Abstract
Understanding and governing technology transitions is essential to cope with major challenges of the 21st century such as climate change or digitization. In this paper, a learning-based approach is developed to explain the dynamics of different transition pathways. Technological know-how is necessary to make effective use of technical innovations embodied in capital. Firms and employees accumulate technology specific knowledge when working with specific machinery. Radical innovation differs by technology type and pre-existing knowledge may be imperfectly transferable across types. This paper addresses the implications of cross-technology transferability of skills for firm-level technology adoption and its consequences for the direction of macro-level technological change. A microeconomically founded model of technological learning is introduced. The model is based on empirical and theoretical insights from the innovation literature. In a simulation study using the macro-economic ABM Eurace@unibi-eco and applied to the context of green 2 technology diffusion, it is shown that a high transferability of knowledge has ambiguous effects. It accelerates the diffusion process initially but comes at the cost of long-term technological stability and specialization. For firms, it is easy to adopt new technology, but also easy to switch back to the incumbent type. Technological instability can be macroeconomically costly.
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Notes
The technical paradigm is more narrowly defined and represents the mindset of engineers and their way of defining a technological problem and its solution.
In another paper, it is shown that this framework can be generalized to a green entrant technology that is favorable because consumers have a higher willingness to pay for green products or lower production costs of green machinery (Hötte 2020b). Other models in climate and environmental economics frame the problem of green technology diffusion as an externality problem with unequal social and private costs. This study is aimed at improving the understanding of learning when a new technology suffers from lower maturity. Climate research has sufficiently shown that the problem of climate economics is not the search for optimal abatement levels trading off costs and benefits of mitigation. Rather, it is important to understand how the transition can be accelerated (cf. Steffen et al. 2018; IPCC 2018). Moreover, the trade-off of mitigation costs and benefits is extremely sensitive to the assumptions of technological change (Löschel 2002). This underlines the relevance of improving the understanding of change. However, it is possible to extend the model and to incorporate climate-induced damage functions and to frame the analysis as an optimal policy problem that can be numerically approached.
This example has actually a historical counterpart, when delivery services for milk, bread or postal services used electric vehicles in the 60-70s (Høyer 2008). A similar example refers to the diffusion of organic farming, which was mainly driven by consumer preference, but lacking experiences in farming practices, regulatory compliance procedures and marketing were reasons for re-conversion to conventional farming (Flaten et al. 2010).
Further information about its computation and relation to other convergence measures can be found in the Supplementary Material SM.II.
The average level of green technology use in T does not necessarily coincide with the transition frequency. The average share of green (conventional) technology use may range well below 100% in the subset of green (conventional) regimes. The average \({\nu ^{c}_{t}}\) accounts for {34.16%, 29.80%, 64.20%} for χdist = 0, 0.5, 1.
It should be noted that the pricing mechanism for capital goods is important for the convergence. In the model, capital prices are adaptively adjusted in response to changes in the relative demand. The frontier is only a stabilizing mechanism if relative technological progress is faster than the relative increase in nominal prices. This is an assumption but alternative configurations are possible in which the economy does not converge because the leading technology becomes too expensive. This might be the case if, for example, resources to produce capital goods are scarce and type-specific. In other words, this mechanism is sensitive to the price elasticity of capital goods supply. In these simulations, the price responsiveness is sufficiently moderate that convergence is possible even when spillovers are perfect.
Further information about its computation is available in the SM.II.
Technical detail can found in SM.II.
References
Acemoglu D (2002) Directed technical change. Rev Econ Stud 69(4):781–809. https://doi.org/10.1111/1467-937X.00226
Acemoglu D, Aghion P, Bursztyn L, Hemous D (2012) The environment and directed technical change. Am Econ Rev 102(1):131–66. https://doi.org/10.1257/aer.102.1.131
Acemoglu D, Akcigit U, Kerr WR (2016) Innovation network. Proc Natl Acad Sci 113(41):11483–11488. https://doi.org/10.1073/pnas.1613559113
Adner R, Kapoor R (2016) Innovation ecosystems and the pace of substitution: Re-examining technology s-curves. Strateg Manag J 37(4):625–648. https://doi.org/10.1002/smj.2363
Allan C, Jaffe AB, Sin I (2014) Diffusion of green technology: a survey. Motu working paper no. 14–04
Antony J, Grebel T (2012) Technology flows between sectors and their impact on large-scale firms. Appl Econ 44(20):2637–2651. https://doi.org/10.1080/00036846.2011.566191
Arndt F, Pierce L (2017) The behavioral and evolutionary roots of dynamic capabilities. Ind Corp Chang 27(2):413–424. https://doi.org/10.1093/icc/dtx042
Arthur WB (1989) Competing technologies, increasing returns, and lock-in by historical events. Econ J 99(394):116–131. https://doi.org/10.2307/2234208
Arundel A, Kemp R (2009) Measuring eco-innovation. UNU-Merit - Working Paper Series 2009–017
Autor DH, Levy F, Murnane RJ (2003) The skill content of recent technological change: An empirical exploration. Q J Econ 118 (4):1279–1333. https://doi.org/10.1162/003355303322552801
Bacon CJ (1992) The use of decision criteria in selecting information systems/technology investments. MIS Q 335–353. https://doi.org/10.2307/249532
Boehm J, Dhingra S, Morrow J et al (2016) Swimming upstream: input-output linkages and the direction of product adoption. CEP Discussion Paper No. 1407
Bower JL, Christensen CM (1995) Disruptive technologies: catching the wave. Harvard Business Review
Breschi S, Malerba F, Orsenigo L (2000) Technological regimes and Schumpeterian patterns of innovation. Econ J 110(463):388–410. https://doi.org/10.1111/1468-0297.00530
Brynjolfsson E, McAfee A (2012) Race against the machine: How the digital revolution is accelerating innovation, driving productivity, and irreversibly transforming employment and the economy. Brynjolfsson and McAfee
Carvalho VM (2014) From micro to macro via production networks. J Econ Perspect 28(4):23–48. https://doi.org/10.1257/jep.28.4.23
Carvalho VM, Voigtländer N (2014) Input diffusion and the evolution of production networks. National Bureau of Economic Research, Working Paper No. w20025
Cohen WM, Levinthal capacity DA (1990) Absorptive A new perspective on learning and innovation. Adm Sci Q 35 (1):128–152. https://doi.org/10.2307/2393553
Cowan R, David PA, Foray D (2000) The explicit economics of knowledge codification and tacitness. Ind Corp Chang 9(2):211–253. https://doi.org/10.1093/icc/9.2.211
Dawid H (2006) Agent-based models of innovation and technological change. In: Tesfatsion L, Judd K (eds) Handbook of computational economics, Volume II: Agent-based computational economics, chapter 25. https://doi.org/10.1016/S1574-0021(05)02025-3. Elsevier, pp 1235–1272
Dawid H, Harting P, Neugart M (2018) Cohesion policy and inequality dynamics: Insights from a heterogeneous agents macroeconomic model. J Econ Behav Organ 150:220–255. https://doi.org/10.1016/j.jebo.2018.03.015
Dawid H, Harting P, van der Hoog S, Neugart M (2019) Macroeconomics with heterogeneous agent models: fostering transparency, reproducibility and replication. J Evol Econ 29(1):467–538. https://doi.org/10.1007/s00191-018-0594-0
Doraszelski U (2003) An RandD race with knowledge accumulation. Rand J Econ 20–42. https://doi.org/10.2307/3087441
Dosi G (1982) Technological paradigms and technological trajectories: a suggested interpretation of the determinants and directions of technical change. Res Policy 11(3):147–162. https://doi.org/10.1016/0048-7333(82)90016-6
Dosi G, Nelson RR (2010) Technical change and industrial dynamics as evolutionary processes. In: Handbook of the economics of innovation. https://doi.org/10.1016/S0169-7218(10)01003-8, vol 1. Elsevier, pp 51–127
Flaten O, Lien G, Koesling M, Løes A-K (2010) Norwegian farmers ceasing certified organic production: Characteristics and reasons. J Environ Manag 91(12):2717–2726. https://doi.org/10.1016/j.jenvman.2010.07.026
Geels FW (2002) Technological transitions as evolutionary reconfiguration processes: a multi-level perspective and a case-study. Res Policy 31 (8-9):1257–1274. https://doi.org/10.1016/S0048-7333(02)00062-8
Geels FW (2018) Disruption and low-carbon system transformation: Progress and new challenges in socio-technical transitions research and the Multi-Level Perspective. Energy Res Soc Sci 37:224–231. https://doi.org/10.1016/j.erss.2017.10.010
Geels FW, Schot J (2007) Typology of sociotechnical transition pathways. Res Policy 36(3):399–417. https://doi.org/10.1016/j.respol.2007.01.003
Gerst MD, Wang P, Roventini A, Fagiolo G, Dosi G, Howarth RB, Borsuk ME (2013) Agent-based modeling of climate policy: An introduction to the ENGAGE multi-level model framework. Environ Model Softw 44:62–75. https://doi.org/10.1016/j.envsoft.2012.09.002
Gillingham K, Newell RG, Pizer WA (2008) Modeling endogenous technological change for climate policy analysis. Energy Econ 30(6):2734–2753. https://doi.org/10.1016/j.eneco.2008.03.001
Grübler A (1991) Diffusion: long-term patterns and discontinuities. In: Diffusion of technologies and social behavior. https://doi.org/10.1007/978-3-662-02700-4_18. Springer, pp 451–482
Grübler A, Nakićenović N, Nordhaus WD (2002) Technological change and the environment. Resources for the Future
Hötte K (2019a) How to accelerate green technology diffusion? An agent-based approach to directed technological change with coevolving absorptive capacity. Bielefeld Working Papers in Economics and Management No. 01-2019 Bielefeld University
Hötte K (2019b) Eurace@unibi-eco: A model of technology transitions, v1.1, Model documentation. Bielefeld Working Papers in Economics and Management No. 08-2019 Bielefeld University
Hötte K (2019c) Skill transferability and the stability of transition pathways-a learning-based explanation for patterns of diffusion. Bielefeld Working Papers in Economics and Management No. 09-2019, Bielefeld University
Hötte K (2019d) Data publication: Skill transferability and the adoption of new technology: A learning based explanation for patterns of diffusion. Data Publication Bielefeld University
Hötte K (2020) How to accelerate green technology diffusion? directed technological change in the presence of coevolving absorptive capacity. Energy Econ 85:104565. https://doi.org/10.1016/j.eneco.2019.104565
Hötte K (2020) The economics of transition pathways: A proposed taxonomy and a policy experiment. Environ Innov Soc Transit 36:94–113. https://doi.org/10.1016/j.eist.2020.05.001
Høyer KG (2008) The history of alternative fuels in transportation: The case of electric and hybrid cars. Util Policy 16(2):63–71. https://doi.org/10.1016/j.jup.2007.11.001
IPCC (2018) Summary for policymakers. In: Masson-Delmotte V, Zhai P, Prtner H, Roberts D, Skea J, Shukla PR, Pirani A, Moufouma-Okia W, Pan C, Pidcock R, Connors S, Matthews JBR, Chen Y, Zhou X, Gomis MI, Lonnoy E, Maycock T, Tignor M, Waterfield T (eds) An IPCC Special Report on the impacts of global warming of 1.5C above pre-industrial levels and related global greenhouse gas emission pathways, in the context of strengthening the global response to the threat of climate change, sustainable development, and efforts to eradicate poverty, Summary for Policymakers. World Meteorological Organization, Geneva, Switzerland
Jaffe AB, De Rassenfosse G (2017) Patent citation data in social science research Overview and best practices. Journal of the Association for Information Science and Technology 68(6):1360–1374. https://doi.org/10.1002/asi.23731
Johnson B, Lorenz E, Lundvall B-Å (2002) Why all this fuss about codified and tacit knowledge? Ind Corp Chang 11(2):245–262. https://doi.org/10.1093/icc/11.2.245
Kemp R, Volpi M (2008) The diffusion of clean technologies: a review with suggestions for future diffusion analysis. J Clean Prod 16(1):14–21. https://doi.org/10.1016/j.jclepro.2007.10.019
Kogut B, Zander U (1992) Knowledge of the firm, combinative capabilities, and the replication of technology. Organ Sci 3(3):383–397. https://doi.org/10.1287/orsc.3.3.383
Köhler J, De Haan F, Holtz G, Kubeczko K, Moallemi E, Papachristos G, Chappin E (2018) Modelling sustainability transitions: An assessment of approaches and challenges. J Artif Soc Soc Simul 21(1):8. https://doi.org/10.18564/jasss.3629
Köhler J., Geels FW, Kern F, Markard J, Onsongo E, Wieczorek A, Alkemade F, Avelino F, Bergek A, Boons F et al (2019) An agenda for sustainability transitions research: State of the art and future directions. Environ Innov Soc Transit. https://doi.org/10.1016/j.eist.2019.01.004
Kuhn M (2018) Caret: Classification and regression training. Technical report. https://CRAN.R-project.org/package=caret.Rpackageversion6.0-81
Lachman DA (2013) A survey and review of approaches to study transitions. Energy Policy 58:269–276. https://doi.org/10.1016/j.enpol.2013.03.013
Lamperti F, Dosi G, Napoletano M, Roventini A, Sapio A (2018) Faraway, so close: coupled climate and economic dynamics in an agent-based integrated assessment model. Ecol Econ 150:315–339. https://doi.org/10.1016/j.ecolecon.2018.03.023
Lemoine D (2018) Innovation-led transitions in energy supply. National Bureau of Economic Research, Working Paper No. w23420
Löschel A (2002) Technological change in economic models of environmental policy: a survey. Ecol Econ 43(2-3):105–126. https://doi.org/10.1016/S0921-8009(02)00209-4
McNerney J, Farmer JD, Redner S, Trancik JE (2011) Role of design complexity in technology improvement. Proc Natl Acad Sci 108 (22):9008–9013. https://doi.org/10.1073/pnas.1017298108
Metcalfe J (1988) The diffusion of innovations: an interpretive study. In: Dosi G, Freeman C, Nelson R, Silverberg G, Soete L (eds) Technical change and economic theory. Pinter
Nelson RR, Phelps ES (1966) Investment in humans, technological diffusion, and economic growth. Am Econ Rev 56(1/2):69–75
Nelson RR, Winter SG (1977) In search of useful theory of innovation. Res Policy 6(1):36–76. https://doi.org/10.1007/978-3-0348-5867-0_14
Nelson RR, Winter SG (1982) An evolutionary theory of economic change. Belknap Press of Harvard University Press
Pizer WA, Popp D (2008) Endogenizing technological change: Matching empirical evidence to modeling needs. Energy Econ 30(6):2754–2770. https://doi.org/10.1016/j.eneco.2008.02.006
Popp D, Newell RG, Jaffe AB (2010) Energy, the environment, and technological change. In: Hall B, Rosenberg N (eds) Handbook of the economics of innovation. https://doi.org/10.1016/S0169-7218(10)02005-8, vol 2. Elsevier, pp 873–937
R Core Team (2018) R: A language and environment for statistical computing. Technical report, Vienna, Austria. https://www.R-project.org/
Rengs B, Scholz-Wäckerle M, van den Bergh J (2020) Evolutionary macroeconomic assessment of employment and innovation impacts of climate policy packages. J Econ Behav Organ 169:332–368. https://doi.org/10.1016/j.jebo.2019.11.025
Rogelj J, Den Elzen M, Höhne N, Fransen T, Fekete H, Winkler H, Schaeffer R, Sha F, Riahi K, Meinshausen M (2016) Paris Agreement climate proposals need a boost to keep warming well below 2 C. Nature 534(7609):631. https://doi.org/10.1038/nature18307
Romer PM (1990) Endogenous technological change. J Polit Econ 98(5, Part 2):S71–S102. https://doi.org/10.1086/261725
Safarzyńska K, Frenken K, van den Bergh JC (2012) Evolutionary theorizing and modeling of sustainability transitions. Res Policy 41(6):1011–1024. https://doi.org/10.1016/j.respol.2011.10.014
Simon HA (1957) Administrative behavior: a study of decision making processes in administrative organization. Wiley, New York
Sjolander A, Dahlqwist E, Martinussen T (2019) Ivtools: Instrumental variables. Technical report. https://CRAN.R-project.org/package=ivtools.Rpackageversion2.2.0
Stasinopoulos MD, Rigby RA, Heller GZ, Voudouris V, De Bastiani F (2017) Flexible regression and smoothing: using GAMLSS in R, Chapman and Hall/CRC, London
Steffen W, Rockström J, Richardson K, Lenton TM, Folke C, Liverman D, Summerhayes CP, Barnosky AD, Cornell SE, Crucifix M et al (2018) Trajectories of the earth system in the anthropocene. Proc Natl Acad Sci 115(33):8252–8259. https://doi.org/10.1073/pnas.1810141115
Teece D, Pisano G (1994) The dynamic capabilities of firms: an introduction. Ind Corp Chang 3(3):537–556. https://doi.org/10.1093/icc/3.3.537-a
Thompson P (2012) The relationship between unit cost and cumulative quantity and the evidence for organizational learning-by-doing. J Econ Perspect 26(3):203–24. https://doi.org/10.1257/jep.26.3.203
Unruh GC (2000) Understanding carbon lock-in. Energy Policy 28(12):817–830. https://doi.org/10.1016/S0301-4215(00)00070-7
Venables WN, Ripley BD (2002) Modern applied statistics with s, vol 4. Springer, New York. http://www.stats.ox.ac.uk/pub/MASS4
Vona F, Consoli D (2014) Innovation and skill dynamics: a life-cycle approach. Ind Corp Chang 24(6):1393–1415. https://doi.org/10.1093/icc/dtu028
Vona F, Marin G, Consoli D, D. Popp. (2015) Green skills. National Bureau of Economic Research Working Paper National Bureau of Economic Research
Wiesenthal T, Dowling P, Morbee J, Thiel C, Schade B, Russ P, Simoes S, Peteves S, Schoots K, Londo M et al (2012) Technology learning curves for energy policy support. JRC scientific and policy reports, 332
Wolf S, Fürst S, Mandel A, Lass W, Lincke D, Pablo-Marti F, Jaeger C (2013) A multi-agent model of several economic regions. Environ Model Softw 44:25–43. https://doi.org/10.1016/j.envsoft.2012.12.012
Zeileis A, Hothorn T (2002) Diagnostic checking in regression relationships. R News 2(3):7–10. https://CRAN.R-project.org/doc/Rnews/
Acknowledgments
I want to thank two anonymous reviewers for their valuable feedback and careful revisions that helped me to improve this work significantly. Moreover, gratitude is also owed to Herbert Dawid, Philipp Harting and Antoine Mandel who made this work possible. The author thankfully acknowledges financial support by the German National Academic Foundation, the Deutsch-französische Hochschule and the Bielefeld Graduate School of Economics and Management. This work uses a modified version of the Eurace@unibi model, developed by Herbert Dawid, Simon Gemkow, Philipp Harting, Sander van der Hoog and Michael Neugart, as an extension of the research within the EU 6th Framework Project Eurace.
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Appendix A: Simulation results
Appendix A: Simulation results
1.1 A.1 Settings
1.2 A.2 Baseline
Here, only some general features of the simulated time series data are shown. Information about the empirical validation is available in SM.I. More detail on this baseline simulations is available in Hötte (2019b). A longer discussion of a similar simulation is provided in Hötte (2020a). A difference to the simulations in Hötte (2020a) is given by lower diffusion barriers of the green technology and another specification of the learning function. The simulation model, the simulated data and a selection of results of descriptive statistics is available in a separate data publication (Hötte 2019d).
In Fig. 7, the time series are dis-aggregated into green, conventional and so-called switching regimes. A simulation run is classified as switching regime if the diffusion process is very volatile, i.e. when \({\nu ^{c}_{t}}\) heavily fluctuates between low and high levels or when \({\nu ^{c}_{t}}\) has not converged to more than 90% or less than 10% in T (cf. Hötte 2020a). This is associated with uncertainty about the final technological state. The time series data illustrate that “technological uncertainty” is costly in terms of aggregate (log) output (Fig. 7j). It is associated with wasted resources because R&D and learning time are invested in a technology that becomes obsolete in the long run. This leads to a delayed technological specialization compared to the green or conventional regimes with a more clear-cut technological path selection. Figure 7d and e show that this is associated with a delayed divergence in relative knowledge stocks which is a reason and a result of uncertainty.
Figure 7g shows the evolution of relative prices for capital goods and Fig. 7h shows this price normalized by the relative productivity. Figure 7f illustrates the price for material resource inputs normalized by real wages. The price evolves such that it accounts for roughly 9.5% of wage costs for an average firm during the whole time horizon.
Figure 7c illustrates an alternative environmental performance measure, called eco-efficiency, that measures the environmental impact (here amount of natural resource inputs) per unit of produced output. The eco-efficiency also improves when the productivity performance in the lock-in regime improved by technical progress which is a relative decoupling of production from environmental damages. Principally, there can be a trade-off between the specialization in the conventional technology and the switch to green technology if the success of the transition is uncertain. However, modeling this trade-off is very sensitive to the modeling assumptions regarding the environmental impact, initial conditions about the available technology options and productivity improvements in both sectors. In this study, the focus is on replacement dynamics in a theoretical way which allows to be agnostic about assumptions that may critically affect such a trade-off analysis.
A two-sided Wilcoxon test indicates that the differences between green and conventional regimes a (cf. Fig. 7) are significant (see SM.I.3).
1.3 A.3 The ease of learning
The pace of relative technological learning is also dependent on the technological difficulty χint. If a technology is very easy to learn, i.e. χint = 0, the learning progress is independent of the time invested in learning which is proxied by \(\nu ^{c}_{i,t}\). If χint is high, the progress is sensitive to \(\nu ^{c}_{i,t}\), i.e. learning is more effective if employees work only with one technology type. In an experiment that is longer discussed in Hötte (2019c), it had been shown that χint is only of minor importance in the presence of cross-technology spillovers.
The impact of the difficulty on the learning speed is most critical in times when firms are transitioning to alternative technology. During a phase of technology change, a trade-off in the allocation of the learning time exists. This trade-off is more pronounced when a technology is difficult to learn. A technology that is easier to learn is associated with lower technology switching costs. This may have an ambiguous effect on green technology diffusion. It is easier to switch to green technology, but it is also easier to switch back if the difficulty is symmetric. Whether increasing returns to learning stabilize an ongoing diffusion process, depends on the extent to which the green technology is adopted in the first years.
The adoption in the early phase is facilitated by cross-technology spillovers reflected in a lower distance χdist. If the transferability is sufficiently low, increasing returns to learning contribute to the stabilization of the technological regimes.
1.4 A.4 Interactions between spillovers and the ease of learning
In the Monte-Carlo experiment in Section 4.3, the learning parameters are drawn at random, i.e. χdist ∈ [0, 1] and χint ∈ [0, 2]. Diffusion barriers at the day of market entry are fixed at a level of 3% (βA = βb = .03) as before. The transition probability accounts for 64%.
In Table 4, means and standard deviation of the initialization are summarized as aggregate and dis-aggregated by regime subsets. The p-value in the last column indicates whether the difference in means between the two regime types is significant. The average mean of the distance χdist is significantly lower in the subset of green regimes. The difference in the χint is only weakly significant at a 10% level. Some general descriptive information of these simulations is provided in SM.III.2.
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Hötte, K. Skill transferability and the stability of transition pathways- A learning-based explanation for patterns of diffusion. J Evol Econ 31, 959–993 (2021). https://doi.org/10.1007/s00191-020-00710-7
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DOI: https://doi.org/10.1007/s00191-020-00710-7
Keywords
- Technological transition
- Technology diffusion
- Technological knowledge
- Knowledge spillover
- Learning
- Absorptive capacity
- Agent-based model