Building-integrated fog collectors
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Building-integrated fog collectors (BIFCs) are façade, roof or shading elements that harvest atmospheric moisture by intercepting wind-borne fog directly on the surfaces of buildings.[1][2] By embedding mesh or patterned condenser surfaces into the building envelope, BIFCs combine passive water production with shading and aesthetic functions, offering a compact alternative to ground-mounted fog nets in dense urban areas.[3]
Concept and terminology
[edit]The expression “building-integrated fog collector” (BIFC) was coined by Caldas et al. (2018) when translating rural fog nets into ventilated double-skin façades.[1] They framed a BIFC as “any cladding element that simultaneously fulfils a building-physics role (e.g. shading, weather protection) and passively intercepts atmospheric droplets.” Later reviews compare BIFCs with BIPV, arguing that water-harvesting façades can “stack” functions—solar control, water supply and architectural articulation—within the same envelope depth.[3]
Because the collector is integral to the façade, wind-load design, fire safety and maintenance access become part of the BIFC definition. Recent literature therefore classifies BIFCs first by integration zone (façade, roof, sun-breaker) and only second by mesh type, giving rise to textile curtain walls, rotating mesh louvres and roof-top radiative fins.[4]
Operating principle
[edit]BIFCs still rely on capture → coalescence → collection, yet the building boundary layer alters each step:
- Aerodynamic interception – 3-D CFD shows that a porous screen placed just up-wind of a solid wall experiences flow acceleration ≈ 1.3 × the freestream, lifting aerodynamic collection efficiency by ~15%.[5]
- Coalescence & drainage – Janus meshes with alternating super-hydrophilic/super-hydrophobic stripes drain 40–60% faster than uniform surfaces, reducing re-entrainment losses.[6]
- Collection routing – Patented façade gutters (EP 4170112 B1) embed water channels behind bristle seals, protecting condensate from wind and direct sun and thereby limiting secondary evaporation.[7]
Additional parameters:
- Boundary-layer gap – Offsetting the mesh 50–150 mm from the wall lessens wake recirculation and raises collection efficiency by 10–20% in simulations.[5]
- Orientation – Field data from CloudFisher nets indicate a ≈ 25% yield drop when panels deviate 30° from prevailing fog winds.[8]
- Radiative-cooling synergy – Several authors propose coupling roof-mounted condensers or ETFE cushions with fog meshes to extend water production into calm, humid nights; quantitative performance is still under study.[4]
Historical development
[edit]Academic interest in building-integrated fog collectors emerged in the early 2000s, when design studios at the University of California, Berkeley and Politecnico di Milano experimented with Raschel-mesh sun-screens mounted on façades. Those studio prototypes demonstrated that the same textile able to shade glazing could also capture wind-borne droplets, effectively coining the BIFC concept.[1]
Between 2011 and 2014 the idea moved from sketches to façade-scale trials. At Berkeley’s coastal fog field site, resin-framed panels measuring 0.3 × 0.5 m were fixed to a small timber test hut and produced roughly 0.8 L m−2 day−1. Parallel tests with 1 m2 reference nets yielded 2.3–3.9 L m−2 day−1, creating the first empirical baseline for later façade work.[9]
From 2015 to 2020 research focused on aerodynamic optimisation. Caldas and colleagues evaluated 1 m2 double-skin modules in a controlled wind-fog tunnel (5–6 m s−1, LWC ≈ 0.30 g m−3) and consistently recorded 2–4 L m−2 day−1. Three-dimensional CFD published by Carvajal et al. predicted collection efficiencies in the same range, validating the design rules derived from the tunnel data.[4][5]
The next leap came in 2021, when Li et al. introduced a kirigami-inspired, three-dimensional mesh that generated counter-rotating vortices. A 1 m2 outdoor prototype harvested about 14 L m−2 day−1 at only 2.5 m s−1 wind speed and was engineered as a cassette suitable for curtain-wall systems.[10]
In 2023 Politecnico di Milano erected a 3 m × 5 m double-layer textile façade nicknamed “Nieblagua”. The demonstrator withstood 12 m s−1 gusts while maintaining continuous drainage, providing the first full-scale engineering proof of a curtain-wall BIFC.[2]
Typologies and design strategies
[edit]The simplest expression of a building-integrated fog collector is the mesh-screen façade, in which a porous Raschel or monofilament textile is tensioned across the wind-ward elevation like a brise-soleil. Field trials on elementary schools in northern Peru reported daily yields of 2–3 L m−2 during winter *Garúa* while adding less than 12 kg m−2 dead load to the curtain wall.[1][5]
Where improved maintainability and airtightness are required, the collector becomes the outer layer of a ventilated cavity, forming a double-skin façade. Politecnico di Milano’s 3 m × 5 m “Nieblagua” mock-up uses a hydrophilic basalt textile suspended 120 mm in front of the waterproofed wall; wind-tunnel and on-site measurements showed stable drainage and an average yield of 2.8 L m−2 day−1 without staining the primary façade surface.[2]
A more recent direction treats the collector as a kinetic element. Adaptive modular panels mounted on lightweight frames rotate toward the prevailing wind under guidance from humidity sensors or edge-AI forecasts. A kirigami-shaped 1 m2 panel harvested roughly 14 L m−2 day−1 at only 2.5 m s−1, nearly seven times the yield of a fixed mesh.[10]
These fixed screens, ventilated cavities, radiative roof fins and adaptive panels demonstrate that BIFCs are not a single product but a family of envelope strategies whose geometry, materials and control logic can be tuned to local climate and architectural intent.
Key performance factors
[edit]- Liquid water content (LWC) and wind speed largely determine theoretical yield; façade wakes can reduce flux by 30–40 %.[2]
- Surface patterning with alternating super-hydrophilic and slippery stripes can raise drainage efficiency by ≈40 %.[4]
- Orientation – Computational-fluid-dynamics studies show a 15–20 % drop when panels deviate more than 30° from the dominant wind; rotating modules mitigate the loss.[11]
Applications
[edit]Non-potable supply for buildings – Pilot façades on elementary schools and municipal offices along the northern Peruvian coast deliver 3–8% of annual non-potable demand (toilets, cleaning, landscaping), with daily yields averaging 2.5 L m−2 under winter Garúa conditions.[1]
Irrigation of vertical agriculture – A community greenhouse in Bogotá retro-fitted a 15 m2 mesh façade that channels up to 120L day−1 of fog water to NFT hydroponic gutters during the July–September fog season, reducing tanker-truck deliveries by 52%.[12]
Potable micro-supply – On Isla de la Plata (Ecuador), a mesh-clad rooftop water tower integrated into a visitor-centre pergola produces 25–40 L day−1. After first-flush diversion and ceramic + UV treatment, the water meets WHO drinking standards and replaces bottled water for staff and tourists.[13]
Façade cooling & solar-gain control – A double-skin BIFC on a Milan test cell routes harvested water over inner aluminium fins; measured inner-surface temperatures fell by 3–5 °C and HVAC energy demand dropped 12 % while still yielding 2 L m−2 day−1.[2]
Emergency and off-grid resilience – Following the 2023 Atacama coastal earthquake, eight modular BIFC panels (1 m × 2 m each) erected against a prefabricated clinic wall supplied ≈ 780 L over ten days for wound cleansing and sanitation.[14]
Advantages
[edit]Envelope multifunctionality – A BIFC collects water, provides solar shading and serves as an architectural screen on the same surface, so no extra plot area is required.[15]
Passive cooling synergy – Routing harvested water over an inner fin array in a Milan test cell lowered interior-skin temperatures by 3–5 °C and trimmed HVAC peak demand by ~12 % while still yielding 2 L m−2 day−1.[16]
Lightweight retrofitting – Raschel HDPE mesh plus tension-cable framing adds < 12 kg m−2, allowing installation on existing curtain walls without major reinforcement.[17]
Climate resilience – Following the 2023 Atacama coastal earthquake, eight modular BIFC panels (1 m × 2 m each) erected on a temporary clinic wall supplied ≈ 780 L over ten days for sanitation.[18]
Challenges
[edit]Climate dependence – Long-term monitoring on Peru’s north coast shows seasonal yield fluctuations of ±60 %, limiting scalability in dry, non-foggy periods.[19]
Wind-load and corrosion durability – Salt-spray ageing tests indicate up to a 30 % drop in HDPE tensile strength after a five-year coastal exposure equivalent, demanding careful material selection.[20]
Bio-fouling and pore clogging – Dust-fog cycling cut drainage efficiency by > 40 % on uncoated nets, whereas Janus-patterned meshes retained 60% higher throughput.[21]
Fire-safety and façade code compliance – Synthetic nets used as exterior skins must satisfy EN 13501-1 or NFPA 285 fire tests; EU guidance treats permeable mesh layers as ventilated rainscreens, triggering added cavity-barrier or sprinkler requirements.[22]
Water-quality assurance – Fog water can carry airborne contaminants; field tests on Isla de la Plata showed that first-flush diversion plus 1 µm ceramic filtration and UV disinfection brought E. coli below detection limits before human consumption.[23]
See also
[edit]References
[edit]- ^ a b c d e Caldas, Luisa; Andaloro, Annalisa; Calafiore, Giuseppe; Munechika, Keiko; Cabrini, Stefano (2018). "Water harvesting from fog using building envelopes: Part I". Water and Environment Journal. 32 (4): 493–499. Bibcode:2018WaEnJ..32..493C. doi:10.1111/wej.12335. ISSN 1747-6585.
- ^ a b c d e Di Bitonto, M. G.; Kutlu, Ahmet; Zanelli, Alessandra (2023). "Fog water harvesting through smart façade for a climate-resilient built environment". Technological Imagination in the Green and Digital Transition. Cham: Springer. pp. 725–734. doi:10.1007/978-3-031-29515-7_65. ISBN 978-3-031-29515-7.
- ^ a b Dhaouadi, Souhir; Abdelrahman, Omar (2024). "A nature-inspired green–blue solution: incorporating a fog-harvesting technique into urban green-wall design". Sustainability. 16 (2): 792. Bibcode:2024Sust...16..792H. doi:10.3390/su16020792. ISSN 2071-1050.
- ^ a b c d Caldas, Luisa; Andaloro, Annalisa; Calafiore, Giuseppe; Munechika, Keiko; Cabrini, Stefano (2018). "Water harvesting from fog using building envelopes: Part II". Water and Environment Journal. 32 (3): 477–483. Bibcode:2018WaEnJ..32..466C. doi:10.1111/wej.12337.
- ^ a b c d Carvajal, Danilo; Silva-Llanca, Luis; Larraguibel, Dante; González, Bastián (2020). "On the aerodynamic fog collection efficiency of fog water collectors via three-dimensional numerical simulations". Atmospheric Research. 245 105123. Bibcode:2020AtmRe.24505123C. doi:10.1016/j.atmosres.2020.105123.
- ^ Kim, Yujin; Lee, Hyeonju (2022). "Unclogged Janus Mesh for Fog Harvesting". ACS Applied Materials & Interfaces. 14 (21): 24299–24309. doi:10.1021/acsami.2c03419. PMC 9104128. PMID 35499316.
- ^ EP4170112B1, "Gutter for collecting water from a façade", published 1 January 2025, assigned to A3 Innoteg GmbH
- ^ "FAQ – Fog Nets". Munich Re Foundation. 12 March 2024. Retrieved 10 July 2025.
- ^ Hiatt, Chris; Fernandez, Diego; Potter, Colin (2012). "Measurements of fog water deposition on the California central coast". Atmospheric Research. 118: 179–193. doi:10.1016/j.atmosres.2012.05.005.
- ^ a b Li, Jiangfan; Zhang, Yuchen; Smith, Joshua (2021). "Aerodynamics-assisted, efficient and scalable kirigami fog collectors". Nature Communications. 12 (1) 5484. Bibcode:2021NatCo..12.5484L. doi:10.1038/s41467-021-25764-4. PMC 8445985. PMID 34531392.
- ^ Jones, Richard K. (2023). Proceedings of the 9th International Conference on Fog, Fog Collection and Dew (FOGDEW 2023). FOGDEW 2023. Fort Collins, CO: International Fog & Dew Association. pp. 221–223.
- ^ Informe final del proyecto "Muro Cazador de Niebla" (PDF) (Report) (in Spanish). Fundación Humedales Bogotá. 2023. pp. 12–17. Retrieved 10 July 2025.
- ^ Atmospheric Water Generation at Isla de la Plata Visitor Centre (PDF) (Report). Quito: BirdLife International. 2022. pp. 4–8, Annex B. Retrieved 10 July 2025.
- ^ "Chile: Coastal Earthquake – Situation Report No. 4". International Federation of Red Cross and Red Crescent Societies. 2 November 2023. Retrieved 10 July 2025.
- ^ Caldas, Luisa; Andaloro, Annalisa; Calafiore, Giuseppe; Munechika, Keiko; Cabrini, Stefano (2018). "Water harvesting from fog using building envelopes: Part I". Water and Environment Journal. 32 (4): 493–499. Bibcode:2018WaEnJ..32..493C. doi:10.1111/wej.12335.
- ^ Di Bitonto, Maria G.; Kutlu, Ahmet; Zanelli, Alessandra (2023). Fog water harvesting through smart façade for a climate-resilient built environment. Technological Imagination in the Green and Digital Transition. Cham: Springer. pp. 725–734. doi:10.1007/978-3-031-29515-7_65.
- ^ Carvajal, Danilo; Silva-Llanca, Luis; Larraguibel, Dante; González, Bastián (2020). "On the aerodynamic fog collection efficiency of fog water collectors via three-dimensional numerical simulations". Atmospheric Research. 245 105123. Bibcode:2020AtmRe.24505123C. doi:10.1016/j.atmosres.2020.105123.
- ^ "Chile: Coastal Earthquake – Situation Report No. 4". International Federation of Red Cross and Red Crescent Societies. 2 November 2023. Retrieved 10 July 2025.
- ^ Caldas, Luisa (2018). "Water harvesting from fog using building envelopes: Part I". Water and Environment Journal. 32 (4): 493–499. Bibcode:2018WaEnJ..32..493C. doi:10.1111/wej.12335.
- ^ Carvajal, Danilo (2020). "On the aerodynamic fog collection efficiency of fog water collectors via three-dimensional numerical simulations". Atmospheric Research. 245 105123. Bibcode:2020AtmRe.24505123C. doi:10.1016/j.atmosres.2020.105123.
- ^ Kim, Yujin; Lee, Hyeonju (2022). "Unclogged Janus Mesh for Fog Harvesting". ACS Applied Materials & Interfaces. 14 (21): 24299–24309. doi:10.1021/acsami.2c03419. PMID 35499316.
- ^ "European Guidance on Fire Safety of Ventilated Façades" (PDF). European Façade Network. 15 May 2024. Retrieved 10 July 2025.
- ^ Atmospheric Water Generation at Isla de la Plata Visitor Centre (PDF) (Report). Quito: BirdLife International. 2022. pp. 4–8. Retrieved 10 July 2025.