Consents Administration Section
Environment Canterbury
PO Box 345
CHRISTCHURCH
July 2006
Dear Sir/Madam,
Name of submitter: New Zealand Recreational Canoeing Association (NZRCA)
The NZRCA is the national representative organisation of canoe/kayak clubs and recreational kayakers throughout New Zealand. The NZRCA is an incorporated society and is affiliated to the NZ Canoe Federation, which is in turn affiliated to the International Canoe Federation. The NZRCA has delegated authority to represent the NZ Canoe Federation on conservation/access issues.
This is a submission on applications from Central Plains Water Trust for various resource consents applying for water abstraction and use within the Central Plains area.
We oppose the applications in
their entirety, and particularly:
·
CRC061940: to divert water in the Rakaia River
towards the intake structure
·
CRC021091: to take water from the Rakaia River
for water enhancement (sic) schemes in the Central Plains area
·
CRC061941: to divert water in the Waimakariri
River towards the upper intake
·
CRC061943: to divert water in the Waimakariri
River towards the lower intake
·
CRC061972: to use water from the Waimakariri
River (lower and/or upper intake)
The reasons for our opposition are set out in the following sections of our submission. We provide additional information emphasising some of the key issues specifically facing recreational paddlers in terms of the Central Plains Irrigation Scheme.
We seek the following decision from the consent authority: Decline all applications.
We wish to be heard in support of our submission. We would consider presenting a joint case at the hearing if others make similar submissions.
We would prefer to refer to the scheme in question as the Central Plains Irrigation Scheme, as opposed to the Central Plains Water Enhancement Scheme, since in our view we do not believe the scheme to exhibit any potential for enhancement of a public water resource.
Yours faithfully,
Kieron Thorpe
Conservation Officer, South Island
New Zealand Recreational Canoeing Association
P.O. Box 284, Wellington
conservation@rivers.org.nz
The proposed Central Plains Irrigation Scheme will
significantly detract from the paddlesports value of
the Waimakariri and Rakaia Rivers.
The proposed reduction of flow will impair the value,
navigability and safety of the river environments. The intention of the scheme
is to remove approximately 45% of the median flow of the Waimakariri river, and
nearly 13% of the median flow of the Rakaia. Such a massive reduction in flows
will have a huge affect on both the Waimakariri and the Rakaia from a paddlesports perspective.
The scheme was initially presented as a water harvesting
scheme that would skim water from the river during times of flood, and was
granted requiring authority status on that basis. Since requiring authority
status was secured, it has become increasingly obviously that the scheme is
intended to be a primarily run of river system, drawing water from the river
during times of low to medium flows. We object strongly to such a total ‘about
face’ of the entire abstraction concept.
The construction, operation and maintenance of water
abstraction works and irrigation canals will impair the value, navigability and
safety of the natural river environment. The preliminary drawings of the
abstraction works show little concern for the safe passage of paddlers and
other non-combustion powered river users. The proposed abstraction systems
will, beyond the drastic loss of amenity, present a very real safety risk to paddlesports and could easily result in loss of life.
Three Assessments of Environmental Effects prepared in 2001
(2) and 2006 (1) make little mention of the widespread use of these rivers for
canoeing and kayaking, and little mention of the many severe detrimental
effects of the proposed scheme on paddlesports.
The Assessments of Environmental Effects released in 2001
also state that “canoeists/kayakers... require a
minimum water depth of...0.1 metres”. This is a categorically wrong statement and
illustrates the extent of ignorance exhibited by Central Plains Water Limited
and its consultants on paddlesports.
Furthermore, CPWL has made no attempt to improve its
knowledge of paddlesports issues.
Consultation with the NZRCA, Arawa
Canoe Club and the Whitewater Canoe Club (two of the
largest such clubs in New Zealand) has been non-existent, despite a recent
press release dedicated to grand claims of multiple recreational benefits the
scheme will deliver. This press release detailed a specific, high profile
recruitment by CPWL "to talk to a range of recreational groups to find out
if there are any opportunities that could be worked into the final design of
the irrigation scheme.” As of this date, and to our knowledge, no such talks
have occurred.
We therefore have no choice but to conclude that CPWL has no
intention of either educating itself on paddlesports
issues, or of undertaking the slightest investigation into recreational
opportunities, let alone actually developing any.
Furthermore, were we to believe CPWL’s
stated intentions, any recreational mitigation suggested by the Assessments of
Environmental Effects is nevertheless vague, ill-informed, irrelevant and quite
clearly the result of very little genuine deliberation.
The suggestion that the recreational potential of flatwater environments such as the proposed irrigation
canals and storage lake is sufficient mitigation for the destruction of a
natural swiftwater resource is frankly insulting to
most river sport enthusiasts.
The Waimakariri River (Cold,
Rushing Water) is the most heavily used river for recreation purposes in
Canterbury. Its proximity to Christchurch has ensured its popularity for many
years, though to have been first used for paddlesports
in the 1880s. The Rakaia River has also been paddled since the 1880s.
Both the Waimakariri and Rakaia are braided through the
Canterbury Plains and as such offer a special paddling experience. Their
constantly changing gravel beds can completely alter the course of the river
overnight. This, couple with the relatively benign nature of a typical rapid,
adds greatly to their value as training environments since it is a stark
reminder to all its paddlers to heed one of our fundamental maxims: “every trip
is on a new river”.
The Waimakariri and Rakaia rivers are best described as swiftwater
environments as opposed to whitewater environments. Swiftwater rivers can be defined as exhibiting strong
currents but few violent and/or highly dangerous rapids. These rivers are ideal
learning environments, as they exhibit relatively swift currents and numerous opportunites to practise the fundamental skill of crossing
from slack water to fast water and vice versa (eddy turns), yet few real
dangers such as boulder sieves, undercut rocks or ‘keeper’ hydraulic jumps.
Their proximity to Christhchurch
and difficulty level of Class 2 (on a scale of 1 to 6) makes the Waimakariri
and Rakaia rivers perfect environments for developing our future athletes.
Should the considerable amenity value of the Waimakariri and
Rakaia rivers be compromised, the nearest rivers of similar nature are the Rangitata and Waitaki. The State
Highway bridge over the Rangitata is approximately
120km from Christchurch. The State Highway bridge over the Waitaki
is approximately 220km from Christchurch.
The demands of the proposed irrigation scheme are in direct
opposition to the needs of over 1000 citizens of Christchurch alone.
Many people paddle on the Waimakariri purely for fun or as
part of a training regime. Numbers naturally increase during the summer, a time
of naturally low flows and high irrigation demand.
Given that in Christchurch alone there are over 600 members
of canoe and kayak clubs and up to 500 individual paddlers, it is estimated
that approximately 100 of these would paddle the Waimakariri at least once a
week. Therefore an estimated five thousand or more personal river experiences
would be threatened annually.
The AEEs lodged by CPWL make no
attempt to estimate the scale of popularity of the Waimakariri and Rakaia
rivers among the paddlesports community.
The Coast to Coast is one of the most well known multisport events in the world. It is held in February and
has been running annually since 1982. Approximately 1000 competitors, from all
over the world, come to kayak 67km of the Waimakariri River. The kayak course
begins at Mt White Bridge, passes through the Waimakariri Gorge, and exits at
the Gorge Bridge.
The AEEs lodged by CPWL make no
mention of the Coast to Coast Race.
The ‘Waimak Classic’, run by Arawa Canoe Club, is held in December and has been running
annually since 1989. On average, it attracts approximately 150 competitors. The
course route is the same as that taken by the kayak leg of the Coast to Coast
Race.
The AEEs lodged by CPWL make no
mention of the Waimak Classic Race.
The Whitewater Canoe Club Brass
Monkey Race is an annual kayak race series held on the Waimakariri. Five races
are held fortnightly throughout June to August of every year since 1989. Up to
150 and 200 competitors paddle a 12 km course from the western end of Coutts Island Road (approx. 2470005E, 5751000N NZMG) to the
State Highway 1 Waimakariri road bridge at Bridgend.
The AEEs lodged by CPWL make no
mention of the Brass Monkey Race.
Numerous coaching organisations
introduce beginner kayakers and multisport
athletes to swift water on the Waimakariri.
The AEEs lodged by CPWL make no
mention of the use of the Rakaia and Waimakariri rivers for paddlesports
instruction.
The proposed irrigation scheme aims to significantly reduce
the flow of the Waimakariri and Rakaia rivers, reducing the median flow of the
Waimakariri by 45% and the Rakaia by 12%. This is a dramatic reduction in the
value paddlers place on the river, and completely unacceptable to our sport.
Paddlers value the variety of experience that a range of
flows brings. A popular paddling maxim is ‘every paddling trip is on a new
river’. Every trip, even on the same river, is a new experience. bringing new
choices of routes or ‘lines’ through a rapid, new rapids in their entirety, and
a different, valued experience.
Nowhere are these facts more starkly obvious than on braided
gravel rivers such as the Waimakariri and the Rakaia.
The ‘hydrograph flatlining’
proposed by CPWL is a direct reduction in the variation of the natural flow
regime of the Waimakariri and Rakaia rivers. This is also a direct reduction in
the variety of experience valued by paddlesports, in
terms of the river’s flow, the choice of routes through the various braided
channels, and the ever-changing nature of the braids themselves.
The Assessments of Environmental Effects submitted on the
Waimakariri and Rakaia intakes in 2001 state that a kayak requires a draft of
0.1m. We dispute this figure for the following reasons.
Kayak and canoe designs come in many shapes and sizes, from multisport race designs in excess of 5 metres long, to whitewater ‘play boats’, many of which are less than 2
metres long.
Larger paddlers in smaller boats can still require drafts of
over 200mm. When held on an edge (much like skis and surfboards, shorter kayaks
and canoes are designed to be dynamically steered by ‘edging’), a paddlesports boat can attain even deeper drafts.
Touring and racing boats, although longer, are designed to
cut through the water in order to sustain higher speeds. These boats are often
much thinner than shorter designs and as such can require depths of up to 250mm
merely to float.
Many longer designs such as touring, sprint and multisport boats feature a rudder. which is required for
safe and effective manoeuvrability.
In most cases, the rudder is hinged such that it will not
break in shallow water. However, water that is shallow enough to cause the
rudder to hinge up will result in impaired manoeuvrability for the kayak. This
can result in:
·
grounding, which can damage the hull,
·
flipping, which in shallow water especially can
force the paddler to exit, or ‘swim’
Rudders generally require depths of between 200 and 300mm.
Most ‘whitewater’ style paddles
have blades approximately 450mm long. Racing wing-style paddle blades are
longer still, up to 550 or 600mm. A correct forward stroke employs a near
vertical blade, fully planted in the water. To effect maximum power and provide
assurance feedback to the paddler, the power hand is often submerged.
A paddle can reach depths of up to 0.7m.
Most downriver paddlers are capable of self-righting their
boats in the event of a capsize, using the well know 'eskimo'
roll procedure. During this manouvre the paddler
reorients his or her body and paddle against the side of the boat and performs
a combined sweeping stroke and body rotation to right the boat.
Were the paddler's freedom to move around underwater denied,
the paddler could be forced to swim, incurring safety risks and generally
lowering the paddlesports value of the river.
When upside down and attempting to reorient the paddle into
a roll set-up, a paddle blade can reach depths of up to 2m.
Further to the points made above, downriver kayaking and
canoeing is a sport in which the paddler moves the boats by harnessing the
energy of the current, using the combined interaction of the paddle, boat and
current. This is analogous to a sailor using the sail and keel of the vessel to
harness the wind. Sailors, as a rule, prefer to sail where the breeze is brisk
enough to provide a degree of excitement. Downriver paddlers view the current
of the river in exactly the same way. Depths that prevent a fully submerged
paddle are useless in these terms. As an example, multisport
and downriver paddlers make little use of the Avon river, where the current
velocity is far below the terms of reference of a downriver trip.
Furthermore, a phenomenon known as 'bottom drag' occurs in
channels less than 2m deep. Bottom drag is caused by the subsurface interaction
of a boat's bow and stern waves against the channel bottom. To prevent bottom
drag occurring to racing paddlecraft, the
International Canoe Federation recommends a minimum channel depth of 2m for
kayak and canoe races.
The banks of the Rakaia and Waimakariri are populated by
willow trees and other types of overhanging vegetation. The banks of the
Waimakariri also feature flood protection and erosion control works. These
works include concrete blocks with protruding steel bars, as well as timber
posts and other such objects.
Bankside vegetation and flood
protection works can form what are known as 'sieves' or 'strainers'. These
present a significant drowning risk to paddlers. Once caught up in a sieve, a
paddler is generally flipped upside down, from which it is essentially
impossible to perform a self rescue roll. The paddler is invariably forced to
swim, whereupon the swimmer is forced further into the bank and under the
trees, branches, steel bars, etc. by the current. From here, neither escape nor
rescue is an easy undertaking and drowning is a very real possibility.
Lower flows in the river narrow the navigable channel width,
especially at bends, where sieves and strainers are most often found. These
channels become exponentially more difficult to navigate, especially in longer
race and touring boats, with an exponential increase in the consequences of a
failure to avoid the hazard.
An important function of medium to high river flows is to
transport sediment from the mountains to the sea.
Reduced flows will result in a major effect on the sediment
transport regime of the river. More sediment will be deposited on the bed and
the bed will rise from its natural level. This will result in bank erosion and
subsequent flooding. In kayaking terms, localised sediment deposition will
directly affect the navigability of the river.
The argument that sediment transport is principally effected
by large floods is incomplete. Smaller floods have an effect too. Were the
ability of the small to medium floods to move sediment undone, then this would
leave more work for the large floods to do. The large floods can only do so
much work, and there is a risk that they will not be able to address the
deficit.
Furthermore, the reduction of average flows and frequency of
smaller floods or ‘freshes’ will enable greater encroachment of riparian
vegetation, which will bind the bankside soils and
make them less susceptible to movement. Once established on sediments that were
once moved by the freshes, this vegetation will hinder the effect of the larger
floods.
It is our contention that permanent alterations to the
morphology of the river and subsequent increases in bankside
vegetation would firstly enhance the risks presented by sieves or strainers as
previously described, and secondly reduce the value of these rivers as a
paddling experience.
River training, or the practise of diverting the river into
one channel that will deliver water to the primary intake, is detrimental to
the value of the river in terms of paddlesports. The
natural river bed is essentially destroyed for the length of the trained
section. The downstream outlet of the diversion channel can become shallow,
since the trained section is usually designed to keep the water level high
enough to allow irrigation takes to continue. These outlets may be difficult or
even impossible to navigate.
Narrowing the river at these sites also poses safety risks.
Passing paddlecraft are forced closer to the
irrigation intakes, which as a rule are something that paddlers try to stay
well away from. One of the proposed sites on the Waimakariri is used as a base
of operations for a commercial jet boating company. Large passenger jet boats
arrive and depart this site on a regular basis during the height of the
paddling season. Forcing paddlesports and jet boats
to share the same narrow stretch of water would constitute a significant safety
risk to all parties.
Furthermore, large plant such as excavators would be
required to operate in the same area to keep the diversion channel in order.
This increases the risk to paddlers still further.
Siltation in the river is a common
side effect of river training works. Silt is an eye irritant and causes damage
to paddlesports clothing.
The drawings of the primary intake structures developed thus
far indicate multiple submerged radial gates built into a headwall. There are
six radial gates 2.5m wide by 1.0m high. We calculate that for a capacity of 20
cubic metres per second (half the take proposed from the Waimakariri), the
average velocity through these submerged gates would be 1.33 metres per second,
or nearly 5 kilometres per hour.
In reality due to friction and boundary effects the maximum
velocity at the orifice is likely to be much higher. Furthermore, were these
structures designed to draw more than half the total take (such that the
capacity of the scheme would be less impacted by ‘shutdown’ maintenance at one
intake site), the velocity will be greater still.
In short, such velocities will create suction effects that
few kayakers or canoeists would have much hope of
overcoming. The likelihood of entrapment and subsequent drowning, should a
swimmer, or even a fully afloat and in control paddler, find him or herself in
the vicinity of one of these structures, is terrifying.
These dire prospects are exponentially worsened by the fact
that the river bed itself would be ‘trained’ to divert the maximum flow
possible directly towards the intakes, and that the overflow spillways at the
intake sites will be difficult, even impossible, to navigate.
Kayaks, especially recreational river running designs, are
among the slowest watercraft available. A small playboat
design, when propelled on flat water by the most powerful paddler, is barely
capable of maintaining a walking pace, even for short periods. An intake
velocity that exceeds the maximum sustainable velocity of any kayak likely to
be in the vicinity could result in entrapment.
Gratings present the following hazards to kayakers:
·
Breaching – this is when a kayak is stuck
broadside on the grating. Breaches can occur anywhere on the roll axis of the
kayak – upright, upside down, or with the beam perpendicular to the water
surface
·
Pitoning – in the case
of kayaks with thin bow or stern sections, the hull can become jammed between
the bars of a typical bar grating.
·
Wrapping – either a breach or a pin can result
in what is termed a ‘wrap’, when the force of the water overcomes the
structural strength of the boat and the boat
crushes. Long multisport boats are particularly
vulnerable to this.
·
Forced exit – if a kayaker
cannot free his or her boat from the obstacle from while remaining inside, he
or she must exit the boat.
·
Entrapment – worse still, if a kayaker wishes to exit but is prevented from doing so by
the obstacle itself, then an entrapment situation is in effect. An entrapment,
for obvious reasons, is widely recognised as a kayaker’s
worst nightmare. Entrapment can occur when the cockpit is forced against the
grating in a breach, or when a pin results in the legs trapped inside the hull,
or simply when the force of water against the paddler’s body overcome the padller’s strength.
An engineered hydraulic jump is one of the most dangerous
hazards posed to downriver paddlesports enthusiasts.
It is a smooth, vertically recirculating designed to reduce the energy of the
current within a concrete lined channel, thereby lowering the scouring
potential of the water in the downstream earth lined channel.
Naturally occurring hydraulic jumps almost always have a
weak point somewhere that enables a skilled paddler to escape whilst remaining
in his or her boat. Even an unskilled paddler, upon deciding to swim, will be
flushed underneath most natural jumps and on downstream, none the worse for
wear.
Engineered hydraulic jumps are constant across the cross
section of the channel, without any ‘tongues’ of current breaking through the
feature that an in-boat paddler might try to head for to effect an escape.
Should an in-boat paddler become trapped in such a feature, they are held in
the recirculation zone. In-boat escape is effectively impossible and the
paddler is eventually forced to swim.
The swimmer is now caught in the recirculation zone, which
usually reaches the bottom of the channel, pushed downstream for a few metres,
then back up to the surface only to be drawn back upstream to the interface to
repeat the whole disorienting process.
The only hope of a solo escape is to surface far enough
downstream to be able to swim away from the interface. Unfortunately the
swimmer is generally highly disoriented by the ordeal and does not know when,
or which way, to swim.
Complete exhaustion could be expected to occur within a few
cycles - within ten to thirty seconds, depending on the size and power of the
jump - and death soon after.
The only hope of rescue from a ‘well engineered’ hydraulic
jump is bankside assistance, generally in the form of
a ‘throwrope’. Unfortunately in a throwrope
rescue situation the rescuee needs to be as alert as
the rescuer, an in such instances this is not usually the case, and more
elaborate and time consuming methods become necessary.
Furthermore, most throw ropes are no more than 20m long, and
the maximum practical distance a throwrope can reach
beyond the bank, even in skilled hands, is half its length. Therefore, in paddlesports terms, any engineered hydraulic jump more than
10m long poses a significant safety risk to even the most well equipped
paddler.
The frequent sluice discharges proposed by CPW will result
in immediate and erratic increases in the flow of the river, known as 'pulse'
floods. This will result in the navigational difficulty of the river increasing
almost immediately and without warning. This presents an especially significant
hazard to instruction groups and learning paddlers. Even experienced paddlers
will be taken very much by surprise and put at risk by pulse floods.
Sluixing discharges will also
release large volumes of sediment, up to 20,000 cubic metres per year per
settling basin. Based on a weekly discharge this equates to 385 cubic metres of
sediment per discharge. High sediment loads cause a great loss of paddling
amenity and present a safety risk.
Worse still is the very real risk of a canal failure. Should
the main canal fail close to the take site, a massive volume of water will be
released into the river without warning, causing massive damage and possible
loss of life.
Large pulse floods will alter the river bed as they happen,
such that anyone on the river at the time will have to contend with large
floods of muddy water and a shifting riverbed at the same time.
There are no bridges proposed over the main irrigation
canals in the vicinity of the river. This will prevent access along the bank at
these sites. Therefore, should a paddler become separated from his or her boat
and swim to the bank upstream of the irrigation take, then he or she will be
unable to walk down the bank to retrieve equipment. The paddler will be forced
to swim past the irrigation intake, in a narrow, trained channel that will be
shared by jetboats and heavy earthmoving equipment.
The potential for canoeing and kayaking facilities on the
lakes and canals of the irrigation scheme is no substitute whatsoever for swiftwater paddlesports. Swiftwater canoeing and kayaking are centred on the
relationship between paddler, boat and the current of the natural river.
To suggest that a flatwater
facility is adequate mitigation for a swiftwater
environment is akin to suggesting that cross-country skiing is similar to
downhill skiing or snowboarding, or that rowing is akin to sailing, or that
swimming is much like scuba diving.
Flatwater and swiftwater
paddling are completely different sports. We trust that this difference, and
the high value the paddlesports community places on
natural swiftwater environments, has been clearly
conveyed by this submission.
Whitewater canoeing and kayaking
is a different sport to swiftwater boating. Whitewater courses are generally designed for slalom and/or
rodeo events and cannot compensate for the loss of swiftwater
environments. Long touring and race boats are totally unsuited to whitewater. Touring trips and races are generally held over
considerable distances that would never be reproduced by an artificial whitewater course.