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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 />

the various guidelines across the 55 RSoE sites is summarised in Table 4.3.<br />

Overall, median values for each <strong>water</strong> <strong>quality</strong> variable met their corresponding<br />

guideline values at around two-thirds or more of sites. Visual clarity <strong>and</strong><br />

dissolved reactive phosphorus (DRP) were the two exceptions; median values<br />

only met guidelines at 44% <strong>and</strong> 55% of sites, respectively.<br />

Table 4.3: Summary of compliance with selected <strong>water</strong> <strong>quality</strong> guidelines/TVs,<br />

based on median values for data collected monthly from 55 RSoE sites over July<br />

2008 to June 2011<br />

Variable Guideline/TV<br />

Number (<strong>and</strong> percentage) of sites<br />

complying with guideline values<br />

Water temperature (ºC) ≤19 55 (100%)<br />

Dissolved oxygen (% saturation) ≥80 49 (89.1%)<br />

pH 6.5–9.0 54 (98.2%)<br />

Visual clarity (m) ≥1.6 24 (43.6%)<br />

Turbidity (NTU) ≤5.6 44 (80.0%)<br />

Nitrite-nitrate nitrogen (mg/L) ≤0.444 39 (70.9%)<br />

Ammoniacal nitrogen (mg/L) ≤0.021 49 (89.1%)<br />

Nitrate nitrogen – toxicity (mg/L) ≤1.7 52 (94.5%)<br />

Total nitrogen (mg/L) ≤0.614 36 (65.5%)<br />

Dissolved reactive phosphorus (mg/L) ≤0.010 30 (54.5%)<br />

Total phosphorus (mg/L) ≤0.033 37 (67.3%)<br />

E. coli (cfu/100mL)<br />

≤100<br />

≤550<br />

35 (63.6%)<br />

51 (92.7%)<br />

4.1.3 Water temperature<br />

None of the 55 RSoE sites recorded a median <strong>water</strong> temperature value greater<br />

than the 19 o C guideline. However, 30 sites exceeded this guideline on at least<br />

one sampling occasion <strong>and</strong> 17 sites exceeded it on more than 10% of sampling<br />

occasions (Table 4.2). Awhea <strong>River</strong> at Tora Road <strong>and</strong> Totara Stream at<br />

Stronvar exceeded the guideline on 33% <strong>and</strong> 27% of sampling occasions,<br />

respectively.<br />

The highest maximum <strong>water</strong> temperature recorded was 25 o C at Waipoua <strong>River</strong><br />

at Colombo Road, just on <strong>Greater</strong> <strong>Wellington</strong>’s RFP critical threshold. The<br />

next highest maximum temperatures were recorded at Awhea <strong>River</strong> at Tora<br />

Road <strong>and</strong> Totara Stream at Stronvar (24.3 o C <strong>and</strong> 24.1 o C, respectively).<br />

RSoE sites located on the lower reaches of the region’s larger rivers<br />

(eg, Ruamahanga <strong>River</strong> at Pukio), sites associated with the eastern Wairarapa<br />

hill country (eg, Awhea <strong>River</strong> at Tora Road), <strong>and</strong> sites on rivers <strong>and</strong> <strong>stream</strong>s<br />

that experience long periods of low flows (eg, Waipoua <strong>River</strong> at Colombo<br />

Road) generally recorded the highest median <strong>water</strong> temperatures. <strong>River</strong>s <strong>and</strong><br />

<strong>stream</strong>s with limited <strong>stream</strong>side vegetation <strong>and</strong> shading (eg, Parkvale Stream at<br />

Weir) also tended to have higher median <strong>water</strong> temperatures (Figure 4.1). In<br />

contrast, sites located in catchments dominated by indigenous forest with hill<br />

elevation source of flows typically recorded the lowest median <strong>water</strong><br />

temperatures over the reporting period (Figure 4.1).<br />

WGN_DOCS-#1100598-V3 PAGE 25 OF 160

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