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Annual report 2006-2007 - Taranaki Regional Council

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45<br />

ecosystems at similar hardness (30 g/m 3 CaCO3) (Figure 16 and Table 12). Elevated<br />

zinc levels have been recorded at this site in the past (Figure 16) but have been below<br />

guideline values since 1999.<br />

Zinc (g/m 3 )<br />

0.035<br />

0.03<br />

0.025<br />

0.02<br />

0.015<br />

0.01<br />

0.005<br />

0<br />

Zinc concentrations in tributary of Kahouri Stream<br />

upstream of Kahouri confluence (KHI000369)<br />

Jun-91<br />

Jun-92<br />

Jun-93<br />

Jun-94<br />

Jun-95<br />

Jun-96<br />

Jun-97<br />

Jun-98<br />

Jun-99<br />

Jun-00<br />

Jun-01<br />

Jun-02<br />

Jun-03<br />

Jun-04<br />

Jun-05<br />

Jun-06<br />

Zinc - acid soluble Zinc - dissolved ANZECC USEPA<br />

Figure 16 Zinc concentrations in tributary upstream of confluence with Kahouri Stream<br />

Biological survey<br />

A macroinvertebrate sample was collected from site D (Figure 1) in the tributary 800<br />

m downstream of <strong>Taranaki</strong> Galvanizers on 17 April <strong>2007</strong>. The sample was sorted and<br />

identified to provide the number of taxa (richness), MCI and SQMCIS scores for each<br />

site.<br />

The MCI is a measure of the overall sensitivity of the macroinvertebrate community<br />

to the effects of organic pollution in stony streams. It is based on the<br />

presence/absence of taxa with varying degrees of sensitivity to environmental<br />

conditions. It may be used in soft-bottomed streams to detect trends over time. The<br />

SQMCIS takes into account taxa abundance as well as sensitivity to pollution, and<br />

may reveal more subtle changes in communities, particularly if non-organic impacts<br />

are occurring. Significant differences in either MCI or SQMCIS between sites indicate<br />

the degree of adverse effects (if any) of discharges being monitored.<br />

The stream at this site had a cloudy flow, with substrate comprising hard clay and<br />

tree roots. Prior to the survey there was a reasonable period of flow recession, being<br />

93 days since a flood in excess of 3 times median flow had occurred.<br />

Site D in the Kahouri Stream tributary would be expected to support ‘poorer’<br />

macroinvertebrate communities than those of the Kahouri Stream due to the clay<br />

substrate, but in this survey the community contained many ‘sensitive’ taxa and had<br />

relatively high MCI and SQMCIs scores, indicating no detrimental effects from<br />

discharges in the Stratford industrial area in the upper part of the tributary which<br />

includes discharges from <strong>Taranaki</strong> Galvanizers, Egmont Tanneries and Firth<br />

Industries.<br />

A full biological <strong>report</strong> is given in Appendix II.

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