BWR environments) in which it is assumed [1] that the slip dissolution model is a
reasonable working hypothesis for the crack propagation mechanism. This baseline
prediction methodology is then extended to treat the effects of irradiation on the
cracking of stainless steel. Further extension to other alloys (e.g., nickel-base,
low-alloy steels) and environments (PWR) is also outlined.
The starting point in this process is the theory and quantitative elements in
Eq. (5). To develop this concept to a state of practical usefulness, it is necessary to
redefine this fundamental equation in terms of measurable engineering or operational
parameters. This involves (a) defining the crack tip alloy-environment composition
in terms of, e.g., bulk alloy composition, anionic concentration or solution
conductivity, dissolved oxygen content or corrosion potential, etc.; (b) measuring the
reaction rates for the crack tip alloy-environment system that corresponds to the
“engineering” system; and (c) defining the crack tip strain rate in terms of continuum
parameters such as stress, stress intensity and loading frequency. Extensive work has
been conducted in these areas, and the progress will be reviewed only briefly in this
chapter before illustrating how these advances have been incorporated into verified,
quantitative life prediction methodologies.
Definition of Crack Tip Alloy-Environment System
On the basis of direct measurements on stainless steel, alloy 600, and low-alloy
steel-water systems at 288°C, it is known that the electrode potential and pH
conditions at the tip of a crevice or crack can differ markedly from those at the
exposed crevice or crack mouth [1,70–74]. These variations are understood and have
been extensively reviewed [45,75–77] in terms of the thermodynamics of various
metal oxidation and metal cation hydrolysis reactions and how they are influenced by
the reduction processes of e.g., dissolved oxygen at the crack mouth. From a
practical viewpoint, the corrosion potential which exists at the deaerated crack tip is
controlled primarily by pH, but it can be defined [1] in terms of the measurable
dissolved oxygen content in the external water environment (Fig. 9) (or preferably
by the measurable corrosion potential of the external system) and the purity of the
external water.
The transient and steady-state concentrations of anions in the crack have also
been experimentally measured and analytically modeled [1,70,78]. The anion level
present at the crack tip is directly dependent on the external anionic activity, the
dissolvable metallurgical impurities (e.g., MnS) level, the corrosion potential
difference between the crack mouth and tip, and convective influences. For example,
the steady-state sulfur anion concentration at the crack tip in low-alloy steels can be
defined by the MnS content, aspect ratio, and orientation; the solution flow rate; and
the oxygen concentration in the water [1,79,80]. Under specific conditions the
dissolved sulfur concentration can be of the order of 3 ppm versus <10 ppb in the bulk
solution. For stainless steel exposed under normal BWR conditions, the potential
drop down the crack length leads to a concentration of anions at the crack tip such
that typical crack tip anion concentrations between 0.1 and 1.0 ppm are expected;
under deaerated operating conditions, where no potential drop exists along the crack
length, the (non-OH
–
) anion content at the crack tip will approximate that in the
bulk environment (e.g., ≈15ppb). To maintain electroneutrality in the crack
enclave, it is necessary that there be a corresponding concentration of cations at the
Corrosion in Nuclear Systems 617
Copyright © 2002 Marcel Dekker, Inc.