River and stream water quality and ecology - Greater Wellington ...
River and stream water quality and ecology - Greater Wellington ...
River and stream water quality and ecology - Greater Wellington ...
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<strong>River</strong> <strong>and</strong> <strong>stream</strong> <strong>water</strong> <strong>quality</strong> <strong>and</strong> <strong>ecology</strong> in the <strong>Wellington</strong> region: State <strong>and</strong> trends<br />
It should also be noted that MCI <strong>and</strong> QMCI thresholds suggested by Stark <strong>and</strong><br />
Maxted (2007) do not take into account the natural variation in<br />
macroinvertebrate community composition that can occur in response to<br />
differences in catchment altitude, geology <strong>and</strong> other geophysical characteristics.<br />
6.1.2 Macroinvertebrate metrics<br />
Summary statistics for the four metrics calculated (MCI, QMCI, %EPT taxa <strong>and</strong><br />
%EPT individuals) calculated for each of the 55 RSoE sites are presented in<br />
Table 6.2. Mean MCI scores across the 55 RSoE sites ranged from a minimum<br />
of 67 (Waiwhetu Stream at Wainuiomata Hill Bridge) to a maximum of 146<br />
(Ruamahanga <strong>River</strong> at McLays). As outlined in Section 2.3, the Waiwhetu<br />
Stream site is known to be occasionally influenced by tidal backflow <strong>and</strong> taxa<br />
indicative of estuarine conditions have been recorded at this site. Because the<br />
MCI was not designed to take into account estuarine influence its application at<br />
this site may not be appropriate. The next lowest mean MCI score recorded<br />
across the 55 sites was 75.9 (Parkvale Stream at Weir).<br />
Based on mean MCI scores, 16 sites were classified as ‘excellent’, 20 sites as<br />
‘good’, 16 sites as ‘fair’ <strong>and</strong> 3 sites as ‘poor’. All sites classed as ‘excellent’<br />
drain up<strong>stream</strong> catchments dominated by indigenous forest. The seven sites<br />
classed as ‘poor’ or within the ‘fuzzy boundary’ of the fair/poor threshold were<br />
found in catchments dominated by pastoral or urban l<strong>and</strong>cover (Figure 6.1). All<br />
but one of these sites have substrate dominated by soft sediment – the<br />
exception being Parkvale Stream at Weir which has a relatively small<br />
catchment dominated by intensive agricultural l<strong>and</strong> use.<br />
Number of sites<br />
25<br />
20<br />
15<br />
10<br />
5<br />
0<br />
Indigenous forest Pasture Urban Exotic forest<br />
Excellent<br />
Good<br />
Fair<br />
Poor<br />
Figure 6.1: Macroinvertebrate <strong>quality</strong> classes assigned to each of the 55 RSoE<br />
sites, grouped according to REC l<strong>and</strong>cover. Quality classes are based on the<br />
application of Stark <strong>and</strong> Maxted (2007) thresholds to mean MCI scores from<br />
annual sampling in 2009, 2010 <strong>and</strong> 2011. Hatched boxes represent sites within<br />
the ±5 MCI unit ‘fuzzy boundary’ between each class (note the result from the<br />
single exotic forestry site falls on the boundary of the fair/good threshold)<br />
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