Abstract
In this paper, we are examining the environmental Kuznets curve (EKC) in the context of a circular economy recycling model. Our model assumes that there are only two factors of production in the production of the final good, a recyclable and a polluting input. We also present two extensions of this basic model by adding technological progress in the production of the polluting input and a dynamic reduction of the influence of the same input respectively. Our results suggest the presence of an inverse-U curve for the EKC confirming the findings of most of the current literature as well as an increasing curve for the recycling output nexus.
![](http://media.springernature.com/m312/springer-static/image/art%3A10.1007%2Fs43615-022-00177-7/MediaObjects/43615_2022_177_Fig1_HTML.png)
![](http://media.springernature.com/m312/springer-static/image/art%3A10.1007%2Fs43615-022-00177-7/MediaObjects/43615_2022_177_Fig2_HTML.png)
![](http://media.springernature.com/m312/springer-static/image/art%3A10.1007%2Fs43615-022-00177-7/MediaObjects/43615_2022_177_Fig3_HTML.png)
![](http://media.springernature.com/m312/springer-static/image/art%3A10.1007%2Fs43615-022-00177-7/MediaObjects/43615_2022_177_Fig4_HTML.png)
Similar content being viewed by others
Data availability
There are no data that are to become available and all the values of the parameter choices in the paper are mentioned in the text.
Notes
As described by Eq. 5, pollution arises from two sources. One is the pollution coming from the polluting input used in the production process and one is pollution coming from unrecycled waste (which is coming from unused product, hence from production). Moreover, there is a last term which reduces pollution as the environment is assumed to be self-renewable at some degree.
A linear choice of the utility function unfortunately would make the consumption path disappear. For this reason, we have opted to use a logarithmic function as it is usual in the literature.
We can assume an input like recycled paper, glass, and plastic for the recyclable input, while primary paper, glass, plastic, metals, or any other primary extracted resource for the polluting input.
We constraint the production function so as to exclude the perfect substitutability of the two inputs, avoiding like that a case where we would have a linear production function.
We want to thank the reviewer for that important note.
One of the most important differences between our model and the one of George et al. [2] lies in the above constraint function (Eq. 4). Both studies include the waste accumulation function, but their meaning is different leading to substantial differences on the results. The George et al. [2] paper assumes that the polluting resource has a unit cost equal to a, and in order to employ this input in the production of the final good they have to face a total cost of az, which is also included in their waste accumulation path, implying its measurement is done in value terms rather than units. On the other hand, we do not take into account that unit cost for the polluting resource, and thus our respective constraint is measured in units, which is consistent with the original EKC.
The extraction and production of renewable resources often involve extensive use of energy, materials, chemicals, and in some cases water, and all this translates into pollution. Hence, for robustness, we have modified the pollution accumulation path to account for pollution stemming from the extraction of the polluting input and we have also included an additional constraint explaining how the remaining stock of the polluting input changes over time. Finally, we based that extension on the first extension model which includes technological progress. The resource extraction resource is followed by an increase of pollution by a rate equal to \(\in\), leading to a total amount of pollution equal to \(\in z\). Hence, the pollution accumulation path is described by: \(\dot P=\left(\theta+\mathit\in\right)Z+\left(1-\beta\right)S-\delta P\). In addition, we assume that the remaining stock of the polluting resource is given by \(\xi\) and that the firm uses the entire resource extracted in the production process. So, \(z\) can be described not only as the polluting input used in the production of the final good but also as the resource extracted. Hence, the law of motion of the remaining stock of the resource is described by: \(\dot\xi=\xi-z\). That constraint is taken from Venables [36] but is adjusted to reflect our model. Solving the Hamiltonian\(H=e^{-pt}u\left(c,P\right)+\lambda\left[\mathit\varnothing\left(\tau\beta S\mathit,A_tz\right)\mathit-c\mathit-z\mathit-\tau\beta S\right]+\mu\left[\left(\mathit\varnothing+\mathit\in\right)z-\delta P+\left(1-\beta\right)S\right]+0\left(\xi-z\right)\), we find an increasing curve for the recycling-output curve while a decreasing curve for the EKC.
The system of differential equations we have to solve consists of nonlinear differential equations; thus, in order to solve them, we need to use a computing environment and for that we use MATLAB.
Figures 1 and 2 have been made by assuming that the weight \(\gamma\) in the production function is equal to 0.5 for both inputs. We have also tried different combinations of weights and parameter values in general with the results being very similar. More plots of this model with different weights can be found in the Appendix 11.
The above results are under the constraint that \(\beta\ast\tau\geq1\). For the case that this does not hold, we are still able to find an increasing curve for the relationship between recycling and output, while for the classical EKC we find that the relationship between pollution and output is just decreasing.
If we assume that technological progress affects the production of the recyclable input \(x\), then the production of this resource becomes more efficient, and less waste is needed to produce it. In particular, to produce the same amount of recyclable input as before, we now need less waste inputs, so the waste pile starts to grow faster and the pollution level coming from the waste increases. Hence, better technology in the production of the recyclable input leads to lower recycling and higher pollution levels.
Figures 3 and 4 have been constructed assuming that the weight \(\gamma\) in the production function is equal to 0.7 for the polluting input and 0.3 for the recyclable input. The plots do not change much when we use different weights and, again, more plots of this model with different weights and parameter values combinations can be found in Appendix 11.
The results depicted in Figs. 3 and 4 are under the same constraint as the basic model. For \(\beta\ast\tau\geq1\) and \(\beta\ast\tau<1\), we get the inverse-U pattern for the EKC and an increasing curve for the recycling-output curve. For the case that this constraint does not hold, the relationship between recycling and output does not change and we still get an increasing curve. For the relationship between pollution and output, we find a decreasing curve showing that the EKC is not characterized by an inverse-U curve anymore.
More plots with different parameter values are available under request from the author but are not included here to conserve space.
Once again, Figs. 13 and 14 have been made by assuming that the weight \(\gamma\) in the production function is equal to 0.5 for both inputs. However, the results are similar under many different combinations of parameter values as well as initial values for the variables, and they are available under request from the author.
In that case the results are not constrained. Both under \(\beta\ast\tau\geq1\) and \(\beta\ast\tau<1\) we get the inverse-U pattern for the EKC and an increasing curve for the relationship between recycling and output.
References
G. M. Grossman, A. B. Krueger (1991) Environmental impacts of a North American free trade agreement
George DA, Lin BC-A, Chen Y (2015) A circular economy model of economic growth. Environ Model Softw 73:60–63
Andreoni J, Levinson A (2001) The simple analytics of the environmental kuznets curve. J Public Econ 80:269–286
Jeffords C, Thompson A (2019) The human rights foundations of an EKC with a minimum consumption requirement: theory, implications, and quantitative findings. Lett Spat Resour Sci 12:41–49
Abrate G, Ferraris M (2010) The environmental Kuznets curve in the municipal solid waste sector, HERMES working paper 1
Stokey NL (1998) Are there limits to growth?, International economic review 1–31.
Lopez R, Mitra S (2000) Corruption, pollution, and the Kuznets environment curve. J Environ Econ Manag 40:137–150
Lieb CM (2004) The environmental Kuznets curve and flow versus stock pollution: the neglect of future damages. Environ Resource Econ 29:483–506
De Bruyn SM, Opschoor JB (1997) Developments in the throughput-income relationship: theoretical and empirical observations. Ecol Econ 20:255–268
Steger TM, Egli H (2007) A dynamic model of the environmental Kuznets curve: turning point and public policy, in: Sustainable Resource Use and Economic Dynamics, Springer 17–34.
Alvarez-Herranz A, Balsalobre-Lorente D (2015) Energy regulation in the ekc model with a dampening effect. J Environ Anall Chem 2:1–10
Balsalobre-Lorente D, Shahbaz M, Ponz-Tienda JL, Cantos-Cantos JM (2017) Energy innovation in the environmental Kuznets curve (EKC): a theoretical approach, in: Carbon footprint and the industrial life cycle, Springer, 243–268.
Kasioumi M (2021) The environmental Kuznets curve: recycling and the role of habit formation, Review of. Econ Anal 13:367–387
Bibi F, Jamil M (2021) Testing environment Kuznets curve (EKC) hypothesis in different regions. Environ Sci Pollut Res 28:13581–13594
Dogan E, Inglesi-Lotz R (2020) The impact of economic structure to the environmental Kuznets curve (Ekc) hypothesis: evidence from European countries. Environ Sci Pollut Res 27:12717–12724
Tenaw D, Beyene AD (2021) Environmental sustainability and economic development in Sub-Saharan Africa: a modified EKC hypothesis. Renew Sustain Energy Rev 143:110897
Isik C, Ongan S, Ozdemir D, Ahmad M, Irfan M, Alvarado R, Ongan A (2021) The increases and decreases of the environment Kuznets curve (EKC) for 8 OECD countries. Environ Sci Pollut Res 28:28535–28543
Selden TM, Song D (1995) Neoclassical growth, the j curve for abatement, and the inverted u curve for pollution. J Environ Econ Manag 29:162–168
Casino B et al (2002) J curve for abatement with transboundary pollution. Economics Bulletin 17:1–9
Kasioumi M, Stengos T (2020) The environmental Kuznets curve with recycling: a partially linear semiparametric approach. J Risk Financial Manage 13:274
Di Vita G (2001) Technological change, growth and waste recycling. Energy Econ 23:549–567
K. Pittel (2006) A Kuznets curve for recycling, Technical Report, Economics Working Paper Series, 2006.
Bernard S (2011) Remanufacturing. J Environ Econ Manag 62:337–351
Bonviu F (2014) The European economy: from a linear to a circular economy. Romanian J Eur Aff 14:78
Ragossnig AM, Schneider DR (2019) Circular economy, recycling and end-of-waste
Banionienea J, Dagilienea L, Donadellib M, Grüning P, Uppnerd MJ, Kizyse R, Lessmannf K (2021) The quadrilemma of a small open circular economy through a prism of the 9r strategies
MacArthur E et al (2013) Towards the circular economy. J Ind Ecol 2:23–44
Hartley K, van Santen R, Kirchherr J (2020) Policies for transitioning towards a circular economy: Expectations from the European Union (EU). Resour Conserv Recycl 155:104634
Patwa N, Sivarajah U, Seetharaman A, Sarkar S, Maiti K, Hingorani K (2021) Towards a circular economy: an emerging economies context. J Bus Res 122:725–735
Zink T, Geyer R (2017) Circular economy rebound. J Ind Ecol 21:593–602
Allwood JM (2014) Squaring the circular economy: the role of recycling within a hierarchy of material management strategies, in: Handbook of recycling, Elsevier, 445–477.
Zhou S, Smulders S (2021) Closing the loop in a circular economy: saving resources or suffocating innovations? Eur Econ Rev 139:103857
Ozokcu S, Ozdemir O (2017) Economic growth, energy, and environmental Kuznets curve. Renew Sustain Energy Rev 72:639–647
Pittel K, Amigues JP, Kuhn T (2005) Endogenous growth and recycling: a material balance approach, Economics Working Paper Series 5
Millimet DL, List JA, Stengos T (2003) The environmental Kuznets curve: real progress or misspecified models? Rev Econ Stat 85:1038–1047
Venables AJ (2014) Depletion and development: natural resource supply with endogenous field opening. J Assoc Environ Resour Econ 1:313–336
Acknowledgements
We would like to thank participants of the conference organized by RCEA in Waterloo on the Future of Growth, May 2021.
Author information
Authors and Affiliations
Contributions
Kasioumi carried out the simulations (70% contribution) and Stengos was responsible for organizing the material (30% contribution).
Corresponding author
Ethics declarations
Competing Interests
The authors declare no competing interests.
Appendices
Appendix 1 Plots
A Plots Based on Our Basic Model
In this section of our paper, we will present more plots showing that the relationship between pollution and output (EKC) as well as recycling and output does not change dramatically when we change the weight (\(\gamma\)) at which firm uses the two inputs in production.Footnote 14 In addition, those plots hold under many other combinations of all the parameter values and initial values for our variables, but they are not included to conserve space (Figs. 5, 6, 7, and 8).
B Plots Based on the First Extension of the Basic Model
In that section, we will display some more plots based on the extension of our basic model (Section “8”), using different values for the wight (\(\gamma\)) that the firm uses. As before, the plots do not change in a high degree and they still hold under many different combinations of all the other parameter values as well as initial values for our main variables (Figs. 9, 10, 11, and 12).
Appendix 2 Extension: The Circular Economy Model with Technological Progress as the Effect of the Polluting Input Changes over Time
An interesting question that we should look into more detail is the importance of the effect that the polluting input has on this economy. Specifically, we want to investigate if a usage reduction of this input in time will change our results. In that case, we assume that there is consumer pressure to the firm for a greener economy, so the firm decides to use less amount of this input in the production process. In that way, the firm will be transformed into a greener firm leading to lower pollution levels coming not only from production but also from the waste stemming from production, satisfying consumer’s preferences in a higher degree.
Under those assumptions, the economy can end up following two totally different paths. In the first one, recycling might fall as less polluting input is used and less pollution units are created, confusing consumers’ who might create false beliefs about the environmental quality and start recycle less. On the other hand, the second scenario is the complete opposite of the previous one. In that one, people will still want to have an as clean as possible environment and continue recycling no matter what the firm decides to do. The difference between those two scenarios is that the first one assumes consumers who care about the environmental quality up to a specific degree and mainly for the current pollution, while the second one assumes consumers who care about the current and future environmental quality. In our model, we do not make any further assumptions about the consumers and we allow the model to reveal which scenario will be the dominant one under the assumptions made on Sections “6” and “8”
To examine whether recycling motives change or not under this economy, we assume that firms decide to constantly use less amount of the polluting input. For that reason, we introduce a new variable \(\alpha\) which will represent the effect of the polluting input, and it will be reduced in time. So, the effect of this input is given by the following formula for which holds:
where \({\alpha }_{0}\) is the initial value of the effect and \(l\) shows the rate at which the effect of the polluting input changes in time.
In that case, the new amount of the polluting input is equal to \({\alpha }_{t}z\) instead of \(z\) that was previously leading to changes of some functions. Specifically, the production function, the waste accumulation path, and the pollution accumulation path have to change because of the addition of the dynamic effect of the polluting input, while the utility function and the instantaneous utility function will remain the same. Hence, the functions we are using to solve this problem are the following:
where A stands for \({A}_{t}={A}_{0}{e}^{(\eta t)}\) and \(\alpha\) stands for \({\alpha }_{t}={\alpha }_{0}{e}^{(-lt)}\) and they are the technological progress and the dynamic effect of the polluting resource respectively.
Once again, we have to maximize the social welfare function (Eq. 26) subject to the two constraints that we have: the pollution accumulation path (Eq. 29) and the waste accumulation path (Eq. 30), both of which differ compared to the previous models we discussed. To solve this problem, we will follow similar steps as in the initial model and we will also use the following Hamiltonian function:
where \(\lambda\) is the shadow price of the waste accumulation path and \(\mu\) is the shadow price of the pollution accumulation path. For the above problem, we assume again that \(c\) and \(z\) are the control variables while \(P\) and \(S\) are the state variables. Under these assumptions, the Euler equation for consumption and the optimal path of the polluting input can be seen in the following two equations respectively:
As we can see, these two functions are similar to the two functions we obtained in Section “Extension: the Circular Economy Model with Technological Progress” in the extension of the initial model. First of all, we see that the Euler function for consumption does not change at all since it does not include the effect of the polluting resource. However, it is affected by some indirect effects coming from the substitution of the derivatives of the production function. On the other hand, the optimal path of the polluting input has a similar function as in the extension model one (Eq. 24), with some differences stemming from the introduction of the polluting input’s effect.
The solution of the system consisting of Eqs. 29, 30, 32, and 33 can be seen in the following plots.Footnote 15 The way of construction of the following plots is similar to the previous two cases: the system of differential equations allows us to calculate directly the numerical values of consumption, pollution, waste, and polluting input which then allow us to calculate recycling and output level over time.
The relationship between pollution and output (EKC) (Fig. 13) is given by an inverse-U curve, while the relationship between recycling and output (Fig. 14) is still an increasing curve.Footnote 16 In both plots, we obtain similar curves as in the plots we had earlier, offering robustness to our previous results. We see that no matter how many variables we add or make them change in time, the plots we are getting are similar to our initial findings, supporting the existing literature as well. As we can see, as economy grows pollution falls and recycling increases, showing that the consumers decide to recycle even under the case that the firm does not pollute the environment in a high degree, which means that the second scenario discussed earlier comes true.
Appendix 3 Parameter Values
In this section, we will provide some more information about the values of the parameters used on all models discussed on this paper. The following table (Table 1) presents the values of the parameters we used to generate the plots of our initial model described in Section “The Circular Economy Model,” while Tables 2 and 3 present the parameter values of the extension models 1 and 2 described in Sections “8” and “9” respectively.Footnote 17 Even though we chose the following specific values, our results are robust to many other combinations of the parameters values and initial values for our variables.
Unfortunately, we are not able to double check if the values we chose for the parameters are consistent with the theory, since the theoretical literature on that topic is quite thin. However, we believe that this is not a problem and it does not reduce the significance of our results since we are able to get similar plots under many other combinations of the parameter values.
Rights and permissions
About this article
Cite this article
Kasioumi, M., Stengos, T. A Circular Model of Economic Growth and Waste Recycling. Circ.Econ.Sust. 3, 321–346 (2023). https://doi.org/10.1007/s43615-022-00177-7
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s43615-022-00177-7