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Presentation 2b Whittaker

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Biologically Induced

Corrosion of Zirconium
702 Heat Exchanger
Tubes
Gary Whittaker, PE

Eastman operates a proprietary


process utilizing a glass lined
tank to process an organic stream
containing a small amount of
mineral acid.
The condenser on top of the GLT
has been plagued by corrosion
problems since it was added to
the system many years ago.

GLT Condenser Layout


vapor out
filtered water out
condenser
filtered water in

Vapor out

process in
GLT

heat in
sludge out

History
Process was designed without a
condenser
First condenser was 316L, failed
quickly
Second condenser was alloy
C-276, failed in two years
Current condenser is Zirconium
702, fails in 18 months

Alloy C-276 Tubesheet

Zr 702 Tubesheet

Zr 702 Tubesheet

Eddy Current Results

Window in shell pre-cleaning

Window in shell post-cleaning

Proposed Corrosion Mechanism


1. Low flow rates through the condenser shell
allow biological infestation to occur.
2. Iron oxidizing bacteria present in the biomass oxidize ferrous ion (Fe+2) in the water to
ferric ion (Fe+3), a strong oxidizer.
3. Chloride Ion (Cl-) is attracted to the biomass to maintain charge balance.
4. Chloride ion combined with a strong
oxidizing agent is known to pit zirconium.

River Water Chemistry

Iron 0.03 mg/L


Chloride 9.5 mg/L

Bio Analysis
Samples of the bio-mass were
collected by the plant micro-biologist
Analysis showed the presence of

filamentous bacterium called


sphaerotilus, a well-known
ferrous oxidizer
Identity was confirmed by both a
staining method and genetic analysis

Sphaerotilus collected from the


condenser.

Sphaerotilus from literature

Laboratory Simulation
Bio-mass samples were collected
and placed in a jar with fresh river
water
After several weeks exposure
samples were taken to measure iron
and chloride levels in the bio-mass

Simulation Results
Chloride 1100 ppm
Iron 4000 to 12000 ppm

Zirconium oxide nodules were found


in the pits.
Zirconium chloride complexes are
the primary corrosion product of
ferric chloride pitting
The complexes are hydrolyzed to
zirconium oxide forming nodules

Conclusions
1. Zr 702 performs better than alloy C-276 in this
mix of hot organic and mineral acids.

2. Biological films composed of iron oxidizing


sphaerotilus form on the shell side of the
exchanger.
3. Biologically produced ferric ion combines with
chloride in the river water to produce a strong
pitting environment under the bio-mass.
4. Low flow through the condenser shell promotes
bio-mass formation and pitting of the tubes.

Questions?

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