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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

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