AUCSC Advanced Course for CP Textook042913_2

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 Advanced Course

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 APPALACHIAN UNDERGROUND CORROSION SHORT COURSE

 ADVANCED COURSE

CHAPTER 1 - PIPE-TO-SOIL POTENTIAL SURVEYS AND ANALYSIS . . . . . . . . . . 1-1

INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1-1

CORROSION MECHANISMS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1-1

PIPE-TO-SOIL POTENTIAL MEASUREMENT . . . . . . . . . . . . . . . . . . . . . . . . . . . 1-2

TYPES OF POTENTIAL SURVEYS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1-2

SINGLE ELECTRODE METHOD . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1-3

TWO ELECTRODE METHOD . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1-3

SIDE-DRAIN MEASUREMENTS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1-4

 ANALYZING PIPE-TO-SOIL POTENTIAL DATA . . . . . . . . . . . . . . . . . . . . . . . . . 1-4

PIPE-TO-SOIL POTENTIAL SURVEYS AND ANALYSIS . . . . . . . . . . . . . . . . . . . 1-5

INTERPRETATION OF POTENTIALS UNDER NON-STRAY CURRENTCONDITIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1-6

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100 MILLIVOLT POLARIZATION CRITERION . . . . . . . . . . . . . . . . . . . . . . . . . . 1-12

CRITERIA FOR SPECIAL CONDITIONS - NET PROTECTIVE CURRENTCRITERION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1-13

OTHER CRITERIA . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1-14

E LOG I CURVE CRITERION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1-14

300 MILLIVOLT POTENTIAL SHIFT CRITERION . . . . . . . . . . . . . . . . . . . . . . . 1-15

USE OF CRITERIA . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1-16

CHAPTER 2 - EVALUATION OF UNDERGROUND COATINGS USING ABOVEGROUND TECHNIQUES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2-1

INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2-1

SURVEY SEQUENCE . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2-1

REFERENCED PROCEDURES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2-1

DEFINITIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2-2

SAFETY CONSIDERATIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2-3

PIPELINE LOCATING . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2-3

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Prepared Backfill and Packaging . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-2

Wire and Cable Attachment . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-3

Magnesium Alloys . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-3

Zinc Alloys . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-3

 Aluminum Alloys . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-4

IMPRESSED CURRENT CATHODIC PROTECTION SYSTEMS . . . . . . . . . . . . . 3-5

Types of Impressed Current Anodes . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-5

High Silicon Cast Iron . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-5

Graphite Anodes . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-6

Mixed Metal Oxide Anodes . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-7

Platinum Anodes . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-8

 Aluminum Anodes . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-9

Mixed Metal Oxide Anodes . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-9

Lead Silver Anodes . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-9

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PERMANENTLY INSTALLED REFERENCE ELECTRODES . . . . . . . . . . . . . . . 3-14

TEST STATIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-14

FLANGE ISOLATORS AND DIELECTRIC UNIONS . . . . . . . . . . . . . . . . . . . . . . 3-15

MONOLITHIC WELD IN ISOLATORS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-16

CASING ISOLATORS AND END SEALS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-16

CONCLUSIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3-16

CHAPTER 4 - DYNAMIC STRAY CURRENT ANALYSIS . . . . . . . . . . . . . . . . . . . . . 4-1

INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4-1

STRAY CURRENTS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4-1

THE EARTH AS A CONDUCTOR . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4-1

POTENTIAL GRADIENTS IN THE EARTH . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4-2

DETECTION OF DYNAMIC STRAY CURRENTS . . . . . . . . . . . . . . . . . . . . . . . . 4-2

Interpreting Beta Curves . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4-3

Determining the Point of Maximum Exposure . . . . . . . . . . . . . . . . . . . . . . . . . 4-4

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CHAPTER 5 - DESIGN OF IMPRESSED CURRENT CATHODIC PROTECTION . . 5-1

INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5-1

REVIEW OF IMPRESSED CURRENT SYSTEM FUNDAMENTALS . . . . . . . . . . 5-1

Definition . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5-1

Theory of Operation . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5-1

 Application . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5-2

 Advantages and Disadvantages . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5-2

INFORMATION USEFUL FOR DESIGN OF AN IMPRESSED CURRENTCATHODIC PROTECTION SYSTEM . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5-2

DESIGN OF AN IMPRESSED CURRENT ANODE BED . . . . . . . . . . . . . . . . . . . 5-3

General . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5-3

Selecting an Anode Bed Site . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5-3

Selecting Anode Bed Type Based on Site Selection . . . . . . . . . . . . . . . . . . . . 5-4

Distributed Anode Bed . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5-4

Remote Anode Bed . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5-4

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DESIGN OF DISTRIBUTED ANODE BED . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5-14

DESIGN OF DEEP ANODE BED . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5-15

CONCLUSIONS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5-16

CHAPTER 6 - DESIGN OF GALVANIC ANODE CATHODIC PROTECTION . . . . . . 6-1

INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6-1

GALVANIC ANODE APPLICATION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6-1

General Uses . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6-1

Specific Uses . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6-1

GALVANIC ANODE CATHODIC PROTECTION DESIGN PARAMETERS . . . . . 6-1

Galvanic Anode Selection . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6-1

 Anode Current Efficiency . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6-2

Current Requirements . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6-2

Electrolyte Resistivity . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6-2

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CHAPTER 7 - MIC INSPECTION AND TESTING

INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7-1

SITE SELECTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7-1

COATING INSPECTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7-2

MIC AND DEPOSIT SAMPLING . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7-2

MIC SAMPLING AND TESTING . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7-2

SUPPORTING ANALYSES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7-3

METALLURGICAL INSPECTION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7-4

 April 29, 2013 Revision

To submit comments, corrections, etc. for this text, please email: [email protected]

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CHAPTER 1

PIPE-TO-SOIL POTENTIAL SURVEYS AND ANALYSIS

INTRODUCTION

The objective of this chapter is to present themost important corrosion control measurement,the pipe-to-soil potential measurement, and thevarious methods that can be used to make thismeasurement.

This chapter will also show how pipe-to-soilpotential data can be used to identify and

evaluate corrosion problems as well as assist indetermining the effectiveness of a cathodicprotection system.

 Also included in this chapter is a discussion of the criteria for cathodic protection and theapplications for each.

 All pipe-to-soil potential values given in thischapter will be with respect to a saturatedcopper/copper sulfate reference electrode

CORROSION MECHANISMS

The corrosion of an underground or submergedmetallic structure is electrochemical in nature.There are basically two different mechanismswhich are responsible for this corrosion andthese are termed electrolytic corrosion andgalvanic corrosion.

Electrolytic corrosion, often called stray current

corrosion, results from currents which areintroduced into the ground from neighboringsources of direct current (DC) such as electricrailways, DC powered machinery, and foreigncathodic protection systems.

Galvanic corrosion is the result of the naturalelectrochemical process that takes place on a

buried metallic structure due to potentialdifferences which exist between points on thesame structure due to different surfaces,

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HIGH IMPEDANCEVOLTMETER

CURBBOX

TESTLEAD

COPPER/COPPER SULFATEREFERENCE ELECTRODE (CSE)

SOIL

PIPE

-0.85

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amount of time that the structure is effected, DCvoltage recording instruments can be

employed.

Non-fluctuating stray current or static straycurrent is not as readily apparent as thedynamic type. In this case, the interferenceeffect from a foreign cathodic protection systemwill usually remain constant and unless there isexisting historical potential data, or one has theopportunity to participate in cooperative

interference testing, this type of stray currentinterference may not be immediately detected.However, there are potential measurementtechniques that can detect this type of straycurrent interference such as lateral potentialsurveys, which will be discussed later in thischapter.

PIPE-TO-SOIL POTENTIAL MEASUREMENT

Before the various test methods and evaluationprocesses are discussed, a review of the pipe-to-soil potential measurement is required. Thismeasurement must be obtained using a highimpedance voltmeter, a calibrated referenceelectrode, an electrolyte present over the pipewhere the reference electrode can be placed,

and a method by which to contact the structureunder test. A high impedance voltmeter isrequired in order to obtain the most accurate

critical when recording these potential valueswhether it be as a negative value or a positive

value. The methods and instrumentationemployed for this testing are critical in order toprovide meaningful data that can be properlyevaluated.

TYPES OF POTENTIAL SURVEYS

 A normal survey of a pipeline system in order toobtain either static or native potential values or 

to ascertain the effectiveness of an existingcathodic protection system might consist of measuring pipe-to-soil potentials at all availabletest locations such as those describedpreviously. However, there are occasions whenit is necessary to obtain additional potentialmeasurements between test points. This isaccomplished by placing the reference

electrode at regular intervals over the pipelineand measuring potentials at each referencelocation. The spacing of the intervals willdepend on the type of survey being performedand the type of detail required. This type of survey will indicate the anodic locations alongan unprotected structure which will be thoseareas with the most negative potentials.However, these more negative potentials may

also correspond to a stray current “pickup”area. In the case of a pipeline under cathodicprotection, this type of survey will reveal those

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It is also important to insure that the pipelineyou are testing is electrically continuous for the

length of pipe to be surveyed.

Detailed over-the-line potential surveys can beconducted using various methods and testequipment which will yield a variety of usefulinformation. The following is a description of some commonly used survey methods.

SINGLE ELECTRODE METHOD

The first method to be discussed is the singleelectrode survey, see Figure 1-2. This surveyutilizes one CSE, a high impedance voltmeter,and a reel of test wire. An additionalrequirement is a point of electrical contact tothe structure being tested.

There are two ways to perform this particular survey. In the first procedure, the pipeline iscontacted through a test lead or other suitableconnection point which is connected to a testreel. The test reel is connected to the positiveterminal of a voltmeter and the testingpersonnel measure potentials along thepipeline at prescribed intervals, carrying andmoving both the voltmeter and the reference

electrode together. Once again, the referenceelectrode is connected to the negative terminalof the voltmeter. This polarity convention can be

using the one electrode method may beaffected by voltage drop in the pipeline and

measuring circuit or by stray currentinterference.

The data can be recorded manually on fielddata sheets or electronically using a recordingvoltmeter or datalogger.

Figure 1-3 shows the basic components andhookups for recording the data electronically

using a computerized system. In this case, thevoltage measuring and datalogging equipmentcan be carried in a compact backpackarrangement by the operator. The operator carries one or two reference electrodes, whichmay be affixed to the bottom of extensionrod(s), which are then “walked” forward at somespecific interval, usually 2½ to 3 feet. Potential

measurements are electronically recorded andstored by the instrument. The long test leadback to the connection to the pipeline at thesurvey starting point can be a one-time-usedisposable light gauge wire. During the courseof the potential survey the operator is able toelectronically note distances, terrain featuresand landmarks as well as other pertinentinformation.

The electronically collected data can then beprocessed by a personal computer in the field

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HIGH IMPEDANCE VOLTMETER

(-)(+)

SINGLE REFERENCE ELECTRODEMOVED ALONG LINE

PERMANENTTEST POINT

PIPELINE

ETC. GRADE

-0.85

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WIRE REEL

(+) (–)EXPENDABLETEST WIRE

PERMANENTTEST POINT

PIPELINE

GRADE

BACKPACKCONTAINING

DATA ACQUISITION ANDLOGGING EQUIPMENT

“WALKING” REFERENCEELECTRODES

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VOLTMETER POSITIONS

(+) (–)

PERMANENTTEST STATION

PIPELINE

ETC.

GRADE

1 2 3 4 5

“A” “B” “A” “B” “A”

NEXT PERMANENTTEST STATION

“LEAP FROGGING” REFERENCEELECTRODES “A” & “B”

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along and directly over the pipeline at somepreselected survey interval from reference

electrode “A”. The potential difference betweenthe two electrodes is then measured andnumerically added or subtracted from theprevious reading in accordance with themeasured polarity of the forward electrode (“B”in this case). This “leap frogging” of the twoelectrodes is continued until the next permanenttest station is reached or any other locationwhere the pipeline can be electrically

contacted.

 At this juncture, the cumulative potential up tothis point is compared to the actual potentialmeasured to a CSE at this second permanenttest station and adjusted as necessary. Thesurvey then continues following the abovedescribed procedure to the next contact point.

The data should be recorded in a permanentlog. See Table 1-1 for a typical recordingformat.

The two electrode method works well. However,it requires that a great deal of care be taken inrecording the data. An error made in thecalculating of potentials or the noting of polarity

at any given point will cause all subsequentcalculated potentials to be erroneous. In thecase of an error, the calculated pipe-to-

areas. Side-drain measurements are conductedutilizing two CSEs and a high impedance

voltmeter, as shown in Figure 1-5. The firstelectrode is placed directly above the pipe, incontact with the soil. The second electrode isplaced in contact with the soil at a 90º angle tothe pipe at a distance approximately equal to2½ times the pipe depth. During testing, theelectrode placed directly above the pipe shouldbe connected to the positive terminal of thevoltmeter and the other electrode to the

negative terminal. Positive side-drain readingsindicate that current is being discharged fromthe pipe at this point, making it an anodic area.Negative side-drain readings normally indicatethat current is flowing towards or onto the pipeat this point, making it a cathodic area. Theside-drain measurements should be takentypically at no more than 5-foot intervals. Testsmust be made on both sides of the pipe, untilthe extent of the problem section has beendetermined.

This technique should be used with caution.Under certain conditions, a relatively stronglocalized anodic cell could exist on the bottomof the pipe with the top of the pipe serving as acathode and negative side-drain readings could

be measured while severe corrosion is actuallyoccurring on the bottom of the pipe at thislocation.

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TABLE 1-1

Typical Data Record For Two Electrode Potential Survey

Conducted on a Cathodically Protected Pipeline

 A B C D Comments

1 -- - -0.860(1) --

2 0.035 + -0.895 --

3 0.021 + -0.916 --

4 0.065 - -0.851 --

5 0.092 - -0.759 Unprotected Area

6 0.045 + -0.804 Unprotected Area

7 0.063 + -0.867 --

8 0.011 + -0.878 --

9 0.020 - -0.858 --

10 0.032 + -0.890 --

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(+)(–)

HIGH IMPEDANCEVOLTMETER

GRADE

PIPE BEING

TESTED

CUSO REFERENCEELECTRODE (TYP.)

4

C

-0.85

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Normally, after the survey data is plotted, the-850 mV value is red-lined on the plot. All areas

below this line are considered to beinadequately protected and in need of remedialmeasures. Figure 1-6 shows a typical pipe-to-soil potential profile of a cathodically protectedpipeline.

On pipelines which are not cathodicallyprotected, the pipe-to-soil potential profile andsurface potential surveys can be used to locate

corroding areas or “hot spots” along thepipeline. Experience has shown that when adifference in pipe-to-soil potential values existalong a pipeline, corrosion occurs at, and for agiven distance on either side of, the mostnegative or anodic points along the pipeline.

Figure 1-7 shows some typical potential andpolarity changes which may be recorded atcorroding or anodic areas on the pipe. Theexact point of “current discharge” can bedetermined by resurveying the effected areaand successively reducing the electrodespacing by one-half. When the exact point of maximum “current discharge” (most negativepotential) has been determined, the pointshould be staked, and all pertinent data

recorded.

Pipe-to-soil potential measurements taken over

localized corrosion cells where the anode andthe cathode are located very close to each

other.

PIPE-TO-SOIL POTENTIAL SURVEYS AND

 ANALYSIS

Figure 1-8 shows a typical potential profile on apipe on which the corrosion activity is one of straight forward galvanic action and is not beinginfluenced by interference currents or bimetallic

corrosion. Figure 1-9 shows a typical potentialprofile on a pipe which is exposed to damageas a result of a rectifier unit on a crossingpipeline. In comparing these two potentialprofiles, it should be noted that irrespective of the condition which exists, anodic areas alwaysexist at the locations where the “over the pipe”potentials are more negative than the “off thepipe” potentials. However, in a straightforwardgalvanic situation such as shown in Figure 1-8,the anodic areas occur at locations where the“over the pipe” potentials are of higher negativevalues than those measured in the cathodicareas. In an interference situation such asshown in Figure 1-9, the anodic areas are atthose locations where the potentials (both“over” and “off” the pipe) are of lower negative

values than those at the cathodic areas.

It should be noted that although a potential

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-0.1

-0.2

-0.3

-0.4

-0.5

-0.6

-1.3

-1.2

-1.1

-1.0

-0.9

-0.8

-0.7

100 200 300 400 500 600 700 800 900 1000 1100 1200 1300 1400 1500 1600 1700 1800 1900

PROTECTED AREAS

(MORE NEGATIVE THAN -0.85VOLT)

-0.85 VOLT

UNPROTECTED AREAS

(LESS NEGATIVE THAN -0.85 VOLT)

NOTE: APPLICABLE CRITERION FOR THIS  LINE IS -0.85 VOLT TO Cu-CuSO

4

   P   I   P   E  -   T   O  -   S   O   I   L   P   O   T   E   N

   T   I   A   L   (   V   O   L   T   S   T   O    C

   U  -   C

   U   S   O 

   )   4

0

-1.4

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CU-CUSO

REFERENCEELECTRODE

(TYP.)

DIRECTION OF SURVEY

GRADE

CATHODIC - ANODIC -CATHODIC

4

+18MV -10MV -2MV +3MV -2MV -4MV

PIPELINE

HIGHIMPEDANCEVOLTMETER(TYP.)

+8MV +12M

CATHODIC - ANODIC - CATHODIC

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CURRENTDISCHARGE-110

-100

-900

-800

-700

-600

-500

-400

-300

-200

-100

CURRENTPICK-UP

CURRENTDISCHARGE

CURRENTPICK-UP

CURRENTDISCHARGE

ANODIC

AREA

CATHODIC

AREA

ANODIC

AREA

CATHODIC

AREA

ANODIC

AREA

25 FEET FROM PIPE

OVER PIPE

   P   I   P   E  –   T   O  –   S   O   I   L   P   O   T   E   N   T

   I   A   L   (   M   I   L   L   I   V   O   L   T   S   )

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-110

-100

-900

-800

-700

-600

-500

-400

-300

-200

-100

CURRENT

CURRENT

DISCHARGE

CURRENT PICK-UP

CATHODIC

AREAANODIC

AREA

CATHODIC

AREA

25 FEET FROM PIPE

OVER PIPE

-120

   P   I   P   E  –   T   O  –   S   O   I   L   P   O   T   E   N   T   I   A   L   (   M   I   L   L   I   V   O   L   T   S   )

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-110

-100

-900

-800

-700

-600

-500

-400

-300

-200

-100

NORMAL GALVANIC

DISCHARGE TO

COPPER NORMAL

25 FEET FROM PIPE

OVER PIPE

-120

   P   I   P   E  –   T   O  –   S   O   I   L   P   O   T   E   N   T   I   A   L

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that type of situation, a complete investigationof the conditions which exist in a given area willusually yield the information necessary toestablish whether the potentials are attributableto interference or bimetallic activity.

Even without knowledge of the surroundingconditions, there are usually sufficientdifferences between two profiles to distinguishthem. Thus, in an interference situation, theportions of the pipe immediately adjacent to the

anodic area are almost always entirelycathodic. In a bimetallic situation, the profile of the pipe outside the area of bimetallic influenceis one which is similar to the normal galvanicprofile shown in Figure 1-8.

For the purpose of distinguishing the type of corrosion activity that is present, in the absenceof a cathodic protection system, the followinggeneral rules can be given.

1. Anodic areas exist at locations where thelateral (off the pipe) measurements are lessnegative than the “over the pipe”measurements. Conversely, cathodic areasexist at locations where the lateralmeasurements are more negative than the

“over the pipe” measurement. This conditionalways holds, irrespective of whether thecorrosion activity is a result of an electrolytic

INTERPRETATION OF POTENTIALS UNDER

NON-STRAY CURRENT CONDITIONS

 After it has been determined that stray currentsare not present, potential measurements can beused in analyzing the galvanic corrosion patternwhich may exist. Surface condition of the pipe,chemical composition of the soil, and other local conditions can greatly influence staticpotentials along the length of a pipeline.Therefore, the more readings taken, the better 

the evaluation. A more comprehensiveinterpretation of potential measurements can bederived from the following statements.

1. The potentials of newer pipes are morenegative than those of older pipes.

2. The potentials of coated pipes (organiccoating such a coal tar, asphalt, plastic tape,etc.) are more negative than those of barepipes.

3. The variation in potential with respect todistance is generally greater along a barepipe than along a coated pipe.

4. The normal potentials taken along a bare

pipe fall in the range of -500 to -600 mV. Anewly installed bare pipe will have higher negative potentials, and very old bare pipe

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It should be understood that all of the abovestatements apply primarily to steel pipelinesthat are in non-stray current areas and are notsubject to bimetallic influences or cathodicprotection. Also, where comparisons are made,such as between coated and bare pipe or between old and new pipe, it is assumed thatother conditions are equal.

These statements are intended as ageneralized guide for interpretation of potential

measurements. They are not to be consideredas scientific principles and they do notnecessarily hold true under all circumstances.They are merely a summation of fieldexperience. They are not derived fromcontrolled experiments or rigid reasoning.Despite the apparently severe qualificationsthat have been applied to these statements, if they are used with care and with completeappreciation of the theory of galvanic corrosion,most corrosion problems can be evaluatedsuccessfully.

COATED CROSS-COUNTRY PIPELINE

WITHOUT CATHODIC PROTECTION

The potential measurements shown in Table

1-2 were recorded during a pipe-to-soil potentialsurvey along a portion of a well-coated,cross-country pipeline. Examining the data in

piping at those locations.

Statements 1 and 2 indicate that older, barelines are of lower negative potentials thannewer, coated lines. The coupling of the coatedline to the bare line makes the potentials on thecoated line less negative at the shorted meter and regulator stations than along the balance of the pipeline. This situation shows theimportance of placing isolating flanges betweennew coated pipe and older bare pipe. This

isolation is needed whether or not cathodicprotection is provided for the coated line. If cathodic protection is not provided, the newcoated pipe will be anodic with respect to theolder, bare pipe. As a result, if there were noisolating flange installed between the twosections, or if the flange were shorted, thenewer coated section of pipe would besubjected to accelerated galvanic corrosionattack. When using isolating flanges or devices,safety precautions must be followed to preventa spark or arc across the isolator during a faultor power surge or static discharge. Devicesexist that will maintain DC isolation while actingas a shunt under the above conditions.

GAS SERVICE LINE

The previous example shows the need for athorough investigation of a situation where

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TABLE 1-2

Potential Measurements

Test StationLocation No.

Description of LocationPipe-to-Soil

Potential (millivolts)

21 Crestdale Regulator Station -703

22 North side of Blue River on Rt. 95 -700

24 South side of Blue River -735

26 Linden Metering Station -542

26 Valve box approximately 7.8 miles South of Blue River -730

28 Creek, 10.2 miles south of Blue River -674

30 Atlantic Regulator Station -563

31 Glendale Metering Station -780

32 Crossing of railroad near Glendale -506

33 Forest Park Regulator No. 1 -480

35 Forest Park Regulator No. 2 -537

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closer inspection however, it was discoveredthat the water service lines in the developmentwere electrically continuous with the gasservice lines. Copper, being cathodic withrespect to steel, will when connected to a steelpipe, cause the potential of the steel pipe tobecome less negative than its natural potential.

 As a result of area relationships (the ratio of areas of copper to steel is greater when thesteel is coated than when it is bare), the effectof copper on the potential of coated steel pipe

will be far greater than that on the potential of bare pipes.

GROUNDING SYSTEM

The next example involves a somewhat similar situation as the previous example, but anextensive copper electrical grounding system isinvolved rather than copper pipes.

 A potential profile was conducted on a newlyinstalled, underground, coated steel pipe. Theover-the-line potentials were in the range of -600 to -700 mV, which seems to be inaccordance with the previous statements. Anoff-the-line potential profile was also conductedon the line. Interestingly, the two profiles were

nearly identical.

Potential profiles were also conducted along

corrosion activity exists. In fact, the condition atthis plant was so severe that leaks developedwithin the first year of operation despite the factthat the pipeline was extremely well-coated andhad been backfilled with sand. The very goodcoating no doubt contributed to the rapiddevelopment of leaks on the pipeline due to theconcentration of current discharge at holidaysin the coating. The corrosion current wasgenerated by the bimetallic coupling.

STEEL GAS AND WATER LINES

In the examples given thus far, it is possiblethat the bimetallic effect of copper could havebeen anticipated without having a completeknowledge of the potential pattern. The nextexample, however, describes a situation whichis similar to a bimetallic corrosion pattern butwhere there is no copper present. This exampleinvolves a group of school buildings. Leaksoccurred on these pipes within the first year,and these leaks were attributed to the verycorrosive soil in which resistivity was less than100 ohm-centimeters. However, potentialmeasurements taken on the gas and water lines were all in the range of -350 to -450 mV.If the corrosion activity was one of 

straightforward galvanic action resulting fromthe corrosiveness of the soil, these potentialswould be considered as very cathodic and,

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the soil to the radiant heat lines in the concrete(there were common structural connections inthe boiler room) made the potential on the gasand water lines less negative than normal.These gas and water lines thus behaved as theanode in a mechanism which is similar to abimetallic couple. The conditions which madethis couple particularly severe were the lowresistivity soil, the proximity of the gas andwater lines to the radiant heat lines, and thefact that the area of the gas and water lines was

small compared to the area of the radiant heatlines. This area relationship was made stillworse by the fact that the gas and water lineswere coated.

The examples given show the manner in whichpipe-to-soil potential measurement can be usedin analyzing a corrosion problem. Theseexamples further show the need for learning asmuch about the structure under investigation aspossible and about any other structures in thearea. The remaining part of this chapter dealswith the current NACE criteria for cathodicprotection of steel and cast iron structures andsome of their applications.

CRITERIA FOR CATHODIC PROTECTION

Cathodic protection criteria are listed in NACEStandard Practice SP0169-2007 “Control of

to-electrolyte boundary must be consideredfor valid interpretation of this voltagemeasurement.

2. A negative polarized potential of at least 850mV relative to a saturated copper/copper sulfate reference electrode.

3. A minimum of 100 mV of cathodicpolarization between the structure surfaceand a stable reference electrode contacting

the electrolyte. The formation or decay of polarization can be measured to satisfy thiscriterion.

SP0169-2007 also states “It is not intended thatpersons responsible for external corrosioncontrol be limited to the criteria listed below.Criteria that have been successfully applied onexisting piping systems can continue to be usedon those piping systems. Any other criteriaused must achieve corrosion controlcomparable to that attained with the criteriaherein.”

Some examples of other criteria that have beenused in the past are:

C

Net Current FlowC E-log I CurveC 300 mV Shift

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instruments are left in place overnight. Thesepotentials can provide a base-line from which toevaluate other measurements.

The -850 mV criterion with cathodic protectionapplied is the one which is almost always usedin areas with significant dynamic stray currentactivity. It is generally accepted that if thepotential of the structure to a CSE remainsmore negative than -850 mV at all times, evenif there are substantial fluctuations in potential

with time, then the pipe can be consideredprotected at that particular test point. It ispossible that the amount of test points surveyedand the frequency at which those surveys areperformed may have to increase in heavy straycurrent areas due to ever-changing conditions.

Limitations of the -850 mV Potential to a

Cu/CuSO4  Reference Electrode With

Cathodic Protection Applied Criterion

 A limitation of this criterion for insuring totalprotection is that potentials can vary widelyfrom one area of the underground structure toanother as a result of coating damage,interference effects, etc. This suggests thepossibility of potentials being less negative than

-850 mV in sections of the pipe between twoconsecutive test locations. Also, the voltagedrop component in the potential measurement

that the polarized potential of the pipeline doesnot reach values at which coating damagecould occur due to hydrogen evolution at thesurface of the pipeline.

 Although this accepted criterion can be, and is,widely used for all types of structures becauseof its straightforward approach and simplicity,its most economical use is in the case of coatedstructures. Use of this criterion to protect an oldbare structure could require substantially higher 

protective current than if one of the other criterion were used.

 Another limitation of this criterion is due to therequirement that potential readings be takenwith the reference electrode contacting theelectrolyte directly over or adjacent to thepipeline to minimize voltage drop. In cases of river crossings, road crossings, etc., where theelectrode cannot be properly placed, analternative criterion may have to be used.

POLARIZED POTENTIAL OF -850 mV

MEASURED TO A Cu/CuSO4 REFERENCE

ELECTRODE

 As discussed in the previous criteria section,

one method of considering the voltage (IR) dropacross the electrolyte is to measure thestructure potential with all current sources “off”

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Limi tations of the Polarized Potential of -850

mV Measured to a Cu/CuSO4  Reference

Electrode Criterion

Polarized potentials well in excess of -850 mVshould be avoided for coated structures in order to minimize the possibility of cathodicdisbondment of the coating. SP0169-2007 alsopoints out that, “Polarized potentials that resultin excessive generation of hydrogen should beavoided on all metals, particularly higher 

strength steel, certain grades of stainless steel,titanium, aluminum alloys, and prestressedconcrete pipe.”

100 mV POLARIZATION CRITERION

The 100 mV polarization criterion, like the -850mV polarized potential, is based on thedevelopment of polarization. This causes thestructure to exhibit a more negative potentialthan in its native state.

Measurement of the polarization shift can bedetermined by either measuring its formation or decay. Determination of the amount of polarization is normally made during thepolarization decay (positive shift) period

subsequent to de-energizing the cathodicsystem, or in the case of galvanic anodes,when they are disconnected When cathodic

leave the structure unprotected for an extendedperiod of time. Normally however, the bulk of the depolarization will take place in the initialphase of the polarization decay; therefore itmay not be necessary to wait the full decayperiod except in those cases in which the totalactual polarization shift of the structure isrelatively close to 100 mV. If, during the earlyphase of polarization decay measurement, thepotential drops 100 mV or more, there is no realneed (unless the actual value is desired) to wait

for further de-polarization. If, on the other hand,the potential drop in the initial phase of thedecay period is only on the order of 50 to 60mV, it may be doubtful that the 100 mV shift willoccur. In this case, a determination should bemade as to whether a longer wait for totalde-polarization is required and justifiable.

In order to determine the formation of polarization on a pipeline/structure, it is firstnecessary to obtain static or native potentials(before the application of cathodic protectioncurrent) on the structure at a sufficient number of test locations. Once the protection system isenergized and the structure has had time topolarize, these potential measurements arerepeated with the current source interrupted.

The amount of polarization formation can thenbe determined by comparing the staticpotentials with the “instant off” potentials.

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point of discharge. The results obtained under these conditions could be misleading.Corrosion personnel must determine theeffectiveness of this criterion in areas of straycurrent activity.

The 100 mV polarization criterion is mostlyused on poorly coated or bare structures and insome instances could be useful in large pipenetworks as in compressor and regulatingstations where the cost of a cathodic protection

system to achieve either a -850 mV “on”potential or a -850 mV polarized potential maybe prohibitive. However, in an economicanalysis, the additional cost of conductingfuture periodic surveys has to be taken intoaccount; as the use of the 100 mV criterion issomewhat more complicated and costly thanthe use of the -850 mV criteria with the cathodicprotection applied.

This criterion can be used on metals other thansteel where there could be some question as towhat specific potential to use as an indication of protection. This criterion is often used for thoseinstallations where it is impractical to meeteither of the -850 mV criterion.

In piping networks, where new pipe is coupledto old pipe, it may be good practice to use the-850 mV polarized potential criterion for the new

C The only additional limitation is related to thetime required for the pipe to depolarize. Insome cases, adequate time may not beavailable to monitor the polarization decay of the pipe to the point where the criterioncould have been met.

CRITERIA FOR SPECIAL CONDITIONS -

NET PROTECTIVE CURRENT CRITERION

This criterion is listed in Section 6 of SP0169-

2007 under a special conditions section tocover those situations for bare or ineffectivelycoated pipelines where it appears that long linecorrosion activity is the primary concern.

This protection criterion is based on thepremise that if the net current at any point in astructure is flowing from the electrolyte to thestructure, there cannot be any corrosion currentdischarging from the structure to the electrolyteat that point. The principle is based on firstlocating points of active corrosion and thenmeasuring current flow to or from the structure.

Some pipeline companies use the side drainmethod for application of this criterion on thebasis that if the polarity of the voltage readings

on each side of the structure indicates currentflow towards the structure, then the structure isreceiving protective current. If the electrode

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structures. The “side drain’ surface method isnormally used in cases of single isolatedpipelines to obtain an indication of whether thepipeline was receiving cathodic protection. If the electrodes that are placed perpendicular tothe pipeline (remote) are positive in relation tothe electrode over the pipeline, it was assumedthat current is flowing toward the pipe.

In cases where there are sources of outsidegradients, it may be difficult to evaluate the

results of these tests properly.

Limitations of the Net Protective Current

Criterion

The use of this criterion is to be avoided inareas of stray current activity because potentialvariations could interfere with its use. Also,extreme care must be taken in commonpipeline corridors because other gradientsources may exist that could result in erroneousor misleading measurements.

Even though the results indicate a net currentflow towards the pipe/structure, that net currentflow is indicative only of what is happening atthe specific point of test and does not represent

what may be happening at other points on thepipeline/structure. Pipeline companies that usethe side drain method for application of this

 Appl ications of the E-Log I Curve Cri ter ion

The E-Log I Curve criterion is not generallyused by itself to evaluate existing cathodicprotection systems. Its primary use is todetermine the potential value, measured withrespect to a reference electrode, which will givea specific minimum current value required for protection. This potential value is to be at leastas negative (cathodic) as that originallymeasured at the beginning of the Tafel segment

of the E-log I curve.

Once the current value and the potential to aremote electrode have been established, futuresurveys consist of checking the current outputof the cathodic protection system and thepotential of the structure to a remote electrode.It is important that the reference electrode belocated in the same place where it was locatedduring the E-Log I tests. Because the testmethod involved is rather elaborate, the use of this method is generally limited to structureswhere conventional means of determiningcurrent requirements would be difficult.Examples of such structures are pipeline river crossings, well casings, piping networks in aconcentrated area, and in industrial parks.

Limitations of the E-Log I Curve Criterion

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300 mV POTENTIAL SHIFT CRITERION

 As opposed to working toward a certainminimum potential value to a referenceelectrode as discussed in some of the previoussections, the 300 mV potential shift criterion isbased on changing the potential of the structurein the negative direction by a specifiedminimum amount. The minimum potential shiftfor steel, as used in the past is 300 mV. Anystable reference electrode may be used with

this criterion because the method consists of measuring a potential shift and is independentof the actual potential of the electrode.Determination of the voltage shift is made withthe protective current applied.

The development of this criterion appears tohave been largely empirical or experimental innature. Although 300 mV is the Figurecommonly used at this time, other values suchas 200 or 250 mV have also been used in thepast. There were, however, two considerationsthat supported this criterion, recognizing thatcorrosion prevention still may not be 100%complete.

The first consideration was that 300 mV may be

greater than the driving potential of most of thegalvanic cells on a structure to be protected. Byshifting the structure in the negative direction by

committee concluded that the actualmeasurements or shift was not representativeof what was occurring on the surface of thestructure. This is due to the fact that when acathodic protection system is energized, animmediate shift of potential, due to a voltage(IR) drop, will be seen. In this particular application this voltage drop value is included inthe measured shift.

 Appl ications of the 300 mV Potent ial Shi ft

Criterion

This criterion has been used for entirestructures and also for hot-spot protection. It ismainly used for bare steel structures whichhave undergone a slow uniform corrosion ratedue to their age. These structures/pipesnormally have a natural potential range fromabout -200 mV to -500 mV as a result of oxidation products developing on the externalsurfaces. This criterion has also been used onsome coated pipelines where soil conditionsalter the natural or static potential of the steel to-500 mV or lower. In this case, the 300 mV shiftmay also be easier to attain than achieving apotential reading of -850 mV, and could beexpected to stop the majority of corrosion.

The 300 mV potential shift criterion is almostalways more applicable to impressed current

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CSE even after the pipe potential is shifted inthe negative direction by 300 mV. If thepotential of the structure is fluctuating morethan the shift required, this criterion cannot bevalid.

If the steel structure is coupled to a more noblemetal, a 300 mV shift might indicate that muchof the adverse effect produced by the dissimilar metal union has been overcome, but it wouldnot necessarily indicate that complete cathodic

protection is being provided to the steelstructure/pipeline itself.

USE OF CRITERIA

It must be noted that there will be situations or conditions where a single criterion cannot beused to evaluate the effectiveness of a cathodicprotection system and it is necessary to employ

a combination of criteria.

There will also be situations when theapplication of the criteria listed may beinsufficient to achieve protection. Someexamples pointed out in the SP0169-2007 aresituations where the presence of sulfides,bacteria, elevated temperatures, acid

environments, and/or dissimilar metals increasethe amount of current required for protection. Atother times values less negative than those

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CHAPTER 2

EVALUATION OF UNDERGROUND COATINGS USING ABOVEGROUND TECHNIQUES

INTRODUCTION

This chapter describes the indirect inspectionmethods intended for use as part of theExternal Corrosion Direct Assessment (ECDA)process for detecting coating flaws anddetermining cathodic protection levels on buriedpipelines. These methods are often morelaborious than surveys completed as part of normal daily operating practices as a result of the requirement for precise data set alignment.Standard pipeline surveys generally investigatedata trends over time or pipeline distance, whileECDA surveys look for small data variationsover short distances.This chapter describes the methods of 

conducting the following surveys for abovegrade indirect inspections. Other inspectionmethods can and should be used as required

stray current conditions, and large coatingholidays.

•  Alternating Current (AC) AttenuationSurveys are used to assess coating qualityand to detect and compare coatinganomalies.

SURVEY SEQUENCE

The sequence in which the surveys areconducted is crucial to optimizing the surveytechniques and data analysis. Coating holidaysurveys (DCVG and ACVG) and AC attenuationsurveys should be completed prior to a CISsurvey. With surveys completed in this manner,

pipe to electrolyte potentials can be measureddirectly above the coating holiday indicationsfound using the DCVG or ACVG method

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• NACE/CEA 54277, Specialized Surveys for Buried Pipelines 1988

• NACE Standard TM0497, MeasurementTechniques Related to Criteria for CathodicProtection on Underground or SubmergedMetallic Piping Systems

• NACE Standard SP0169, Control of External Corrosion on Underground or Submerged Metallic Piping Systems

• NACE Standard SP0177, Mitigation of  Alternating Current and Lightning Effects onMetallic Structures and Corrosion ControlSystems

DEFINITIONS

a) Anomaly: Any deviation from nominal

conditions in the external wall of a pipe, itscoating, or the electromagnetic conditionaround the pipe.

b) Cathodic Protection (CP): A technique toreduce the corrosion of a metal surface bymaking the surface the cathode of anelectrochemical cell.

c) Close-Interval Survey (CIS): A method of measuring the potential between the pipe

which the same indirect inspection tools areused.

g) Electrolyte: A chemical substancecontaining ions that migrate in an electricfield. For the purposes of this chapter,electrolyte refers to the soil or liquidadjacent to and in contact with a buried or submerged metallic piping system,including the moisture and other chemicalscontained therein.

h) Electromagnetic Inspection Technique: Anaboveground survey technique used tolocate coating defects on buried pipelinesby measuring changes in the magnetic fieldthat are caused by the defects.

i) External Corrosion Direct Assessment(ECDA): A four-step process that combines

pre-assessment, indirect inspections, directexaminations, and post assessment toevaluate the impact of external corrosion onthe integrity of a pipeline.

 j) Fault: Any anomaly in the coating, includingdisbonded areas and holidays.

k) Holiday: A discontinuity (hole) in aprotective coating that exposes thestructure surface to the environment.

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p) Pipe-to-Electrolyte Potential: SeeStructure-to-Electrolyte Potential.

q) P i p e - t o -S o i l P o t e n t i a l : S e eStructure-to-Electrolyte Potential.

r) Region: See ECDA Region.

s) Structure-to-Electrolyte Potential: Thepotential difference between the surface of a buried or submerged metallic structure

and the electrolyte that is measured withreference to an electrode in contact with theelectrolyte.

SAFETY CONSIDERATIONS

 Appropriate safety precautions, including thefollowing, should be observed when makingelectrical measurements.

• Be knowledgeable and qualified in electricalsafety precautions before installing,adjusting, repairing, removing, or testingimpressed current cathodic protectionequipment.

• Use properly insulated test lead clips and

terminals to avoid contact with anunanticipated high voltage (HV). Attach testclips one at a time using the single-hand

area. Remote lightning strikes can createhazardous voltage surges that travel alongthe pipeline.

• Use caution when stringing test leadsacross streets, roads, and other locationssubject to vehicular and pedestrian traffic.When conditions warrant, use appropriatebarricades, flagging, and/or flag persons.

• Observe appropriate Company safety

procedures, electrical codes, and applicablesafety regulations.

PIPELINE LOCATING

The pipeline must be located and marked toensure that subsequent measurements aremade directly above the pipeline. An inductiveor conductive pipe locating device can be used.

The pipe should be located within six (6) inchesperpendicular of the pipe centerline and surveyflags or paint marks placed directly above thepipeline every 100 feet using a slack chaindistance technique or a measuring wheel. Slackchain stationing error shall be no more than 2%+/-.

The locating flags/paint marks can benumbered using a permanent marker by writingthe flag number directly on the flag or painting

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DIRECT CURRENT VOLTAGE GRADIENT

SURVEYS (DCVG)

Direct current voltage gradient (DCVG) surveysare used to evaluate the coating condition onburied pipelines. Voltage gradients arise as aresult of current pickup or discharge at coatingholidays. In a DCVG survey, the DC signal iscreated by interrupting the pipeline’s CP currentor a temporary CP current, and the voltagegradient in the soil above the pipeline is

measured. Voltage gradients are located by achange in the interrupted signal strength atgrade.

DCVG is the only method that can be used toapproximate the size of a coating holiday.DCVG signal strength is not always proportionalto holiday size, as the orientation of the holidayand other factors affect the measured signal.

DCVG surveys are capable of distinguishingbetween isolated and continuous coatingdamage. The shape of the gradient fieldsurrounding a holiday provides this information.Isolated holidays, such as rock damage,produce fairly concentric gradient patterns inthe soil. Continuous coating damage, such as

disbonded coatings or cracking, produceselongated patterns.

resistance contact situations.

The current interrupter is installed in series with

the current source and set to cycle at a fast ratewith the “on” period less than the “off” period. Acommon interruption cycle is 0.3 seconds onand 0.7 seconds off. This short cycle allows for a quick deflection by the analog voltmeter needle.

DCVG surveys can be performed with

impressed current CP systems energized.Sacrificial anodes and bonds that are notdisconnected show up as anomalies. Sacrificialanodes and bonds to other structures areusually disconnected to prevent signal loss andenhance current flow down the pipeline under investigation.

The IR drop is measured at the test stations in

the proximity of the DCVG survey. It isdesirable to have a minimum of 100 to 400 mVof IR drop in soil environments and more IRdrop when surveying on asphalt/concrete, in thesection of pipeline to be surveyed. If at theestimated daily survey section limits there is nota 100 to 400 mV IR drop, then the currentoutput of the CP current source should be

increased to achieve the desired result. If theoutput cannot be increased, then the section of pipe with the 100 to 400 mV IR drop is the only

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parallel metallic structures by disconnectingelectrical bonds, negative drains to rectifiers,etc. In pipeline right of ways with multiple

electrically continuous pipelines or metallicconduits/structures, variations in the surveytechnique must be considered. For example, if parallel pipelines (metallic structures) are lessthan ten (10) feet from the pipeline under investigation, then the perpendicular probeshould be placed at half the distance betweenthe two pipelines, however, difficulties may be

encountered with current flow to the parallelmetallic structure. The perpendicular probemust be placed on the side of the investigatedpipeline without a parallel pipeline (metallicstructure). If the pipeline under investigationhas pipelines (metallic structures) on either side, then the probe should be placedperpendicular, but not above or in closeproximity to the parallel pipeline (metallic

structures).

If the voltmeter indicates a coating holiday,additional measurements should be made toconfirm the coating holiday is on the pipelineunder investigation and not the parallel pipeline.These tests include gradient measurements onboth sides of the pipeline and parallel with the

pipeline under investigation to confirm thecoating holiday location.

voltmeter at the same rate as the interrupter switching cycle. The amplitude of the swingincreases as the coating holiday is approached

and decreases after it has been passed.Current flow from the interrupted current sourceto the pipeline indicates a possible coatingholiday while current flow away from thepipeline indicates current flow past the pipeline.

When a coating holiday is found, additionalgradient measurements can be beneficial to

confirm its location and that the indication is notcurrent traveling past the pipeline. Thesegradient measurements can be made on bothsides of the pipe and parallel with the pipe oneach side of the assumed coating holiday.

 A straight-line attenuation effect is assumedbetween test station locations to calculate thesignal strength at intermediate coating holiday

locations. In order to calculate the coatingholiday size (%IR), the difference between theon and off potentials at each test station, valve,or other above grade appurtenance must bemeasured and recorded.

One reference electrode is placed at the baseof the test station or other electrical contact

point, in contact with the soil while the secondelectrode porous tip contacts the test stationwire or other properly cleaned electrical contact

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The estimated signal strength can beexemplified by using the data presented inFigure 2-6.

Estimated signal strength at defect:

Precisely locating a coating holiday is achievedby marking the approximate location of theholiday at the area where the maximumamplitude is indicated. Near the approximatecoating holiday location and offset from the lineby approximately 10 ft, the probes are placed

along the voltage gradient to obtain a null (zero)on the meter. A right-angle line through thecenter of the probe locations passes over thecoating holiday epicenter, as shown in point Ain Figure 2-7. This geometrical procedurerepeated on opposite sides of the pipelinelocates the exact point above the holiday.

 A survey flag, wooden stake, paint mark, or lathe is often placed at the indication epicenter and identified by a unique indication number

The percentage IR is used to develop a coating

condition classification system to prioritizecoating damage.

Once an indication is located, its size or severity is estimated by measuring the potentiallost from the holiday epicenter to remote earth.This potential difference is expressed as afraction of the total potential shift on the pipeline(the difference between the “on” and “off”

potential, also known as the IR drop) resultingin a value termed % IR. DCVG survey readingscan be broken into four groups based onapproximate size as follows:

Category 1: 1% to 15% IR - Indications in thiscategory are often considered of lowimportance. A properly maintained CP system

generally provides effective long-termprotection to these areas of exposed steel.

= 200 mV +1500

500 + 1500300 - 200 mV

= 200 mV + 75 mV

= 275 mV

Over the line to remote earth voltages = 25+ 15+ 6 + 4 + 3 +1+1 mV

  = 55 mv

Percentage IR =Over the line to remote earth voltage * 100%

Signal Strength

  =55* 100

275

  = 20%

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DEFECT

1500 yds 500 yds

200 mV 375 mV300 mV

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Category 4: 61% to 100% IR - The amount of exposed steel indicates that this indication is amajor consumer of protective CP current and

that massive coating damage may be present.Category 4 indications typically indicate thepotential for serious problems with the coating. These example categories are empirical innature and are based on the results of prior exploratory excavations at holiday locationsdetermined by DCVG surveys.

 ALTERNATING CURRENT VOLTA GE

GRADIENT SURVEYS (ACVG)

 Alternating current voltage gradient (ACVG)surveys are used to evaluate the coatingcondition on buried pipelines. Voltage gradientsarise as a result of current pickup or dischargeat coating holidays. In an ACVG survey, the AC

signal is created by a low frequency transmitter connected to the pipeline and the voltagegradient in the soil above the pipeline ismeasured. Voltage gradients are located by achange in the signal strength at grade.

 ACVG signal strength is not always proportionalto holiday size, as the orientation of the holiday

and other factors affect the measured signal.

ACVG surveys are capable of distinguishing

 An AC current attenuation survey may beperformed with impressed current CP systemsenergized, however by turning off the rectifier 

and using the positive and negative leads at therectifier station, the signal-generationcapabilities of the equipment can bemaximized. Sacrificial anodes and bonds thatare not disconnected show up as anomalies.Sacrificial anodes and bonds to other structuresare usually disconnected to prevent signal lossand enhance current flow down the pipeline.

The signal generator (transmitter) is connectedto the pipeline and appropriately grounded toearth. A constant AC signal is produced andtransmitted along the pipe. The transmitter isenergized and adjusted to an appropriateoutput. Typically, the largest attainable currentoutput is chosen to maximize the length of pipethat can be surveyed. An impressed current

anode bed or magnesium anode can be used toestablish an electrical ground.

The receiver consists of a handheld,symmetrical, multi-axis antenna array. Theelectromagnetic field radiating from the pipelineis measured by the detector.

The detector is used to measure the attenuationof the signal current that has been applied tothe pipe. An electrical current, when applied to

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magnitude will increase as the holiday isapproached.

The survey continues until the receiver indicates that the coating holiday has beenpassed (signal magnitude decreases anddirection arrow reverses direction) at whichpoint the operator reverses direction andshortens the interval between readings.

When the holiday is centered between the two

probes, the magnitude will be zero and thedirection arrows will not indicate a consistentcurrent direction.

The probe assembly can be used to the side of the pipe (perpendicular to the pipe) to confirmthe coating indication location. The holidaylocation is indicated by the maximum signalmagnitude with the probes placed

perpendicular to the pipe.

Either store the data in the receiver unit or record the information in the project field book.

CLOSE-INTERVAL SURVEYS (CIS)

CIS is used to measure the potential difference

between the pipe and the electrolyte. Data fromclose interval surveys are used to assess theperformance and operation of the CP system.

evaluate CP system performance inaccordance with the NACE pipeline CP criteriaas found in SP0169. On and Off surveys

measure the potential difference between thepipe and the electrolyte as the CP currentsource(s) is switched on and off.

On and Off surveys rely on electronicallysynchronized current interrupters at each CPcurrent source, bond, and other current drainpoint that influences the pipeline potential in the

survey area. The ratio of the On-to-Off interruption cycle should be long enough for readings to be made but short enough to avoidsignificant depolarization. A three second On,one second Off cycle period or similar can beused to maintain pipeline polarization over timeand allow accurate Off potentials to berecorded.

The copper sulfate reference electrodes (CSE)are placed directly over the pipeline, typically at2.5 to 5 foot intervals such that both On and Off potentials can be measured and recorded ateach reference cell location.

The accuracy of the on and off data can beverified by recording a continuous datalog

(waveprint) at test stations or points of electricalcontact such as valves or risers. This data logwill illustrate proper interrupter synchronization

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copper sulfate reference electrodes, smallgauge CIS wire (30 AWG), wire dispenser, andpipe/cable locating equipment (See above

section on pipe locating).

Standard current interrupter units include 30,60, or 100 ampere AC and DC interruptioncapacity, AC or battery-powered units, withelectronic synchronization and Global PositionSatellite (GPS) timing.

Prior to the CIS, a rectifier influence survey maybe completed to determine the CP currentsources which must be interrupted for theaccurate measuring of Off potentials. Theseinclude company rectifiers, galvanic anodesystems, foreign company rectifiers, andelectrical bonds to foreign company structures.Individually, each CP current source should betested. A current interrupter is used to

interrupt the CP current source suspected of influencing the CIS pipeline segment. Typically,a slow interruption cycle is used such as a tensecond On, five second Off period.Pipe-to-electrolyte potentials are measured atthe furthest test points suspected of influencefrom the suspect CP current source.

Test points are monitored moving away fromthe suspect CP current source. Once a 10 mVor less difference between On and Off pipe to

surveying is taking place, the interruptersshould be programmed to turn off in order tominimize the affects of depolarization.

 A 30, 32, or 34 AWG gauge insulated wire iselectrically connected to a test station test wire,valve, or other electrically continuous pipelineappurtenance and one terminal of thevoltmeter. The other terminal of the voltmeter isattached to the reference electrode.

The pipeline is located with a pipe locator prior to collecting data to ensure that the referenceelectrode is placed directly over the pipeline(See Pipe Locating Section).

Industry standard copper sulfate referenceelectrodes (CSE) should be used for potentialmeasurements. See NACE Standard TM0497.Reference electrodes should be calibrated with

an unused control reference electrode daily, theresults of which should be recorded in theproject field book. The control referenceelectrode should be a recently chargedelectrode not used to gather data in the field.To calibrate the CSE, the ceramic porouselectrode tips are placed tip to tip to measurethe voltage difference between the two

electrodes or both tips are immersed in acontainer of potable water. A digital voltmeter on the millivolt scale is used to measure the

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the completion of CIS each day. The data canbe retrieved from the datalogger each day andanalyzed for the existence of dynamic stray

currents, de-energizing of a CP source, or improper current interrupter operation.

On and Off pipe-to-electrolyte potentials arethen measured and recorded typically at 2.5 to5 foot intervals using a high-input impedancevoltmeter/datalogger. The datalogger shouldhave the ability to adjust the time during the Off 

cycle at which the handheld datalogger storesthe Off potential value due to the possibility of inductive/capacitive spiking. The datalogger should be programmed such that the On andOff pipe to electrolyte potentials are measuredand stored from a time period beyond thespiking as determined by the waveprintsdiscussed above. 

Pipe-to-electrolyte potential measurementsshould be measured and recorded at each teststation and foreign pipeline crossing from eachtest wire within accessible test stations. Near ground (NG), metallic IR Drop (IR), and far ground (FG) On and Off pipe-to-electrolytepotential measurements should be made ateach point of pipeline connection.

If the Off metallic IR drop exceeds 5 mV, thesurvey should be halted and an investigation

purposes. When a numbered flag isencountered, the flag number can also beentered into the data stream.

 All permanent landmarks should be identifiedand entered into the data logger during thesurvey. These include pipeline markers, testpoints, fences, casing vents, creeks, and roadnames.

Upon completion of the survey, all CIS wire

should be retrieved. Flags can be left in placeuntil the final ECDA process/surveys arecompleted and deemed appropriate for finalremoval.

 AC CURRENT ATTENUATION SURVEYS

(ELECTROMAGNETIC)

 AC current attenuation surveys are used to

provide an assessment of the overall quality of the pipe coating within a section or as acomparison of several sections. A current isapplied to the pipeline, and coating damage islocated and prioritized according to themagnitude and change of current attenuation.

 AC current attenuation surveys may beperformed with impressed current CP systems

energized, however by turning off the rectifier and using the positive and negative leads at therectifierstation,signal-generationcapabilitiesof

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along the pipe. The transmitter is energized andadjusted to an appropriate output. Typically, thelargest attainable current output is chosen to

maximize the length of pipe that can besurveyed. An impressed current anode bed or magnesium anode can be used to establish anelectrical ground. If operating rectifiers areinterfering with the signal, then turn the unitsoff.

Signals are measured using the receiver unit.

The receiver consists of a handheld,symmetrical, multi-axis antenna array. Theelectromagnetic field radiating from the pipelineis measured by the detector. The detector isused to measure the attenuation of a signalcurrent that has been applied to the pipe. Anelectrical current, when applied to a well-coatedburied pipeline, gradually decreases asdistance increases from the point of current

application. The electrical resistivity of thecoating under test and the surface area incontact with the soil per unit length of pipe arethe primary factors affecting the rate of declineand the frequency of the signal.

The logarithmic rate of decline of the current(attenuation), which is effectively independentof the applied current and marginally affectedby seasonal changes in soil resistivity, providesan indication of the average condition of the

accuracy of the readings may be affected bydistortions in the AC signal caused by other underground piping and conduits, traffic control

signaling, or vibrations due to passing vehicles.

Survey data are analyzed after the survey todetermine which survey intervals exhibitreduced coating quality.

SUMMARY

The indirect above ground inspectiontechniques discussed in this chapter are usedto identify and define coating faults and in turnthose areas where corrosion activity may haveoccurred or may be occurring. Two or more of these inspection techniques should be usedwhen conducting this indirect inspection testingso that different types of data can be comparedand analyzed to determine whether there is any

correlation. The effectiveness of the testingtechniques employed will depend on factorss u c h a s o p e r a t o r e x p e r i e n c e ,pipeline/coating/CP circuit conditions, depth of pipe, and type of cover at grade.

Should significant coating damage be indicatedfrom these tests, the pipeline should be

excavated and examined for possible corrosiondamage and the appropriate remedial actionsshould be taken.

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CHAPTER 3

MATERIALS FOR CATHODIC PROTECTION

INTRODUCTION

This chapter will discuss common materialsused for underground cathodic protectioninstallations. Some of the materials haveestablished track records and some are newwith very little known about the long term lifeeffects in a particular environment. For our purposes, we will define "long term" as any

material with a successful application record inunderground use of more than 20 years.

People who specify cathodic protectionmaterials must understand the advantages andlimitations of a product and how the productrelates to any given application. Furthermore,they must be able to convey in writing, thespecifics of how the product is to be

manufactured or supplied to assure that it willconform to predetermined design life criteria.

grade

When specifying materials, either requisitioningor purchasing, the following should be checked:

1. Specify materials completely.

2. Make sure that complete specifications areon the purchase order.

3. Check material received to ensure that itconforms to the original specifications.

Usage:

1. Follow the manufacturer's recommendationsand instructions.

2. Use compatible components.

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anode and the structure is referred to as the"driving potential" or "driving voltage".

The amount of current produced by a galvanicanode is a function of the driving potential andthe circuit resistance in accordance with Ohm'sLaw.

Figure 3-1 shows a schematic diagram of atypical galvanic anode installation.

Table 3-1 lists metals that are used as galvanicanodes and their alloys. For each alloy the tableshows its open circuit potential, current capacityand consumption rate. Impurities and grain sizewill cause wide ranges in these theoreticalvalues.

These are representative values taken fromliterature provided by various manufacturers. In

general, magnesium is preferred for use in soilsand fresh water. Zinc is generally limited to usein sea water, brackish water, sea mud, andsoils with resistivities below 1500 ohm-cm.

 Aluminum is generally limited to sea water,brackish water, and sea mud environments.

 An important point to consider for maximumservice life is the cost per ampere hour of current capacity, once it has been establishedthat the driving potential is sufficient for the

situation will take the resistivity of theenvironment into account and will balancecurrent requirements against desired life to

determine the size, number, and weight of anodes needed. Design of galvanic anodecathodic protection systems is covered in detailin Chapter 6 of the Advanced Course.

Prepared Backfi ll and Packaging

Magnesium and zinc anodes for use in soils are

typically supplied with a prepared backfillaround the anode.

The most commonly used backfill for magnesium and zinc anodes consists of:

75% Hydrated Gypsum (CaSO4 @ 2H20)20% Bentonite Clay5% Sodium Sulfate

The purpose of the prepared backfill is:

It increases the effective surface area of theanode which lowers the anode-to-earth contactresistance.

The bentonite clay absorbs and retainsmoisture.

The gypsum provides a uniform, low resistance

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GRADE

#12 AWG TEST LEAD (TYP.)

#12 AWG ANODE LEAD WIRE

PROTECTED PIPELINE

TEST STATION

BUS BAR OR SHUNT

GALVANIC ANODE

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 As an historical side note, zinc was formerlythought to perform better in a backfill of 50%gypsum and 50% bentonite. Over the years it

was determined that zinc may passivate if sodium sulfate is not used in the backfill.

To keep the backfill uniformly around theanode, the anodes with their lead wire attachedare placed in cloth bags or cardboard boxesand the prepared backfill is then added. Clothbagged anodes are usually placed within alayered paper bag for resistance to shortperiods of inclement weather and handlingdamage. Prior to installation, the paper bag isremoved and discarded, permitting the clothbag containing the backfill to absorb moisture,allowing the anode to start putting out currentsoon after installation. During transportationand/or handling the anodes may shift in theprepared backfill. This may result in uneven

consumption of the anode, reduction of currentoutput and premature failure of the anode. Thiscondition can be avoided by carefulspecification of transportation packaging andfield handling precautions. Anodes packaged incardboard boxes or bags with centralizingdevices may tend to reduce anode shifting.

Wire and Cable Attachment

Galvanic anodes for use in soil are typically

Zinc anodes do not have a recessed core, sothe cable is crimped and silver soldered to theextended rod core and coated with a piece of 

heat shrinkable polyethylene tubing or severallaps of electrical tape to protect the connection.

Magnesium Alloys

Magnesium anodes are produced in a widevariety of sizes and shapes to fit designparameters. They may be cast in molds or 

extruded into ribbon or rod shapes, with steelspring, perforated strap or wire cores as shownin Figure 3-2. The core is important because itshould extend 85 percent or more through theanode to reduce the internal circuit resistance.Table 3-2 shows the weights and dimensions of some common magnesium anodes. Thechemical composition of the different alloys isshown in Table 3-3.

Four (4) magnesium alloys are available. Their respective potential values and consumptionrates will be an important part of thecalculations used to design a cathodicprotection system using magnesium anodes.The potential values and consumption rates of the 4 magnesium alloys are shown in Table 3-3.

The purchaser should request a verifiablespectrographic analysis of any anode purchase

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TABLE 3-2

Magnesium Anode Dimensions and Weights

Nominal Dimensions (Inches) - See Figure 3-2

  Alloy A B C D E F GPackaged

Weight (lbs)

1 AZ63 3.2 Rd 2 6 6 - - 3.6

3 H.P./AZ63 3 3 6 8 6 - - 95 H.P./AZ63 3 3 10 12 5 - - 12

6 H.P./AZ63 3 3 10 - - 12.5 5 14

9 H.P./AZ63 3 3 13.5 17 6 - - 27

12 AZ63 4 4 12 18 7.5 - - 32

17 H.P. 3.5 3.5 25.5 30 6 - - 42

17 AZ63 3.5 3.5 28 - - 32 5.5 45

20 H.P. 2 2 60 - - 71 4.5 65

32 H.P./AZ63 5.5 5.5 21 25 8 - - 72

32 H.P./AZ63 5.5 5.5 21 - - 24 7.5 70

40 H.P. 3.5 3.5 60 64 6 - - 105

48 H.P. 5.5 5.5 32 36 8 - - 10650 AZ63 7 7 15 24 10 - - 110

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TABLE 3-3

Composition of Magnesium Alloy

Element AZ63B(H1A)

 AZ63C(H1B)

 AZ63D(H1C)

M1C(High Potential)

 Aluminum (Al) 5.3 - 6.7% 5.3 - 6.7% 5.0 - 7.0% < 0.01%

Zinc (Zn) 2.5 - 3.5% 2.5 - 3.5% 2.0 - 4.0% -

Manganese (Mn) 0.15 - 0.7% 0.15 - 0.7% 0.15 - 0.7% 0.5 - 1.3%

Silicon (Si) < 0.10% < 0.30% < 0.30% < 0.05%

Copper (Cu) < 0.02% < 0.05% < 0.10% < 0.02%

Nickel (Ni) < 0.002% < 0.003% < 0.003% < 0.001%

Iron (Fe) < 0.003% < 0.003% < 0.003% < 0.03%

Others (each) - - - < 0.05%

Others (total) < 0.30% < 0.30% < 0.30% < 0.30%

Magnesium (Mg) Balance Balance Balance Balance

Performance Characteristics*

AZ63B AZ63C AZ63D M1C

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major factor. They are available in a variety of sizes and shapes including bracelet anodes for marine pipelines, docks and piers, hull anodes

for marine vessels, and in ribbon form for use inutility ducts and for AC mitigation. Zinc is notrecommended in environments wherecarbonates or bicarbonates are found, or wherethe temperature of the electrolyte is over 120ºF. Under these situations zinc becomescathodic to steel, rather than anodic, and itsuse should be avoided.

Table 3-4 shows the weights and dimensions of some common zinc anodes.

The chemical composition of the different alloysis shown in Table 3-5.

When used strictly as an anode, zinc is wellsuited for low resistivity environments such as

sea water, salt marshes, and brackish water.Zinc normally becomes impractical for protecting large bare areas when the resistivityof the electrolyte exceeds 1500 ohm-cm.

Zinc anodes are also used as grounding cellsfor electrical protection of isolators. Zincgrounding cells are usually made from 2 or 4zinc anodes separated by a 1" isolating spacer and packaged in a cloth bag with backfill. Eachanode has a lead wire (typically AWG #6) which

indium, to reduce the passivating effect of theoxide film that forms on aluminum. Thecomposition of each alloy is shown in Table 3-6.

The mercury alloys are effective in high chlorideenvironments where chloride levels areconsistently greater than 10,000 ppm. Seawater has an average chloride level of 19,000ppm.

Indium alloys are effective in waters containing1000 ppm or more of chlorides.

The mercury alloy is used in free flowing seawater and its principle advantage is its highcurrent capacity. The current capacity of eachalloy is shown in Table 3-6. Its primarydisadvantages are that it cannot be used inbrackish water, in silt/mud zones, or at elevatedtemperatures. Under high humidity atmospheric

storage conditions some grades have beenknown to degrade and become totally unusableprior to installation. There is some controversyalso concerning the long term environmentaleffects of this alloy in sea water since itcontains mercury.

The indium alloy is used in free flowing seawater, brackish water, silt/mud zones, and atelevated temperatures. Its basic limitation is alower current capacity than the mercury alloy.

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TABLE 3-4

Zinc Dimensions and Weights

  Weight (lbs) Height Width Length Core (dia.” )

Bare Zinc Anodes

5 1.4 1.4 9 0.250

12 1.4 1.4 24 0.250

18 1.4 1.4 36 0.250

30 1.4 1.4 60 0.250

30-A 2.0 2.0 30 0.250

45 2.0 2.0 45 0.250

60 2.0 2.0 60 0.250

Zinc Ribbons

2.4 1.0 1.250 -- 0.185

1.2 0.625 0.875 -- 0.135

0.6 0.500 0.563 -- 0.130

0.25 0.344 0.469 -- 0.115

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TABLE 3-5

Zinc Alloy Compositions

Element ASTM B418-01

Type I(sea water)

 ASTM B418-01Type II(soil)

 Aluminum 0.1 - 0.5% < 0.005%

Cadmium 0.025 - 0.07% < 0.003%

Iron < 0.005% < 0.0014%

Lead < 0.006% < 0.003%

Copper < 0.005% < 0.002%

Others — 0.1%

Zinc Balance Balance

TABLE 3-6

 Aluminum Al loy Composit ion and Performance

Element

Mercury Family

 AI/Hg/Zn

Indium Family

 Al/In/Zn

Zi (Z ) 0 35 0 60% 2 8 6 5%

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4

6

1

2

3

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The anodes should be identified by heatnumber and date of manufacture. The chemicalanalysis should detail the heat number, the date

of manufacture, a listing of the impurities withthe percentages of each, and be signed by atechnically qualif ied person. Somemanufacturers identify each anode with a stampor tag; others may label each pallet of bareanodes with an identity number painted on theside.

IMPRESSED CURRENT CATHODIC

PROTECTION SYSTEMS

Unlike galvanic systems, impressed currentsystems utilize an external power source suchas a rectifier, electrically connected to anodeswith a low consumption rate. The anodes areconnected to the positive terminal of the rectifier and the circuit is completed by attaching the

negative terminal to the structure to beprotected. Figure 3-4 shows the components inan impressed current system.

 An impressed current system is used to protectlarge bare and coated structures and structuresin high resistivity electrolytes. Care must betaken when employing this type of system sothat cathodic coating damage and the potentialfor the development of stray currents, adverselyaffecting other foreign structures, are

of acids. It goes without saying that if corrosion

personnel do not effectively detail the type of anode construction they expect, they willprobably get less than they expected. Thefollowing are minimum details to address in ananode specification.

1. Anode Type, Size and Shape - composition,dimensions and weight, within 2%.

2. Lead Wire - size, type, insulation/thickness,length.

3. Type of Lead Wire Connection - end, center,<0.02 ohms resistance.

4. Lead Wire Termination - epoxy cap, fullencapsulation, shrink cap.

5. Packaging - bare, canister size/gauge,backfill type, weight.

6. Palletizing - size, padding, number per pallet.

7. Options - lifting rings, centering devices.

The sections of the specification covering thevarious types of impressed current anodes

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CATHODICPROTECTIONRECTIFIER

BURIED ANODEBED

CATHODICPROTECTION

CURRENT FLOW

NEGATIVERETURN CABLE

AC POWER SUPPLYTO RECTIFIER

 ( - ) ( + )

POSITIVEHEADER CABLE

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TABLE 3-7

Cast Iron Composit ion

 ASTM A518 Grade 3

ELEMENT COMPOSITION

Silicon 14.2 - 14.75%

Carbon 0.70 - 1.10%

Manganese 1.50% max

Molybdenum 0.20%

Chromium 3.25 - 5.00%

Copper 0.50% max

Iron Balance

TABLE 3-8

Typical Cast Iron Rod Anode Dimensions

NOMINAL

WEIGHT lbs (kgs)

NOMINAL

DIAMETERin (mm)

NOMINAL

LENGTHin (mm)

NOMINAL

 AREAft² (m²)

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The principal reason for the good performanceof cast iron anodes is the formation of a siliconoxide (SiO2) film on the anode surface, reducing

the rate of oxidation, and retarding theconsumption rate. Chromium is added toproduce a chlorine resistant alloy and improveits life in chloride containing soils and water.

Cast iron anodes have good electricalproperties and the resistivity of the alloy is 72micro ohm-cm at 20º C. In soils, the anodes areusually backfilled with metallurgical or calcinedpetroleum coke breeze to increase the effectiveanode surface area and provide uniformconsumption. By increasing the diameter or length of a cylindrical anode, the anode toelectrolyte resistance is lowered. Increasing thelength has a greater effect than increasing thediameter.

The high tensile strength of the anode is anasset in some circumstances, but it is brittleand subject to fracture from severe mechanicaland thermal shock.

Cast iron anodes are manufactured in a widevariety of dimensions, shapes and weights.Table 3-8 shows the weights and dimensions of some common high silicon cast iron anodes,

Solid cast iron anodes have the lead wires

rate to be about 0.7 pounds per ampere year ata discharge rate of 3.5 amps per square foot of anode surface area. No data has been provided

for soil or mud conditions but consumption inthese environments could double or triple theconsumption rate.

Tubular anodes range in size from 2.187" to4.750" in diameter, and from 46 pounds to 175pounds in weight, with surface area rangingfrom 50 percent - 170 percent greater thanconventional rod type anodes. The anode cableconnection strength should be tested to beequal to the breaking strength of the cablewithout any change in the 0.004 ohms or lessconnection resistance.

Thus, for the following cable sizes, connectionpull test values should be:

Connection Strength Cable Break Strength

No. 8 - 799 pounds 525 pounds

No. 6 - 1258 pounds 832 pounds

No. 4 - 1980 pounds 1320 pounds

Graphite Anodes

Graphite rods have been used as an impressed

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TEFLON (FEP) SLEEVE WITHPOLYETHYLENE WASHER (OPTIONAL)

1” EPOXY CAP(OPTIONAL)

EPOXYSEALANT

POTTINGCOMPOUN

D

TAMPEDTELLURIUM

LEADCONNECTIO

N

SHRINK CAP OR FULLEPOXY

ENCAPSULATION(OPTIONAL)

LEAD WIRE(LENGTH AND INSULATION AS SPECIFIED)

ANODE

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D CENTER CONNECTION

NOMINAL

WEIGHTlbs (kgs)

NOMINAL

DIAMETERin (mm)

NOMINAL

LENGTHin (mm)

NOMINAL

 AREAft² (m²)

31 (14) 2.6 (66) 41 (1067) 2.4 (.22)

50 (23) 2.6 (66) 60 (1520) 3.5 (.33)

46-50 (21-23) 2.2 (56) 84 (2130) 4.2 (.39)

63-70 (29-32) 2.6 (66) 84 (2130) 4.9 (.46)

85-95 (39-43) 3.8 (97) 84 (2130) 7.0 (.65)

110-122 (50-55) 4.8 (122) 84 (2130) 8.8 (.82)

175-177 (79-80) 4.8 (122) 84 (2130) 8.8 (.82)

230 (104) 4.8 (122) 84 (2130) 8.8 (.82)

260 (118) 6.7 (170) 76 (1981) 11.4 (1.06)

270 (122) 6.7 (170) 84 (2130) 12.3 (1.14)

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micro-crystalline wax, or phenolic based resin.

There is controversy concerning the best type

of filler and even whether a filler really reducesmoisture penetration over long periods of time.Whatever filler is used, it should be applied bya method that assures complete penetration of the cross-section of the graphite anode. Insoils, graphite anodes must be backfilled withmetallurgical or calcined petroleum coke breezeto increase the effective anode surface areaand provide a uniform low consumption rate.

The anode to lead wire connection is just ascritical as with a cast iron anode. Figure 3-7shows a typical graphite anode to lead wireconnection. Both end and center connectionsare available. Additional specification detailsshould include:

1. Type of connector - lead, brass, molten,compression, centered.

3. Connect ion sealant-thermoplast ic,thermosetting (epoxy).

4. Cable sealant - TFE tubing, shrink cap,encapsulation.

5. Impregnation - wax, linseed oil, resin.

bare or packaged. Special handling andpadding is necessary to prevent cracking andbreaking.

Mixed Metal Oxide Anodes

Mixed metal oxide anodes were developed inEurope during the early 1960's for use in theindustrial production of chlorine and causticsoda. The first known use of the technology for cathodic protection use occurred in Italy toprotect a sea water jetty in 1971. These anodesexhibit favorable design life characteristicswhile providing current at very high densitylevels. The oxide film is not susceptible to rapiddeterioration due to anode acid generation,rippled direct current, or half wave rectification,as is common with other precious metalanodes.

The composition of the anode consists of atitanium rod, wire, tube or expanded mesh(refer to Figure 3-8) with the oxide film bakedon the base metal. Sometimes these anodesare referred to as dimensionally stable or ceramic anodes.

For oxygen evolution environments such assoils, the anode oxide consists of rutheniumcrystals and titanium halide salts in an aqueoussolution that is applied like a paint on the base

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PottingCompound

Zone

Tamped Tellurium

Lead Connection

Epoxy

SealantZone

ConnectionLock

Rings

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BALLAST RING

COPPER

ELECTRICAL CONTACT TITANIUMSTRING ANODE

CABLE

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resistivity) that the current is discharged fromthe oxide rather than the base metal even witha rectifier voltage of 90 volts in soils. This is in

contrast to the insulating titanium dioxide filmthat naturally forms on the surface of baretitanium. When the mixed metal oxide film hasbeen consumed, the insulating titanium dioxidefilm will cover the anode and not allow currentto discharge unless the applied voltage isgreater than 10 volts in sea water or 50 to 70volts in fresh water.

The maximum recommended current densitiesfor various electrolytes are:

Soil, Mud, Fresh Water: 9.0 amps/ft2 (20 years)Sea water: 55.7 amps/ft2 (15 years)

 Anodes in soil or mud must be backfilled withfine, low resistance, calcined petroleum coke

breeze for maximum life and performance.Even when the anode is pre-packaged withpetroleum coke, conservative engineering

 judgment would dictate that the anode packagebe surrounded with metallurgical coke, prior tofinishing the backfilling with native soil.Consumption rates at these densities rangefrom 0.5 mg/Ay in sea water to 5 mg/Ay in cokebreeze, fresh water and sea mud.

As with any anode, the connection must be

Platinum Anodes

Platinum can be used as an anode coating for 

many types of cathodic protection installations.Structures in a vast array of environments suchas underground, offshore, concrete, power plants, and the internal surfaces of piping, tanksand machinery have utilized platinum for cathodic protection systems. In sea water,platinum has a low consumption rate, 0.00018pounds per ampere year, so only a smallamount is needed for a twenty-year anode life.In soil and fresh water, the consumption mayrange up to 0.005 pounds per ampere year depending on the resistivity of the electrolyteand the amount of coke breeze surrounding theanode in soil applications. Pure platinum, byitself, would be too expensive. Therefore, it isnormally coated over noble base metals suchas titanium and niobium. When anodes are in

the form of wire and rods, there may be acopper core to increase the conductivity for lengths in excess of 25 feet since titanium andniobium are relatively poor electrical conductorscompared to copper. Wire anodes for use indeep anode beds, and packaged anodes for surface anode beds are manufactured. Figure3-9 shows different types and sizes of platinumanodes.

The passive film on titanium starts to break

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20% Niobium

Diameter Inches

Nb ThicknessInches

Resistancemicrohm/ft

Pt Thicknessµ-in (2X)*

.750 .038 22 300 (600)

.500 .025 50 200 (400)

.375 .019 89 150 (300)

.250 .013 201 100 (200)

.188 .009 356 75 (150)

.125 .006 806 50 (100)

40% Niobium

Diameter Inches

Nb ThicknessInches

Resistancemicrohm/ft

Pt Thicknessµ-in (2X)*

.375 .038 113 150 (300)

.250 .025 256 100 (200)

.188 .019 453 75 (150)

.125 .013 1025 50 (100)

.093 .010 1822 38 (75)

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vacuum. This provides an oxide free, lowresistance bond between the metals.

Cladding involves wrapping a thin sheet of platinum around a rod and spot welding theplatinum to the base metal at the overlap area.

Electrodeposition techniques plate a film of platinum on the base metal.

Thermal decomposition and welded techniquesexhibit the same problems as cladding, and asof the late 1980's are rarely used.

Each process has its advantages anddisadvantages and the corrosion worker shouldevaluate them for each application.

The anode to cable connection is critical andimproper connections will result in very early

premature failure. Users should assure that theanodes are manufactured in compliance withtheir specifications by skilled personnel under the guidance of established quality controlmethods.

The major disadvantage to platinum is poor resistance to anode acid evolution in staticelectrolytes, rippled direct current, and half 

wave rectifiers. Use of a 3-phase transformer rectifier in sea water systems has been known

protection using other anode materials that willwithstand icing.

Lead Silver Anodes

Lead alloy anodes are only used in free flowingsea water applications and may employ variousmetals such as antimony, lead, tin, and 1 or 2%silver. Commonly supplied in rod or strip form of 1.5" diameter by 10" long, they have been usedextensively in Europe with a 2% silver alloy,which doubles its life.

Upon initial startup, the consumption rate isabout three pounds per ampere year andeventually a black, passive film of lead peroxideforms to extend the life of the anode, resultingin consumption of about 0.2 pounds per ampereyear. Normal current density ranges from 3 to25 amps per square foot. In silting or low

chloride conditions, this oxide film does notform and the anode is consumed rapidly.

Cable connections are made by drilling a holeand silver soldering the lead wire at the base of the hole. The connection cavity is then filledwith epoxy to prevent moisture penetration.

Installation is accomplished by hanging the

anodes from a structure, dock or pier in aperforated fiberglass pipe or by a support

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ANODE

LEAD WIRE

MAGNETITE

COPPER

LAYER

MAGNETITE

ANODE

PLASTIC

COMPOUND

PLASTIC

CAP

POROUSBODY

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Magnetite anodes installed in free flowingsea-water (25 ohm-cm) is a normal application.

Polymer Conduct ive Anodes

In 1982, an anode material was test marketedto provide a small amount of current inrestricted spaces such as internal pipesurfaces, heat exchangers, utility ducts, andareas shielded from conventional anode bedcurrent.

The material resembles electrical cable butactually consists of a stranded copper conductor with an extruded, conductivepolyethylene (see Figure 3-11). This concept isused in underground concentric power cablesas a conductive shield around the ground wires.The polymer contains carbon granules whichdischarge the current. The anode should be

backfilled in carbonaceous coke breeze for maximum life.

 An optional plastic mesh is available, toseparate the anode from the cathode inrestricted spaces, preventing electrical shortingbetween the anode and cathode. Currently thematerial is available in four different diametersand the current output ranges from 3 to 9

milliamperes per linear foot.

Backfill for Impressed Current Anodes

Special carbonaceous backfill is used to

surround most impressed current anodesinstalled in soil in order to reduce the anodebed resistance and extend the anode life. Theonly exception applies to anodes used inphotovoltaic power supply systems, wheremagnesium anode backfill is used due to thehigh back voltage encountered withcarbonaceous backfill.

Coke breeze is conductive and transfers currentfrom the anode to the interface of native soil.Some types pass the current more efficiently bymore electronic conductance and others areless efficient and current passes electrolytically.The first type is metallurgical coke breeze,derived as a waste by-product of coking(heating) coal, associated with steel production.

The composition and particle size of coke maygreatly enhance the life of an anode and shouldbe considered at the design stage. Most oftenthe particle size is about 0.375" (d") and smaller for surface anode bed backfill. The smaller theparticle size, the greater the compaction andconductivity is. Metallurgical coke should notexceed 50 ohm-cm when measured using

 ASTM G-58 Soil Box Test Method, temperature

corrected. The carbon, iron, copper, sulfur content and weight per cubic foot are important

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POROUS ABRASION-RESISTANT

NON-CONDUCTIVE BRAID

STRANDED COPPER

CONDUCTOR

HEAT SHRINKABLE

END CAP

POLYMER GRAPHITE

ANODE MATERIAL

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TABLE 3-9

Coke Breeze Composition

TypeBulk Density

(lb/cu ft)Porosity

(%)Carbon(lb/cu ft)

Metallurgical 45 48.0 32.51

Petroleum, calcined

Delayed 48 59.5 47.76

Fluid 54 56.7 49.93

70 44.0 64.73

74 40.8 68.53

TABLE 3-10

Wire And Cable Insulation Designations

Designation Insulation Thick (in) Cable Size Specification

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tension and promote pumping and compactionin deep anode beds.

WIRE AND CABLE

Conductors typically used for undergroundservice are made of solid or stranded copper,with a variety of insulation materials designedfor the type of electrical and chemical exposureto be encountered (see Table 3-10).

Conductors are rated on their ampacity under 

certain temperature and service conditions (seeTable 3-11). Insulation values also varydepending on wet or dry conditions. Thefollowing data are general in nature, coveringthe most common types, and specification datashould be obtained directly from manufacturer pertaining to their product.

CABLE TO STRUCTURE CONNECTIONS

The most common method of connectingcables to structures is the exothermic weldingprocess.

Exothermic welding uses a graphite mold tocontain a mixture of copper alloy andmagnesium starter powder. After igniting the

powder with a flint gun, the powder becomesmolten and drops on the cable and structure.

The technique of pin brazing is based mainlyupon electric-arc silver soldering using a pinbrazing unit, a hollow brazing pin containing

silver solder and flux.

 A thin layer of silver is transferred from thebrazing pin to between the pipe and the cable.It creates a metallurgical bond between thematerials.

The pin brazing process uses a lower temperature than the exothermic welding

process.

Structures that contain certain types of flammable substances may require the use of grounding clamps to make the cableattachment.

Special attention should be given to coating any

attachment or cable splice to prevent bi-metalliccorrosion attack. The coating should be solventfree to prevent deterioration of the insulation.

CABLE SPLICES

Cables can be spliced together usingexothermic welding, high compression crimps,or split-bolts as shown in Figure 3-13.

SPLICE ENCAPSULATION

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TABLE 3-11

Conductor Ampacities And Resistances

NACE Corrosion Engineer’s Reference Book

Size AWG

 Ampacity*(Copper)

Resistance(Ohms/1000 ft @ 25º C)

No. 16 6 4.18

No. 14 15 2.62

No. 12 20 1.65

No. 10 30 1.04

No. 8 50 0.652

No. 6 65 0.411

No. 4 85 0.258

No.2 115 0.162

No. 1 130 0.129

No. 1/0 150 0.102

No. 2/0 175 0.0811

No. 3/0 200 0.0642

No. 4/0 230 0.0509

250 MCM 255 0 0423

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MOLDHANDLE

MOLD

STARTING POWDER

CADWELD

WELD

SEALING DISK

SLEEVE

(IF REQUIRED)

HOLD MOLD

FIRMLY

AGAINST

CLOSE COVER

AND

IGNITE STARTING

POWDER WITH

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INSULATE SPLICE WITH TWOHALF LAPPED LAYERS OF

RUBBER ELECTRICAL TAPEAND TWO HALF LAPPED LAYERSOF PLASTIC ELECTRICAL TAPE

SELF-ADHERINGFLEXIBLE RUBBER

INSULATING MATERIAL

HEAT SHRINKABLEWRAP SLEEVE

EXOTHERMICWELD CONNECTION

INSULATED STRANDEDCOPPER CABLE

EXOTHERMICALLY WELDED SPLICE

COMPRESSION CONNECTION

COMPRESSION CONNECTOR

2 HALF LAPPED LAYERSOF PLASTIC TAPE

INSULATED STRANDEDCOPPER CABLE

SPLIT BOLT

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electrical rubber insulating tape extending 2inches on adjacent insulation, paying specialattention to the crease area if wrapping a "Y"

connection, as in an anode header cable splice.The entire area is then wrapped with 3 laps of PVC electrical tape and coated with anelectrical sealant to complete the splice.

Epoxy molds (Figure 3-14) have been usedextensively over the years with some mixedresults. Epoxy does not bond to the release oilsused on wire, permitting moisture to travel

eventually into the connection. Since there is nochemical bond to polyethylene, the mold mustextend far enough over the adjacent insulationto prevent hygroscopic moisture migration.

Epoxy molds should not be disturbed or backfilled for 30 minutes at 70º F so that themixture begins to cross link and bonds to the

surfaces. Any movement will distort the materialand reduce the adhesion. During cold weather,this time will be extended to approximately 3hours at 32º F.

Heat shrinkage tubing of irradiated polyethylenewith an effective electrical sealant is used toinsulate in-line cable splices. This method hasproven to be very effective and inexpensive.

Care must be taken when using a propanetorch so as not to melt or distort the cable

1. Transformer-Rectifier 

2. Solar Photovoltaic Cells

3. Thermoelectric Generators

4. Turbine Generator Units

5. Engine Generator Units

6. Wind Powered Generators

Transformer-rectifiers, commonly referred to assimply "rectifiers", are the most frequently usedpower source for impressed current anodesystems. The unit consists of a step downtransformer to reduce alternating current to anacceptable level, and a rectifying element toconvert the alternating current (AC) to directcurrent (DC). Output terminals and a host of 

options and accessories complete the finalassembly of the unit. Figure 3-15 shows atypical rectifier circuit.

Specifying the various options is easilyaccomplished using the following options menu.Selecting them properly requires knowledge.

Options

1. Enclosure Type UtilitySwing Out

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EPOXY MOLD

INSULATINGRESIN

1/4” MIN.1/2” MAX.

FILLINGORIFICE

COMPRESSIONSPLICE

CONNECTOR

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TO AC LINE

LIGHTNING ARRESTERS

CIRCUIT BREAKERS

INPUT

CHANGEOVER

BARS

TRANSFORMER

SECONDARY

TAP CHANGE

CIRCLE

RECTIFIERSTACK

  E X Y Z C

AC

 Y4 Z4 Z1  Z3 Z2

  X3 X1

X4 X2

  X

  Y3 Y1

 Y4 Y2

  Y

  Z3 Z1

Z4 Z2

  Z

X4 X1  X3 X2

460 230 460 230460 230

C C C

B BB

A A A

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 Automatic Potential ControlSolid State Control

 (no taps)IR Drop Free

4. Rectifying Selenium BridgeElement Selenium Center Tap

Silicon BridgeSilicon Center Tap

5. Circuit Type Center Tap, Single

  PhaseBridge, Single PhaseThree Phase WyeThree Phase BridgeMultiple Output Circuit

6. AC Input 115 volts230 volts, single or

3 phase460 volts, single or   3 phase115/230 volts230/460 volts, 3 phase115/460 volts

7. DC Volts Specify maximum DC  output in volts

8 DC Amperes Specify maximum DC

Cabinet LegsCabinet Side Door Slide Out Racks

High Ambient OperationSpecial TapsCoolant - Oil cooled unitsNon-Standard Access  Knockouts

 AC Frequency -other than 60 hz

Elapsed Time Meter Convenience Outlet -

115 volts

JUNCTION BOXES

Junction boxes are an enclosure for terminatingmultiple cables to a common electrical bus bar.

 An anode junction box can be used to connect

multiple anode cables to a common electricalbus bar. The rectifier positive cable is fedthrough a conduit to the main anode bus and aperpendicular bus terminates the lead wires atindividual terminals. Leads may be attached tofixed value current limiting resistors and thecurrent output can be measured by connectinga DC voltmeter across each respective shunt.

 A typical anode junction box is shown in Figure

3-16.

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TO POSITIVE

TERMINAL OF

RECTIFIER POSITIVE

BUS

RESISTOR (TYP.)

SIZE BASED ON

CURRENT REQUIRED

WIRE

SHUNT

(TYP.)

DISTRIBUTION

BOX

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PERMANENTLY INSTALLED REFERENCE

ELECTRODES

There are 3 types of permanently installedreference electrodes that are used for monitoring the potential of a structure or as asensor in conjunction with potentially controlledrectifiers. They are:

High Purity Zinc

Copper/Copper Sulfate Electrode

Silver/Silver Chloride Electrode

If the electrode is to be buried, it must besurrounded with special backfill to increase theion trap area. Zinc is particularly subject to theeffects of polarization and should besurrounded with a 75%/20%/5% mixture of 

prepared backfill to prevent this passivationeffect.

Copper bearing electrodes with a saturatedsulfate solution will become contaminated in thepresence of chlorides and are limited to freshwater and chloride free environments for maximum life.

Silver bearing electrodes with a saturatedchloride solution are used in sea water and

Flange MountRoundSquare

Explosion Proof -Specify Type, ClassCondulet

2. Construction PolycarbonateFlake Filled Polyester Cast IronCast aluminum

 ABS Polymer 

ThermosettingComposite

3. Terminals Specify Number Plated BrassCopper BrassBanana Plugs

Stainless SteelLock Washers

4. Hub Type Slip Fit, sizeThreaded, sizeDouble HubSingle Hub

5. Hub Size Specify size and quantity

6 Post Type Treated wood size

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Waterproof SealSlip FitExposed Terminals

Locking Type

11. Terminal Polyester Laminate - 0.125"Blocks Polycarbonate

12. Options Shorting Bars - specifyquantity, material

Lightning Arresters -specify type

Fixed Current LimitingResistors -specify amperage

Variable Slide WireResistor - specifyamperage

Rotary Rheostat -  specify amperage

Meters - specify type, rangeLocking DevicesShunts - specify amperage

Figure 3-17 shows some typical test stations.

FLANGE ISOLATORS AND DIELECTRIC

UNIONS

To isolate cathodically protected structuresrequires the mechanical insertion of

2. Gasket TypeS Full Face “E” (with bolt holes)S

Ring “F” (without bolt holes)S “D” for RTJ flanges

3. MaterialsS Plain Phenolic - 225º F, max.S Neoprene Faced Phenolic - 175º F, max.S Glass/Phenolic - 350º F, max.S  Aramid Fiber - 450º F, max.S Epoxy/Glass - 350º F

4. Sealing ElementS Nitrile Sealing Element - 250º F, max.S Viton - 350º F, max.S Teflon - 450º F, max.

5. Pressure RatingS  ANSI Class - 150 lbs to 2500 lbs

6. Isolating SleevesS Polyethylene - 180º F, max.S Phenolic - 225º F, max.S Mylar - 300º F, max.S  Acetal - 180º F, max.S Nomex - 450º F

7. Isolating Washers

S Glass/Phenolic - 300º FS High Temp Phenolic - 350º F

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PERMANENTREFERENCEELECTRODE

LOWRESISTIVITYBACKFILLCLOTH

LEAD WIRE

BUSHING

TEST WIRE

PROTECTEDPIPE

CONDUIT, GALVANIZEDSTEEL OR LEXAN

GRADE

WOODENPOLE

GALVANIZEDSTEEL STRAP (TYP.)

POLE MOUNTEDTEST STATION

TERMINALBOARD

FLUSH MOUNTEDTEST STATION

GRADE

TEST WIRE

PROTECTEDPIPE

LEAD WIRE

PERMANENTREFERENCEELECTRODE

LOW RESISTIVITYBACKFILL

CLOTHSACK

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ISOLATING GASKET

CATHODICALLY

PROTECTED

SIDE

ISOLATING WASHER

STEEL WASHER

STEELWASHER

STANDARD

BOLT OR STUD

COAT FLANGES

TO BE BURIED

UNPROTECTED

SIDE

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ISOLATING MATERIAL

(MOLDED NYLON)

NUT

FLANGEDMETAL

BODIES

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distribution service lines, and hydraulic lines.

MONOLITHIC WELD IN ISOLATORS

Monolithic weld in isolators are factoryassembled, one piece, isolating devicesdesigned to eliminate underground isolatingflanges. They eliminate bolts and washerstherefore providing a uniform surface to easilyapply an exterior dielectric coating.

They are available in pipe sizes up to 120

inches diameter in all ANSI pressure ratings.Factory pretested, they assure high dielectricqualities and are available with an internalcoating to reduce bridging of the insulating gapwhen the product carried in a conductive liquid.

CASING ISOLATORS AND END SEALS

Since the mid-1980's, the effects of electricallyshorted casings has received enhancedscrutiny from regulatory agencies. The causeand effect relationship of electrically shortedcasings should be well known to the reader bynow, and the purpose of this section is toacquaint the reader with the types of materialsthat are currently available. Careful selectionand installation of the components during

construction, either new or rehabilitative, willreduce the possibility of a shorted casing.

casing or crossing. The isolator should have aquality coating and be properly designed for theparticular project.

 Another form of casing isolation is anonconductive wax filler, used in conjunctionwith isolating rings, to fill the annular spacebetween the carrier and the casing. If doneproperly, the filler will prevent ground water penetration and condensation from filling theannular space with electrolyte, thus preventingion flow. It will also prevent atmospheric

corrosion from occurring within the casing.

If the casing has been in service, it should beflushed with water to remove debris. The endseals are usually replaced with new seals thatcan accommodate the weight and installationpressures encountered during the fillingprocedure. For new and rehabilitated casings,

the vents are temporarily sealed off and thecasing is pressurized to determine if the filler will be contained.

Complications that may arise are, stitch weldedcasing, perforated casing, out of round casing,improper seals and constricted vent openings.

Casing end seals (Figure 3-20) have

traditionally consisted of rubber boots held inplace with hose clamps, shrink sleeves with

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CASING

ISOLATING

SPACER (TYP.)

PAVEDROADWAY

END SEAL

GRADE

METALLIC VENTPIPE (TYP.)

PIPE

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CHAPTER 4

DYNAMIC STRAY CURRENT ANALYSIS

INTRODUCTION

This chapter will review the causes andcommon means of detecting and mitigatingdynamic stray current effects. Steady state, or static, stray current has been covered inChapter 5 in the Intermediate Course text.

This chapter presents detailed information ondynamic stray currents emanating from directcurrent (DC) sources. While alternating current(AC) may create a potential safety hazard, itseffect on corrosion of ferrous structures is notfully understood. A brief discussion on stray ACappears at the end of this chapter.

STRAY CURRENTS

Stray currents are defined as electrical currentsflowing through electrical paths other than the

chlorine and smelter plants. Telluric, or natural

sources of dynamic stray currents, are causedby disturbances in the earth’s magnetic fielddue to sun spot activity. Telluric effects havenot been shown to contribute to corrosion, butthey do, however, create measurementdifficulties and can interfere with one’s ability toassess cathodic protection systemperformance.

THE EARTH AS A CONDUCTOR

In order to understand the control of straycurrent, one must first understand what thesestray currents are. In underground corrosion,we are dealing with the earth as a hugeelectrolytic medium in which various metallicstructures are buried and often interconnected.

The earth is an electrolyte because of the water contained in the soils. This water causes

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evident that a metallic structure in the earthmay be a far better conductor of electricity thanthe earth itself, even seawater. Resistivities for 

copper and iron are less than 10 x 10

-6

  ohmcentimeters, while that for lead is approximately22 x 10-6  ohm centimeters. It is readilyunderstandable, therefore, that should currentflowing in the earth produce a potentialdifference (voltage gradient) crossed by such ametallic conductor, the conductor will readilyacquire a part of the current that is flowing. SeeFigure 4-1. Thus, pipelines and cables can

become major conductors of stray currents inthe earth environment.

POTENTIAL GRADIENTS IN THE EARTH

How do the stray currents that accumulate onmetallic structures underground get into theearth? As in any electrical circuit, it is

necessary to have potential differencesbetween two points in order to have a currentflow. One also must have an electrical circuit,that is, a source of the current and a return for that current. The magnitudes of current will bedependent upon the electrical potential andelectrical resistance. The amount of currentwhich will flow on any one structure will beinversely proportional to the resistance of the

various parallel electrical paths that join the twopoints of different electrical potential in the

may be indications of strong adverseelectrolytic currents, but in the majority of caseswhere voltage swings are less than 10 millivolts

negligible interference exists.

In practice, if the positive swing does not causea potential less negative than -0.850 volts (IRdrop free), then negligible corrosion can beexpected.

DETECTION OF DYNAMIC STRAY

CURRENTS

The easiest way to keep abreast of possibleinterference problems in an area is throughcontact with Corrosion or ElectrolysisCoordinating Committees. These committeesact as clearinghouses for information onunderground plant locations and knowninterference sources.

Dynamic stray currents are present if thestructure-to-soil potential is continuallyfluctuating while the reference electrode is keptin a stationary position in contact with the soil.See Figure 4-2. These potential changes are adirect result of current changes at the source of the interference due to loading variations. Thiswould also be detected by constantly changing

line current measurements (Figure 4-3).

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-2.00

-1.80

-1.60

-1.40

-1.20

-1.00

-0.80

-0.60

12:00 PM 2:24 PM 4:48 PM 7:12 PM 9:36 PM 12:00 AM 2:24 AM 4:48 AM 7:12 AM 9:36 AM 12:00 PM

   V  g   (   V  o   l   t  s   t  o   C  u

   /   C  u   S   O   4   )

Time

Pipe-to-Soil Potential vs Time

Vg-Min Vg-Ave Vg-Max -0.85 V

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   V

E

gsc

sc

 

4. Trace the current flow along the structureback to its source. This can be done byobserving the current flow at intervals

along the interfered structure by utilizingmillivolt drop test station lead wires, todetermine the direction of the current flow.This technique is illustrated in Figure 4-3.

Let us assume that a situation exists where asingle generating unit is causing interferenceproblems. A voltmeter connection, to be usedfor pipe-to-soil potential (Vgsc) measurements, is

made between the pipeline and a referenceelectrode, somewhere within the earth currentpattern of the generator and its load. Observingthe fluctuating potential readings at this pointalone would not enable one to determine if thereadings are being taken at a point where thepipeline is picking up or discharging current. If measurements are being taken at a point of current pickup, a negative potential swing wouldoccur. A positive swing would indicate adecrease of current flow and a condition of thepipe returning to its steady state condition.Readings observed at a discharge point,swinging in the positive direction would indicatean increase in current leaving the line and anegative swing would indicate a decrease incurrent discharge.

The determination of whether test locations are

indicates, a positive value for Esc occurs whencurrent flows from the stray current source tothe pipeline. Conversely, a negative value of Esc

indicates a flow from the pipeline to the straycurrent source. The slope of a straight linedrawn through the data points is the value of Beta (β):

 As indicated, this type of testing requires that

voltage measurements be taken at two differentlocations. Many readings should be taken at thetwo locations simultaneously. The meters usedat the two locations must be identical or elsecomparison of the two sets of readings will bedifficult.

In most cases, a dual channel recorder such asan X-Y plotter is used or a multi-channel datalogger is used.

Interpreting Beta Curves

Beta curves, which are sloped from the bottomright hand side of the graph to the top left side,would indicate an area of current pick up. Whatthis means is that as the current output of the

source increases, the current pick up by theinterfered structure also increases. An example

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0.0

0.5

1.0

1.5

2.0

2.5

3.0

3.5

4.0

-1.60 -1.40 -1.20 -1.00 -0.80 -0.60 -0.40

     E     S     C

     (     V     O     L     T     S     )

Vgsc1 (VOLTS)

∆Vgsc

∆Esc

∆Vgscβ =

∆Esc

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0.0

0.5

1.0

1.5

2.0

2.5

3.0

3.5

4.0

-1.00 -0.80 -0.60 -0.40 -0.20 0.00 0.20

     E     S     C

     (     V     O     L     T     S     )

V 2 (VOLTS)

∆Vgscβ =

∆Esc

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structure may be picking up stray currents froman additional source or that the suspectedsource is not causing the interference. Plotsdescribing two or more distinct lines wouldindicate the presence of more than oneinterfering current sources. The slopes of theselines will indicate whether currents aredischarging or being picked up according totheir slopes and the polarity of the meter connections.

Determining the Point of Maximum

Exposure

The point of maximum exposure can bedetermined based on the slopes of the plotteddischarge beta curves. The beta curve whichhas the most horizontal (largest) slope indicatesthe location of maximum exposure. Figure 4-7shows this graphically.

In practice, the calculated slopes can be plottedversus distance to indicate clearly the locationof the largest slope (indicative of the mosthorizontal line).

METHODS OF MITIGATING THE EFFECTS

OF DYNAMIC STRAY CURRENT

There are several general methods used toreduce or mitigate the effects of dynamic stray

substations should be spaced at a maximum of about one-mile apart. Modern rail transitsystems use welded rail; this reduces thevoltage drop in the rail, which in turn reducesthe stray current induced in the earth.

Similarly, when dealing with equipment, if isolated electrical positive and negative circuitscan be used, stray current problems will beavoided because the currents never reach theearth. When welding is done, care should betaken to assure that the welding electrode and

the ground are relatively close together and theelectrical path between them is of negligibleresistance. Thus, no voltage drop of anysignificance will exist between them.

Mitigation (Drainage) Bonds and Reverse

Current Switches

Mitigation bonds and reverse current switchesare used to mitigate the effects of stray currentcorrosion on a structure.

The purpose of a mitigation, or drainage bondis to eliminate current flow from a metallicstructure into the electrolyte by providing ametallic return path for such current. Thedrainage bond will allow the stray current to

flow through the structure and back to thesource, through the bond. Figure 4-8 shows the

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current to the interfering structure through thebond.

Before the mitigation bond can be sized, thepoint of maximum exposure must be located.This is done as described earlier under “Determining the Point of Maximum Exposure”.

 As previously indicated, dynamic stray currenttesting requires potential measurements takensimultaneously at two different locations. Thesereadings can be taken by two technicians who

are in communication with each other by radioso that one can tell the other when to take areading. Many readings should be taken at thetwo locations simultaneously. Meters used atthe two locations must have identicalcharacteristics or comparison of the two sets of readings will be difficult.

To facilitate the taking of these potentialreadings, strip chart recorders can be set up atthe two locations. Recordings obtained over a24-hour period will normally provide all the datarequired. The corresponding readings taken atthe two locations can then be plotted on linear graph paper. This plot of points is known as a“beta curve”. Several locations should be testedlongitudinally along the pipeline within the

exposure area. The location of the recorder atthe source remains constant. A separate set of

straight-line plot referred to as the beta curve.The slope of the plotted line will indicatewhether the interfered structure in the area of the test is picking up current, dischargingcurrent or neither.

Once the location of maximum exposure isdetermined and its negative slope or beta curveplotted, the size of the resistance bond can bedetermined. The required size of the resistancebond is such that its installation will cause thebeta curve at the point of maximum exposure to

assume a neutral or pick-up slope. Figure 4-9shows a beta curve at a point of maximumexposure as well as the required mitigationcurve.

Sizing the Mitigation (Drain) Bond

Two methods are available to size the bond,trial and error and mathematical. Both areexplained below.

Trial and Error Method

In relatively simple cases, such as where asingle source of stray current is involved, a trialand error solution may be possible. The size of the resistance bond can be determined by

installing temporary cables and variableresistors and determining when stray current

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0.0

0.5

1.0

1.5

2.0

2.5

3.0

3.5

4.0

-0.80 -0.60 -0.40 -0.20 0.00 0.20 0.40

     E     S     C

     (     V     O     L     T     S     )

V (VOLTS)

∆Vgsc

β =∆Esc

MITIGATION CURVE

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anticipated currents must be known to sizecable and associated electrical equipmentproperly. A mathematical solution can providethe designer with these anticipated values.

This method is based upon the electricalrelationships between the source and thepipeline. The measured potential-to-earth of apipeline is a combination of its natural potential-to-earth plus the sum of all potential changescaused by the DC sources influencing it.

The test set ups for the mathematical methodare shown in Figures 4-10 and 4-11. Figure4-10 explains the test procedure for determiningthe internal resistance (Rint) between thepipeline and the stray current source. Figure 4-11 shows the procedure to determine thechange in pipe to soil potential per ampere of drain current.

The beta curve at the point of maximumexposure, such as the one shown in Figure4-12, is plotted. The equations used in reachingthe solution are as follows:

Equation 1

Vg =   ∆Vgo +  ∆Vgcp +  ∆Vgsc +  ∆Vgb

Where:

In the case of a dynamic stray current:

Equation 2

 ∆Vgsc  = β x  ∆Esc (See Figure 4-4)

Where:

β  =  ∆Vgsc / ∆Esc

If no cathodic protection is present, Equation 1simplifies to Equation 3:

Equation 3

Vg  = Vgo + β +  ∆Esc +  ∆Vgb

For the dynamic stray currents to be mitigated:

Equation 4

β  x  ∆Esc  =  ∆Vgb  (Vg - Vgo must = 0)

From Figure 4-12, the value for Vgo  = 0.570volts and β  (the slope of the plotted points) =0.017.

 ∆Vgb  is the change in potential-to-soil of theinterfered structure caused by a bond current.

The value of  ∆Vgb  can be calculated for anygiven bond current from Equation 5:

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R E xV I

  x E  - Rb sc

g 1

scint

 

  

E I x (R R )

IE

Ri R

I12.0

0.070 0.0294  12.0

0.0994

sc b int b

b

sc

nt b

b

 

Equation 7

I x EV

Ib sc

g

   

 

 

 

  

The resistance of the bond can be calculatedfrom Ohm’s Law:

Equation 8

Esc = Ib x (Rint + Rb)

Or, rearranging:

Equation 9

RE

I  Rb

sc

bint

Substituting:

Equation 10

Or:

The bond resistance value, 0.0294 ohm for thisexample, can be a simple cable or acombination of cable and variable or fixedresistors. The bond must also be sized topermit the maximum current flow and stillremain in the ampacity range for the bond. In adynamic stray current situation, the maximumcurrent can be calculated once the maximumopen circuit voltage between the structures isknown. This value is usually obtained by usinga recording voltage instrument over severaloperating cycles of the stray current source to

measure the peak value. For most stray currentsources the typical cycles is 24 hours.

For example, if the maximum value of opencircuit voltage, Esc, is 12.0 volts, substitution of this value into Equation 8 and rearranging theequation gives the value of the maximum straycurrent through the bond 120.7 amperes asshown below:

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TABLE 4-1

Rint Data - See Figure 4-10

E1 (Volts) I1 (Amperes) Rint (ohms)

On +1.30 36.0

Off -1.15 0

Delta +2.45 36.0 0.068

On +0.80 39.0

Off -1.80 0

Delta +2.60 39.0 0.067

On +0.50 41.0

Off -2.30 0

Delta +2.80 41.0 0 .068

On +2.10 29.0

Off 0.00 0

Delta +2.10 29.0 0.072

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TABLE 4-2

 Vg /I1 Data - See Figure 4-11

Vg (Volts) I1 (Amperes)   Vg /I1 (V/A)

On 0.645 34.0

Off 0.590 0

Delta 0.055 34.0 0.00162

On 0.635 23.0

Off 0.600 0

Delta 0.035 23.0 0.00150

On 0.770 82.0

Off 0.620 0

Delta 0.150 82.0 0.00183

On 0.770 86.0

Off 0.625 0

Delta 0.145 86.0 0.00168

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ground appurtenances to buried equipotentialmats are recommended if the AC pipe-to-soilpotential exceeds 15 volts.

Dynamic AC stray currents may be generatedby AC welding operations, bad grounds inbuildings or AC electrified railroads.

For information on AC mitigation, the reader isreferred to NACE Standard PracticeSP0177-2007 “Mitigation of Alternating Currentand Lightning Effects on Metallic Structures and

Corrosion Control Systems”.2

CONCLUSIONS

Stray current interference on a pipeline cancause severe local corrosion that could lead toa hazardous situation, product leakage andcostly repairs. Therefore, every effort should bemade to avoid interference problems and, if they exist, to mitigate their effects.

Stray currents can be classified as being either static or dynamic. Static interference currentsare defined as those, which maintain a constantamplitude, direction and electrolytic path.Dynamic interference currents are defined asthose, which continually vary in amplitude,

direction and electrolytic path. Staticinterference is always caused by man-made

Stray AC can cause corrosion and be a safetyhazard.

REFERENCES

1. R. A. Gummow, “AC Corrosion – AChallenge to Pipeline Integrity,” MaterialsPerformance, 38, 2 (Feb. 1999)

2. NACE Standard Practice SP0177-2007“Mitigation of Alternating Current andLightning Effects on Metallic Structures and

Corrosion Control Systems”, NACEInternational, Houston, Texas

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CHAPTER 5

DESIGN OF IMPRESSED CURRENT CATHODIC PROTECTION

INTRODUCTION

The objective of this chapter is to providecorrosion control personnel with informationnecessary to design an impressed currentcathodic protection system for undergroundstructures.

This chapter will discuss the variousparameters which must be considered in the

design of an impressed current cathodicprotection system. These parameters includethe following:

1. Protective current requirements

2. Anode bed resistance

3. Anode bed layout

4. Anode life expectancy5 Rectifier sizing

corrosion. The protective current is either developed from within the cell or introduced to

the cell from an external source which is largeenough to overcome the effect of corrosioncurrents being discharged from the anodicareas of the structure. When the surface of thestructure is fully polarized, corrosion of thestructure is controlled. In a sense, the corrosionprocess is not eliminated but merely transferredto an expendable, or sacrificial, material

(anode).

Theory of Operation

The impressed current cathodic protectionsystem utilizes an external power source toprovide a potential difference between theanode(s) and the protected structure. Theanodes are connected to the positive terminal

and the structure to the negative terminal of thepower source Current flows from the anodes

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Application

The impressed current cathodic protectionsystem, in most cases, utilizes a variable power source. Impressed current systems are capableof protecting large structures or structureswhich require greater magnitudes of currentthan can be provided economically by agalvanic anode system. These systems can bedesigned to protect bare (uncoated) structures,poorly coated, or well coated structures. As theamount of surface area to be protected

increases, the total current requirementincreases and impressed current systemsbecome the system of choice.

Advantages and Disadvantages

Impressed current systems can be designed for a variety of applications with a reasonabledegree of flexibility. This is a distinct advantageof this type of system, along with the ability toincrease or decrease the current output, either automatically or manually, by changing theoutput voltage. The disadvantages of thesystem are the increased maintenancerequirements, tendency for higher operatingcosts, and possibility of contributing to straycurrent interference on neighboring structures.

INFORMATION USEFUL FOR DESIGN OF AN

positively indicate the more seriousproblem areas.

4. What is the pipe diameter, wall thicknessand weight per foot? Is there any data onany changes in these items along the routeof the line?

5. What are the location and constructiondetails of all corrosion test points whichhave been installed along the line? If notest points have been installed for 

corrosion test purposes, determinelocations where contact can be made withthe pipeline for test purposes (other thanby driving contact bars down to the pipe).

6. Is the line of all-welded construction or aremechanical couplers used?

7. What are the locations of branch taps?

8. What are the locations of purposelyisolating flanges or couplers, if any, used tosectionalize the line or to isolate itelectrically from other portions of thesystem or from piping of other ownership?

9. Obtain route maps and detail maps giving

as much data as is available.

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does the electric line operate, and whatmethod is used for grounding the towers?(This information is significant becauserectifier installations and isolating joints inwell coated pipelines, closely parallel tohigh-voltage electric lines, may bedamaged by induced AC voltage surgesunder electric system fault conditions if preventive measures are not taken.)

13. Is the line now operated at elevatedtemperatures, or will it be so operated in

the foreseeable future? (High temperaturecould cause deterioration of coatings usedand increase the current requirement toachieve corrosion control.)

14. Is AC power available to provide power tothe rectifier?

DESIGN OF AN IMPRESSED CURRENT

ANODE BED

General

There are several steps to be taken indesigning an impressed current anode bed. Theinitial steps include:

C

Selecting an anode bed site.S l ti d b d t

determination of protective current outputand rectifier size. Usually, the lower theresistivity, the fewer number of anodesrequired to deliver a given current. In manycases, the area of lowest resistivity isconsidered a prime location for an anodebed site.

b. Soil Moisture - Another factor to consider inthe selection of an anode bed site is the soilmoisture at the proposed anode depth. Inmost cases, soil resistivity decreases as the

moisture increases until the soil becomessaturated. When possible, anodes should beinstalled below the water table (assumingthe water resistivity is not too high), or inareas of high moisture content such asswamps, ditches, creek beds, etc.

c. Interference With Foreign Structures  -Structures such as pipelines, undergroundmetallic sheathed electrical cables, or wellcasings, may be subjected to stray currentinterference problems. Therefore, anodebeds should be located away from foreignstructures whenever possible. Local utilitiesshould be contacted to determine if underground structures exist in the area of the proposed anode bed location.

d Power Supply Availability - The selection

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ANODE BED

CATHODIC PROTECTION

GRADIENT FIELD SURROUNDINGPROTECTED STRUCTURE

ANODIC GRADIENTFIELD SURROUNDING

ANODE BED

NEGATIVERETURN CABLE

DIRECTIONOF CURRENTFLOW (TYP.)

RECTIFIER

(+)

(–)

(+)

(+)

(–)

(–)

POSITIVE HEADER CABLE

D d b d ll ff ti h d th) f il li hi h i ti it

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Deep anode beds are usually effective whenhigh surface soil resistivities exist over deeper low-resistivity areas where the anodes areinstalled.

Hybrid Anode Bed

In some cases, on complex structures, differentanode bed types are used in combination toafford complete protection to the pipeline. Anexample may be the case where a remoteanode bed has been used to protect several

miles of a well coated pipeline, but shieldingfrom foreign structures occurs in a localizedarea. In this case, a distributed anode bedmight be considered to supplement theeffectiveness of the remote anode bed. Thiscombination of anode beds is sometimesreferred to as a hybrid approach.

The designer may find himself involved in cases

where site availability is scarce and where thetype of anode bed to be selected is dependenton the sites available. A similar case woulddevelop if the size of the site available isrestricted. These conditions may develop inurban areas or in instances in which the landowner may not wish to sell or lease any land for the installation.

Land limitations may dictate that the installation

depth) surface soil overlies a high resistivitylayer of rock which, in turn, overlies a layer of soil of relatively low resistivity. The currentdischarge from a deep anode bed in this type of 

soil arrangement could extend laterally for considerable distances and work its way upthrough the higher resistivity rock layer to thesurface soil where the structure to be protectedis installed.

In contrast with the above example, the casemay be where the surface resistivity is low and

the underlying soil is of high resistivity. In thiscase, a surface remote or distribution type of anode bed can be effectively utilized and adeep anode bed should not be considered.

In the cases where there are no restrictions tothe type of anode bed to be utilized from any of the parameters listed in the preceding sections,economics would then be the deciding factor.

Tests Required for Anode Bed Design

The design of an impressed current anode bedis normally based on test data acquired in thefield. The basic tests that should be conductedare soil resistivity and current requirement tests.

Soil resistivity tests are conducted along theroute of the pipeline and at the locations

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TABLE 5-1

Typical Soil Resistivity Data

Galvanometer Dial Reading

Multiplier SettingResistance

(Ohms)Spacing (ft) Factor  

Resistivity(Ohm-cm)

2.4 10 24 2.5 191.5 11,490

1.6 10 16 5 191.5 15,320

10.2 1 10.2 10 191.5 19,533

6.2 1 6.2 15 191.5 17,801

2.6 1 2.6 20 191.5 9,958

8.2 0.1 0.82 25 191.5 3,926

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TABLE 5-2

Typical Current Requirements Based On Coating System Effective Resistance

Effective Coating Resistance (1)

(ohm-ft²)

Current Requirement

(Ampere)

Bare Pipe (2) 187.50

10,000 3.73

25,000 1.49

50,000 0.75

100,000 0.37

500,000 0.075

1,000,000 0.0373

5,000,000 0.007

“Perfect Coating” 0.000015

(1) Effective coating resistance, as defined in the above table, of 10,000 to 25,000 ohm-ft² indicates poor application or handling during installation. Resistance of 100,000 to 5,000,000 ohm-ft² indicates good

Lowest “OFF” Potential = -0 523 Volts at amperes and not 2 amperes per anode bed

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V

V  I

I   org

REQ

 A

T1

Lowest Voltage Shift

Required Voltage Shift 

 Applied Current Used

Current Required (I )T1

  0.0470.327

  0.40I

I 2.783 amperesT

T

Lowest OFF Potential = -0.523 Volts atLocation No.2

Potential Shift ( ∆V) at That Location During

Test = -0.047 Volts

Potential Shift Required = -0.850 - (-0.523) =0.327 Volts

Total Current Required can be calculated asfollows:

Substituting the Values:

Step No. 4

The current required for achieving -0.850 voltsthroughout the tested section of the pipe is 3.73amperes.

There are several points that the designer

amperes and not 2 amperes per anode bed.

3. The tests do not take into account futurechanges which might necessitate more

current, such as additional deterioration of the coating.

In cases where the pipeline/structure has notbeen installed, or when current requirementtests are not feasible, current requirements canbe estimated by selecting a current density andapplying that current density to the pipeline

surface area.

There are many different tables that have beenpublished outl ining current densityrequirements. One such table is shown asTable 5-3, and was taken from the NACECORROSION ENGINEER’S REFERENCEBOOK.

 As an example, if a proposed pipeline were tobe coated and buried in relatively neutral (notalkaline nor acidic) but corrosive soil (due tonon-homogeneous conditions), one mightselect 2 ma/ft2  as the appropriate currentdensity to establish the total currentrequirement. If the pipeline was anticipated tohave a 95% coating efficiency, then 2 mA would

be applied to the 5% of the pipeline that wasbare.

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TABLE 5-3

Approximate Current Requirements for Cathodic Protection of Steel

Environment mA/ft²

Sea Water - Cook Inlet 35 - 40

- North Sea 8 - 15

- Persian Gulf 7 - 10

- US - West Coast 7 - 8

- Gulf of Mexico 5 - 6

- Indonesia 5 - 6

Bare Steel in Soil 1 - 3

Poorly Coated Steel in Soil or Water 0.1

Well Coated Steel in Soil or Water 0.003

Very Well Coated Steel in Soil or Water 0.003 or less

d = Pipeline Diameter (ft) 3 Current Required for Protection

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d Pipeline Diameter (ft)

L = Length of Pipeline (ft)

.05 = 5% of Pipe Requiring Protection

(Bare Area)

B = 3.1415

 AS =   B A 2 A 5280 A 2 A 0.05

 AS = 3317.5 ft2

Step No. 2

Calculate the current required based on a 2ma/ft2 current density as follows:

IT = Id x AS

Where:

IT = Total Current Required (Amperes)

Id = Current Density (mA/ft2)

 AS = Total Surface Area (ft2)

IT = (.002)(3317.5)

IT = 6.64 Amperes

Regardless of the method that is used todetermine the current required to achieveprotection, it is wise to consider increasing that

3. Current Required for Protection

4. Shape and Size of Anode

5. Maximum Anode Material Density

6. Life Expectancy

Of the above items, Nos. 1, 2, 4, and 5 areinterdependent. The consumption rate andmaximum allowable density depend on theanode material as do the shape and size of theanodes.

The first step in this phase of the design should,in most instances, be the selection of the anodematerial. Items to be considered for thisselection are environmental conditions,consumption rate, and sizes available.

 Although not a general problem with mostunderground structures, there could be

instances where the anode material could besubjected to acidic or alkaline soil environmentswhich could be detrimental to the anodematerial. Under these conditions, it would bewise to check with the anode manufacturers toinsure that the actual environment will notadversely affect the anode material. Another environmental factor that could affect thematerial selection is whether the anodes will be

installed in soil or water, or a combination of b th

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Calculating the Anode Resistance-to-Earth N = Number of vertical anodes in parallel

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R0.00521

L  ln

8 L

d1V 

 

 

  

   

  

R0.00521

L  ln

4L + 4L S L

dS

S

L

S L

L1H

2 2 2 2 2

 

 

 

 

 

 

 

  

Calculating the Anode Resistance to Earth

The next step in the design process is thecalculation of the resistance-to-earth of the

anodes. There are exceptions to this approach,such as in those cases in which the utility or thecompany has established a preferred range of anode bed resistance. If this is the case, thenthe preferred anode bed resistance becomesthe primary factor in calculating the number of anodes required for the installation.

There are two basic approaches to calculatingthe resistance of an anode bed:

1. By using existing formulas, and

2. By using existing charts.

The anode bed resistance-to-earth can becalculated using one of the following formulas,

as applicable, for the anode bed design:

Single Vertical Anode (H. B. Dwight formula)

Where:

RV = Resistance-to-earth of single verticalanode in ohms

N Number of vertical anodes in parallel

d = Anode diameter in feet

S = Spacing between anodes in feet

Single Horizontal Anode (H. B. Dwight formula)

Where:

RH = Resistance-to-earth, in ohms, of the

horizontal anode

 ρ = Effective soil resistivity in ohm-cm

L = Horizontal anode length in feet

N = Number of vertical anodes in parallel

d = Anode diameter in feet

S = Twice anode depth in feet

NOTE: When using prepackaged anodes or anode backfills (such as coke breeze), thedimensions of the canister or the backfillcolumn must be substituted in the aboveformulas for the anode dimensions.

Using the anode bed/anode resistance-to-earth

formulas listed above can be somewhatcomplicated and time consuming. Therefore,

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5.0

6.0

7.0

8.0

9.0

10.0

   T   A   N   C   E  -   T   O  -   E   A   R   T   H

   I   N

   O   H   M   S R with ρ = 10000 ohm-cm

R with ρ = 8000 ohm-cm

R with ρ = 6000 ohm-cm

R with ρ = 4000 ohm-cm

RESISTANCE-TO-EARTH OF 3" X 60"

ANODES IN A VERTICAL INSTALLATION

IN 8" X 7' COLUMN OF COKE BREEZE.

SPACING = 10 FEET.

ρ = 10000 ohm-cm

ρ = 8000 ohm-cm

2 0

3.0

4.0

A   N

   O   D   E

   B   E   D

   R   E   S   I

ρ = 6000 ohm-cm

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0.5

0.6

0.7

0.8

0.9

1.0

   T   A   N   C   E  -   T   O  -   E   A   R   T   H

   I   N

   O   H   M   S R at 10' Spacing

R at 15' Spacing

R at 20' Spacing

R at 25' Spacing

RESISTANCE-TO-EARTH OF 3" X 60"ANODES IN A VERTICAL INSTALLATIONIN 8" X 7' COLUMN OF COKE BREEZE.

ρ = 1000 OHM-CM.

10' Spacing

15' Spacing

20' Spacing

0 2

0.3

0.4

A   N

   O   D   E

   B   E   D

   R   E   S   I

25' Spacing

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0.5

0.6

0.7

0.8

0.9

1.0

   A   N   C   E

  -   T   O  -   E   A   R   T   H

   I   N

   O   H   M   S R at 10' Spacing

R at 15' Spacing

R at 20' Spacing

R at 25' Spacing

10' Spacing

15' Spacing

20' Spacing

RESISTANCE-TO-EARTH OF 3" X 60"ANODES IN A VERTICAL INSTALLATIONIN 8" X 7' COLUMN OF COKE BREEZE.

ρ = 1000 OHM-CM.

0.3

0.4

A   N   O

   D   E

   B   E   D

   R   E   S   I   S

25' Spacing

five (25) 2" x 60" anodes is to be installed in an Calculating Total Circuit Resistance

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R0.00521

N L  ln

8 L

d1

2 L

Sln 0.656 NV 

 

 

 

 

  

   

  

R0.00521 10000

25 7  ln

8 7

0.6671

2 7

15ln 0.656 25V

 

 

 

 

  

   

( )8" x 7' column of 50 ohm-cm coke breeze. Anodes are connected in parallel at 15'spacings. Soil resistivity is 10,000 ohm-cm.

Method No. 1  -- Using Sunde’s formula tocalculate the anode bed resistance-to-earth:

Substituting the values in the above formula:

 After making all the calculations, the result is:

RV = 1.8 ohms

Method No. 2 -- Using the graph in Figure 5-5to determine the anode bed resistance-to-earth:

Step No. 1:

Locate the number of anodes on the horizontalaxis of the graph (25) and draw a vertical line

up to the curve representing anodes at 15'spacing

g

The total circuit resistance includes thefollowing:

C Resistance-to-earth of the pipeline or structure

C Resistance of the CP system cables

C Resistance-to-earth of the anodes (anodebed resistance)

The resistance-to-earth of the pipeline/structuremay be significant or negligible, depending onlength of pipe and soil resistivity. Using thevalues on Table 5-2 and assuming, for example, that the current requirements listedare necessary to shift the pipe-to-soil potentialapproximately 0.40 volt, then, applying Ohm’sLaw, the resistance-to-earth values for thoseconditions range from 0.0021 ohm (0.40/187.5 -

negligible) to 57.14 ohms (0.40/0.007 - verysignificant). The mid-range current requirement(0.37 ampere) represents a resistance-to-earthvalue of 1.081 ohms (0.40/0.37) which might bea significant percentage of the total circuitresistance.

The last factor to calculate for the circuit

resistance is the resistance of the positive andnegative cables. The first step would be to

RC = Cable resistance The cable resistance (RC) can be calculated

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R

0.00521

N L   ln

8 L

d 1

2 L

S ln 0.656 N

R 3.08 ohms

 ABed

 ABed

 

 

 

 

 

 

 

 

  

C

RS = Pipeline/structure-to-earth resistance

EXAMPLE:

Calculate the total circuit resistance of theconventional anode bed shown in Figure 5-6,using ten (10) 2" x 60" graphite anodes in 8" x7' columns of 50 ohm-cm coke breeze backfill.Soil resistivity is 8,000 ohm-cm. Currentrequired for protection is 15 amperes. The pipeto be protected is 3-mile long, 16-diameter 

carbon steel pipe. Assume a coating resistanceof 500,000 ohm-ft2.

Step No. 1

Calculate R ABed:

Step No. 2

Calculate RC, based on the effective system

cable length and the resistance of the cable per 

( C)using the following formula:

RC = Rcable x Lcable

Where:

Rcable = Resistance per linear foot of cablebased on a standard cable resistancetable such as the one shown in Table5-4. In this example, No.4 AWG cableis being used with a resistance of 

0.2540 ohm per 1,000 ft.

RC  = 383.5 x 0.2540/1000

RC = 0.0974 ohm

Step No. 3

Calculate RS for the 3 miles of coated 16-inch

diameter carbon steel pipe, assuming a coatingresistance of 500,000 ohm-ft2.

RS = R/AWhere:

R = Coating resistance (ohm-ft²) = 500,000ohm-ft²

 A = Surface area of pipe (ft²) = 66,350 ft²R 500 000/66 350 7 53 h

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2” X 60” GRAPHITEANODE (TYP.) INSTALLED

IN 8” X 7’ COLUMNS

OF COKE BREEZE(50 OHM CM)

15 FT.(TYP.)

CATHODICPROTECTION

RECTIFIER

LPOS 1

16 FT.

R(+)

LPOS 2

135 FT.

300 FT.

NO. 4 AWGNEGATIVERETURNCABLE

   (  –   )

ISOLATINGFLANGE (TYP.)

3 MILES

16 INCH DIAMETERCARBON STEEL PIPE

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TABLE 5-4

Concentric Stranded Single Conductor Copper Cable Parameters

Size

AWG

Overall Diameter Not

Including Insulation

(Inches)

Maximum DC

Resistance @

20º C (Ohms/1000 ft)

Maximum Allowable

DC Current Capacity

(Amperes)

14 0.0726 2.5800 15

12 0.0915 1.6200 20

10 0.1160 1.0200 30

8 0.1460 0.6400 45

6 0.1840 0.4030 65

4 0.2320 0.2540 85

3 0.2600 0.2010 100

2 0.2920 0.1590 115

1 0.3320 0.1260 130

1/0 0.3730 0.1000 150

2/0 0.4190 0.0795 175

the previous section, the total circuit deterioration.

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resistance consists of the anode bed-to-soilresistance, the cable resistance and thepipeline (structure)-to-earth resistance.

2. Total Current Required. The total currentrequired to protect the pipeline/structurebased on current requirement tests. Asmentioned earlier, the test results arenormally increased by 20% or more toprovide for future requirement increases.

3. Back Voltage.  The back voltage is thevoltage that exists in opposition to theapplied voltage between the anodes and theprotected structure. Anode bed anodes withcarbonaceous backfill will usually have aback voltage of about 2 volts. In areas of unusual soil composition, the back voltagemay be slightly higher, but, for designpurposes, 2 volts should be used unless

experience in a specific area dictatesotherwise.

Using these three factors, the minimum DCoutput of the power supply can bedetermined/calculated. The required currentoutput of the power supply is equal to the totalcurrent required plus a percentage for later 

deterioration. The DC output voltage can becalculated using the following formula:

IR   = Surface Area of Pipe x Current Density

IR   = 66,350 ft2 x 0.003 mA/ft2

IR   = 0.199 Amp

With 20% spare capacity IR = 0.239 Amp.

Step No. 2

Calculate required power supply voltage usingRT from previous example.

V0 = IR x RT + Vb

V0 = (0.239x10.71) + 2

V0 = 4.56 Volts

The required output rating as calculated is notwhat would be considered a standard off-the-shelf rating. The actual rating of the rectifier unit

purchased should be based, whenever possible, on standard available ratings. In thiscase, the closest rating might be 4 amps and 8volts.

DESIGN OF DISTRIBUTED ANODE BED

The distributed anode bed is installed in closeproximity to the pipeline/structure to be

protected. Distributed anode beds are usedi il h it i d i d t t t li it d

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potential of the earth in the vicinity of at t Th th t ti l i t

pipeline/structure.

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structure. The earth potential swing conceptinvolves having the protected structure interceptthe anodic gradient field surrounding the

distributed anode bed, as shown in the figure.The part of the structure that is within thegradient field of the anode bed is in soil whichis electrically positive with respect to remoteearth. This means that, within the anodicgradient field, the structure is negative withrespect to adjacent earth, even though it maynot be made more negative with respect to

remote earth. Within the anodic gradient field,that part of the structure closest to the anodebed is normally most negative with respect toadjacent earth. Figure 5-9 shows how thegradient from the anode bed influences thepotential of the pipeline-to-earth.

In designing a distributed anode bed, thedesigner considered that each individual anode

created a gradient around itself and that theeffect on the pipeline/structure is additive.Figure 5-10 shows the additive effect of twoadjacent anodes.

 A similar gradient effect is also created by adistributed anode bed that uses a linear anode.

The design of a distributed anode bed is similar to that of the remote anode bed as far as

Deep anode beds are also used when the soilstrata are so arranged that the upper layers of 

soil are of high resistivity with underlying layersof lower resistivity.

 A deep anode bed is usually more expensive tobuild than a conventional anode bed of comparable capacity. In addition, the anodes of a deep anode bed are well below grade leveland are inaccessible for maintenance should

failure occur in the anode material or in theconnecting cables. Although there arereplaceable deep anode bed systems on themarket, it may be more economical to abandona malfunctioning system in place and install anew anode bed close to the original one, rather than to attempt system repairs.

The design procedure for a deep anode bed is,

for all practical purposes, the same as that for a conventional anode bed. The deep anode bedoperates on the same concept as theconventional anode bed, making the protectedpipeline/structure more negative with respect tothe surrounding soil, as illustrated in Figure5-11.

Graphite and high silicon-content cast ironanodes in coke breeze backfill are often used

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However, it should be noted that, whendesigning a deep anode bed the anode bed

Other problems associated with deep anodebeds are:

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R0.00521

L  ln

8 L

d1V 

 

 

  

   

  

designing a deep anode bed, the anode bedresistance-to-earth should be calculated usingthe total length of the backfill column install as

illustrated by the following example:

EXAMPLE:

 A deep anode bed consists of four 2" x 60"high-silicon chromium-bearing cast iron anodeswith a column 40' long of coke breeze backfill inan 8" diameter hole. The effective soil resistivityat anode depth is 10,000 ohm-cm.

The deep anode bed resistance-to-earth can becalculated using H. B. Dwight’s formula for asingle vertical anode as follows:

Where:

RV = Resistance-to-earth of single anode

 ρ = Effective soil resistivity = 10,000ohm-cm

L = Anode length = 40 ft

d = Anode diameter = 0.667 ft

beds are:

1. Cable Insulation - Some types of cable

insulation, such as the HMWPE, areattacked by chlorine gas and ozone.Special insulation, such as Kynar® or Halar®, should be used.

2. The anode-lead connection is a verycritical point of the system, and stepsshould be taken to preclude later problems.

3. As the steel casing consumes, theresistance of the anode bed may increasebecause of the layer of iron oxide thatdevelops.

CONCLUSIONS

Many parameters must be considered when

designing an impressed current cathodicprotection system. As previously discussed,these parameters include the following:

1. Current density required for protection,

2. Life expectancy of installation,

3. Anode bed layout,

4. Anode bed resistance, and

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CHAPTER 6

DESIGN OF GALVANIC ANODE CATHODIC PROTECTION

INTRODUCTION

Galvanic anodes remain an important anduseful means for cathodic protection of pipelines and other buried structures. Theapplication of cathodic protection utilizinggalvanic anodes is nothing more than theintentional creation of a galvanicelectrochemical cell in which two dissimilar metals are electrically connected while buried in

a common electrolyte. In the “dissimilar metal”cell, the metal higher in the electromotive series(or more “active”) becomes anodic to the lessactive metal and is consumed during theelectrochemical reaction. The less active metalreceives cathodic protection at its surface dueto the current flowing through the electrolytefrom the anodic metal. The design of a galvaniccathodic protection system involves

consideration of all factors affecting the proper 

Specific Uses

The following are some specific uses for galvanic anode cathodic protection systems:

1. For protecting structures where a source of DC or AC power is not available.

2. For clearing interferences caused byimpressed current cathodic protection

systems or other DC sources, where theinterferences are not of great magnitudes.

3. For protecting sections of well-coatedpipelines.

4. For providing hot-spot protection on barepipelines where complete cathodicprotection is impractical.

following to determine the most economicalanode material to use:

in the previous chapter for the design of theimpressed current system These approaches

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anode material to use:

1. Required amount of protective current

2. Total weight of each type of anode

3. Anode life calculations

4. Desired life of installation

5. Efficiency of anode types

6. Theoretical consumption rate

7. Driving potential

8. Soil or water resistivity

9. Cost of anode material

10. Shipping costs

11. Degree of skill required for installing thegalvanic anode system

Table 6-1 shows some of these parameters for several anode materials. The order of priority of the above factors will probably change for eachinstallation.

Anode Current Efficiency

 Anode current efficiency is a measure of thepercentage of the total anode current outputwhich is available in a cathodic protection

impressed current system. These approachesare identical for the galvanic anode system.

Electrolyte Resistivity

The selection of the galvanic anode material isprimarily dependent upon the resistivity of thesurrounding electrolyte (soil). As discussed inChapter 3, the low driving potentials of thevarious galvanic anode material alloys limit their economical use to the lower resistivity soils.Zinc anodes are seldom used in soils withresistivity values greater than 1,500 ohm-cm.Magnesium anodes are generally used in soilswith resistivity values between 1,000 and10,000 ohm-cm. Ideally, the galvanic anodebed should be installed in the area of lowestresistivity. Soil resistivity surveys should beconducted as described in Chapter 5 of theBasic Course.

Total Circuit Resistance

Total circuit resistance depends upon thefollowing:

C  Anode bed resistance - Rabed

C Resistance of interconnecting cables - Rckt

C Resistance to earth of the cathode( t t ) R

TABLE 6 1

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TABLE 6-1

Typical Operating Characteristics of Galvanic Anodes

GalvanicAnode Material

Theoretical OutputCharacteristics

(amp-hr/lb)

Actual Output*Characteristics

(amp-hr/lb)

ConsumptionRates

(lb/amp-yr)

CurrentEfficiency

NegativePotential (Volts)

to CuCuSO4

Zinc(MiI-A-18001 U)

370 370 23.7 90% 1.10

Magnesium(H-1 Alloy)

1000 250 - 580 15 - 35 25 - 58% 1.40 - 1.60

Magnesium (High Potential)

1000 450 - 540 16 - 19 45 - 54% 1.70 - 1.80

* Based on shown current efficiencies.

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 Anode bed resistance of a galvanic anodesystem can be calculated using the same

Cathode-to-Earth Resistance (Rcathode)

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R 0.00521N L

  ln 8 Ld

1 2 LS

ln 0.656 Nabed =⋅

⋅⋅

− +⋅

⋅ ⋅⎛ ⎝ ⎜   ⎞

 ⎠⎟

 ρ 

R

0.00521 1500

5.5 6   ln

8 5.5

0.417 1

2 5.5

15 ln 0.656 6abed =

⋅ ⋅

− +

⋅ ⋅

⎛ 

⎝⎜

  ⎞

⎠⎟

system can be calculated using the sameformulas used to determine the resistance of the impressed current anode bed.

Example:

Calculate the resistance of a galvanic anodebed consisting of six prepackaged 60 lb zincanodes (5" x 66" long) spaced 15' apart,center-to-center, average soil resistivity in thearea is 1,500 ohm-cm.

Where:

Rabed = resistance of the total number of vertical anodes in parallel (ohms)

D  = electrolyte resistivity (ohm-cm)

L = length of anode (feet)

d = anode diameter in feet

N = number of anodes in parallel

S = spacing between anodes in feet

The cathode-to-earth resistance is resistancebetween the structure and electrolyte.

On a coated pipeline this resistance can becalculated by first determining the effectivecoating resistance (Rc) (as discussed inChapter 2) and then using the followingformula:

Rcathode = Rc/n

Where:

Rcathode = resistance of pipeline to earth (ohms)

Rc = effective coating resistance - ohmsper average square foot of surfacearea (ohm-ft² )

n = the number of square feet of pipelinesurface area

Example:

 Assuming a 10-mile section of 36" diameter pipe with a coating resistance of 50,000 ohms(Rc) for one average square foot. The pipe-to-earth resistance (Rcathode) can be calculated asfollows:

St N 1

TABLE 6-2

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TABLE 6-2

Resistance of Concentric Stranded Copper Single Conductors

Size AWGMax. DC Resistance

@ 20º C (ohms/1000 ft)

14 2.5800

12 1.6200

10 1.0100

8 0.6400

6 0.4030

4 0.2540

3 0.2010

2 0.1590

1 0.1260

1/0 0.1000

2/0 0.0795

sufficient in itself. An examination of theestimated life of the anodes must be

pound anodes of magnesium and zinc, eachdischarging 0.1 amp. Assume 90% current

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Years LifeTh A E UF

Hr I=

× × ×

×

Years Life0.114 10 0.50 0.85

0.10

  4.8 years=

× × ×

=

Years Life0.0424 10 0.90 0.85

0.10  3.2 years=

× × ×

=

est ated e o t e a odes ust beundertaken in order to determine whether thedesign will provide protection for a reasonable

period of time. The following expression may beused to calculate the estimated life of theanode:

Where:

Th = Theoretical amp-hours/lb

 A = Anode weight (lbs)

E = Current Efficiency expressed as adecimal

UF = Utilization Factor - typically 85 percentexpressed as a decimal (0.85) -- the

point at which the anode should bereplaced even though the anode metalmay not be entirely consumed.

Hr = Hours per year  

I = Current (amps)

The utilization factor accounts for a reduction inoutput as the surface area of the anodedecreases with time, limiting the anode output.

d sc a g g 0 a p ssu e 90% cu e tefficiency for zinc and 50% for magnesium.Each anode is assumed to require replacement

when it is 85% consumed.

Using the above formulas, the life expectancieswork out as follows:

1. For magnesium:

2. For zinc:

The calculated life figures reflect the effect of different rates of consumption of the two metalsas well as the effect of current efficiency.

G A L V A N I C A N O D E D E S I G N

CALCULATIONS

 A well-coated pipe is 36 inches in diameter and2,500 feet long. The average soil resistivity inthe area is 1,000 ohm-cm. The desired system

Step No. 3 W = 117 lbs of magnesium

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R0.00521

N L  ln

8 L

d1

2 L

Sln 0.656 Nabed  =

− +

⋅ ⋅⎛ ⎝ ⎜

  ⎞ ⎠⎟

 ρ 

R0.00521 1000

7 2  ln

8 2

0.6251

2 2

15ln 0.656 7abed   =

− +

⋅ ⋅⎛ ⎝ ⎜

  ⎞ ⎠⎟

Calculate current requirements. The anode bedshould be designed to achieve a satisfactory

amount of polarization. After polarizationgalvanic anodes tend to self-regulate and thecurrent output at the anode bed will declinewhile protection is maintained. As a rule of thumb, the amount of current required topolarize the pipe is four times the amount of current required to maintain protection.

a. Current required to maintain protection(lprotect) on the pipe can be calculated asfollows, assuming a current requirement of 0.003 mA/ft2, typical for a well coated,electrically isolated pipe. This is based on1.5 mA/ft2  of exposed metal and on 0.2%coating damage.

lprotect = 0.003 mA/ft2 x surface area

lprotect = 0.003 mA/ft2 x 23,550 ft2

lprotect = 71 mA = 0.071 Amperes

b. The current required to polarize (Ipolarize) thepipe, by rule of thumb is based on a currentrequirement of 0.012 mA/ft2  (four timescurrent required for protection). This alsoapproximated the current required shouldcoating deteriorate to a total of 0.8%

Based upon the above calculated anodematerial weight requirement, it appears that 7 -

17 lb anodes (4" x 4" x 17"), with backfill outer dimensions of 7.5" x 24", will provide sufficientanode material for the desired life.

Step No. 5

Calculate the anode bed resistance (Rabed) for an anode bank assuming center-to-center anode spacing of 15 feet.

Rabed = 0.99 ohm

Step No. 6

Calculate the cathode to earth resistance(Rcathode) assuming an effective coatingresistance (Rc) of 15,000 ohm-ft2.

Rcathode = Rc/surface area

Rcathode = 15,000 ohm-ft2/23,550 ft2

I Anode Potential Cathode Potential

abed =

Where:

i = current output for magnesium anode in

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IR R R

abed

abed cathode ckt

=

+ +

I 1.55 1.00.99 0.64 0.042

  0.329 Ampereabed =−

+ +

=

The anode bed current output (Iabed) calculatedabove exceeds the previously calculatedcurrent values required to polarize and protectthe structure, therefore the design will beeffective in providing cathodic protection. Oncethe pipe polarizes (usually within a few months),the anode current will drop to the protectivelevel of about 0.071 amperes, thus further extending anode life. Also, using the polarizingcurrent in these calculations allows for coatingdeterioration over time.

Figure 6-2 shows a detail of a typical systemlayout for this design.

Simplified Calculations

From the previous example, we can see that itcan be rather time consuming to calculate thevarious resistive factors required to design agalvanic anode bed, and often certainassumptions must be made that result in anapproximate current output calculation. Theoutput of magnesium and zinc anodes has

im = current output for magnesium anode inmilliamperes

iz = current output for zinc anode inmilliamperes

D  = soil resistivity in ohm-cm

f = anode shape factor from Table 6-3

y = driving voltage factor from Table 6-4

The equations assume a minimum soil

resistivity of 500 ohm-cm and a distancebetween anode and structure of 10 feet. Theequations and factors were developed basedon bare or poorly coated structures. Because of the increased circuit resistance occurring withwell coated structures, the calculated currentvalue should be reduced by 20 percent. Thiscan be done by multiplying i as shown above,by 0.80.

Example

Calculate the number of anodes required toprotect 10,000 feet of well coated, electricallyisolated 16" pipe at a pipe-to-soil potential of 0.85 volts in a soil of 2,500 ohm-cm. Assume acurrent requirement of 1.5 mA/exposed square

foot of metal and coating damage of 1%. Use32 lb k d t d d ll i

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THREADED TERMINAL WITH TWOASA BINDING NUTS (TYP.)

TEST BOX

BUS BAR ORSHUNT

TERMINALBOARD

ANODELEAD WIRE

PIPE LEADWIRES

GRADE

TEST BOX - SEE DETAIL

CREOSOTED POST

CONDUIT STRAP (TYP.)

RIGID CONDUIT

MAGNESIUMANODEPIPELINE

2” MIN18”

C4” BA

TABLE 6-3

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Anode Shape Factors (f)

Anode Weight (lbs) Anode Factor (f)

Standard Anodes

3 (Packaged) 0.53

5 (Packaged) 0.60

9 (Packaged) 0.71

17 (Packaged) 1.00

32 (Packaged) 1.06

50 (Packaged - anode dimension 8" dia x 16") 1.09

50 (Packaged - anode dimension 5" x 5" x 31") 1.29

  Long Anodes

9 2.75" x 2.75" x 26" backfill 6" x 31" 1.01

10 1.50" x 4.50" x 72" backfill 4" x 78" 1.71

18 2.00" x 2.00" x 72" backfill 5" x 78" 1.81

TABLE 6-4

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Driving Voltage Correction Factors (Y)

P/S Standard Magnesium High-Potential Magnesium Zinc

-0.70 1.21 2.14 1.60

-0.80 1.07 1.36 1.20

-0.85 1.00 1.29 1.00

-0.90 0.93 1.21 0.80

-1.00 0.79 1.07 0.40

-1.10 0.64 0.93 --

-1.20 0.50 0.79 --

TABLE 6-5

Multiple Anode Adjustment Factors

Step 3 coating and soil, a greater amount of current isavailable to the pipe closest to the anode. The

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i 120000 f y i 120000 1.06 1.002500

m m=⋅ ⋅ ⇒   =

⋅ ⋅

 ρ 

Numbercurrent requirement

anode output

Number629 mA

50.9 mA / Anode

Number 12.4 or 13 anodes

=

=

=

Calculate the anode current output: (im)

im = 50.9 mA (0.0509 amps)

Step 4

Calculate the number of anodes required:

 Anodes could be spaced evenly along the lineat intervals of 10,000/13 or about every 769feet.

Step 5

Calculate anode life:

attenuation of current is more pronounced ascoating quality decreases, so an individual

galvanic anode protecting a “hot spot” on a barepipe will protect a much smaller area of pipethan that indicated above. For a series of individually connected anodes, the potentialincrease on the pipe that results betweenadjacent anodes, is additive.

 Anodes are commonly connected in parallel inorder to achieve higher current output at agiven location. The approximate current outputof a group of anodes can be calculated bymultiplying the calculated current output of asingle anode by the appropriate adjusting factor indicated in Table 6-5.

Example

The current output (It) of six 32 lb pre-packagedstandard alloy magnesium anodes connected inparallel can be calculated as follows, based ona current output of 50.88 mA for an individualanode. Assume an anode spacing of 10 feet.

It = 50.88 mA x Adjusting Factor (Table 6-5)

It = 50.88 mA x 4.902

It = 249.41 mA

recorded in a permanent log.

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Current measurements will enable the life of theanode to be predicted, and their timely

replacement scheduled accordingly. Additionalanodes should be installed where low potentialswarrant their installation. Damaged facilitiesshould be repaired to ensure that adequatelevels of protection are maintained.

CONCLUSIONS

 As was the case with the design of theimpressed current cathodic protection system,the design of the galvanic anode systemwarrants the consideration of various factors.These factors include the following:

1. Soil resistivity

2. Current Requirements

3. Anode Material Selection

4. Life Expectancy

The resistivity of the soil and the resistance toearth of the structure being protected have agreat impact on design and systemperformance when using galvanic anodes. Thisis due to the fact that the driving potential of thesystem is limited to the natural potential

difference between the anode material and the

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CHAPTER 7

MIC INSPECTION AND TESTING

INTRODUCTION

Microbiologically induced corrosion (MIC) hasbeen actively studied in recent years becauseof its potentially deleterious effect on importantunderground structures, such as pipelines. Themost well known bacteria associated withpipeline corrosion are the sulfate reducingbacteria (SRB). These bacterial are active indeaerated environments often associated with

wet, poorly drained soils (that promote oxygenexclusion), require a nutrient that is near thepipe and often the carbonaceous material of thecoating, and have a sulfurous (rotten eggs)odor associated with the sulfate reductionprocess. If conditions change, they maybecome dormant and another type of bacteriamay become active. Because bacterial live incommunities, there is also a synergistic effect

among them whereby the reaction products of

and steel at coating damage and suspectedMIC areas; sampling the soil, groundwater, or 

pipe-surface products for MIC testing; carryingout the MIC testing using commerciallyavailable field test kits; and visually inspectingthe corroded areas for MIC characteristics.

SITE INSPECTION

Before excavation of the pipeline, the

topography of the surrounding area of the digand the soil type should be noted. Thisinformation is useful in assessing the likelyconditions that can support various types of bacteria. For example, low, wet areas with claysoils collect and hold water, and tend toexclude oxygen to promote deaeratedconditions. Soils with more sand or rock allowwater and/or air to migrate more readily to the

pipe and promote more aerated conditions

seam, if present)

C i d/ th di t ti f

coating against the pH paper for a few secondsand remove, then remove the pH paper. Note

d d th l f th i l ti t

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• Corrosion and/or cathodic protection surfaceproducts present

N Location (see above)

N Type (e.g., deposit, nodule, or films)

N Color (e.g., brown, black, white, or gray)

N Smell (e.g., none, earth, rotten eggs)

• Soil type (e.g., sand, gravel, silt, clay, rock)

• Soil moisture (e.g., wet, dry).

Do not remove any coating or surface productsat this time. Only the person performing thefield test should remove coating or productsfrom the pipe surface at his discretion until

testing is complete.

COATING INSPECTION

Coating inspection for MIC testing purposesshould precede any other type of coatingevaluation planned.

Identify likely area of MIC or other forms of 

corrosion from the visual inspection above

and record the color of the paper in relation tothe chart provided with the paper. Determine

the pH of groundwater away from the pipe inthe ditch if possible for reference. Compare thetwo pH values to determine if the pH near thepipe is elevated. An elevated pH indicates thepresence of cathodic protection currentreaching the pipe. A pH above about 9 wouldbe considered elevated for most soils. It is notuncommon to determine a pH of 12 to 14 for well protected steel.

MIC AND DEPOSIT SAMPLING

Once the pipe is exposed, the soil and anysuspected deposits must be sampled andtested immediately. The coating around thesuspected area of corrosion should be carefullyremoved using a knife or similar instrument.

Sample contamination must be kept to aminimum. Therefore, avoid touching the soil,corrosion product, or film with hands or toolsother than those to be used in sample collectionand provided with the test kits.

MIC SAMPLING AND TESTING

 A minimum of three samples should be

collected and tested Two samples should be

to determine if the bacteria count near the pipeis elevated.

 A test kit that tests for five types of bacteriatests for:

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 Additional samples may be taken and tested

from other locations where bacterial activity issuspected.

Collect the soil, film, or liquid sample followingthe detailed procedures outlined in the test kit.Inoculate the vials at the dig site. Mark the sideof each vial with the appropriate dilutionnumber, as well as the tray next to it, using apermanent marker. Each tray should be markedto identify the following:

• Date and time sample collected• Location where the sample was taken• Location of the dig site.

This same information must be put on theoriginal box in which the sample tray is to be

stored. The box of samples should be stored atambient temperature with the box top closed; itis not necessary to incubate the samples atelevated temperature. All unused test kitsshould be stored in a refrigerator to prolongshelf life.

 After one (1), two (2), and five (5) days, viewthe sample bottles and record the result. Use

the rating number (1 through 5) corresponding

• Sulfate reducing bacterial (BlO-SRB)

• Acid producing bacteria (BlO-APB)• Aerobic bacteria (BlO-AERO)• Iron-related (depositing) bacteria (BlO-IRB)• Low-nutrient bacteria (BlO-LNB).

The presence and viability of these four (or five)types of bacteria are tested in each of the four (or five) colored strings of bottles in each tray.The bottles in each string contain a fast-actingnutrient specific to the bacterium tested. Sometest kits give a quantitative indication of theviability of each bacterium from 10 to 105

bacterium/ml by the serial dilution of the sampleand subsequent growth in each string; other test kits give a quantitative indication from 10 to104 bacterium/ml.

SUPPORTING ANALYSES

Corrosion and other types of deposits on thepipe may be analyzed in the field using the testkit to assist in interpretation of MIC and other corrosion, or cathodic protection products. Thiskit can be used to qualitatively analyze for thepresence of carbonate (CO3

+2), sulfide (S-2),ferrous iron (Fe+2), ferric iron (Fe+3), calcium

(Ca+2) and hydrogen (H+1 pH) ions

other than a carbonate, an oxide for example,may only show the presence of ferric or ferrousi b t ith H th t i i il t th t f th

knife or spatula use to clean the surface or obtain the sample product.

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ion, but with a pH that is similar to that of thereference sample or lower. In addition, cathodic

protection films may not necessarily show thepresence of calcium or carbonate, but will havean elevated pH compared with the referencesample. For most types of soils, the pH isgreater than about nine (9). An elevated pH isnot usually associated with the presence of SRB.

PositiveResult SRB

CorrosionFilm

CorrosionOxide

CPFilm

CO3-2 Yes Yes

S-2 Yes

Fe+2 Yes Yes Yes

Fe+3 Yes Yes

Ca

+2

Yes

pH Elevated

METALLURGICAL INSPECTION

The form of the corrosion pits associated withMIC is reasonably distinctive. These features

can be observed in the field with the unaidedl i

Examine the corroded area newly cleaned first

visually with the unaided eye. Then use a lowpower magnifying lens at 5X to 50X power toexamine the detail of the corrosion pits. MICoften has the following features:

• Large craters up to 2 or 3 inches (5 to 8 cm)in diameter or more

• Cup-type hemispherical pits on the pipe

surface or in the craters

• Sometimes the craters or pits aresurrounded by uncorroded metal

• Striations or contour lines in the pits or craters running parallel to longitudinal pipeaxis (rolling direction)

• Sometimes tunnels can be seen at the endsof the craters also running parallel to thelongitudinal axis of the pipe.

Some examples of these features are shown inother materials. The cupping action of the pitsis a result of the local action of the bacteria.The striations follow the rolling direction of the

steel made into the pipe and are believed to be

MIC OF 304 SS WELDUnder Tubercle Illustrated

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From Little, Wagner,and Mansfeld

TUBERCLE BUILD-UP WITHIRON-RELATED BACTERIA

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Fe-Related Bacteria

 Aerated

Chloride 

Deaerated

Low pH

IRB Create a Differential Oxygen Corrosion Cell with Low pH Environment 

METALLURGICALPope and GRI 

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MICROBIOLOGICAL Aerobic and Anaerobic 

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 Aerobic Require O2 and Nutrient

• Consume O2 and

Produce Organic

 Acids Corrosive toSteel

• Protection

Requirements LessWell Defined

Occur with AnaerobicBacteria

• Form Complex

Communities

Dominated by AcidProducing Bacteria

• MIC a Result of

Microbe Community,Not SRB Alone

MICROBIOLOGICAL COMMUNITY Example APB and SRB

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Organic Nutrients Feed APB

•  APB Products Nutrientsfor SRB

• SRB Fed by Organic

 Acids and Sulfate• Produce more APB and

SRB

• Chlorides with Acids (H+)

Lower pH and CorrodeSteel

 APB

Organic Acids(Lactic, formic, acetic, etc)

SRB Sulfate

 APB APB

SRB

H2S CO2 Acids 

Organic Nutrients

MICROBIOLOGICALSRB Theory (Anaerobic) 

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8H2O

8OH-

+8H+

 • 4Fe4Fe+2+8e-  (A)

• 8H++8e-8H (C)

• SO4-2+8H +Bacteria  

 S-2

+4H2O• Fe+2+S-2FeS (A)

• 3Fe+2+6OH- 3Fe(OH)2 

(A)

• FeS Depolarizes

Need Nutrient – Soil biomass

 – Coating adhesive

• Need No or Low O2

 – Wet soil

 – Low areas

 – Crevices

• More Protection (Current)

Needed to Overcome

Effects

MIC TESTING

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•Field Test Kits for Viable Bacteria – SRB, APB, anaerobic, aerobic, iron related

 – Bacteria count—10 to 105 (104) colonies/ml

•Test Soil or Surface Product

• Create Slurry

• Inoculate Culture Media Vials

• Compare After 2 - 5 Days, 15 Days

TEST KIT INTERPRETATION

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Presence of Bacteria Not Conclusive ofMIC

• SRB Often Do Not Dominate

Not Uncommon to Find All Tested BacteriaPresent

• Interpret Indications with Caution – 1 to 3 bottles  – may have problem

 – 1 to 5 bottles  – possible problem

CULTURE TESTResults

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 Aerobic Bacteria Test

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 APB Bacteria Test

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