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Evaluating intervention options to achieve environmental benefits in the residential sector

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Abstract

Government intervention schemes in the form of policy instruments and financial incentives or rebates can have a major influence on the adoption of technologies by residential consumers to reduce their natural resource consumption and greenhouse gas emissions. However, the pattern and rate of consumer uptake of voluntary schemes are not always well-understood or easily taken into account in future scenarios analyses. This paper presents an innovative extension of the Bass diffusion model that has been integrated with multi-criteria analysis to enable explicit consideration and balancing of the impacts of technology cost, financial benefits, demographic suitability and household income on the likelihood of adoption. This ‘Intervention Options’ model is formulated into a constrained integer programming problem to allow optimisation of the size and timing of government rebates to maximise adoption rate and, ultimately, environmental benefits. The model’s capability is demonstrated using an Australian case study of 25,000 households, and historical information on the uptake of solar hot water and solar photovoltaic panels in Brisbane, Queensland. Case study results reveal new insights and important context-relevant trends that could assist policy makers to substantially improve the effectiveness of intervention schemes to achieve environmental goals within desired budgets.

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References

  • Australian Government (2008) Carbon pollution reduction scheme: Australia’s low pollution future, Department of Climate Change. http://www.climatechange.gov.au

  • Australian Government (2010) Department of Environment, Water, Heritage and the Arts—number of solar PV systems installed by month from 2000 to 2009. http://www.environment.gov.au

  • Bass FM (1969) A new product growth model for consumer durables. Manag Sci 15(5):215–217

    Article  Google Scholar 

  • Bass FM, Krishnan TV, Jain DC (1994) Why the Bass model fits without decision variables. Mark Sci 13:203–273

    Article  Google Scholar 

  • Bhat CR, Guo JY (2004) A mixed spatially correlated logit model: formulation and application to residential choice modeling. Transp Res Part B 38:147–168

    Article  Google Scholar 

  • Cochrane JL, Zeleny M (1973) Multiple criteria decision making. University of South Carolina Press, Columbia

    Google Scholar 

  • Everdigen Y, Aghina W, Fok D (2005) Forecasting cross-population innovation diffusion: a Bayesian approach. Int J Res Mark 22:293–308

    Article  Google Scholar 

  • Greene AL, Patterson PD, Sing M, Li J (2005) Feebates, rebates and gas-guzzler taxes: a study of incentives for increased fuel economy. Energy Policy 33:757–775

    Article  Google Scholar 

  • Guidolin M, Mortarino C (2010) Cross-country diffusion of photovoltaic systems: modelling choices and forecasts for national adoption patterns. Technol Forecast Soc Chang 77(2):279–296

    Article  Google Scholar 

  • Higgins A, Foliente G, McNamara C (2011) Modelling intervention options to reduce GHG emissions in housing stock—a diffusion approach. Technol Forecast Soc Chang 78(4):621–634

    Article  Google Scholar 

  • Horksy D (1990) A diffusion model for incorporating product benefits, price, income and information. Mark Sci 9(4):342–364

    Article  Google Scholar 

  • Horne M, Jaccard M, Tiedemann K (2005) Improving behavioral realism in hybrid energy–economy models using discrete choice studies of personal transportation decisions. Energy Econ 27:59–77

    Article  Google Scholar 

  • Jaccard M, Dennis M (2006) Estimating home energy decision parameters for a hybrid energy/economy policy model. Environ Model Assess 11:91–100

    Article  Google Scholar 

  • Jager J (2006) Stimulating the diffusion of photovoltaic systems: a behavioural perspective. Energy Policy 34:1935–1943

    Article  Google Scholar 

  • Jain DC, Rao K (1990) Effect of price on the demand for durables: modelling, estimation and findings. J Bus Econ Stat 8(2):163–170

    Google Scholar 

  • Kemp R, Volpi M (2008) The diffusion of clean technology: a review with suggestions for future diffusion analysis. J Clean Prod 16(S1):S14–S21

    Google Scholar 

  • Koeppel S, Urge-Vorsatz D (2007) Assessment of policy instruments for reducing greenhouse gas emissions from buildings. Central European University report to the United Nations Environment Programme, Sustainable Building and Climate initiative (UNEP-SBCI), Paris

  • Lobel R, Perakis G (2011) Consumer choice model for forecasting demand and designing incentives for solar technology. Social Science Research Network, MIT, Cambridge

  • Mansfield E (1961) Technical change and the rate of imitation. Econometrica 29(4):741–766

    Article  Google Scholar 

  • Marsdon Jacob Associates (2007) The economies of rainwater tanks and alternative water supply options. A report for the Australian Conservation Foundation, Nature Conservation Council and Environment Victoria, April 2007. http://www.marsdonjacob.com.au

  • Mills D (2010) Greenhouse gas emissions from energy use in Queensland homes, Sustainability Innovation Division, Department of Environmental and Resource Management, Queensland Government

  • Paevere P, Higgins A (2011) Diffusion Modelling of Electric Vehicle Uptake in Australia. World Sustainable Building Conference SB11 Helsinki

  • Palangkaraya A, Yong J, Webster W, Dawkins P (2009) The income distributive implications of recent private health insurance policy reforms in Australia. Eur J Health Econ 10:135–148

    Article  Google Scholar 

  • Queensland Government (2008) Household projections: Queensland Local Government Areas 2007. Department of Local Government, Planning, Sports and Recreation. http://www.lgp.qld.gov.au/pifu

  • Rao Usha K, Kishore VVN (2010) A review of technology diffusion models with special reference to renewable energy technologies. Renew Sustain Energy Rev 14(3):1070–1078

    Article  Google Scholar 

  • Scarpa R, Willis K (2010) Willingness to pay for renewable energy: primary and discretionary choice of British households for micro-generation technologies. Energy Econ 32:129–136

    Article  Google Scholar 

  • Sener I, Pendyala R, Bhat C (2009) Accommodating spatial correlation across choice alternatives in discrete choice models: application to modelling residential location choice behaviour. Transportation Research Board Annual Meeting 2009 Paper #09-2281

  • Soderholn P, Klassen G (2007) Wind power in Europe: a simultaneous innovation-diffusion model. Environ Resour Econ 36:163–190

    Article  Google Scholar 

Download references

Acknowledgements

The authors thank Ms. Cheryl McNamara, Ms. Julia Anticev and Mr. Stephen Egan of CSIRO for processing the model data and implementing the calibration routine. We also thank Ms. Rowan Gray of Brisbane City Council for support in selecting the appropriate case study suburbs and providing data.

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Correspondence to Andrew Higgins.

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Handled by Nick Harvey, University of Adelaide, Australia.

Appendix: Mathematical model and solution algorithm

Appendix: Mathematical model and solution algorithm

The main decision variable is based on the cost of the technology: \( x_{d,j}^{t} \) where j = 3 for upfront cost. For the optimisation, we let

$$ x_{d,3}^{t} = xb_{d}^{t} + c_{d}^{t} $$

where \( xb_{d}^{t} \) is the base cost without rebate, and \( c_{d}^{t} \) is the size (in AUD) of the incentive (rebate). For the optimisation, \( c_{d}^{t} \) is the decision variable. In most practical circumstances, it would be undesirable for \( c_{d}^{t} \) to be different for every demographic by location by building type \( d \in D \). The decision variable \( c_{d}^{t} \) may differ for building types (e.g. apartment versus separate house) and may need to differ under some means testing (e.g. \( c_{d}^{t} \) = 0 for high income categories of \( d \in D \)). To accommodate this situation, let \( DD^{k} \subset D \) be a subset of D where

$$ c_{d}^{t} = c_{d'}^{t} \, \forall d,d^{'} \in DD^{k} $$
(9)

That is, all incentives \( c_{d}^{t} \) within category set \( DD^{k} \) are of the same value.

$$ \cup DD^{k} \, \forall k = D,\;DD^{k'} \cap DD^{k} \, = 0 $$

That is the combination of all \( DD^{k} \) category sets = DD.

The size of the incentive will have upper and lower bounds:

$$ lb_{d}^{t} \le c_{d}^{t} \le ub_{d}^{t} $$
(10)

where \( lb_{d}^{t} ,ub_{d}^{t} \) are the lower and upper bounds of the incentive as defined by the user.

The budget constraint is:

$$ \sum\limits_{t \in T} {\sum\limits_{d \in D} {c_{d}^{t} \cdot A_{d}^{\prime } (t) \le B} } $$
(11)

where B is the total budget.

Constraints on maximum number of incentive changes across the planning horizon:

$$ h_{d}^{t} = \left\{ {\begin{array}{*{20}l} 1 & {{\text{if }}c_{d}^{t} - c_{d}^{t - 1} \ne 0} \\ 0 & {\text{otherwise }} \\ \end{array} } \right. $$

where:

\( h_{d}^{t} \in \left\{ {0,1} \right\} \), an integer variable with value 0 or 1. \( h_{d}^{o,t} = 1 \) if incentive \( c_{d}^{t} \) changes from time t − 1 to time t.

Then

$$ \sum\limits_{t \in T} {h_{d}^{t} \le \beta } \quad \forall o \in O,d \in D $$
(12)

where \( \beta \) is an input parameter for the maximum number of changes in the incentives over the planning horizon.

Objective functions

Two objective functions are considered.

Objective 1

The first objective is to maximise the total number of adopters at a key time period t = T subject to the budget:

$$ {\text{Max}}\;Z = \sum\limits_{d \in D} {A_{d} (T)} $$
(13)

for the case of summing over all options.

Equation 13 is subject to the constraints given in Eqs. 17 and 912.

Objective 2

The second objective is to minimise the cost to achieve a desired level of adoption at key time period t = T

$$ {\text{Min}}\;Z = \sum\limits_{t \in T} {\sum\limits_{d \in D} {c_{d}^{t} \cdot A_{d}^{\prime } (t)} } $$
(14)

subject to

$$ \sum\limits_{d \in D} {A_{d}^{o} (T) > {\text{AD}}} $$
(15)

and the constraints in Eqs. 17 and 912, where AD is the minimal level of adoption.

Greedy search heuristic for optimising rebates

There is a wide range of suitable meta-heuristics for solving the sub-problems for \( c_{d}^{t} \), including simulated annealing and tabu search, genetic algorithms and hybrid heuristics. Any of these methods can be applied and a comparison between methods is beyond the scope of this paper. In this study, we used a simple multi-start greedy search method.

The greedy search heuristic is based on the establishment of moves so as to transform a current solution to one of the neighbouring solutions. The greedy search escapes local optimal solutions by allowing up-hill (non-improving) moves to be performed when no down-hill (improving) moves are available. At each iteration, the neighbourhood (or a sample of it) is searched for which the move found in the search is applied, regardless of whether it is an uphill move. Instead of searching the entire neighbourhood, which can be very large, our algorithm will randomly select a subset N1, N2 for neighbourhoods 1 and 2 respectively. This sampling feature also helps escape local optimal solutions. Two neighbourhoods are applied:

  • Neighbourhood 1: Modify the incentive (rebate) for categories \( d \in DD^{k} \) from time period t′ through to time period t″. That is, set \( c_{d}^{t} \) = v for all \( d \in DD^{k} \) and \( t^{'} \le t \le t^{''} \).

  • Neighbourhood 2: Perform neighbourhood 1 twice simultaneously, where the incentives for one are modified upwards and the other are modified downwards.

The two neighbourhoods for the decision variables, \( c_{d}^{t} \), complement one another during the heuristic routine. Neighbourhood 1 is applied more frequently when it is difficult to improve the solution due to constraints (10, 11, 12). After \( \phi^{'} \) continuous iterations where the best solution is not improved, the search is intensified by replacing the current solution with the best so far. The greedy search used is described by Algorithm 1, based on objective 1 in Eq. 13.

Algorithm

Set \( \phi \) = 0

Set \( \phi^{'} \) = 25 which is the number of iterations without solution improvement.

C is the matrix solution of values \( c_{d}^{t} \)

Z′ represents the best found objective function overall.

Z″ represents the objective function of the working solution within the algorithm.

C′ represents the solution with the best found objective function overall.

C″ represent the working solution internally within the minor iteration of the algorithm.

N1 is the sample size for neighbourhood 1.

N2 is the sample size of neighbourhood 1 + 2.

Obtain an initial solution by running the model with no incentives (C = 0) and let Z be the objective function value.

Let Z′ = Z, Z″ = Z, C′ = C, C″ = C

REPEAT ! This is the major iteration

 REPEAT ! This is the minor iteration

  Randomly generate a sample of size N2 of solutions in the neighbourhood of C, whilst satisfying constraints 10–12.

  Let \( Z_{i} \) be the solution from the N2 solutions with the largest objective function

  IF \( Z_{i} \) > Z″, then Z″ = \( Z_{i} \), C″ = \( C_{i} \)

  IF \( Z_{i} \) > Z, then Z′ = Z, C′ = C, \( \phi \) = 0

  ADD \( C_{i} \) to the tabu list of the TL most recent solutions, and remove the oldest solution

  ADD 1 to \( \phi \)

UNTIL \( \phi = \phi^{'} \)

Z″ = Z′, C″ = C′

UNTIL convergence criteria is achieved.

For this case study, convergence was achieved after 30 min of CPU time on a standard dual core 2.8 GHz PC, as improvement in the solution was negligible after that time.

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Higgins, A., Foliente, G. Evaluating intervention options to achieve environmental benefits in the residential sector. Sustain Sci 8, 25–36 (2013). https://doi.org/10.1007/s11625-012-0160-x

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