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A Circular Economy Model of Economic Growth with Circular and Cumulative Causation and Trade

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Abstract

The idea of a circular economy, first discussed by Kenneth Boulding in the 1960s and ‘70 s and reintroduced by environmental economists David Pearce and R. Kerry Turner in 1990, is a characterization of how goods and services can be produced and consumed in an ecologically sound and environmentally sustainable manner that meets concerns of overuse of resources, waste management, and climate change, inter alia, through the conscious interlinking of disparate economic activities. The notion of circular and cumulative causation (CCC), through which certain positive and negative effects are promoted and reinforced by positive feedbacks, also is not new. George et al. (2015) have presented a theoretical circular economy model of economic growth that leads them to infer that the maintenance or improvement of environmental quality is incompatible with economic growth. However, Donaghy (2021b) has demonstrated how, when sources of CCC are introduced to the model of George et al., a different conclusion may be reached; CCC may be harnessed to bring about desirable systems properties, such as those of a circular market economy. The present paper reviews the arguments and findings of the latter two studies and extends the analysis by introducing trade between three national or regional economies in an environmentally polluting resource, other materials, and recycling technologies. Results of numerical simulation exercises suggest that there could be gains from trade in terms of progress by multiple economies in aggregate towards an international or interregional circular growth economy. The paper also suggests how aspects of the Pearce and Turner model of a circular economy not presently included in theoretical circular economy models of economic growth (closed or open) can be accommodated.

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Fig. 3

(Source: Donaghy (2021b))

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Data Availability Statement

Data sharing not applicable to this article as no datasets were generated or analyzed during the current study.

Notes

  1. The concept of a ‘circular economy’ discussed in this paper, which is rooted in industrial ecology, differs from conceptions of economies as circular flows of resources, investments, manufactured goods, services, and payments in that the former places greater emphasis on flows of materials and energy than the latter. However, one of this paper’s referees is quite correct in pointing out that the concept of a production system as a circular flow is much older than the literature on ‘circular economy’ as here construed and can be traced back at least as far as the network-based approach to characterizing an economy in Leontief’s 1928 paper (Leontief 1928 [1991]). For an exemplary graphical depiction of circular flows in the economy of Nova Scotia in 1965, see Czamanski (1973, p.31).

  2. According to the second law of thermodynamics, as resources are extracted from clean ores and circulated through the economy, their entropy—the degradation of matter and energy—increases.

  3. Ulanowicz et al. (2009) may be helpful in modeling this network resilience. Marchese et al. (2018) discuss how notions of resilience and sustainability have been interpreted in various literatures. In this paper we interpret resilience in terms of the ability of a system to return to operability and sustainability in terms of securing for future generations the same level of welfare as generations now living.

  4. One of this paper’s referees has suggested that the functional network structure Fig. 1 depicts is an architecture of complexity and connectivity and that it would be fruitful to examine how interventions at different junctures in this functional network would affect connectivity and hence complex systems performance. (See Sec. 6 on future research, below, for further discussion.).

  5. In a more recent article, Reike et al. (2018) extend the number of R’s associated with circular economies to ten.

  6. Odum and Odum (2007) suggest that circular economies should manifest a cyclical pulsing pattern with orderly descent and decession followed by growth and succession.

  7. Note that, given the level of theoretical abstraction of their model, the activity of reuse does not feature in their analysis. George et al. contrast their modeling exercise with that of Brock and Taylor (2010), which focuses on technical progress in pollution abatement and establishes the ‘environmental Kuznets curve’ (EKC) as a necessary by-product of convergence to a sustainable growth path. The EKC is an inverted U-shaped curve relating the growth and then decline in environmental pollution as a nation’s income per capita increases. (See Stern 2004).

  8. Emergent behavior of a system would seem to be the most critical signature of complexity for Casti (1997).

  9. See the essays collected in Berger (2009) for a thorough discussion of many aspects of circular and cumulative causation.

  10. The ‘Keynes-Ramsey Rule’ asserts that consumption will be increasing or decreasing over time according to whether the rate of interest (or rate of return on an asset) is greater or less than the rate of time preference (Turnovsky 1997, p. 23).

  11. This model, as well as that of George et al., may be viewed as steps taken toward a network-based analysis of the relationship between circularity and growth.

  12. Note that Q is aggregate output, not GDP, and that costs of investment and capital adjustment are assumed to be quadratic. Rewriting (14) with Q as the dependent variable gives an expression with components of GDP, material inputs, and residual waste on the RHS.

  13. At this stage of our argument, three important observations of one of this paper’s referees must be acknowledged. The first is that both decreasing and increasing returns to scale can arise from the production and use of residuals, such as waste in this model. (See Quadrio Curzio 1986.) We have hedged against the former result occurring by our selection of functional forms, parameters, and initial values of variables. The second observation is that, as von Neumann (1935–37) has argued, because there are inherent limits to growth in any embodied technology, IRS and technical progress may facilitate getting beyond particular growth constraints but may require activation of specific feedback relationships between activities in a production network to be effective. Lastly, and as Cardinale (2019) has argued, different production networks may present different impediments to or opportunities for achieving sustainable development and so may require different policy interventions or structural changes.

  14. The model was simulated—the social planner’s optimal control problem was solved—over a period of 35 years using the program APREDIC in the WYSEA software package of Wymer (2012). A ceiling on the use of the polluting resource was imposed beyond year 25 to be the value at year 25, to represent a target limit set by policy to reduce use of the resources, and investments in physical and human capital were bounded from below at 3% and 5%, respectively to induce human capital deepening. (Given the macro level of economic activity modeled, the third R of circular economy, reuse, is not represented.).

  15. George et al. suggest as a next step studying trade in resources and recycling technologies between countries with developing and developed economies. In such a study, there would be two countries, A and B. “Country A is a resource-abundant country and Country B is a high-tech country which develops the recycling technology. An international circular economy can come into existence as long as both countries reuse and recycle more waste for production and consumption [than accumulates] (George et al. 2015, p.63).”.

  16. This assumption enables us to distinguish between a high-tech orientation and resource-based orientation to growth in the simulations to follow.

  17. Once again, note that Q is aggregate output, not GDP, and that costs of investment and capital adjustment are assumed to be quadratic. Moreover, other materials, \({OM}_{i}\), are now included in the balance equation, since they are (potentially) a traded commodity.

  18. It should be noted that the overall increase in waste stocks in the simulation with trade relative to the simulation without is an artifact of the specification of the waste equation of each economy. Because it is a balance equation, as costs of inputs are lowered the rate of growth in waste increases. Simulations with the present model suggest that, while it may be possible to reduce pollution with economic growth, waste handling remains a problem.

  19. Pindyck (1978) distinguishes between ‘exhaustible’ resources and ‘nonrenewable’ resources. Whereas the latter do not exhibit growth or regeneration, new reserves of exhaustible resources can be acquired through exploratory effort and regeneration. (See Conrad and Clark 1987).

  20. Donaghy and Wymer (2011) demonstrate how Pindyck’s (1978) nonlinear model of intertemporal optimization can be estimated with data on oil exploration and extraction in Nigeria by continuous-time econometric methods, hence can be embedded in an empirical macroeconomic growth model.

  21. In their article summarizing divergent perspectives on options for value retention and the most common views of a 10R typology—which extends the 3R typology discussed above—Reike et al. (2018) conclude that “policymakers and businesses should focus their efforts on realization of the more desirable, shorter loop retention options, like remanufacturing, refurbishing and repurposing – yet with a view on feasibility and overall system effects. Scholars, on the other hand, should assist the parties contributing to an increased circular economy in practice by taking up a more active role in attaining consensus in conceptualizing the circular economy (p. 246).”.

  22. The optimization problem of the social planner, in terms of a current-value Hamiltonian, is set up differently from that of George et al. for this modeling variant to increase ease of algebraic manipulation.

  23. The discount factor \({e}^{-\rho t}\) in the optimality and first-order necessary conditions has been eliminated in (4.8)–(4.16) through cancelation where universally instantiated.

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Appendices

Appendix A

The current-value Hamiltonian for the social planner’s optimal control problem posed in Donaghy (2021b) can be written as followsFootnote 23:

$$H={e}^{-\rho t}\frac{1}{\gamma }{\left(\omega c\cdot {P}^{-\eta }\right)}^{\gamma }+ \lambda {e}^{-\rho t}[Q-c-\alpha z{-I}_{k}(1+\frac{{a}_{1{I}_{k}}}{2K}){-I}_{h}(1+\frac{{a}_{2{I}_{h}}}{2HC}) -\beta S-\dot{S}]$$
$$+\mu_1e^{-\rho t}\left[\vartheta z-\delta P+\left(1-\beta\right)S-\dot P\right]+\mu_2e^{-\rho t}\lbrack\beta S-\dot R\rbrack+q_1e^{-\rho t}\left(I_k-\dot K\right)+q_2e^{-\rho t}\left(I_h-\dot{HC}\right).$$
(31)

The zero-order optimality conditions for the control variables, costate equations, and transversality conditions can be obtained in a manner similar to that presented for the model of George et al.Footnote 24

$${H}_{c}={(\omega c\cdot {P}^{-\eta })}^{\gamma -1}{P}^{-\eta }-\lambda =0.$$
(32)
$${H}_{z}=\lambda \left(\kappa {\theta }_{2}{Q}^{\frac{\sigma +\kappa }{\kappa }}{z}^{-\left(1+\sigma \right)}-\alpha \right)+{\mu }_{1}\vartheta =0$$
(33)
$${H}_{{I}_{K}}=-\lambda \left(1+{a}_{1}\frac{{I}_{K}}{K}\right)+{q}_{1}=0.$$
(34)
$${H}_{{I}_{HC}}=-\lambda \left(1+{a}_{2}\frac{{I}_{HC}}{HC}\right)+{q}_{2}=0.$$
(35)
$${H}_{S}=-\dot{\lambda }+\rho \lambda =\lambda \left({Q}_{S}-\beta \right)+{\mu }_{1}\left(1-\beta \right)+{\mu }_{2}\beta ,$$
(36)

where \({Q}_{S}=\kappa {\theta }_{1}{Q}^{\frac{\sigma +\kappa }{\kappa }}{(\beta S)}^{-(1+\sigma )}.\) 

$${H}_{R}=-\dot{{\mu }_{2}}+ \rho {\mu }_{2}=\lambda {Q}_{R}-{\mu }_{1}{\beta }_{R}S+{\mu }_{2}{\beta }_{R}S,$$
(37)

where

\({Q}_{K}=\kappa {\theta }_{3}{Q}^{\frac{\sigma +\kappa }{\kappa }}{K}^{-(1+\sigma )}\), and \({\vartheta }_{K}=\epsilon \chi {HC}^{\epsilon }{K}^{-\epsilon -1}\).

$$H_K=-\dot{{q}}+\rho{q}_{1}= \lambda \left({Q}_{K}+\frac{{a}_{1}{I}_{HC}^{2}}{2{HC}^{2}}\right)+{\mu }_{1}{\vartheta }_{K},$$
(38)
$${H}_{HC}=-\dot{{q}_{2}}+\rho {q}_{2}=\lambda \left({Q}_{HC}+\frac{{a}_{2}{I}_{HC}^{2}}{2{HC}^{2}}\right)+{\mu }_{1}{\vartheta }_{HC}.$$
(39)

where

\({Q}_{HC}= \kappa {\theta }_{4}{Q}^{\frac{\sigma +\kappa }{\kappa }}{HC}^{-(1+\sigma )}\) and \({\vartheta }_{HC}=-\epsilon \chi {HC}^{\epsilon -1}{K}^{-\epsilon }\)

$$\underset{t\to \infty }{\mathrm{lim}}\lambda S{e}^{-\rho t}=0, \underset{t\to \infty }{\mathrm{lim}}{\mu }_{1}P{e}^{-\rho t}=0, \underset{t\to \infty }{\mathrm{lim}}{\mu }_{2}R{e}^{-\rho t}=0,$$
$$\underset{t\to \infty }{\mathrm{lim}}{q}_{1}K{e}^{-\rho t}=0, \underset{t\to \infty }{\mathrm{lim}}{q}_{2}HC{e}^{-\rho t}=0.$$
(40)

Manipulation of these equations yield expressions for the rates of change in c and z that are homologous to Eqs. (11) and (12) in the model of George et al. (2015) considered in Sect. 3.

To conduct a deterministic dynamic simulation with the model of Donaghy (2021b), the optimality conditions and co-state equations were manipulated to obtain a mathematically equivalent set of conditions that are strictly in terms of ‘observable quantities’ and easier to solve numerically. (Essentially, information in the first-order necessary conditions for an optimal control solution was used to substitute for co-state variables with expressions in terms of state and control variables while ensuring that all necessary feedbacks were retained.) The simulated model comprises.

  1. 1)

    Eqs. (15) and (16) as previously defined,

  2. 2)

    the following modifications of Eqs. (14), (17) and (18):

    $$\dot{S}=Q-c-\alpha z-k\bullet K\left(1+\frac{{a}_{1}k\cdot K}{2K}\right)- h\cdot HC\left(1+\frac{{a}_{2}h\cdot HC}{2HC}\right) -\beta S,$$
    (41)
    $$\dot{K}=k\cdot K,$$
    (42)

where \(k\equiv \frac{\dot{K}}{K},\)

$$\dot{HC}=h\cdot HC,$$
(43)

where \(h\equiv \dot{\frac{HC}{HC},}\)

  1. 3)

    two new second-order equations, defining rates of change in the rates of physical and human capital formation:where.

    $$\dot k=\left(\frac1{a_1}+k\right)\left(\rho+\frac{\acute{\lambda }}{\lambda }\right)-\frac{Q_K}{a_1}-0.5k^2-\frac{\mu_1}\lambda\vartheta_Kz,$$
    (44)
    $$\dot{h}=\left(\frac{1}{{a}_{2}}+h\right)\left(\rho +\frac{\acute{\lambda }}{\lambda }\right)-\frac{{Q}_{HC}}{{a}_{2}}-0.5{h}^{2}-\frac{{\mu }_{1}}{\lambda }{\vartheta }_{HC}z,$$
    (45)

\(\lambda \equiv {U}_{c}={\left(\omega c\cdot {P}^{-\eta }\right)}^{\gamma -1}{P}^{-\eta }, \frac{\dot{\lambda }}{\lambda }=\frac{{U}_{cc}\cdot \dot{c}}{{U}_{c}},{U}_{cc}=(\gamma -1){(\omega c\cdot {P}^{-\eta })}^{\gamma -2}{P}^{-2\eta }\), and \({\mu }_{1}=\frac{\lambda \left(\alpha -{Q}_{z}\right)}{\vartheta },\) and \({Q}_{z}=\kappa {\theta }_{2}{Q}^{(\sigma +\kappa )/\kappa }{z}^{-(1+\sigma )}\).

  1. 4)

    two new first-order equations, defining the rates of change in consumption and use of the polluting resource:

    $$\dot{c}=\frac{\eta \gamma \left(\vartheta z-\delta P+\left(1-\beta \right)S\right)c}{P\left(\gamma -1-\frac{{U}_{cc}}{{U}_{c}}\right)},$$
    (46)
    $$\dot{z}=(\frac{\dot{{\mu }_{1}}}{{\mu }_{1}}-\frac{\dot{\lambda }}{\lambda })\left(\frac{{Q}_{z}-\alpha }{{Q}_{zz}}\right),$$
    (47)

where \(\frac{\dot{{\mu }_{1}}}{{\mu }_{1}}=\rho +\delta -\eta {U}_{P}\vartheta /({U}_{c}\left({Q}_{z}-\alpha \right))\), \({U}_{P}=-\eta {\left(\omega c\cdot {P}^{-\eta }\right)}^{\gamma -1}c\cdot {P}^{-\eta -1},\) and \({Q}_{zz}=\left(\sigma +\kappa \right){\theta }_{2}{Q}^{\frac{\sigma }{\kappa }}{z}^{-\left(1+\sigma \right)}-\frac{\left(1+\sigma \right){Q}_{z}}{z},\) and.

  1. 5)

    the transversality conditions (40)

The modifications of Eqs. (14), (17) and (18) resulting in (4143) just entail redefinition of variables.

To derive the second-order equation (44), divide (34) and (37) each by \(\uplambda\) to obtain

$$-\left(1+{a}_{1}\frac{{I}_{K}}{K}\right)+{q}_{1}/\lambda =0,$$
(48)

and

$$-\dot{\frac{{q}_{1}}{\lambda }}+\frac{\rho {q}_{1}}{\lambda }=\left({Q}_{K}+\frac{{a}_{1}{I}_{K}^{2}}{2{K}^{2}}\right)+\left(\frac{{\mu }_{1}}{\lambda }\right){\vartheta }_{K}.$$
(49)

Then, defining k \(\equiv\) IK/K and q1\(\equiv\) q1/\(\lambda\), note that \(\dot{{q}_{1}{^{\prime}}}=\dot{({q}_{1}/\lambda )}=\frac{{\dot{q}}_{1}\lambda -{q}_{1}\dot{\lambda }}{{\lambda }^{2}}=\frac{\dot{{q}_{1}}}{\lambda }-\frac{{q}_{1}}{\lambda }\frac{\dot{\lambda }}{\lambda }=\dot{{q}_{1}}/\lambda -{q}_{1}^{^{\prime}}\frac{\dot{\lambda }}{\lambda }.\).

So \(-\dot{{q}_{1}}/\lambda =-\dot{{q}_{1}^{^{\prime}}}+{q}_{1}^{^{\prime}}\frac{\dot{\lambda }}{\lambda }.\) Upon making substitutions for equivalent expressions in (37), we obtain

$$-\dot{{q}_{1}^{^{\prime}}}+{q}_{1}^{^{\prime}}\frac{\dot{\lambda }}{\lambda }+\rho {q}_{1}^{^{\prime}}={Q}_{K}+{a}_{1}{k}^{2}+\left(\frac{{\mu }_{1}}{\lambda }\right){\vartheta }_{K}.$$
(50)

Now differentiating (48) completely with respect to time and substituting into (50) \(\left(1+{a}_{1}k\right)\) for \({q}_{1}^{^{\prime}}\) and \(-{a}_{1}\dot{k}\) for \(-\dot{{q}_{1}^{^{\prime}}}\) we obtain

$$-{a}_{1}\dot{k}+\left(\rho +\frac{\dot{\lambda }}{\lambda }\right)\left(1+{a}_{1}k\right)= {Q}_{K}+{a}_{1}{k}^{2}+\left(\frac{{\mu }_{1}}{\lambda }\right){\vartheta }_{K},$$
(51)

Which, upon rearranging, gives (44). 45) can be obtained by proceeding similarly.

To derive equation (46), first differentiate zero-order condition (32) totally with respect to time to get, upon cancellation of terms,

$$\frac{\left(\gamma -1\right)\dot{c}}{c}-\frac{\gamma \eta \dot{p}}{p}=\frac{\dot{\lambda }}{\lambda }.$$
(52)

Isolating \(\dot{c}\) yields

$$\dot{c}=\frac{1}{(\gamma -1)}\left(\frac{\dot{\lambda }}{\lambda }+\gamma \eta \frac{\dot{P}}{P}\right)c.$$
(53)

Substituting \(\frac{{U}_{cc\bullet }\dot{c}}{{U}_{c}}\) for \(\frac{\dot{\lambda }}{\lambda }\) and isolating \(\dot{c}\) once again yields

$$\dot{c}=\frac{\frac{\gamma \eta \dot{p}}{p}}{\left(1-\frac{{U}_{cc\bullet }c}{{U}_{c}\left(\gamma -1\right)}\right)},$$
(54)

where \(\dot{p}\) is defined by (15).

To derive equation (47), rewrite (33) as

$${H}_{z}=\lambda \left({Q}_{z}-\alpha \right)+{\mu }_{1}\vartheta =0.$$
(55)

Isolate \({\mu }_{1}\) to obtain

$${\mu }_{1}=\frac{\lambda \left(\alpha -{Q}_{z}\right)}{\vartheta }.$$
(56)

Differentiate the resulting expression totally with respect to time to obtain

$$\dot{{\mu }_{1}}=\frac{\dot{\lambda }\left(\alpha -{Q}_{z}\right)}{\vartheta }+\frac{\lambda \left(-{Q}_{zz}\cdot \dot{z}\right)}{\vartheta }.$$
(57)

Dividing (57) by (56) yields

$$\frac{\dot{{\mu }_{1}}}{{\mu }_{1}}=\frac{\dot{\lambda }}{\lambda }+\frac{\left(-{Q}_{zz}\cdot\dot{z}\right)}{\left(\alpha -{Q}_{z}\right)}.$$
(58)

Isolating \(\dot{z}\) in this expression yields (47).

Similar algebraic manipulations were performed to solve the model in the simulations discussed in Sect. 5 of this paper.

Appendix B

The current-value Hamiltonian for the problem faced by the social planner in each of the three countries, i = A, B, and C, in the absence of trade can be written as follows:

$$H_i=e^{-\rho t}\frac1\gamma\left(\omega c_i\cdot P_i^{-\eta}\right)^\gamma+\lambda_ie^{-\rho t}\left[Q_i-c_i-\alpha_{zi}z{-\alpha_{OMi}{MO}_i-I}_{ki}\left(1+\frac{a_{1I_{ki}}}{2K_i}\right)-\overline{h_i}{HC}_i\left(1+0.5a_2\overline{h_i}\right)-\beta S_i-\dot{S_i}\right]+\mu_{1i}e^{-\rho t}\left[\vartheta_iz_i-\delta P_i+\left(1-\beta_i\right)S_i-\dot{P_i}\right]+\mu_{2i}e^{-\rho t}\left[\beta_iS_i-\dot{R_i}\right]$$
$$+{q}_{i}{e}^{-\rho t}\left[{I}_{ki}-\dot{{K}_{i}}\right].$$
(59)

The zero-order optimality conditions for the control variables, the costate equations, and transversality conditions can be obtained by appropriate differentiation of (5.7) as follows.

$${H}_{ci}={(\omega {c}_{i}\cdot {{P}_{i}}^{-\eta })}^{\gamma -1}{{P}_{i}}^{-\eta }-{\lambda }_{i}=0.$$
(60)
$${H}_{zi}={\lambda }_{i}\left(\kappa {\theta }_{2}{{Q}_{i}}^{\frac{\sigma +\kappa }{\kappa }}{{z}_{i}}^{-\left(1+\sigma \right)}-\alpha \right)+{\mu }_{1}{\vartheta }_{i}=0.$$
(61)
$${H}_{{I}_{Ki}}=-{\lambda }_{i}\left(1+{a}_{1}\frac{{I}_{Ki}}{{K}_{i}}\right)+{q}_{1i}=0.$$
(62)
$${H}_{Si}=-\dot{{\lambda }_{i}}+\rho {\lambda }_{i}={\lambda }_{i}\left({Q}_{Si}-{\beta }_{i}\right)+{\mu }_{1}\left(1-{\beta }_{i}\right)+{\mu }_{2}{\beta }_{i},$$
(63)

where

$${Q}_{Si}=\kappa {\theta }_{1}{{Q}_{i}}^{\frac{\sigma +\kappa }{\kappa }}{({\beta }_{i}{S}_{i})}^{-(1+\sigma )}.$$
$${H}_{Pi}=-\dot{{\mu }_{1i}}+\rho {\mu }_{1i}=-\eta {\left(\omega {c}_{i}\cdot {{P}_{i}}^{-\eta }\right)}^{\gamma -1}{c}_{i}\cdot {P}^{-\eta -1}-{\mu }_{1i}.$$
(64)
$${H}_{Ri}=-\dot{{\mu }_{2i}}+ \rho {\mu }_{2i}=\lambda {Q}_{Ri}-{\mu }_{1}{\beta }_{Ri}{S}_{i}+{\mu }_{2}{\beta }_{Ri}{S}_{i},$$
(65)

where

\({Q}_{Ri}=\frac{\kappa {\theta }_{1}{Q}^{\frac{\sigma +\kappa }{\kappa }}{\left({\beta }_{i}{S}_{i}\right)}^{-\left(1+\sigma \right)}{{\beta }_{i}}^{2}\phi {S}_{i}}{{{R}_{i}}^{2}},\) and \({\beta }_{Ri}=\frac{{{\beta }_{i}}^{2}\phi }{{{R}_{i}}^{2}}\).

$${H}_{Ki}= -\dot{{q}_{1i}}+\rho {q}_{1i}=\lambda \left({Q}_{Ki}+\frac{{a}_{1}{I}_{Ki}^{2}}{2{{K}_{i}}^{2}}\right)+{\mu }_{1i}{\vartheta }_{Ki},$$
(66)

where

\({Q}_{Ki}=\kappa {\theta }_{3}{{Q}_{i}}^{\frac{\sigma +\kappa }{\kappa }}{{K}_{i}}^{-(1+\sigma )},\) and \({\vartheta }_{Ki}=\epsilon \chi {{HC}_{i}}^{\epsilon }{{K}_{i}}^{-\epsilon -1}\).

$$\underset{t\to \infty }{\mathrm{lim}}{\lambda }_{i}{S}_{i}{e}^{-\rho t}=0, \underset{t\to \infty }{\mathrm{lim}}{\mu }_{1}{P}_{i}{e}^{-\rho t}=0, \underset{t\to \infty }{\mathrm{lim}}{\mu }_{2}{R}_{i}{e}^{-\rho t}=0, \underset{t\to \infty }{\mathrm{lim}}{q}_{1i}{K}_{i}{e}^{-\rho t}=0.$$
(67)

In the second simulation in which there is trade between the three economies, the zero-order optimality condition for the polluting resource, (B.3) is modified for economies A, and C as follows:

$${H}_{zi}={\lambda }_{i}\left(\kappa {\theta }_{2}{{Q}_{i}}^{\frac{\sigma +\kappa }{\kappa }}{{z}_{i}}^{-\left(1+\sigma \right)}-{\alpha }_{zi}\right)+{\mu }_{1}\left({\vartheta }_{i}+{\boldsymbol{\varphi }}_{{\varvec{z}}{\varvec{i}}}\right)=0, i=\mathrm{A\; and\; C}.$$
(68)

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Donaghy, K.P. A Circular Economy Model of Economic Growth with Circular and Cumulative Causation and Trade. Netw Spat Econ 22, 461–488 (2022). https://doi.org/10.1007/s11067-022-09559-8

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