Difference between revisions of "Screens and straining"
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| − | Drinking water, domestic use, and small-scale productive use. More often screens are used for small communities (households use [[Straining (fabric or micro)|other methods]]). | + | Drinking water, domestic use, and small-scale productive use. More often screens are used for small communities or schools (households use [[Straining (fabric or micro)|other methods]]). The source best used for screens is surface water (not rainwater or groundwater). |
===Construction, operations and maintenance=== | ===Construction, operations and maintenance=== | ||
Revision as of 00:40, 4 October 2013
Screens or sieves are great for straining larger particles out of water and are a simple, but flexible technology for diverse configurations. These work well applied at (inlet of) central treatment facilities, but simple use makes it suitable for decentralized or rural applications. They can be placed at surface water inlets to prevent debris or coarse material from reaching subsequent treatment processes. Debris mostly includes organic material like leaves, duckweed and algae. In vicinity of near-urban settlements, plastic wastes are typical. Debris needs to be properly disposed and managed according to its characteristics and volume.
Suitable conditions
Drinking water, domestic use, and small-scale productive use. More often screens are used for small communities or schools (households use other methods). The source best used for screens is surface water (not rainwater or groundwater).
Construction, operations and maintenance
The screens are mostly simple steel grids or larger sheets of screening material. For removing algae, microstrainers with openings of 10-60µm are used after screens. Although generally, those with a mesh-size of 2-8cm are preferred. Straight screens can be manufactured locally and cleaned manually. Cylindrical or drum strainers require mechanical cleaning (backwashing). They require regular debris removal, but lower debris load reduces cleaning frequency. Management requirements depend on cleaning mechanisms. Maintenance is low and can be combined with the cleaning of other facilities. Training on debris management might be required.
Requires no specific social campaign as the method is widespread and is not applied directly at household level. Screening only removes larger particles (turbidity solids), therefore it cannot guarantee safe water quality. The must be applied in combination with other treatment processes.
Costs
Costs depend on the design and the cleaning mechanism applied. Expenses can be kept low by using manual labor for cleaning and maintenance. Screens are normally donor-financed, or occasionally user-financed.
Acknowledgements
- Surface water intake and small dams, revised by Nhamo Masanganise.
- Screening. Lenntech.
- Screening and straining. Veolia Water.
