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On-Site Wastewater Treatment and Disposal Systems - Forced ...

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7.2.4.6 Considerations for Multi-Home <strong>and</strong> Commercial<br />

<strong>Wastewater</strong>s<br />

Designs of the mound system for larger flows follow the same design<br />

principles as for smaller flows. In cluster systems serving more than<br />

five homes, however, peak flow estimates can be reduced because of flow<br />

attenuation, but contributions from infiltration through the collection<br />

system must be included. Peak flow estimates should be based on the to-<br />

tal number of people to be served (see Chapter 4). Rates of infiltra-<br />

tion vary with the type of collection sewer used (19)(20).<br />

With commercial flows, the character of the wastewater is an important<br />

consideration. Proper pretreatment is necessary if the character is<br />

significantly different than domestic wastewater.<br />

Modifications to the design of the mound system may be desirable for<br />

larger flows on sloping sites or in slowly permeable soils. In both<br />

instances, the absorption area should be broken up into a series of<br />

trenches or smaller beds. This is beneficial on sloping sites because<br />

the beds can be tiered to reduce the amount of fill required (see Figure<br />

7-14). Depths of fill material below beds should not exceed 4 to 5 ft<br />

(1.3 to 1.7 ml because differential settling will cause the bed to set-<br />

tle unevenly. If the system is tiered, each trench or bed must be dosed<br />

individually. This can be done by automatic valving or alternating<br />

pumps or siphons.<br />

In sites with slowly permeable soils, breaking the absorption area into<br />

smaller trenches or beds helps distribute the effluent over much wider<br />

areas. Spacing of the beds or trenches should be sufficient so that the<br />

wastewater contributed from one trench or bed is absorbed by the natural<br />

soil before it reaches the lower trench or bed (see Table 7-10). The<br />

beds or trenches should be as long as the site allows. A long bed, bro-<br />

ken into several shorter systems, each served by a pump or siphon, is<br />

preferred over two or more short parallel beds, especially in soils<br />

where the effluent moves downslope.<br />

Flexibility in operation should also be incorporated into systems serv-<br />

ing larger flows, since a failure can create a significant problem.<br />

Alternating bed. 'systems should be considered. A three-bed system is<br />

suggested where each bed contains 50% of the required absorption area<br />

(19). Two beds are always in operation, providing 100% of the needed<br />

infiltrative surface. The third bed is alternated into service on a<br />

yearly schedule. Thus, each field is in service for two years <strong>and</strong><br />

"rested" for one year to rejuvenate. The third bed also acts as a<br />

st<strong>and</strong>by unit in case one bed fails. The idle fields can be put into<br />

service immediately while the failed bed is rehabilitated.<br />

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