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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 />

6. Macroinvertebrates – state <strong>and</strong> trends<br />

This section assesses state <strong>and</strong> trends in macroinvertebrate community health<br />

in river <strong>and</strong> <strong>stream</strong>s across the <strong>Wellington</strong> region, based on the results of<br />

monitoring conducted annually at 55 RSoE sites in late summer/early autumn.<br />

The current state of macroinvertebrate health is presented first, using annual<br />

data from 2009, 2010 <strong>and</strong> 2011. Temporal trends are then examined for the<br />

period 2004 to 2011.<br />

6.1 State<br />

6.1.1 Approach to analysis<br />

Macroinvertebrate samples collected annually in 2009, 2010 <strong>and</strong> 2011 were<br />

used to determine the current state of macroinvertebrate health at each of the<br />

55 RSoE sites. Due to changes in the number of samples collected over the<br />

reporting period (from 2004 to 2009 three replicate samples were collected<br />

from each site, whereas in 2010 <strong>and</strong> 2011 just one sample was collected) <strong>and</strong><br />

some inconsistencies in the resolution of taxonomic identification between<br />

years, an initial data screening <strong>and</strong> ‘clean up’ process was undertaken prior to<br />

data analysis. 22 As a result of this exercise, some of the metric scores presented<br />

here may differ slightly to those presented in earlier reports (eg, Perrie &<br />

Cockeram 2010).<br />

Consistent with the SoE reporting recommendations in Stark <strong>and</strong> Maxted<br />

(2007), the current ‘state’ of macroinvertebrate community health was<br />

determined using the Macroinvertebrate Community Index (MCI). However,<br />

additional metrics – Quantitative MCI (QMCI), %Ephemeroptera-Plicoptera-<br />

Trichoptera (EPT) taxa 23 <strong>and</strong> %EPT individuals 23 – were also calculated <strong>and</strong><br />

are discussed where relevant (see Appendix 3 for more information on the<br />

various macroinvertebrate metrics). Mean metric scores were calculated for<br />

each site across the three years <strong>and</strong> compared against the <strong>quality</strong> class<br />

thresholds in Stark <strong>and</strong> Maxted (2007) (Table 6.1). Stark <strong>and</strong> Maxted (2007)<br />

note that these thresholds should be interpreted as having ‘fuzzy boundaries’,<br />

with a margin of ±5 or ±0.2 units applied to the MCI or QMCI thresholds,<br />

respectively.<br />

Table 6.1: Interpretation of MCI-type <strong>and</strong> QMCI scores (from Stark & Maxted 2007)<br />

Quality class MCI <strong>and</strong> MCIsb QMCI<br />

Excellent ≥ 120 ≥ 6.00<br />

Good 100―119 5.00―5.99<br />

Fair 80―99 4.00―4.99<br />

Poor

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