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The role of global land use in determining greenhouse gas - - PowerPoint PPT Presentation

The role of global land use in determining greenhouse gas mitigation costs Presented by Steven Rose (U.S. EPA) Co-authors: Thomas Hertel and Huey-Lin Lee (Purdue Univ.) Brent Sohngen (Ohio State Univ.) EMF-22 Workshop, Tsukuba, Japan,


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SLIDE 1

The role of global land use in determining greenhouse gas mitigation costs

Presented by Steven Rose (U.S. EPA) Co-authors: Thomas Hertel and Huey-Lin Lee (Purdue Univ.) Brent Sohngen (Ohio State Univ.)

EMF-22 Workshop, Tsukuba, Japan, December 12-14, 2006

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SLIDE 2

Motivation

  • Land is a significant source of GHG emissions

– Deforestation: 1/3 of total carbon emissions since 1850 – Land management and land use change: 75% of N2O, 50% of CH4

  • Previous studies suggest land-based mitigation is cost-effective

– e.g., Sohngen and Mendelsohn (2003), Rao and Riahi (2006), van Vuuren et al. (2006), Jakeman and Fisher (2006)

  • Analytical challenges for land modeling

– Land-use competition and overall market reallocations – Land-based mitigation competition and net emissions effects – Land heterogeneity and dynamics – Lack of key consistent global data—land, emissions, mitigation costs

  • New global datasets—land, emissions, mitigation costs

Opportunities for improving our understanding of the mitigation role of land

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SLIDE 3

Objective: Analyze land allocation decisions and global general equilibrium feedbacks in mitigation

Outline

  • Model structure
  • Land, emissions, sequestration data
  • Analysis set-up
  • Results
  • Conclusions & plans
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SLIDE 4

Expanded GTAP-AEZ

  • Static global CGE
  • Prototype applications:

– 3 Regions: USA, China, ROW; maximum disaggr GTAP regions (nearly 100) – 24 Sectors – 5 land-using sectors (3 crop, ruminant livestock, forestry)

  • Max sectors = 57 of which 10 in agriculture
  • Production with intra- and inter-regional land heterogeneity

– AEZs: 18 different types of land within each region aggregated to 6 AEZs – Land supply and demand same as G-Dyn presentation

  • GHG emissions and sequestration modifications

– Non-CO2

  • Incorporate new detailed non-CO2 GHG emissions inventory data (N2O, CH4, F-gases)
  • Model 3 classifications of emissions – output, intermediate inputs, factor inputs

– Forest carbon

  • Incorporate new detailed forest carbon stock data
  • Model intensive and extensive carbon management options

– Introduce emissions pricing – Calibrate mitigation responses to PE model responses

  • Given land emphasis, focus is on non-CO2 GHGs and forest sequestration
  • Future: bring into dynamic model, add CO2 emissions and soil carbon
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SLIDE 5

Land endowments – biophysical heterogeneity

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SLIDE 6

Land endowments – economic heterogeneity

1 AEZ1 3 AEZ3 5 AEZ5 7 AEZ7 9 AEZ9 11 AEZ11 13 AEZ13 15 AEZ15 17 AEZ17

1 p d r 4 v _ f 7 p fb

2 0 0 0 4 0 0 0 6 0 0 0 8 0 0 0 1 0 0 0 0 1 2 0 0 0 1 4 0 0 0 1 6 0 0 0 1 8 0 0 0 2 0 0 0 0

G T A P c r o p s e c to r s la n d r e n t ( 2 0 0 1 U S D , m illio n ) 1 p d r 2 w h t 3 g r o 4 v _ f 5 o s d 6 c _ b 7 p fb 8 o c r

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SLIDE 7

Detailed non-CO2 emissions & forest sequestation data

  • New GTAP 2001 non-CO2 emissions data

– Corresponds to GTAP v6 data 2001 base year and complements GTAP 2001 CO2 emissions data – Highly disaggregated – explicitly for more precise mapping to economic activity (output and input)

  • 226 countries
  • Currently 24 non-CO2 GHG emissions categories (N2O, CH4, F-gases) with 119

types of emissions with subcategory disaggregation

– To be expanded further to all subcategories in new USEPA dataset (29 categories, 153 non-CO2 & Other CO2 subcategories)

  • Data developed from:

– Annex 1: UNFCCC CRFs – Non-Annex 1: National Communications, ALGAS, IPCC inventory methods, EDGAR (biomass burning, Other CO2), some extrapolation from 2000 data

  • New GTAP regional 2000 forest carbon stock data by AEZ,

management type, and tree age cohort

  • Soil carbon stock data also available (but not yet implemented in the

model)

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SLIDE 8

Non-CO2 emissions sources for land sectors

GHG/category GTAP-AEZ sector Paddy rice Other grain Other crops Ruminant livestock Non- ruminant livestock Forest Ruminant animal products Other meat products Processed rice Other food processing Wood processing Methane (CH4) Enteric fermentation x x Manure management x x Rice cultivation x Biomass burning x x x x Other industrial non-agriculture x Stationary and mobile combustion x x x x x x x x x x x Nitrous oxide (N2O) Agricultural soils x x x Manure management x x Pasture, range, and paddock x x Biomass burning x x x x Other industrial non-agriculture x Stationary and mobile combustion x x x x x x x x x x x

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SLIDE 9

Base year non-CO2 emissions profiles in the model

GTAP-AEZ sectoral Non-CO2 emissions distribution by region

200 400 600 800 1000 1200 1400 1600 1800 2000 1 USA 2 CHN 3 ROW MtCeq 24 RWTrade 23 NTrdServices 22 OthManufact 21 OthExtractn 20 Transport 19 Services 18 EnrgIntnsMnf 17 WoodProcessn 16 OthFoodPrcsn 15 ProcessdRice 14 OtherMeatPrd 13 Rumint_Prods 12 GasDistribut 11 Electricity 10 RefinedFuels 9 Gas 8 Oil 7 Coal 6 Forest 5 NonRuminLivs 4 Ruminants 3 OtherCrops 2 OtherGrain 1 PaddyRice

China Paddy Rice 85% CH4 15% N2O

(in Ceq)

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SLIDE 10

Modeling non-CO2 emissions

  • 3 categories -
  • Input – emissions related to

input use; mitigation involves reducing input intensity

– Intermediate input – e.g., fertilizer use in maize – Endowment – e.g, paddy rice land

  • Output – emissions treated

as distinct input to production, substitution for commercial inputs captures mitigation options:

– Use when emissions not linked to input use – Calibrate CES elasticity following Hyman et al.

USA China ROW 1 PaddyRice 2.971 70.160 137.364 Total non-CO2 GHG emissions (MtCeq)

0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100% USA China ROW Intermediate input Endowment Output

Paddy Rice

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SLIDE 11

Calibrating mitigation responses: Non-CO2 mitigation

  • Non-CO2 mitigation

– New engineering mitigation cost estimates for detailed technologies—both agriculture and other sectors (USEPA, 2006) – Calibrate the relevant substitution elasticity and appropriate share of sector emissions with a partial equilibrium closure

  • Forest sequestration supply

– Regional forest carbon supply curves Sohngen and Mendelsohn (2006) – afforestation and forest management – Calibrate forest carbon production intensification and extensification responses

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SLIDE 12

Calibrating forest sequestration responses

Carbon price Extensive Margin Intensive Margin Wood Products Access Margin** Total US 5 1.672

  • 1.663
  • 0.476

0.839 0.371 10 3.509 6.802

  • 0.238

1.346 11.419 20 7.023 24.585

  • 0.084

2.866 34.390 50 17.811 73.503

  • 0.948

5.147 95.513 100 43.069 102.749

  • 0.132

9.298 154.986 200 118.287 119.006 1.667 19.931 258.893 500 270.741 286.616 0.537 25.322 583.216 CHINA 5 0.440 3.018

  • 0.028

4.733 8.164 10 0.612 14.865

  • 0.282

9.966 25.161 20 1.210 26.899

  • 0.372

21.765 49.501 50 4.154 73.928

  • 1.532

53.501 130.051 100 12.797 98.522

  • 2.018

77.089 186.390 200 73.532 97.503

  • 1.325

77.089 246.799 500 108.663 202.142

  • 5.082

77.089 382.812 ROW 5 143.218 31.572

  • 3.614
  • 19.259

151.917 10 281.670 78.626

  • 5.956
  • 2.370

351.969 20 539.266 114.936

  • 9.437

14.203 658.968 50 1203.164 250.691

  • 19.898

66.875 1500.832 100 1672.509 387.619

  • 29.708

80.424 2110.845 200 2189.741 366.732

  • 21.178

93.365 2628.660 500 2885.440 868.723

  • 47.496

103.227 3809.894

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SLIDE 13

Calibration example – ROW forest extensification

ROW forest sector sequestration MAC: extensification, 20-year annual equivalent abatement 25 50 75 100 125 150 175 200 100 200 300 400 500 600 700 800 900 1000 1100 1200 1300 1400 1500 1600 1700 1800 1900 2000 2100 2200 Abatement - MMTCE 2001 USD $ per tonne of C GTAP-AEZ_extensification DGTM_Land Storage

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SLIDE 14

Calibration example – USA forest intensification

USA forest sector sequestration MAC: intensification, 20-year annual equivalent abatement 25 50 75 100 125 150 175 200

  • 5

5 15 25 35 45 55 65 75 85 95 105 115 125 135 145 155 Abatement - MMTCE 2001 USD $ per tonne of C GTAP-AEZ_intensification DGTM_age/management storage

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SLIDE 15

Analysis of mitigation responses

  • 1. Intra- and inter-regional GE effects:
  • A. USA carbon tax
  • B. ROW carbon tax
  • C. Global carbon tax
  • 2. Individual carbon tax decomposition:

GE with global carbon tax

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SLIDE 16

USA sectoral mitigation w/ US carbon tax

GE MAC of USA: USA-only carbon tax, sectoral and region total

10 20 30 40 50 60 70 80 90 100 50 100 150 200 250 abatement - mmtce 2 1 U S D p e r to n n e

  • f

C .

Regional AG+FRS abatement Regional agriculture abatement Regional forest total sequestration USA forest intensification abatement USA AGR sectoral GE-MAC: USA-only taxed

10 20 30 40 50 60 70 80 90 100 5 10 15 20 25 30 Abmatement - MMTCE 2 1 U S D p e r to n n e

  • f

C .

1 PaddyRice 2 OtherGrain 3 OtherCrops 4 Ruminants 5 NonRuminLivs Tot_AGR

forest total ag intensification

  • ther grain

ruminants

  • ther crops

non ruminant

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SLIDE 17

ROW sectoral mitigation w/ US carbon tax

ROW AGR sectoral GE-MAC: USA-only taxed

10 20 30 40 50 60 70 80 90 100

  • 8
  • 7.5
  • 7
  • 6.5
  • 6
  • 5.5
  • 5
  • 4.5
  • 4
  • 3.5
  • 3
  • 2.5
  • 2
  • 1.5
  • 1
  • 0.5

Abmatement - MMTCE 2 1 U S D p e r to n n e

  • f

C .

1 PaddyRice 2 OtherGrain 3 OtherCrops 4 Ruminants 5 NonRuminLivs Tot_AGR GE MAC of ROW: USA-only carbon tax, sectoral and region total

40 50 60 70 80 90 100 1 U S D p e r to n n e

  • f C

. 10 20 30

  • 30
  • 25
  • 20
  • 15
  • 10
  • 5

abatement - mmtce 2

Regional AG+FRS abatement Regional agriculture abatement Regional forest total sequestration ROW forest intensification abatement

forest total ag intensification

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SLIDE 18
  • 30,000
  • 25,000
  • 20,000
  • 15,000
  • 10,000
  • 5,000

5,000 10,000 15,000 20,000 25,000 USA CHN ROW USA CHN ROW USA only ROW only millions 2001 US$ Rice OtherGrain OtherCrops Ruminants NonRuminants OthFood

Change in regional agricultural trade balances due to unilateral carbon tax: $100/t

USA only tax ROW only tax

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SLIDE 19

ROW sectoral mitigation w/ US carbon tax

USA AGR sectoral GE-MAC: ROW-only taxed

10 20 30 40 50 60 70 80 90 100

  • 14
  • 13
  • 12
  • 11
  • 10
  • 9
  • 8
  • 7
  • 6
  • 5
  • 4
  • 3
  • 2
  • 1

Abmatement - MMTCE 2 1 U S D p e r to n n e

  • f C

.

1 PaddyRice 2 OtherGrain 3 OtherCrops 4 Ruminants 5 NonRuminLivs Tot_AGR ROW AGR sectoral GE-MAC: USA-only taxed

10 20 30 40 50 60 70 80 90

  • 8
  • 7.5
  • 7
  • 6.5
  • 6
  • 5.5
  • 5
  • 4.5
  • 4
  • 3.5
  • 3
  • 2.5
  • 2
  • 1.5
  • 1
  • 0.5

Abmatement - MMTCE 2 1 U S D p e r to n n e

  • f C

. 100

1 PaddyRice 2 OtherGrain 3 OtherCrops 4 Ruminants 5 NonRuminLivs Tot_AGR

USA sectoral mitigation w/ ROW carbon tax ruminants

  • ther crops

rice

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SLIDE 20

USA sectoral mitigation w/ global carbon tax USA sectoral mitigation w/ US carbon tax

GE MAC of USA: USA-only carbon tax, sectoral and region total

30 40 50 60 70 80 90 100 2 1 U S D p e r to n n e

  • f

10 20 50 100 150 200 250 abatement - mmtce C .

Regional AG+FRS abatement Regional agriculture abatement Regional forest total sequestration USA forest intensification abatement

forest total ag intensification

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SLIDE 21

Mitigation affects intra-regional land competition

Percentage change in USA land rents and land use by sector following a $100/tonne USA carbon tax 1. For a given use, similar land rent responses across AEZs 2. Changes in land rents reflect the net effect of mitigation costs and land competition (i.e., changes in land prices and changes in acreage) – mitigation cost/subsidy dominates in rice and forestry, land competition dominates in other ag sectors 3. How carbon price applied matters—taxing land (rice) vs. taxing non-land inputs (other grain) 4. Land reallocation occurring – within and across sectors!

Forest Paddy Rice Other Grain Other Crops Ruminants AEZ1 1225.7

  • 21.39

10.13 14.08 17.59 AEZ2 1224.09

  • 19.4

9.93 13.88 17.38 AEZ3 1223.97

  • 19.18

9.91 13.86 17.36 AEZ4 1225.44

  • 20.85

10.07 14.02 17.53 AEZ5 1228.88

  • 25.59

10.41 14.36 17.91 AEZ6 1235.81

  • 38.88

11.19 15.16 18.71 Forest Paddy Rice Other Grain Other Crops Ruminants AEZ1 2.23

  • 0.06
  • 0.98
  • 0.32
  • 0.84

AEZ2 0.1

  • 0.04
  • 0.79

0.31 0.42 AEZ3 0.11

  • 0.09
  • 0.77

0.54 0.21 AEZ4 2.38

  • 0.05
  • 1.85
  • 0.39
  • 0.05

AEZ5 6.96

  • 0.73
  • 3.95
  • 1.57
  • 0.42

AEZ6 12.61

  • 1.05
  • 3.05
  • 7.22
  • 0.37

Percentage change in land rents Percentage change in land use, weighted by AEZ land rent share

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SLIDE 22

Emissions/sequestration change from region (%) Type/region of taxation USA CHN ROW USA

  • 0.01

CHN Output related emissions ROW 0.03 0.01

  • 0.02

USA

  • 8.27

0.08 0.61 CHN 0.28

  • 4.26

0.32 Purchased input related emissions ROW 1.73 0.27

  • 2.54

USA

  • 1.98

0.01 0.19 CHN

  • 0.04
  • 12.88
  • 0.04

Primary factor related emissions ROW 0.79 0.15

  • 7.41

USA

  • 75.37

0.04 0.6 CHN 0.09

  • 42.96

0.18 Forest sequestration ROW 6.27 0.9

  • 131.58

Total Impact

  • 76.48
  • 58.63
  • 139.69

The role of individual carbon taxes in global responses ($100/tC global tax)

1. Comparative mitigation advantages evident (via carbon intensities and input prices – e.g., ruminant intensities 0.9562 for China and 0.0099 for USA)

  • Unique regional responses to an identical tax
  • Unique regional mitigation portfolios (in levels in particular)

2. Leakage associated with most individual taxes

  • 24 vs.

11 MtCeq

  • 2438 vs.

18 MtCeq

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SLIDE 23

Conclusions

  • Biophysical and economic land characteristics create

comparative abatement advantages for land endowments intra- and inter-regional land reallocations

  • International market structure influences regional

mitigation responses

  • International leakage is an important component of

total GHG emissions

  • Global GE feedbacks can increase the profitability of

production despite increasing emissions subject to a carbon tax

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SLIDE 24

Extra slides

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SLIDE 25

Land demand

Total land demanded by sector j AEZ N AEZ 2 ..... AEZ 1

AEZ

σ = 20

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SLIDE 26

Land supply

Grazing Crop 1 Crop 2 Crop N Land of AEZ i Forestry Agriculture Crops .....

1

Ω = -0.25

2

Ω = -0.5

3

Ω = -1

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SLIDE 27

Emissions/sequestration pricing

  • The economic impact of an emissions tax associated with input usage depends
  • n the size of the tax AND the emissions intensity of the input.
  • The larger the emissions intensity, the greater the impact of a given carbon tax
  • n the sector/input in question.

– Equation CHNGETAXFD (all,i,TRAD_COMM)(all,j,PROD_COMM)(all,r,REG) del_TFD_L(i,j,r) = del_TFDO_L(i,j,r) + [UNITDEMIT(i,j,r)/PM_L(i,r)] * [c_TAUIEMIT(i,j,r) - (PM_L(i,r)*AVEDTAUI(i,j,r)/100) * pm(i,r)]; – Formula (all,i,TRAD_COMM)(all,j,PROD_COMM)(all,r,REG) UNITDEMIT(i,j,r) = QFDEMIT(i,j,r)/QFD_L(i,j,r) ;

Emissions intensity

Emission intensities (MtC/$ of input) Forest carbon intensities (MtC/$ of land rent) Input USA China ROW USA China ROW Fertilizer in crops production 0.0062 0.0044 0.0044 0.057 0.016 0.148 Ruminant livestock capital 0.0099 0.9562 0.0154 Land in paddy rice 0.0040 0.0125 0.0049

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SLIDE 28

Calibration of USA cropland GHG mitigation costs

  • 500
  • 400
  • 300
  • 200
  • 100

100 200 300 400 500 0% 10% 20% 30% 40% 50% 60% $/tCeq Engineering costs Calibrated

Calibration example – USA cropland

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SLIDE 29

Modeling forest carbon

VA

σ

T

σ

CARBON

σ

AEZ

σ

Intermediate Inputs (excluding forest) Value Added Carbon Skilled Labor Unskilled Labor Natural Resource Capital Land Forest AEZ1 AEZ2 ….. AEZ6

qomac

σ

Output Output-Emissions composite Output-related emissions