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coaltech upper olifants river catchment wetland inventory ...

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More important in the removal of metals is the role played by algae. Algae are manganese<br />

accumulators and can accumulate other metals as well. The metal uptake ability of algae is<br />

controlled by the specific bioaccumulation and physical-chemical factors present. Although<br />

algae can accumulate vast amounts of metals in relation to mass, the distribution of algae in<br />

<strong>wetland</strong>s is limited and therefore the total metal uptake by algae in the <strong>wetland</strong>. The most<br />

important role of plants in the removal of metals from the system are therefore not in the<br />

accumulation of metals, but in changing the environment to that more suitable for the<br />

removal of toxicants (Palmer et al 2002, Kotze 2000, Kotze et al 2000).<br />

Acid mine drainage has entered the Kromdraaispruit <strong>wetland</strong> (located approximately 20 km<br />

north-west of Witbank) for 20 years, a <strong>wetland</strong> with distinct morphological zones. The<br />

Kromdraaispruit <strong>wetland</strong> is located in the Kromdraaispruit, a tributary of the Zaalklapspruit,<br />

flowing into the Wilge River. Vegetation in the <strong>wetland</strong> removes high percentages of influent<br />

metals. The accumulation of iron and manganese takes place in the roots and aerial parts<br />

(stems and leaves) of the <strong>wetland</strong> vegetation (Limpitlaw 1995). It was determined that the<br />

biochemical water quality of acid mine drainage passing through a <strong>wetland</strong> improves with<br />

distance moved through the <strong>wetland</strong>. It was also determined that the concentration of<br />

sulphate-reducing bacteria increases with distance away from the pollution source (Limpitlaw<br />

1996). The immobilisation of metals was best in the areas of optimal organic adsorption of<br />

metals (Limpitlaw 1995, 1996).<br />

Permanently wet seeps can function to reduce nitrate, sulphate, iron and manganese. Where<br />

there are both nitrates and sulphates in the groundwater competition occurs for the available<br />

carbon and reduction is therefore a slower process. Similar processes occur in the seasonal<br />

seeps, but the leaching of immobilised substances can occur before soil saturation, thereby<br />

affecting changes to the redox potential and pH of the site. Organic materials in the <strong>wetland</strong><br />

are lost when the water levels drop (Palmer et al 2002).<br />

Wetland Database for UORC - 37 -

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