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 />
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 />
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