We encountered five recent cases in
supply chain risk management that applied multiple criteria
analysis models to supply chain risk management decisions. We
present value analysis and SMART models, using the contexts of the
other studies as a basis. We have simplified the longer models with
the intent of presenting the essence of the decision context, while
demonstrating value analysis. In this chapter we review these five
cases, which usually applied analysis to evaluate alternative
suppliers, either relatively as sources of various types of risk,
or in a selection decision.
Case 1: Ȍztűrk and Ȍzḉelik (2014) 1
This study focused on a method to
identify suppliers with emphasis on sustainable awareness. They
utilized the triple bottom line paradigm, considering
sustainability along with social and financial aspects. These
authors used TOPSIS, 2 which has the relative advantage
over SMART of being applicable to large numbers of alternatives.
But the treatment of criteria, weights, and scores is common to
TOPSIS and SMART. They also used fuzzy modeling, and a group
context, but since they converted fuzzy input to crisp numbers and
used a group decision set of preferences, the method works the same
once numbers are modified. Based on the data provided in their
paper, we can infer the following risk order. We provided specific
swing weights in Table 4.1:
Table
4.1
Case 1 Weights
Risk
|
Rank
|
Based on 1st
|
Weight
|
---|---|---|---|
ECON1: Costs
|
1–3
|
100
|
0.127
|
ECON2: Quality
|
1–3
|
100
|
0.127
|
SOC2: Social responsibility
|
1–3
|
100
|
0.127
|
ECON3: Lead time/on-time delivery
|
4–5
|
90
|
0.115
|
ENV2: Resource consumption
|
4–5
|
90
|
0.115
|
ENV1: Pollution control
|
6
|
75
|
0.096
|
SOC4: Employment practices
|
7
|
60
|
0.076
|
ENV3: Green product and eco-design
|
8
|
50
|
0.064
|
ECON4: Technology capability
|
9
|
40
|
0.051
|
SOC1: Health and safety practices
|
10
|
30
|
0.038
|
ENV4: Environmental management system
|
11–12
|
25
|
0.032
|
SOC3: Education infrastructure
|
11–12
|
25
|
0.032
|
Total
|
785
|
1.000
|
Scores for suppliers (which we made up)
on each criterion are given below, along with resultant value
scores in Table 4.2:
Table
4.2
Case 2 Scores
Criteria
|
Weights
|
Supplier1
|
Supplier2
|
Supplier3
|
---|---|---|---|---|
ECON1: Costs
|
0.127
|
0.200
|
0.600
|
0.950
|
ECON2: Quality
|
0.127
|
0.900
|
0.800
|
0.600
|
SOC2: Social responsibility
|
0.127
|
0.600
|
0.850
|
0.400
|
ECON3: Lead time/on-time delivery
|
0.115
|
0.800
|
0.600
|
0.500
|
ENV2: Resource consumption
|
0.115
|
0.300
|
0.800
|
0.650
|
ENV1: Pollution control
|
0.096
|
0.850
|
0.950
|
0.500
|
SOC4: Employment practices
|
0.076
|
0.700
|
0.850
|
0.300
|
ENV3: Green product and eco-design
|
0.064
|
0.950
|
0.900
|
0.800
|
ECON4: Technology capability
|
0.051
|
0.850
|
0.700
|
0.800
|
SOC1: Health and safety practices
|
0.038
|
0.800
|
0.950
|
0.350
|
ENV4: Environmental management system
|
0.032
|
0.800
|
0.900
|
0.350
|
SOC3: Education infrastructure
|
0.032
|
0.950
|
0.850
|
0.650
|
Value
scores
|
0.688
|
0.788
|
0.588
|
Supplier 1 has stronger characteristics
with respect to quality, environmental issues and safety, but is
expensive. Supplier 2 has good quality, moderate risk and moderate
cost. Supplier 3 has lower quality, higher risk, and lowest cost.
With this set of scores and one particular set of weights, supplier
2, who emphasizes quality, has the highest score. Value analysis
provides a means to utilize these scores to identify areas of
potential improvement.
Value Analysis
Here Supplier 1 clearly is deficient
relative to cost and resource consumption. Supplier 2 is relatively
strong on everything, but if Supplier 1 vastly improved cost and
resource consumption, it could outrank Supplier 2. Supplier 3 is
weak on a number of social and environmental factors.
Case 2: Samvedi, Jain and Chan (2013) 3
This study applied fuzzy AHP and TOPSIS
to a model to assess risk for a supply chain. Thus it did not
involve a specific decision, but rather was meant to provide a
metric for evaluation of overall supply chain risk. They had four
top-level categories of risk {supply risk, demand risk, process
risk, and environmental risk by which they included political
environment}. The methodology, as in Case 1, could be applied to
evaluation of suppliers as well. Table 4.3 gives criteria and
shows weight generation, using Samvedi et al. general criteria
ranking and our own specific values.
Table
4.3
Case 2 Weights
Risk
|
Rank
|
Based on 1st
|
Weight
|
---|---|---|---|
Env3: Natural disasters
|
1
|
100
|
0.184
|
Env4: Economic downturns
|
2
|
67
|
0.123
|
Dem1: Sudden demand fluctuation
|
3
|
54
|
0.099
|
Env2: Political instability
|
4
|
42
|
0.077
|
Dem2: Market changes
|
5
|
41
|
0.075
|
Sup4: Sudden hike in costs
|
6
|
36
|
0.066
|
Env1: Terrorism
|
7
|
30
|
0.055
|
Sup1: Outsourcing risks
|
8
|
29
|
0.053
|
Dem4: Forecasting errors
|
9–10
|
27
|
0.050
|
Sup2: Supplier insolvency
|
9–10
|
27
|
0.050
|
Proc1: Machine failure
|
11
|
20
|
0.037
|
Sup3: Supply quality
|
12
|
16
|
0.029
|
Proc3: Quality problems
|
13
|
15
|
0.028
|
Dem3: Competition change
|
14
|
14
|
0.026
|
Proc2: Labor strike
|
15
|
11
|
0.020
|
Proc4: Technological change
|
16
|
8
|
0.015
|
Env5: Social & cultural
grievances
|
17
|
7
|
0.013
|
Total
|
544
|
Table 4.4 shows scores for three
suppliers the might be evaluated. Supplier 1 might be a high
quality, high cost alternative, Supplier 2 a bit inferior to
Supplier 1 on cost but higher on quality, and Supplier 3 located in
a higher risk area.
Table
4.4
Case 2 Scores
Risk
|
Weights
|
Supplier1
|
Supplier2
|
Supplier3
|
---|---|---|---|---|
Env3: Natural disasters
|
0.184
|
0.70
|
0.80
|
0.30
|
Env4: Economic downturns
|
0.123
|
0.60
|
0.50
|
0.20
|
Dem1: Sudden demand fluctuation
|
0.099
|
0.70
|
0.90
|
0.10
|
Env2: Political instability
|
0.077
|
0.95
|
0.80
|
0.20
|
Dem2: Market changes
|
0.075
|
0.70
|
0.80
|
0.40
|
Sup4: Sudden hike in costs
|
0.066
|
0.50
|
0.70
|
0.30
|
Env1: Terrorism
|
0.055
|
0.80
|
0.50
|
0.10
|
Sup1: Outsourcing risks
|
0.053
|
1.00
|
1.00
|
0.30
|
Dem4: Forecasting errors
|
0.050
|
0.70
|
0.80
|
0.40
|
Sup2: Supplier insolvency
|
0.050
|
0.60
|
0.80
|
0.30
|
Proc1: Machine failure
|
0.037
|
0.90
|
0.95
|
0.50
|
Sup3: Supply quality
|
0.029
|
0.90
|
1.00
|
0.40
|
Proc3: Quality problems
|
0.028
|
0.95
|
1.00
|
0.50
|
Dem3: Competition change
|
0.026
|
0.80
|
0.90
|
0.50
|
Proc2: Labor strike
|
0.020
|
0.80
|
0.40
|
0.50
|
Proc4: Technological change
|
0.015
|
0.70
|
0.50
|
1.00
|
Env5: Social & cultural
grievances
|
0.013
|
0.70
|
0.60
|
0.20
|
Value
scores
|
0.735
|
0.765
|
0.296
|
The value score can be used to rank
suppliers. Here Supplier 2 is better than Supplier 1, and both are
radically better than Supplier 3.
Value Analysis
The score matrix in Table 4.4 is fairly clear on
relative advantages, as always. The best performance is indicated
by bold scores. Supplier 2 is safest on natural disaster, demand
fluctuation, market change, and cost hikes. Supplier 1 has
advantage on economic stability, political stability, and
anti-terrorism program. Supplier 3 is relatively inferior except
for the ability to adapt to technological change. Furthermore, this
set of criteria focused on risk, without emphasis on cost
advantage. Suppliers usually can’t do much about these types of
risks—they are inherent in location. It is possible that such risks
might be valuable to consider in site location decisions.
Case 3: Onat, Gumus, Kucukvar and Tatari (2006) 4
This study used TOPSIS and
intuitionist fuzzy multi-criteria decision making modeling to
evaluate alternative vehicle technologies. They compared seven
types of vehicles with 16 criteria (using the triple bottom line
paradigm of economic, social, and environmental) as in Table
4.5:
Table
4.5
Case 3 Weight development
Criteria
|
Rank
|
Based on 1st
|
Weight
|
---|---|---|---|
Env7: Total GHG emissions
|
1–2
|
100
|
0.084
|
Env9: Water withdrawal
|
1–2
|
100
|
0.084
|
Env8: Total energy consumption
|
3
|
99
|
0.083
|
Soc1: Employment
|
4
|
96
|
0.081
|
Soc3: Injuries
|
5
|
85
|
0.072
|
Econ1: Foreign Purchases
|
6–9
|
79
|
0.066
|
Econ3: GDP
|
6–9
|
79
|
0.066
|
Env5: Carbon fossil fuel
|
6–9
|
79
|
0.066
|
Env6: Carbon electricity
|
6–9
|
79
|
0.066
|
Env3: Forestry
|
10
|
74
|
0.062
|
Env4: Cropland
|
11–12
|
68
|
0.057
|
Env10: Hazard waste
|
11–12
|
68
|
0.057
|
Soc2: Tax
|
13
|
63
|
0.053
|
Econ2: Profit
|
14
|
58
|
0.049
|
Env2: Grazing
|
15
|
48
|
0.04
|
Env1: Fishery
|
16
|
13
|
0.011
|
Total
|
1188
|
The seven vehicle types were:
-
Internal combustion vehicles (ICV)
-
Hybrid electric vehicles (HEV)
-
Plug-in electric range 10 miles (P10)
-
Plug-in electric range 20 miles (P20)
-
Plug-in electric range 30 miles (P30)
-
Plug-in electric range 40 miles (P40)
-
Battery elective vehicles (BEV)
Table 4.6 gives scores and shows
value calculations:
Table
4.6
Case 3 scoring
Weight
|
ICV
|
HEV
|
P10
|
P20
|
P30
|
P40
|
BEV
|
|
---|---|---|---|---|---|---|---|---|
Env7
|
0.084
|
1.00
|
.40
|
.30
|
.25
|
.30
|
.35
|
.70
|
Env9
|
0.084
|
.40
|
.30
|
.60
|
.70
|
.80
|
.90
|
1.00
|
Env8
|
0.083
|
.90
|
.40
|
.50
|
.60
|
.70
|
.80
|
.85
|
Soc1
|
0.081
|
.60
|
.58
|
.40
|
.45
|
.50
|
.70
|
.90
|
Soc3
|
0.072
|
.70
|
.75
|
.50
|
.55
|
.65
|
.75
|
.80
|
Econ1
|
0.066
|
.50
|
.40
|
.34
|
.30
|
.32
|
.36
|
.38
|
Econ3
|
0.066
|
.40
|
.38
|
.30
|
.36
|
.37
|
.39
|
.60
|
Env5
|
0.066
|
.60
|
.40
|
.38
|
.34
|
.34
|
.34
|
.50
|
Env6
|
0.066
|
.60
|
.50
|
.35
|
.37
|
.40
|
.48
|
.70
|
Env3
|
0.062
|
.40
|
.45
|
.30
|
.35
|
.60
|
.70
|
.90
|
Env4
|
0.057
|
.60
|
.50
|
.40
|
.45
|
.55
|
.65
|
.80
|
Env10
|
0.057
|
1.00
|
.60
|
.40
|
.30
|
.25
|
.20
|
.10
|
Soc2
|
0.053
|
.80
|
.70
|
.60
|
.50
|
.40
|
.30
|
.35.
|
Econ2
|
0.049
|
.60
|
.55
|
.50
|
.53
|
.70
|
.75
|
.90
|
Env2
|
0.040
|
.70
|
.70
|
.50
|
.60
|
.60
|
.65
|
.70
|
Env1
|
0.011
|
.60
|
.55
|
.40
|
.55
|
.60
|
.70
|
.90
|
Value
|
0.652
|
0.493
|
0.421
|
0.443
|
0.501
|
0.564
|
0.677
|
Value Analysis
In this case, there were clear
distinguishing performance scores, and each of the alternatives has
some compensating advantage. There were quite a few criteria. While
it is often best to focus on fewer criteria, if there are a number
of measurable items falling into clear categories, as is the case
here, it can work. In this case criterion Env1 (related to
fisheries) there is very little impact, and in fact the small
weight of 0.011 is further minimized by the range of scores of the
seven alternatives (0.4–0.9).
Alternative BEV scores highest, and is
best on many metrics, weak on hazardous waste, tax, and foreign
purchases. Alternative ICV is very close to BEV in weighted score,
with strenchts in GHG emission, hazardous waste, and energy
consumption while having slight weakness on water withdrawal and
GDP impact. The HEV vehicle has few strengths, although it is best
on grazing impact, which has a low weight. The plug-ins are best on
nothing, although none are dominated (as often is the case with
many criteria). As to value analysis, looking at weaknesses
provides guidance for design improvement for any of the
alternatives.
Case 4: Infante, de Mendonḉa, Purcidinio and Valle (2013) 5
This study used ELECTRE multi-criteria
decision making modeling to evaluate oil and gas companies, again
using the triple bottom line. They compared the biggest five global
oil and gas companies with two economic, ten environmental, and
three social criteria as in Table 4.7:
Table
4.7
Infante et al. criteria
Criteria
|
|||
---|---|---|---|
Econ1
|
Total production
|
Economic value/day
|
Max
|
Econ2
|
Investment impact
|
qualitative
|
Max
|
Env1
|
Direct energy consumption
|
Barrels/year
|
Min
|
Env2
|
Water withdrawal
|
Barrels/year
|
Min
|
Env3
|
Greenhouse gas emission
|
Tons/barrel/year
|
Min
|
Env4
|
Indirect greenhouse gas emission
|
Tons/barrel/year
|
Min
|
Env5
|
Sulpher oxide emission
|
Tons/barrel/year
|
Min
|
Env6
|
Nitrous oxide emission
|
Tons/barrel/year
|
Min
|
Env7
|
Water discharge
|
Volume & quality
|
Min
|
Env8
|
Waste
|
Tons/barrel/year
|
Min
|
Env9
|
Spill volume
|
Volume
|
Min
|
Env10
|
Expenditure—environmental protection
|
Dollar/barrel/year
|
Max
|
Soc1
|
Workforce employed
|
Employees
|
Max
|
Soc2
|
Work-related deaths
|
Deaths/employee
|
Min
|
Soc3
|
Work-related illness
|
Rate/hour
|
Min
|
Infante et al. evaluated firms over
time, with scores provided for each year from 2005 through 2010. We
will base our scores to reflect 2010 numbers in their data. The
matrix of scores for each criterion by option are given below,
along with calculation of overall value score. Table 4.8 shows input measures
from the original article:
Table
4.8
Case 4 Measures
q
|
p
|
PetroB
|
BP
|
RDS
|
ExMob
|
Chev
|
|
---|---|---|---|---|---|---|---|
Econ1
|
0.207
|
0.413
|
1.956
|
3.499
|
1.793
|
3.980
|
2.616
|
Econ2
|
0.253
|
0.507
|
5
|
3
|
2
|
5
|
2
|
Env1
|
42.372
|
72.831
|
756.832
|
706.766
|
895.208
|
929.227
|
1002.963
|
Env2
|
39.322
|
71.767
|
255.085
|
221.129
|
498.953
|
195.662
|
286.909
|
Env3
|
12.610
|
24.439
|
82.390
|
89.247
|
124.973
|
91.065
|
49.147
|
Env4
|
3.080
|
6.097
|
1.334
|
6.025
|
22.345
|
11.727
|
8.949
|
Env5
|
23.365
|
44.129
|
196.139
|
56.743
|
302.825
|
126.586
|
136.751
|
Env6
|
18.390
|
35.578
|
319.702
|
130.055
|
250.98
|
96.311
|
131.620
|
Env7
|
41.967
|
77.967
|
264.318
|
57.400
|
438.226
|
156.468
|
309.987
|
Env8
|
78.333
|
152.598
|
663.428
|
325.166
|
2311.411
|
417.909
|
193.904
|
Env9
|
44.993
|
82.034
|
404.551
|
204.825
|
449.155
|
172.132
|
268.284
|
Env10
|
191626
|
383251
|
1459916
|
1870477
|
5161248
|
3192585
|
2023640
|
Soc1
|
3113.581
|
6311.123
|
72088.4
|
86460
|
90045
|
81300
|
58712
|
Soc2
|
0.022
|
0.045
|
0.143
|
0.006
|
0.087
|
0.047
|
0.062
|
Soc3
|
0.066
|
0.138
|
0.597
|
0.354
|
0.720
|
0.324
|
0.318
|
Infante et al. utilized equal weights,
and then demonstrated sensitivity to weights in some variants.
Based on ELECTRE approaches, scores were generated in one of the
metrics that method offers, with a score of 0 below some minimum (a
q parameter) and 1 at or above some maximum (a p parameter). The
scores in Table 4.9 reflect a linear formulation for input
measures between q and p.
Table
4.9
Case 4 Scores
PetroB
|
BP
|
RDS
|
ExMob
|
Chev
|
|
---|---|---|---|---|---|
Econ1
|
0.489
|
0.875
|
0.448
|
0.995
|
0.654
|
Econ2
|
1
|
0.5
|
0.25
|
1
|
0.250
|
Env1
|
0.811
|
0.977
|
0.349
|
0.236
|
0
|
Env2
|
0.816
|
0.930
|
0.003
|
1
|
0.710
|
Env3
|
0.537
|
0.439
|
0
|
0.413
|
1
|
Env4
|
0.933
|
0.699
|
0
|
0.414
|
0.553
|
Env5
|
0.415
|
0.973
|
0
|
0.694
|
0.653
|
Env6
|
0
|
0.850
|
0.245
|
1
|
0.842
|
Env7
|
0.388
|
0.979
|
0
|
0.696
|
0.257
|
Env8
|
0.743
|
0.930
|
0
|
0.879
|
1
|
Env9
|
0.318
|
0.984
|
0.169
|
1
|
0.772
|
Env10
|
0
|
0.106
|
1
|
0.484
|
0.150
|
Soc1
|
0.442
|
0.729
|
0.801
|
0.626
|
0.174
|
Soc2
|
0
|
0.940
|
0.130
|
0.530
|
0.380
|
Soc3
|
0.258
|
0.865
|
0
|
0.940
|
0.955
|
Infante et al. utilized equal weights,
with weight changes representing sensitivity analysis. Table
4.10 shows
results for various combinations of weights. The first set of
weights divides 1/3rd by the number of criteria within each
category, yielding weights of 0.167 for economic factors, 0.033 for
environmental factors, and 0.111 for social factors. The second row
assigns each of the 15 criteria a weight of 0.067, which is equal
for all, but biases analysis toward environmental factors because
there are ten measures as opposed to two or three. The last three
rows show relative emphasis on economic, environmental, and social
factors in turn. Highest value function for each oil company is
identified in bold:
Table
4.10
Results for weight combinations
Econ
|
Env
|
Soc
|
PB
|
BP
|
RDS
|
ExMob
|
Chev
|
---|---|---|---|---|---|---|---|
0.167
|
0.033
|
0.011
|
0.490
|
0.770
|
0.280
|
0.795
|
0.515
|
0.067
|
0.067
|
0.067
|
0.477
|
0.785
|
0.230
|
0.735
|
0.558
|
0.444
|
0.011
|
0.033
|
0.668
|
0.712
|
0.328
|
0.937
|
0.471
|
0.050
|
0.080
|
0.033
|
0.494
|
0.782
|
0.211
|
0.724
|
0.571
|
0.050
|
0.011
|
0.267
|
0.311
|
0.824
|
0.302
|
0.729
|
0.508
|
When economic factors are emphasized,
Exxon Mobil performed well in 2011. When environmental factors
received heaviest weight, BP did best (possibly in response to Gulf
of Mexico oil spill history). BP also did well when social factors
were emphasized, again possibly explicable in light of recent
history. Infante et al. did a commendable job in looking at annual
performances. Here our point is to demonstrate use of multiple
criteria models, in this case as a performance measure.
Value Analysis
This example provided more concrete
alternatives, making the comparison potentially clearer. The clear
winner was to outsource production of finished goods to China. Of
course, there are many Chinese manufacturers, so a more focused
analysis might be required to select specific vendors.
All of the options considered had
equivalent scores on ANSI compliance. That does not diminish the
importance of this criterion, but for this set of alternatives,
this factor does not bear on the decision. All other criteria
distinguished among the available choices to some degree.
The recommended source had some
relative weaknesses. Transportation risk is something that might
not be able to be improved a great deal, due to geographic
location. This also plays a role in relative scores for most of the
other criteria where this alternative had relative disadvantage.
But China’s relative advantages in cost, quality, and fulfillment
performance gave it a strong advantage in this analysis.
The second highest value score came
from obtaining parts in China, and assembling in existing
facilities in Mexico. The scores indicate relative advantages in
reducing supplier fulfillment risk and wrong partner risk. This
alternative had the greatest room for improvement in transportation
risk management, order fulfillment risk, and on-time delivery. It
also scored relatively low on a number of other criteria that had
low weights, and thus are less important to improve in this
specific decision.
Outsourcing to Mexico was next in
value score. This alternative was quite weak in cost, the most
important criterion, and average on the second most important
criterion of product quality. These clearly would be areas calling
for improvement. Constructing the new facility clearly has a high
cost impact, giving use of existing Mexican facilities more
attractive in this case.
Case 5: Gaudenzi and Borghesi (2006) 6
This application used AHP in the style
of a business scorecard. While the authors gave a good discussion
of criteria and its components, the data they provide for relative
weights referred only to the top level factors of On-time delivery,
completeness, correctness, and damage/defect free products. They
also gave examples demonstrating scoring of departments within the
organization on each of these four criteria by managerial
subjective assessment, as well as using a more metric-driven model.
Furthermore, they gave ranges for relative weight importance (which
could be used for alternative multicriteria models 7 such as
HIPRE). 8
In this study, data for relative
criteria importance was given in ranges. We present the extremes
below in development of SMART weights in Table 4.11:
Table
4.11
Case 5 Weight development
Criteria
|
Mean
|
weights
|
Extreme1
|
weights
|
Extreme2
|
Weights
|
---|---|---|---|---|---|---|
On-time delivery
|
100
|
0.317
|
100
|
0.402
|
50
|
0.215
|
Completeness
|
90
|
0.286
|
66
|
0.265
|
100
|
0.429
|
Correctness
|
75
|
0.238
|
50
|
0.201
|
50
|
0.215
|
Damage-defect free
|
50
|
0.159
|
33
|
0.133
|
33
|
0.142
|
315
|
249
|
233
|
The last two criteria have fairly
consistent weights, so we chose weight of 0.21 for Correctness and
0.14 for Damage-defect free products. The first two had quite a
range, as each extreme had a different first selection. Using the
maximum weight for the first and subtracting 0.35 as the weight for
the third and fourth ranked criteria, weights were generated. Using
on-time delivery as the most important criteria yielded a weight
for completeness outside the extreme weights, so we raised that
weight to 0.29, lowering the weight for on-time delivery to 0.36.
No adjustment was necessary to keep weights within range for the
set of weights assigning completeness the greatest weight as shown
in Table 4.12:
Table
4.12
Case 5 Weights
Criteria
|
On-time first
|
Completeness first
|
---|---|---|
On-time delivery
|
0.36
|
0.22
|
Completeness
|
0.29
|
0.43
|
Correctness
|
0.21
|
0.21
|
Damage-defect free
|
0.14
|
0.14
|
Gaudenzi and Borghesi gave two sets of
scores to evaluate risks within their departments. Scores based on
managerial input as well as a model used by Gaudenzi and Borghesi
are demonstrated with both sets of weights generated above. Scores
here are presented in a positivist perspective, with 1.0
representing the best performance. Therefore low resulting scores
are associated with the most problematic departments.
The first set of value scores reflect
weights emphasizing on-time delivery, with manager subjective
scores shown in Table 4.13:
Table
4.13
Case 5 Value calculation with subjective
scores
weights
|
Procurement
|
Warehouse
|
OrderCycle
|
Manufact.
|
Trans.
|
|
---|---|---|---|---|---|---|
On-time delivery
|
0.36
|
0
|
0.5
|
1
|
0.5
|
0
|
Completeness
|
0.29
|
0
|
0.5
|
1
|
1
|
1
|
Correctness
|
0.21
|
1
|
1
|
1
|
1
|
0.5
|
Defect free
|
0.14
|
0.5
|
1
|
1
|
1
|
0
|
Value
scores
|
0.28
|
0.675
|
1
|
0.82
|
0.395
|
The scores themselves highlight where
risks exist (0 indicates high risk, 0.5 medium level risk). The
value scores give something that could be used to assess overall
relative performance by department. Order cycle has no problems, so
it has to score best. Manufacturing seems to have their risks well
under control. Procurement and transportation departments are more
troublesome.
The second set uses the same weights,
but scores based on model inputs (see Table 4.14):
Table
4.14
Case 5 Value calculation with model
inputs
Weights
|
Procurement
|
Warehouse
|
OrderCycle
|
Manufact.
|
Trans.
|
|
---|---|---|---|---|---|---|
On-time delivery
|
0.36
|
0
|
0
|
1
|
0.5
|
0
|
Completeness
|
0.29
|
0
|
0
|
1
|
1
|
1
|
Correctness
|
0.21
|
1
|
1
|
0.5
|
1
|
0.5
|
Defect free
|
0.14
|
1
|
0.5
|
1
|
1
|
0
|
Value
scores
|
0.35
|
0.28
|
0.895
|
0.82
|
0.395
|
The implications are similar, except
that the warehousing department shows up as facing much more
risk.
We can repeat the analysis using
weights emphasizing completeness. Using managerial subjective
scores (Table 4.15):
Table
4.15
Case 5 Value calculations emphasizing
completeness and subjective scores
Weights
|
Procurement
|
Warehouse
|
OrderCycle
|
Manufact.
|
Trans.
|
|
---|---|---|---|---|---|---|
On-time delivery
|
0.22
|
0
|
0.5
|
1
|
0.5
|
0
|
Completeness
|
0.43
|
0
|
0.5
|
1
|
1
|
1
|
Correctness
|
0.21
|
1
|
1
|
1
|
1
|
0.5
|
Defect free
|
0.14
|
0.5
|
1
|
1
|
1
|
0
|
Value
scores
|
0.28
|
0.675
|
1
|
0.89
|
0.535
|
This set of weights gives the
transport department a better performance rating, but otherwise
similar performance to the earlier analysis.
Finally, we use the model scores for
weights emphasizing completeness (Table 4.16):
Table
4.16
Case 5 Value calculations emphasizing
completeness with model scores
weights
|
Procurement
|
Warehouse
|
OrderCycle
|
Manufact.
|
Trans.
|
|
---|---|---|---|---|---|---|
On-time delivery
|
0.22
|
0
|
0
|
1
|
0.5
|
0
|
Completeness
|
0.43
|
0
|
0
|
1
|
1
|
1
|
Correctness
|
0.21
|
1
|
1
|
0.5
|
1
|
0.5
|
Defect free
|
0.14
|
1
|
0.5
|
1
|
1
|
0
|
Value
scores
|
0.35
|
0.28
|
0.895
|
0.89
|
0.535
|
Here the warehouse department appears
to face the greatest risk, followed by the procurement
department.
The Guadenzi and Borghesi article
presents an interesting application of multiple criteria analysis
to something akin to business scorecard analysis, extending it to
provide a potential departmental assessment of relative degree of
risk faced.
Value Analysis
This application differs, because its
intent is to provide a balanced scorecard type of model. This can
be very useful, and interesting. But value analysis applies only to
hierarchical development, because Gaudenzi and Borghesi apply AHP
to performance measurement.
Conclusions
The cases presented here all applied
multiple criteria models. This type of model provides a very good
framework to describe specific aspects of risk and to assess where
they exist, as well as considering their relative performance. The
value scores might be usable as a means to select preferred
alternatives or as performance metrics. Through value analysis,
they can direct attention to features that call for the greatest
improvement.
Value analysis can provide useful
support to decision making by first focusing on hierarchical
development. In all five cases presented here, this was
accomplished in the original articles. Nonetheless, it is important
to consider over-arching objectives, as well as means objectives in
light of over-arching objective accomplishment.
Two aspects of value analysis should
be considered. First, if scores on available alternatives are
equivalent on a specific criterion, this criterion will not matter
for this set of alternatives. However, it may matter if new
alternatives are added, or existing alternatives improved. Second,
a benefit of value analysis is improvement of existing
alternatives. The score matrix provides useful comparisons of
relative alternative performance. If decision makers are not
satisfied with existing alternatives, they might seek additional
choices through expanding their search or designing them. The
criteria with the greatest weights might provide an area of search,
and the ideal scores provide a design standard.
Notes
- 1.
Ȍztűrk, B.A. and Ȍzḉelik, F. (2014). Sustainable supplier selection with a fuzzy multi-criteria decision making method based on triple bottom line. Business and Economics Research Journal 5(3), 129–147.
- 2.
Olson, D.L. (2005). Comparison of weights in TOPSIS models. Mathematical and Computer Modelling 40(7–8), 721–727.
- 3.
Samvedi, A., Jain, V. and Chan, F.T.S. (2013). Quantifying risks in a supply chain through integration of fuzzy AHP and fuzzy TOPSIS, International Journal of Production Research 51(8), 2433–2442.
- 4.
Onat, N.C., Gumus, S., Kucukvar, M. and Tatari, O. (2016). Application of the TOPSIS and intuitionistic fuzzy set approaches for ranking the life cycle sustainability performance of alternative vehicle technologies. Sustainable Production and Consumption 6, 12–25.
- 5.
Infante, C.E.D. de C., de Mendonḉa, F.M., Purcidonio, P.M. and Valle, R. (2013). Triple bottom line analysis of oil and gas industry with multicriteria decision making. Journal of Cleaner Production 52, 289–300.
- 6.
Gaudenzi, B. and Borghesi, A. (2006). Managing risks in the supply chain using the AHP method. The International Journal of Logistics Management 17(1), 114–136.
- 7.
Olson, D.L. (1996). Decision Aids for Selection Problems. New York: Springer.
- 8.
Mustajiki, J. and Hämäläinen, R.P. (2000). Web-HIPRE: Global decision support by value tree and AHP analysis, INFOR 38:3, 208–220; Geldermann, J., Bertsch, V., Treitz, M., French, S., Papamichail, K.N. and Hämäläinen, R.P. (2009). Multi-criteria decision support and evaluation of strategies for nuclear remediation management, Omega 37:1, 238–251.