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<strong>atw</strong> Vol. 62 (<strong>2017</strong>) | Issue 8/9 ı August/September<br />
DECOMMISSIONING AND WASTE MANAGEMENT 546<br />
Steel<br />
St 12<br />
# 1.0330<br />
GGG 40.3<br />
# 0.7043<br />
Canister materials for wastes<br />
with negligible heat production<br />
Experiments with fine-grained steel<br />
(material number 1.0566) were performed<br />
under anaerobic conditions at<br />
35 °C in solution 1 and 2 (see Tab. 2).<br />
Measured mass losses and corrosion<br />
rates are shown as function of time.<br />
Figure 9 shows significant scatter<br />
of the corrosion rates in both brines.<br />
Especially one of the parallel samples<br />
in MgCl 2 -rich solution at the time step<br />
of 548 days showed by a factor of 2<br />
higher corrosion rate in comparison to<br />
the other samples. The sample did not<br />
show local corrosion phenomena such<br />
as pitting corrosion, however, the<br />
Corrosion<br />
medium<br />
| | Fig. 6.<br />
Mass loss of steel 1.0566 in MgCl 2 -solution depending on S/V ratio at<br />
150 °C.<br />
| | Fig. 8.<br />
XRD pattern of corrosion products of steel 1.0566 in NaCl (top) and MgCl 2<br />
solution (middle) at 90 °C.<br />
Exposure<br />
time<br />
days<br />
corrosion attack produced shallow<br />
pits. The distribution of these shallow<br />
pits explains the scatter of data. As<br />
mentioned above, the corrosion rate<br />
was independent of the solution.<br />
Untreated plane samples of St 12<br />
(material no. 1.0330) [7] and nodular<br />
cast steel GGG 40.3 [15] were investigated<br />
under dry interim storage<br />
conditions (aerobic conditions). The<br />
steels showed uniform corrosion rates<br />
but also localized corrosion processes<br />
(pitting). The general corrosion rate<br />
was determined to about 10 µm/yr.<br />
This rate decreased with increasing<br />
time as well as pitting corrosion. Under<br />
conditions in ventilated galleries<br />
General<br />
corrosion rate<br />
µm/a<br />
| | Tab. 3.<br />
Corrosion phenomena of untreated plane samples of St 12 (material no. 1.0330) and nodular cast steel (material no. 07043) under<br />
aerobic conditions (iron ore mine Konrad) [7].<br />
| | Fig. 7.<br />
General corrosion rate of nodular cast steel GGG40.3 at 150 °C as function<br />
of time.<br />
| | Fig. 9.<br />
General corrosion rates of fine-grained steel 1.0566 as function of time in<br />
MgCl 2 -rich p and NaCl solution s at 35 °C.<br />
Maximum<br />
penetration depth<br />
µm<br />
Konrad 1250 m level @ 45 °C 133 21.2 280<br />
covered by iron ore 378 305.0 740<br />
Konrad water 121 18.0 120<br />
@ 50 °C 381 23.5 130<br />
Konrad 1250 m level @ 45 °C 90 650 1600<br />
covered by iron ore 180 460 1700<br />
365 430 1200<br />
Konrad water 90 250 -<br />
@ 50 °C 180 260 200<br />
365 270 100<br />
in the iron ore mine Konrad, corrosion<br />
rates of < 100 µm/yr. were observed.<br />
The measurements were performed<br />
by contacting the steel samples with<br />
crushed iron ore implying definite<br />
water contents. For the conditions of<br />
the iron ore mine, higher uniform<br />
corrosion rates up to about<br />
600 µm/yr. as well as pitting corrosion<br />
rates of 1.7 mm/yr. were measured.<br />
These tests were made in the closed<br />
gallery with a relative humidity of<br />
80 % at 42 °C on the -1,250 m level of<br />
the Konrad Mine. The results of the<br />
tests are summarized in Table 3.<br />
Summary and conclusions<br />
During the period between 1980 and<br />
2004, a huge number of corrosion<br />
tests were performed at KIT-INE. The<br />
database contains more than 5,600<br />
datasets for metals. Due to the fact<br />
that high temperature conditions<br />
were expected in the disposal, most<br />
of the experiments were performed<br />
at temperatures between 150 and<br />
200 °C. Most of the corrosion experiments<br />
were carried out in closed autoclaves<br />
simulating the deep disposal<br />
redox conditions. The attacking<br />
solutions were selected according<br />
the host rocks under investigation at<br />
this time.<br />
It needs to be mentioned that<br />
different host rocks together with the<br />
rock specific disposal concepts significantly<br />
influences the selection of the<br />
Decommissioning and Waste Management<br />
Corrosion of Canister Materials for Radioactive Waste Disposal ı Bernhard Kienzler