United States Environmental Protection Agency (EPA)

New JerseyDepartment of Environmental Protection (DEP)

DEP Site Remediation Program

January 1996

 

Straight Talk On Tanks

Leak Detection Methods For Petroleum Underground Storage Tanks And Piping Regulated In New Jersey

 

 

 

 

 

 

 

 

 

 

 

Printed on Recycled Paper

 

Contents

 

Do You Have Questions About Leak Detection? 1

An Overview Of Leak Detection Requirements 2

Secondary Containment With Interstitial Monitoring 6

Automatic Tank Gauging Systems 8

Vapor Monitoring 10

Groundwater Monitoring 12

Statistical Inventory Reconciliation 14

Tank Tightness Testing With Inventory Control 16

Manual Tank Gauging 20

Leak Detection For Underground Piping 22

Publications And Videos About USTs 26

Applicability and Summary of Regulated Underground Storage Tanks 28

NOTE: The requirements for underground storage tanks referred to in this booklet can be found in the Code of Federal Regulations (CFR) at 40 CFR, Part 280, in the New Jersey Administrative Code (NJAC) at NJAC 7:14B-1 et seq. and at P.L. 1994, c.14. Sections of the CFR can be ordered from the U.S. Government Printing Office, Washington, DC 20402 (or call (202) 783-3238). Sections of the NJAC can be ordered from the Office of Administrative Law at (609) 292-6395.

DISCLAIMER: Any reference to or depiction of commercial products in this booklet is solely for explanatory purposes and is not intended as an endorsement of these products.

n Do You Have Questions About Leak Detection?

As an owner or operator of state and federally regulated underground

storage tanks (USTs) storing petroleum products (motor fuels, lubricating oil, waste oil):

n Do you understand the basic leak detection requirements for USTs?

n Are you confused about choosing the most appropriate leak detection method for your state and federally regulated UST?

These are important questions, because your state and federally regulated UST and its underground piping must have leak detection NOW. (It is important to note, however, that heating oil USTs are currently regulated only by the state. Leak detection is not required for these tanks at this time, but probably will be in the future.)

This booklet begins with an overview of the regulatory requirements for leak detection. Each following section focuses on one leak detection method or the special requirements for piping.

In this booklet, you will find answers to many basic questions about how leak detection methods work and which methods are most appropriate for your UST site.

Why is leak detection so important?

As of June 1995, over 5,600 confirmed leaks from regulated USTs had been reported in New Jersey. At sites without leak detection, leaks were discovered late, after contamination had spread, requiring difficult and costly cleanups.

By contrast, if you have effective leak detection, you can respond quickly to signs of leaks. You can minimize the extent of environmental damage and the threat to human health and safety. Early action on your part also protects you from the high costs that can result from cleaning up extensive leaks and responding to third-party liability claims.

If you are not sure if your UST system is regulated and required to have leak detection, please refer to the DEP chart "Applicability and Summary of Regulated Underground Storage Tanks" on page 28.

 

An Overview Of Leak Detection Requirements

All new federally regulated USTs (those installed after December 1988) must have leak detection when they are installed.

USTs installed before December 1988 (called "existing USTs") had compliance deadlines for leak detection phased in over 5 years.

By December 1993, all "federally regulated existing USTs" had to have leak detection.

The DEP has identified the following methods that owners and operators may use to meet the state and federal leak detection requirements:

n Secondary Containment With Interstitial Monitoring

n Automatic Tank Gauging Systems

n Vapor Monitoring

n Groundwater Monitoring

n Statistical Inventory Reconciliation

n Other Methods Approved By DEP

The leak detection methods noted above are all monthly monitoring methods and eventually everyone must use at least one of them. However, as a temporary method (until 1998 or for 10 years after installing or upgrading an UST), you can combine tank tightness testing with inventory control (or with manual tank gauging if you have a small tank). So, in order to fullfill your leak detection requirements, you can use a combination of tank tightness testing and inventory control until 1998, or, if you installed new tanks or upgraded your tanks after December 1988, you can use this combination for up to 10 years after the installation or upgrade. See page 4 for a complete explanation.

Brief descriptions of leak detection methods appear on the next two pages. More complete descriptions appear in the following sections.

Leak detection requirements for piping differ somewhat from those for tanks. Leak detection methods for piping include secondary containment with interstitial monitoring, vapor monitoring, groundwater monitoring, statistical inventory reconciliation, electronic pressure monitoring, and tightness testing. Pressurized piping must also have an automatic line leak detector. See pages 22-25 for descriptions of the requirements for suction and pressurized piping.

 

 

n Secondary Containment With Interstitial Monitoring (see pages 6-7)

Secondary containment consists of using a barrier, an outer wall, a vault, or a liner around the UST or piping. Leaked product from the inner tank or piping is directed towards an "interstitial" monitor located between the inner tank or piping and the outer barrier. Interstitial monitoring methods range from a simple dipstick to a continuous, automated vapor or liquid sensor permanently installed in the system.

n Automatic Tank Gauging Systems (see pages 8-9)

A probe permanently installed in the tank is wired to a monitor to provide information on product level, water level and temperature. These systems automatically calculate the changes in product volume that can indicate a leaking tank.

n Vapor Monitoring (see pages 10-11)

Vapor monitoring measures product "fumes" in the soil around the UST to check for a leak. This method requires installation of carefully placed monitoring wells. Vapor monitoring can be performed manually on a periodic basis or continuously using permanently installed equipment.

n Groundwater Monitoring (see pages 12-13)

Groundwater monitoring senses the presence of liquid product floating on the groundwater. This method requires installation of monitoring wells at strategic locations in the ground near the tank and along the piping runs. To discover if leaked product has reached groundwater, these wells can be checked periodically by hand or continuously with permanently installed equipment. This method cannot be used at sites where groundwater is more than 20 feet below the surface.

n Statistical Inventory Reconciliation (see pages 14-15)

In this method, a trained professional uses sophisticated computer software to conduct a statistical analysis of inventory, delivery, and dispensing data, which you must supply regularly.

n Other Methods Approved By DEP

DEP can approve any technology that is used at least monthly and meets a performance standard of detecting a leak of 0.2 gallons per hour with a probability of detection of at least 95 percent and a probability of false alarm of no more than 5 percent.

n Tank Tightness Testing With Inventory Control (see pages 16-19)

This method combines periodic tank tightness testing with monthly inventory control. Tightness tests are tests performed by trained professionals. You must also use monthly inventory control. Inventory control involves taking daily measurements of tank contents and recording deliveries and amount pumped. Note: this combined method can be used during the first 10 years following new tank installation or upgrade of your existing UST. After that, you must use monthly monitoring methods. (This combined method can also be used temporarily, until December 1998, with tanks that have not been upgraded with spill, overfill, and corrosion protection.)

n Manual Tank Gauging (see pages 20-21)

Manual tank gauging can be used only for tanks of 2,000 gallons or less capacity. This method requires keeping the tank undisturbed for at least 36 hours each week, during which the contents of the tank are measured twice at the beginning and twice at the end of the test period. Each measurement is compared with the weekly standards on page 21. At the end of the month, you average the weekly tests and compare the results to the standards shown on page 21 to see if your tank may be leaking. This method can be used by itself only for tanks up to 1,000 gallons. Tanks between 1,001 and 2,000 gallons can use this method in combination with periodic tank tightness testing instead of inventory control. This combined method, however, can be used only during the first 10 years after tank installation or upgrade. (The combined method can also be used temporarily, until December 1998, with tanks that have not been upgraded with spill, overfill, and corrosion protection.)

Look For The "Proof" Of A Third-Party Evaluation

An evaluation performed by a third party (someone who is independent of the manufacturer or vendor of the leak detection system) shows that a leak detection system can work as designed. The evaluation follows required evaluation procedures, and often takes place in a laboratory.

Although an evaluation and its resulting documentation are technical, you should be familiar with the evaluation's "results" form and, when provided, its "description" form. You should obtain these forms from the leak detection vendor and keep them on file. They contain a signed certification that the system performed as described, as well as documenting any limitations of the system (such as maximum UST size or minimum amount of product in the UST). This information is important to your compliance with the UST requirements. For example, if a tank tightness test was evaluated and certified only for tests taking 2 hours or more, then your UST must be tested for at least 2 hours or it would fail to meet the leak detection requirements. EPA also advises that a leak detection system should not be used on UST systems more than 1.5 times the capacity of the UST used in the evaluation.

Required "Probabilities" For Some Leak Detection

The regulations require not only that leak detection methods be able to detect certain leak rates, but that they also give the correct answer consistently. In general, methods must detect the specified leak rate with a probability of detection of at least 95 percent and a probability of false alarm of no more than 5 percent. Simply stated, this means that, of 100 tests of USTs leaking at the specified rate, at least 95 of them must be correctly detected. It also means that, of 100 tests of non-leaking USTs, no more than 5 can be incorrectly called leaking. This is what is meant by the "probabilities" noted in this booklet.

 

Which leak detection method is best for you?

There is no one leak detection system that is best for all sites, nor is there a particular type of leak detection that is consistently the least expensive.

Each leak detection method has unique characteristics. For example, vapor detection devices work rapidly and most effectively in porous soils, while liquid detectors are only appropriate for areas with a high water table.

Identifying the best leak detection choice for your UST depends on a number of factors including substance stored, cost (both initial installation cost and long-term operation and maintenance cost), facility configuration (such as complexity of piping runs and manifolded tanks), groundwater depth, soil type, seasonal rainfall and temperature ranges, availability of experienced installers, and other variables.

You should look around extensively for experienced, professional vendors and DEP certified installers of leak detection. Ask questions that help you find the most reliable, cost-effective leak detection for your type of facility. Some possible information sources are: references from fellow UST owners, oil marketers, equipment suppliers, trade journals, trade associations, state and local trade associations (especially those for petroleum marketers and UST owners), and the yellow pages of your telephone directory (look under "tanks").

In New Jersey, any person and firm installing leak detection equipment must be certified by DEP. Ask any contractor you interview to show his and the firm's certification card. An up-to-date list of certified firms can be obtained from DEP's Bureau of Revenue by calling (609) 777-1007 ($40.00/copy).

For additional information about federal UST requirements, contact the DEP at (609) 292 8761 or contact EPA's RCRA/Superfund Hotline at 800 424-9346.

Secondary Containment With Interstitial Monitoring

Will you be in compliance?

When installed and operated according to the manufacturer's specifications, secondary containment with interstitial monitoring meets the state and federal leak detection requirements for new and existing USTs. Operation of the monitoring device at least once each month fulfills the requirements for the life of the tank. Secondary containment with interstitial monitoring can also be used to detect leaks from piping (see the section on leak detection for piping starting on page 22).

How does the leak detection method work?

Secondary containment

n Secondary containment provides a barrier between the tank and the environment. The barrier holds the leak between the tank and the barrier so that the leak is detected. The barrier is shaped so that a leak will be directed towards the interstitial monitor.

n Barriers include:

Ø Double-walled or "jacketed" tanks, in which an outer wall partially or completely surrounds the primary tank;

Ø Internally fitted liners ("bladders"); and

Ø Leakproof excavation liners that completely surround the tank.

n Clay and other earthen materials cannot be used as barriers.

Interstitial monitors

n Monitors are used to check the area between the tank and the barrier for leaks and alert the operator if a leak is suspected.

n Some monitors indicate the physical presence of the leaked product, either liquid or gaseous. Other monitors check for a change in condition that indicates a hole in the tank, such as a loss of vacuum or a change in the level of a monitoring liquid between the walls of a double-walled tank.

n Monitors can be as simple as a dipstick used at the lowest point of the containment to see if liquid product has leaked and pooled there. Monitors can also be sophisticated automated systems that continuously check for leaks.

What are the regulatory requirements?

n The barrier must be immediately around or beneath the tank and contain all leaking product.

n The interstitial monitor must be checked at least once every 30 days.

n A double-walled system must be able to detect a release through the inner wall.

n An excavation liner must:

Ø Direct a leak towards the monitor;

Ø Not allow the specific product being stored to pass through it any faster than 10-6 cm/sec;

Ø Be compatible with the product stored in the tank;

Ø Not interfere with the UST's cathodic protection;

Ø Not be disabled by moisture;

Ø Always be above the groundwater and the 25-year flood plain; and

Ø Have clearly marked and secured monitoring wells, if they are used.

Will it work at your site?

n The monitoring system should be properly matched to the substance stored to insure that a failure of the primary container will be detected.

Anything else you should consider?

n This method works effectively only if the barrier and the interstitial monitor are installed correctly. Therefore, trained and experienced installers are necessary.

 

 

 

 

 

 

Automatic Tank Gauging Systems

Will you be in compliance?

When installed and operated according to the manufacturer's specifications, automatic tank gauging systems (ATGS) meet the state and federal leak detection requirements for new and existing USTs. A test performed each month fulfills the requirements for the life of the tank. (For additional requirements for piping, see the section on leak detection for piping starting on page 22.)

How does the leak detection method work?

n The product level and temperature in a tank are measured continuously and automatically analyzed and recorded by a computer.

n In the "inventory mode," the ATGS replaces the use of the gauge stick to measure product level and perform inventory control. This mode records the activities of an in-service tank, including deliveries.

n In the "test mode," the tank is taken out of service and the product level and temperature are measured for at least one hour. Some systems, known as "continuous ATGS," do not require the tank to be taken out of service to perform a test. This is because these systems can gather and analyze data during many short periods when no product is being added to or taken from the tank.

What are the regulatory requirements?

n The ATGS must be able to detect a leak no larger than 0.2 gallons per hour with certain probabilities of detection and of false alarm. Some ATGS can also detect a leak of 0.1 gallons per hour with the required probabilities.

Will it work at your site?

n ATGS have been used primarily on tanks containing gasoline or diesel, with a capacity of up to 15,000 gallons. If considering using an ATGS for larger tanks or products other than gasoline or diesel, discuss its applicability with the manufacturer's representative. Remember, do not use an ATGS if your UST is more than 1.5 times the capacity of the UST used in the third-party evaluation of that ATGS.

n Water around a tank may hide a leak by temporarily preventing the product from leaving the tank. To detect a leak in this situation, the ATGS should be capable of detecting water in the bottom of a tank.

Anything else you should consider?

n The ATGS probe is permanently installed through an opening (not the fill pipe) on the top of the tank. Each tank at a site must be equipped with a separate probe.

n The ATGS probe is connected to a monitor that displays ongoing product level information and the results of the monthly test. Printers can be connected to the monitor to record this information.

n ATGS are often equipped with alarms for high and low product level, high water level, and theft.

n ATGS can be linked with computers at other locations, from which the system can be programmed or read.

n For ATGS that are not of the "continuous" type, no product should be delivered to the tank or withdrawn from it for at least 6 hours before the monthly test or during the test (which generally takes 1 to 6 hours).

n An ATGS can be programmed to perform a test more often than once per month (a recommended practice).

 

 

Vapor Monitoring

Will you be in compliance?

When installed and operated according to the manufacturer's instructions, vapor monitoring meets the state and federal leak detection requirements for new and existing USTs. Operation of a vapor monitoring system at least once each month fulfills the requirements for the life of the tank. Vapor monitoring can also be installed to detect leaks from piping (see the section on leak detection for piping starting on page 22).

How does the leak detection method work?

n Vapor monitoring senses or measures "fumes" from leaked product in the soil around the tank to determine if the tank is leaking.

n Fully automated vapor monitoring systems have permanently installed equipment to continuously or periodically gather and analyze vapor samples and respond to a release with a visual or audible alarm.

n Manually operated vapor monitoring systems range from equipment that immediately analyzes a gathered vapor sample to devices that gather a sample that must be sent to a laboratory for analysis. Manual systems must be used at least once a month to monitor a site.

n All vapor monitoring devices should be periodically calibrated according to the manufacturer's instructions to ensure that they are properly responding.

n Before installation, a site assessment is necessary to determine the soil type, groundwater depth and flow direction, and the general geology of the site. This may only be performed by a New Jersey certified subsurface evaluator.

n Vapor monitoring requires the installation of monitoring wells within the tank backfill. The number of wells and their placement is very important. Only an experienced New Jersey certified contractor may properly design and construct an effective monitoring well system.

 

What are the regulatory requirements?

n The UST backfill must be sand, gravel or crushed stone that will allow the vapors to easily move to the monitor.

n The backfill should be clean enough that previous contamination does not interfere with the detection of a current leak.

n The substance stored in the UST must vaporize easily so that the vapor monitor can detect a release.

n High ground water, excessive rain, or other sources of moisture must not interfere with the operation of vapor monitoring for more than 30 consecutive days.

n Monitoring wells must be secured and clearly marked.

Will it work at your site?

n Before installing a vapor monitoring system, a site assessment must be done to determine whether vapor monitoring is appropriate at the site. A site assessment usually includes at least a determination of the groundwater level, background contamination, stored product type, and soil type. This assessment may only be performed by a New Jersey certified subsurface evaluator.

Anything else you should consider?

n For existing sites, care must be taken to insure that tank integrity is not compromised during well installation.

Groundwater Monitoring

 

Will you be in compliance?

When installed and operated according to the manufacturer's instructions, a groundwater monitoring system meets the state and federal leak detection requirements for new and existing USTs. Operation of a groundwater monitoring system at least once each month fulfills the requirements for the life of a tank. Groundwater monitoring can also be used to detect leaks in piping (see the section on leak detection for piping starting on page 22).

How does the leak detection method work?

n Groundwater monitoring involves the use of permanent monitoring wells placed close to the UST. The wells are checked at least monthly for the presence of product that has leaked from the UST and is floating on the groundwater surface.

n The two main components of a groundwater monitoring system are the monitoring well (typically a well of 2-4 inches in diameter) and the monitoring device.

n Detection devices may be permanently installed in the well for automatic, continuous measurements for leaked product.

n Detection devices are also available in manual form. Manual devices range from a bailer (used to collect a liquid sample for visual inspection) to a device that can be inserted into the well to electronically indicate the presence of leaked product. All devices must be operated at least once a month.

n Before installation, a site assessment is necessary to determine the soil type, groundwater depth and flow direction, and the general geology of the site. This assessment may only be performed by a New Jersey certified subsurface evaluator.

n The number of wells and their placement is very important. Only an experienced New Jersey certified contractor may properly design and construct an effective monitoring well system.

 

 

What are the regulatory requirements?

n Groundwater monitoring can only be used if the stored substance does not easily mix with water and floats on top of water.

n If groundwater monitoring is to be the sole method of leak detection, the groundwater must not be more than 20 feet below the surface, and the soil between the well and the UST must be sand, gravel or crushed stone.

n Monitoring wells must be properly designed and sealed to keep then from becoming contaminated from outside sources. The wells must also be clearly marked and secured.

n Wells should be placed in the UST backfill so that they can detect a leak as quickly as possible.

n Product detection devices must be able to detect one-eighth inch or less of leaked product floating on top of the groundwater.

Will it work at your site?

n In general, groundwater monitoring works best at UST sites where:

Ø Monitoring wells are installed in the tank backfill; and

Ø There are no previous releases that will interfere with the system.

n A professionally conducted site assessment performed by a New Jersey certified subsurface evaluator is critical for determining these site-specific conditions.

Anything else you should consider?

n For existing sites, care must be taken to insure that tank integrity is not compromised during well installation.

Statistical Inventory Reconciliation

Will you be in compliance?

Statistical inventory reconciliation (SIR), when performed according to the vendor's specifications, meets state and federal leak detection requirements for new and existing USTs as follows. SIR with a 0.2 gallon per hour leak detection capability meets the state and federal requirements for monthly monitoring for the life of the tank and piping. SIR with a 0.1 gallon per hour leak detection capability meets the state and federal requirements as an equivalent to tank tightness testing. (For additional requirements for piping, see the section on leak detection for piping starting on page 22.)

How does the leak detection method work?

n SIR analyzes inventory, delivery, and dispensing data collected over a period of time to determine whether or not a tank system is leaking.

n Each operating day, the product level is measured using a gauge stick or other tank level monitor. You also keep complete records of all withdrawals from the UST and all deliveries to the UST. After data have been collected for the period of time required by the SIR vendor, you provide the data to the SIR vendor.

n The SIR vendor uses computer software to conduct a statistical analysis of the data to determine whether or not your UST may be leaking. The SIR vendor provides you with a test report of the analysis.

What are the regulatory requirements?

n To be allowable as monthly monitoring, a SIR method must be able to detect a leak at least as small as 0.2 gallons per hour and meet the state and federal regulatory requirements regarding probabilities of detection and of false alarm. Data must be submitted at least monthly.

n To be allowable as an equivalent to tank tightness testing, a SIR method must be able to detect a leak at least as small 0.1 gallons per hour and meet the state and federal regulatory requirements regarding probabilities of detection and of false alarm.

n The individual SIR method must have been evaluated with a third party test procedure to certify that it can detect leaks at the required level and with the appropriate probabilities of detection and of false alarm.

n If the test report is not conclusive, you must take the steps necessary to find out conclusively whether your tank is leaking. Because SIR requires multiple days of data, you will probably have to use another method.

n You must keep on file both the test reports and the documentation that the SIR method used is certified as valid for your UST system.

Will it work at your site?

n Generally, few product or site restrictions apply to the use of SIR.

n SIR may be used on manifolded UST systems only when the method is evaluated and approved for this type of system.

n SIR has been used primarily on tanks no more than 18,000 gallons in capacity. If you are considering using a SIR method for larger tanks, discuss its applicability with the vendor. Remember, do not use any SIR method if your UST is more than 1.5 times the capacity of the UST used on the third-party evaluation of that SIR method.

n Water around a tank may hide a hole in the tank or distort the data to be analyzed by temporarily preventing a leak. To detect a leak in this situation, you must check for water at least once a month.

Anything else you should consider?

n Data, including product level measurements, dispensing data, and delivery data, should all be carefully collected according to the SIR vendor's specifications. Poor data collection produces inconclusive results and noncompliance.

n The SIR vendor will generally provide forms for recording data, a calibrated chart converting liquid level to volume, and detailed instructions on conducting measurements.

n SIR should not be confused with other release detection methods that also rely on periodic reconciliation of inventory, withdrawal, and delivery data. Unlike manual tank gauging or inventory control, SIR uses a sophisticated statistical analysis of data to detect releases. This analysis can only be done by competent, trained practitioners.

 

 

Tank Tightness Testing With Inventory Control

Will you be in compliance?

When performed according to the manufacturer's specifications, periodic tank tightness testing combined with monthly inventory control can temporarily (as described below) meet the state and federal leak detection requirements for new and existing USTs.

These two leak detection methods must be used together, because neither method alone meets the state and federal requirements for leak detection for tanks. Tightness testing is also an option for underground piping, as described in the section on leak detection for piping starting on page 22.

Because they must be used together, both tank tightness testing and inventory control are discussed in this section. Tank tightness testing is discussed first, followed by inventory control.

 

Tank Tightness Testing

How does the leak detection method work?

Tightness tests include a wide variety of methods. Other terms used for these methods include "precision," "volumetric," and "nonvolumetric" testing.

n Many tightness test methods are "volumetric" methods in which the change in product level in a tank over several hours is measured very precisely (in milliliters or thousandths of an inch).

n Other methods use acoustics or tracer chemicals to determine the presence of a hole in the tank. With such methods, all of the factors in the following bullets may not apply.

n For most methods, changes in product temperature also must be measured very precisely (thousandths of a degree) at the same time as level measurements, because temperature changes cause volume changes that interfere with finding a leak.

n For most methods, a net decrease in product volume (subtracting out volume changes caused by temperature) over the time of the test indicates a leak.

n The testing equipment is temporarily installed in the tank, usually through the fill pipe.

n The tank must be taken out of service for the test, generally for several hours, depending on the method.

n Many test methods require that the product in the tank be a certain level before testing, which often requires adding product from another tank on-site or purchasing additional product.

n Some tightness test methods require all of the measurements and calculations to be made by hand by the tester. Other tightness test methods are highly automated. For some test methods, after the tester sets up the equipment, a computer controls the measurements and analysis.

n A few methods measure properties of the product that are independent of temperature, such as the mass of the product, and so do not need to measure product temperature.

n Some automatic tank gauging systems are capable of meeting the regulatory requirements for tank tightness testing and can be considered as an equivalent method.

What are the regulatory requirements?

n The tightness test method must be able to detect a leak at least as small as 0.1 gallon per hour with certain probabilities of detection and of false alarm.

n Tightness tests must be performed periodically. When tightness testing is chosen as the method of leak detection: 1. New tanks and upgraded existing tanks must be tightness tested at least every five years for up to ten years following installation or upgrade ("Upgraded" tanks have spill, overfill, and corrosion protection.); 2. Existing tanks that have not been upgraded must be tightness tested at least every year until 1998 (subsequently these tanks must be upgraded, replaced, or closed).

n After the applicable ten year time period noted above, you must have a monitoring method that can be performed at least once per month. See the other sections of this booklet for allowable monthly monitoring options.

Will it work at your site?

n Tank tightness testing has been used primarily on tanks no more than 15,000 gallons in capacity containing gasoline and diesel. If you are considering using tightness testing for larger tanks or products other than gasoline or diesel, discuss the method's applicability with the manufacturer's representative. Remember, do not use any tank tightness test method if your UST is more than 1.5 times the capacity of the UST used in the third party evaluation of that tank tightness test method.

Anything else you should consider?

n For most methods, the test is performed by a testing company. You just observe the test.

n Manifolded tanks generally should be disconnected and tested separately.

n Depending on the method, up to 4 tanks can be tested at one time. Generally, an automated system is necessary to test 3 or 4 tanks at a time.

n Procedure and personnel, not equipment, are usually the most important factors in a successful tightness test. Therefore, well-trained and experienced testers are very important. In New Jersey, tank tightness testers must be certified by the DEP.

 

Inventory Control

How does the leak detection method work?

Inventory control requires daily measurements of tank contents and arithmetic calculations that let you compare your "stick" inventory (what you've measured) to your "book" inventory (what your recordkeeping indicates you should have). Some people call this process "inventory reconciliation." If the difference between your "stick" and "book" inventory is too large, your tank may be leaking.

DEP has a booklet, Doing Inventory Control Right, that fully explains how to do inventory control. The booklet also contains standard reporting forms. You can order this free booklet by calling 609-292-8761 and asking for Doing Inventory Control Right.

n UST inventories are determined daily by using a gauge stick and the data is recorded on a form. The level on the gauge stick is converted to a volume of product in the tank using a calibration chart, which is often furnished by the UST manufacturer.

n The amounts of product delivered to and withdrawn from the UST each day are also recorded. At least once each month, the gauge stick data and the sales and delivery data are reconciled and the month's overage or shortage is determined. If the overage or shortage is greater than or equal to 1.0 percent of the tank's flow-through volume plus 130 gallons of product, the UST may be leaking.

What are the regulatory requirements?

n Inventory control must be used in conjunction with periodic tank tightness tests.

n The gauge stick should be long enough to reach the bottom of the tank and marked so that the product level can be determined to the nearest one-eighth of an inch.

n A monthly measurement must be taken to identify any water at the bottom of the tank.

n Deliveries must be made through a drop tube that extends to within one foot of the tank bottom.

n Product dispensers must be calibrated to the local weights and measures standards.

Will it work at your site?

If your tank is not level, inventory control may need to be modified. You will need to get a corrected tank chart.

Anything else you should consider?

n Inventory control is a practical, commonly used management tool that does not require closing down the tank operation for long periods.

n You can perform inventory control yourself.

n The accuracy of tank gauging can be greatly increased by spreading product-finding paste on the gauge stick before taking measurements (or by using in-tank product level monitoring devices).

n Inventory control, although not necessary for systems with monthly monitoring, is a useful tank management practice.

 

 

Manual Tank Gauging

Will you be in compliance?

NOTE: Manual tank gauging can only be used for smaller tanks. Tanks 1,000 gallons or less can use this method alone, but tanks from 1,001-2,000 gallons can only use manual tank gauging when it is combined with tank tightness testing. Manual tank gauging cannot be used for tanks over 2,000 gallons. When performed according to recommended practices, manual tank gauging meets the state and federal leak detection requirements for USTs with a capacity of 1,000 gallons or less for the life of the tank. (For additional requirements for piping, see the section on leak detection for piping starting on page 22.)

How does the leak detection method work?

DEP has a booklet, Manual Tank Gauging, that fully explains how to do manual tank gauging correctly. The booklet also contains standard reporting forms. You can order this free booklet by calling (609) 292-8761 and asking for Manual Tank Gauging.

n Four measurements of the tank's contents must be taken weekly, two at the beginning and two at the end of at least a 36-hour period during which nothing is added to or removed from the tank. See the table on the next page.

n The average of the two consecutive ending measurements are subtracted from the average of the two beginning measurements to indicate the change in product volume.

n Every week, the calculated change in tank volume is compared to the standards shown in the table on the next page. If the calculated change exceeds the weekly standard, the UST may be leaking. Also, monthly averages of the four weekly test results must be compared to the monthly standard in the same way. See the table on the next page.

What are the regulatory requirements?

n Liquid level measurements must be taken with a gauge stick that is marked to measure the liquid to the nearest one-eighth of an inch.

n Manual tank gauging may be used as the sole method of leak detection for tanks with a capacity of 1,000 gallons or less for the life of the tank. Tanks between 551 and 1,000 gallons have two testing standards based on their diameter (see table). These tanks also may use a combination of manual tank gauging and periodic tank tightness testing for the life of the tank (see table for testing standards).

Table of Test Standards for Manual Tank Gauging

Tank Size

Minimum Duration Of Test

Weekly Standard (1 test)

Monthly Standard (4-test average)

up to 550 gallons

36 hours

10 gallons

5 gallons

551-1,000 gallons (when tank diameter is 64")

44 hours

9 gallons

4 gallons

551-1,000 gallons (when tank diameter is 48")

58 hours

12 gallons

6 gallons

551-1,000 gallons

(also requires periodic tank tightness testing)

36 hours

13 gallons

7 gallons

1,001-2,000 gallons (also requires periodic tank tightness testing)

36 hours

26 gallons

13 gallons

n For tanks with a capacity of 1,001-2,000 gallons, manual tank gauging must be combined with periodic tightness testing. See the earlier section on tank tightness testing for details on this method.

n Unless the tank is 1,000 gallons or less, this combined method will meet the federal requirements only temporarily (as explained above). You must eventually have another monitoring method that can be performed at least once a month. See the other sections of this booklet for allowable monthly monitoring options.

n Tanks greater than 2,000 gallons in capacity may not use this method of leak detection to meet these regulatory requirements.

Will it work at your site?

n Manual tank gauging is inexpensive and can be an effective leak detection method when used as described above with tanks of the appropriate size.

Anything else you should consider?

n You can perform manual tank gauging yourself. Correct gauging, recording, and interpretation are the most important factors for successful tank gauging. The accuracy of tank gauging can be greatly increased by spreading product-finding paste on the gauge stick before taking measurements.

Leak Detection For Underground Piping

Will you be in compliance?

When installed and operated according to the manufacturer's specifications, the leak detection methods discussed here meet the state and federal regulatory requirements for the life of new and existing underground piping systems. Your UST may have suction or pressurized piping. You can the difference between the two types of piping by the location of the product pump. In a suction system, the product pump is located in the dispenser housing, while the pump in a pressurized system is submerged in the UST. Leak detection requirements for the two types of piping systems are discussed below.

What are the regulatory requirements for suction piping?

n No leak detection is required if the suction piping has (1) enough slope so that the product in the pipe can drain back into the tank when suction is released and (2) has only one check valve, which is as close as possible beneath the pump in the dispensing unit. If a suction line is to be considered exempt based on these design elements, there must be some way to check that the line was actually installed according to these plans.

n If a suction line does not meet all of the design criteria noted above, one of the following leak detection methods must be used:

Ø A line tightness test at least every 3 years; or

Ø Monthly interstitial monitoring; or

Ø Monthly vapor monitoring; or

Ø Monthly groundwater monitoring; or

Ø Monthly statistical inventory reconciliation.

The line tightness test must be able to detect a leak at least as small as 0.1 gallon per hour with certain probabilities of detection and of false alarm.

Interstitial monitoring, vapor monitoring, groundwater monitoring, and statistical inventory reconciliation have the same regulatory requirements for piping as they do for tanks. See the earlier sections of this booklet on those methods.

 

 

 

 

What are the regulatory requirements for pressurized piping?

Each pressurized piping run must have one leak detection method from each set below:

An Automatic Line Leak Detector:

Ø Automatic flow restrictor; or

Ø Automatic flow shutoff; or

Ø Continuous alarm system.

And One Other Method:

Ø Monthly interstitial monitoring; or

Ø Monthly vapor monitoring; or

Ø Monthly groundwater monitoring; or

Ø Monthly statistical inventory reconciliation; or

Ø In-line electronic pressure monitor; or

Ø Annual tightness test.

n The automatic line leak detector (LLD) must be designed to detect a leak at least as small as 3 gallons per hour at a line pressure of

10 pounds per square inch within 1 hour by shutting off the product flow, restricting the product flow, or triggering an audible or visual alarm.

n The line tightness test must be able to detect a leak at least as small as 0.1 gallon per hour when the line pressure is 1.5 times its normal operating pressure. The test must be conducted at least every 12 months. If the test is performed at pressures lower than 1.5 times operating pressure, the leak rate to be detected must be correspondingly lower.

n Automatic LLDs and line tightness tests must also be able to meet the state and federal regulatory requirements regarding probabilities of detection and false alarm.

n Interstitial monitoring, vapor monitoring, groundwater monitoring, and statistical inventory reconciliation have the same regulatory requirements for piping as they do for tanks. See the earlier sections of this booklet on those methods.

How do the leak detection methods work?

Automatic line leak detectors (LLDs)

n Flow restrictors and flow shutoffs can monitor the pressure within the line in a variety of ways: whether the pressure decreases over time; how long it takes for a line to reach operating pressure; and combinations of increases and decreases in pressure.

n If a suspected leak is detected, a flow restrictor keeps the product flow through the line well below the usual flow rate. If a suspected leak is detected, a flow shutoff completely cuts off product flow in the line or shuts down the pump.

n A continuous alarm system constantly monitors line conditions and immediately triggers an audible or visual alarm if a leak is suspected. Automated internal, vapor, or interstitial line monitoring systems can also be set up to operate continuously and sound an alarm, flash a signal on the console, or even ring a telephone in a manager's office when a leak is suspected.

n Both automatic flow restrictors and shutoffs are permanently installed directly into the pipe or the pump housing.

n Vapor and interstitial monitoring systems can be combined with automatic shutoff systems so that whenever the monitor detects a suspected release the piping system is shut down. This would qualify as a continuous alarm system. Such a setup would meet the monthly monitoring requirement as well as the LLD requirement.

Line tightness testing

n Tracer methods do not measure pressure or flow rates of the product. Instead they use a tracer chemical to determine if there is a hole in the line. With tracer methods, all of the factors below may not apply.

n The line is taken out of service and pressurized, usually above the normal operating pressure. A drop in pressure over time, usually an hour or more, suggests a possible leak.

n Most line tightness tests are performed by a testing company. You just observe the test. The test must be performed by a New Jersey certified individual and company.

n For most line tightness tests, no permanent equipment is installed.

n In the event of trapped vapor pockets, it may not be possible to conduct a valid line tightness test. There is no way to tell definitely before the test begins if this will be a problem, but long complicated piping runs with many risers and dead ends are more likely to have vapor pockets.

n Some permanently installed electronic systems can meet the requirements of a line tightness test.

Secondary containment with interstitial monitoring

n A barrier is placed between the piping and the environment. Double-walled piping or a leakproof liner in the piping trench can be used.

n A monitor is placed between the piping and the barrier to sense a leak if it occurs. Monitors range from a simple stick that can be put in a sump to see if a liquid is present, to continuous automated systems, such as those that monitor for the presence of liquid product or vapors.

n Proper installation of secondary containment is the most important and the most difficult aspect of this leak detection method. Trained and experienced New Jersey certified installers are necessary.

n See the section on secondary containment for additional information. Secondary containment for piping is similar to that for tanks.

Vapor or groundwater monitoring

n Vapor monitoring detects product that leaks into the soil and evaporates.

n Groundwater monitoring checks for leaked product floating on the groundwater near the piping.

n A site assessment must be used to determine monitoring well placement and spacing.

n UST systems using vapor or groundwater monitoring for the tanks are well suited to use the same monitoring method for the piping.

n See the earlier sections on vapor and groundwater monitoring. Use of these methods with piping is similar to that for tanks.

In-Line electronic pressure monitor

n In-line electronic pressure monitors check for loss of pressure in a line when no product is dispensed. This method may be used once every 30 days or every time the dispenser turns off. It must be able to detect a leak as small as 0.2 gallons per hour with certain probabilities of detection and false alarm.

PUBLICATIONS

TITLE AVAILABLE FREE FROM

Musts For USTs: A Summary Of The Federal Regulations For Underground Storage Tank Systems

Booklet clearly summarizes federal UST requirements for installation, release detection, spill, overfill, and corrosion protection, corrective action, closure, reporting and recordkeeping. (About 40 pages.)

Normas Y Procedimientos Para T.S.A.

Spanish translation of Musts For USTs. (About 40 pages.)

Tank Issues: Site Characterization For External Leak Monitoring

Booklet discusses natural and man-made site characteristics that need to be considered in the design of a vapor or groundwater monitoring system. (About 5 pages.)

Tank Issues: Design And Placement Of Floating Liquid Monitoring Wells

Booklet discusses site conditions that affect the performance of liquid product monitors and the construction and placement of monitoring wells. (About 5 pages.)

Dollars And Sense: Financial Responsibility Requirements For Underground Storage Tanks

Booklet clearly summarizes the "financial responsibility" required of UST owners and operators by federal UST regulations. (About 16 pages.)

An Overview Of Underground Storage Tank Remediation Options

Fact sheets provide information about technologies that can be used to remediate petroleum contamination in soil and groundwater. (About 26 pages.)

Controlling UST Cleanup Costs

Fact sheet series on the cleanup process includes: Hiring a Contractor, Negotiating the Contract, Interpreting the Bill, Managing the Process, and Understanding Contractor Code Words. (About 10 pages.)

 

You can call EPA's toll-free RCRA/Superfund Hotline at 800 424-9346 and order free copies. Just identify the titles you want. Or you can write and ask for titles by addressing your requests to:

NCEPI

Box 42419

Cincinnati, OH 45242

Or you can fax your order to NCEPI at 513 891-6685.

 

Doing Inventory Control Right: For Underground Storage Tanks

Booklet describes how owners and operators of USTs can use inventory control and periodic tightness testing to meet federal leak detection requirements. Contains reporting forms. (About 16 pages.)

Manual Tank Gauging: For Small Underground Storage Tanks

Booklet provides simple, step-by-step directions for conducting manual tank gauging for tanks 2,000 gallons or smaller. Contains reporting forms. (About 12 pages.)

Don't Wait Until 1998: Spill, Overfill, And Corrosion Protection For Underground Storage Tanks

Information to help owners and operators of USTs meet the 1998 deadline for compliance with requirements to upgrade, replace, or close USTs installed before December 1988. (About 16 pages.)

 

 

 

 

You can call DEP at 609 292-8761 to request these three publications.

VIDEOS

TITLE/COST AVAILABLE FROM

Doing It Right

Illustrates proper installation of underground tanks and piping for installation crews. Part 1: Tanks (24 minutes); Part 2: Piping (16 minutes). Cost: $25

Doing It Right II: Installing Required UST Equipment

Illustrates installation of spill and overfill equipment, observation wells, and piping leak detection (23 minutes). Cost: $60

Doing It Right and Doing it Right II Set Cost: $75

Keeping It Clean: Making Safe And Spill-Free Motor Fuel Deliveries

Making pollution-free deliveries to USTs. Includes Stage 1 vapor recovery, overfill prevention and spill containment. For fuel tanker drivers and UST owner/operators (25 minutes). Cost: $60

Petroleum Leaks Underground

How liquids and vapors move in the subsurface and why early response to leaked petroleum is so important. Part 1: How Liquids Move (14 minutes); Part 2: How Vapors Move (15 minutes). Cost: $75

Straight Talk On Leak Detection

Overview of the leak detection methods available for complying with federal regulations. Part 1: Straight Talk From Tank Owners (owners address the problems of UST compliance [5 minutes]); Part 2: Straight Talk On Leak Detection (30 minutes). Cost: $40

 

 

Environmental Media Center

Box 30212

Bethesda, MD 20814

301 654-7141

800 522-0362

Visa and MasterCard accepted

 

Tank Closure Without Tears: An Inspector's Safety Guide

Focuses on explosive vapors and safe tank removal (30 minutes). Video and Booklet Cost: $35; Booklet: $5

What Do We Have Here?: An Inspector's Guide To Site Assessment At Tank Closure

Inspecting sites for contamination where tanks have been removed.

Part 1: Site Assessment Overview (30 minutes); Part 2: Field Testing Instruments At A Glance (14 minutes); Part 3: Soil And Water Sampling At A Glance (7 minutes). Video and Booklet Cost: $45; Booklet: $5

Searching For The Honest Tank: A Guide To UST Facility Compliance Inspection

Covers major steps of UST inspections from protocols and equipment to enforcement and followup; from cathodic protection to leak detection. Directed at inspectors, yet also helpful to owners and operators (30 minutes). Video and Booklet Cost: $40; Booklet: $5

New England Interstate Environmental Training Center

ATTN:VIDEOS

2 Fort Road

South Portland, ME 04106

207 767-2539

NOTE: Only shaded UST classifications are currently required to comply with leak detection requirements. However, any UST with an individual capacity of 110 gallons or less is regulated by the state UST law only, and need not comply with leak detection requirements at this time.

Substance Stored/

Use

Tank

Capacity*

Applicable

Law(s)

Comments/

Explanations

Heating Oil for

sale, distribution,

or commercial use

any

amount

Federal and

state UST

laws

Fuel oil dealers, and others who sell, distribute, or use heating oil in a commercial process, must comply.

Heating Oil for

non-residential

heating

more than

2,000

gallons

State UST

law

Facilities with aggregate UST capacities of 2,000 gallons or less are exempt from the state UST law. Heating oil tanks of any size used for residential heating are also exempt.

Motor Fuels

for non-residential

use or sale

any

amount

Federal and

state UST

laws

Includes petroleum products used in the operation of a motor: gasoline, diesel, aviation, gasohol, etc.

Motor Fuels

for farm or

residential use

more than

1,100

gallons

Federal and

state UST

laws

USTs located at a residence but used for business purposes are required to comply. Owners of farm USTs should contact the DEP at the number below for special applicability information.

Waste Oil

any

amount

Federal and

state UST

laws

Waste Oil includes used automotive crankcase oil and other used lubricating oils.

Hazardous

Wastes

 

any

amount

State UST

law

Although they are not regulated by the federal UST law, hazardous wastes ARE regulated by Subtitle C of the Resource Conservation and Recovery Act (42 U.S.C. §6921). For hazardous waste classification and technical assistance, contact the DEP Bureau of Advisement and Manifest at (609) 292 8341.

Other Hazardous

Substances

any

amount

Federal and

state UST

laws

A list of hazardous substances is available from the DEP by calling the number below.

* All gallonage figures are based upon the manufacturer's nominal tank capacity only. All gallonage totals are aggregate for the substance stored at the specific site.

For Applicability Questions call (609) 777 0899.