Filtration is the easiest way to remove solids from water and wastewater streams. In wastewater systems, filtration is used to decrease suspended solids getting into the publicly owned treatment works or water-reuse systems or to increase solids in sludge dewatering applications.
Filter selection begins after an organization determines the required level of filtration or filtered water quality; decides whether or not filtrate will be disposed or reused; identifies how a lot space is available; calculates the amount of capital available to buy, operate, and maintain the system; decides whether the system ought to be automated or handbook; and considers any pertinent water conservation requirements.
The level of solids removal or filtered-water quality desired defines the type and size of filter essential; most are available with various automation levels and worth ranges.
Proper filter dimension is decided by flow rate and the amount, size, and type of solids to be removed. Particle sizes and filtration levels will be determined by filtering water and solids via various sizes of filter paper and measuring the total solids content material of filtered water.
Solids remaining in filtered water will be the identical dimension or smaller than the last filter paper used and will indicate which filter media opening dimension to use. (A filter producer or laboratory may be hired to perform this procedure.) The quantity of solids in water or wastewater will be determined by a laboratory analysis of total solids; flow can be determined from plant records or an in-line flow meter.
The following equation is used to calculate solids loadings (how quickly a filter will load with solids): solids (lb/h) = flow (gal/min) x total solids (ppm) x (8.34/60/1,000,000).
After solids loading, filter space, and filter media opening dimension have been determined, the amount of time required earlier than cleaning, or back-washing, ought to be calculated, and the fate of filtrate waste should he determined.
In different words, after a filter is backwashed, the place will wastewater go? Backwashing often requires as much as 10% of the total filtered quantity, a 10:1 ratio. For instance, 379 m3 (one hundred,000 gal) of filtered water would generate 38 m3 (10,000 gal) of backwash that contains concentrated strong and will require additional treatment.
Some wastewater must be pretreated earlier than filtration. Oily wastewater, for example, tends to agglomerate quickly between or over filter media and requires conditioning before filtration. Fine-grade filtration systems are susceptible to fouling from biological development, yeast, and different microorganisms; performing bench tests or consulting with filter producers about particular applications is recommended.
Y-Strainers
Y-strainers are the best, least costly ($30 to $a hundred) filters, however they’ve a small filter area and require frequent maintenance. They typically are used on small pipes to protect such equipment as seals, pumps, and nozzles from solids buildup.
Bag Filters
Bag filters basically are bigger Y-strainers. These filters are bags of selected pore sizes which are enclosed in a pressure housing with a removable cover for cleaning. They are easy to make use of, come in variable filtering sizes, and are relatively low in price, especially for remaining filtration or applications with low solids loadings. Bag filters don’t exceed 203 mm (8 in.) in diameter; for bigger diameters, an inline bank with a number of filters in a single housing is used.
The value of carbon or stainless metal bag filter housings varies according to measurement, from $a hundred for a fifty one-mm (2-in.) housing to $3000 for a 1219 mm (48-in.) housing. Filter bags range in value from $6 to $10 for pore sizes of 25 to 800 microns. Bags are available straight or pleated. Pleated bags provide added surface area but price more than twice as much as flat ones. The disadvantages of bag filters embrace high upkeep necessities for systems which are underdesigned or have high solids loads and the price of bag replacement.
Vacuum Filters
Vacuum filters use a slowly rotating vacuum (negative pressure) drum that pulls soiled liquid from the outside of the drum and media to the inside of the drum. The vacuum filter usually is packaged with a pre-batch treatment system to coagulate the wastestream before filtration. The advantage of this filter is its ability to filter a wide range of wastewaters. The disadvantages embrace gradual system throughput and high costs related with the filter media, which must be applied constantly to the batch pretreatment tank instantly earlier than vacuum filtration. In addition, the filtering media enhance total sludge volume as a lot as 60%. Because vacuum filter price usually includes the pretreatment system, a unit that processes 19 m3/d (5000 gal/d) can price $60,000.
Cyclone Separators
Cyclone separators are relatively new. Because they’ve higher rotating speeds than vacuum filters, they create a significant quantity of centrifugal energy to filter wastewater by means of varied media sizes. The rotating filter makes use of a fixed-micronsize medium, equivalent to diatomaceous earth, to filter the wastestream. The benefits of cyclone separators embody their ability to handle variable throughputs, filter various particle sizes, and produce drier sludge cake than vacuum filters for about the same cost (around $60,00). heir drawbacks are similar to those of vacuum filters, namely high filter media prices and sludge volume.
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