisabeth (Lisa) DeMarco
Partner, Macleod Dixon LLP
Head International Climate Change & Toronto Energy Groups
Direct Telephone: (416) 203-4431
Facsimile: (416) 360-8277
Email: [email protected]