Table
2: fish density approximation
Species |
Technique |
Date/Location |
Fish
no./area fished |
Density(fish/m2) |
Koaro |
Electric fishing
(1 pass) |
27/05/04, Gorge
lower 1 km |
5/130 |
0.039 |
Koaro |
Electric fishing
(1 pass) |
10/06/03, Above
dam |
31/240 |
0.13 |
LF eel |
Electric fishing
(1 Pass) |
27/05/04, Gorge lower 1 km |
5/130 |
0.039 |
LF eel |
Electric fishing
(1 Pass) |
10/06/03, Above
dam |
11/240 |
0.045 |
Shortjaw K |
Spotlighting
|
27/05/04 Below
gorge outlet |
4/1600 |
0.0025 |
Shortjaw K |
Spotlighting |
2001 –
GB/NthWest Nelson
SJK survey (D.O.C.) |
Mean density
of 34 sjk stms |
0.0048 |
Invertebrate densities, expressed in number
of animals per square metre, showed a similar
density pattern to koaro density differences (Appendix 2). The average
number of animals per
square metre in samples taken above the gorge on 09/07/04 equals 1774
animals. This
compares to an average of 381 animals per square metre in the top of the
gorge, downstream
of the dam, from samples taken on the same date. Earlier samples taken
on 27/05/04, in the
lower end of the gorge (sites 1 & 2), have an average density of 353
animals per square metre.
While not the specific focus of this assessment, a blue duck was noted
in the main-stem
Parapara River around 300 metres below the Glen Gyle confluence. One suspected
blue duck
feather was also located around 1 km above the gorge outlet.
Discussion
At time of survey, the Parapara River had
a moderate flow having just dropped from a recent
winter rainfall event. The Glen Gyle Stream had been subject to a very
high intensity
localised rainfall event in January 2004, and severe erosion had occurred
within this tributary.
As a result, very little instream fish cover or invertebrate food production
existed within this
tributary, as gravel/cobble interstices had all been in-filled. There
was only one pool within
the lower 200 metres which had retained fish cover, in the form of an
undercut bank, and it
was within this pool that two shortjaw kokopu were captured in a fyke
net. Very few
invertebrates were observed, although kick net sample results show the
presence of some
species (Appendix 2). The stream should slowly recover from this natural
event after a period
of years and pools/fish cover should slowly reform, along with increased
invertebrate recolonisation.
The native fish assemblage within the Parapara River Gorge and the intermediate
gradient
section of the river immediately below the gorge outlet, was a typical
representation of
Fish & Game New Zealand Nelson Marlborough Region
Sports Fish and Game Bird Management ...p19
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