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"Distribution Technology - CORRECT ANSWER=> any arrangement of equipment and/or material that distributes sewage within and on-site sewage system." "Drainfield - CORRECT ANSWER=> subsurface soil absorption system, and soil dispersal component" "Drainrock - CORRECT ANSWER=> cleaned washed gravel or crushed rock ranging in size from 3/4" to 2.5", and containing no more than two percent by weight passing a US No.8 sieve and no more than one percent by weight passing through a US No. 200 Sieve." "Effluent - CORRECT ANSWER=> liquid waste discharged to a septic tank or other on-site sewage system" "Expanding Clay - CORRECT ANSWER=> means a clay soil with the mineralogy of clay particles. Clay particles expand when absorbing water" "expansion - CORRECT ANSWER=> a change in residence, facility or site that results in the quantity of sewage to exceed the original design" "Extremely gravely - CORRECT ANSWER=> soils with 60% or more, but not less than 90% rock fragments by volume."
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distributes sewage within and on-site sewage system."
2.5", and containing no more than two percent by weight passing a US No.8 sieve and no more than one percent by weight passing through a US No. 200 Sieve."
system"
particles expand when absorbing water"
sewage to exceed the original design"
fragments by volume."
health by inadequately treating the sewage, or creating a potential direct or indirect contact between sewage and the public."
animals that are cultured in standard tests. Generally expressed as colonies per 100 ml."
washing machines, and dishwashers."
permanently, or as the result of the tides."
no discharge outlet"
step, expressed as gallons per square foot per day, (gal./sq.ft./day)"
agriculture and petroleum extraction and refining"
component to which effluent is applied and through which effluent moves into original, undisturbed soil or other porous treatment media."
systems or components"
components functioning as designed"
coherent of solid mass not separated into peds of any kind"
When disturbed, soil material parts into mixture of whole peds, broken peds, and material that is not in peds."
which is performed by observations and measurements, to determine if the system is functioning as intended and if system is in need of maintenance."
or nearby the property it serves. that conveys, stores, treats, and/or provides subsurface soil treatment and dispersal of sewage. It consists of a collection system, a treatment component or treatment sequence, and a soil dispersal component."
system that is protected and maintained for replacement of the OSS upon its failure"
wastewater from a domestic home"
of water and the growth of roots."
or more; for example, pebbles, cobbles, stones, and boulders."
excavation are designed to dispose septic tank effluent, also called "dry wells""
within septic tanks, pump chambers, holding tanks, and OSS components"
kitchen, bath, and laundry wastes from residences, buildings, industrial establishments or other places."
temperature and dissolved oxygen,"
holding tank, grease interceptor, recirculating filter tank or any other tanks as they relate to on-site sewage systems including tanks for use with proprietary pruducts"
component into the soil dispersal , final treatment and recycling"
the soils capacity to act as an acceptable treatment and dispersal medium for sewage"
Certified Soil Scientist"
fragments as described in WAC 246-272A-0220 (2)(e)"
when soil is disturbed, and the soil material separates mainly into peds when removed,"
58.17, including both long and short subdivisions, planned unit developments, including mobile home parks"
that can deliver small, precise doses of effluent to soil surrounding the drip distribution pipping."
trenches of beds containing either a distribution pipe within a layer of drainrock covered with a geotextile, or a approved graveless distribution technology, designed and installed in original, undisturbed soil, with either gravity or pressure distribution of the treated effluent"
artificial unlined depressions for a significant periods of the year."
intervals."
further treatment and/or disposal into a soil enviornment"
separation and soil type with treatment components"
three feet or less"
(B) Flow from a mobile home site in a mobile home park (C) Four hundred and fifty gallons of sewage per day where the proposed development is not a single family residence or mobile home park"
volume"
seasonal"
determine the depth to a water table for locating an OSS (B) used to monitor the affects of an OSS (C) an interceptor or curtain drain constructed to lower the water table"
drain field and reserve drain field ~ 5' from sewage tank, and distribution box ~ 2' from building sewer and non-perforated distribution line"
drain field ~ 5' from sewage tank, and distribution box ~ N/A from building sewer and non-perforated distribution line"
~ 5' from sewage tank, and distribution box ~ N/A from building sewer and non-perforated distribution line"
~ N/A from sewage tank, and distribution box ~ N/A from building sewer and non-perforated distribution line"
~ 5' from sewage tank, and distribution box ~ N/A from building sewer and non-perforated distribution line"
~ 10' from edge of drain field and reserve drain field ~ N/A from sewage tank, and distribution box ~ N/A from building sewer and non-perforated distribution line" "Down-gradient cuts or banks with less than 5 ft. of original undisturbed soil above a restrictive layer due
reserve drain field ~ N/A from sewage tank, and distribution box ~ N/A from building sewer and non-perforated distribution line" "Down-gradient cuts or banks with at least 5 ft. of original undisturbed soil above a restrictive layer due
reserve drain field ~ N/A from sewage tank, and distribution box ~ N/A from building sewer and non-perforated distribution line"
"Other adjacent soil dispersal components/subsurface storm water infiltration systems Set backs: -
~ N/A from sewage tank, and distribution box ~ N/A from building sewer and non-perforated distribution line"
Gravelly and very gravelly coarse sands, all extremely gravelly soils excluding soil types 5 and 6, all soil types with greater than or equal to 90% rock fragments."
Coarse sands."
Medium sands, loamy coarse sands, loamy medium sands."
Fine sands, loamy fine sands, sandy loams, loams."
Very fine sands, loamy very fine sands; or silt loams, sandy clay loams, clay loams and silty clay loams with a moderate or strong structure (excluding platy structure)."
Other silt loams, sandy clay loams, clay loams, silty clay loams." "Soil Type Descriptions: Soil Type: 7
Sandy clay, clay, silty clay, strongly cemented or firm soils soil with a moderate or strong platy structure any soil with a massive structure any soil with appreciable amounts of expanding clays."
"Treatment Component Performance Levels and Method of Distribution (Vertical Separation in inches) :
1.) A - pressure with timed dosing 2.) B - pressure with timed dosing 3-6.) B - pressure with timed dosing" "Treatment Component Performance Levels and Method of Distribution (Vertical Separation in inches) :
1.) B - pressure with timed dosing 2.) B - pressure with timed dosing
nonresidential source, three times the design flow"
-Soil Textural Classification Description -Loading Rate for Residential Effluent Using Gravity or Pressure Distribution (gal./sq. ft./day)"
and the local health officer;"
department;"
surface water from accumulating over any component of the OSS."
site sewage system with very special and limited applications. Simply, the HTSS provides a means to collect and temporarily store sewage from a facility or dwelling, for subsequent removal and transport to an approved treatment and disposal site."
incorporates a holding tank, the services of a sewage pumper/hauler, and the off-site treatment and disposal of the sewage generated at the site served by the HTSS."
specific information and requirements for pumping service frequency and approved disposal of holding tank contents."
system must be designed and installed such that no overflow is allowed, other than within the structure at the elevation of the lowest fixture served."
the holding tank system should direct surface water flow away from the tank and access points."
throughout the holding tank system must be able to function as designed while exposed to sewage, sewage gases, and physical forces caused by repeated tank filling and pumping which is inherent to system operation."
treatment facility approved by the Department of Ecology; or, Other treatment and disposal sites approved by the local health officer."
installation must be inspected by the local health officer before use."
the tank, tested at site after installation, by filling with water;"
high groundwater areas or conditions;"
of the service access(es), access ports, risers, lids, and covers;"
the lids and covers from inappropriate or unapproved access;"
venting provided by the design and the installation. Venting should exhaust above the roof line of the building;"
surfaces around the access ports, equipment and methods for cleaning sewage spills; and"
going service contract on the property deed"
addition to the initial installation permit), with the requirement for maintaining a service contract;"
provide O&M assurance. Examples of management entities include: cities & towns, public utility districts, water & sewer districts, special-use districts, and corporations with demonstrated capacity to assure long-term management."
to sun and wind where evaporation and transpiration will be maximized."
in drainage ways, depressions, or areas subject to flooding."
around the mound."
consider drainage constraints for both upgradient and downgradient area drainage. The local health officer may require additional site evaluations and/or testing to analyze the site before siting the mound system."
the mound can be situated such that the effluent can move laterally down both slopes. The level site allows lateral flow in all directions, but may present problems as the groundwater mound that develops under the mound may rise to the ground surface beneath the mound in slowly permeable soils. The most common application is the sloping site where all the liquid moves in one direction away from the mound (Figure 3). However, proper design can overcome this limitation. The mound should be placed on the upper portions of the slope, not at the base of the slope. On a site with a complex slope (two directions), the mound should be located so that the treated wastewater is not concentrated in one area downslope."
trees or large boulders are less desirable for installing a mound system because of difficulty in preparing the surface and because of the reduced infiltration area (exposed soil) available beneath the mound. Tree roots, stumps and boulders are like rock fragments, they occupy space, and thus reduce the amount of soil available for receiving and transmitting treated wastewater away from the mound area."
stumps cut off at ground level rather than disturbing the native soil by removing them. A larger-than- normal mound area may be necessary if many, or large, stumps or boulders are involved, so sufficient soil is available to accept the effluent. The amount of increased basal area and/or mound size should be technically justified and sufficient to make up for the soil infiltration area lost to the tree trunks, stumps, and boulders."
system extra care and consideration must be given to adequately prepare the soil infiltrative surface under less-than-ideal conditions. Such a site may very well necessitate meticulous hand spading of part or all of the area under the mound. Like the amount of additional area required to make up for the lost infiltration area, the method employed and care required to satisfactorily prepare the site is a designer's responsibility."
meet the minimum vertical separation requirements specified by WAC 246-272A-0230 and WAC 246- 272A-0280. See Table 5 for possible applications for mounds consistent with the vertical separation requirements in rule. A minimum of 12 inches of undisturbed, unsaturated, original soil as measured from the original ground surface is required for placement of a mound after all clearing, leveling and other site disturbance during lot development is complete."
inches of undisturbed, unsaturated, original soil as measured from the original ground surface is required for mounds meeting the treatment component performance level effluent of Treatment Level C. (See 3.8.2)."
inches of undisturbed, unsaturated, original soil as measured from the original ground surface is required when the mound is preceded by a treatment technology identified on the List of Registered On- site Treatment and Distribution Products as meeting Treatment Level A or B and (See 3.8.3):"
for dispersal only, or"
minimum of 24 inches of media depth and is being used on a site with conditions requiring Treatment Level A."
site evaluation indicates the depth of soil to a water table is less than 18 inches, there is a need to confirm that there are at least 12 inches during the wet season. Therefore when there is any doubt that there is sufficient unsaturated soil depth, the permit should be held for a wet season evaluation to identify accurately the location of high water tables. As potential vertical separation (or soil depth)
distribution system must be designed in accordance with the Recommended Standards and Guidance for Pressure Distribution or Recommended Standards and Guidance for Subsurface Drip Systems. Design, layout, and installation of the pump chamber-to-mound transmission line must consider, and satisfactorily address, the potential for channeling groundwater or surface water to either the mound or the pump chamber causing infiltration-related problems."
monitoring ports, one placed in the infiltration bed down to the gravel-sand interface (except where subsurface drip distribution system is used), and one downslope from the bed down to the sand-native soil interface. Another useful monitoring port would be installed through the sandnative soil interface into the native soil several inches. See Figure 9 for examples of monitoring ports and anchoring methods"
egress for construction vehicles, assuring that adequate protection is afforded the mound, and surrounding areas, especially downslope areas. The mound system, including the area around the base and downslope, must be protected to prevent damage caused by vehicular, livestock, or excessive pedestrian traffic."
submitted as a part of the project design"
reserve area is not subject to damage or soil compaction from vehicular or other site development activity."
temporary construction fence or protective barrier around the proposed mound, designated reserve, and the adjacent area (particularly downslope from the primary and reserve mound sites) to assure that the area is not damaged by other construction activity before installation of the mound system. These areas must be unmistakably identified on the site so as to preclude potential site damage. Such fencing or identification is the responsibility of the sewage system designer."
specifications for proper grading, diking, ditching and subsurface drainage to prevent the intrusion of off- site surface and subsurface waters into the mound area,"
installation equipment and construction procedures. (See Appendix G. Site Preparation and Construction.)"
a mound system are just as critical as the design of the system. Good design with poor construction will result in system failure. It should be emphasized that the soil must only be worked when the moisture
content is low to avoid compaction and puddling. Consequently, installations must be made only when the soil is as dry as required. The approved construction plan must be followed."
provide biodegradation and decomposition of wastewater constituents by bringing the wastewater into close contact with a well-developed aerobic biological community attached to the surfaces of the filter media."
unsaturated downward flow of the effluent through the filter media. The filter media may be mineral sand or equivalently sized crushed glass meeting one of the media."
in a watertight vessel below the surface of the ground, or wholly or partially elevated in a containment vessel. Proper function requires that influent to the filter be distributed over the media in controlled, uniform doses."
dosing, these systems require timed dosing with associated pump chambers, electrical components, and distribution network, with a minimum of 4 to 18 doses per day (depending on the sand media) spread evenly over a 24-hour period. Filtrate (treated effluent) is collected and discharged from the bottom of the sand filter by either a gravity discharge underdrain or a pump discharge underdrain."
sites with shallow soil conditions where treatment must be accomplished before the effluent is discharged into the soil. Intermittent sand filter effluent may be dispersed to a soil profile containing as little as 12 inches of vertical separation in soil types 2 through 6. Intermittent sand filters are also used as part of a mitigation strategy when horizontal separations are reduced."
sited, designed, installed, operated, and maintained, an intermittent sand filter system consistent with these recommended standards and guidance is expected to achieve treatment performance equal to Treatment Level B." "Intermittent Sand Filter Systems: 2. Application Standards,
for intermittent sand filters are the same as required for sewage tanks (WAC 262-272A-0210)." "Intermittent Sand Filter Systems: 2. Application Standards,
technology and are included in the Department of Health's List of Registered On-site Treatment and Distribution Products (Registered List) as a Category 1 treatment technology" "Intermittent Sand Filter Systems: 2. Application Standards,
levels become increasingly critical to the on-site sewage system design, function, and the protection of public health." "Intermittent Sand Filter Systems: 3. Design Standards
required. The dosing frequency or dose volume is dependent on the media specification used with the sand filter. To assure that appropriate dose volumes are delivered to the sand filter, the timer must be set to dose the filter at the following minimum dosing frequency:" "Intermittent Sand Filter Systems: 3. Design Standards
Number of Doses/Day :
doses/day) very little effluent is applied to the filter at any one dose resulting in unsaturated film-like flow. If the dose volume exceeds the water holding capacity of the filter media, the applied liquid fills the pore spaces allowing the wastewater to pass through the filter untreated. However, if the dose volume does not exceed the water holding capacity of the media, the applied wastewater will flow around the sand grains in a thin film maximizing oxygen diffusion, and maximizing contact between the organics in the effluent and the microbial growth on the media. The filter media meeting the Coarse Sand Media specification has a lower water holding capacity than the sand meeting the ASTM C-33 specification. Thus, a smaller dose volume or higher dosing frequency is required to promote the unsaturated film-like flow. Because of the larger unit wetted surface area of ASTM C-33 sand, a larger volume of wastewater may be applied at one time without exceeding its water holding capacity. The large surface allows unsaturated flow conditions to occur at a higher dose volume or lower dosing frequency"
either mineral sand or equivalently sized crushed glass."
Membrane Lined Pit"
as the parent membrane material" "Intermittent Sand Filter Systems: Containment Vessel Standards (B. Installation Standards) 2. Site
foundation to accept the liner must be stable and structurally sound including appropriate compaction. Make sure the potential for sink hole development and differential settlement is avoided;"
"Intermittent Sand Filter Systems: Containment Vessel Standards (B. Installation Standards) 2. Site
chemical binding agents must not adversely affect the membrane because they are potentially abrasive agents."
the liner must be protected by being fully buried. In cases where portions of the liner may be subjected to direct exposure to the weather, the exposed portions of the liner must be covered. A construction option to accomplish this is to install a finish rim over the exposed liner portions."
follow settlements within limits. Unreasonable strain reduces thickness and may reduce life expectancy by lessening the chemical resistance of the thinner (stretched) material. Membrane liners must be installed to minimize strain (or elongation to the fabric) anywhere in the flexible membrane liner system;" "Intermittent Sand Filter Systems: Containment Vessel Standards (B. Installation Standards) 5.
(1) Sand to "bed" liner, at a minimum depth of 3 inches to protect liner from punctures," "Intermittent Sand Filter Systems: Containment Vessel Standards (B. Installation Standards) 5.
(2) A non-woven, needle-punched synthetic geotextile fabric with a thickness strong enough to protect the liner." "Intermittent Sand Filter Systems: Containment Vessel Standards (B. Installation Standards) 5.
(3) Grade the bottom to provide a sloping liner surface, from the outside edge of the filter toward the point of underdrain collection. Slopes must be equal to 8 inches fall overall or 1 inch of fall per 1 foot of run, whichever is the greater." "Intermittent Sand Filter Systems: Containment Vessel Standards (B. Installation Standards) 5.
of possible puncture points from foreign objects." "Intermittent Sand Filter Systems: Containment Vessel Standards (B. Installation Standards) 5.
desirable temperature range for membrane installation is 42° F to 78° F. Lower or higher temperatures may have an adverse effect on transportation, storage, field handling and placement, seaming and backfilling and attaching boots and patches may be difficult. Installing liners outside the desirable temperature range should be avoided at all times"