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manufacture, processing and use of stainless steel - International ...

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mg <strong>of</strong> dust per animal. In another treatment group, animals received four separate<br />

instillations at six-monthly intervals, each containing 20 mg/animal. Each <strong>of</strong> the four<br />

treatment groups contained at least 50 females <strong>and</strong> 50 males. Two controls groups<br />

were <strong>use</strong>d: one group <strong>of</strong> untreated animals <strong>and</strong> a second group <strong>of</strong> saline-treated<br />

animals. Animals were observed until spontaneous death occurred or they became<br />

moribund <strong>and</strong> were killed.<br />

Bodyweight <strong>and</strong> survival <strong>of</strong> treated animals was similar to that <strong>of</strong> controls. Tumour<br />

incidence was examined <strong>and</strong> in all four treatment groups showed no increase over the<br />

control incidence. This study deviates from EC <strong>and</strong> OECD guidelines in that a<br />

different route <strong>of</strong> exposure was employed, <strong>and</strong> a non-st<strong>and</strong>ard dosing regime was<br />

<strong>use</strong>d. Further, similar to the previously reported study, it is uncertain whether the<br />

MTD was <strong>use</strong>d or was even achievable. With these limitations in mind, this study<br />

provides no evidence for the carcinogenicity <strong>of</strong> the grinding dust from this austenitic<br />

<strong>stainless</strong> <strong>steel</strong>.<br />

The carcinogenicity <strong>of</strong> grinding dust from <strong>stainless</strong> <strong>steel</strong>, administered by i.p.<br />

injection, was investigated in female Wistar rats (Pott et al. 1992, 1991). The<br />

<strong>stainless</strong> <strong>steel</strong> <strong>use</strong>d in the experiment was "nickel alloy 29"; this was milled to give a<br />

particle diameter <strong>of</strong>

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