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以綠色導向政策探討低經濟價值再生材料之回收供應鏈

168

improvement of product greenness. They are often strategic for the business and may not

apply to the maximum rationality in optimization. For example, the decision of EDRM

mixture

σ

is often driven by the procurement cost while the environmentally friendly product

design

ξ

is determined by the level of acceptance in the consumer market. On the other hand,

the ingredient mixture and product composition are costly in realizing frequent change. They

can take as given for the purpose of analysis in this paper.

To urge manufacturers to move toward GSCM, government agencies plan to apply

economic instruments – a pollution tax (denoted by

ϕ

for producing one unit of a

manufactured product) and a subsidy (denoted by ε for recycling one unit of an end-of-life

product) – to manufacturers in charge of manufacturing and end-of-life product recycling.

This study employs a variable rate tax, which depends on product eco-design or the level of

effluent

ξ

. Governments collect less tax if the product emits less effluent. In this study, the

amount of tax is linear to the effluent, that is,

ϕ

i

ξ

i

.

The game in the analysis is Stackelberg. The government acts as the first leader and the

two suppliers are the second leaders, and the manufacturers follow the actions. By above set

of game, the relationship among each player can then be readily induced. We begin modeling

the closed-loop supply chain by manufacturers’ profits:

π

mi

=

pq

i

– (

σ

xi

+

σ

yi

)

q

i

q

i

ϕ

i

ξ

i

q

i

, where

w

x

and

w

y

are the wholesale prices for manufacturer

i

for procuring a unit of

virgin and recycled materials, respectively, and

is the marginal cost of producing a unit

of products. The virgin-material supplier can determine its wholesale price

w

xi

to each

manufacturer and seek to maximize profit

π

x

=

σ

xi

q

i

c

x

σ

xi

q

i

, where

c

x

denotes the

marginal cost for generating a unit of virgin materials. The EDRM material supplier also

determines its wholesale price

to each manufacturer and seeks to maximize profit

π

y

=

q

i

c

h

h

i

c

u

(1-

η

)

h

i

+

, where

c

h

and

c

u

are the marginal costs of

collecting and final disposal of the waste.

We temporarily use a notation here and this one will be substituted by a new symbol

w

later for a simplification of notations. In response to the legislative requirements for the

input amount of EDRMs to produce a unit of product as well as the recycled-material supply

process, the system converts waste into usable materials, at which

σy

i

q

i

=

ηh

i

at a fixed

conversion rate η. Assuming a long-term flow balance condition in the closed-loop supply

chain, the

h

i

part in the profit of EDRM supplier can be replaced by

σy

i

q

i

/

η

.

The government’s optimal decisions with respect to the environmental taxes (

ϕ

) and

subsidies ( ) for managing recycled-material supply chain members are developed as the

Stackelberg first leader. Drawing from the concept of social welfare (SW) maximization