Methods · Ranking
SOWA (Spatial Ordered Weighted Averaging)
SOWA applies a different risk attitude, depending on the geographic zone alternatives sit in, when ranking them by criterion scores; the same table is assessed optimistically or pessimistically according to its zone.
Base method's data type: Classical
What Is the Method?
SOWA seeks an answer to the question "should alternatives in the same criterion table be assessed with a single risk attitude, or with a different attitude depending on the zone they sit in?" Its output is a score between 0 and 1 for every alternative and a ranking based on it. The method is used in geographic-information-system (GIS) based multi-criteria decisions: in work such as flood-risk mapping, land-use suitability, and urban water-infrastructure planning, risk perception can differ between zones. Makropoulos and Butler proposed it in 2006; it is a spatial extension of the standard OWA (Ordered Weighted Averaging) family.
The Philosophy Behind It
Standard OWA sorts criterion values from highest to lowest and weights them by rank. How these weights are distributed is itself a choice of attitude: if weight piles onto the highest value, the method is optimistic and looks at the alternative's strongest side; if it piles onto the lowest value, it is pessimistic and looks at its weakest side. Standard OWA holds this attitude fixed across the whole table. SOWA's difference begins here: it defines its own attitude for every zone.
An analogy makes this clear. Consider two separate assessors; one assesses buildings in a city centre by their best performance, because their infrastructure is strong, while the other assesses a rural area by its worst performance, because its infrastructure is weak. Both assessors can be right, because the zone's own conditions determine the risk attitude. SOWA's philosophical consequence is this: the method is partly compensatory, but the degree of compensation varies from zone to zone. One zone may allow wide compensation between criteria while another allows almost none.
How It Works
The method proceeds through six steps.
First, scaling the criteria onto the 0-1 range. For a benefit criterion, every value is divided by the column's largest value; for a cost criterion, the column's smallest value is divided by every value. If the data already sits within this range, this step is skipped.
Second, determining the zone attitude. Which zone each alternative belongs to is known in advance. A separate rank-weight list (λ) is defined for every zone, and this list is used to calculate the zone's degree of optimism (ORness). If ORness is close to 1, the zone is optimistic and rewards the best criterion; if close to 0, it is pessimistic and penalises the worst criterion.
Third, ranking the alternative's own criteria. Each alternative's criterion values are sorted from highest to lowest within themselves. Which criterion is best and which is worst for that alternative follows from this; this ordering can differ from alternative to alternative.
Fourth, calculating the regional score. The zone's λ list, the criterion weights, and the alternative's own ranking are combined to produce a normalised score between 0 and 1. This step blends the zone's risk attitude with the alternative's actual performance.
Fifth, regional diagnostics. ORness and the degree of trade-off are calculated for every zone; if the trade-off degree is close to 1, a wide balance is struck between criteria, and if close to 0, almost no balance is struck.
Sixth, ranking. Alternatives are ranked from the highest score to the lowest.
The formulas behind each step, the intermediate tables and the citation formats are given on the DecisionMind method page; this card carries no formulas.
How to Read the Output
The SOWA score shows how good an alternative is judged to be under the risk attitude of the zone it sits in. Two alternatives with identical criterion values can receive different scores if they sit in different zones; this is not a calculation error, it follows from the method's definition. A low score does not mean "the alternative is bad," it means "weak when assessed under this zone's risk attitude." Had the same alternative sat in a different zone, its score could have been different.
Thus instead of writing:
"SOWA found A3 to be the worst alternative"
the report should read:
"A3 is the weakest alternative when assessed under the pessimistic risk attitude of the zone it sits in; had the same alternative sat in an optimistic zone, it would have come out best"
Data Type and Inputs
SOWA works with crisp data: one number per cell. DecisionMind offers SOWA only in this base form; there is no separate data-type extension (fuzzy, grey, intuitionistic and so on). You need alternatives in rows, criteria in columns, one number per cell; direction information for every criterion; criterion weights summing to 1; a mapping showing which zone each alternative belongs to; and a separate rank-weight list (λ) for every zone. SOWA produces no weights of its own; it takes them from outside. A minimum of two alternatives and two criteria is required; the comfortable range for the number of criteria is two to eight.
When to Use It, When Not To
SOWA is a suitable choice if your decision problem divides into geographic or administrative zones and there is a justified reason for the risk attitude to differ between them. If the zone boundaries themselves are contested, or if the whole decision is to be assessed with a single risk attitude anyway, SOWA is not needed; a single-attitude method such as standard OWA or TOPSIS is enough. If the same λ list is given to every zone, SOWA already reduces to standard OWA; in that case, using the spatial extension serves no purpose.
Risk attitude varying by zone, a geographic/administrative division exists → SOWA
A single risk attitude applies across the whole table → standard OWA or TOPSIS
Zone boundaries are arbitrary or unjustified → clarify the zone definition first, then consider SOWA
Weights rather than a ranking are needed → AHP, BWM, SWARA (subjective) or Entropy, CRITIC (objective)
Strengths
SOWA's core strength is its ability to model geographic heterogeneity explicitly. Rather than assessing the same criterion table with a single attitude, it takes each zone's own understanding of risk into account. It brings the extremes of the OWA family (MAX, which looks at the best, MIN, which looks at the worst, and the simple average) together within a single framework, and thanks to the ORness and trade-off-degree diagnostics, every zone's attitude can be shown and justified with a number.
Weaknesses
Its limitations stem largely from the zone definition. Zone boundaries are a modelling decision, and this decision itself can be contested; moving an alternative from one zone to another can change the result substantially (Malczewski and Rinner, 2015). Second, if the same λ list is given to every zone, the method reduces to standard OWA and the point of the spatial extension is lost. Third, the method has, since 2006, been applied mainly in GIS-based environmental planning; its track record in other fields is limited.
Common Mistakes
The most common mistake is giving the same rank-weight list to every zone. This reduces SOWA to standard OWA and loses the spatial risk difference entirely. A second mistake is drawing zone boundaries arbitrarily rather than from data; zone boundaries should rest on a flood map, an administrative boundary, or a similar justification. A third is assuming the score's denominator is a fixed number for the zone. The denominator is recalculated according to each alternative's own criterion ranking; using a fixed number gives a wrong result.
The governing principle is this:
A SOWA result is a product of both the alternative's performance and the risk attitude assigned to the zone it sits in; if the zone assignment changes, so does the result, and the report must show this plainly.
Cases
Each case opens with a decision table, describes in words what the method does to it, and shows how to read the result. The first case is DecisionMind's validation example. The remaining cases are illustrative constructions.
1. Water management: Assessing infrastructure options in flood-risk zones
A municipal water authority will choose among three infrastructure options across two different zones. Two criteria apply: flood capacity and cost effectiveness, both scored "higher is better." A1 and A2 are in the "near zone," where the risk attitude is optimistic (λ=[0.7; 0.3]); A3 is in the "distant zone," where the risk attitude is pessimistic (λ=[0.3; 0.7]). The criterion weights are 0.6 for C1 and 0.4 for C2.
| Option | C1 | C2 | Zone |
|---|---|---|---|
| A1 | 0.80 | 0.40 | near |
| A2 | 0.40 | 0.90 | near |
| A3 | 0.95 | 0.05 | distant |
| Direction | higher is better | higher is better | n/a |
| Weight | 0.60 | 0.40 | n/a |
The method ranks each alternative's criteria within itself, combines this with its zone's λ list, and produces a normalised score.
| Option | SOWA score | Rank |
|---|---|---|
| A1 | 0.7111 | 1 |
| A2 | 0.7043 | 2 |
| A3 | 0.4022 | 3 |
The result reads as follows. A3's C1 (0.95) is the highest value in the table, but its C2 (0.05) is the lowest. Because A3 sits in the distant zone, it is assessed under the pessimistic attitude, and its weak criterion dominates; its score falls to 0.4022, putting it last. A1 and A2, sitting in the near zone, are assessed under the optimistic attitude, which brings their strong criteria to the fore.
The authority hesitates here. Had A3 sat in the near zone with the same criterion values, it would have scored 0.75 and come first; to confirm this, the same calculation was repeated by hand with the near zone's λ list, giving 0.75. So the reason A3 comes last is not its performance alone but its assignment to the distant zone. The authority should separately question whether the zone boundary accurately reflects where A3 sits.
In the report: "Under the distant zone's pessimistic risk attitude, A1 is the best option (0.7111); had A3 been assessed in the near zone with the same criterion values, it would have scored 0.75 and come first, so the accuracy of the zone boundary should be confirmed separately."
Source: Makropoulos and Butler (2006). The figures are a validation example prepared for DecisionMind's SOWA engine, faithful to the source paper's logic but not matched to a specific page number. Note: the DecisionMind team is separately reviewing single-criterion direction-test behaviour in this family of methods, which use data- and reference-point-sensitive weighting.
2. Waste management: Siting a regional solid-waste transfer facility
A metropolitan municipality will choose a site for a solid-waste transfer facility from among three candidate areas. Two criteria have been set: transport distance (lower is better) and an environmental impact score (higher is better). Two of the candidate areas sit in a "sensitive zone" around dense housing, where the risk attitude is pessimistic; each candidate is assessed by its weakest criterion there. The third candidate sits in an out-of-town "buffer zone," where the risk attitude is optimistic.
The method penalises the two candidates in the sensitive zone by their weakest criterion and rewards the candidate in the buffer zone by its strongest criterion. Suppose the result places the sensitive-zone candidate with a middling environmental impact but a short distance in third place with a low score, while raising the second candidate to first place, despite a high environmental impact, because it sits in the buffer zone.
The municipality hesitates here: the buffer-zone candidate's environmental impact score is in fact low, but the optimistic attitude has overlooked this weakness. If the "buffer" definition of the zone boundary is revised, the result may change. The report should therefore show which data (a housing-density map, wind direction) the zone boundaries rest on.
In the report: "Under the buffer zone's optimistic risk attitude, the second candidate comes out ahead; this candidate's environmental impact score is low, and the buffer-zone boundary should be reviewed again."
3. Mining: Prioritising rehabilitation at abandoned mine sites
An environmental agency will determine the rehabilitation order for three abandoned mine sites. Two criteria apply: the level of soil contamination (lower is better) and distance to the nearest settlement (higher is better). Sites close to settlements sit in an "urgent zone" and are assessed under the pessimistic attitude; distant sites sit in a "monitoring zone" and are assessed under the optimistic attitude.
The method brings the urgent-zone sites forward by their worst contamination values, while assessing the monitoring-zone site by its best criterion and giving it low priority. Suppose the site with the highest contamination but closest to a settlement comes first, while the site with middling contamination but distant comes last.
The agency hesitates here: the distant site's contamination appears low priority because it sits in the monitoring zone, but contamination can spread over time. The zone attitude's assumption that "distant = low priority" may not hold for every type of contaminant. The report should therefore also state a re-assessment schedule for sites in the monitoring zone.
In the report: "Under the urgent zone's pessimistic attitude, the site with the highest contamination is the top priority; the site in the monitoring zone comes out low priority, but should be re-assessed within six months given the risk of contamination spreading."
4. What Not to Do
Had all three zones in the water-management case been given the same λ=[0.7; 0.3] list, SOWA would reduce to standard OWA and A3's position in the distant zone would have had no effect at all; this makes the spatial extension pointless. A second error is redrawing zone boundaries after the data has been collected, by looking at the result; the zone definition should be fixed before the analysis, on an independent basis (a flood map, an administrative boundary). A third error is reading A3's score of 0.4022 as "this alternative performed badly"; the score only shows how that performance was assessed under the distant zone's risk attitude.
Sources
For the formulas behind each step, the intermediate tables and citation formats (BibTeX, RIS, APA), see the DecisionMind method page: decisionmind.app/library/sowa
Makropoulos, C. K., & Butler, D. (2006). Spatial ordered weighted averaging: incorporating spatially variable attitude towards risk in spatial multi-criteria decision-making. Environmental Modelling & Software, 21(1), 69-84. DOI: 10.1016/j.envsoft.2004.10.010
Yager, R. R. (1988). On ordered weighted averaging aggregation operators in multicriteria decisionmaking. IEEE Transactions on Systems, Man, and Cybernetics, 18(1), 183-190. DOI: 10.1109/21.87068
Makropoulos, C. K., Butler, D., & Maksimovic, C. (2003). Fuzzy logic spatial decision support system for urban water management. Journal of Water Resources Planning and Management, 129(1), 69-77. DOI: 10.1061/(ASCE)0733-9496(2003)129:1(69)
Malczewski, J., & Rinner, C. (2015). Multicriteria Decision Analysis in Geographic Information Science. Springer, Advances in Geographic Information Science. DOI: 10.1007/978-3-540-74757-4