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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 />

8. Discussion<br />

This section revisits the main findings from Sections 4 through 7. A regional<br />

overview of state <strong>and</strong> trends in river <strong>and</strong> <strong>stream</strong> health is presented first, with<br />

this information then considered in a national context. The principal issues<br />

affecting the region’s rivers <strong>and</strong> <strong>stream</strong>s are discussed <strong>and</strong> key management<br />

issues identified, with brief consideration also given to down<strong>stream</strong> receiving<br />

environments. Lastly, monitoring limitations <strong>and</strong> knowledge gaps are outlined.<br />

8.1 Regional overview<br />

8.1.1 State<br />

Analysis of RSoE <strong>water</strong> <strong>quality</strong>, periphyton <strong>and</strong> macroinvertebrate data<br />

collected at 55 sites (46 in the case of periphyton) over the period July 2008 to<br />

June 2011 found that:<br />

27 (49%) sites were assigned ‘good’ or ‘excellent’ <strong>water</strong> <strong>quality</strong> grades,<br />

indicating that median values for at least five of the six key indicator<br />

variables in <strong>Greater</strong> <strong>Wellington</strong>’s Water Quality Index (WQI) met<br />

guideline values;<br />

27 (59%) sites were classed as ‘good’ or ‘excellent’ in terms of<br />

compliance with MfE (2000) periphyton cover/biomass guidelines,<br />

indicating infrequent or nil occurrence of nuisance periphyton growth; <strong>and</strong><br />

36 (65%) sites were classed as having ‘good’ or ‘excellent’<br />

macroinvertebrate community health, based on a comparison of mean MCI<br />

scores against the thresholds in national guidance provided by Stark <strong>and</strong><br />

Maxted (2007).<br />

The remaining sites (35–51% depending on the indicator) were classed as<br />

having ‘fair’ or ‘poor’ <strong>water</strong> <strong>quality</strong> or ecosystem health. While this report has<br />

not attempted to assess the suitability of rivers <strong>and</strong> <strong>stream</strong>s for other, values 28<br />

such as recreational use <strong>and</strong> trout fishery/spawning, these values are also likely<br />

to be impaired at some RSoE sites. For example, the two Ruamahanga <strong>River</strong><br />

sites with a WQI grade of ‘fair’ (Gladstone <strong>and</strong> Pukio) are in close proximity to<br />

recreational <strong>water</strong> <strong>quality</strong> monitoring sites with Suitability for Recreation<br />

Grades of ‘poor’ (see Greenfield et al. 2012). Similarly, sites on a number of<br />

river <strong>and</strong> <strong>stream</strong> reaches listed in <strong>Greater</strong> <strong>Wellington</strong>’s existing Regional<br />

Fresh<strong>water</strong> Plan (WRC 1999) as supporting trout habitat (eg, Taueru <strong>River</strong> at<br />

Gladstone, Kopuaranga <strong>River</strong> at Stewarts, Mangatarere Stream at SH 2 <strong>and</strong><br />

Huangarua <strong>River</strong> at Ponatahi Bridge), frequently exceeded MfE (2000)<br />

periphyton guidelines for protection of trout habitat <strong>and</strong> angling values.<br />

Water <strong>quality</strong>, periphyton cover/biomass <strong>and</strong> macroinvertebrate health all<br />

showed clear linkages with up<strong>stream</strong> catchment l<strong>and</strong>cover (Figure 8.1). Sites<br />

classified as having ‘good’ or ‘excellent’ <strong>water</strong> <strong>quality</strong> <strong>and</strong> ecosystem health<br />

tend to be located on the upper reaches of rivers <strong>and</strong> <strong>stream</strong>s that drain the<br />

28 The specific values that rivers <strong>and</strong> <strong>stream</strong>s in the <strong>Wellington</strong> region are to be managed for are currently being considered as part of the<br />

review of <strong>Greater</strong> <strong>Wellington</strong>’s existing Regional Fresh<strong>water</strong> Plan.<br />

PAGE 100 OF 160 WGN_DOCS-#1100598-V3

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