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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 />

Table 5.2: Criteria <strong>and</strong> MfE (2000) thresholds used to assign each RSoE site to<br />

one of four periphyton classes. Note that a site only had to exceed one of the<br />

<strong>stream</strong>bed cover or biomass thresholds to be categorised into a particular class<br />

Quality<br />

class<br />

Excellent<br />

Good<br />

Fair<br />

Poor<br />

Explanation<br />

Minimal exceedance of<br />

<strong>stream</strong>bed cover guidelines<br />

<strong>and</strong> full compliance with<br />

biomass guidelines<br />

Infrequent non-compliance<br />

with <strong>stream</strong>bed cover <strong>and</strong>/or<br />

biomass guidelines<br />

Intermittent non-compliance<br />

with <strong>stream</strong>bed cover <strong>and</strong>/or<br />

biomass guidelines<br />

Frequent non-compliance<br />

with <strong>stream</strong>bed cover <strong>and</strong>/or<br />

biomass guidelines<br />

Guidelines/thresholds used to determine class<br />

Streambed cover<br />

(%n exceedances)<br />

Mat Filamentous<br />

(60%)<br />

(30%)<br />

Chlorophyll a<br />

(n exceedances)<br />

50 mg/m 2 120 mg/m 2<br />

20 3 ≥ 2<br />

<strong>quality</strong> <strong>and</strong> shade (one-off measures, see Appendix 8) substrate size (mean of<br />

three assessments), <strong>and</strong> estimates of mean annual maximum accrual derived by<br />

Thompson <strong>and</strong> Gordon (2010b).<br />

(a) Cautionary notes<br />

The number of observations of periphyton <strong>stream</strong>bed cover made at each of the<br />

46 RSoE sites varied significantly over the reporting period. On average,<br />

observations could not be made on seven sampling occasions at each site<br />

(range 0 to 20), due to either high turbidity, high flows or because the site<br />

could not be accessed (eg, road closure). As a result, several sites had less than<br />

60% of the potential number of <strong>stream</strong>bed cover assessments (max n=36).<br />

The MfE (2000) cover <strong>and</strong> biomass thresholds for trout habitat <strong>and</strong> angling in<br />

Table 5.1 do not apply to all RSoE sites as not all rivers <strong>and</strong> <strong>stream</strong>s in the<br />

<strong>Wellington</strong> region are valued for trout fishing or spawning. In addition, the<br />

periphyton biomass thresholds for the protection of aquatic biodiversity do not<br />

take into account natural variation in periphyton biomass that can occur in<br />

response to differences in catchment altitude, geology <strong>and</strong> other geophysical<br />

characteristics.<br />

5.1.2 Periphyton cover<br />

Twenty six RSoE sites exceeded MfE (2000) guidelines for periphyton<br />

<strong>stream</strong>bed cover at least once (<strong>and</strong> typically more than once) during the reporting<br />

period (Table 5.3). The guideline for filamentous <strong>stream</strong>bed cover was more<br />

frequently exceeded than the mat cover guideline (25 sites <strong>and</strong> 6 sites,<br />

respectively). Sites that exceeded the guideline for mat periphyton cover<br />

typically also exceeded the filamentous periphyton guideline at some time during<br />

the reporting period except at one site, Hutt <strong>River</strong> opposite Manor Park Golf Club.<br />

PAGE 58 OF 160 WGN_DOCS-#1100598-V3

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