Management of the Metal Removal Fluid Environment

Mist Collectors


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Proper ventilation and ductwork are necessary for the health and comfort of those working in the shop. But where metal removal fluid is in use, it’s also necessary to install air filtration systems, known as "mist collectors." Mist collectors reduce the amount of MRF aerosols in the workplace atmosphere.

 

 

 

system components

 

 

 

multiple stages of filters

 

glossary terms:

pocket filter
cartridge filter
DOP
HEPA

 

 


types of filters for each stage


1st and 2nd stage

 

 

 

 

 

 

 

2nd stage

 

 

3rd stage

 

 

 

 

effectiveness of filters

 

 

 

 

 

 

 

 

 

 

location of mist collector discharge

 

 

 

 

 

 

 

 

if air is recirculated

Mist collectors should be designed and maintained using ANSI B 11 TR 2-1997 as a guide.
Poorly maintained mist collectors may increase metal removal fluid aerosol concentrations in workplace atmospheres. It is important to inspect air cleaner filters and clean them regularly or replace them, as appropriate. Collected aerosol should never be allowed to drain back into the fluid system.

What are the components of such a filtration system?

There are many commercial mist collection systems available, but the best design for a given application depends on many factors of each specific application.

In general, commercial filters have multiple stages.

The first stage is relatively inefficient. It filters out the largest droplets.
The second stage is more efficient. It may use pocket or cartridge filters.
The final stage, using DOP or HEPA (high efficiency particulate air) filters, usually removes 95% of whatever has not been removed in the first two stages.
Most filters are effective when new, but they may rapidly lose effectiveness as they become loaded with liquid. Filters become more efficient as solids cake onto the filter, but less efficient with liquid loading. Filters with high liquid loading may release droplets or vapor back out into the air. As filter loading increases, the pressure drop increases, and the power required to move air through the system increases, as does operating cost.

What types of filters are used for the first stage?

Primary and secondary filters:

Open cell foam designed to coalesce MRF particles (that is, to collect small, individual droplets and combine them until they form a liquid that can be drained)
Metal mesh filters of various sizes designed to remove large droplets
Centrifugal filters, which are designed to remove airborne droplets through centrifugal force and drain them out of the system.
Helical tube systems, with many helical elements housed in a tube and mounted in a common frame (these elements cause the air to rotate, and centrifugal force throws the particles onto the tube, where they collect)
Electrostatic precipitators, which electrostatically charge the droplets and attract them to a collection element, where they coalesce and drain out of the system
Disposable filters designed to be replaced on a regular basis

What are the types of second-stage filters?

The same kinds of filters are used for the second stage as for the first stage.

What are the types of final-stage filters?

Media bags with an air-to-medium (cloth) ratio of no more than 10 CFM/sq. ft.(10 cubic feet per minute of air to a square foot of medium)
Rigid cell: 250-500 FPM face velocity
Cartridge filters with an air-to-medium ratio of 10 CFM per square foot maximum

Are some filters more effective than others?

For first-stage filters, experimental work has shown that metal mesh filters were as efficient as the other designs, and they experienced lower pressure drop. Efficiencies for metal mesh filters can be significantly increased with only modest increases in pressure drop.
For second-stage filters, electrostatic precipitators have generally been found to be as efficient as pocket filters. They experience very low pressure drops, require only moderate maintenance, and provide long service life. Other filters, such as pocket filters, lose their efficiency more rapidly, but in some applications can last up to a year. For mineral oil, up to 30% of the mist entering the system can be expected to evaporate and pass through the filter as vapor. For some mineral oils, collectors with multiple stages had the lowest overall efficiency (still quite acceptable), but the electrostatic precipitator provided the highest overall efficiency, perhaps because the oil droplets were removed from the air stream and drained away before they could evaporate.
For third-stage filters, all 95% DOP filters have high efficiency for droplets of all sizes, but the lifetime efficiency of these final-stage filters depends on the efficiency of the first- and second-stage filters.
A useful discussion of the costs of controlling MRF mists can be found in the Proceedings of the November 13-16, 1995 AAMA symposium, The Industrial Metalworking Environment Assessment & Control (page 321).
Does it matter where the mist collector discharge is located?
The discharge of the mist collector can be directed back into the shop or it can be directed outdoors through the roof or wall of the building. Each method of discharge has its supporters.
Discharging the cleaned air back into the shop can save energy in some instances, since the air does not need to be replaced by supply air. Possible disadvantages of this method are that an improperly operating mist collector will return some mist to the shop. Also, vapors are not removed by the filters and these may contribute to mist levels in the shop or contribute to odor problems.
Discharging the mist collector exhaust from the building eliminates the possibility of increasing the indoor mist level and it eliminates moisture and vapors from the building. The disadvantages can be increased need for building supply air and increased energy costs. There may also be a need to obtain an EPA permit for venting the process air from the building.

What if air is recirculated?

Where recirculation of exhaust ventilation is used,

The air must be adequately cleaned of contaminants, chemical and microbial, before it is recirculated.
Equipment used to clean air should be efficient enough to meet rigorous collection standards and to maintain their efficiency over time.
Monitoring of recirculated air should be performed often enough to assure that contaminant levels do not exceed established limits.

 

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