# Optimal Operational Decision Making of Manufacturers and Authorized Remanufacturers with Patent Licensing under Carbon Cap-and-Trade Regulations

Authors: Biyu Liu; Zhongsheng Hua; Qinhong Zhang; Haidong Yang; Athanasios Migdalas
Journal: Complexity
 (2020)

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## Abstract

Constrained by production capacity and the pressure to reduce emissions, many original equipment manufacturers (OEMs) authorize third-party remanufacturers (TPRs) to remanufacture patented products. We investigate the operational decisions of OEMs and authorized TPRs under carbon cap-and-trade regulations in a two-echelon supply chain. We first formulate an operational decision model for OEMs before a TPR enters. Then, for the cases of centralized and decentralized decision making, we formulate an operational decision-making model for the TPR and, subsequently, establish one for the OEM after the TPR enters. We further analyze the effects of carbon emissions cap, trading price of carbon permits, yield rate, and consumer willingness to pay (WTP) on optimal decisions. Our results indicate: whether TPRs accept authorization remanufacturing depending on the ratio of carbon emissions cap to carbon emissions for producing per remanufactured product; royalty rate is negatively affected by trading price of carbon permits and per remanufactured product’ carbon emissions other than that for per new product, and can offset the threat caused by TPRs; the implementation of carbon cap-and-trade regulations causes OEMs to charge TPRs lower royalty rate; centralized decision making increases the total profit of the supply chain and delivers superior environmental benefits. As yield rate and WTP increase, the total profit increases, increasingly sensitive to WTP.


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## Body

## 1. Introduction

Environmental pollution has received significant attention in the past few decades and many countries have implemented various carbon emission regulations, such as carbon cap-and-trade, carbon emission taxes, and carbon offsets, to reduce carbon emissions [1]. According to data gathered for the Product Carbon Footprint (PCF) pilot project in Germany, production in manufacturing industry generates inordinate amounts of carbon emissions [2].Remanufacturing has been conceived as a significant strategy to achieve energy conservation and emissions reduction [3, 4]. According to Jiang et al. [5], remanufacturing can decrease air pollutants by over 80% compared to manufacturing. Similarly, Smith and Keoleian [6] signify that, in the United States, remanufacturing of automobile engines decreases energy consumption by 68%–83% and reduces carbon emissions by 73%–87%. The importance of remanufacturing is further evident in the large number of end-of-life (EOL) vehicles, which will presumably exceed 100 million by 2020 [7].The large volume of used products, however, poses a great challenge to OEMs’ capacity; with the result that OEMs typically authorize third-party remanufacturers (TPRs), we also call it as authorized remanufacturers to undertake remanufacturing activities and resell the remanufactured products without involving the OEMs [8]. In recent years, such practices have developed in some countries [9]. For example, in 2010, China’s National Development and Reform Commission (CNDRC) announced that the Chinese government focused specifically on developing the remanufacturing industry (China Remanufacturing, 2015). By 2013, CNDRC approved 28 remanufacturers, a majority of them being TPRs, who were operating as authorized remanufacturers (National Development and Reform Commission, 2015). In particular, Apple signed an agreement with Foxconn in 2015, under which Foxconn was authorized to remanufacture EOL iPhones and resell them in Chinese market [10].Although authorized remanufacturing can greatly reduce carbon emissions, it also inevitably results in a competition threat to OEMs (e.g., [11]). OEMs must balance the goal of emissions reduction and the problem of demand competition caused by authorized remanufacturing under carbon emission regulations. Furthermore, TPRs must clarify the effects of regulations on their decisions and respond to remanufacturing authorization with optimal decision making. Thus, we address the following problems: what is the condition that TPRs accept authorization? What is the optimal royalty rate that OEMs charge TPRs to satisfy both parties? How do carbon emission regulations affect the optimal decisions of OEMs and TPRs? Should OEMs decrease the production quantity and sales price after TPRs enter? Would their profit level be significantly affected with the constraint of carbon emission regulations? To the best of our knowledge, few studies have addressed these issues. Given that more than 20 countries and regions globally have adopted cap-and-trade regulations [12], we examine the optimal operational decisions of OEMs and TPRs under this regulation. In particular, we first propose an optimal production and pricing decision-making model to address an OEM’s decision problem before a TPR enters. Then, for the cases of centralized and decentralized decision making, we formulate an operational decision-making model for the TPR and, subsequently, establish one for the OEM after the TPR enters. We also compare the differences between these decision-making approaches. Finally, we investigate how the optimal decisions for the OEM and TPR change with respect to the carbon emission cap, the trading price of carbon permits, yield rate, and the consumer willingness to pay (WTP).The remainder of this paper is organized as follows. Section2 reviews the associated literature. Section 3 describes the problem, and in Section 4, we formulate the aforementioned models to derive the optimal decisions for OEMs and TPRs under carbon cap-and-trade regulations. Section 5 discusses the results and presents a sensitivity analysis with numerical examples. We conclude our study and propose future research in Section 6. All proofs are provided in the Appendix.


## 2. Literature Review

Our study covers three important streams in the literature: demand competition between new and remanufactured products, authorized remanufacturing, and operational decision making of OEMs and TPRs under carbon emission regulations.Demand competition in new and remanufactured products has been investigated extensively. Some scholars studied the competition from the perspective of OEMs [13, 14]. Some scholars extend this case to consider both OEMs and TPRs. They investigated the competition in production quantity, service, and price (e.g., [3, 8, 15, 16]). Several papers also researched the competition between OEMs and TPRs but in different settings. For example, Mitra and Webster [17] formulated a two-period model to explore government subsidies’ effect on remanufacturing when an OEM competes with a TPR. Wu [18] studied the competition between OEMs and TPRs in recycling and sales markets by building a closed-loop supply chain (CLSC) model. Zhu et al. [19] considered a duopoly with competition in the sales of new products in trade-ins markets within a two-period planning horizon. Hong et al. [20] discussed the quantity competition between an OEM and a TPR with technology licensing in the reverse channel of a CLSC. Ho et al. [21, 22] investigated the effects of green consumers’ purchase behaviors on demand and price by contemplating both internal and external competition. Zhou and Gupta [23] studied the life cycle pricing strategies based on the different generations of new and remanufactured products. Some scholars introduced warranty policy as a competition to remanufactured products. For example, based on this policy, Liao [24] proposed a newsvendor model to capture the remanufacturing system’s features. Liu et al. [25] identified the conditions of the optimal pricing and production strategies on new and remanufactured products considering a nonrenewing free replacement warranty. Sun et al. [26] analyzed the differentiation competition between OEM and TPR owning to customers’ different sensitive points on new and remanufactured products. These studies, however, do not provide a comprehensive discussion with regard to such competition in light of the effects of carbon emission regulations.Compared to competition in remanufacturing, authorized remanufacturing has received less attention in the literature. As regards the difference between outsourcing and authorized remanufacturing, Zou et al. [10] compared the two by formulating a game model between an OEM and a TPR and signified that TPRs prefer the authorization approach when consumers perceive remanufactured products with less value. Zhang et al. [27] and Zhang et al. [28] investigated the strategy implications of authorization between two firms in a differentiated Stackelberg framework when the innovator faces uncertain research and development outcomes. Other studies have explored ways in which the OEMs charge royalty fees for authorized remanufacturing. Hashiguchi [29] proposed that TPRs purchasing licenses from OEMs are immune from allegations of patent infringement. In most authorized remanufacturing operations, OEMs charge TPRs royalty fees. Abdulrahman et al. [4] suggested that OEMs should charge TPRs more royalty fees so that they could achieve efficient allocation of the excess benefits generated by remanufacturing. Huang and Wang [30] proved a robust region for the royalty fee and production decisions with the context of demand disruptions. Our literature review indicates that a few studies have examined the decisions of OEMs and TPRs regarding authorized remanufacturing. The following studies investigated authorized remanufacturing from different aspects. Oraiopoulos et al. [31] examined an OEM’s decisions on optimal royalty fee when a TPR undertook remanufacturing activities. Based on this study, Hong et al. [20] investigated the optimal collection and remanufacturing decisions by considering competition not only in the forward channel but also in the reverse one. Further, Zhang et al. [32] studied the same decisions but combing with government policy, and Huang and Wang [33] analyzed the effects of strategic consumer behavior on different remanufacturing scenarios. Considering different authorized members, Zhao et al. [34] developed the operational decision models of OEMs and retailers with two cases, one of which the OEMs remanufacture and the other is to authorize remanufacturing to the retailers. However, they did not consider the effects of carbon emission regulations. In practice, regulations affect the decision making of the OEMs and the authorized remanufacturers because of the different carbon emissions generated when producing new products as opposed to remanufacturing products.Studies addressing operational issues in manufacturing under carbon emission regulations are numerous (e.g., [27, 35]) but less in the case of remanufacturing. One study [36] noted that carbon emission regulations create carbon costs and hence complicate production decisions regarding new and remanufactured products. Some scholars discussed the optimal production decisions on manufacturing and remanufacturing under carbon tax policy. Combing with government subsidy policy, Cao et al. [37] studied the optimal production and pricing decisions in a dual-channel supply chain. Cao et al. [38] further investigated the optimal warranty period and trade-in strategies for new and remanufactured products by considering the trade-in subsidies policy. To the best of our knowledge, there are only a few papers that have covered remanufacturing decisions considering cap-and-trade regulations that are most closely related to this study. By considering independent and substitutable demand markets under carbon cap-and-trade regulations, Chang et al. [39] presented optimal production decisions for a manufacturer who produces both new and remanufactured products. The results indicate that regulations greatly influence the production decisions in manufacturing and remanufacturing. Similar to this study, Wang et al. [40] examined a capital-constrained OEM’s production decisions with a downward substitution strategy under cap-and-trade regulations and found that a carbon emission constraint always encourages the OEM to generate more remanufactured products. By considering trade-ins for remanufactured products, Miao et al. [41] derived the optimal pricing and production decisions under cap-and-trade regulations. Zhang et al. [32, 42] further introduced green innovation into a hybrid manufacturing and remanufacturing system and examined the joint pricing strategies and green innovation policy. Their results indicate that carbon emission regulations can increase sales of remanufactured products while decreasing the demand for new products. A few papers further investigated the effects of carbon emission regulations’ parameters on remanufacturing decisions. Liu et al. [43] investigated the optimal production decisions of an independent remanufacturer under cap-and-trade regulations and compared the results to those under other regulations. The results indicate that a higher carbon emission cap would be better for promoting the development of remanufacturers. Shu et al. [44] investigated the impact of a carbon emissions quota and its trade prices on remanufacturing decisions and provided some insights for governments and firms in terms of carbon permits allocation. Owning to the variation of the tax price, Dou et al. [45] analyzed the effects of the tax price on the production planning of manufacturing and remanufacturing. However, the aforementioned papers only consider the effects of carbon cap-and-trade regulations in settings without authorized remanufacturing. In fact, under authorized remanufacturing, carbon emission regulations exert different effects on the decision making of the OEMs and the TPRs.In summary, our study is different from extant research as follows. First, we investigate the condition that TPRs accept authorization under cap-and-trade regulations; second, we examine the effects of cap-and-trade regulations on the decision making of OEMs and authorized TPRs with patent licensing. Presently, the literature only covers the effects of authorized remanufacturing without this constraint; third, we specify the effects of yield rate and consumer WTP on the decision making of OEMs and TPRs. To the best of our knowledge, our study is the first to address the above issues with the consideration of both authorized remanufacturing and carbon cap-and-trade regulations.


## 3. Problem Description

We consider a supply chain comprising an OEM and a TPR, in which the OEM manufactures new products and authorizes the TPR to undertake acquisition and remanufacturing. To analyze the effects of the TPR on the OEM, we discuss two scenarios. In scenario 1, the OEM sells new products as a monopolist without remanufacturing; in scenario 2, the OEM still sells new products while facing competition from the TPR.Throughout the paper, we let the subscriptsm and r denote the OEM and the TPR, respectively. The notations used in the model are listed in Table 1.Table 1
Notation.
NotationDescriptionModel parametercmManufacturing cost per unit of new productcrRemanufacturing cost per unit of remanufactured product (generally,cr < cm)emCarbon emissions for producing a new producterCarbon emissions for producing a remanufactured product (generally,em > er)ɛ1Selling price for one unit of carbon emission permitɛ2Buying price for one unit of carbon emission permit. For simplicity, we setɛ1 < ɛ2MmCarbon emissions cap the government allocates to the OEMMrCarbon emissions cap the government allocates to the TPRAMarket capacityΘConsumer’s willingness to payΓYield rate,γ ϵ (0, 1)ΑQuantity that the consumers return voluntarily at zero priceΒSensitivity of consumers to acquisition priceGAcquired quantity of used productGGovernment subsidy per unit of acquired used productDecision variables for TPRp2rSales price per unit of remanufactured product in scenario 2q2rRemanufacturing quantity/demand for remanufactured products in scenario 2uAcquisition price the TPR collects per unit of used productDecision variables for OEMqimManufacturing quantity/demand for new products in scenarioi, i = 1, 2pimSales price per unit of new product in scenarioifRoyalty rate that the OEM charges the TPR per unit of remanufactured productObjective functionПimTotal profit of OEM in scenarioi, i = 1, 2П2rTotal profit of TPR in scenario 2ПsTotal profit of the entire supply chain with centralized decision makingAccording to Ferguson and Toktay [13], the relationship between demand and price for new and remanufactured products can be described as follows.In scenario 1, since remanufacturing does not occur, we have(1)p1m=A−q1m,where A is assumed to be the same for the two scenarios, that is, market expansion and contraction are not considered in this study.In scenario 2, the OEM only produces new products and the TPR makes remanufactured products. The collected used products are remanufactured with yield rateγ, that is,(2)q2r=yGu,with G(u) = α + βu, where α indicates consumer environmental consciousness and β indicates the influence of unit acquisition price on the acquired quantity.Then, we have the following inverse demand functions:(3)p2m=A=q2m−θq2r,(4)p2r=θA−q2m−q2r,where if θ = 0, consumers are only willing to pay new products; if θ = 1, consumers are willing to pay the same for new or remanufactured products. As the majority of consumers are eclectic, we assume 0 < θ < 1.


## 4. Model Formulation and Solution

We first establish a production and pricing decision-making model for the OEM under cap-and-trade regulations in scenario 1. Then, in scenario 2, for the cases of centralized and decentralized decision making, we formulate an operational decision-making model for the TPR and, subsequently, establish one for the OEM.In scenario 1, since the OEM only produces new products, the OEM’s profit can be described as(5)∏1m=q1mp1m−cm+ε1Mm−q1mem+−ε2q1mem−Mm+,where (a − b)+ means max{a − b, 0}. Hence, we have(6)∏1m=q1mp1m−cm−ε2q1mem−Mm,Mm≤q1mem,q1mp1m−cm+ε1Mm−q1mem,otherwise.In scenario 2, the profits of the OEM and the TPR, respectively, are(7)∏2m=q2mp2m−cm+q2rf+ε1Mm−q2mem+−ε2q2mem−Mm+,(8)∏2r=q2rp2r−cr−f+Gug−u+ε1Mr−q2rer+−ε2q2rer−Mr+.


### 4.1. OEM’s Production and Pricing Decision Making in Scenario 1

As mentioned above, in scenario 1, all the market demand is satisfied by the OEM’s new products. We can, therefore, easily derive the optimal solutions as Proposition1.Proposition 1.
In scenario 1, the optimal production quantityq1m∗ and the optimal sales price p1m∗ for new products, respectively, are as follows:(9)q1m∗=Mm/em,q1m″≤Mm/em≤q1m′,A−cm−B/2,otherwise,(10)p1m∗=A−Mm/em,q1m″≤Mm/em≤q1m′,A+cm+B/2,otherwise,where q1m'=A−cm−ε1em/2; it means the OEM’s manufacturing quantity, which maximizes the profits, when the government allocates the OEM enough carbon emission permits. q1m'′=A−cm−ε2em/2; it means the OEM’s manufacturing quantity, which maximizes the profits when the carbon emission permits allocated by government are not enough for the OEM to manufacture new products.(11)B=ε1em,Mm/em>q1m',ε2em,Mm/em<q1m'′.Thus, the corresponding profit is(12)∏1m∗=q1m∗p1m∗−cm+ε1Mm−q1m∗em+−ε2q1m∗em−Mm+.The proof is provided in Appendix A.In order to analyze the relationship betweenMm/em and the optimal manufacturing quantity, we define Mm/em as the virtual manufacturing quantity. The carbon emissions generated by manufacturing these new products exactly equal the carbon emissions quota from the government.As shown in Proposition1, the value of Mm/em affects the optimal decisions of the OEM in scenario 1. When the virtual manufacturing quantity is between q1m'′ and q1m', the optimal manufacturing quantity equals the virtual manufacturing quantity, which is not affected by the trading price. The reason is if the OEM manufactures less than the virtual manufacturing quantity, the savings on marginal cost from reducing a unit new product are less than the loss in marginal revenue; if the OEM manufactures more than the virtual manufacturing quantity, the marginal revenue from increasing a unit new product is less than the marginal cost. Therefore, in this case, the optimal quantity decision for the OEM should beMm/em. This generally occurs when carbon emission permits are traded at a low selling price but a high buying price. Otherwise, the optimal manufacturing quantity is negatively related to the trading price. The OEM can pursue profit maximization by setting different sales prices for new products and adjusting production strategies based on the trading price of carbon permits.


### 4.2. Decision Making of the OEM and TPR in Scenario 2

In scenario 2, the OEM only produces new products, and the TPR remanufactures the acquired used products with the OEM’s authorization.


#### 4.2.1. Decentralized Decision Making

After the TPR enters, competition exists between the OEM and the TPR. We use a Stackelberg model to describe this competition. The OEM is the market leader, whereas the TPR is the follower. The Stackelberg game problem is solved through the backward method. First, we solve the TPR’s optimal quantity/price of the remanufactured products under the condition that the decisions of the OEM are given. We then solve the OEM’s optimal decisions after obtaining the TPR’s optimal decisions. The optimal decisions can be summarized as Propositions2 and 3.Proposition 2.
Givenq2m∗, the strategies of the TPR are expressed as follows:(13)q2r∗=0,q2r'′≤Mr/er≤q2r',γβγθA−q2m∗−cr−f∗−C+βg+α2θβγ2+2,otherwise,(14)p2r∗=random,q2r'′≤Mr/er≤q2r',θγβγcr+f∗+C−βg−α+θβγ2+2A−q2m∗2θβγ2+2,otherwise,(15)u∗=random,q2r'′≤Mr/er≤q2r',βγθA−q2m∗−2αγ−cr−f∗−C+βg−α2θβ2γ2+2β,otherwise,(16)G∗u∗=α+βu∗,(17)∏2r∗=q2r∗p2r∗−cr−f∗+Gu∗g−u∗+ε1Mr−q2r∗er+−ε2q2r∗er−Mr+,where q2r∗, p2r∗, u∗, and G∗u∗ are the TPR’s optimal decisions on remanufacturing quantity, sales price of remanufactured products, acquisition price, and quantity of the used products, respectively; q2m∗ and f∗ are the OEM’s optimal decisions on manufacturing quantity and royalty rate; ∏2r∗ is the corresponding profit; q2r' represents the TPR’s remanufacturing quantity, which maximizes the profits when the government allocates the TPR enough carbon emission permits; and q2r'′ represents the TPR’s remanufacturing quantity, which maximizes the profits when the carbon emission permits allocated by the government are not enough for the TPR to remanufacture collected used products.(18)q2r'=βγ2θA−q2m∗−ε1er−cr−f∗+βγg+αγ/2θβγ2+2,q2r'′=βγ2θA−q2m∗−ε2er−cr−f∗+βγg+αγ/2θβγ2+2,(19)C=ε1er,Mr/er>q2r',ε2er,q2r'′>Mr/er.The proof is provided in Appendix B.In order to analyze the relationship betweenMr/er and the optimal remanufacturing quantity, we define Mr/er as the virtual remanufacturing quantity based on Mr similar to scenario 1.From Proposition2, the following conclusions can be drawn.The virtual remanufacturing quantity affects the optimal operational decisions of the TPR. When the virtual remanufacturing quantity is betweenq2r'′ and q2r', the TPR would not accept authorization from the OEM. In this case, if the TPR does not consider the OEM’s decision, the optimal remanufacturing quantity should be Mr/er. But if q2r∗=Mr/er, the profit of the OEM increases monotonously vs. royalty rate f, for which the TPR’s best choose is to refuse authorization. Otherwise, the optimal decisions of the TPR are related to the trading price of carbon emission permits. The remanufacturing quantity, acquisition price, and acquisition quantity of used products are negatively affected by the trading price of carbon emission permits (ɛ1 or ɛ2); however, the sales price of remanufactured products is positively affected.Proposition 3.
Given the TPR’s pricing strategies, the OEM’s strategies are as follows: whenq2r∗=Mr/er≤q2r', q2m∗ are as the same as in scenario 1; otherwise,(20)q2m∗=Mm/em,q2m'′≤Mm/em≤q2m',2A−cmθβγ2+1+θγβγcr−θA+C−βg−α−2θβγ2+1D4θβγ2−2θ2βγ2+4,otherwise,(21)f∗=βγθA−cr−C+βg+α2βγ,(22)p2m∗=A−q2m∗−θq2r∗,(23)∏2m∗=q2m∗p2m∗−cm+q2r∗f∗+ε1Mm−q2m∗em+−ε2q2m∗em−Mm+,where q2m∗, f∗, and p2m∗ are the OEM’s optimal decisions on manufacturing quantity, royalty rate, and sales price of new products, respectively; ∏2m∗ is the corresponding profit; q2m' represents the OEM’s manufacturing quantity to maximize its profits when the government allocates it enough carbon emission permits; and q2m'′ represents the OEM’s manufacturing quantity to maximize its profits when the carbon emission permits allocated by the government are not enough for the OEM to manufacture new products.(24)q2m'=2A−cmθβγ2+1+θγβγcr−θA−βg−α+C−2θβγ2+1ε1em4θβγ2−2θ2βγ2+4,q2m'′=2A−cmθβγ2+1+θγβγcr−θA−βg−α+C−2θβγ2+1ε2em4θβγ2−2θ2βγ2+4,(25)D=ε1em,Mm/em>q2m',ε2em,Mm/em<q2m'′.The proof is provided in Appendix C.As defined in scenario 1, we noteMm/em as the virtual manufacturing quantity in scenario 2. From Proposition 3, we can conclude the following:(1)
WhenMm/em is between q2m'′ and q2m', the optimal manufacturing quantity of the OEM should equal the virtual manufacturing quantity. This case is the same as in scenario 1, i.e., the TPR would not enter. Otherwise, the OEM’s optimal decisions are related to the trading price and the carbon emissions generated per new and remanufactured product.(2)
The optimal royalty rate (f∗) is negatively affected by the trading price of carbon emission permits (ɛ1 or ɛ2). This result illustrates that the OEM charges the TPR a low royalty rate when the trading price is high. But even with a low royalty rate, the total royalty fee is not lower since remanufacturing quantity rises. Additionally, the optimal royalty rate is also related to carbon emissions per remanufactured product but is not affected by that of new product.


#### 4.2.2. Centralized Decision Making

In this case, the OEM and the TPR make joint decisions to maximize the total profit of the entire supply chain. The total profit of the whole supply chain can be described as(26)∏s=q2mp2m−cm+q2rp2r−cr+Gug−u+ε1Mm+Mr−q2mem−q2rer+−ε2q2mem+q2rer−Mm−Mr+.The optimal decisions are summarized as Proposition4.Proposition 4.
With centralized decision making, the strategies of both parties are(27)q2m∗∗=q2mc′'′,q2mc′'em+q2rc′'er≤Mm+Mr≤q2mc′em+q2rc′er,A−cm−Bc2−θq2r∗∗,otherwise,(28)q2r∗∗=q2rc′'′,q2mc′'em+q2rc′'er≤Mm+Mr≤q2mc′em+q2rc′er,γβg+α+βγ2θcm−cr+Cc2θβγ2−θ2βγ2−1,otherwise,(29)p2m∗∗=A−q2m∗∗−θq2r∗∗,(30)p2r∗∗=θA−q2m∗∗−q2r∗∗,(31)u∗∗=q2r∗∗−αγ/βγ,(32)∏S∗∗=q2m∗∗p2m∗∗−cm+q2r∗∗p2r∗∗−cr+Gug−u+ε1Mm+Mr−q2m∗∗em−q2r∗∗er+−ε2q2m∗∗em+q2r∗∗er−Mm−Mr+,where q2m∗∗ and p2m∗∗ are the OEM’s optimal decisions on manufacturing quantity and sales price of new products, respectively; q2r∗∗, p2r∗∗, and u∗∗ are the remanufacturer’s optimal decisions on remanufacturing quantity, sales price of remanufactured products, and acquisition price of used products, respectively; ∏s∗∗ is the corresponding total profit of the whole supply chain; and,(33)q2mc′=A−cm−ε1em2−θq2rc′,q2mc′'=A−cm−ε2em2−θq2rc′',q2mc′'′=Mm+Mr−erq2rc′'′em,(34)q2rc′=γβg+α+βγ2θcm−cr+ε1θem−er2θβγ2−θ2βγ2−1,q2rc′'=γβg+α+βγ2θcm−cr+ε2θem−er2θβγ2−θ2βγ2−1,q2rc′'′=βγ22Mm+Mrer−θem−A−cmerem+em2γβγθA−cr+βg+α2βγ2er2−2θerem+θem2+em2,(35)Bc=ε1em,Mm+Mr>q2mc′em+q2rc′er,ε2em,Mm+Mr<q2mc′'em+q2rc′'er,(36)Cc=ε1θem−er,Mm+Mr>q2mc′em+q2rc′er,ε2θem−er,Mm+Mr<q2mc′'em+q2rc′'er.The proof is provided in Appendix D.From Proposition4, the following conclusions can be drawn:(1)
When the total carbon emission capsMm+Mr allocated to the OEM and the TPR are between q2mc′'em+q2rc′'er and q2mc′em+q2rc′er, the decisions of the OEM and the TPR are not affected by the trading price but are related to carbon emissions caused by producing new and remanufactured product.(2)
When the total carbon emissions caps of the OEM and the TPR are less thanq2mc′'em+q2rc′'er or more than q2mc′em+q2rc′er and θem > er holds, remanufactured products’ sales price decreases, but remanufacturing quantity and acquisition price increase with the increase of ɛ1 and ɛ2. However, the sales price for new products increases, while manufacturing quantity decreases as ɛ1 and ɛ2 increases. When θem ≤ er, the opposite occurs.According to the above propositions, carbon emissions cap does affect the operational decisions of the OEM and the TPR and plays a great role in the TPR’s decision on accepting authorization or not. Therefore, the government must set a reasonable carbon emissions cap for the OEMs and the TPRs. Conversely, based on their carbon emission caps and the trading price of carbon emission permits, the OEMs and TPRs must adjust their strategies in time to maximize their profits. In addition, WTP (θ) also affects the decisions. It is believed that producing a large number of remanufactured products while reducing the quantity of new products is economical, and therefore the total profit of the entire supply chain increases when θ is high. When the demand for remanufactured products increases, the TPR is compelled to collect an increasing number of used products to satisfy the demand. Thus, the environmental benefits also improve.


## 4.1. OEM’s Production and Pricing Decision Making in Scenario 1

As mentioned above, in scenario 1, all the market demand is satisfied by the OEM’s new products. We can, therefore, easily derive the optimal solutions as Proposition1.Proposition 1.
In scenario 1, the optimal production quantityq1m∗ and the optimal sales price p1m∗ for new products, respectively, are as follows:(9)q1m∗=Mm/em,q1m″≤Mm/em≤q1m′,A−cm−B/2,otherwise,(10)p1m∗=A−Mm/em,q1m″≤Mm/em≤q1m′,A+cm+B/2,otherwise,where q1m'=A−cm−ε1em/2; it means the OEM’s manufacturing quantity, which maximizes the profits, when the government allocates the OEM enough carbon emission permits. q1m'′=A−cm−ε2em/2; it means the OEM’s manufacturing quantity, which maximizes the profits when the carbon emission permits allocated by government are not enough for the OEM to manufacture new products.(11)B=ε1em,Mm/em>q1m',ε2em,Mm/em<q1m'′.Thus, the corresponding profit is(12)∏1m∗=q1m∗p1m∗−cm+ε1Mm−q1m∗em+−ε2q1m∗em−Mm+.The proof is provided in Appendix A.In order to analyze the relationship betweenMm/em and the optimal manufacturing quantity, we define Mm/em as the virtual manufacturing quantity. The carbon emissions generated by manufacturing these new products exactly equal the carbon emissions quota from the government.As shown in Proposition1, the value of Mm/em affects the optimal decisions of the OEM in scenario 1. When the virtual manufacturing quantity is between q1m'′ and q1m', the optimal manufacturing quantity equals the virtual manufacturing quantity, which is not affected by the trading price. The reason is if the OEM manufactures less than the virtual manufacturing quantity, the savings on marginal cost from reducing a unit new product are less than the loss in marginal revenue; if the OEM manufactures more than the virtual manufacturing quantity, the marginal revenue from increasing a unit new product is less than the marginal cost. Therefore, in this case, the optimal quantity decision for the OEM should beMm/em. This generally occurs when carbon emission permits are traded at a low selling price but a high buying price. Otherwise, the optimal manufacturing quantity is negatively related to the trading price. The OEM can pursue profit maximization by setting different sales prices for new products and adjusting production strategies based on the trading price of carbon permits.


## 4.2. Decision Making of the OEM and TPR in Scenario 2

In scenario 2, the OEM only produces new products, and the TPR remanufactures the acquired used products with the OEM’s authorization.


### 4.2.1. Decentralized Decision Making

After the TPR enters, competition exists between the OEM and the TPR. We use a Stackelberg model to describe this competition. The OEM is the market leader, whereas the TPR is the follower. The Stackelberg game problem is solved through the backward method. First, we solve the TPR’s optimal quantity/price of the remanufactured products under the condition that the decisions of the OEM are given. We then solve the OEM’s optimal decisions after obtaining the TPR’s optimal decisions. The optimal decisions can be summarized as Propositions2 and 3.Proposition 2.
Givenq2m∗, the strategies of the TPR are expressed as follows:(13)q2r∗=0,q2r'′≤Mr/er≤q2r',γβγθA−q2m∗−cr−f∗−C+βg+α2θβγ2+2,otherwise,(14)p2r∗=random,q2r'′≤Mr/er≤q2r',θγβγcr+f∗+C−βg−α+θβγ2+2A−q2m∗2θβγ2+2,otherwise,(15)u∗=random,q2r'′≤Mr/er≤q2r',βγθA−q2m∗−2αγ−cr−f∗−C+βg−α2θβ2γ2+2β,otherwise,(16)G∗u∗=α+βu∗,(17)∏2r∗=q2r∗p2r∗−cr−f∗+Gu∗g−u∗+ε1Mr−q2r∗er+−ε2q2r∗er−Mr+,where q2r∗, p2r∗, u∗, and G∗u∗ are the TPR’s optimal decisions on remanufacturing quantity, sales price of remanufactured products, acquisition price, and quantity of the used products, respectively; q2m∗ and f∗ are the OEM’s optimal decisions on manufacturing quantity and royalty rate; ∏2r∗ is the corresponding profit; q2r' represents the TPR’s remanufacturing quantity, which maximizes the profits when the government allocates the TPR enough carbon emission permits; and q2r'′ represents the TPR’s remanufacturing quantity, which maximizes the profits when the carbon emission permits allocated by the government are not enough for the TPR to remanufacture collected used products.(18)q2r'=βγ2θA−q2m∗−ε1er−cr−f∗+βγg+αγ/2θβγ2+2,q2r'′=βγ2θA−q2m∗−ε2er−cr−f∗+βγg+αγ/2θβγ2+2,(19)C=ε1er,Mr/er>q2r',ε2er,q2r'′>Mr/er.The proof is provided in Appendix B.In order to analyze the relationship betweenMr/er and the optimal remanufacturing quantity, we define Mr/er as the virtual remanufacturing quantity based on Mr similar to scenario 1.From Proposition2, the following conclusions can be drawn.The virtual remanufacturing quantity affects the optimal operational decisions of the TPR. When the virtual remanufacturing quantity is betweenq2r'′ and q2r', the TPR would not accept authorization from the OEM. In this case, if the TPR does not consider the OEM’s decision, the optimal remanufacturing quantity should be Mr/er. But if q2r∗=Mr/er, the profit of the OEM increases monotonously vs. royalty rate f, for which the TPR’s best choose is to refuse authorization. Otherwise, the optimal decisions of the TPR are related to the trading price of carbon emission permits. The remanufacturing quantity, acquisition price, and acquisition quantity of used products are negatively affected by the trading price of carbon emission permits (ɛ1 or ɛ2); however, the sales price of remanufactured products is positively affected.Proposition 3.
Given the TPR’s pricing strategies, the OEM’s strategies are as follows: whenq2r∗=Mr/er≤q2r', q2m∗ are as the same as in scenario 1; otherwise,(20)q2m∗=Mm/em,q2m'′≤Mm/em≤q2m',2A−cmθβγ2+1+θγβγcr−θA+C−βg−α−2θβγ2+1D4θβγ2−2θ2βγ2+4,otherwise,(21)f∗=βγθA−cr−C+βg+α2βγ,(22)p2m∗=A−q2m∗−θq2r∗,(23)∏2m∗=q2m∗p2m∗−cm+q2r∗f∗+ε1Mm−q2m∗em+−ε2q2m∗em−Mm+,where q2m∗, f∗, and p2m∗ are the OEM’s optimal decisions on manufacturing quantity, royalty rate, and sales price of new products, respectively; ∏2m∗ is the corresponding profit; q2m' represents the OEM’s manufacturing quantity to maximize its profits when the government allocates it enough carbon emission permits; and q2m'′ represents the OEM’s manufacturing quantity to maximize its profits when the carbon emission permits allocated by the government are not enough for the OEM to manufacture new products.(24)q2m'=2A−cmθβγ2+1+θγβγcr−θA−βg−α+C−2θβγ2+1ε1em4θβγ2−2θ2βγ2+4,q2m'′=2A−cmθβγ2+1+θγβγcr−θA−βg−α+C−2θβγ2+1ε2em4θβγ2−2θ2βγ2+4,(25)D=ε1em,Mm/em>q2m',ε2em,Mm/em<q2m'′.The proof is provided in Appendix C.As defined in scenario 1, we noteMm/em as the virtual manufacturing quantity in scenario 2. From Proposition 3, we can conclude the following:(1)
WhenMm/em is between q2m'′ and q2m', the optimal manufacturing quantity of the OEM should equal the virtual manufacturing quantity. This case is the same as in scenario 1, i.e., the TPR would not enter. Otherwise, the OEM’s optimal decisions are related to the trading price and the carbon emissions generated per new and remanufactured product.(2)
The optimal royalty rate (f∗) is negatively affected by the trading price of carbon emission permits (ɛ1 or ɛ2). This result illustrates that the OEM charges the TPR a low royalty rate when the trading price is high. But even with a low royalty rate, the total royalty fee is not lower since remanufacturing quantity rises. Additionally, the optimal royalty rate is also related to carbon emissions per remanufactured product but is not affected by that of new product.


### 4.2.2. Centralized Decision Making

In this case, the OEM and the TPR make joint decisions to maximize the total profit of the entire supply chain. The total profit of the whole supply chain can be described as(26)∏s=q2mp2m−cm+q2rp2r−cr+Gug−u+ε1Mm+Mr−q2mem−q2rer+−ε2q2mem+q2rer−Mm−Mr+.The optimal decisions are summarized as Proposition4.Proposition 4.
With centralized decision making, the strategies of both parties are(27)q2m∗∗=q2mc′'′,q2mc′'em+q2rc′'er≤Mm+Mr≤q2mc′em+q2rc′er,A−cm−Bc2−θq2r∗∗,otherwise,(28)q2r∗∗=q2rc′'′,q2mc′'em+q2rc′'er≤Mm+Mr≤q2mc′em+q2rc′er,γβg+α+βγ2θcm−cr+Cc2θβγ2−θ2βγ2−1,otherwise,(29)p2m∗∗=A−q2m∗∗−θq2r∗∗,(30)p2r∗∗=θA−q2m∗∗−q2r∗∗,(31)u∗∗=q2r∗∗−αγ/βγ,(32)∏S∗∗=q2m∗∗p2m∗∗−cm+q2r∗∗p2r∗∗−cr+Gug−u+ε1Mm+Mr−q2m∗∗em−q2r∗∗er+−ε2q2m∗∗em+q2r∗∗er−Mm−Mr+,where q2m∗∗ and p2m∗∗ are the OEM’s optimal decisions on manufacturing quantity and sales price of new products, respectively; q2r∗∗, p2r∗∗, and u∗∗ are the remanufacturer’s optimal decisions on remanufacturing quantity, sales price of remanufactured products, and acquisition price of used products, respectively; ∏s∗∗ is the corresponding total profit of the whole supply chain; and,(33)q2mc′=A−cm−ε1em2−θq2rc′,q2mc′'=A−cm−ε2em2−θq2rc′',q2mc′'′=Mm+Mr−erq2rc′'′em,(34)q2rc′=γβg+α+βγ2θcm−cr+ε1θem−er2θβγ2−θ2βγ2−1,q2rc′'=γβg+α+βγ2θcm−cr+ε2θem−er2θβγ2−θ2βγ2−1,q2rc′'′=βγ22Mm+Mrer−θem−A−cmerem+em2γβγθA−cr+βg+α2βγ2er2−2θerem+θem2+em2,(35)Bc=ε1em,Mm+Mr>q2mc′em+q2rc′er,ε2em,Mm+Mr<q2mc′'em+q2rc′'er,(36)Cc=ε1θem−er,Mm+Mr>q2mc′em+q2rc′er,ε2θem−er,Mm+Mr<q2mc′'em+q2rc′'er.The proof is provided in Appendix D.From Proposition4, the following conclusions can be drawn:(1)
When the total carbon emission capsMm+Mr allocated to the OEM and the TPR are between q2mc′'em+q2rc′'er and q2mc′em+q2rc′er, the decisions of the OEM and the TPR are not affected by the trading price but are related to carbon emissions caused by producing new and remanufactured product.(2)
When the total carbon emissions caps of the OEM and the TPR are less thanq2mc′'em+q2rc′'er or more than q2mc′em+q2rc′er and θem > er holds, remanufactured products’ sales price decreases, but remanufacturing quantity and acquisition price increase with the increase of ɛ1 and ɛ2. However, the sales price for new products increases, while manufacturing quantity decreases as ɛ1 and ɛ2 increases. When θem ≤ er, the opposite occurs.According to the above propositions, carbon emissions cap does affect the operational decisions of the OEM and the TPR and plays a great role in the TPR’s decision on accepting authorization or not. Therefore, the government must set a reasonable carbon emissions cap for the OEMs and the TPRs. Conversely, based on their carbon emission caps and the trading price of carbon emission permits, the OEMs and TPRs must adjust their strategies in time to maximize their profits. In addition, WTP (θ) also affects the decisions. It is believed that producing a large number of remanufactured products while reducing the quantity of new products is economical, and therefore the total profit of the entire supply chain increases when θ is high. When the demand for remanufactured products increases, the TPR is compelled to collect an increasing number of used products to satisfy the demand. Thus, the environmental benefits also improve.


## 4.2.1. Decentralized Decision Making

After the TPR enters, competition exists between the OEM and the TPR. We use a Stackelberg model to describe this competition. The OEM is the market leader, whereas the TPR is the follower. The Stackelberg game problem is solved through the backward method. First, we solve the TPR’s optimal quantity/price of the remanufactured products under the condition that the decisions of the OEM are given. We then solve the OEM’s optimal decisions after obtaining the TPR’s optimal decisions. The optimal decisions can be summarized as Propositions2 and 3.Proposition 2.
Givenq2m∗, the strategies of the TPR are expressed as follows:(13)q2r∗=0,q2r'′≤Mr/er≤q2r',γβγθA−q2m∗−cr−f∗−C+βg+α2θβγ2+2,otherwise,(14)p2r∗=random,q2r'′≤Mr/er≤q2r',θγβγcr+f∗+C−βg−α+θβγ2+2A−q2m∗2θβγ2+2,otherwise,(15)u∗=random,q2r'′≤Mr/er≤q2r',βγθA−q2m∗−2αγ−cr−f∗−C+βg−α2θβ2γ2+2β,otherwise,(16)G∗u∗=α+βu∗,(17)∏2r∗=q2r∗p2r∗−cr−f∗+Gu∗g−u∗+ε1Mr−q2r∗er+−ε2q2r∗er−Mr+,where q2r∗, p2r∗, u∗, and G∗u∗ are the TPR’s optimal decisions on remanufacturing quantity, sales price of remanufactured products, acquisition price, and quantity of the used products, respectively; q2m∗ and f∗ are the OEM’s optimal decisions on manufacturing quantity and royalty rate; ∏2r∗ is the corresponding profit; q2r' represents the TPR’s remanufacturing quantity, which maximizes the profits when the government allocates the TPR enough carbon emission permits; and q2r'′ represents the TPR’s remanufacturing quantity, which maximizes the profits when the carbon emission permits allocated by the government are not enough for the TPR to remanufacture collected used products.(18)q2r'=βγ2θA−q2m∗−ε1er−cr−f∗+βγg+αγ/2θβγ2+2,q2r'′=βγ2θA−q2m∗−ε2er−cr−f∗+βγg+αγ/2θβγ2+2,(19)C=ε1er,Mr/er>q2r',ε2er,q2r'′>Mr/er.The proof is provided in Appendix B.In order to analyze the relationship betweenMr/er and the optimal remanufacturing quantity, we define Mr/er as the virtual remanufacturing quantity based on Mr similar to scenario 1.From Proposition2, the following conclusions can be drawn.The virtual remanufacturing quantity affects the optimal operational decisions of the TPR. When the virtual remanufacturing quantity is betweenq2r'′ and q2r', the TPR would not accept authorization from the OEM. In this case, if the TPR does not consider the OEM’s decision, the optimal remanufacturing quantity should be Mr/er. But if q2r∗=Mr/er, the profit of the OEM increases monotonously vs. royalty rate f, for which the TPR’s best choose is to refuse authorization. Otherwise, the optimal decisions of the TPR are related to the trading price of carbon emission permits. The remanufacturing quantity, acquisition price, and acquisition quantity of used products are negatively affected by the trading price of carbon emission permits (ɛ1 or ɛ2); however, the sales price of remanufactured products is positively affected.Proposition 3.
Given the TPR’s pricing strategies, the OEM’s strategies are as follows: whenq2r∗=Mr/er≤q2r', q2m∗ are as the same as in scenario 1; otherwise,(20)q2m∗=Mm/em,q2m'′≤Mm/em≤q2m',2A−cmθβγ2+1+θγβγcr−θA+C−βg−α−2θβγ2+1D4θβγ2−2θ2βγ2+4,otherwise,(21)f∗=βγθA−cr−C+βg+α2βγ,(22)p2m∗=A−q2m∗−θq2r∗,(23)∏2m∗=q2m∗p2m∗−cm+q2r∗f∗+ε1Mm−q2m∗em+−ε2q2m∗em−Mm+,where q2m∗, f∗, and p2m∗ are the OEM’s optimal decisions on manufacturing quantity, royalty rate, and sales price of new products, respectively; ∏2m∗ is the corresponding profit; q2m' represents the OEM’s manufacturing quantity to maximize its profits when the government allocates it enough carbon emission permits; and q2m'′ represents the OEM’s manufacturing quantity to maximize its profits when the carbon emission permits allocated by the government are not enough for the OEM to manufacture new products.(24)q2m'=2A−cmθβγ2+1+θγβγcr−θA−βg−α+C−2θβγ2+1ε1em4θβγ2−2θ2βγ2+4,q2m'′=2A−cmθβγ2+1+θγβγcr−θA−βg−α+C−2θβγ2+1ε2em4θβγ2−2θ2βγ2+4,(25)D=ε1em,Mm/em>q2m',ε2em,Mm/em<q2m'′.The proof is provided in Appendix C.As defined in scenario 1, we noteMm/em as the virtual manufacturing quantity in scenario 2. From Proposition 3, we can conclude the following:(1)
WhenMm/em is between q2m'′ and q2m', the optimal manufacturing quantity of the OEM should equal the virtual manufacturing quantity. This case is the same as in scenario 1, i.e., the TPR would not enter. Otherwise, the OEM’s optimal decisions are related to the trading price and the carbon emissions generated per new and remanufactured product.(2)
The optimal royalty rate (f∗) is negatively affected by the trading price of carbon emission permits (ɛ1 or ɛ2). This result illustrates that the OEM charges the TPR a low royalty rate when the trading price is high. But even with a low royalty rate, the total royalty fee is not lower since remanufacturing quantity rises. Additionally, the optimal royalty rate is also related to carbon emissions per remanufactured product but is not affected by that of new product.


## 4.2.2. Centralized Decision Making

In this case, the OEM and the TPR make joint decisions to maximize the total profit of the entire supply chain. The total profit of the whole supply chain can be described as(26)∏s=q2mp2m−cm+q2rp2r−cr+Gug−u+ε1Mm+Mr−q2mem−q2rer+−ε2q2mem+q2rer−Mm−Mr+.The optimal decisions are summarized as Proposition4.Proposition 4.
With centralized decision making, the strategies of both parties are(27)q2m∗∗=q2mc′'′,q2mc′'em+q2rc′'er≤Mm+Mr≤q2mc′em+q2rc′er,A−cm−Bc2−θq2r∗∗,otherwise,(28)q2r∗∗=q2rc′'′,q2mc′'em+q2rc′'er≤Mm+Mr≤q2mc′em+q2rc′er,γβg+α+βγ2θcm−cr+Cc2θβγ2−θ2βγ2−1,otherwise,(29)p2m∗∗=A−q2m∗∗−θq2r∗∗,(30)p2r∗∗=θA−q2m∗∗−q2r∗∗,(31)u∗∗=q2r∗∗−αγ/βγ,(32)∏S∗∗=q2m∗∗p2m∗∗−cm+q2r∗∗p2r∗∗−cr+Gug−u+ε1Mm+Mr−q2m∗∗em−q2r∗∗er+−ε2q2m∗∗em+q2r∗∗er−Mm−Mr+,where q2m∗∗ and p2m∗∗ are the OEM’s optimal decisions on manufacturing quantity and sales price of new products, respectively; q2r∗∗, p2r∗∗, and u∗∗ are the remanufacturer’s optimal decisions on remanufacturing quantity, sales price of remanufactured products, and acquisition price of used products, respectively; ∏s∗∗ is the corresponding total profit of the whole supply chain; and,(33)q2mc′=A−cm−ε1em2−θq2rc′,q2mc′'=A−cm−ε2em2−θq2rc′',q2mc′'′=Mm+Mr−erq2rc′'′em,(34)q2rc′=γβg+α+βγ2θcm−cr+ε1θem−er2θβγ2−θ2βγ2−1,q2rc′'=γβg+α+βγ2θcm−cr+ε2θem−er2θβγ2−θ2βγ2−1,q2rc′'′=βγ22Mm+Mrer−θem−A−cmerem+em2γβγθA−cr+βg+α2βγ2er2−2θerem+θem2+em2,(35)Bc=ε1em,Mm+Mr>q2mc′em+q2rc′er,ε2em,Mm+Mr<q2mc′'em+q2rc′'er,(36)Cc=ε1θem−er,Mm+Mr>q2mc′em+q2rc′er,ε2θem−er,Mm+Mr<q2mc′'em+q2rc′'er.The proof is provided in Appendix D.From Proposition4, the following conclusions can be drawn:(1)
When the total carbon emission capsMm+Mr allocated to the OEM and the TPR are between q2mc′'em+q2rc′'er and q2mc′em+q2rc′er, the decisions of the OEM and the TPR are not affected by the trading price but are related to carbon emissions caused by producing new and remanufactured product.(2)
When the total carbon emissions caps of the OEM and the TPR are less thanq2mc′'em+q2rc′'er or more than q2mc′em+q2rc′er and θem > er holds, remanufactured products’ sales price decreases, but remanufacturing quantity and acquisition price increase with the increase of ɛ1 and ɛ2. However, the sales price for new products increases, while manufacturing quantity decreases as ɛ1 and ɛ2 increases. When θem ≤ er, the opposite occurs.According to the above propositions, carbon emissions cap does affect the operational decisions of the OEM and the TPR and plays a great role in the TPR’s decision on accepting authorization or not. Therefore, the government must set a reasonable carbon emissions cap for the OEMs and the TPRs. Conversely, based on their carbon emission caps and the trading price of carbon emission permits, the OEMs and TPRs must adjust their strategies in time to maximize their profits. In addition, WTP (θ) also affects the decisions. It is believed that producing a large number of remanufactured products while reducing the quantity of new products is economical, and therefore the total profit of the entire supply chain increases when θ is high. When the demand for remanufactured products increases, the TPR is compelled to collect an increasing number of used products to satisfy the demand. Thus, the environmental benefits also improve.


## 5. Numerical Examples

In this section, numerical examples are provided to examine the results of the comparison between the decisions before and after a TPR enters, under decentralization and centralization, and with or without the constraint of cap-and-trade regulations. As yield rate and WTP are also considerably affecting optimal decision making, we elaborate their effects in a series of figures. We set the base parameters to the following values:A = 1200, G(u) = 20 + 4u, cm = 300, em = 1.5, cr = 150, er = 1, g = 1, γ = 0.9, θ = 0.7, ε1 = 40, ε2 = 50, Mm = 700, and Mr = 10.


### 5.1. Results of Optimal Decision Making

By substituting the parameter values into the solutions inSection 4, we obtain the optimal decisions in scenario 1 are as follows: p1m∗ = 780, q1m∗ = 420, and ∏1m∗ = 216,400. The results in scenario 2 are presented in Table 2 and 3.Table 2
The results in scenario 2 without a constraint on carbon emission regulations.
Itemsp2mq2mp2rq2rfuG∏2m∏2r∏sA750434.72520.4221.83348.331.0624.25203,227.51480.46203,707.97B750405.01511.5064.27—12.8571.41——204,642.35Note. A—decentralized decision making; B—centralized decision making.Table 3
The results in scenario 2 with cap-and-trade regulations.
Itemsp2mq2mp2rq2rfuG∏2m∏2r∏sA780404.26541.2822.48328.331.2424.98217,171.8112,509.72229,681.53B780373.66532.1066.20—13.3973.55——230,672.82Note. A—decentralized decision making; B—centralized decision making.Figure1 presents the difference of the OEM’s profit before and after the TPR enters (i.e., ∏2m∗−∏1m∗, which we denote as Δ∏m) with respect to yield rate.Figure 1
Difference in the OEM’s profit before and after the TPR enters vs. yield rate.It can be observed from Figure1 that overall, the difference increases as yield rate increases. There exists an inflection point; however, under cap-and-trade regulations, the difference declines precipitously when yield rate is approximately 0.4. This inflection point occurs when the total carbon emissions are equal to the cap. Afterwards, the difference still increases.


### 5.2. Effects of Yield Rate on Optimal Decision Making

In this section, we setθ = 0.7 and plot Figures 2–7 to illustrate the effects of yield rate. We denote Case 1 and Case 2 as decentralized decision making without or with a constraint of cap-and-trade regulations and Case 3 and Case 4 as centralized decision making without or with a constraint of cap-and-trade regulations, respectively.Figure 2
(a) Manufacturing quantity/demand for new products and (b) remanufacturing quantity/demand for remanufactured products vs. yield rate.
(a)(b)Figure 3
(a) Sales price for remanufactured products and (b) acquisition price for used products vs. yield rate.
(a)(b)Figure 4
Royalty rate vs. yield rate.Figure 5
Profit of (a) the OEM and (b) the TPR vs. yield rate.
(a)(b)Figure 6
Total profit of the entire supply chain vs. yield rate.Figure 7
Difference in total profit with centralized and decentralized decision making vs. yield rate.We conclude the following based on Figure2. (1) As yield rate increases, the demand for new products decreases, whereas the demand for remanufactured products increases in all four cases, which are in accord with the propositions in Section 4. (2) Compared to decentralized decision making, the effects of the yield rate on the demand for new and remanufactured products with centralized decision making are greater. Especially, the increase in the demand for remanufactured products is more evident. (3) Under cap-and-trade regulations, the demand for new and remanufactured products is less than that without a constraint on carbon emissions. However, the effects on the demand for new products are greater than those on remanufactured products. This trend occurs because the carbon emissions generated by manufacturing new products are larger than those generated by remanufactured products.Figure3(a) shows the sales price for remanufactured products decreases as yield rate increases. However, the magnitude of the decrease with centralized decision making is more evident than that with decentralized decision making. This finding is explained by the fact that a high yield rate implies a low remanufacturing cost, which allows the TPR to lower its sales price. Under cap-and-trade regulations, the sales price is higher than that without a constraint on carbon emissions. This occurs because cap-and-trade regulations cause an increase of the TPR’s remanufacturing cost. Figure 3(b) indicates that in all four cases, acquisition price first increases and then decreases as yield rate increases. This occurs because at the beginning, as yield rate increases, the demand for remanufactured products increases. However, when yield rate reaches a threshold, the demand for remanufactured products and acquisition price for used products reach the maximum since the TPR can collect enough used products at a low acquisition price to satisfy the demand for remanufactured products. As shown in Figure 3(b), with centralized decision making, the acquisition price clearly varies, but with decentralized decision making, the price almost maintains a stable level with respect to yield rate. And the aforementioned threshold of yield rate with centralized decision making is higher than that with decentralized decision making. This implies that compared to decentralized decision making, centralized decision making urges the TPR to improve yield rate and achieve more environmental benefits. As regards the constraint on carbon emissions, the acquisition price under cap-and-trade regulations is relatively lower, which indicates that cap-and-trade regulations can provide a stronger incentive for TPRs to further collect used products owning to a low price.As evident from Figure4, regardless of a constraint on carbon emissions or not, royalty rate decreases as the yield rate increases, but decreases more when yield rate is low. Compared to the case without a constraint on carbon emissions, the royalty rate is lower under cap-and-trade regulations, which means the implementation of cap-and-trade regulations can motivate the OEM to reduce the royalty rate. As a result, the TPR benefits from remanufacturing with a low royalty fee. In addition, the increase in yield rate increases the demand for remanufactured products, for which the OEM still can maintain a high total royalty fee, thereby forming a virtuous cycle between the OEM and the TPR.In Figure5, the profit of the OEM and the TPR increases as yield rate increases regardless of the presence of a constraint on carbon emissions. This finding suggests that improving yield rate is a satisfactory measure to increase the profits of the OEM and the TPR. Figure 5 further illustrates that the profit under cap-and-trade regulations is higher than that without the constraint on carbon emissions. However, this result depends on the size of the carbon emissions cap that the government allocates to the TPR and the OEM. If the carbon emissions cap is not sufficiently high, then the profit under cap-and-trade regulations may be even lower than that without a constraint on carbon emissions.Figure6 demonstrates that the total profit of the entire supply chain increases in all four cases. Under cap-and-trade regulations, the total profit is higher than that in the case without the constraint on carbon emissions, which indicates the implementation of cap-and-trade regulations can improve the supply chain’s profits. Moreover, the total profit with centralized decision making is higher than that with decentralized decision making. Figure 7 shows the difference in the total profit with centralized and decentralized decision making (i.e., ∏s∗∗−∏2m∗+∏2r∗, which we denote as ∆∏s) with respect to yield rate. Overall, the difference increases with respect to yield rate. Consequently, the higher the yield rate is, the larger the effects of centralized decision making on the total profit are. However, the increase under cap-and-trade regulations is less than that without a constraint on carbon emissions.


### 5.3. Effects of WTP on Optimal Decision Making

Similar to Section5.2, we set γ = 0.8 and plot a series of figures reflecting the effects as follows.Figure8 illustrates that regardless of cap-and-trade regulations or a lack thereof, the demand for new products decreases, whereas the demand for remanufactured products increases as WTP increases. This result matches what is found in practice. It is noteworthy that the decrease in the demand for new products and the increase in the demand for remanufactured ones with centralized decision making are more substantial than that in the case with decentralized decision making. This result signifies that the effects of decision-making approach on the demand for new and remanufactured products are more significant. In addition, under cap-and-trade regulations, the demand for new products is always lower than that in that case without a constraint on carbon emissions. Accordingly, the implementation of cap-and-trade regulations can motivate the TPR to remanufacture more used products by taking full advantage of the low carbon emissions.Figure 8
(a) Manufacturing quantity/demand for new products and (b) remanufacturing quantity/demand for remanufactured products vs. WTP.
(a)(b)Figure9(a) indicates that as WTP increases, the sales price for remanufactured products increases rapidly in all four cases. The difference among the four cases is not highly significant. This suggests that decision-making approach and carbon emission regulations do not substantially affect remanufactured products’ sales price with respect to WTP. Figure 9(b) illustrates that the acquisition price also increases with WTP in all four cases. However, the increases are more apparent with centralized than with decentralized decision making. With respect to WTP, the effect of cap-and-trade regulations on acquisition price is negligible.Figure 9
(a) Sales price for remanufactured products and (b) acquisition price for used products vs. WTP.
(a)(b)Figure10 shows that the royalty rate increases with WTP in Case 1 and Case 2. The reason is because an increase in WTP makes remanufactured products more competitive in the market, which in turn implies that the TPR will own more market share. To respond to this threat, the OEM will increase the royalty rate, which is in accord with Proposition 3.Figure 10
Royalty rate vs. WTP.As seen in Figure11, with the increase of WTP, both the OEM and the TPR profits increase with or without the constraint of cap-and-trade regulations. However, under cap-and-trade regulations, the profit is always higher. This indicates the implementation of cap-and-trade regulations is helpful not only for the OEM but also for the TPR.Figure 11
Profit of (a) the OEM and (b) the TPR vs. WTP.
(a)(b)Figure12 shows that as WTP increases, the total profit of the entire supply chain increases in all four cases, but increases more with centralized decision making. This result declares that centralized decision making is a more economical approach to the supply chain compared to decentralized decision making.Figure 12
Total profit of the entire supply chain vs. WTP.


## 5.1. Results of Optimal Decision Making

By substituting the parameter values into the solutions inSection 4, we obtain the optimal decisions in scenario 1 are as follows: p1m∗ = 780, q1m∗ = 420, and ∏1m∗ = 216,400. The results in scenario 2 are presented in Table 2 and 3.Table 2
The results in scenario 2 without a constraint on carbon emission regulations.
Itemsp2mq2mp2rq2rfuG∏2m∏2r∏sA750434.72520.4221.83348.331.0624.25203,227.51480.46203,707.97B750405.01511.5064.27—12.8571.41——204,642.35Note. A—decentralized decision making; B—centralized decision making.Table 3
The results in scenario 2 with cap-and-trade regulations.
Itemsp2mq2mp2rq2rfuG∏2m∏2r∏sA780404.26541.2822.48328.331.2424.98217,171.8112,509.72229,681.53B780373.66532.1066.20—13.3973.55——230,672.82Note. A—decentralized decision making; B—centralized decision making.Figure1 presents the difference of the OEM’s profit before and after the TPR enters (i.e., ∏2m∗−∏1m∗, which we denote as Δ∏m) with respect to yield rate.Figure 1
Difference in the OEM’s profit before and after the TPR enters vs. yield rate.It can be observed from Figure1 that overall, the difference increases as yield rate increases. There exists an inflection point; however, under cap-and-trade regulations, the difference declines precipitously when yield rate is approximately 0.4. This inflection point occurs when the total carbon emissions are equal to the cap. Afterwards, the difference still increases.


## 5.2. Effects of Yield Rate on Optimal Decision Making

In this section, we setθ = 0.7 and plot Figures 2–7 to illustrate the effects of yield rate. We denote Case 1 and Case 2 as decentralized decision making without or with a constraint of cap-and-trade regulations and Case 3 and Case 4 as centralized decision making without or with a constraint of cap-and-trade regulations, respectively.Figure 2
(a) Manufacturing quantity/demand for new products and (b) remanufacturing quantity/demand for remanufactured products vs. yield rate.
(a)(b)Figure 3
(a) Sales price for remanufactured products and (b) acquisition price for used products vs. yield rate.
(a)(b)Figure 4
Royalty rate vs. yield rate.Figure 5
Profit of (a) the OEM and (b) the TPR vs. yield rate.
(a)(b)Figure 6
Total profit of the entire supply chain vs. yield rate.Figure 7
Difference in total profit with centralized and decentralized decision making vs. yield rate.We conclude the following based on Figure2. (1) As yield rate increases, the demand for new products decreases, whereas the demand for remanufactured products increases in all four cases, which are in accord with the propositions in Section 4. (2) Compared to decentralized decision making, the effects of the yield rate on the demand for new and remanufactured products with centralized decision making are greater. Especially, the increase in the demand for remanufactured products is more evident. (3) Under cap-and-trade regulations, the demand for new and remanufactured products is less than that without a constraint on carbon emissions. However, the effects on the demand for new products are greater than those on remanufactured products. This trend occurs because the carbon emissions generated by manufacturing new products are larger than those generated by remanufactured products.Figure3(a) shows the sales price for remanufactured products decreases as yield rate increases. However, the magnitude of the decrease with centralized decision making is more evident than that with decentralized decision making. This finding is explained by the fact that a high yield rate implies a low remanufacturing cost, which allows the TPR to lower its sales price. Under cap-and-trade regulations, the sales price is higher than that without a constraint on carbon emissions. This occurs because cap-and-trade regulations cause an increase of the TPR’s remanufacturing cost. Figure 3(b) indicates that in all four cases, acquisition price first increases and then decreases as yield rate increases. This occurs because at the beginning, as yield rate increases, the demand for remanufactured products increases. However, when yield rate reaches a threshold, the demand for remanufactured products and acquisition price for used products reach the maximum since the TPR can collect enough used products at a low acquisition price to satisfy the demand for remanufactured products. As shown in Figure 3(b), with centralized decision making, the acquisition price clearly varies, but with decentralized decision making, the price almost maintains a stable level with respect to yield rate. And the aforementioned threshold of yield rate with centralized decision making is higher than that with decentralized decision making. This implies that compared to decentralized decision making, centralized decision making urges the TPR to improve yield rate and achieve more environmental benefits. As regards the constraint on carbon emissions, the acquisition price under cap-and-trade regulations is relatively lower, which indicates that cap-and-trade regulations can provide a stronger incentive for TPRs to further collect used products owning to a low price.As evident from Figure4, regardless of a constraint on carbon emissions or not, royalty rate decreases as the yield rate increases, but decreases more when yield rate is low. Compared to the case without a constraint on carbon emissions, the royalty rate is lower under cap-and-trade regulations, which means the implementation of cap-and-trade regulations can motivate the OEM to reduce the royalty rate. As a result, the TPR benefits from remanufacturing with a low royalty fee. In addition, the increase in yield rate increases the demand for remanufactured products, for which the OEM still can maintain a high total royalty fee, thereby forming a virtuous cycle between the OEM and the TPR.In Figure5, the profit of the OEM and the TPR increases as yield rate increases regardless of the presence of a constraint on carbon emissions. This finding suggests that improving yield rate is a satisfactory measure to increase the profits of the OEM and the TPR. Figure 5 further illustrates that the profit under cap-and-trade regulations is higher than that without the constraint on carbon emissions. However, this result depends on the size of the carbon emissions cap that the government allocates to the TPR and the OEM. If the carbon emissions cap is not sufficiently high, then the profit under cap-and-trade regulations may be even lower than that without a constraint on carbon emissions.Figure6 demonstrates that the total profit of the entire supply chain increases in all four cases. Under cap-and-trade regulations, the total profit is higher than that in the case without the constraint on carbon emissions, which indicates the implementation of cap-and-trade regulations can improve the supply chain’s profits. Moreover, the total profit with centralized decision making is higher than that with decentralized decision making. Figure 7 shows the difference in the total profit with centralized and decentralized decision making (i.e., ∏s∗∗−∏2m∗+∏2r∗, which we denote as ∆∏s) with respect to yield rate. Overall, the difference increases with respect to yield rate. Consequently, the higher the yield rate is, the larger the effects of centralized decision making on the total profit are. However, the increase under cap-and-trade regulations is less than that without a constraint on carbon emissions.


## 5.3. Effects of WTP on Optimal Decision Making

Similar to Section5.2, we set γ = 0.8 and plot a series of figures reflecting the effects as follows.Figure8 illustrates that regardless of cap-and-trade regulations or a lack thereof, the demand for new products decreases, whereas the demand for remanufactured products increases as WTP increases. This result matches what is found in practice. It is noteworthy that the decrease in the demand for new products and the increase in the demand for remanufactured ones with centralized decision making are more substantial than that in the case with decentralized decision making. This result signifies that the effects of decision-making approach on the demand for new and remanufactured products are more significant. In addition, under cap-and-trade regulations, the demand for new products is always lower than that in that case without a constraint on carbon emissions. Accordingly, the implementation of cap-and-trade regulations can motivate the TPR to remanufacture more used products by taking full advantage of the low carbon emissions.Figure 8
(a) Manufacturing quantity/demand for new products and (b) remanufacturing quantity/demand for remanufactured products vs. WTP.
(a)(b)Figure9(a) indicates that as WTP increases, the sales price for remanufactured products increases rapidly in all four cases. The difference among the four cases is not highly significant. This suggests that decision-making approach and carbon emission regulations do not substantially affect remanufactured products’ sales price with respect to WTP. Figure 9(b) illustrates that the acquisition price also increases with WTP in all four cases. However, the increases are more apparent with centralized than with decentralized decision making. With respect to WTP, the effect of cap-and-trade regulations on acquisition price is negligible.Figure 9
(a) Sales price for remanufactured products and (b) acquisition price for used products vs. WTP.
(a)(b)Figure10 shows that the royalty rate increases with WTP in Case 1 and Case 2. The reason is because an increase in WTP makes remanufactured products more competitive in the market, which in turn implies that the TPR will own more market share. To respond to this threat, the OEM will increase the royalty rate, which is in accord with Proposition 3.Figure 10
Royalty rate vs. WTP.As seen in Figure11, with the increase of WTP, both the OEM and the TPR profits increase with or without the constraint of cap-and-trade regulations. However, under cap-and-trade regulations, the profit is always higher. This indicates the implementation of cap-and-trade regulations is helpful not only for the OEM but also for the TPR.Figure 11
Profit of (a) the OEM and (b) the TPR vs. WTP.
(a)(b)Figure12 shows that as WTP increases, the total profit of the entire supply chain increases in all four cases, but increases more with centralized decision making. This result declares that centralized decision making is a more economical approach to the supply chain compared to decentralized decision making.Figure 12
Total profit of the entire supply chain vs. WTP.


## 6. Conclusions and Future Research

In this paper, we study the effects of cap-and-trade regulations on the optimal decisions for an OEM and an authorized TPR in a two-echelon CLSC. In this proposed CLSC, the OEM only manufactures new products but no remanufactured products in scenario 1, and in scenario 2 the OEM still produces new products but competes with an authorized TPR. This authorized TPR collects and remanufactures used products with the patent licensing from the OEM. In this context, we investigate the optimal operational decisions of both parties with decentralized and centralized decision making under cap-and-trade regulations in a Stackelberg model.The results indicate the following. (1) The implementation of carbon cap-and-trade regulations causes lower royalty rate and less manufacturing quantity, but higher sales prices for new and remanufactured products. Cap-and-trade regulations are helpful not only for the OEM but also for the TPR. (2) The optimal operational decisions of the OEM and the TPR are affected by the trading price of carbon emissions permits and their carbon emissions caps allocated by the government. Whether the TPR accepts authorization remanufacturing or not depends on the ratio of carbon emission cap to carbon emissions caused by producing remanufactured product. (3) With centralized decision making, the total profit of the entire supply chain can be improved. In this situation, the acquired quantity of the used products collected by TPRs is more considerable and the consumers can buy remanufactured products at lower prices than those with decentralized decision making. (4) As yield rate and WTP increase, total profit increases. Furthermore, the profit is highly sensitive to WTP. Therefore, to improve their benefits, TPRs can prioritize increasing customers’ WTP and subsequently improving yield rate.This study, however, has some limitations. First, other carbon emission regulations are not considered. Extending the current work and investigating how other regulations affect decisions and the differences among them presents a worthwhile concern. Second, a deterministic yield rate is assumed in this paper. More practical implications can perhaps be obtained by setting a stochastic yield rate. Finally, in this study, we considered the demand in a deterministic case; extending this study to a stochastic case presents another future research direction.



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*Source: 1864641-2020-07-22.xml*