The main disadvantage is the requirement for very clean water. The small orifice or emitter through which the water must pass can easily be clogged by soil particles, organic matter, minerals and sediment in the water and by algae growth. Other disadvantages are the limited area covered by each application device, potential animal, insect, or mechanical damage, greater design and maintenance requirements, often higher initial investment and replacement cost, and the high level of management required.
Figure 1 shows most of the components of a low volume system. The type of pump selected is normally governed by the water source. Straight centrifugal or self-priming centrifugal pumps are generally used on surface water sources. However, submersible or turbine pumps, which are normally used in wells, can be used on surface water supplies.

Figure 1. Schematic of the components of a low volume irrigation system.
Power sources include electric, internal combustion engine (gasoline, liquid petroleum and diesel) and tractor PTO. Electric power is required for submersible pumps. The other types of pumps can be operated by any of the power sources. If the system is to be automated, electric power is preferred. High efficiency pumps should be selected whenever possible.
Filters and water distribution devices are discussed elsewhere in this paper. The pipe distribution system includes main line, sub-mains, manifolds pipe and lateral lines. The type of water distribution device (line source, point source and micro- spray, micro-spinner, and spray stake) determine some of the system hardware. The line source system includes the lateral line as an integral part of the emission device. The tube is manufactured of polyethylene (PE) plastic with a wall thickness of 4 to 25 mil. Generally, at least 8 mil wall thickness is recommended. If the tube is to be used for more than one season, a thicker wall is recommended. Most of the line source systems use a 0.5 inch diameter lateral line.
The lateral line for point source systems is normally high carbon, low density PE pipe. Wall thickness is normally 30 to 50 mil. Tube inside diameter will vary from 0.375 to 1 inch. The micro-sprinklers normally use a PE or polyvinyl chloride (PVC) plastic lateral line. A PE micro-tube conveys water from the lateral line to the micro-sprinkler.
Submains or manifold can be layflat hose, PE pipe or PVC pipe. Main line is normally PVC pipe, but layflat hose, PE pipe or metal pipe can be used.
Controls and monitoring equipment can simply be gate valves, check valves and pressure gages. For larger, more complicated systems, many are equipped with automatic controllers, electric or hydraulic valves, water meters, soil moisture monitoring equipment, and back flow prevention. Automatic controls and valves allow greater flexibility in operation of the system. A water meter allows the user to determine how much water is being used. Daily monitoring of the water meter will indicate when emitters or orifices are becoming clogged or when there is a significant leak in the system. Soil moisture equipment gives information on the adequacy of irrigation. Back flow prevention equipment protects water supplies from chemicals or fertilizers that might be back-siphoned into the water supply.
Fertilizer injectors allow the grower to add fertilizer on a regular basis. This should lead to yield increases and prevent fertilizer from leaving the site, either as deep seepage or as surface runoff. If chemicals are needed to adjust water quality, a chemical feed pump is needed. Also limited chemigation (mainly herbicides and nematocides) can be accomplished through the low volume system.

Figure 2. Schematic of a line source irrigation system typically used with vegetable crops such as tomatoes.

Figure 3. Schematic of a point source low-volume irrigation system typically used with nursery container and tree fruit crops.

Figure 4. Discharge rate variation as influenced by emitter design-pressure versus non-pressure compensating.
Both turbulent and laminar flow emitters are available. Also pressure compensating emitters and non-pressure compensating emitters are supplied. Most non-pressure compensating emitters are designed to operate at approximately 15 psi. The pressure compensating emitters will operate at 10 to 60 psi with approximately the same discharge rate. Normal discharge rates are 0.5, 1.0 or 2.0 gallons per hour (gph) for both pressure compensating and non-pressure compensating emitters. A few manufacturers provide emitters with flow rates lower than 0.5 ggh. Figure 4 shows the discharge (emitter flow rate) versus pressure from a nominal 1 gph emitter. Note that discharge rate is more constant for the pressure compensating emitter than for the non-pressure compensating emitter. Because of the more complex design, pressure compensating emitters have a higher initial cost.
There are also multi-outlet emitters, where up to six micro-tubes can be attached to irrigate areas around the emitter. Most point-source systems are designed to irrigate tree, shrub and vine crops. However, they can be used for row crops.

Figure 5. Schematic of micro-spray, micro-spinner, and spot spitter.

Figure 6. Schematic of spot spitter in a container.
Filtration may include filters to remove materials found in the water and possibly chemical adjustment of the water. Filters are normally divided into primary filters and secondary filters. It is generally accepted that a sand media filter is the best primary filter and is a necessity for surface water supplies. Mechanical filters such as screen filters, sand separators and disc filters, may also be used as primary filters for ground water supplies. Minerals in ground water may require the addition of chemicals such as acids, chlorine and softeners to ensure satisfactory operation of the filters. Screen filters, "and separators, disc filters, in-line Y- strainers and cartridge filters are generally considered to be secondary filters. The primary filter is normally located next to the water source and the secondary filters are located nearer the point of delivery to the lateral lines. Figure 7 shows schematics of some of the different types of filters.

Figure 7. Schematic of several types of filters used for low volume irrigation.
Chemicals, such as acids, chlorine, softeners, etc. are normally injected near the water source. Injection can be continuous feed or intermittent, depending on water quality. Individual chemicals or mixtures of chemicals may be injected.
Filters require cleaning (backwashing, flushing, or physical cleaning) to remove contaminants. If this is neglected, the filter becomes clogged and contaminants enter the drip system. Pressure drop across the filter is used as a guide on the frequency of cleaning. Generally, if the pressure drop exceeds 5 psi, the filter should be cleaned. Pressure gages should be placed on either side of the filter to indicate when cleaning is needed based on pressure drop across the filter. Sand media filters should be installed in tandem to allow filtered (clean) water to be used for backwashing. Water is forced back through the filter in the opposite direction to the filtering process to clean the filter and remove contaminants. Screen filters and disc filters may be flushed, backwashed or physically cleaned. Sand separators are normally flushed. (Contaminants are removed by opening a valve and letting water wash them out.)
Design rules for low volume systems are modified from those normally used for other types of irrigation systems. This is especially true for those systems using non-pressure compensating emitters or orifices. Since these systems operate at low pressure and it is desirable to have uniform discharge from each orifice, there can be little variation in pressure. For example, a line source system that requires 8 psi at the orifice should have a maximum pressure differential in the field of 1.6 psi (.20 x 8 of psi = 1.6 psi). The pressure loss should be divided between the sub-main and/or header in the field and the laterals.
The pressure loss should be proportional as follows: not over 45 percent in the sub-main and/or header and not over 55 percent in the lateral. For the system with orifice operating pressure of 8 psi, pressure drop in the sub-main and/or header should not exceed 0.72 psi. Pressure drop in the lateral should not exceed 0.88 psi. In practice, what the designer tries to accomplish is to have approximately 8 psi pressure at the head of each lateral. At the end of the lateral, pressure should be no less than 7.12 psi. In the header or sub-main supplying a group of laterals, pressure should not be greater than 8.72 psi.
If the field has elevation differences, it may be necessary to install pressure regulators on the main, sub-main, or header pipes. If laterals have to be installed on a slope, the laterals should be run down slope rather than upslope. This allows elevation change to counteract pipe friction loss.
The most efficient design is to zone field(s) so that a portion of the field is irrigated at one time. Once that section or zone is irrigated, another zone is irrigated. This allows the use of smaller pumps, power units, and main line. For vegetable crops, the most efficient irrigation is to operate each zone for 10 to 20 minutes at one time and then switch to another zone. To meet daily water needs, each zone might operate four to six times per day.
It is possible to utilize the same procedure for point-source emitters and micro-sprinklers or spray stakes. Certainly the designer needs to consider ways to minimize system initial cost and yet have a design that will meet peak crop water needs.
As water temperature increases, viscosity decreases and water discharge can increase. With uniform orifices or emitters and no friction loss in the lateral line, this can cause those emitters most distant from the header pipe to have a higher flow rate than the emitters closest to the header pipe. Water temperature can increase due to the flow of the water through the pipe. Sizes of main line pipe, header pipe and lateral line need to be considered in system design to insure that pressure loss due to friction does not adversely affect orifice discharge. This is more important for non-pressure compensating orifices than for pressure compensating emitters. It is equally important to consider the elevation changes on water pressure. For each 2.31 feet of change, there is a 1 psi differential.
In areas where there is considerable elevation difference, high pump pressure may be required to provide adequate pressure at the highest elevation. Pressure regulators are needed to reduce that pressure at lower elevations. It may not be possible to overcome this problem, but it should be considered in the design.
Inadequate backwashing or flushing of filters can increase pressure and horsepower requirements. Ignoring leaks, clogged or partially clogged emitters, orifices or spray nozzles, dirty filters and/or pump and power unit performance will lead to inefficiency. Using main line, header pipe, or laterals that are too small will increase friction loss and lead to inefficiency and non-uniform water application. Selecting an inefficient pump, a pump with too high pressure, or an improperly matched pump and power unit can increase pumping costs. At times, using pressure compeneating emitters rather than non-pressure compensating emitters with a couple of pressure reducing valves can reduce efficiency.