Fiberglass Tank and Pipe Institute - Petroleum Product
Permeability of Synthetic Membranes for the Containment of Petroleum Products
Fiberglass Tank & Pipe Institute
Sullivan D. Curran, P.E. Executive Director

Introduction
Synthetic membranes for the containment of petroleum products are typically made of thermoplastic or rubber materials and are permeable. While there are accepted permeability values for petroleum aboveground secondary containment areas, there are additional considerations when using these materials for underground tank and piping applications. This paper discusses the historical rationale, applicable test methods, permeation values and recommendations for the application of thermoplastic and rubber membranes in the design of petroleum tank and piping secondary containment systems.

What is permeability? Permeability is defined as the rate of molecular diffusion of a gas or liquid through another substance or material. It may be thought of as "slow motion" mixing, with the rate a function of the relative polarities and sizes of the molecules in the liquids and containment material.

Permeability should not be confused with the liquid transport mode known as hydraulic conductivity. For example, soil porosity transports most of the foreign material by "hydraulic conductivity", whereas membranes transport vapors and liquids, with this phenomenon called "permeability".

The permeability of a material is affected by the stored liquid’s molecule polarity and size as discussed below.

Molecule Polarity: Highly polar liquids, such as alcohol-based methanol and ethanol, will mix more readily with another polar substance, such as nylon or polyester materials. Non-polar liquids, such as gasoline aromatic components (e. g., benzene, toluene, xylene), will mix more readily with another non-polar substance, such as polyethylene.

Hence, both polar and non-polar materials, such as nylon, polyester and polyethylene, are permeable to a gasoline-alcohol mixture.

Molecule Size: Small-sized molecules, such as methanol, will mix more readily than medium-sized molecules, such as toluene, or a large molecule, such as Methyl Tertiary Butyl Ether (MTBE).
Hence, both polar and non-polar materials are more permeable to gasoline-oxygenates using alcohol, rather than petroleum based MTBE.

With the foregoing as a background, following is a discussion on the design criteria for the permeability of aboveground and underground tank and piping containment areas used for petroleum product applications.

Aboveground Containment
There are two nationally-adopted and a proposed permeability requirement for the lining material used in secondary containment areas. Of the current requirements, the earliest addresses fire safety for large tank and piping installations, whereas, more recently, there are local or anticipated Environmental Protection Agency (EPA) environmental protection rules. In addition, Underwriters Laboratories Inc. (UL) proposed a standard for "Excavation Liners for Secondary Containment of Flammable and Combustible Liquids, Subject 1854."

Fire Safety: The National Fire Protection Association (NFPA) Flammable and Combustible Liquids Code NFPA 30 states that the "walls of a diked area shall be of earth, steel, concrete, or solid masonry designed to be liquid-tight and to withstand full hydrostatic head." Also, the Code states that, in areas where tanks contain Class I liquids (e. g., gasoline) and are "located in extremely porous soils [the tanks] may require special treatment to prevent seepage…." NFPA staff commented on the term "liquid-tight" and stated that it means the liquid will not soak through the dike wall, at least for some reasonable length of time (i.e., it is assumed that the spilled liquid will be removed as soon as the fire emergency is stabilized).

Environmental Protection: In 1973, EPA published their Spill Prevention, Control and Countermeasures (SPCC) requirements and, in 1991, published proposed revisions that will likely require containment retention to be "without substantial loss" for a period of at least 72 hours. This requirement is consistent with the fire code philosophy that a tank or piping spill cleanup should be completed within three days. However, several states and local jurisdictions specify criteria that will not permit the use of impermeable soils or untreated concrete (e. g., Alaska, New Jersey, New York and Florida).

Underwriters Laboratories: In 1995 UL proposed Subject 1854 which outlines the investigation of "Excavation Liners for Secondary Containment of Flammable and Combustible Liquids." The materials may be fabric, reinforced rigid plastic (i.e., thermo or thermosetting plastic) or non-rigid plastic (i. e., thermoplastic). Test liquids include gasolines, methanol, ethanol and alcohol-gasoline mixtures. Test method ASTM E96-94 is conducted over a 28-day period to determine the amount of permeation.

Permeability Design Criteria for Aboveground Containment: Although today there isn’t a nationwide permeability standard, where required locally a common factor is 10-7 cm/sec. This permeability value is often obtained by using synthetic membranes. The design engineer should also be aware that UL 1854 sets the rate of permeation at not greater than 0.25 ounces/square foot/24 hours (79.6 ml/square meters/24 hours). There are a variety of synthetic materials available including polyethylene, high-density polyethylene (HDPE), polyester, butyl rubber, neoprene and polyurethane. These materials should be evaluated for chemical compatibility of the membrane for possible chemical spills in the area; durability and other forms of deterioration such as that caused by bacteria in the soil. One alternative to pre-manufactured flexible membranes is a spray-on application of urethane or polysulfide. A geotextile fabric is often placed prior to the spray application to increase the durability of the lining. In conclusion, the design engineer is well positioned to design dike walls and containment basins with confidence that future retrofitting should not be required.

Underground Containment
Requirements for underground containment at petroleum facilities are relatively new when compared to those for aboveground facilities. While EPA included requirements for Underground Storage Tanks (UST’s) in their 1988 Technical Requirements, it wasn’t until the 1996 edition of NFPA 30 that a fire code addressed piping "secondary containment of liquids and associated vapors."

Fire Safety and UL: The 1996 edition of NFPA 30 requires that tanks and piping, "including those incorporating secondary containment, shall be built in accordance with recognized standards of design, or approved equivalents" and identifies appropriate tank standards and UL 971 "Standard for Nonmetallic Underground Piping for Flammable Liquids." The UL 971 test method consists of sealing an 18-inch length of pipe with appropriate fittings. The pipe sample is weighed empty, filled with the test liquid, and weighed monthly over a 180-day period for primary pipe and twice a week over 30 days for secondary containment pipe. The differences in weight are used to determine the permeability rate.

Environmental Protection: In 1988, EPA published Technical Standards for the "secondary barrier" around or beneath the UST system. The barrier is to "consist of artificially constructed material that is sufficiently thick and impermeable (at least 10-6 cm/sec. for the regulated substance stored) to direct a release to the monitoring point and permit its detection." Also, the barrier is to be "compatible with the regulated substance stored so that a release from the UST system will not cause a deterioration of the barrier allowing a release to pass through undetected."

The EPA test criteria is expressed in terms of cm/sec and is the coefficient of permeability derived from ASTM D 3385-73, the standard test method for "Infiltration Rate of Soils in Field Using Double-Ring Infilterometers." Thus, this and similar test methods are designed for soils and not "artificially constructed materials", such as thermoplastics. The EPA value of 10-6 cm/sec is the acceptable value for the coefficient of permeability (k) for gasoline retention in aboveground containment areas. This value is achieved with a bentonite soil layer and was established in field test work by Gulf Oil, Imperial Oil and others and was cited in PACE Report No. 79-2, March 1979.

In summary, EPA did not reference an appropriate ASTM test method or permeation criteria for the design of synthetic materials in UST service. However, it appears that the intent of the EPA requirement is to limit secondary containment to artificially-constructed material (e. g., thermoplastic), which is impermeable to all motor fuels (e. g., gasoline-alcohol mixtures), for the period of time necessary for a leak to be monitored and mitigated.

UL 971 Allowable Leakage: While there is considerable experience with the design of aboveground secondary containment areas, there is less experience with the design of underground containment areas…. And there is a difference!

Leak Detection Frequency: Aboveground containment design assumes that a spill will be observed and cleaned up within three days. However, it may be 30 days when most prudent UST operators would check for liquid or vapors in sumps as is done in observation wells.

Underground Leak Detection Design: Systems are available to monitor continuously dispenser and tank sumps for the accumulation of underground piping/joint leaks and/or dispenser and tank sump spills into the secondary containment system. These are costly systems, not required in their entirety by the EPA rule. However, many operators depend on monthly monitoring and annual tightness testing and will want to be aware of the permeation levels permitted under UL 971. This test protocol permits secondary containment permeation of 0.079 ounces per square foot per day and conducts their test for 30 days. The surface area measurement is made from the inside diameter (ID) of the pipe. For example, if 500 feet of 1 ½ inch underground coaxial secondarily contained pipe is installed in a typical retail service station, then the allowable leakage from permeation over a 30 day period is 3.6 gallons.

Conclusions
If the design engineer accepts the UL 971 allowable permeation rate of 3.6 gallons over a 30-day period, then it is important that secondary containment is designed to drain freely to the tank sump and avoid the retention of product. Hence, the design and construction should consider the following:
Piping Slope - PEI RP 100 (1994) states that piping "should be sloped 1/8 inch per foot to the tank"…."And "should be evenly and adequately supported to prevent creation of traps or sumps." API RP 1615 (1996) states that piping "should have a uniform slope of not less than 1/8 inch per foot down towards the tank" and that "traps or sags should be avoided in all piping." Maintaining the proper slope is relatively easy due to the nature of rigid piping. However to do the same using flexible piping, care should be taken to first level and then compact the trench bedding in an effort to maintain a constant slope after the site is backfilled and settlement occurs.

Dispenser Sumps – The bottom of a dispenser sump must be below the inlet level of the secondary pipe and will inhibit drainage to and detection in the tank sump. If the sump material is permeable i. e., thermoplastic (e. g., polyethylene) rather than thermo-setting plastic (e. g., fiberglass), then periodic inspections or product sensors should be employed to ensure product accumulation is removed to prevent leakage due to permeation.

Corrugated Piping Containment – The corrugations in some secondary containment piping systems will not drain completely and, thus, retain some liquid. Vapor rather than liquid monitoring at the tank sump may be employed to detect when this occurs and the system should be purged.

May, 1997

References
  1. "State of the Art Review – Petroleum Product Containment Dyking"
  2. Report No. 79-2, March 1979, Petroleum Association for Conversation of the Canadian Environment (PACE)
  3. "State-of-the Art Review: Tank Bottom Lining Systems and Impervious Diked Areas" Final Report, January, 1988, Golder Associates Inc., Atlanta, Georgia
  4. Standard test Method for "Infiltration Rate of Soils in Field Using Double-ring Infiltrometers" ASTM D 3385-75
  5. State of Maryland Tank Dike Permeability Recommendation letter written by Mobil Oil Corporation, 1988
  6. Storage Tank and Piping, Chapter 35, Secondary Containment, February 12, 1995 Chevron Company, USA
  7. "UL 971 Nonmetallic Underground Piping for Flammable Liquids" October 30, 1995, Underwriters Laboratories Inc.
  8. "Installation of Underground Petroleum Storage Systems" American Petroleum Institute Recommended Practice 1615, March 1996
  9. "Installation of Underground Liquid Storage Systems" Petroleum Equipment Institute Recommended Practice 100-94
  10. 40 CFR Parts 280 ; Underground Storage Tanks; Technical Requirements Federal Register, September 23, 1988
  11. "Permeation" paper dated 1/12/95; Ameron, Fiberglass Pipe Group
  12. "Just the Facts" paper dated December, 1996; Smith Fiberglass Products Inc.

    May, 1997
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