| Literature DB >> 33976904 |
Zaitizila Ismail1, Yun Ii Go1.
Abstract
Water is indispensable for human survival. Freshwater scarcity and unsustainable water are the main growing concerns in the world. It is estimated that about 800 million people worldwide do not have basic access to drinking water and about 2.2 billion people do not have access to safe water supply. Southeast Asia is most likely to experience water scarcity and water demand as a result of climate change. Climate change and the increasing water demand that eventually contribute to water scarcity are focused upon here. For Southeast Asia to adapt to the adverse consequences of global climate change and the growing concern of environmental water demand, fog water harvesting is considered as the most promising method to overcome water scarcity or drought. Fog water collection technique is a passive, low maintenance, and sustainable option that can supply fresh drinking water to communities where fog is a common phenomenon. Fog water harvesting system involves the use of mesh nets to collect water as fog passes through them. Only minimal cost is required for the operation and maintenance. In conclusion, fog water harvesting seems to be a promising method that can be implemented to overcome water scarcity and water demand in Southeast Asia.Entities:
Keywords: drought; economic feasibility; fog collectors; sustainability; vulnerability
Year: 2021 PMID: 33976904 PMCID: PMC8101349 DOI: 10.1002/gch2.202000036
Source DB: PubMed Journal: Glob Chall ISSN: 2056-6646
Water withdrawal by region[ , , , , , , , ]
| Continental Runoff [km³ per year] | ||||||||
|---|---|---|---|---|---|---|---|---|
| Study | ||||||||
| Region | Vörösmarty et al.[
| Cosgrove and Rijsberman[
| Hanasaki et al.[
| Döll and Siebert[
| FAO[
| Shiklomanov[
| Oki et al.[
| Wada et al.[
|
| Africa | 4520 | 6470 | 1400 | 1400 | 1800 | 4050 | 5815 | 2132 |
| Asia | 13 700 | 23 813 | 21 400 | 18 800 | 19 400 | 13 510 | 13 014 | 22 948 |
| Europe | 2770 | 3588 | 1600 | 1200 | 1300 | 2900 | 6286 | 3922 |
| Oceania/Australia | 714 | 2680 | 200 | 300 | 200 | 2400 | 1912 | 2630 |
| North America | 5890 | 5145 | 2400 | 1900 | 2000 | 7890 | 5345 | 6225 |
| South America | 11 700 | 20 760 | 1200 | 1000 | 1900 | 12 030 | 14 906 | 1646 |
Land area and human population based on UN estimation[ ]
| Countries | Land area [km2] | UN population estimates [thousands] | |||
|---|---|---|---|---|---|
| 2015 | 1980 | 1990 | 2000 | 2010 | |
| Brunei | 5769 | 189 | 252 | 327 | 399 |
| Cambodia | 181 035 | 6506 | 9532 | 12 447 | 14 138 |
| Indonesia | 1 913 579 | 150 820 | 184 346 | 213 395 | 239 871 |
| Laos | 236 800 | 3235 | 4192 | 5317 | 6201 |
| Malaysia | 330 290 | 13 833 | 18 209 | 23 415 | 28 401 |
| Myanmar | 676 577 | 32 865 | 39 268 | 44 958 | 47 963 |
| Philippines | 300 000 | 47 064 | 61 629 | 77 310 | 93 261 |
| Singapore | 719 | 2415 | 3017 | 3919 | 5086 |
| Thailand | 513 120 | 47 483 | 57 072 | 63 155 | 69 122 |
| Timor‐Leste | 14 870 | 581 | 743 | 830 | 1124 |
| Vietnam | 330 951 | 54 023 | 67 102 | 78 758 | 87 848 |
| Southeast Asia | 4 503 710 | 359 014 | 445 362 | 523 831 | 593 414 |
Water in Southeast Asia (World bank 2013, 2015, 2016)[ , , ]
| Region | Internal renewable freshwater resources | Access to improved water source | Access to improves sanitation facilities | Urban population | ||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| per capita cubic meters (m3 per inhabitant per year) | % of total population | % of total population | % growth | |||||||||
| 2011 | 2013 | 2014 | 2010 | 2012 | 2015 | 2010 | 2012 | 2015 | 1990–2011 | 2012–2013 | 2013–2014 | |
| Brunei | 20 939 | 20 345 | 20 364 | – | – | – | – | – | – | 2.2 | 1.8 | 1.8 |
| Cambodia | 8431 | 7968 | 7868 | 64 | 71 | 76 | 31 | 37 | 42 | 2.1 | 2.7 | 2.6 |
| Indonesia | 8332 | 8080 | 7935 | 82 | 85 | 87 | 54 | 59 | 61 | 2.5 | 2.7 | 2.7 |
| Laos | 30 280 | 28 125 | 28 463 | 67 | 72 | 76 | 63 | 65 | 71 | 4.7 | 4.9 | 4.6 |
| Malaysia | 20 098 | 19 517 | 19 397 | 100 | 100 | 98 | 96 | 96 | 96 | 2.5 | 2.7 | 2.5 |
| Myanmar | 20 750 | 18 832 | 18 770 | 83 | 86 | 81 | 76 | 77 | 80 | 2.5 | 2.5 | 2.5 |
| Philippines | 5050 | 4868 | 4832 | 92 | 92 | 92 | 74 | 74 | 74 | 2.2 | 1.3 | 1.3 |
| Singapore | 116 | 111 | 110 | 100 | 100 | 100 | 100 | 100 | 100 | 2.1 | 1.6 | 1.3 |
| Thailand | 3229 | 3350 | 3315 | 96 | 96 | 98 | 96 | 93 | 93 | 1.7 | 3 | 2.9 |
| Timor‐Leste | 6986 | 6961 | 6777 | 69 | 71 | 72 | 47 | 39 | 41 | 4.2 | 4.8 | 4.7 |
| Vietnam | 4092 | 4006 | 3961 | 95 | 95 | 98 | 76 | 75 | 78 | 3.1 | 3.1 | 3.0 |
Figure 1Internal renewable freshwater resources per capita cubic (m3 per inhabitant per year) in Southeast Asia (2011, 2013, 2014).[ , , ]
Water resources index classes[ ]
| Per capita water availability (m3/c/y) | Stress level |
|---|---|
| >1700 | No stress |
| 1000–1700 | Moderate stress |
| 500–1000 | High stress |
| <500 | Extreme stress |
Figure 2Percentage in total population in access water source and sanitation facilities in Southeast Asia (2011, 2013, 2014).[ , , ]
Figure 3Percentage in total population in urban growth in Southeast Asia (2011, 2013, 2014).[ , , ]
Figure 4Climate risk index in Southeast Asia: Ranking for 1999–2018 (Eckstein et al. 2019).[ ]
Ranking climate risk (RCI), dominant hazards of Southeast countries, climate risk index for 2018; Kreft et al., 2016;[ ] Eckstein et al. 2019;[ ] Thinkhazard 2017[ ]
| RCI | Country | Dominant hazards | CRI score | Fatalities in 2018 (Rank) | Fatalities per 100 000 inhabitants (Rank) | Losses in million US$ (PPP) (Rank) | Losses per unit GDP in % (Rank) |
|---|---|---|---|---|---|---|---|
| 1 | Myanmar | Floods, landslides, cyclone | 53.83 | 20 | 43 | 59 | 79 |
| 2 | Philippines | Cyclones, landsides, floods, droughts, earthquake, tsunami, volcano | 11.17 | 4 | 14 | 7 | 14 |
| 3 | Vietnam | Droughts, typhoon, cyclones, sea level rise, floods, landslides | 26.17 | 9 | 33 | 18 | 32 |
| 4 | Thailand | Sea level rise, floods, drought, cyclones | 68.83 | 25 | 59 | 60 | 105 |
| 5 | Cambodia | Floods, cyclones | 47.67 | 29 | 17 | 79 | 72 |
| 6 | Indonesia | Droughts, floods, landslides, sea level rise, earthquake, tsunami, volcano, cyclone | 68.17 | 11 | 74 | 42 | 104 |
| 7 | Laos | Floods, landslides, cyclone | 35.5 | 26 | 8 | 69 | 51 |
| 8 | Malaysia | Droughts, floods | 84.83 | 45 | 61 | 96 | 123 |
| 9 | Brunei | Floods | 125 | 115 | 115 | 135 | 135 |
| 10 | Singapore | Floods | 125 | 115 | 115 | 135 | 135 |
Fog harvesting's technical feasibility, water yield, and parameters investigated in the research
| No | Title | Technical Feasibility | Yield | Parameters | Ref | |||
|---|---|---|---|---|---|---|---|---|
| 1 | Electrostatically driven fog collection using space charge injection. |
Adopt electrical forces to overcome aerodynamic drag forces. Use ion emitter to introduce space charge into the fog and direct them to collector via imposed electric field. | 30 min of exposure to corona discharge resulted in 30 mL of water collection. |
Collection efficiency, area. Acceleration phase, electric field. Terminal velocities, corona discharge. |
[
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| 2 | Experimental study of fog water harvesting by stainless steel mesh. |
Adopt stainless steel and black double layer plastic mesh. Operates at zero energy and waste. Require dust cleaning. |
2.8–3.72 L m−2 per day (using SFC) 2.0–3.10 L m−2 per day (using CFC) |
Frame and mesh material, area. Gutter material, diameter, length, closure, position, angle of fixing. Fog frequency, formation height, cloud base height. |
[
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| 3 | The effects of surface wettability on the fog and dew moisture harvesting performance on tubular surfaces. |
Comparative study of wettability under dewing and fogging conditions. Oil‐infused surfaces suitable fogging harvesting determined by water removal efficiency. Well‐wetting surfaces with lower barrier to nucleation of condensates suitable for dew harvesting determined by water capture efficiency. |
In 90 min, ≈3.5–4.375 g (fog harvesting) In 90 min, ≈2.75–3.375 g (dew harvesting) |
Harvesting efficiency. Contact angle. Droplet mass, falling frequency. Frequency ratio, mass ratio. Nucleation rate, nucleation energy barrier. |
[
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| 4 | Fog‐water collection for community use. |
Review climatic and topographic features that determined fog formation. |
Chile, Falda Verde (1.5 L m−2 per day) S. Africa, Soutpansberg (3 L m−2 per day) Ecuador, P. Grande (4 L m−2 per day) Guatemala, Tojquia (6 L m−2 per day) Canary Islands, Tenerife (10 L m−2 per day) Cape Verde, Serra M. (12 L m−2 per day) |
Amount collected. Quality of fog water. Impact of technology to communities. |
[
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| 5 | Mist harvesting using bioinspired polydopamine coating and microfabrication technology. |
Adopt biopolymer of polydopamine and negative photolithography method. Use porous membrane surfaces with contrast wettability. | 97 mg cm−2 h−1 |
Contact angle. Surface free energy, surface tension, dispersive components. Surface morphology, topography, roughness. Water collection rate. Wetting properties. |
[
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| 6 | A facile strategy for the fabrication of a bioinspired hydrophilic‐superhydrophobic patterned surface for highly efficient fog‐harvesting. |
Adopt super hydrophobically modified metal‐based gauze on the surface of hydrophilic polystyrene sheet. Can easily control the pattern's dimensions by changing the gauze mesh size and thermal pressing temperature. Low cost for replicability. | 41–159 mg cm−2 h−1 |
Mesh size. Intensity, binding energy. Water contact angle, sliding angle, droplet volume. Copper gauge size. Thermal treatment temperature. |
[
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| 7 | A twice electrochemical‐etching method to fabricate superhydrophobic‐super hydrophilic patterns for biomimetic fog harvest. |
Use electrochemical‐etching method for fabrication with boiling‐water immersion method Fabricate superhydrophobic‐superhydrophilic patterned surface. High etching potential resulted a uniform superhydrophilic dimple. | ≈6000–12 000 mg h−1 |
Etching current, voltage. Contact angle. Etching time. Surface morphology, wettability. Dimple depth. Droplet number, mass. |
[
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| 8 | Fog water collection: Challenges beyond Technology. |
Review challenge and opportunity of fog collection. Standard and large fog collectors are made of polypropylene mesh nets (Raschel nets). SFC size of 1 m2, LFC size ranging from 40–48 m2. Width to height ration around 2.5–3.0. |
In Tojquia, Guatemala, 28 units of LFCs provided 5000 L per day. Partial or complete failure in Serra M., Cape Verde; El Tofo & Padre H., Chile; Pachamama G., Ecuador. |
Economic factor. Community development. Capacity building. Policies support. Stakeholder involved. |
[
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| 9 | Quantification of Fog Water Collection in Three Locations of Tenerife (Canary Islands). |
Use cylindrical wire‐harp gauges and modified Juvik‐type fog water gauges. 46 cm high, 20 cm outer diameter. Water funnel connected to a Rain‐O‐Matic tipping bucket gauge. | 10–40 L m−2 per day |
Volumes, frequency of fog water. Wind speeds, solar radiation. Temperature inversion, relative humidity. |
[
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| 10. | Cactus kirigami for efficient fog harvesting: simplifying a 3D cactus into 2D paper art |
Adopt cactus‐inspired FC. Spines from 3D cone to 2D triangle via wax infused kirigami. Anisotropic shape for efficient capture of droplets. Directional droplet self‐propulsion. | 4 g cm−2 h−1 under fog flow 220 cm s−1 |
Mass per unit area, wind flow speed, contact angle. Spine‐to‐spine width, track‐to‐track width. Spine density, tracks. |
[
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Water collection rates from fog collectors[ , ]
| Project | Large fog collector (LFC) water production: L/40m2/year (m3) |
|---|---|
| Gobabeb, Nambia | 11 500 |
| Chungungo, Chile | 43 800 |
| Lepelfontein, South Africa | 14 700 |
| Ilam, Nepal | 52 300 |
| Sidi Ifni, Morocco | 31 800 |
| Tenerife, Canary Islands | 69 000 |
| Meija, Peru | 75 600 |
| Hajja, Yemen | 17 100 |
| Dhofur, Oman | 61 600 |
| Chanaral, Chile | 21 900 |
| Nefasit, Eritrea | 12 600 |
| Tojquia, Guatemala | 37 800 |
Projects and research in fog harvesting and its financial, economic feasibility and model scalability
| No | Title | Financial / Economic Feasibility | Scalability | Ref |
|---|---|---|---|---|
| 1 | Exploring fog water harvesting potential and quality in the Asian region, Kingdom of Saudi Arabia. |
2 m × 20 m fog collection system. 7600 SR/unit (USD 1 = SR. 3.75) Cost: 90.77 SR m−3 ( | Life cycle of fog collector and interest rate requirement. |
[
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| 2 | Fog and dew as potable water resources: maximizing harvesting potential and water quality concerns. |
0.07 USD L−1 (bottled water: 0.22 USD L−1), Kutch region, Western India. 0.0011–0.0017 USD L−1 (trucked water: 0.0016 USD L−1), Chile. |
Increase pH, use filters and noncorrosive piping and water storage. Disinfection requirement. |
[
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| 3 | Fog water collection: challenges beyond technology. |
Raschel mesh: 25–50 USD m−2 For LFC, 1000–2000 USD for 40 m2, 1200–2400 USD for 48m2 For LFC, 200 USD/unit for 40m2, Dar Si Hmad, Morocco (5 USD m−2). High efficiency 3D spacer fabric net: 830 USD m−2 1.96–3.06 USD m−3, Atama Desert, Chile. 1.7–3.3 USD m−3, Eritrea. |
Cost depends on the mesh material, piping, water tanks etc. Depends on its availability and price at the local area. High efficiency net can double or triple the yield, withstand wind speed of 120 km h−1. Mesh selection depends on durability, water draining characteristic etc. Labor and subsidies availability for LFC. |
[
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| 4 | Fog‐water collection for community use. |
For 60‐unit LFC with 6.2 km pipeline, 100 m3 storage: 37 000 USD, Chile. For 100‐unit LFC: 40 000 USD. | Cost depends on site access, piping length, product lifespan. |
[
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| 5 | Reviewing fog water collection worldwide and in Oman. | 1.87 USD m−3 (water truck 7.25 USD m−3). |
Depends on equipment durability, meteorological conditions. Cost depends on piping, distance from point of use, storing. Material depends on availability in the local market etc. |
[
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| 6 | Review of sustainable methods for atmospheric water harvesting. |
400 USD for 48 m2 LFC. 100–200 USD for 1 m2 SFC. 500 USD/net for nylon net, Lima, Peru. |
Depend on country and material Eiffel collector (4 × 8 × 0.3) m Harp collector (2 × 4 × 0.3) m Diagonal Harp collector (2 × 4 × 0.3) m |
[
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| 7 | Fog harvesting on the verge of economic competitiveness. | 350 USD/module of production cost. |
Require business model for enterprise and legal adaption. Eiffel collector: simplicity, high yield, reproducibility, robustness. Harp collector: best surface‐water yield ratio |
[
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| 8 |
Can fog and rain harvesting secure safe drinking water in rural Cameroon? – Case study of Bafou (mountainous) and Mora (low‐lying) Villages. | 45 000 USD for complete Bafou's fog‐harvesting system. Including structural material, transport, labor, and maintenance. |
Prepare multiple alternative water sources during drought. Assessment of microbiology and chemistry experts is desirable on water quality. |
[
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| 9 | Fog as a Fresh‐water resource: overview and perspectives | 150 USD for SFC. |
Depend on local market situation. Cost covers piping, shipping, storage, transport. Might require meteorology and water supply expert. |
[
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| 10 | Cactus kirigami for efficient fog harvesting: simplifying a 3D cactus into 2D paper art | 0.5 USD m−2 for construction cost. |
Use paper‐based substrate. Simplified structure, tunable and scalable. Low‐cost materials, bioinspired interfaces. |
[
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Figure 5a) 18 m2 flat‐panel fog collector at Mount Machos with the water tanks; b) single layer Rashel mesh (35% shading); c) stainless steel poly‐yarn mesh used in South Africa; d) 3D prototype poly‐material mesh; e) Raschel net (PP), double‐layered; f) Dimple dot fabric (PES); g) Enkamat (PA6); h) Shade net (HDPE); i) Spacer fabric (PES); j) Hail protection net (HDPE), double layered. Reproduced with permission.[ ] Copyright 2014, Springer Nature. Reproduced with permission.[ ] Copyright 2015, Martina Mayerhofer.