What standards and references are used for the review and approval of engineering designs?
A number of standards and references are used by the Water and Wastewater Treatment Program for the review of engineering designs and as regulatory tools.
A list of commonly used standards and references is:
- ADEQ Bulletins
- MAG Standards
- EPA Standards and Guidelines – For example:
- American Water Works Association Standards
- NSF InternationalNSF 60 and NSF 61 Standards and Certifications
- "Wastewater Engineering: Treatment and Reuse", Metcalf and Eddy, ISBN No. 0070418780 - Reference book for wastewater treatment plant and reuse (reclaimed) water systems design
- "Design of Municipal Wastewater Treatment Plants - MOP 8, 4th Edition" (ASCE MOP 76), 3 Volumes, Water Environment Federation, ISBN No. 0-7844-0342-2 - Reference for wastewater treatment plant design
What treatment processes have been utilized on previously approved projects?
Water Treatment Processes
- Sedimentation
- Coagulation/Flocculation
- Filtration
- Membranes (electrodialysis reversal, micro, ultra, nano, reverse osmosis)
- Dissolved Air Floatation
- Clarification
- Ground Water Treatment (Arsenic, Nitrate, Fluoride, TDS, etc. removal) – Absorption, Ion Exchange, Coagulation & Filtration, Membranes, etc.
- Special Treatment – pH Correction, Polishing, Desalination, Brine Concentration, Evaporation, Distillation, Vapor Recompression, etc.
- Disinfection – Chlorine, UV, Ozone, Chlorine Dioxide, etc.
- Solids Handling – Thickeners, Presses, Centrifuges, Drying Beds, etc.
Wastewater Treatment and Water Reclamation Processes
- Sedimentation
- Activated Sludge/Extended Aeration
- Oxidation Ditches
- Sequencing Batch Reactors (SBRs)
- Clarification (Primary and Secondary)
- Coagulation/Flocculation
- Filtration
- Membranes (micro, ultra, nano, reverse osmosis)
- Dissolved Air Floatation
- Special Treatment – pH Correction, Polishing, Desalination, Brine Concentration, Evaporation, Distillation, etc.
- Disinfection – Chlorine, UV, Ozone, etc.
- Solids Handling – Aerobic/Anaerobic Digesters, Thickeners, Presses, Centrifuges, Drying Beds, Cyclones, etc.
- Effluent Disposal – Reuse, Recharge, Discharge
- Odor Control – Chemical Injection Systems, Dry and Wet Scrubbers, Biofilters, etc.
What information is required for a blending plan approval?
The following information should be included in the blending plan submittal package:
- A brief narrative describing the dilution and contaminant sources and the methodology used to achieve proper blending.
The narrative should detail how proper blending is to be maintained using manual or automatic controls, safety interlocks,
online analyzers and operational procedures.
- An analysis of possible failure modes which might affect the blending system and identification of any special conditions
such as emergency or seasonal operation of the blending system.
- If construction work is associated with the blending plan then design drawings are required as part of the blending plan submittal.
Otherwise, a sketch showing the existing configuration of the blending system, including major system components connected to the
blending system such as wells, reservoirs and booster pumps should be included in the blending plan submittal package.
- Identification of the Point-of-Entry downstream from the blending point.
- Laboratory analyses and reports documenting the contaminant concentrations of all dilution and contaminant sources. If sufficient
historical water quality data are available a 90th percentile value should be calculated for various sources' contaminant concentrations.
- The nominal flow rate and contaminant concentrations for each of the dilution sources.
- The nominal flow rate and contaminant concentrations for each of the contaminant sources.
- If a dilution or contaminant source is a well then the Arizona Department of Water Resources (ADWR) well identification number and the
physical address of the well should be provided.
- The physical address of the blending point. If a physical address is not available then the cross streets or GPS coordinates of the
blending point should be submitted.
- Identification of the point downstream of the blending point which will provide proper mixing of the blended stream (i.e. a static
mixer or storage reservoir) prior to the blended stream being discharged into the water distribution system.
What are the separation distance requirements for underground piping?
The separation distance for potable water and sewer pipelines located in the public right-of-way is governed by Arizona Administrative
Code (AAC) R-18-5-502.C. The separation distance for reclaimed water pipelines located in the public right-of-way is governed by AAC
R-18-9-602.F. The Maricopa Association of Government’s "Uniform
Standard Details for Public Works Construction" standards 404-1 and 404-2 detail the separation distance and protection requirements
for the installation of potable water, reclaimed water and sewer pipelines for MAG participants.
The separation distance between potable water and sewer pipelines from other pipelines such as non-potable ground, surface, irrigation,
storm, industrial, etc., pipelines located in the public right-of-way is not defined by the regulations or MAG standards. The MCESD
recommends that these non-potable pipelines:
- Be separated from potable water pipelines as specified by AAC R-18-5-502.C.
- Be located no closer than two feet vertically nor six feet horizontally from all other pipelines unless the non-potable pipeline is
encased in at least six inches of concrete or using mechanical joint ductile iron pipe or other materials of equivalent or greater
tensile and compressive strength at least 10 feet beyond any point on the pipeline conveyance within the specified minimum separation distance.
The MCESD will determine the separation distance requirements for these pipelines and pipelines not located in the public right-of-way on a case-by-case basis.
What are the design requirements for hose bibbs and hose stations?
The basic design requirements are as follows:
- Appropriate backflow prevention devices (for example vacuum breakers) must be installed at all hose bibs.
- Signage must be installed at all hose bibbs. Signs for non-potable water hose bibbs should state "Caution: Non-potable Water, Do Not Drink"
and display the international 'do not drink' symbol. Signs for reclaimed water hose bibbs should state "Caution: Reclaimed Water, Do Not Drink"
and display the international 'do not drink' symbol.
- Hoses and hose racks must be installed at all hose bibbs. This requirement may be waived for unmanned facilities which do not routinely require
clean-up or maintenance using hoses.
Is emergency power required for a water treatment plant?
Yes in most cases. The requirement is specified in the Arizona Department of Environmental Quality's (ADEQ) Engineering Bulletin No. 10, "Guidelines
for the Construction of Water Systems" in Chapter 4, Section A.4.
The only exception would be for:
- A plant that is 100 percent redundant to another potable water source (e.g. a surface water treatment plant or a groundwater well field)
that is capable of meeting the peak day demand for the water distribution area being served and the plant and the redundant potable water
source are on separate electrical grids or power supplies.
- A plant that is 100 percent redundant to another potable water source (e.g. a surface water treatment plant or a groundwater well field)
that is capable of meeting the peak day demand for the water distribution area being served and the redundant potable water source has
redundant feeds from two different electrical grids or an emergency power supply.
- A plant which serves a water distribution area that has sufficient system storage capacity to meet the peak day demand and it can be
demonstrated that the plant can be restored to normal operation within 24 hours after the interruption of service.
Requests for an exception will be reviewed and approved by the MCESD on a case-by-case basis.
Is emergency power required for groundwater production facilities?
Groundwater production facilities (typically a groundwater well, reservoir and booster pump station that do not treat the groundwater) usually
do not require emergency power. However, emergency power may be required to meet the regulatory requirements for the distribution system as
noted in next question below.
Is emergency power required for distribution system facilities?
The requirement for back-up power for distribution system facilities is driven by three Arizona Administrative Code (AAC) requirements as follows:
- R18-5-502.B - A potable water distribution system shall be designed to maintain and shall maintain a pressure of at least 20 pounds per
square inch at ground level at all points in the distribution system under all conditions of flow.
- R18-5-503.A - The minimum storage capacity for a CWS [community water system] or a non-community water system that serves a residential population
or a school shall be equal to the average daily demand during the peak month of the year. Storage capacity may be based on existing consumption and
phased as the water system expands.
- R18-5-503.B - The minimum storage capacity for a multiple-well system for a CWS [community water system] or a non-community water system that serves a
residential population or a school may be reduced by the amount of the total daily production capacity minus the production from the largest producing well.
Conformance with item 1 is usually implemented by the construction of one or more reservoirs to provide storage capacity for a distribution system service
area. Properly designed reservoirs located at the high water elevation of a service area can provide hydraulic head to maintain a nominal system pressure
of 20 psi. In some cases, isolated service areas may be fed by redundant supply sources instead of using reservoirs to maintain system pressure.
Conformance with items 2 and 3 is implemented by sizing the reservoirs to provide sufficient capacity to meet the required capacity for peak and fire flow
demands in combination with redundant supply sources feeding a distribution system service area such as surface water treatment plants, groundwater wells,
booster pump stations and pressure reducing valve stations.
Emergency power may be required for groundwater wells, booster pump stations and pressure reducing valve stations acting as a source of supply to isolated
service areas. For example, a service area with insufficient storage capacity fed by two other service areas via booster pump stations that are on the same
electrical grid would not conform to the AAC requirements as loss of power would result in a loss of pressure in the distribution system.
An engineering analysis of the distribution system should be performed when adding new or modifying existing groundwater wells, booster pump stations and
pressure reducing valve stations to determine if emergency power is required at these facilities. The analysis should calculate the required minimum storage
capacity for peak demand and fire flows and address the impact of system wide interruptions due to loss of power, major transmission pipeline ruptures and
equipment failure.
What are the requirements for equipment and process redundancy for a water treatment plant?
The Arizona Department of Environmental Quality's (ADEQ) Engineering Bulletin No. 10, "Guidelines for the Construction of Water Systems", Chapter 4, Section
A.4 states:
"Unless the treatment plant can be taken out of service for a period of time for maintenance and repair work, two or more of all
essential treatment units or items shall be provided. With one unit or item out of service, the remaining units or items shall meet the design capacity of the
plant. When deciding whether or not to install more than one unit, the consequences of failure of that unit should be considered."
An engineering analysis should be performed when designing a new or modifying an existing water treatment plant to determine what process units and types of
equipment require redundancy and increased reliability. The analysis should address the impact and the criticality of process interruptions and equipment failure
and assess the length of time the process or system would be out of service.
What are the requirements related to the rated capacity of a water treatment plant?
The rated capacity of a water treatment plant is based upon the ‘firm capacity’ of the facility. Firm capacity refers to the available capacity of a system or
process with the largest unit out of service. Thus, the reliability and redundancy of a water treatment plant's equipment and process units are integral to the
plant's firm capacity.
As noted in Question before, reliability and redundancy requirements are based on installed redundant equipment and process units. Using analytical or statistical
methods such as ‘predicted downtime', ‘mean time between failure’ or other types of failure mode analysis to justify the reliability of systems or processes within
a water treatment plant is not an acceptable means of determining the rated capacity of the plant. A water treatment plant's rated capacity is solely based on its
firm capacity.
The rated capacity of a water treatment plant is critical in determining when an expansion of a plant is required. The Arizona Department of Environmental Quality's
(ADEQ) Engineering Bulletin No. 10, "Guidelines for the Construction of Water Systems", Chapter 4, Section A.6 states:
"Expansion of the plant is indicated when the maximum daily demands of the system approach the rated capacity of the existing plant. As a
general rule, steps to provide additional treatment capacity should be taken at least 5 years before present capacity is reached to allow sufficient time for engineering
investigations, design, financing and construction"
What are some key issues when converting a groundwater production facility to a water treatment plant?
A number of key issues need to be addressed when converting an groundwater production facility to a water treatment plant:
- Physical Space Limitations - A typical groundwater production facility consists of a well, reservoir and booster pump station. The addition of treatment process
equipment may exceed the physical size of the existing site.
- Access and Visibility - Access to an existing site may be constrained or limited. Sites in residential areas may have to be accessed only during daylight hours
and may require architectural features to provide a level of aesthetics compatible with the neighborhood.
- Noise and Lighting - Noise associated with new treatment equipment may be an issue if the site is located in a residential neighborhood or has neighbors in
close proximity. Lighting may have to be muted as compared to what is typical for a water treatment plant.
- Special Use Permit - For facilities located in unincorporated areas of the County a special use permit is required to be obtained from the
Maricopa County Planning and Development Department. Similar types of permits
may be required for facilities located in incorporated areas of the County by the city or town which has jurisdiction.
- Waste Streams - Treatment processes typically generate solid and/or liquid waste streams. Storage and the disposal of these streams can be problematic. Storage
basins may have to be covered to provide vector control.
- Emergency Power - Emergency power is required for water treatment plants. See the very first question on top for additional details.
- Reliability - Reliability may have to be increased when converting a groundwater production facility to a water treatment plant.
- Operator Certification - Groundwater production facilities are operated by Water Distribution certified operators. Water treatment plants must be operated by
Water Treatment certified operators.
What are the design requirements for venting wet wells, clearwells, tanks and reservoirs?
The requirements are specified in the Arizona Department of Environmental Quality's (ADEQ) Engineering Bulletin No. 10, "Guidelines for the Construction of Water
Systems", Chapter 6, Section E.9.
In addition to the installation of inverted 'U' type vents, MCESD also allows the use of recent designs such as 'chair' or cross-flow vents provided these vents
have an air flow direction change of 90 degrees in the horizontal plane prior to air entering/leaving the containment vessel.
In all cases, vents shall have a 16-mesh corrosion resistant screen installed to prevent the ingress of birds and insects.
What are the design requirements for wet well, clearwell, tank or reservoir overflows?
The requirements are specified in the Arizona Department of Environmental Quality's (ADEQ) Engineering Bulletin No. 10, "Guidelines for the Construction of Water
Systems", Chapter 6, Section E.6.
In addition to the installation of overflow piping with a 16-mesh corrosion resistant screen, MCESD also allows the use of alternative designs such as the use of
counterweighted flapper valves or self-sealing valves that will open and close automatically when an overflow occurs.
In all cases, overflows shall have a 16-mesh corrosion resistant screen installed or provide a mechanical means of sealing the overflow opening to prevent the
ingress of birds and insects.
If the overflow from a storage vessel is not connected to a sewer or storm water system a suitable means on onsite containment must be included in the design.
Onsite retention basins with riprap line channels and sides are typically used to contain an overflow and prevent erosion. Care should be taken in the design
to insure that underground vaults and access points are not located in close proximity to overflow channels or retention basins.
What are the design requirements for entry hatches on wet wells, clearwells, tanks and reservoirs?
The requirements are specified in the Arizona Department of Environmental Quality's (ADEQ) Engineering Bulletin No. 10, "Guidelines for the Construction of
Water Systems", Chapter 6, Section E.8.
Entry hatches shall be constructed with seals to prevent the entry of unsafe water, birds and insects into the containment vessel. Typical entry hatch designs
include frames with integral curbs and frame overlapping covers with rubber or plastic seals.
Can pump seal water be discharged to a pump wet well?
Pump seal water shall only be discharged to a wet well if the seal water is free of contaminants and of equal water quality to the water contained in the
wet well. A finished water pump utilizing plant service water for the pump seal water source cannot discharge the seal water into the wet well as this
installation would be a cross connection between potable and non-potable water systems.
Is emergency power required for a wastewater treatment plant and collection system lift stations?
Yes in most cases. Maricopa County Environmental Health Code (MCEHC) Chapter I, Section 2, Regulation 5 states:
"For systems that treat, or which are designed to treat greater than 10,000 gallons/day, a standby power source shall be provided at
all sewage treatment systems and/or pump stations where a temporary power failure may allow a discharge of raw or partially treated sewage. Standby power
may be via a standby generator, separate feeders from separate substations, a loop feeder on separate transformers from a common substation, or a high-level
alarm with portable generators. Standby power also shall be provided to any sewage treatment systems and/or pump stations, regardless of size, if a temporary
power failure may allow a discharge into surface waters classified as 'Unique Waters', by the Arizona Department of Environmental Quality."
Is emergency power required for collection system odor control stations?
No. However, the MCESD may require emergency power be installed on an odor control station if a loss of power would result in nuisance odors being generated. The requirement for emergency power will be determined by the MCESD as part of the review and approval process.
What are the design requirements for equipment and process redundancy for a wastewater treatment plant?
The requirements for equipment and process reliability and redundancy are defined within the various chapters of the Arizona Department of Environmental Quality's (ADEQ) Engineering Bulletin No. 11, "Minimum Requirements for Design, Submission of Plans and Specifications of Sewage Works". The bulletin essentially requires that two or more of all essential treatment units or items shall be provided. With one unit or item out of service, the remaining units or items shall meet the design capacity of the plant.
Reliability and redundancy requirements can usually be met by using redundant treatment process trains or designing a single treatment process with parallel piping and equipment which provides full redundancy (i.e. main and standby process unit(s) or equipment).
An engineering analysis should be performed when designing a new or modifying an existing wastewater treatment plant to determine what process units and types of equipment require redundancy and increased reliability. The analysis should address the impact and the criticality of process interruptions and equipment failure and assess the length of time the process or system would be out of service.
What are the requirements related to the rated capacity of a wastewater treatment plant?
The rated capacity of a wastewater treatment plant is based upon the ‘firm capacity’ of the facility. Firm capacity refers to the available capacity of a system or process with the largest unit out of service. Thus, the reliability and redundancy of a water treatment plant's equipment and process units are integral to the plant's firm capacity.
As noted in previsous question, reliability and redundancy requirements are based on installed redundant equipment and process units. Using analytical or statistical methods such as ‘predicted downtime', ‘mean time between failure’ or other types of failure mode analysis to justify the reliability of systems or processes within a wastewater treatment plant is not an acceptable means of determining the rated capacity of the plant. A wastewater treatment plant's rated capacity is solely based on its firm capacity.
The rated capacity of a wastewater treatment plant is critical in determining when an expansion of a plant is required. Two stipulations that are normally included in a wastewater treatment plant's operating permit are based on the rated capacity of the plant. Those stipulations are:
- "By the time the average day maximum month flow to the Facility reaches eighty percent (80%) of the Facility's rated capacity, the Owner shall have initiated planning and design of the next expansion of the Facility."
- "By the time the average day maximum month flow to the Facility reaches ninety percent (90%) of the Facility's rated capacity, the Owner shall have initiated construction of the next expansion of the Facility."
Besides being used in determining when an expansion of a facility is required the rated capacity is also used as a basis of design for determining peaking factors. Since short term (instantaneous) influent flows may exceed the rated capacity of the facility, peaking factors are used during the design process to determine if flow equalization or additional equipment is required to handle the peak flows to the plant.
What are the minimum setback requirements for a wastewater treatment plant?
Arizona Administrative Code (AAC) R18-9-B201.I specifies the minimum setback requirements for a wastewater treatment plant from the nearest adjacent property line. The specific setback distance requirements depend on no or full noise, odor, and aesthetic controls. Full noise odor and aesthetic controls by the AAC as:
Full noise, odor, and aesthetic controls means that all treatment components are fully enclosed, odor scrubbers are installed on all vents, and fencing aesthetically matched to that in the area surrounding the facility
Noise control is further defined in the Arizona Department of Environmental Quality's (ADEQ) Engineering Bulletin No. 11, "Minimum Requirements for Design, Submission of Plans and Specifications of Sewage Works", Chapter 6, Section B as:
Noise control is defined as a sound level at the nearest existing property line not to exceed 50 dB on the A network of a sound level meter.
What are the design requirements for venting wet wells, dry wells, basins, tanks and reservoirs?
All wet wells, dry wells, basins, tanks and reservoirs require venting. Wet and dry wells require forced ventilation and basins, tanks and reservoirs require normal ventilation.
Wet wells require 12 continuous air changes per hour or 60 intermittent air changes per hour based on the volume of the head space above the minimum sewage level. Dry wells require six continuous air changes per hour or 30 intermittent air changes per hour based on the volume of the dry well.
Wet wells and dry wells are usually vented by force draft fans or blowers in combination with odor control devices located on the ventilation discharge from the wet or dry well. National Fire Protection Association (NFPA) Section 820 specifies that all continuous ventilation systems should be fitted with flow detection devices connected to an alarm system to indicate ventilation system failure.
Basins, tanks and reservoirs are usually vented using inverted 'U' type, 'chair' or cross-flow vents using normal air currents.
In all cases, vents shall have a 16-mesh corrosion resistant screen installed to prevent the ingress of birds and insects.
What are the design requirements for wet well, basin, tank or reservoir overflows?
Overflows of wastewater must be contained and not allowed to spill onto the ground. If the overflow from a storage vessel is not connected to a sewer or the head works
of the plant a suitable means of onsite containment must be included in the design. Typically, lined onsite emergency retention basins are used to contain an overflow.
Counterweighted flapper valves or self-sealing valves which open and close automatically when an overflow occurs must be installed on the end of the overflow discharge
pipe to control odors and prevent the ingress of birds and insects.
Does reclaimed water have to be disinfected?
Arizona Administrative Code (AAC) R18-11-301 through 309 classifies reclaimed water into five class types A+, A, B+, B and C based on water quality standards for fecal
coliforms. All reclaimed water classes except for Class C are required to be disinfected. Class C reclaimed water may be required to be disinfected if the water quality
standards for fecal coliforms defined in AAC R18-11-307.B.2a or b cannot be met.
Can a reclaimed water storage lake or reservoir be uncovered?
A reclaimed water storage lake or reservoir is not required to be covered provided it is after the Point-of-Compliance (POC) defined by the Aquifer Protection Permit
for the wastewater facility producing the reclaimed water. Typically the POC is on the discharge of a wastewater treatment plant. If the POC for a wastewater treatment
plant is located downstream from the plant's onsite reclaimed water storage reservoir then the reservoir would have to be covered.
Reclaimed water lakes or storage reservoirs located within the distribution system or at reuse sites such as golf courses typically do not have to be covered as they
usually are located downstream of the POC.
What are the identification requirements for pipes, valves and other equipment in reclaimed water service?
The minimum identification requirements are defined by Arizona Administrative Code (AAC) R18-9-601 through 603 for pipeline or open conveyance of reclaimed water.
The color purple shall be used for identifying all valves and other equipment used for conveying reclaimed water. For pipelines the pipe must be marked on opposite
sides with “CAUTION: RECLAIMED WATER LINE” labeling in intervals of three feet or less.
Aboveground reclaimed water piping must be labeled per the preceding paragraph and colored purple or wrapped with durable purple tape. Underground piping must be
identified with one of the following alternatives:
- The pipe must be labeled per the preceding paragraph and colored purple or wrapped with durable purple tape.
- Identification sleeving (pipe socks) made from an inert polyethylene plastic, 4 mils thick, purple in color with the words “CAUTION: RECLAIMED WATER LINE”
or similar wording printed in 1-1/2" high black lettering continuously along the entire length may be installed on the pipe.
- Identification tape made from inert polyethylene plastic, 4.0 mils thick and no less than 3" wide with the words “CAUTION: RECLAIMED WATER LINE” or similar
wording printed in 1-1/2" high black lettering continuously along the entire length may be installed parallel to the centerline and on top of the pipe. The
identification tape must be installed continuously for the entire length of the pipe and be securely fastened with plastic adhesive tape banded around both
the pipe and the identification tape at no more than 4-foot intervals.
MAG participants should reference Section 616 in the Maricopa Association of Government’s
"Uniform Standard Specifications for Public Works Construction" for additional guidelines for installing reclaimed water piping and equipment.
What are the signage requirements for reclaimed water facilities or reuse irrigation systems?
The signage requirements are defined by Arizona Administrative Code (AAC) R18-9-704.H for reclaimed water reuse sites. Signage requirements vary depending on the
Class of reclaimed water in use at a site. Classes A+ and A may be used at open access sites where access to reclaimed water by the general public is uncontrolled.
Classes B+, B and C may be used at restricted access sites where access of the general public to areas served by reclaimed water is controlled.
All impoundments with open access including lakes, ponds, ornamental fountains, waterfalls, and other water features must be posted with signs regardless of the
class of reclaimed water. The signage and notification requirements for other types reuse sites are identified in Table 1 of AAC R18-9-704.H. Signs must read
“Caution: Reclaimed Water, Do Not Drink” and display the international “do not drink” symbol.
Can backwash from the filter system on a storage lake or impoundment be discharged?
Backwash water from a filter system is considered to be wastewater and must be properly disposed. Proper disposal methods include sending the backwash water to a
sewer system or using the backwash water for surface irrigation at the reuse site. A permit issued by the sewer utility company may be required to discharge the
backwash water to the sewer system.
Backwash water may not be discharged to a drywell (for example, a storm water retention basin drywell) unless an Aquifer Protection Permit has been obtained from
the Arizona Department of Environmental Quality permitting such disposal. Other backwash water disposal alternatives will be considered on a case-by-case basis.
Can reclaimed water be discharged to a dry well?
Reclaimed water shall not be discharged to a drywell (for example, a storm water retention basin drywell) unless an Aquifer Protection Permit has been obtained
from the Arizona Department of Environmental Quality permitting such disposal.
Can reclaimed water be discharged to the waters of the United States?
Reclaimed water, including reclaimed water mixed with surface water, ground water or rain water may not be discharged to the waters of the United States unless an
AZPDES permit approving such a discharge has been obtained from the Arizona Department of Environmental Quality.
What is the minimum thickness for reclaimed water storage lake liner?
The minimum thickness for a reclaimed water storage lake liner is 60 mils for a High Density Polyethylene (HDPE) liner. Other liner thicknesses and material of
construction may be considered if it can be demonstrated that the proposed liner will meet the best available demonstrated control technology (BADCT) requirements
for Aquifer Protection Permits.
Liners are only required for lakes storing Class A, B and C reclaimed water. However, liners are usually installed on all storage lakes to minimize loss of reclaimed
water from the lake due to percolation.