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 />
The ecological significance of these trends is unclear. However, at some sites<br />
where a deteriorating trend in MCI was identified (eg, Whareroa Stream at<br />
Waterfall Road <strong>and</strong> Waiwhetu Stream at Wainuiomata Hill Road), the<br />
magnitude of the deteriorating trend resulted in the site moving into a lower<br />
macroinvertebrate class during the reporting period (Figure 6.6). Application<br />
of two thresholds used in other regions to identify ecologically significant<br />
trends – a relative rate of change greater than 1% per year <strong>and</strong> an overall<br />
change greater than 20% (Stark 2010; Collier & Hamer 2012) – resulted in all<br />
23 <strong>and</strong> 16 trends, respectively, being classed as ecologically significant.<br />
However, these thresholds are considered arbitrary <strong>and</strong> so should be used with<br />
caution. For future reporting of macroinvertebrate metric trends it is<br />
recommended that alternative methods for assessing ecological significance be<br />
explored, including the method used by Collier <strong>and</strong> Hamer (2012); this method<br />
bases the threshold for ecological significance on the degree of ‘natural<br />
variation’ at reference sites over time.<br />
MCI score<br />
140<br />
120<br />
100<br />
80<br />
60<br />
RS11: Whareroa S - Waterfall Rd<br />
RS27: Waiwhetu S - Wainui Hill Br<br />
RS33: Ruamhanga R - Gladstone<br />
RS38: Kopuaranga R - Stewarts<br />
RS41: Waingawa R - South Rd<br />
Excellent<br />
Good<br />
40<br />
2003 2004 2005 2006 2007 2008 2009 2010 2011 2012<br />
Figure 6.6: Mean Macroinvertebrate Community Index (MCI) scores for samples<br />
collected annually between 2004 <strong>and</strong> 2011 from five RSoE sites where significant<br />
declining trends were detected. Red lines <strong>and</strong> the grey b<strong>and</strong>s represent Stark <strong>and</strong><br />
Maxted (2007) thresholds <strong>and</strong> corresponding fuzzy boundaries, respectively<br />
In general, no clear reasons could be found for the observed trends in<br />
macroinvertebrate metrics. However, corresponding trends in <strong>water</strong> <strong>quality</strong> or<br />
periphyton variables may have had a bearing on results at some sites. For<br />
example:<br />
The decline in %EPT taxa identified at Whangaehu <strong>River</strong> 250 m from<br />
confluence coincided with a deterioration in visual clarity <strong>and</strong> an increase<br />
in turbidity, dissolved reactive phosphorus <strong>and</strong> total phosphorus (based on<br />
non-flow adjusted data) (Section 4.2.2).<br />
PAGE 84 OF 160 WGN_DOCS-#1100598-V3<br />
Fair<br />
Poor