Program Scenario: Surface drip irrigation · N₂O emission reduction · SOC not credited · Sugar beet compatible
Research Design Overview

Step 1 — Pre-Screening

Hard filters applied to all 26 DSİ hydrological basins. Basins eliminated if: drip adoption already >70% (low additionality), irrigated area too small for program scale, or technically incompatible (e.g. rice-dominant). Reduces the pool to analytically comparable candidates.

Step 2 — Criterion Finalization

15 criteria selected through stakeholder interviews, literature review, and expert consultation. Criteria span infrastructure readiness, agronomic compatibility, farmer behavioral readiness, market conditions, and program logistics. 5 criteria use expert rating (1–7 linguistic scale); 10 use secondary data with researcher-based classification (1–5 scale). Each criterion is justified and operationalized with a defined data source.

Step 3 — Fuzzy BWM (Criterion Weights)

Best-Worst Method (Guo & Zhao, 2017) with fuzzy linguistic comparisons. Expert panel (n=5–7) identifies best and worst criteria, then compares others pairwise. Yields criterion weights with explicit consistency check (ξ*). Two weight profiles: one per scenario.

Step 4 — Fuzzy TOPSIS (Basin Ranking)

Technique for Order Preference by Similarity to Ideal Solution. Expert-rated criteria use a 1–7 linguistic scale (VL/L/ML/M/MH/H/VH → TFN7); secondary data criteria use 1–5 (VL/L/M/H/VH → TFN5). Weighted normalized decision matrix compared against Fuzzy Positive Ideal Solution (FPIS) and Fuzzy Negative Ideal Solution (FNIS). Closeness coefficient (CC) determines ranking.

Step 5 — Sensitivity Analysis

Two approaches: (1) Weight perturbation ±10%, ±20% to test ranking stability; (2) Criterion exclusion — toggling off specific criteria tests how sensitive the ranking is to each dimension (e.g., removing tillage-related criteria, lab distance, or social co-benefits). Basins robust across all conditions are identified as priority candidates.

Step 6 — Scenario Comparison

Scenario A (Surface Drip + N₂O only) and Scenario B (SDI + N₂O + SOC) are compared side-by-side. Differences arise from criterion weights — tillage willingness weighted ~2× higher in B (adoption is a structural commitment). Robust basins appearing in top tiers of both scenarios are the strongest program candidates.

Two Program Scenarios

Scenario A — Surface Drip + N₂O only

  • Drip tape installed seasonally, removed before harvest/tillage
  • Compatible with all row crops incl. sugar beet
  • Carbon methodology: N₂O emission reduction only (VM0042)
  • SOC not credited — tillage is not structurally prevented
  • Tillage willingness: lower weight (behavioral, not structural)
  • Lower upfront investment per farmer

Scenario B — SDI + N₂O + SOC

  • Subsurface drip at 30–45 cm depth, permanent installation
  • Incompatible with deep-harvest crops (sugar beet, peanut)
  • Carbon methodology: N₂O + Soil Organic Carbon (VM0042)
  • SOC accumulation enabled by structural no-tillage
  • Tillage willingness: higher weight (adoption commitment)
  • Higher investment, longer payback, greater carbon upside
Criterion List & Operationalization
Note: All scores in the interactive model are preliminary placeholders based on secondary data and interview insights. Final scores will be determined through expert surveys (Fuzzy BWM) and data collection per the defined sources below.
#CriterionTypeMeasurementData Source Wt AWt B
Criterion Weights
Preliminary weights shown. Final weights will be determined by Fuzzy BWM expert elicitation.
Total weight: 100%
BWM Weight Estimator (simplified)

Select best & worst criteria. Rate each criterion vs. best (1=equal importance, 9=extremely less important). Computed weights will be applied to the sliders above.

Basin Prioritization Map Scenario A
Ranking:
High priority
Medium
Low priority
Pre-screened out
Fuzzy TOPSIS Ranking
RankBasinProvinces CC Scored⁺d⁻
Criteria Exclusion Test

Toggle criteria on/off to simulate different analytical scenarios. Try removing expert-only criteria, behavioral criteria, or logistics criteria to see which dimensions drive the ranking.

Weight Perturbation
Applies random ±% perturbation to each weight, then re-normalizes
Ranking Comparison: Baseline vs. Current Settings
Basin Baseline Rank Baseline CC Current Rank Current CC Change
How this works: Enter raw values for quantitative criteria — the system classifies them to 1–5 based on defined thresholds. For researcher-classified criteria, enter your 1–5 directly. Expert-rated criteria use 1–7 (you rate based on interview insights; these will later be replaced by actual expert survey responses). Click Apply & View Rankings when done to update the map and rankings.
◈ Quantitative Criteria — Raw Data Entry Auto-classified to 1–5 based on thresholds
Energy: OKSURE 2024 outage minutes/year per province. Water Stress: WRI Aqueduct 4.0 Water Stress indicator (0–5 scale, 2030 BAU). Lab Distance: km from basin centroid to nearest ISO 17025 accredited GC lab.
Thresholds — Energy (min/yr): <200=5, 200–600=4, 600–1200=3, 1200–2400=2, >2400=1  |  Water Stress (0–5): <1=1, 1–2=2, 2–3=3, 3–4=4, >4=5  |  Lab Distance (km): <200=5, 200–350=4, 350–500=3, 500–700=2, >700=1
◉ Researcher-Classified Criteria — 1–5 Score Entry VL=1 · L=2 · M=3 · H=4 · VH=5
★ Expert-Rated Criteria — 1–7 Score Entry VL=1 · L=2 · ML=3 · M=4 · MH=5 · H=6 · VH=7
Placeholder values (4=M) shown. These will be replaced with actual expert survey responses from Fuzzy BWM elicitation.