Table of Contents Table of Contents
Previous Page  165 / 330 Next Page
Information
Show Menu
Previous Page 165 / 330 Next Page
Page Background

臺大管理論叢

27

卷第

2

165

its usage by an ordinary manufacturer, e.g., most composite material products and

construction wastes (The Economist, 2002). For example, cost savings from procuring

EDRMs may not be proportionate to quality loss or degeneration in the final product. While

supply source is constantly unsteady and unsecure, EDRMs also suffer from indefinite

delivered quantity and possibly high acquisition costs. Furthermore, unlike virgin materials,

EDRMs usually have limited applications, are consumed in small amounts, and account for

only a fraction of the entire bill of materials; hence they are often not prioritized in material

usage. Owing to the challenges, previous literature leaves space for our improvement in

addressing the issues of a closed-loop supply chain for EDRMs. The following research

questions are addressed: How can a EDRM supply chain be sustainable without artificially

enforcing the minimum content of EDRM in the final products? When will a EDRM closed-

loop supply chain sustain without government intervention?

Our outcomes suggest that a simple subsidy mechanism in cost-based taxing (Dobbs,

1991) can encourage a manufacture to employ more EDRMs. We suggest that governments

should get involved in recycling such profitless materials. The manufacturers can therefore

rely on the decisions of both governments and EDRM suppliers in determining the

production amount of green products.

2. Related Literature

Although managerial topics in material recovery have been studied extensively, most

studies ignore the heterogeneity in material characteristics and underestimate the difficulty in

recycling certain kinds of materials. For instance, closed-loop systems are limited to

investigating the interaction between members such as manufacturers and retailers, in

dealing with end-of-life product collection, but supply chain behavior caused by material

heterogeneity and economic market viability is disregarded (The Economist, 2002).

Because of the low economic value and inferior channel power, EDRMs behave

differently in conventional economic instruments. Poor handling of EDRMs discourages the

industry from collecting these materials. Consequently, based on the GSCM concepts

proposed by Majumder and Groenevelt (2001), Ferrer and Swaminathan (2006), and Sheu

and Talley (2011), this paper investigates how economic instruments and product quality loss

dictate the aggregate decisions of key members in a green supply chain in the strategic

planning domain.

The gaps in existing research present a research opportunity for the current study, which

concerns the use of recycled materials in the industrial market rather than in the consumer