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 ...
You also want an ePaper? Increase the reach of your titles
YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.
<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 />
Appendix 2: <strong>River</strong> Environmental Classification (REC)<br />
As outlined in Section 2.1, rivers <strong>and</strong> <strong>stream</strong>s in the <strong>Wellington</strong> region are diverse <strong>and</strong><br />
some may have differing <strong>water</strong> <strong>quality</strong> simply due to their size, climate <strong>and</strong> underlying<br />
geology rather than due to human-induced impacts. To reduce this bias, comparisons<br />
between RSoE sites are undertaken using the <strong>River</strong> Environment Classification (REC).<br />
REC characterises river environments at six hierarchical levels, corresponding to a<br />
controlling environmental factor (Snelder et al. 2003). The factors, in order from the<br />
largest spatial scale to the smallest, are climate, source-of-flow, geology, l<strong>and</strong>cover,<br />
network position <strong>and</strong> valley l<strong>and</strong>form. The first four REC factors are explained in<br />
Table A2.1. See Appendix 1 for the REC description for each RSoE site.<br />
Table A2.1: REC classification levels, classes, mapping characteristics <strong>and</strong> criteria used to<br />
assign river segments to REC classes (after Snelder et al. 2003)<br />
Classification level<br />
<strong>and</strong> scale<br />
Climate<br />
(10 3 – 10 4 km 2 )<br />
Source of flow<br />
(10 2 – 10 3 km 2 )<br />
Geology<br />
(10 – 10 2 km 2 )<br />
L<strong>and</strong>cover*<br />
(10 km 2 )<br />
Classes <strong>and</strong> notation<br />
Warm extremely wet<br />
(WX)<br />
Warm wet (WW)<br />
Warm dry (WD)<br />
Cool extremely wet (CX)<br />
Cool wet (CW)<br />
Cool dry (DC)<br />
Mountain (M)<br />
Hill (H)<br />
Low elevation (L)<br />
Lake (Lk)<br />
Alluvium (Al)<br />
Hard sedimentary (HS)<br />
Soft sedimentary (SS)<br />
Volcanic basic (VB)<br />
Volcanic acidic (VA)<br />
Plutonic (Pl)<br />
Miscellaneous (M)<br />
Bare (B)<br />
Indigenous forest (IF)<br />
Pastoral (P)<br />
Tussock (T)<br />
Scrub (S)<br />
Exotic forest (EF)<br />
Wetl<strong>and</strong> (W)<br />
Urban (U)<br />
Mapping<br />
characteristics<br />
Mean annual<br />
precipitation, mean<br />
annual potential<br />
evapotranspiration,<br />
mean annual<br />
temperature.<br />
Catchment rainfall<br />
volume in elevation<br />
categories, lake<br />
influence index.<br />
Proportions of each<br />
geological category in<br />
section catchment.<br />
Proportions of each<br />
l<strong>and</strong>cover category in<br />
section catchment.<br />
Class assignment criteria<br />
Warm: mean annual temperature ≥<br />
12˚C<br />
Cool: mean annual temperature 500 mm <strong>and</strong> 50% annual precipitation volume<br />
>1,000 m ASL<br />
H: 50% precipitation volume 400 to<br />
1,000 m ASL<br />
L: >50% rainfall 0.033<br />
Class = spatially dominant geology<br />
category unless combined soft<br />
sedimentary geological categories<br />
exceed 25% of catchment area, in<br />
which case class = SS.<br />
Class = spatially dominant l<strong>and</strong>cover<br />
category unless pastoral exceeds 25%<br />
of catchment area, in which case class<br />
= P, or unless urban exceeds 15% of<br />
catchment area, in which case class =<br />
U.<br />
* It is important to note that l<strong>and</strong>cover types that are not classified as dominant using the REC criteria may still significant affect river <strong>and</strong> <strong>stream</strong><br />
<strong>water</strong> <strong>quality</strong> <strong>and</strong> <strong>ecology</strong>. Further, in many cases, the current ‘condition’, as measured at each RSoE site, is the result of the cumulative impacts<br />
of all l<strong>and</strong>cover types <strong>and</strong> associated activities in the up<strong>stream</strong> catchment.<br />
WGN_DOCS-#1100598-V3 PAGE 131 OF 160