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• Dripline <br />• Emitters <br />• Vacuum release valve <br />• Return manifold <br />• Flush valve <br />• Controller <br />The pump draws wastewater effluent from the dose <br />tank, preferably on a timed cycle, to dose the <br />distribution system. Before entering the network, <br />the effluent must be prefiltered through mechanical <br />or granular medium filters. The former are used <br />primarily for large SWIS systems. The backflush <br />water generated from a self-cleaning filter should <br />be returned to the headworks of the treatment <br />system. The effluent enters the supply manifold <br />that feeds each dripline (figure 4-17). If turbulent <br />flow emitters are used, the filtered wastewater must <br />first pass through a pressure regulator to control the <br />Figure 4-17. Pressure manifold and flexible drip lines <br />prior to trench filling <br />Source: Ayres Associates. <br />maximum pressure in the dripline. Usually, the <br />dripline is installed in shallow, narrow trenches 1 to 2 <br />feet apart and only as wide as necessary to insert <br />the dripline using a trenching machine or vibratory <br />plow. The trench is backfilled without any porous <br />medium so that the emitter orifices are in direct <br />contact with the soil. The distal ends of each <br />dripline are connected to a return manifold. The <br />return manifold is used to regularly flush the <br />dripline. To flush, a valve on the manifold is <br />opened and the effluent is flushed through the <br />driplines and returned to the treatment system <br />headworks. <br />Because of the unique construction of drip distribu- <br />tion systems, they cause less site disruption during <br />installation, are adaptable to irregularly shaped lots <br />or other difficult site constraints, and use more of <br />the soil mantle for treatment because of the shallow <br />depth of placement. Also, because the installed cost <br />per linear foot of dripline is usually less than the <br />cost of conventional trench construction, dripline <br />can be added to decrease mass loadings to the <br />infiltration surface at lower costs than other <br />distribution methods. Because of the equipment <br />required, however, drip distribution tends to be <br />more costly to construct and requires regular <br />operation and maintenance by knowledgeable <br />individuals. Therefore, it should be considered for <br />use only where operation and maintenance support <br />is ensured. <br />The dripline is normally a ''V2 -inch -diameter flexible <br />polyethylene tube with emitters attached to the <br />inside wall spaced I to 2 feet apart along its length. <br />Because the emitter passageways are small, friction <br />losses are large and the rate of discharge is low <br />(typically from 0.5 to nearly 2 gallons per hour). <br />Two types of emitters are used. One is a "turbulent - <br />flow" emitter, which has a very long labyrinth. <br />Flow through the labyrinth reduces the discharge <br />pressure nearly to atmospheric rates. With increas- <br />ing in-line pressure, more wastewater can be forced <br />through the labyrinth. Thus, the discharges from <br />turbulent flow emitters are greater at higher <br />pressures (figure 4-18). To more accurately control <br />the rate of discharge, a pressure regulator is <br />installed in the supply manifold upstream of the <br />dripline. Inlet pressures from a minimum of 10 psi <br />to a maximum of 45 psi are recommended. The <br />second emitter type is the pressure -compensating <br />4-28 USEPA Onsite Wastewater Treatment Systems Manual <br />