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 />
influenced the deteriorating trends reported for many sites. The 2004 <strong>and</strong> 2005<br />
summers at the start of the trend analysis period were characterised by high<br />
river flows <strong>and</strong> frequent freshes, contributing to low periphyton biomass <strong>and</strong><br />
high macroinvertebrate scores.<br />
Analysis of NZFFD records identified a statistically significant decline in<br />
indigenous fish community condition in the <strong>Wellington</strong> region (particularly<br />
evident at pastoral sites) between the earliest time period (1960–1990) <strong>and</strong> the<br />
two more recent periods (1991–2000 <strong>and</strong> 2001–2010) examined. As will be<br />
discussed next, this observation is also present in the national record.<br />
8.2 National context<br />
The strong relationship between river/<strong>stream</strong> health <strong>and</strong> l<strong>and</strong>cover/l<strong>and</strong> use in<br />
this report is consistent with patterns observed in other regions (eg, Collier &<br />
Hamer 2010; Neale 2010) <strong>and</strong> across New Zeal<strong>and</strong> (eg, Quinn & Raaphorst<br />
2009; Ballantine et al. 2010; Ballantine & Davies-Colley 2010); rivers <strong>and</strong><br />
<strong>stream</strong>s located in catchments dominated by indigenous forest typically have<br />
better <strong>water</strong> <strong>quality</strong>, healthier macroinvertebrate communities <strong>and</strong> less<br />
periphyton growth than those located in pastoral <strong>and</strong> urban catchments. Fish<br />
communities generally exhibit a similar pattern (Joy 2009).<br />
8.2.1 Water <strong>quality</strong><br />
Making direct comparisons between the data presented in this reported with<br />
similar data reported by other regional councils or nationally is problematic<br />
given differences in monitoring site networks (eg, number <strong>and</strong> location of<br />
sites), sampling frequency, <strong>and</strong> sampling <strong>and</strong> analytical methods between some<br />
regions. However, the recent analysis of regional <strong>water</strong> <strong>quality</strong> data sets<br />
undertaken as part of the L<strong>and</strong> <strong>and</strong> Water New Zeal<strong>and</strong> (LAWNZ) 29 initiative<br />
provides an indication of how <strong>water</strong> <strong>quality</strong> in the <strong>Wellington</strong> region currently<br />
compares with the rest of New Zeal<strong>and</strong>. According to this analysis<br />
(summarised in Table 8.1), for the period January 2004 to December 2011:<br />
RSoE sites classed as upl<strong>and</strong> (>150 m altitude) forest were generally in a<br />
similar or better condition than the national average (median), although<br />
three of the seven RSoE sites in this class recorded median DRP<br />
concentrations above the national median.<br />
Regional median values for most variables in the lowl<strong>and</strong> (