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8/9/2019 ppchem-05-2011-3
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8/9/2019 ppchem-05-2011-3
2/8263PowerPlant Chemistry 2011, 13(5)
PPCHEM
chemistry. All drum units in the sys-
tem have a mixed metallurgy feed-
water heater system and no con-
densate polishing. The cycle
guidelines are listed in Table 1.
These operating parameters have
served the system well. The peri-
ods between chemical cleanings of
the boilers have averaged ten
years or better over the last 20
years. The cleaning solvents used
are either diammonium or tetra-
ammonium ethylenediaminetetra-
acetic acid (EDTA) depending on
whether the boiler is natural or
forced circulation. No extensive
layup techniques were used on theunits during scheduled or forced
maintenance outages because
outage and down time was kept to
a minimum. Because of chronic
reheater tube failures due to out-
of-service corrosion suffered by all
the units, dry air blower systems
were installed on the reheater sec-
tions on all units. Unit unavailability
from boiler tube leaks averaged approximately 5 %, and a
majority of these failures were from corrosion fatigue.
CHANGING OPERATING CONDITIONS
With the slowdown in the economy, electric generation
needs reduced. In 2009 a majority of the drum units in the
FirstEnergy system were placed on an economic reserve
condition. That is, the units were shut down but needed to
be available within a 72 h timeframe for operational dis-
patch. 72 h were needed because many of the plant staff
were assigned elsewhere in the company (normally to the
Transmission and Distribution Departments) while the
units were not operating. To assure that the units were
ready for operation, boiler or feedwater systems were notdrained. In addition, boiler pressure checks were per-
formed to assure that during the shutdown and subse-
quent cool-down of the unit corrosion fatigue cracks did-
n't occur or could be immediately repaired. After the first
week of unit shutdown and subsequent leak checks, a
nitrogen blanket was applied to the drum.
The requirements of economic reserve along with the
boiler leak checks made cycle protection very difficult to
obtain. Corrosion in a unit cycle is most easily shown by
the 'corrosion triangle' (Figure 1).
Corrosion occurs when all three elements are allowed to
come together, much in the same way as in the firefight-
ers' fire prevention triangle. When any one of the con-
tributing elements is removed from the situation, corrosion
cannot occur. There are two basic ways this may be
accomplished in an electric utility boiler. The first is to dry
out all components. Once water, or moisture, is removed
from the system, corrosion is stopped, hence the reason-
ing for the installation of dry air blowers on the reheat sec-
tions of the boiler. The second option is to remove all the
air, or oxygen, in the system. This is accomplished by
evacuating all the air from an area and replacing it with
nitrogen.
Boiler Parameters
pH 9.1 to 9.6
Specific conductivity [S cm1] 5 to 20
Cation conductivity [S cm
1
] < 10Silica [mg L1] < 0.2 (pressure dependent)
Feedwater Parameters
pH
Specific conductivity [S cm1] 1.6 4.0
Cation conductivity [S cm1] < 0.2
Sodium [g L1] < 3
Dissolved oxygen [g L1]< 20 at the condensate pump discharge
< 5 at the economizer inlet
ORP [mV] 200 350Hot Reheat Steam
Sodium [g L1] < 3
Cation conductivity [S cm1] < 0.2
Table 1:
Cycle chemistry guidelines.
Water Oxygen
Exposed metal
Figure 1:
Corrosion triangle.
An Alternative Chemistry for Both Operational and Layup Protection of High-Pressure Steam-Water Cycles
8/9/2019 ppchem-05-2011-3
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8/9/2019 ppchem-05-2011-3
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An Alternative Chemistry for Both Operational and Layup Protection of High-Pressure Steam-Water Cycles PPCHEM
PowerPlant Chemistry 2011, 13(5) 265
Case History I
The Eastlake #2 unit is a 124 bar, 130 MW forced circula-
tion Combustion Engineering boiler with a GE turbo-gen-
erator located in Eastlake, Ohio, on the shore of Lake Erie.
This unit had spent various amounts of time throughout
2009 in an economic reserve condition ranging from one
week to two months. During the off-line periods the unit
was available at all times to restart. Analyses for iron were
conducted by grab sampling in an effort to understand
when the greatest amount of corrosion was occurring and
if our current efforts in unit layup were satisfactory. This
grab sampling and iron analysis was also conducted on
the other units with similar results. Sampling was con-
ducted at the condensate pump discharge, low-pressure
(LP) heater outlet (deaerator inlet), economizer inlet, boiler,
and hot reheat. Figures 68 show the typical iron results
that were observed.
EPRI best practice for iron corrosion transport [3] is
2 g L1 maximum at the economizer inlet. At steady
state loads, the Eastlake units were able to maintain below
5 g L1 maintaining the guideline limits given in Table 1.
Iron corrosion throughout the cycle was at its maximum
during transient load and startup conditions. More trou-
bling were the iron concentrations at the hot reheat point.
Dry air had been used on this section for the last several
years when the unit came off line. Although
there were no large spikes in iron as seen on
the feedwater section, it was obvious therewas corrosion in the hot reheat.
Anodamine was injected into the conden-
sate pump discharge of the Eastlake #2 unit
on March 30, 2010. The injection rate was set
for approximately 350 g L1 and as pre-
dicted cycle cation conductivity increased.
Within 24 hours the amine formulation was
throughout the cycle and all chemistry control
parameters were being met and maintained
with the exception of the cycle cation conduc-
tivity. The cycle cation conductivity had
increased by 0.17 S cm1 from the back-
ground normal 0.18 S cm1 to approximately
H O2
Cathode
(O being the most common)2
Anode (Fe)
2H O + 2e2
2OH + H2
Fe 2+Fe + 2e Fe O2 3 Fe O3 4, (FeO Fe O ) 2 33+Hematite, Fe 2+Magnetite, Fe
Figure 5:
Protection triangle.
350
300
250
200
150
100
50
0
1
TotalIron
[g
kg
]
Unit off line
Sampled during
load increase
Startup
Condensate pump discharge
LP heater outlet
Economizer inlet
Sampled during
load increase
Time [d]
1 2 3 4 5 6 7
Figure 6:
Feedwater iron analyses.
140
120
100
80
60
40
20
0
1
TotalIron
[g
kg
]
Unit off line
Time [d]
1 2 3 4 5 6 7
Figure 7:
Boiler iron analyses.
80
60
40
20
0
1
TotalIron
[g
kg
]
Unit off line
Time [d]
1 2 3 4 5 6 7
Figure 8:
Hot reheat iron analyses.
8/9/2019 ppchem-05-2011-3
5/8266 PowerPlant Chemistry 2011, 13(5)
PPCHEM An Alternative Chemistry for Both Operational and Layup Protection of High-Pressure Steam-Water Cycles
0.35 S cm1. The unit was scheduled for a
shutdown over the weekend two days later,
which gave an excellent chance to determine if
corrosion rates had been reduced during this
short injection period. Sampling commenced
immediately after the unit was placed back inservice with amine injection. The unit was
again taken off line because of a tube failure.
Amine injection continued at a rate of approxi-
mately 350 g L1. The results of the grab
sampling are shown in Figure 9.
The addition of the proprietary amine formula-
tion to Eastlake #2 continued until November
30, 2010. Transient and startup iron corrosion
analyses continued; long-term results are
shown in Figure 10. Analyses of organics were
also made during this period with the resultsgiven in Table 2. As expected, the organic acid
levels throughout the cycle had increased,
accounting for the increase in the cycle cation
conductivities.
All iron data was averaged to determine the
numerical reduction in iron transport and is
shown in Table 3. These averages are derived
from grab sampling; the majority of the sam-
ples were taken during transient loading con-
ditions.
Iron results given in the graphs and tables are
total iron concentrations, that is, the combina-
tion of Fe2+ and Fe3+ analyzed by way of the
ferrozine method. While reductions in total
iron are seen in the data, it is very interesting
to note these reductions include significantly
lower Fe2+ ( 2 g L1) and copper oxides
(highest 1 g L1). A direct reaction occurs
between iron and reducing water to form solu-
ble species and hydroxides. When iron cor-
rodes in an aqueous solution, both oxidation
and reduction occur at the anode and cathode
respectively. At the anode, an oxidationprocess occurs [6]:
Fe Fe2+ + 2e (1)
2H2O + 2e 2OH + H2 (2)
Reduction of Fe2+ concentrations is seen as the metal sur-
face (anode) is protected by the filming amine. Validation
of this protection was also demonstrated on Eastlake #2
when the amine feed was interrupted for a one-week
period several months into the testing period, resulting in
both corrosion product oxides once again increasing out
of specification (iron increased to 15 g L1 and copper to
11 g L1). Note that during the Anodamine chemical
injection period and once again after reinstallation of
dosage following the interruption in feed, during base load
and during transient load situations both copper and iron
were measured as equal to and/or lower than control lim-
its (iron) or below detectable limits (copper).
With any proposed change in operation, management
needs to understand immediate pay back. Listing num-
bers and showing graphs may not generate interest if real
dollar savings are not shown. Unfortunately, reductions in
corrosion transport may not correlate directly to reduc-
tions in corrosion fatigue failures for quite some time.
Pitting damage from past corrosive conditions remains
within the tubes and residual stresses will continue to
cause cracking [7]. Savings can be found elsewhere.
200
180
160
140
120
100
80
60
40
20
0
1
TotalIron
[g
kg
]
Date [mm/dd/yyyy]
03/31/2010
04/02/2010
04/04/2010
04/06/2010
04/08/2010
04/10/2010
04/12/2010
04/14/2010
04/16/2010
04/18/2010
04/20/2010
04/22/2010
04/24/2010
04/26/2010
Off-reserve Off-FO
LP heater discharge
Hotwell pump discharge
Economizer inlet
Boiler
Hot reheat
Morning ramp-upRamp-up in load
(startup)
Figure 9:Subsequent startups and transient load sampling after addition of proprietary
amine formulation.
FO forced outage
350
300
250
200
150
100
50
0
1
T
otalIron
[g
kg
]
Condensate pump discharge
LP heater outlet
Economizer inlet
Date [mm/dd/yyyy]
02/17/2010
02/24/2010
03/03/2010
03/10/2010
03/17/2010
03/24/2010
03/31/2010
04/07/2010
04/14/2010
04/21/2010
04/28/2010
05/05/2010
05/12/2010
05/19/2010
05/26/2010
06/02/2010
06/09/2010
06/16/2010
06/23/2010
06/30/2010
Anodamine injection
Normalchemistry
parameters
Figure 10:
Results of iron sampling before and after addition of proprietary amine
formulation.
8/9/2019 ppchem-05-2011-3
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PPCHEMAn Alternative Chemistry for Both Operational and Layup Protection of High-Pressure Steam-Water Cycles
Assuming that corrosion product oxide release and trans-
port from the economizer inlet are responsible for all the
deposit buildup within the boiler, the approximate
34 g L1 iron calculates to 95 kg of iron being trans-
ported to the boiler. A chemical cleaning on this particular
unit occurs approximately every ten years with 950 kg of
iron (Fe3O4) removed. Hence, the iron corrosion product
oxide transport rate measured at the economizer is very
closely verified by previous chemical cleaning history on
the boiler. Using the averaged iron maximum corrosion
product rate of 6.7 g L1 now measured, this equates to
18 kg iron transported. Using the same cleaning criteria of
approximately 950 kg removed, a chemical cleaning
would be required every 50 years for this particular boiler.
I leave it to the reader to calculate the money and
improved availability/generation saved from reducing out-
age, in addition to the time, costs and environmental limi-
tations required to complete necessary boiler cleanings.
Case History II
Anodamine has been used on four other drum units as a
preservation method when the unit is taken off line.
Approximately 72 hours before a known unit shutdown,the amine is injected at a rate of approximately 300
500 g L1 and applied until the
unit is removed from service. As
with the Eastlake #2 experience, all
unit cycle cation conductivities
increased from approximately 0.2
to 0.4 S cm1. Initial injectionsvaried in success however. Several
of the units' cycle cation conduc-
tivity values increased dramatically
to nearly 1.0 S cm1 even though
amine injection rates were kept at
300 g L1. Unfortunately no sam-
ples were obtained during these
high cation conductivity periods. In
subsequent injections of the
amine, however, the cation con-
ductivity values did not increase to
the originally seen high values(~ 1.0 S cm1). This phenomenon
seems to depend upon the boiler cleanliness and last
chemical cleaning. 'Clean' unit boilers do not see unusu-
ally high cation conductivities (an approximately
0.2 S cm1 increase over ambient values due to organic
acid production). 'Dirty' boilers, or those with higher mag-
netite deposition loading, seem to experience a higher
cycle cation conductivity increase (an approximately 0.4
to 1.0 S cm1 increase) for several days. After the initial
amine injection and several days of operation with the
chemical, the cycle cation conductivity values decrease to
the approximate 0.2 S cm1increase over ambient val-
ues. Acetate levels in all units are comparable to those
listed in Table 2. Figures 11 and 12 show visual inspec-
tions of the condenser and a superheater tube during a
unit outage. Similar results were found after the unit was
idle for two months. Notice the hydrophobic characteris-
tics and that the water droplets do not touch the metal
surfaces.
Case History III
FirstEnergy management was concerned about the
increased cycle cation conductivities and acetate concen-
tration levels. These measurements were clearly outsiderecommended turbine manufacturers guidelines [3,9,10].
Before Anodamine Use Anodamine Injection
Feedwater and steam BDL 40 60 g L1 acetate
Boiler BDL 0.2 0.3 mg L1 acetate
Table 2:Average boiler and cycle acetate concentrations. Detection limit = 0.03 mg L1.
BDL below the detection limit
Condensate LP Heater Econ Boiler Hot
Pump Out Inlet Reheat
Previous chemistry 21.8 47.9 34.4 23.8 17.5
Anodamine use 8.5 7.9 6.7 9.9 7.4
Table 3:
Total average iron corrosion levels before and after amine use. All data is stated in g L1 Fe.
Figure 11:
Condenser
door.
Figure 12:
Superheater
tube.
8/9/2019 ppchem-05-2011-3
7/8268 PowerPlant Chemistry 2011, 13(5)
PPCHEM An Alternative Chemistry for Both Operational and Layup Protection of High-Pressure Steam-Water Cycles
The supplier R & D proposed a
newly developed formulation,
Anodamine HPFG, a fully water-
soluble, non-toxic, cyclohexyl-
amine-free thermally stable amine
formulation designed to continueexisting levels of metal protection
throughout the entire steam-water
cycle but to effectively eliminate
cation conductivity increases.
On November 30, 2010 the
Anodamine HPFG solution was
introduced into the Eastlake #2
and #3 condensate pump dis-
charges. As discussed, unit #2 had
been on a constant feed of the
original formulation while the #3unit had been subjected to injec-
tions only 72 hours before a
scheduled unit shutdown. After an
initial increase in the cycle cation
conductivity on Eastlake #3, the
cycle cation conductivity de-
creased during steady amine injec-
tion until the unit was taken off line
for a scheduled economic reserve
off (see Figure 13). Eastlake #2 has
been injected continually with the
new amine formulation to date at a
rate of 300350 g L1. Econo-
mizer inlet cation conductivity data
for that unit is given in Figure 14.
Increases in the economizer inlet
cation conductivity are normally
seen during a drop in unit load
(feedwater flow) or during a unit
startup. Analysis of the cycle
waters revealed organic acids,
acetate, etc. to be BDL (below
detection limits). Inspections of the
condenser have given the same
positive visual evidence of metalhydrophobic characteristics and water beading as with
the previous amine formulation as discussed and shown
under case history II (see Figure 11).
CONCLUSION AND FURTHER STUDY
Apart from the ever important cycle treatment require-
ments of ongoing system protection, stability of oxides,
lowering of iron transport, preventing or limiting of FAC,
and protection of both ferrous and admiralty alloys in
mixed metallurgy systems, there is also a simultaneous
occurrence of moisture and oxygen during unit off condi-
tions causing corrosion within the cycle. Traditional miti-
gation strategies include dry layup of the system, which
requires the use of nitrogen. Capital investment of bulk
storage and piping systems needs to be undertaken to
adequately protect the cycle if this path is chosen [11,12].
In addition, the safety aspects of using nitrogen should
never be minimized and include asphyxiation (> 18 % oxy-
gen is fatal), compressed gas dangers, and freeze poten-
tial. The other traditional option is wet layup. This option
includes increasing the feedwater ORP with a reducing
chemical [11] (hydrazine) in mixed metallurgy feedwater
heater systems, which can lead to FAC. Wet layup also
requires capital investment of deoxygenation equipment
or, at the very least, techniques to deoxygenate makeup
water to the unit as the recommended guidance for dis-
0.50
0.45
0.40
0.35
0.30
0.25
0.20
0.15
0.10
1
Conductivity[S
cm
]
11/30/2010,
09:00
11/30/2010,
12:00
11/30/2010,
15:00
11/30/2010,
18:00
11/30/2010,
21:00
12/01/2010,
00:00
12/01/2010,
03:00
12/01/2010,
06:00
12/01/2010,
09:00
12/01/2010,
12:00
12/01/2010,
15:00
12/01/2010,
18:00
12/01/2010,
21:00
Unit off line
Injection of Anodamine HPFG
Date [mm/dd/yyyy, h:min]
Figure 13:
Eastlake #3 economizer inlet cation conductivity during injection of the new amine
formulation.
1
Cond
uctivity[S
cm
]
11/30/2010
12/02/2010
12/05/2010
12/12/2010
12/19/2010
12/26/2010
01/02/2011
01/09/2011
01/16/2011
01/23/2011
01/30/2011
02/02/2011
02/04/2011
02/06/2011
02/13/2011
02/20/2011
Unit off line
Injection of Anodamine HPFG
Injection of Anodamine HPFG
Unit off
Unit off
Date [mm/dd/yyyy]
0.50
0.45
0.40
0.35
0.30
0.25
0.20
0.15
0.10
Figure 14:
Eastlake #2 economizer inlet cation conductivity during Anodamine HPFG injection.
8/9/2019 ppchem-05-2011-3
8/8269PowerPlant Chemistry 2011, 13(5)
PPCHEMAn Alternative Chemistry for Both Operational and Layup Protection of High-Pressure Steam-Water Cycles
solved oxygen in the boiler is < 100 g L1 before firing
[11]. In addition, the feedwater system piping and other
susceptible piping throughout the cycle is prone to FAC if
all chemistry conditions are not at optimal levels. These
non-optimal conditions also occur during normal unit
operation.
The use of filming amine technology to protect out-of-ser-
vice metal surfaces would eliminate the use of nitrogen
and other traditional deoxygenation techniques for metal
protection along with the costs and safety concerns asso-
ciated with it. Utility equipment would be ready for imme-
diate operation while also being protected from corrosive
conditions. An excellent balance of unit protection and
unit availability would be achieved. A one-year monitoring
period that included continuous operation with a film-
forming amine, Anodamine, along with use for layup
protection in multiple units has shown that this type ofchemical control program can protect both iron and cop-
per systems even when exposed to oxidizing all-volatile
treatment and ammonia cycle conditions. Testing of this
program also indicates a significant reduction in Fe2+, an
indication of protection against FAC. Introduction of the
filming amine chemistry in all units did not cause corrosion
product increases or any other unwanted side affects.
Recent positive testing of the water-soluble Anodamine
HPFG product showed thermal stability throughout the
entire steam-water cycle. This grade was able to keep
cycle cation conductivity values equal to previous condi-
tions, below and in compliance with turbine manufacturer
guidelines of 0.2 S cm1 (not degassed cation conduc-
tivity) and showed no appreciable levels of organic degra-
dation products like carbon dioxide, acetate/formate, etc.
FirstEnergy has entered into a tailored collaboration (TC)
project with EPRI and several other U.S. utilities to further
test the use of this proprietary amine formulation and its
effectiveness for cycle preservation.
REFERENCES
[1] Interim Consensus Guidelines on Fossil Plant Cycle
Chemistry, 1986. Electric Power Research Institute,
Palo Alto, CA, U.S.A., CS-4629.
[2] Cycle Chemistry Guidelines for Fossil Plants: Phos-
phate Treatment for Drum Units, 1994. Electric
Power Research Institute, Palo Alto, CA, U.S.A., TR-
103665.
[3] Cycle Chemistry Guidelines for Fossil Plants: Phos-
phate Continuum & Caustic Treatment, 2004. Electric
Power Research Institute, Palo Alto, CA, U.S.A.,
1004188.
[4] Deoxygenation in Cycling Fossil Plants, 1992. Elec-
tric Power Research Institute, Palo Alto, CA, U.S.A.,
TR-100181.
[5] Flow-Accelerated Corrosion in Power Plants, 1998.
Electric Power Research Institute, Palo Alto, CA,
U.S.A., TR-106611-R1.
[6] Guidelines for Controlling Flow-Accelerated Corro-
sion in Fossil and Combined Cycle Plants, 2005.
Electric Power Research Institute, Palo Alto, CA,U.S.A., 1008082.
[7] Verib, G. J., Conversion of a Drum Boiler from
Phosphate to Caustic Treatment. Eighth International
Conference on Cycle Chemistry, 2006, Calgary,
Canada.
[8] Dooley, B., McNaughton, W., Boiler Tube Failures:
Theory and Practice Volume 2: Water-Touched
Tubes, 2007. Electric Power Research Institute, Palo
Alto, CA, U.S.A., 1012757.
[9] Steam Purity Requirements for Turbine Operation,
Alstom Power, HTGD 90 486 V0001F.
[10] Steam Purity Recommendations for Utility Steam
Turbines, 2004. General Electric Company, GEK
72281c.
[11] Cycling, Startup, Shutdown, and Layup Fossil Plant
Cycle Chemistry Guidelines for Operators and
Chemists, 2009. Electric Power Research Institute,
Palo Alto, CA, U.S.A., 1015657.
[12] Cycle Chemistry Guidelines for Startup, Shutdown,
and Layup of Combined Cycle Units with Heat
Recovery Steam Generators, 2009. Electric Power
Research Institute, Palo Alto, CA, U.S.A., 1015657.
THE AUTHOR
George J. Verib (B.E., Chemical Engineering, Cleveland
State University, Cleveland, OH, U.S.A.) is the cycle chem-
istry consultant at the FirstEnergy Corp. He has held vari-
ous positions in fossil-fired plant laboratories and corpo-
rate laboratories for over 32 years and now serves as the
company water quality consultant. George Verib has
authored 15 papers on various aspects of makeup water
production, condensate polishing, and boiler water treat-
ment. He is a registered professional engineer in Ohio
(U.S.A.) and a recipient of the EPRI Innovators Award for
oxygenated water treatment in once-through boilers and
of the Technical Transfer Award for caustic treatment
chemistry in subcritical drum boilers.
CONTACT
George J. Verib
76 South Main Street
Akron, Ohio 44308
U.S.A.
E-mail: [email protected]