Lincoln University Digital Dissertation Copyright Statement The digital copy of this dissertation is protected by the Copyright Act 1994 (New Zealand). This dissertation may be consulted by you, provided you comply with the provisions of the Act and the following conditions of use: 


you will use the copy only for the purposes of research or private study you will recognise the author's right to be identified as the author of the dissertation and due acknowledgement will be made to the author where appropriate you will obtain the author's permission before publishing any material from the dissertation. T H E
MA N G A N U I 0 T E A 0
R I V E R
AN INVENTORY OF RIPARIAN STRIP
'EGETATION AND ITS INFLUENCE
ON BLUE DUCK HABITAT
'BY:
JOHN RICH,
DIP P+RM'
A dissertation as part of the· Diploma.' in Parks and Recreation
Management, Lincoln College, December 1988
2/ ...
C
0
N
T
E
N
T
S
P A G E
1.
Study Summary
3
2.
Manganuioteao River - Location and Description
4
3.
The riparian strip - a definition and application
' 7
to the Manganuioteao River system.
4.
Vegetation Surveying
8
4.1
Method
8
4.2
Surveying Sheet Explanation
9
5.
An Interpretation Guide for 1110,000 Cadastral Maps
13
6.
Results and Recommendations Discussion
14
7.
Key to Cadastral Maps
19
MAPS
Map 1
Location and Setting
Map 2
The Study Area
Cadastral Maps 1 - 12
6
18
20
FIGURES
Figure 1 - an explanation of riparian strip width
measurements
8
3/ ...
1.
STUDY SUMMARY
This is a study of the riparian strips of the Manganuioteao River.
The study focuses on the vegetation of the riparian strip.
It is
basically a very broad inventory, designed as an introduction
to further riparian ecosystem research on this river.
Information
available from this study will also be a guide to making immediate
and long term management decisions.
The study only concentrates on the Manganuioteao River itself, ignoring
the various tributaries.
These will be completed at a later date.
There are two study goals.
1.
To form an inventory of riparian strips on the Manganuioteao River (80%)
2.
To attempt to establish if the vegetation type and condition is a
reason why no blue duck live downstream from Ruatiti Domain (2Q%).
In addition to these goals some management suggestions are made for
the riparian strips.
I would like to eKpress my thanks to the staff of the Wanganui District
of the Department of Conservation, particularly John Heaphy, John Ombler and
Bob Halsey, whose help was invaluable.
4/ .•.
2.
MANGANUIOTEAO RIVER - LOCATION AND DESCRIPTION
The Manganuioteao
River.
River is the third largest tributary of the Wanganui
It begins on the western slopes of Mt Ruapehu at over 2000
metres above sea level and flows in a south westerly direction for
80 kilometres, eventually running into the Wanganui River at 56 metres
above sea level.
The nearest town to the river is Raetihi, while Ohakune
and National Park are also nearly.
mainly to the middle reaches.
Road access to the river is limited
The river is fed by several tributaries.
The quality of the water in these tributaries contributes to the
excellent water quality of the Manganuioteo River.
Nearly all the riparian strips on the river are privately owned, apart
from the designated Section 58 strips, upstream from the Ruatiti Domain.
Man has been living in the valley since about 1100 A.D. when the valley
became an important access route from Wanganui> to: the volcanic
plateau.
Since the turn of the centuary, with increased European
influence with the development of farms, the surrounding valley
vegetation has been extensively modified.
Much land has since reverted
to native vegetation particularly in the lower stretches.
Riparian
vegetation has remained relatively unchanged, particularly in the lower
reaches.
The rainfall average per year for the valley is about 2000 millimetres.
The lower reaches receive about 1400 millimetres per year while the
upper reaches receive about 5000 millimetres per year.
The valley
climate is generally mild with still, hot conditions in summer and
temperature inversions with morning mists in spring and autumn.
The river is very gorgy and fast flowing for much of its length.
pools have developed on the river.
Permanent
These pools are remarkably stable,
which is typical of the whole Manganuioteao River ecosystem.
5 I . ..
The wildlife is well known and valued on the Manganuioteao River.
The
river is home to the largest colony of blue duck in the North Island
and is also home to many other birds, fish, mammals and insects
dependant in some way on the river for survival.
The recreation opportunities using the river as a resource are valued
by many.
Angling is a popular pastime because of the good fishing
and water quality and beacuse of the accompanying solitude and this
is particularly popular when the river is in flood.
Other activities
include hunting, camping, picnicing, swimming, nature, observation and
tourism.
The river scenery is another recreation attraction.
The intrinsic
values the river holds are high and visitor numbers to the area
reflect this.
The river has, in the past, been threatened by hydro electric development.
In March 1988, a preservation order was imposed on the river protecting
the water against any such development.
In time, protection will
hopefully extend to include the riparian strips.
T~e
wildlife,
recreational and intrinsic values the river offers will then be
totally protected from development.
6/ .•.
I
\
\
\
I
I
I
I
I
/
I
/
I
I
I
.
I
I
I
""
I
I
''
~
\
•I
(\
• Mt Ruapehu
,/,/!!?,
<T~/ -:
I
01
I
1<,
Road.,
'-..._
1~.:t;-·
....
I
'\,
1
I
J
Contours
.'
'
""'
0
10km
U:~···
.·r"'
.:~
··:'
MAP 1
'Wa'ouru
'·------- --iJ
Roads
10
I
1
·...,
./QOhakune
_,--6-_ .,..,....,---- ... ,
__..-/ Raetihi
"-,
- - _.,.
........
~~·.:..
,,0<: Wmganu i
{',.... ·y..,""J
•
. .
I
:t::'l
,"
,~
/\>
I
I
Location and setting.
I
39' 2o's
7I . ..
3.
THE RIPARIAN STRIP -.A. DEFINITION AND APPLICATION TO THE MANGANUIOTEAO
RIVE~ SYSTEM
Riparian strips are basically the banks on either side of a river.
In the case of the Manganiuoteao
River the riparian strip is the
piece of land stretching lengthwise along both sides of the river, from
its beginning to its confluence with the Wanganui River.
is of various widths.
The riparian strip
The width boundaries are, firstly, the edge of
the river and secondly, where the vegetation on the river bank changes.
Riparian strips are an essential part of the complete river ecosystem.
They provide nutrients to the water as well as shelter for the wildlife
living in the river ecosystem.
Vegetation on the riparian strips also
helps hold the river bank together.
The riparian strips can also
contribute to the intrinsic value of p river.
The riparian strips on the Manganuioteao River can be described as stable.
This is particularly evident where plants are flourishing on cliffs.
They grow there because the stable conditions allow them to.
This
stableness no doubt contributes to the water quality of the river.
The water quality is outstanding.
This is due in part to the slow
erosion rate of the river banks and thus the Manganuioteao River
remains largely silt free.
Water quality does diminish from the confluence
of the Ruati ti and the Manganuioteao Rivers do.wnstream. This is due to
the relatively high silt content in the Ruatiti Stream.
The riparian
strips downstream from this point, however, remain stable.
The riparian strips on the Manganuioteao River are very diverse.
features range from cliffs to fertile river terraces.
The land
The vegetation
'
clothing the riparian strips is also diverse, ranging from beech to lowland
forest.
There are many signs of man alteration with the occurrance of such
vegetation as pasture and silver wattle groves.
The riparian vegetation on the Manganuioteao River is largely. mature and
unmodified.
The retention of this vegetation is one reason why blue duck
favour this river so much.
The vegetation offers shelter and security for
the bird.
Riparian strip dive.rsity on the Manganuioteao River contributes to the
intrinsic value. , The intrinsic value must further increase if the strips
are protected.
8; ...
S U R V E Y I N G
4.
4.1
Method
Surveying of the riparian strips was carried out between August
~Jra
ana August
31st 1988.
Surveying was carried out from the adjacent road where this was
possible.
A raft was used for the majority of the surveying, giving access to
the more remote riparian strips.
process and
~~lowed
The raft also streamlined the surveying
surveys to be taken from a
'blue ducks eye' point of view.
Each of the riparian strips' survey boundaries were determined by the change in
vegetation.
A new riparian strip suivey was carried out where one type of
riparian vegetation gave way to another.
vegetation types are easy to separate.
into 135 separate surveys.
Changes in vegetation are distinct and
The riparian strips were broken down
The length of the strips range from 100 to 2000
metres.
Each riparian strip width boundary was determined by how far away the adjacent
land use was.
The maximum and minimum width of a vegetation strip was measured
from mean water level.
~I
Vlf-.
FIGURE 1 - AN EXPLANATION OF RIPARIAN STRIP WIDTH MEASUREMENTS
9/ ...
The measurement ran across the lie of the land to the edge of the adjacent land
use.
Due to the time restriction, measurements taken were an estimate only and
should not be taken as completely accurate.
Vegetation surveys were kept simple because of the large
land area that
had to be covered and because of the limited surveying time available.
The
vegetation strip survey sheet used allowed not only for simplicity but also
consistancy ..
A set standard developed throughout surveying from the use of this
simplistic and concise survey sheet.
A photograph was taken of most riparia.,n strips to clarify oach survey.
survey sheets have a corresponding photograph attached.
Most
Some ourvey sheets have
no photographs because one reel of film failed to develop.
The surveys rate each riparian strip on
v~getation
condition, vegetation
coverage, the native/exotic species ratio, hrnwsi.ng level, the main plant
species present and whether or not fencing is desirable.
4.2 ·
Surveying Sheet Explanation
A full explanation of how the survey sheet has been filled out and should be
interpreted is given as follows1
Date:
The date in which a particular survey was carried out.
Sheet Number:
This number corresponds to the riparian strip number marked
on
the accompanying cadastral maps.
1. 1:10,000 Map No:
The file number of the cadastral map this particular
riparian strip can be marked or located.
2.
Stream Name:
3.
Aerial Photo Number:
The name of the stream or river the survey was taken on.
strip can be found on.
The file number of the aerial photograph the riparian
io; ...
4.
Owner's Name:
than one owner.
,who owns the r1parian strip being! surveyed.
Some surveys can be marked
1
S.58'.
Can be more
This means the owner of
part of the riparian strip is the Crown and is administered under Section 58
of the Land Act.
5.
Aspect:
The direction the riparian strip faces, using the river edge as
the forward facing edge.
6.
Slope:
river.
The angle the riparian strip is in relation to the surface of the
For example, if the riparian strip was a cliff rising perpendicular from
the waters edge it would have a slope described on the sheet as '60.+ 1
7.
Width of Strie=
The shortest and the longest distance from the waters
edge to where land use changes.
Where
~here
is
no
•
On some ripariah strips land use does not change.
land use change that can be visually seen from the surface
of the river the maximum distance is marked as being infinite.
8.
Fencing:
Good
fencing is totally stock proof.
The fence is in a good state of repair and
will require no maintenance in the near future.
Moderate
fencing is still stock proof but holes and gaps exist.
there will be a hole big enough for stock to get through.
Occasionally
This fence is easily
fixable but if left unattended will deteriorate.
Poor
fencing is not stock proof.
Much maintenance will be required to make
stock proof.
Absent
fencing is no fencing on the riparian strip.
Each survey sheet gives a short statement saying why fencing should or should
not be required.
Often suggestions are made as alternatives to fencing.
9.
The survey sheet lists 14 different types or classes of
Vegetation:
vegetation.
A cross is made on the survey sheet beside the type or types
of vegetation occurring in the surveyed strip.
The letter 'D' often written
beside a vegetation type refers to the vegetatation type within the surveyed
strip.
It means that the vegetation strip is covered by over 50% of that
particular vegetation type.
If more than one 'D' is written then the
vegetation types with 'D' beside them occupy an equal amount of ground and
together they are dominant over the other vegetation types.
The types of vegetation listed on the surveyed are defined as follows:
Pasture grazed - Grazed paddock.
Pasture ungrazed - Paddock that has not been grazed for some time.
grass is full of weeds.
Often
11/ ...
Shrubland - Plants not more than three metres high of both native and exotic
varieties.
They do not cover more than 80% of the surveyed riparian strip.
Scrub - Plants not more than three metres high of
bot~
native and exotic
varieties, covering between 80 and 100% of the riparian strip.
Podocarp Dominated - The occurrance of. the 'podocarp forest' species, such
as Rimu, Totara, Kahikatea and Rewarewa.
These trees can be in any stage
of development.
Cliff Dwelling - Plants growing on a cliff not more than one metre in height.
Cliff Dwelling is made up of fences, flaxes, mosses, liverworks and orchids.
It can be a combination of all these or one particular type.
Tawa - The occurrance of tawa within the riparian strip.
Can be in any
stage of development.
Kamahi
The occurrance of Kamahi within the riparian strip.
Can be in any
stage of development,
Red Beech - The occurrance of red beech within the riparian strip.
any size.
Can be
A rare occurrance in the overall study area.
Black Beech - The occurrance of black beech within the riparian strip in any
size or shape.
- The occurrance of beech trees that are the result of a
cross pollunation between red and black beech species.
identify.
Very difficult to
Some might occur in various places but are identified as red or
black beech.
Wattle - The occurrance of wattle of any size.
Very common on the riparian
strips.
Wetlands - An area of swamp - like vegetation.
Did not occur on any of the
surveyed riparian strips •.
Other - The notable emergence of any other species found on the riparian
strips.
10.
Such species are Poplar, Willow and Karaka.
Canopy Species Represented in Understorey:
This indicates whether or
not the plants or trees that form the vegetation canopy occur in the
understorey.
More often than not a lack of canopy species in the understorey
means that browsing is occurring.
Four vegetation levels are looked at when assessing the
vegetation condition.
These are as follows:
Canopy - is the tallest plants or trees occurring in the riparian strip.
actual height does not matter.
The
For example, with a riparian strip of grazed
12/ ...
pasture the canopy would be the uppermost blades of grass at a height of, say,
60 centimetres above the ground.
With a riparian strip of wattle the
canopy would be the tallest wattles occurring - say 15 metres.
Sub Canopy - Contains the plants which reach a height of between 60 - 80% of
the canopy height.
Understorey - Contains the plants which reach a height of between 30 - 60% of
the overall canopy height.
Ground Cover
overall
Contains the plants which reach a height of between 0 - 30% of the
canopy height.
The condition of each of the above strata is rated as being good, medium,
poor or absent.
These ratings are defined as follows:
Good - The strata is undamaged and in healthy condition.
There are no holes
in the strata and no natural or man influenced damage.
Medium- Some evidence of damage but the damage is repairing itself.
The
strata still looks healthy apart from minor blemishes.
Poor - r!fuch damage l)as occurred or the strata has not developed or is developing.
Gaps in the vegetation strata are very obvious.
Damage is not repairing
itself.
- The strata does not occur in any shape or form.
12.
Length of Strip Covered By this Sheet:
river bank of the vegetation strip.
The length along the corresponding
This measurement follows the flow of
the, river and is not made 'as the crow flies' from the start of the riparian
strip to the end.
13.
for.
14.
Adjoining Land Use:
What the land adjoining the riparian strip is used
This land may be any size from a road to a national park.
Bird Species Noted:
The occurrance of any bird in the riparian strip
not normal or typical of the area.
15.
Types of Farm or Feral Animals Present:
in the surveyed riparian strips.
An indication of any animals present
Nothing is filled in if there are no
animals seen on the riparian strip, even if there is obvious sign that an
animal has been present.
16.
Photograph Taken:
An indication of the availability of a picture for
later cross reference.
17.
Observer's Name:
carried out the survey.
The name (names) of the person (people) who
13/ ...
5.
AN INTERPRETATION GUlDE.FOR }: 10,000 CADASTRAL MAPS
The 1:10,000 cadastral maps are designed to give an overall indication
of the vegetation types found on the Manganuioteo River riparian
strips.
The maps display the study area starting at the upstream
boundary.
They work their way downstream in sequence.
Each map focuses exclusively on the riparian strip.
strip is shown in bold capitals.
The owner of each
While every effort has been made
to ensure that the owners of the land they are associated with are
correct, some areas may have changed owners or were not cited correctly
when the owners were established.
Each surveyed riparian strip is divided by arrows and numbered accordingly.
The colours indicate the dominant vegetation type or types for each
riparian strip.
type.
These colours are only an indication of vegetation
Where the shading occurs on each riparian strip is not
necessarily the place in the strip where that particular vegetation
is found.
It merely indicates that this type of vegetation is found
in that particular riparian strip.
Section 58 strips are also shown on the maps.
exist.
They are just 'paper' roads.
Some roads shown do not
14f ••.
6.
RESULTS AND RECOMMENDATIONS DISCUSSION
The study area can be divided into two parts.
One .part is the upstream
section, from .the Ruatiti River/Manganuioteao River confluence and the
other part is the downstream section from this point.
A.
THE UPSTREAM SECTION
The riparian strips on the upstream section are dominated by scrub.
scrub is largely native and mostly in reasonably good condition.
This
Other
notable types of vegetation are cliff dwelling, wattle, podocarpftawa/
kamahi forest and beech.
It is interesting to note that, apart from
the odd tree, the beech species end at the scenic reserve just down
from the Ruatiti Domain (Section 51).
The occurrance of the marked Section 58 strip on the upstream.section of
the river gives the Conservation Department the legal power to exclude
grazing and other vegetation destruction activities from these riparian
strips.
Such action, however, would most certainly cause rifts between
the land owners and the Conservation Department.
Such action from the
Conservation Department would need to be executed with a great deal of
diplomacy.
There are several riparian strips on the upstream section of the river where
the native bush cover is in very good condition.
These areas need only
small improvements to make them fully stockproof thus encouraging secondary
regrowth.
They should be given top priority in stockproofing because
of their condition and ease to fix.
These areas are identified as
follows.
1.
Section 1 and 3:
The vegetation condition here can easily be improved
by fixing existing fences and adding fences where needed on the boundaries of
the vegetation strips.
Animal exclusion would encourage vegetation undergrowth
greatly improving the overall vegetation condition.
2.
Section 6 and 7:
The fencing condition here is not as fixable.
Fencing, however, would greatly enhance the quality of the vegetation
coverage.
15/ ...
3.
Section 16:
A small amount of fencing down each side of the riparian
strip, combined with the repair of existing fencing, will totally exclude
it from browsing animals.
4.
38:
The Ram Paddock.
Existing vegetation is mature
forest, but the undergrowth is heavily browsed.
needs the most immediate action.
This riparian strip
The sooner it is fenced the sooner the
vegetation will return to its former excellent condition.
A ring fence
around this riparian strip would be relatively cheap and would greatly
enhance regenerating, second growth vegetation.
This section would
benefit with the enforcement of a QEII covenant on the strip or,
failing this, a possible management or leasing agreement between the
owner and the Conservation Department.
5.
Section 37:
Once again the extension to already moderate fencing
would enhance and improve an area of excellent vegetation.
·6.
Section 42:
strip.
7.
There is already good fencing around the top of this
Fencing down each side would totally exclude stock.
Section 46:
Ruatiti Domain.
would really enhance the undergrowth.
browsed.
An area where exclusion of stock
Most existing regrowth has been
As this paddock is fenced and publicly owned browsing would
be easy to exclude.
8.
Section 49:
with fencing.
Another important vegetation area that would benefit
The existing canopy is excellent but the ground - cover is
non existant due to heavy browsing.
A fence across the peninsula would
be relatively inexpensive and very effective.
While these areas are seen as the most important areas for fencing in the
upstream section, the ultimate goal the fencing and/or protection of the
whole upstream riparian strip area by covenant,
other means.
leasing, reserving or
The upstream should be given priority for protection over
the downstream section because of the blue duck presence.
The riparian strips on the upstream section, which is the boundary of blue
duck presence1 are more sheltered, gorgy and less exposed to the sun than
the downstream section.
The vegetation, despite being browsed in many
16/.~.
places, is overall tall and dense and a miKture of native and eKotic.
Generally the canopy is in good condition and must contribute to the
favourable blue duck habitat.
The enforcement of riparian strip
protection would help stabalize and perhaps increase blue duck numbers
on the upstream section.
B.
THE DOWNSTREAM SECTION
The downstream section is dominated by cliffdwelling, scrub and shrubland
vegetation.
This t¥pe of vegetation reflects the unmodified nature of
riparian strips on this part of the river.
were once browsed or farmed are now
Many riparian: strips that
well advanced into the forest
regeneration process.
The downstream section lacks the large podocarp beech and
taw~
canopy tress
found in the upstream section, although wattle is present in many sections.
In some places, however, canopy, trees are appearing in the regeneration.
The lack of large canopy trees means that the downstream section of the
river generally lacks the shelter and coolness of the upstream section,
which seems to be an essential component of blue duck habitat.
The downstream section lacks any Section 58 strips.
This means that this
section of the river will be a lot harder to seek protection for than
the upstream section.
Consultation between the Conservation Department and
the riparian strip owners will be necessary to develop protection
strategies for the downstream section.
Most riparian strips on the downstream section are being damaged by browsing.
While sheep and cattle are present much of the damage is being done by
goats, particularly from Section 110 downwards.
60 goats were counted.
In one 1km section,
A deal between landowners and the Conservation
Department will be necessary to get rid of the goats. Winstones Ltd, the
owner of much of the land where goats occur, should be agreeable to goat
destruction on their land as it is also in their interest to have no goats.
In general it would be easier and cheaper to do drive out or destroy live
stock in the lower section rather -than fence.
Much of the land is obviously
no longer paying as farmland and is being allowed to revert to bush.
17 I ...
Fencing riparian strips in the downstream section would be impractical and
costly.
The alternative is to remove remaining livestock from these
riparian strips.
C.
IN GENERAL - SUMMARY
Landowners up and down the river now need to be informed of the status of
the riparian strips.
They need to know the benefits stable riparian
strips bring to the wildlife, the intrinsic value of the area and to
their arable land.
The presentation of the riparian strips will
almost certainly happen with the backing of the landowners.
The riparian strips of the Manganu1oteao River contribute much to the
overall river ecosystem.
The wildlife, recreational and intrinsic
values of the river are all enhanced by the stable, relatively unmodified
conditions of the riparian strips.
The upstream section should have
first priority for protection because of the blue duck population.
Particular importance should be placed on those sections mentioned.
Legally the upstream section is easier to protect because of the presence
of designated Section 58 strips.
The downstream. section, while harder to get protected, should not be
excluded.
The removal of stock and to a lesser extent, fencing, should
be encouraged and the landowners should be fully informed of the values
of riparian strips.
This inventory shows the value and feasibility of riparian strip protection
on the Manganuioteao River.
before it is too late.
Action must now be taken to get this protection
......_
175° 10 E
co·
Ruati!i ·
Stm
<
l:il
p::
<
DOWr\IS-r~eArrl
~
::::>
E-<
Ul
l:il
:I:
E-<
39° 2d
s
N
P-o
~
0
1
2km
f
I
19 / ...
7.
OLIVE~
84
)
D
GJ
KEY TO CADASTRAL MAPS
- Land owner's name.
- The index number of the riparian strip.
- Arrow marking the boundary of each surveyed strip.
- Grazed or ungrazed pasture dominated.
- Shrubland (up to 80% cover) dominated.
- Scrub (continuous cover) dominated.
D
- Cliff dwelling dominated.
- Podocarp dominated .
- Tawa or kamahi dominated .
- Beech dominated (various species)
D
- Wattle dominated.
- Othe r dominated .
25
sao I ~·a.
80.9371
501"3887
MonqQm•• aliZo
9
Sc.enu.:. Ras<&rV&
80.9371
FOREST
T A T E
Gaz 1922
p t 19'
5013887
Pt 20
501
580)
32
Pt 21
380.7080
31
41. 6826
RICHARDSON
so 22781
so 28717
•
l
~
.:...
~
724 . 000
Pt 8
23
80. 9371
DOC
3
80. 1277
F
Gaz 1922
R E S T
p 1511
~-
30
4
14.5181
79.7230
~
.
RICHARDSON
..::r
15
'-----
80.9371
~
50 1404~
\{)
ct
a...
ct.
14040)
~
~
16
~
50 1:::,800
Pt 2
so
CT 48 2/ 26
14049
- ------- - ___6_8..:._3_1_8_?_ _
722 , 000
~
.....tl.J
50 l4.04q
, 0
f'
19
@
~
80.9371
~
~;.,
501405l
18
50·0)371
50 1405:2
17
81.7464
p t 16
CT 48ti 49
82. 368 7
Road and Bridge
Reserve
~4
53. 6208
43
so
23.8359
22746
50 22 7 4<0
501
14
81.7 465
llUW
5 0 1405 2
3
80.9371
720,000
5014052.
13
80. 9371
so
Vl
14052
rl
~
::;:::;:::.-
?-0
~
-
12
• 9371
so
14052
80 . 937 1
o ,....u_..._... ..,., .._ ,.,_.,..,,M.tmont of Land8 and Survey under
~
-
}00
36
79.6977
so 24335
'23
80.9318
50\4040)
33
75.4232
so 23197
20
80 . 7701
2
101.5761
so
14051
Recreation Reserve
1
0. 8093
1984/
1B
80.9371
Pt . 22
CT 237.' 140
80 . 6665
so
I
,
so
1405:2..
'
-----"""'i';i VliLKERU
8
14052
Pt. 19
80 . 6!33
8
40.6709
OLD~,
501554-7
so
G<;;>~ 1980p .3f.49 ~~~~~
Clas~. ·a~ a
97. 1245
R~. tor
Sc.em·c Pvrpo::.es
i
33
75.4232
SQ 14051
I
14266
so
722 000
L . . R~~­
(8rid9&}
Pt4
15<0·<00
so
6oJ~;.1980p.~2 72
Gf~0/25
23197
14049
(1 · 2.14-0)
. 50 ::4.'3 :2..00
(:2.73·!), .
5014050
WILliAMS
Pt. 3
CT 19A/133 ·
(2)
80.4565
50 !4051
Pt.2
Recreation Rese
1
0. 8093
CT 1921217
79.0907
[
1984/213
I
( 1)
FAHEY
:' t. t
CT 616 / 30
70 . 1370
SO I<C02"3
2.8
so
0.7284
14
so
so 14050
1984/213
so '4° 52 VOELKERLING
Pt. 22
2
CT 237 / 140
4 ·7312.
DP 11300>
80.6665 .
Pt. 4
so 1405l
156.6034
47
5014050
3 1767
CT 460/ 254
, .,,,
r,~n~;'
nnn
L.P. Reservn
<.t.-ec , Jo.nt'"j)
Go.z 1qs2 pZ5 4
so
28216
9
~
.
230 .6708
5015841
~
2
177 . 0499
0
"'
\f:)
\.0
Q..
~
so
15847
12 4
~
ooo
20
161.5100
so
30349
SO 12724 Tope
SO 12586 Tope
\
'
~
4
149 . 5313
~
230 · (;:,1013
5015547
9 50 1584~
.....
'
WAIMARINO
COUNTY
103 . 3971
~~·
__....~....-so 12sss ~
.~--
so 12750
so
16194
~
DOC
s
_...,~.,..ikiariki
so
~
~
15847
51
Gox. 1950p 3649
(.la5sif,·ad
~
a5
a
A<ZS
for Scanic Pvrposq.s
~
·----~
-~ ~
WEST
\.
~- l~:., ft~\&V~l\~T
~fW:JI H
q;6f111ttlftJ
~ llf~ ,\t
~
3.J3B~B2..
2..2. :l- · 7502.
-
-
ffi
3J2
ML~8"'32
- ---
~ /!ffillill
\
I
,.
722 000
\
1 1a~ t33
u 4:Jti5
~
so
5_
Rl
c
!:!:
=t
Q,
m
o
~ ~
co(!)
-Pl
~.,g-~
-· -< ...
I'D
5-JJ~O
0
c
14050
;::; 0
loll
-
I'D
"C
-::t:-~
'tl ~~3I'D
Ill
::! :D './) co
~
mc a
urcn1'1 <
o
"'
·'·
o
en
:I < Q c:
(Hol ·~74 ?J)
:OJ ·~:
g,~P::J
f!'P
"
ll
0 0
1405A;
~
'-.ijj ~
z ::
::r Rl
3.J 3A ~"<J 38.lC2
46 . 5622
ovoc:-v
JJ
n~ /"
,.,.,
~
•
~
WEST..
"-......._
~
V§
.
3.13B::l..B2.
\I
--t
2..1?..·
ML~8"32
.,_
--
~ ITi~4x3~~". _~~~. .~ ;,_ .
Q..
q:
t
333
I.
,. 9764
- 3410
---
-
~
3H 1
75~')..
A
~
~
(1<01·
.f
\
'-
55
ML 3832
ML 349
I.
I
I.
.
74 ?.>)
•
62
I.
I
3H4
45 -0861
. ML\3410
T
~~-LARSON
14 · 5~87
ML~8:3l
3~3-A
59WRIGHT
161. 6846
- I
M L30)4-4
3H30
.
655
67
ML 3410
ML 3944
,
Scale 1:10 000
Ar eas in hectafos aro shown thus
2. 0432
Areh lc ~:. tha11 one hectare are expressed thus
0 . 4552
WhiCh is Bllual to 4552 square metres.
Pubi.Uihed by the Department of l.,and& and Survey under
thf authority of the Surveyor General.
CROWN COPYRIGHT RESERVED. REPRODUCTION
PROHIBITED without permlasion of the Chief Surveyor.
6 Jl5
Cl
520/2·:
rj\
t0
0
...____
~
~
................................................................................. .......
Re-Order Filemaster '' D''
SELF-ADHESIVE Pli'l
Patent Number 137841
0
0
0
Published by the Department of Survey and Land Information
under the authority of the Surveyor General.
CROWN COPYRIGHT RESERVED. REPRODUCTION
PROHIBITr.r• without permission of the Chief Surveyor.
6 2D5 . DOO
INDEX TO
AD JOIN ING SHEETS
=
=
=
Lr>
=
c.o
so
0
<D
14
"'
LARSON
72
~24~7~--~
~r
3G
292 . 5877
ML 1406
S2u 1. 2 S20 2. 2 S20 3 . 2
I
\'·
ML ?_0)8G ·
1a
130 . 8095
S l O I 1 S20 2. 3 S20 3. 3
ML
3H
96
123.
\
3K 282A
ML3
3K2828
3 I. 059 6
29. 036 1
I
so
1658
LARSON
S20 1. 4 S20 2. 4 S20 3. 4
3E1
- ·----- ----
94
~ ill] ill ~ [ill ~
Pt 3K283
I
.
CT 460/ 222
213. 8 20 7
ML 2g8co
I
.
[}{]~00~
I
3K2A
Pt. 3K281
60/ 1238
30 . 4374
I
47. 99 57
I
ML 2473
c.r S0/353
{ :2.71 · 15"~)
Ml
~Q.a
i ID .8253
ML505B
~
/
3Kl
I 3LtA1
ML208CO
.I
MW~
pt 3LIA2
H . 4624
3L1B
200 . 0563
Ml 450)?
I
I
I 104
I
ML 5088
ML 3592
I
ML ~5q2_
Pt
I
3~5
CT 456. 260
28 1 1896
•
•
•
M
PRtNCE
'
0
·
- -·
-
-------
··-·- - - ·-
-~
i
108 1
I
ML 1591
ML 2473 8
-··
- -~.
---· , -
ML 2473
1o1"1~
·.,_
I
INSTONES!
~
. - . -
"
BAKK
'
'"
ML 350)2
3M4
71. 01 47
~- . -
.I\\ n
n
61 0923
"~
7 16 000
s~o/t-3
5028553
so 19534
ML 5088
ML 3592
OWEN
ML
Pt
CT
-t--#---
WINSTO ES
30
I.
t47 . 3055
II
-
~~_gq:E
I
I
3~5
45~/ 260
2BL~SD
-----~---~
--
I'
M L 2473A
ML 1591
ML 2473 8
I.
ML 2473
ML 3592
ML 350)2
3M4
UAKK
71 . 0147
3M3
n
u.
~
3M2
3M1
1\ 0147
~ -
80 .9371
61 0923
ML
92
716 000
~I
Pt 8
~
•
688.6379
Pt3E3
5014G02
CT 237 176
-- . I
',
134. 1912
~
0
10
()
T"
so
I
0
422 .7300
~
I""
M L 2.30)7
-p_
33135
I
3T
' 40 . 4432
ML 2473A
·-·-·-·-·~-· ·-·~
~
·-·-~­
so 14692
\
~
~
so 17570
716 , 000 .
/ ,I'
30
.·
147 . 3055
I
I
M L 247-A
ML 2473 A
ML 1406 A
ML 1406
3C
290. 1596
f'/1 L /._~1- 7 3 A
-o'
0~
~
12tf~
WINSTONES
I
122
mllo) ~.
lo)
r
,-~
.
,.
1
~
1
144 . 4727
126
I
ML 2A-73A
3N2A
144 . 1692
I
ML}2682
I
Jr
144 .
ffJfiP II
1?~0 /7!·3
ML 2473 A
so 17570
ML 1406A
000
134~~
.
1406
3C
ML 2473A
290 . 1596
39
3B
144.4727
ML2473A
6 re kahi katea
3A1A
142. 3861
ML34-l5
714 . 000
3At8
130.0558
MI.. 3lt!5
Ml_ 3415
3A2
16581
155. 7027
ML34-15
AI MARIN
129
30
,,.. n
so
so
so
so
~
I
15268
12726
12727
:?.6721
;:-...
~
~
~
I
I
155 . 7027
ML3Lrl5
28
8
2~·1127
SOIG625
Wtianganui
Gaz
.129
National· Pari<
1986
so
p
506 ~
17570
-
134
2
8 \. 837 5
Whanganui . Nationa
Park
caz 1986 p 5 62
so
166
712,000
3S
291. 1510
A
ML24-73-
ML 1406 A
i
__
---
R i:ver
ML 1406
...
...-'
TARANAKI
._
___
---
NO . ClSTRICT
ML 3277.
-----·--.scal e 1:
-:
Ar us in
Hact a'rps'
to,ooo
a e
~ hown thus
: 2'.0 ~ 3: .
Published by th~·De,J!tantmem .et9urvey. ·arui~ L.nu lnftJrrTwt!n
·.nder the authority of the Surve fcn::G~erat:; '
CROWN COP~St~:tfl'Cft&SEAV Effi '.R'EP.M · Ot:JCTIO('qc
.a, r. as tes s. tllan Qnl'
lfllrch ic
J!U"I
ec He :'He expressed thus
0 . ~5t7 .
• a ~55J ;quare rutres.
Tr-ig ,Plan \26BS
\272~
12.54q
12538