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Scope
All freshwater ecosystems (such as streams, lakes, wetlands, geothermal
systems and underground aquifers) and the freshwater species within them.
These waterbodies and ecosystems are interconnected with both land and
estuarine and coastal ecosystems.
Desired outcome for 2020
The extent and condition of remaining natural freshwater ecosystems and
habitats are maintained. Some degraded or scarce habitats, such as lowland
river systems, important wetlands and riparian areas, are restored or
increased in area. Intact natural freshwater areas are protected and their
natural character is maintained.
Human activities in catchments are managed in an integrated way, avoiding,
remedying or
mitigating the adverse effects of land and water use (including pollution and
sedimentation) on
freshwater ecosystems. All freshwater ecosystems support biological communities
largely comprising
indigenous species. Plant and animal pests are managed to prevent further
spread, and eradicated
where necessary, to protect threatened indigenous ecosystems and species.
Introduced fish
(including sports fish such as trout and bio-control species such as grass carp)
and introduced
game (such as ducks) are managed so that they do not pose threats to indigenous
species of plants
or animals.
There have been no further human-induced extinctions of indigenous freshwater
species.
Threatened species are on their way to recovery within their natural habitat, or
in temporary ex
situ facilities where necessary. The harvest of indigenous and introduced
freshwater species is
sustainable and does not pose a threat to freshwater biodiversity.
Land managers and communities continue to be actively involved in protecting and
restoring
freshwater bodies and habitats of special value to them.
State of freshwater biodiversity
New Zealand has over 70 major river systems and numerous streams, with over four
million kilometres
of channel covering about 3000 square kilometres. A few of these rivers include
significant channels
within cave systems, and many of them are interconnected with underground
freshwater sources.
Most rivers, for part of their length, flow through farmland and many also flow
through urban areas.
Although a significant proportion of upland streambed is included within
protected areas, very few
lowland river systems have any form of protection. Many are ecologically
degraded through biological
invasions, reduced water quality, channelisation, sedimentation and removal of
floodplain connections,
all of which have adversely affected freshwater biodiversity.
The habitat of some freshwater species (for example, blue duck) is now severely
restricted. Only a
couple of complete river systems still lie within unmodified catchments and
remain free of introduced
species.
There are over 770 lakes and innumerable ponds, covering around 3400 square
kilometres. People
have also created numerous lakes and ponds, and these, and some natural lakes,
are managed for a
variety of purposes including water supply and power generation. Their
biodiversity values vary widely.
The 30 or so large deep lakes are of generally high water quality and some
support almost intact
indigenous ecosystems. However, many of the around 700 shallow lakes are
degraded by nutrient
enrichment causing eutrophication - a few to the extent that they are incapable
of sustaining fish
life. Most of the fish communities are dominated by introduced species, and
invasive exotic plant
species are extensive in most lake systems.
Wetlands represent some of New Zealand's most diverse ecosystems. However,
swamps, bogs and
marshes now cover only 1000 square kilometres, representing a loss of over 90
percent of the original
area of wetland systems. There is great regional variation in the extent of
loss, ranging from 63 percent
in Southland to 99 percent in the Bay of Plenty. Of the remaining wetlands, many
are degraded to
varying extents by weed invasions, stock access, modifications to hydrological
regimes, and barriers
to fish migration. However, some of the remaining wetlands are large and have
internationally
significant biodiversity values, as do some remaining geothermal areas.
As a result of pressures on freshwater habitats, and the effects of introduced
species, pests and weeds
and harvesting pressures, many freshwater species (particularly birds and
insects) have a significantly
restricted distribution. One third of the 29 identified species of indigenous
freshwater fish is threatened.
There are still sizeable gaps in our knowledge of freshwater species
(particularly in relation to algae
and invertebrates) and of habitat requirements (including effects of riparian
management). Public
awareness, and to a lesser extent scientific effort, have been focused on the
more obvious species,
especially fish and birds.
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Riparian reserves at Lake Taupo don't just benefit the trout
Lake Taupo is New Zealand's largest lake and is an important tourist,
recreational and
environmental asset. Its waters have generally remained clear and clean, thanks
to initiatives of
the local community and the Council in planning to protect the water quality in
the lake as the
district grew up around it. However, as development grows, the water quality of
the lake is coming
under increasing pressure.
Action was first taken in the 1950s, at a time of rapid development. Some 20 000
hectares of
buffer reserves were created around the margin of Lake Taupo and the waterways
that feed it.
Urban development was carefully planned, with key areas reserved or land uses
restricted. By
1981, around 6000 hectares of land had been reserved for conservation purposes,
and a further
12 000 hectares had limited land uses.
Although the riparian buffer reserves are not continuous around the river
margins and lakeshore,
their presence reduces sediment and nutrients entering the lake, and also
benefits biodiversity.
They protect important spawning grounds for trout, and also habitat for many
native fish and
freshwater invertebrate species.
Monitoring of a riparian reserve along the Whangamata Stream near Taupo has
shown an increase
in the variety of native plants and trees, as the original riparian plantings
have undergone their
own "succession" - with new woody native species invading the
flax-dominated stream banks. Fernbirds, fantails, bellbirds and pukeko have returned, and the stream is now
an important
wildlife area.
Most of these changes have occurred on private land, but Environment Waikato
(the regional
council), Taupo District Council and DoC, with assistance from iwi, have also
helped to manage
some of the riparian reserves. Some of the older reserves are now being used as
showcases to
demonstrate the benefits of riparian protection. |
Current management
Freshwater management is characterised by relatively complex and sometimes
overlapping
responsibilities for freshwater environments and species, under a large number
of laws. Natural waters
are vested in the Crown and managed and allocated by regional councils, while
DoC, Land Information
New Zealand (LINZ), regional councils and territorial authorities have various
responsibilities for
managing the beds of waterbodies and their surrounding land areas. Freshwater
species are managed
by DoC (most indigenous species), the Ministry of Fisheries (Mfish) (fish
species for which there is
some commercial harvesting), or fish and game councils (sports fish and game
birds).
Freshwater biodiversity issues are largely addressed within a broader water
management context. A
number of policy mechanisms are used or are being developed to manage freshwater
resources. These
include: RMA planning tools, such as district and regional plans; initiatives
under the Sustainable
Land Management Strategy and National Agenda for Sustainable Water Management (NASWM);
the
Environmental Performance Indicators programme; the 1986 New Zealand Wetlands
Management
Policy; the 1994 New Zealand Coastal Policy Statement; water conservation
orders; conservation
management strategies; and iwi management plans.
Some waterbodies, principally lakes and wetlands, are partly protected within
public conservation
lands or on private land. Wetlands are now eligible for Nature Heritage Fund and
Nga Whenua Rahui
funding for protection. Very few rivers are protected for all or even most of
their length, although
eight water conservation orders (four more are pending) protect the waters of
outstanding rivers or
lakes.
Summary of issues
Managing freshwater habitats and ecosystems
The threats to freshwater biodiversity are diverse and pervasive. Many land use
practices adversely
affect freshwater biodiversity, through their effects on freshwater habitats and
ecosystems, including
underground water systems. These practices include drainage, flood control
schemes, removal of
riparian vegetation, stock access and the addition of sediment, nutrients and
contaminants from
agricultural, forestry, industrial, residential and urban runoff. Management
responsibilities and
accountabilities are often not clearly specified in the freshwater environment.
- Reduced flows in some rivers limit freshwater biodiversity, and therefore
water allocation decisions
- often seen primarily as an economic issue - may have significant biodiversity
implications.
- Barriers to fish migration in rivers can prevent fish from completing their
life cycles; most
indigenous fish species are diadromous (meaning that they migrate to and from
the sea) and
most catchments in New Zealand have some artificial barriers. For some species
(such as eels) the
effects of the barriers preventing downstream migration to spawning grounds may
be the hardest
to overcome.
- Poor water quality in many rivers also frequently limits freshwater
biodiversity, and therefore
decisions about land use, as well as discharges to water, have significant
implications for aquatic
biodiversity.
- The grazing and drainage of significant wetlands continue to reduce and
degrade wetland habitats
and ecosystems. Estuarine habitats - important to the life cycle of diadromous
fish such as
whitebait and some commercial fisheries such as snapper - are often most at risk
from land use
activities and coastal development. Indigenous freshwater biodiversity values
have not yet been
adequately incorporated into sustainable land management strategies and
production sector
strategies.
- Possible sea level rise may also pose a threat to estuarine habitats and flood
plain wetlands.
- Geothermal ecosystems whose surface features are reserved may still be at risk
from the effects of
energy or fluid extraction through use of connected fields.
- There are very few freshwater ecosystems remaining in their original or
pristine state, and without
active management these may be at risk of loss of indigenous biodiversity and as
benchmarks to
compare with more modified ecosystems.
- Management of freshwater biodiversity presents special challenges because of
the need to integrate
land, water and fisheries management and to coordinate the use of a range of
policy and
management tools. The fragmented and overlapping responsibilities for management
of freshwater
ecosystems do not help effective coordination and integration, and
accountabilities of agencies
that share responsibility are often inadequately specified. The need for
coordination also applies
to the areas between freshwater and coastal environments.
- The Crown's property and other interests in freshwater biodiversity are
generally not well specified
and in some instances are being challenged by iwi.
Protection of freshwater habitats
The existing network of protected areas includes some freshwater bodies, but is
far from representative
of the full range of freshwater ecosystems and habitats.
- Information about protection priorities is deficient, but key areas known to
be poorly represented
include lowland lakes and rivers, floodplain wetlands, mid-altitude wetlands,
and geothermal
ecosystems.
- The gap between land and freshwater environments in achieving representative
protected areas
suggests that a different approach is required in protecting freshwater
ecosystems, with a special
focus on the sympathetic management of freshwater and surrounding land areas.
- Protecting freshwater biodiversity requires a high level of coordination
between management
agencies to ensure protection mechanisms are applied in a complementary and
integrated way.
Freshwater biosecurity and pest control
Many freshwater ecosystems are subject to a high degree of invasion by
introduced pest species,
significantly affecting indigenous habitats and ecological processes (see
Theme
Five).
- Most freshwater ecosystems have been significantly modified by introduced
species.
- Many animal and plant pests are highly invasive in freshwater environments,
but are not detected
until the extent of their spread makes them difficult to control.
- Effective technologies for control or eradication of known pests (for example,
koi carp) are not
always available.
- Policies, responsibilities and accountabilities for containing the spread of
already established
introduced freshwater species that have the potential to become serious pests
are not fully
developed.
- The illegal transfer and release of aquatic species create significant risks
to indigenous freshwater
biodiversity.
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Saving the dwarf inanga
Dwarf inanga is a small endemic galaxid fish, distinctive as our only native
freshwater fish species
which is fully adapted to living in lake environments. Its natural distribution
is restricted to only
a few dune lakes in Northland. Populations of dwarf inanga have declined over
the last 30 years
and the species is ranked as threatened. Currently, the National Institute of
Water and Atmospheric
Research (NIWA) is carrying out research in several of the lakes to try and
isolate what is causing
the fish's decline.
One idea was that the inanga were being preyed on by rainbow trout that had been
stocked in
some of the lakes. However, trials have shown that the presence of the trout
does not seem to
affect the abundance of the inanga. Recent trials are pointing to the
mosquitofish (a native of
southwest USA) - introduced around the world to control mosquitoes - as the
culprit. Despite
being smaller, the mosquitofish has been observed in Northland to kill or
immobilise dwarf inanga. Scientists are now wondering if the trout may help the survival of the
inanga by
preying on the mosquitofish.
Management trials are continuing, but now with a much clearer idea of the
relationships between the indigenous and introduced fish in the lakes. With
expansion of the mosquitofish range in the North Island, questions are also
being asked about its possible role in the decline of other native fish and
aquatic invertebrates. |
Protection of indigenous freshwater species
Indigenous freshwater species are threatened from a variety of causes, including
land use impacts and
competition or predation from pest species.
- Protection of threatened freshwater species depends largely on protection or
restoration of their
habitat, including the physical and biological characteristics of the habitat.
- Our knowledge of the distribution and taxonomy of many indigenous freshwater
species is limited.
Existing survey and monitoring programmes are generally not sufficient to define
freshwater
biodiversity or to identify changes in freshwater species composition and
abundance or habitat
condition.
- The effects of some introduced species on indigenous freshwater biodiversity
are not fully
understood.
- We do not have sufficient knowledge about all freshwater species that are
commercially harvested
(for example, eels) to be confident that their harvest is sustainable in some
areas.
- Some rare or vulnerable freshwater species (such as giant and short-jawed
kokopu fish) are
harvested as part of otherwise sustainable whitebait fisheries. This can create
difficulties in
providing a secure status for such species and for protecting fragile
populations from unnecessary
harvest.
Cultural and economic values and awareness of freshwater biodiversity
New Zealanders hold a range of cultural and economic values in relation to
freshwater environments
and fisheries that can both complement and conflict with the conservation of
indigenous biodiversity.
- Recreational fishing for species such as trout, salmon or whitebait is highly
valued by many New
Zealanders (and overseas visitors). This creates a strong interest in the
protection and restoration
of freshwater habitat, but sometimes also creates a potential conflict between
the protection of
indigenous and introduced species.
- Maori cultural values with respect to water quality and interests in
protecting freshwater ecosystems
and habitats to enable the use of freshwater species generally complement
objectives to conserve
and sustainably use freshwater biodiversity (see Theme Seven).
- There is a generally low level of public understanding of the special
characteristics, values and
vulnerabilities of freshwater biodiversity (see Theme Eight).
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Trout and indigenous biodiversity
Trout were first introduced into New Zealand in 1867. They were liberated widely
and are now
present in nearly all freshwater systems throughout the country except on
Stewart Island. Trout
are the backbone of New Zealand's freshwater game fishery. However, they have
also had significant
adverse impacts on indigenous freshwater species and ecosystems, and their
continuing effects
are not fully understood.
The effects of trout on indigenous freshwater biodiversity are considered under
the Conservation
Act as part of the process of preparing sports fish and game plans for approval
by the Minister of
Conservation, or in the case of national parks and reserves, as part of DoC's
management plan
reviews. Fish and game councils, DoC, iwi authorities, regional councils,
territorial local
authorities and members of the public all have an opportunity to participate in
these processes.
The New Zealand Fish and Game Council has adopted a policy that trout should not
be introduced
into catchments where they are not already present. On the basis of current
knowledge about the
interaction between trout and indigenous freshwater biodiversity, the New
Zealand Biodiversity
Strategy does not promote a significant reduction in the current distribution of
trout. However,
in some places (at the margins of their distribution) where trout threaten
indigenous species or
the natural character of pristine ecosystems, they may need to be reduced or
removed.
A significant part of the work of fish and game councils is concerned with
protecting and enhancing
habitat for trout, which usually also benefits the indigenous species that live
in these places. |
Action Plan
Objective 2.1 Protection and sustainable management of freshwater ecosystems24
a) Ensure that management mechanisms, including mechanisms under the Resource
Management Act and protected area statutes, adequately provide for the
protection of
freshwater biodiversity from adverse effects of activities on land and in water.
b) Protect a full range of remaining natural freshwater ecosystems and habitats
to conserve
indigenous freshwater biodiversity, using a range of appropriate mechanisms.
Actions:
a) Provide appropriate national guidance and assistance to decision makers and
management
agencies on the protection of freshwater biodiversity through a national policy
statement on
biodiversity, the National Agenda for Sustainable Water Management (NASWM) and
the
Sustainable Land Management Strategy.
Key players: MfE*, DoC, MAF, LAs, LGNZ, iwi/hapu, primary production sector,
NGOs25
b) Develop and apply a comprehensive classification system for freshwater
ecosystems, in line
with the framework and criteria developed under the Environmental Performance
Indicators
Programme, to help identify protection priorities.
Key players: MfE*, DoC, research providers, RCs, iwi/hapu
c) Progressively protect priority representative freshwater habitats, using a
suite of protective
mechanisms.
Key players: DoC*, MfE, LGNZ, RCs, QEII Trust, Landcare Trust, F&GNZ, NGOs,
iwi/hapu
d) Review the range of available protective mechanisms for freshwater
biodiversity and determine
any required changes to improve their efficiency and effectiveness, including
the removal of
disincentives to protection.
Key players: DoC*, MfE, LAs, iwi/hapu, primary production sector, land managers,
community
groups, QEII Trust
e) Support, and where necessary develop, joint national and regional/local
incentive mechanisms
for protecting scarce and under-represented freshwater bodies and their
surrounding areas on
private land, and provide support to landowners to maintain the biodiversity
values of these
areas (see Action 1.1f).
Key players: DoC*, MfE, LAs, iwi/hapu, primary production sector, land managers,
community
groups, QEII Trust
f) Provide advice and support to land managers and communities (both rural and
urban) who wish
to protect freshwater waterways, wetlands and habitats in their area to
encourage the protection
of areas that are a priority for indigenous freshwater biodiversity.
Key players: DoC*, MfE, LAs, iwi/hapu, primary production sector, land managers,
community
groups, QEII
g) Develop clear national criteria for protecting and managing biodiversity in
wetlands and
geothermal systems through a review of the 1986 Wetlands Policy and 1986
Geothermal Policy,
and incorporate in a national policy statement on biodiversity (see Action
1.1d).
Key players: DoC*, MfE*, RCs, F&GNZ, MoC, iwi/hapu, NGOs
h) Expand monitoring procedures (and establish new ones) for freshwater bodies
(including lakes,
rivers, underground systems, wetlands and geothermal systems) important for
indigenous
biodiversity to enable early action to maintain these ecosystems.
Key players: DoC*, MfE, research providers, RCs, iwi/hapu
Objective 2.2 Managing pests in natural freshwater habitats and
ecosystems
Prevent, control and manage plant and animal pests that pose a threat to
indigenous freshwater
biodiversity.
Action:
a) Develop and implement strategies and plans, including national and regional
pest management
strategies, to manage those plants and animals posing a threat to indigenous
freshwater biodiversity
and those potential pest species already present in New Zealand but not yet
widespread.
Key players: DoC*, RCs*, Biosecurity Council, MAF, iwi/hapu, research providers
Objective 2.3 Freshwater habitat restoration
Restore areas of degraded or scarce natural freshwater habitat and ecosystems
that are priorities
for indigenous biodiversity.
Actions:
a) Develop and implement regionally based strategies and action plans to
prioritise, restore and
maintain priority freshwater and riparian ecosystems and to provide
opportunities for
collaboration between regions and between land and water managers.
Key players: DoC*, MfE*, LAs, iwi/hapu, F&GNZ, NGOs
b) Compile regional inventories of significant artificial barriers to the
migration to and from the
ocean of indigenous freshwater species and progress priority actions to restore
fish passage.
Key players: DoC*, RCs, F&GNZ, iwi/hapu
Objective 2.4 Threatened freshwater species management
Enhance population numbers and ranges of indigenous freshwater species
threatened with
extinction and prevent additional species and ecological communities from
becoming threatened.
Actions:
a) Extend threatened species priority-setting systems to cover indigenous
freshwater species.
Key players: DoC*, NGOs, research providers, iwi/hapu
b) Increase and implement planned recovery actions to cover priority threatened
freshwater species
so that viable representative populations are maintained or restored across
their natural range.
Key players: DoC*, research providers, LAs, NGOs, iwi/hapu
Objective 2.5 Management of freshwater species for harvest
Ensure that harvest of indigenous and introduced freshwater species and
associated activities do
not adversely affect indigenous freshwater biodiversity.
Action:
a) Ensure fisheries management planning assesses risks to threatened indigenous
species from their
harvest and from introduced species, and take appropriate action to manage these
risks, and
where necessary, clarify fisheries management responsibilities.
Key players: DoC*, Mfish, F&GNZ, NGOs, iwi/hapu
23 Actions shown in bold are priority actions (see Part Four).
24 Objectives 2.1a and b are interrelated and actions a) - h) will collectively
contribute to their achievement.
25 See key to key
players.
*Government lead
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