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 />
<strong>water</strong> temperatures due to samples being taken later in the season. These<br />
conditions are reflected in both periphyton biomass <strong>and</strong> periphyton cover<br />
measurements being at their lowest across all 46 sites in the first two years of<br />
the trend period (Figure 5.9). The low biomass values recorded in 2003/04 <strong>and</strong><br />
2004/05 are likely to have influenced the increasing trends detected at several<br />
sites (eg, Figure 5.8).<br />
Mean filamentous <strong>stream</strong>bed cover (%)<br />
Chlorophyll a (mg/m 2 )<br />
80<br />
70<br />
60<br />
50<br />
40<br />
30<br />
20<br />
10<br />
0<br />
300<br />
250<br />
200<br />
150<br />
100<br />
50<br />
0<br />
2004 2005 2006 2007 2008 2009 2010 2011<br />
2004 2005 2006 2007 2008 2009 2010 2011<br />
Figure 5.9: Box plots summarising the range of annual measurements of mean<br />
filamentous periphyton cover (top) <strong>and</strong> periphyton biomass (as represented by<br />
chlorophyll a, bottom), based on data collected from 46 RSoE sites with hard<br />
substrates between September 2003 <strong>and</strong> June 2011. Note that some outliers have<br />
been excluded from the periphyton biomass plots for clarity<br />
Assessment of summer-time 25 th percentile flows 21 at flow recorder sites at or<br />
near RSoE sites that exhibited increasing periphyton trends showed that across<br />
the region, flows during the 2003/04 <strong>and</strong> 2004/05 summers were considerably<br />
higher than the rest of the reporting period (Figure 5.10). At some rivers or<br />
<strong>stream</strong>s (eg, the Ruakokoputuna <strong>River</strong> in eastern Wairarapa which is<br />
considered to have similar flow patterns to the Awhea <strong>River</strong>) there was a<br />
notable decline in 25 th percentile summer-time flows across the period while at<br />
others (eg, Porirua Stream) summer-time low flows fluctuated following a peak<br />
in 2004 <strong>and</strong> 2005. In general, Keenan et al. (2012) noted that since 2005 there<br />
have been lower annual 7-day low flows <strong>and</strong> more low flow days per year<br />
compared to average.<br />
21 25 th percentile flow was used to indicate lowest summer-time flows when periphyton growth tends to be greatest. Other statistics such as<br />
median <strong>and</strong> minimum flow showed similar patterns.<br />
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