Chapter 8 Economy wide modelling 8 1 Inputoutput

Chapter 8 Economy wide modelling 8. 1 Input-output analysis 8. 2 Environmental input-output analysis 8. 3 Costs and prices 8. 4 Computable general equilibrium models Learning objectives § learn about the basic input–output model of an economy and its solution § find out how the basic input–output model can be extended to incorporate economy– environment interactions § encounter some examples of environmental input–output models and their application § learn how the input–output models, specified in terms of physical or constant-value flows, can be reformulated to analyse the cost and price implications of environmental policies, such as pollution taxes, and how these results can be used to investigate the distributional implications of such policies § study the nature of computable general equilibrium (CGE) models and their application to environmental problems

Box 8. 1 Using input-output analysis to consider the feasibility of sustainable development The Brundtland Report claimed that sustainable development was feasible. This was an assertion rather than a demonstration - the report did not put together the technological and economic possibilities looked at in various parts of the report and examine them for consistency. Duchin and Lange (1994), hereafter DL, is a report on a multisector economic modeling exercise, using input-output analysis, to look at the feasibility of sustainable development as envisaged in the Brundtland Report. DL used an input-output model of the world economy which distinguished 16 regional economies, in each of which was represented the technology of 50 industrial sectors. This model was used to generate two scenarios for the world economy for the period 1990 to 2020. The reference scenario assumes that over this period world GDP grows at 2. 8% per year, while the global population increases by 53%. DL take 2. 8% per year to be what is implied by the Brundtland Report's account of what is necessary for sustainable development. In this reference scenario production technologies are unchanging over the period 1990 -2020. The second scenario is the OCF scenario, where OCF stands for Our Common Future, the title of the Brundtland Report. This uses the same global economic and demographic assumptions as the reference scenario, but also has technologies changing over 1990 -2020. In the OCF scenario DL incorporate into the input-output model's coefficients technological improvements as envisaged in the Brundtland Report in energy and materials conservation, changes in the fuel mix for electricity generation, and measures to reduce SO 2 and NO 2 emissions per unit energy use. As indicators of environmental impact, the analysis uses the input-output model to track fossil fuel use and emissions of CO 2, SO 2 and NO 2. In the reference scenario, all of these indicators increase by about 150% over 1990 -2020. With the technological changes, there are big environmental improvements in the OCF scenario. But the indicators still go up - by 61% for fossil fuel use, by 60% for CO 2, by 16% for SO 2, and by 63% for NO 2. Given the assumed economic and population growth, the technological improvements are not enough to keep these environmental damage indicators constant. DL conclude that sustainable development as envisaged in the Brundtland Report is not feasible.

Input-output accounting 1 Table 8. 1 Input-output transactions table, $million Sales to: Intermediate sectors Purchases from Agriculture Manufacturing Service s Households Exports Intermediate sectors Agriculture 0 400 0 500 100 Total outpu t 1000 Manufacturing 350 0 150 800 700 2000 Services 100 200 0 300 0 600 Primary inputs Imports 250 600 50 Wages 200 500 300 Other value added Total input 100 300 1000 2000 600 across a row Final demand down a column

Input-output accounting 2 Because of the accounting conventions adopted in the construction of an I/O transactions table, the following will always be true: 1. For each industry: Total output Total input, that is, the sum of the elements in any row is equal to the sum of the elements in the corresponding column. 2. For the table as a whole: Total intermediate sales Total intermediate purchases, and Total final demand Total primary input Note the use here of the identity sign, , reflecting the fact that these are accounting identities, which always hold in an I/O transactions table. Reading across rows the necessary equality of total output with the sum of its uses for each industry or sector can be written as a set of ‘balance equations’: (8. 1) where Xi = total output of industry i Xij = sales of commodity i to industry j Yi = sales of commodity i to final demand n = the number of industries

Input-output modelling 1 To go from accounting to analysis, the basic assumption is (8. 2) where aij is a constant. Substituting 8. 2 into 8. 1 gives (8. 3) as a system of n linear equations in 2 n variables, the Xi and Yi, and n 2 coefficients, the aij. If the Yi – the final demand levels – are specified, there are n unknown Xi – the gross output levels – which can be solved for using the n equations.

Input-output modelling 2 In matrix notation, (8. 3) is which can be written (8. 4) where X is an n x 1 vector of gross outputs, A is an n x n matrix of coefficients aij, and Y is an n x 1 vector of final demands, Yi. With I as the identity matrix, (8. 4) can be written which has the solution (8. 5) where (I – A)-1 is the inverse of (I-A). This can be written (8. 6) L is often known as the Leontief inverse, in recognition of inventor of i-o analysis

Input-output modelling 3 (8. 7) – the lij are the elements of L. The Xi are the gross output levels for the final demands Yj. From the 3 -sector transactions table, the coefficients which are the elements of matrix A are Solving the system of three equations with these coefficients for the final demands from the transactions table gives the gross output levels from that table Agriculture X 1 = 999. 96 Manufacturing X 2 = 2000. 01 Services X 3 = 599. 94 Solving for Y 1 = 700, Y 2 = 1800, Y 3 = 400 gives Agriculture X 1 = 1180. 51 - for ∆Y 1 = 100, ∆X 1 = 180. 51 Manufacturing X 2 = 2402. 79 – for ∆Y 2 = 300, ∆X 2 = 402. 79 Services X 3 = 758. 26 – for ∆Y 3 = 100, ∆X 3 =158. 32

Environmental input-output analysis – changes in final demand Analysing the environmental effect of final demand changes Suppose that in addition to the data of Table 8. 1 we also know that the use of oil by the three industries was Agriculture Manufacturing Services 50 Pj 400 Pj 60 Pj With Oi for oil use in industry i, assume (8. 8) so that Then for get and hence

Attributing resource use and emissions to final demand deliveries 1 adding vertically gives which can be written (8. 10) where i 1 = r 1 l 11 + r 2 l 21 + r 3 l 31 etc. The left-hand side of equation 8. 10 is total oil use. The righthand side allocates that total as between final demand deliveries via the coefficients i. These coefficients give the oil intensities of final demand deliveries, oil use per unit, taking account of direct and indirect use. The coefficient i 1, for example, is the amount of oil use attributable to the delivery to final demand of one unit of agricultural output, when account is taken both of the direct use of oil in agriculture and of its indirect use via the use of inputs of manufacturing and services, the production of which uses oil inputs.

Attributing resource use and emissions to final demand deliveries 2 For the three sector example, the oil intensities are Agriculture Manufacturing 0. 1525 Servics 0. 2467 0. 1617 which with final demand deliveries of Agriculture Manufacturing 600 1500 Services 300 gives total oil use of 510 PJ, allocated across final demand deliveries as Agriculture 91. 50 Manufacturing 370. 05 Services 48. 51 As compared with the industry uses of oil from which the ri were calculated, these numbers have more oil use attributed to agriculture and less to manufacturing and services. This reflects the fact that producing agricultural output uses oil indirectly when it uses inputs from manufacturing and services.

Attributing resource use and emissions to final demand deliveries 3 In matrix algebra, which would be the basis for doing the calculations where the number of sectors is realistically large, n, the foregoing is O = RX = RLY = i. Y (8. 11) to define the intensities, where O is total resource use (a scalar) R is a 1 n vector of industry resource input coefficients i is a 1 n vector of resource intensities for final demand deliveries and X, L and Y are as previously defined. The resource uses attributable to final demand deliveries can be calculated as O = R* Y (8. 11/) where O is an n 1 vector of resource use levels R* is an n n matrix with the elements of R along the diagonal and 0 s elsewhere. With suitable changes of notation, all of this applies equally to calculations concerning waste emissions.

CO 2 intensities Australia Extract from Table 8. 3 CO 2 intensities and levels for final demand deliveries, Australia 1986/7 Sector CO 2 Intensitya CO 2 tonnes % of total Ag, forest, fishing 1. 8007 (6) 13. 836 (8) 4. 74 Food products 1. 532 (8) 11. 540 (10) 4. 00 Basic metal products 4. 4977 (4) 20. 25 (4) 6. 94 Electricity 15. 2449(1) 43. 747 (1) 14. 99 Gas 9. 9663 (3) 4. 675 (18) 1. 60 Construction 0. 7567 (19) 28. 111 (3) 9. 64 Community services 0. 4437 (26) 17. 802 (6) 6. 10 a. tonnes x 103/($A x 106) It is frequently stated that about 45% of Australian CO 2 emissions are from electricity supply. Much of that electricity output is input to other sectors, not delivery to final demand for electricity, and here gets attributed to other deliveries to final demand that it is used in the production of.

Box 8. 2 Attributing CO 2 emissions to UK households 1 Percentage of embedded CO 2 due to imports CO 2 emissions attributable to UK households CO 2 intensity household expenditure CO 2 attributable to UK households up 20% CO 2 embedded in imports CO 2 intensity of household expenditure down 20% Druckman and Jackson’s ‘embedded’ = indirect

Box 8. 2 Attributing CO 2 emissions to UK households 2 Table 8. 4 CO 2 emissions attributable to UK households 1992 -2004 Total Tonnes CO 2 x 106 Percentage Embedded Vehicle Use Flights Direct 1992 467. 2 49. 3 13. 2 2. 9 34. 6 1993 462. 1 50. 0 13. 4 3. 1 33. 5 1994 454. 1 50. 2 13. 3 3. 2 33. 2 1995 456. 8 51. 8 13. 0 3. 4 31. 8 1996 475. 0 50. 2 13. 2 3. 3 33. 3 1997 460. 0 51. 0 13. 9 3. 6 31. 6 1998 475. 4 51. 2 13. 3 3. 9 31. 6 1999 474. 8 51. 3 13. 7 4. 3 30. 7 2000 490. 2 51. 3 13. 1 4. 8 30. 9 2001 518. 8 52. 2 12. 5 4. 6 30. 6 2002 533. 0 53. 7 12. 6 4. 6 29. 1 2003 542. 1 54. 0 12. 2 4. 6 29. 2 2004 557. 4 54. 5 12. 0 4. 8 28. 7 Source: Druckman and Jackson (2009) Figures in first column correspond to index numbers in Figure 8. 1

Box 8. 2 Attributing CO 2 emissions to UK households 3 Table 8. 5 CO 2 emissions attributable to UK Supergroups 2004 Tonnes CO 2 Percentage Per household Per capita Embedded Flights Vehicle Use Direct 1. Prospering suburbs 26. 5 (1) 10. 4 (1) 54. 0 5. 5 12. 6 27. 9 2. Countryside 24. 9 (2) 10. 2 (2) 53. 8 5. 4 12. 4 28. 4 3. Typical traits 22. 4 (3) 9. 2 (3) 55. 1 5. 0 12. 3 27. 6 4. City living 18. 7 (5) 8. 3 (4) 56. 1 4. 3 11. 7 27. 9 5. Blue collar 19. 5 (4) 8. 0 (5) 54. 0 4. 5 12. 0 29. 6 6. Muticultural 18. 2 (6) 7. 7 (6) 55. 6 4. 0 11. 7 28. 8 7. Constrained by circumstances 16. 1 (7) 7. 4(7) 54. 2 3. 9 11. 1 30. 8 UK mean 21. 5 9. 0 54. 5 4. 8 12. 0 28. 7 Source: Druckman and Jackson (2009) Figures in brackets are ranks The worst-off spend a larger share of budget on direct energy use

Analysing the effects of technical change In 3 sector example Direct energy conservation A technological innovation that cuts per unit oil use in Manufacturing by 25% reduces total economy oil use by 100 Pj, 20%. Indirect energy conservation An innovation in the use of Manufacturing output in the Agriculture sector which cuts a 21 from 0. 35 to 0. 25 reduces total economy oil use by 24. 13 PJ, 5%. Combining direct and indirect energy conservation With both the reduction in oil use in Manufacturing and the use of Manufacturing in Agriculture, total oil use is cut by 118. 70 Pj, 23. 3%, less than the sum of the independent changes, because the direct cut in oil input to Manufacturing is being applied to a smaller gross output for that sector Energy conservation and CO 2 emissions reduction can be pursued by materials saving innovation. In the Australian data, cutting all input coefficients for Basic Metals by 10% would cut total CO 2 emissions by 1. 4%. Cutting the final demand for electricity by 10% would cut total CO 2 emissions by 1. 5%

Input-output modelling - costs and prices 1 For the columns of the transactions table (8. 12) or (8. 13) where Vj is primary input cost. With intermediate inputs as fixed proportions of industry outputs (8. 14) With prices which are all unity (8. 15) where vj is primary input cost per unit output

Input-output modelling – costs and prices 2 In matrix algebra (8. 15) is (8. 16) where P is an n x 1 vector of prices, A’ is the transpose of the n x n matrix of input-output coefficients, and v is an n x 1 vector of primary input coefficients. Rearranging (8. 16) which with I as the identity matrix is which solves for P as written more usefully as (8. 17) where L is the n x n Leontief inverse

Input-output modelling – costs and prices 3 For the 3 sector illustration transaction table the primary cost coefficients are Agriculture Manufacturing 0. 55 0. 70 Services 0. 75 Using these in (8. 17) with the Leontief inverse gives P 1 = 1, P 2 = 1 and P 3 =1. The usefulness of the analysis lies in figuring the effects on prices of changes to elements in the vector of primary cost vector, and/or of changes in the elements of the A matrix.

Carbon taxation in the three sector example CO 2 emissions arising in each sector are, kilotonnes Agriculture Manufacturing 3660 29280 Services 4392 The change in prices for the changes in the v coefficients is given by (8. 18) where ∆v′ is the transposed vector of changes in the primary input cost coefficients and ∆P′ is the transposed vector of consequent price changes. For the postulated rate of carbon taxation, using the figures above for emissions and the data from Table 8. 1 gives for which equation 8. 18, with L as given above, yields so that the price of the output of the agricultural sector, for example, rises by 18. 74% The results are conditional on no changes in the elements of the A matrix. If the carbon tax leads to changes in technology – substitution away from fossil fuels/energy conservation – the results here give an upper-bound to the price changes

The regressivity of carbon taxation 1 Extracts from Table 8. 7 Price increases due to a carbon tax of A$20 per tonne Sector Percentage Price Increase Rank Agriculture, forestry and fishing 1. 77 9 Food products 1. 46 16 Basic metals, products 9. 00 5 Electricity 31. 33 1 Gas 21. 41 2 Construction 1. 60 13 Community services 0. 93 21

The regressivity of carbon taxation 2 Given data on household expenditure patterns across the income distribution, using such with input-output price results can figure the changes in the cost of living for household groups. (8. 19) where CPI stands for Consumer Price Index h indexes household groups βhj is the budget share for commodity j for the household group h

The regressivity of carbon taxation 3 Table 8. 8 CPI impacts of carbon taxation Decile 1 Accounting for direct and indirect impacts % 2. 89 Accounting for only direct impacts % 1. 53 2 3. 00 H 1. 66 H 3 2. 97 1. 60 4 2. 85 1. 44 5 2. 88 1. 45 6 2. 77 1. 35 7 2. 80 1. 31 8 2. 77 1. 28 9 2. 67 1. 16 10 2. 62 L 1. 10 L All households 2. 79 1. 31 Direct impact when accounting only for household expenditure on electricity, gas, and petroleum and coal products. H is highest CPI impact, L lowest. Assumption is that expenditure patterns do not change in response to carbon tax.

Box 8. 3 Input-output analysis of rebound in Spanish water supply 1 Rebound is where technological change improving efficiency leads to an increase in use. Llop (2008) looks at an 18 x 18 A matrix for Spain, where industry 18 is water supply to calculate commodity price changes for 3 scenarios 1. The a coefficients in row 18 are reduced by 20% and in column 18 increased by 20% - water is used and supplied more efficiently 2. Imposition of 40% tax on price industries pay for water 3. Scenarios 1 and 2 combined With j =1, . . . 18, Pj 0 is the price of the jth commodity initially and Pj 1 is the price after the imposition of the scenario change, and similarly for Xj 0 and Xj 1. Let k be the ratio, the same across all sectors, by which expenditure changes when price changes, so that Pj 1 Xj 1 = k. Pj 0 Xj 0 and with Pj 0 =1 for all j, this means Xj 1 = k(Xj 0/Pj 1). gives the quantity demanded by industry j following a price change.

Box 8. 3 Input-output analysis of rebound in Spanish water supply 2 Scenario 1 Scenario 2 Scenario 3 Water Use change % Expenditure constant, k=1 20. 08 -28. 65 -14. 30 Table 8. 6 Changes in total industrial water use k = 1 is unitary elasticity of demand Expenditure down 10%, k=0. 9 8. 07 -35. 79 -22. 87 Expenditure up 10%, k=1. 1 32. 09 -1. 52 -5. 73 k = 0. 9 is approximately elasticity 0. 9 k = 1. 1 is approximately elasticity 1. 1 These results show 1. The change in total industrial water usage is very sensitive to the elasticity of demand 2. For the elasticities considered, there is rebound – efficiency improvements lead to greater use 3. Scenario 3 – that rebound effects can be offset by the introduction of a tax

Computable general equilibrium models CGE models are empirical versions of the Walrasian general equilibrium system and employ standard neoclassical assumptions – Market clearing Walras’s law Utility maximisation by households Profit maximisation/cost minimisation by firms Unlike input-output models, CGE models have substitution responses in production and consumption CGE models have been much used in relation to environmental issues.

An illustrative two-sector CGE model - data Manufacturi ng 1. 3490 Consumption Agriculture Agricultur e 0 3. 1615 Total output 4. 5105 Manufacturing 1. 1562 0 3. 1615 4. 3177 Wages 2. 5157 1. 4844 Other value added 0. 8386 1. 4843 Total input 4. 5105 4. 3177 Table 8. 9 Transactions table for the two-sector economy Only relative prices matter. Set the price of labour at unity. Then Agriculture P 1 = 2. 4490 Manufacturing P 2 = 3. 1355 Labour W = 1 Oil P = 1. 1620 With these prices get an input-output transactions table in physical units. Each Pj of oil gives rise to 73. 2 tonnes CO 2 emissions Agriculture Manufacturing Consumption Total output Agriculture 0 0. 5508 1. 2909 1. 8417 Manufacturing 0. 3687 0 1. 0083 1. 3770 Labour 2. 5157 1. 4844 Oil 0. 7217 1. 2774 Emissions 52. 8484 93. 5057 Table 8. 10 Physical data for the two-sector economy

An illustrative two-sector CGE model – market clearing and walras 1. Market clearing In regard to the use of intermediate goods in production use the standard input-output assumption, so (8. 20) 2. Connected markets Together with demand supply equations (8. 21) ties together the various markets, where Y is total household income, W is the wage rate, P is the price of oil, and Ri is oil used in the ith sector.

An illustrative two sector CGE model – household demand 3. Utility maximisation and household demand In the absence of sufficient data for proper econometric estimation it is usual to assume a plausible functional form and ‘calibrate’ from the benchmark data. Here Max subject to gives (8. 24) Using the benchmark data this is (8. 25) with solution α = β. The value α = 0. 5 is imposed.

An illustrative two-sector CGE model – intermediate demand production Intermediate demand From Table 8. 9, the transactions table Production (8. 26) With Constant Returns to Scale, profits are zero always and there is no supply function – firms produce to meet demand. Factor demand equations derived using cost minimisation. Numerical values fixed by calibration against benchmark data – Table 8. 10

An illustrative two-sector CGE model Box 8. 4 The illustrative CGE model specification and simulation results Computable general equilibrium model specification (1) C 1 = Y/2 P 1 (10) L 2 = UL 2 X 2 (2) C 2 = Y/2 P 2 (11) UR 1 = [0. 33(W/P)]0. 75 (3) X 1 = 0. 4 X 2 + C 1 (12) R 1 = UR 1 X 1 18 equations in 18 endogenous variables – W, P, Y, E, R and for i=1, 2 ULi, URi, Ci, Pi, Xi, Li Eqtns 1 and 2 – household demands Eqtns 3 and 4 – commodity balances (4) X 2 = 0. 2 X 1 + C 2 (13) UR 2 = [W/P]0. 5 (5) P 1 = 0. 2 P 2 + WUL 1 + PUR 1 (14) R 2 = UR 2 X 2 (6) P 2 = 0. 4 P 1 + WUL 2 + PUR 2 (15) E = E 1 + E 2 = e 1 R 1 + e 2 R 2 (7) UL 1 = [3(P/W)]0. 25 (16) Y = W(L 1 + L 2) + P(R 1 + R 2) (8) L 1 = UL 1 X 1 (17) L 1 + L 2 = L* Eqtn 16 – household income (9) UL 2 = [P/W]0. 5 (18) R 1 + R 2 = R* Eqtns 17 and 18 – fixed factor endowments, fully employed Eqtns 5 and 6 – pricing Eqtns 7, 9, 11, 13 – factor input per unit output Eqtns 8, 10, 12, 14 – convert to factor demands Eqtn 15 – total emissions

The solution algorithm 1. Take in parameter values and factor endowments 2. Labour is numeraire, W =1 (only interested in relative prices) 3. Assume value for P and use eqtns 7, 9, 11 and 13 to get unit factor demands 4. Use with solutions to eqtns 5 and 6 to get commodity prices and with assumed temporary value for X 1 get L 1 by eqtn 8 and R 1 by eqtn 12 5. L 2 = L* - L 1 6. Calculate X 2 and L 2 7. Get manufacturing demand for oil from eqtn 14 8. Get Y from eqtn 16 9. Get household commodity demands from eqtns 1 and 2 10. Compare (R 1 + R 2) with R*. For (R 1 + R 2)>R* increase P and repeat steps 1 to 10 until (R 1 + R 2) is close enough to R* For (R 1 + R 2)<R* reduce P and repeat steps 1 to 10 until (R 1 + R 2) is close enough to R* Stop

Simulation results for the illustrative model Table 8. 11 Computable general equilibrium model results A and B differ only in regard to relative prices Base case A Base case B 50% emissions reduction Reduction case as proportion of base case W 1 5 1 1 P 1. 1620 5. 7751 2. 3990 2. 0645 P 1 2. 4490 12. 2410 3. 0472 1. 2443 P 2 3. 1355 15. 6702 4. 3166 1. 3767 X 1 1. 8416 1. 8421 1. 4640 0. 7950 X 2 1. 3770 1. 0341 0. 7510 L 1 2. 5157 2. 5164 2. 3983 0. 9533 X 1 and X 2 fall L 2 1. 4844 1. 4836 1. 6017 1. 0790 L 1 down L 2 up R 1 0. 7216 0. 7226 0. 3332 0. 4618 R 2 1. 2774 1. 2780 0. 6677 0. 5227 R 2 2 1 0. 5000 E 1 52. 8484 24. 3902 0. 4618 E 2 93. 5057 48. 8756 0. 5227 E 146. 3541 73. 2658 0. 5000 Y 6. 324 31. 615 6. 3990 1. 0119 C 1 1. 2909 1. 2912 1. 0503 0. 8136 C 2 1. 0083 1. 0087 0. 7415 0. 7354 U 1. 1409 1. 1412 0. 8825 0. 7735 A reproduces original price and quantity data – calibration C cuts total emissions by 50%. P, P 1 and P 2 increase The loading of the total emissions reduction across sectors is efficient Households consume less of both commodities Higher nominal national income Lower utility

Box 8. 5 CGE modelling of energy rebound in the UK Improvements in energy efficiency may be partially or wholly offset by consequent increases in demand - a lower effective price for energy leads to its substitution for other inputs lower production costs increase income and demand Rebound is where there is partial offset Backfire is where the energy demand eventually increases Rebound/Backfire is an empirical question Allen et al (2007) use the CGE model UKENVI to investigate the question for the UK economy 25 commodities, 5 energy commodities 3 classes of agent – households, firms and government Rest of the world a single entity Calibrated on 2000 data base from the 1995 UK input-output tables

Rebound definitions ∆EE - the initial percentage change in energy efficiency ∆EM - the percentage change in total energy use after the economy has responded to the initial shock R - percentage rebound. with ∆EE<0, four cases can be distinguished: 1. ∆EM < 0 and greater in absolute value than ∆EE implies R < 0. 2. ∆EM < 0 and equal in absolute value to ∆EE implies R = 0. 3. ∆EM < 0 and smaller in absolute value than ∆EE implies 0 < R < 100. 4. ∆EM > 0 implies R > 100 If all agents respond rationally to a cut in the effective price of energy, as they do in CGE models, case 1 is going to be null, empty. Case 4 is Backfire

UKENVI - industry production structure Constant elasticity of substitution production functions with 2 inputs Output Figure 8. 2 Production structure of UKENVI model Value Added Intermediates ROW composite UK composite Labour Energy composite Non-electricity Electricity Renewable Non-renewable Capital Non-oil Oil Coal Gas

UKENVI results Table 8. 12 Selected simulation results from UKENVI % Change from Base Year Central case Elasticity of substitution reduced Constant costs Government expenditure adjusts Exogenous labour supply Real wage resistance GDP 0. 17 0. 16 -0. 33 0. 20 -0. 04 0. 90 Employment 0. 21 0. 03 0. 26 0. 00 0. 95 CPI -0. 27 -0. 23 0. 17 -0. 13 -0. 10 -0. 68 Rebound Electricity 27. 0% 11. 6% -10. 4% 26. 4% 21. 2% 47. 4% Non-electricity 30. 8% 13. 2% -3. 6% 30. 6% 24. 0% 55. 4% ‘Long run’ adjustments to an exogenous shock where all sectors improve energy use efficiency by 5% at third input level in Figure 8. 2. Central case shows rebound, but not backfire. The long run % change is smaller than the initial efficiency improvement Outcomes for all variables depend on model configuration – rebound can be avoided if efficiency gains accompanied by increased costs.

International distribution of abatement costs Table 8. 13 Costs associated with alternative instruments for global emissions reductions Region Option 1 Option 2 Option 3 EC – 4. 0 – 1. 0 – 3. 8 N. America – 4. 3 – 3. 6 – 9. 8 Japan – 3. 7 +0. 5 – 0. 9 Other OECD – 2. 3 – 2. 1 – 4. 4 Oil exporters +4. 5 – 18. 7 – 13. 0 Rest of world – 7. 1 – 6. 8 1. 8 World – 4. 4 – 4. 2 Figures are for % changes in GDP All options cut global emissions by 50% Option 1. Each region taxes fossil fuel production Option 2. Each region taxes fossil fuel consumption Option 3. A global tax is collected by an international agency which disposes of revenue by grants to regions based on population size This is least cost for World, but not for all regions, and under it ROW – mostly developing nations – gains.

Alternative uses of carbon tax revenue Table 8. 14 Effects of carbon taxation according to use of revenue S 1 S 2 Real Gross Domestic Product 0. 07 – 0. 09 Consumer Price Index – 0. 18 0. 42 Budget Balance* – 0. 02 0. 31 Employment 0. 21 – 0. 04 CO 2 Emissions – 3. 9 – 4. 7 Results from the ORANI CGE model for Australia. ORANI has a government sector, and overseas trade. S 1 Carbon tax to raise A$2 billion, used to reduce payroll tax S 2 Carbon tax to raise A$2 billion, used to reduce government deficit In both, money wage rate is fixed and the labour market does not clear. ‘Short run’ simulations * as percentage of GDP Carbon taxation has output and substitution effects in labour market A reduction in demand on account of GDP contraction due to trade effects of acting unilaterally An increase in demand due to higher relative price of fossil fuel input relative to labour input – plus reduced payroll tax effect in S 1

Benefits and costs of CGE modelling As compared with input-output models, the main benefit of CGE models is the inclusion of behavioural responses by consumers and producers. This is modelled as optimising behaviour – not everybody accepts that economic agents are in fact fully rational, and/or well-informed But: CGE models are not about short/medium term prediction. They are about insights into underlying tendencies. Data is a problem for CGE models – calibration rather than estimation CGE model results typically sensitive to changes in parameter values There are limits to the accuracy with which the variables that these models track are measured. Looking at UK annual GDP estimates, current price 1991 to 2004, the change between the first published number and the most recent available in 2006 ranged from 0. 4% to 2. 8% of GDP. That CGE model results are consistent with economic theory is not surprising – they incorporate it.