Dataset for: A Typology-Based Scalable Framework for Rooftop Rainwater Harvesting to Improve Industrial Water Sustainability in Bangladesh's Textile Industry

Published: 8 September 2026| Version 1 | DOI: 10.17632/w8c435r5ds.1
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Description

This dataset supports a study investigating whether industrial-scale rooftop rainwater harvesting (RWH) feasibility can be screened using a simplified structural typology, rather than requiring detailed facility-by-facility audits. The underlying hypothesis is that two readily observable structural variables, workforce scale and usable rooftop catchment area, are sufficient to predict RWH demand coverage and emission-reduction potential across heterogeneous industrial facilities. Data collection: 67 textile factories were selected via stratified random sampling (90% confidence, finite population correction, N=6,447 registered units) from Bangladesh's two dominant textile industrial belts (Dhaka-Gazipur-Narayanganj-Narsingdi and Chattogram). For each factory, workforce size was obtained from DIFE registration categories; usable rooftop area was digitised from high-resolution satellite imagery and classified into Small/Medium/Large classes using Jenks Natural Breaks; annual harvestable rainwater volume was estimated from local rainfall and rooftop area; non-potable water demand was estimated from workforce size; and CO2e emission reductions were calculated from avoided groundwater pumping energy. Each factory was assigned to one of nine workforce-rooftop typologies (T1-T9), a 3x3 matrix crossing three workforce bands with three rooftop size classes. Key findings: demand coverage varied systematically by typology, from 6% (High Workforce-Small Roof, T7) to 499% (Medium Workforce-Large Roof, T6). Three structural feasibility zones emerged: Surplus (>100% coverage: T1, T2, T6), Balanced (50-100%: T5, T9), and Deficit (<30%: T4, T7, T8). One typology (T3, Low Workforce-Large Roof) had zero sampled factories. Emission reductions ranged from 0.15 to 2.82 t CO2e/yr per factory and scaled primarily with rooftop size rather than coverage percentage. Interpretation and use: each row represents one factory; columns report raw inputs (location, workforce, rooftop area) and derived outputs (typology, coverage %, emission savings). Researchers can use this dataset to replicate the typology classification, verify reported summary statistics, or extend the analysis to other industrial contexts or sectors.

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Steps to reproduce

1. Sample selection: Apply stratified random sampling to DIFE-registered textile factories in Dhaka and Chattogram Divisions, using a finite population correction formula (N=6,447, z=1.645 for 90% confidence, e=0.10, p=0.5) to derive the target sample size of 67 factories, proportionally allocated across industrial subsector and geographic distribution. 2. Rooftop digitisation: For each sampled factory, delineate the rooftop boundary manually using high-resolution satellite imagery (e.g., Google Earth Pro), applying a rooftop utilisation factor to convert digitised area to usable catchment area. 3. Size classification: Classify usable rooftop area into Small, Medium, and Large classes using Jenks Natural Breaks, applied across the full sample. 4. Typology assignment: Cross-classify each factory's workforce band (Low/Medium/High, from DIFE registration category) with its rooftop size class to assign one of nine typologies (T1–T9). 5. Harvest volume and demand: Estimate annual harvestable rainwater volume from local rainfall data and usable rooftop area; estimate non-potable water demand from workforce size. 6. Coverage and emissions: Calculate demand coverage (%) as harvested volume divided by demand; calculate CO2e emission reductions from the groundwater pumping volume displaced, using a regional emission factor. Full formulas and parameter values are reported in the accompanying manuscript's Methods section.

Categories

Industrial Ecology, Integrated Water Resources Management, Rainwater Harvesting

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