Indicator 1.3.2 - Status of in situ and ex situ conservation efforts for native tree species in each ecozone
core indicator
The conservation of genetic resources is a key objective
in meeting sustainable resource management
and biodiversity objectives. Strategies for maintaining
sufficient genetic diversity in native forest species
require an understanding of species biology and ecology.
This information is used to identify the threats
to genetic diversity and to develop management
plans and objectives. Gene conservation strategies
typically use a combination of in situ and ex situ conservation
methods. In situ conservation manages
genetic resources in their native habitats whereas
ex situ conservation manages genetic resources in
special facilities or collections (Ledig et al. 1998).
In situ and ex situ gene conservation strategies are
developed to ensure that native tree species, and
their associated plant communities, maintain a full
genetic component. This is done to enable them to
adapt to changes resulting from stress imposed by
environmental factors (e.g., climate change) or by disturbance
factors such as harvesting, wildfires, disease
(Indicator 2.3), land use conversion (Indicator 2.2),
or invasive alien species (Indicator 1.2.4). Conservation
of genetic resources of native tree species also
provides sources of genetic variation that may add
potential biological, social, and economic value for
the benefit of future generations in forest-based communities
(Indicator 5.1.4). Although tree species that
become locally extinct due to human activities may
be reintroduced through artificial regeneration and
appropriate forest management for species diversity,
the loss of genetic diversity that accompanies local
extinction may take generations, or be impossible, to
recover (Mosseler 1992).
In situ conservation can be either passive (e.g., leaving
the area undisturbed) or active (e.g., prescribed burning)
and can occur on both protected and managed
lands. In situ conservation is generally considered
economically more feasible (especially for noncommercial
species) and provides the opportunity for
the species to evolve among pests, symbionts, and
competitors occurring in the ecosystem (Rogers and
Ledig 1996). Understanding gene flow and dispersal
distance and patterns is important both from the
perspective of planning for in situ conservation and
for protection of natural ecosystems from alien genes.
Natural regeneration is considered one of several in
situ conservation strategies and is a common management
approach for reforestation in Canada. In some
provinces such as British Columbia, where natural
regeneration systems account for only an estimated
20% of the reforestation practices, a more comprehensive
gene conservation program is pursued. In addition,
the establishment and mapping of seed zones help
to control the transfer of seed or vegetative material,
ensuring that seeds or seedlings used for reforestation
are planted in the same general location where the
seeds were collected.
Ex situ conservation plays an important role,
especially when in situ conservation is not feasible
(e.g., when suitable habitat has been lost) or when
attempting to protect specific genes or genotypes.
Most provinces and territories have clone banks, seed
orchards, provenance trials, and progeny tests for
ex situ gene conservation for commercial and some
other indigenous tree species. Seed banks that are managed
at both the provincial and national levels, such
as the National Tree Seed Centre, also provide ex situ
conservation of the genetic diversity of Canadian
tree and shrub species and are sources of germ plasm
for research, reforestation, or restoration projects.
The conservation of forest genetic resources in Canada
is achieved through the combined efforts of federal,
provincial/territorial, and nongovernmental agencies.
For example, in situ conservation is carried out in
protected areas or other conservation lands across
Canada. Anetwork of conservation data centers and
natural heritage information centers across the country
maintains databases on occurrences and species
status assessments. These centers are coordinated by
NatureServe Canada, a nonprofit association that
collaborates with government agencies and NGOs.
Table 1.3a describes some of the other provincial and
territorial initiatives contributing to the conservation
of forest genetic resources. Because there is a wide
diversity of land ownership and management agencies
involved in genetic conservation, it is difficult to
access information on all these activities.
In 2003, in an attempt to report on the status of genetic
diversity in Canada's forests, the Canadian Forest
Service of Natural Resources Canada surveyed experts
from various agencies across Canada on the status
of gene conservation for indigenous tree and shrub
species (Beardmore et al. 2003). The results of the
survey indicated that 58 tree species require conservation
measures throughout one or more parts of their
ranges. In addition, for 20 of the tree species in the
survey, there was not enough information to determine
their conservation status. Many of the tree species
identified as requiring some form of genetic conservation
are from the Carolinian forests of southern
Ontario. Populations of these indigenous tree species,
rare in the Mixedwood Plains ecozone, have been
severely reduced due to multiple stresses including
agricultural development and urbanization (Beardmore
et al. 2003). Several temperate zone conifers (white
and red pine, eastern hemlock, red and white spruce)
have experienced serious population declines over
the past 150 years, and gene pool degradation of
white pine and white spruce is probable. Similarly,
shade-tolerant angiosperms such as sugar maple and
beech have been subjected to selective harvesting or
high grading that will probably affect the genetic qualities
of future generations (Reid and Mosseler 1995).
Specific conservation initiatives have been established
for several of the 58 species. For example, proactive
measures put in place to ensure that eastern white
pine, threatened as a result of high grading in the
nineteenth century, by the subsequent introduction
of white pine blister rust, and by infestations of the
white pine weevil, does not become a species at risk
include the establishment of
-
genetic selection and conservation programs,
a seed orchard, reforestation and silvicultural
guidelines, and several moratoria on its future
harvest in Newfoundland (Ministry of Forest
Resources and Agrifoods 1999);
-
progeny testing and a white pine restoration
program in Quebec (Daoust and Beaulieu
2004); and
-
a silviculture guide (OMNR 1998) and a
conservation policy for old-growth forests
in Ontario (OMNR 2003).
Table 1.3a Description of in situ and ex situ genetic conservation efforts for native tree species
| Jurisdiction |
Authority, organization, and/or program(s) |
Program description or ojective |
|
| Newfoundland and Labrador |
Tree species are protected in forests managed on crown lands and in protected areas through an in situ approach |
- Red and white pine are protected from harvest by legislation. Multijurisdictional committees advise on future management and conservation of these species.
- Maintain all ex situ plantations of black and white spruce as reservoirs of natural genetic variation
- Maintain seed and clone banks to preserve gene pool of most commercial tree species
|
| Prince Edward Island |
In situ conservation of tree species are protected in forests managed on provincial forest lands, provincial parks, and areas protected under the Natural Areas Protection Act |
- Objectives:
To protect tree and shrub species through appropriate management To establish protected areas for rare tree and shrub species
|
| Nova Scotia |
Tree species are protected in forests managed on crown lands and in protected areas through an in situ approach |
|
| New Brunswick |
Tree species are protected in forests managed on crown lands and in protected areas through an in situ approach |
- Objectives:
To maintain on crown lands old and/or late seral stages for a full range of naturally occurring forest types equivalent to 12% of the total area in each vegetative community defined by the 1982 provincial inventory
To protect unique forest sites by preserving sites with high or unique ecological, historical, cultural, or scenic value
|
| Gene Conservation Working Group, Atlantic Forestry Centre |
- Identifies conservation needs for forest genetic resources and develops conservation protocols
- Educates the forest sector, the public, and other appropriate sectors about gene conservation
|
| Quebec |
Tree species are protected in forests managed on crown lands and in protected areas through an in situ approach |
- Objective:
To protect tree and shrub species through a network of protected areas and through forest management practices
- Protected areas status granted in particular to protect rare tree and shrub species, notably under the Natural Heritage Conservation Act and the Forest Act. (It is assumed that almost all of the tree and shrub species that occur naturally in Quebec can be found in protected areas.)
- Conservation of genetic diversity through natural regeneration, seed bank, and provenance tests
|
| Exceptional Forest Ecosystems Program, Ministère des Ressources naturelles et de la Faune |
- Identifies and protects exceptional forest ecosystems, i.e., those with rare forest type, ancient forests, or forests sheltering threatened or vulnerable plant species
|
| Ontario |
Committee on the Status of Species at Risk in Ontario (COSSARO) |
- Ensures uniform, science-based, defensible approach to provincial status evaluations and recovery work for species at risk
|
| Forest Genetics Ontario |
- Objectives:
To conserve the adaptive variation within species in artificial regeneration programs. To conserve a broad genetic base in natural regeneration. To promote restoration strategies for vulnerable, threatened, and endangered species. To develop species management plans for species of concern. To actively manage seed orchards to meet the demand for genetically enhanced stock. To deploy genetically enhanced stock in a way that is sensitive to ecological concerns.
|
| Manitoba |
Endangered Species Advisory Committee |
- Advises minister on species of conservation concern, including recommendations for listing species under the Manitoba Endangered Species Act. Two rare native tree species (white pine and hackberry) have been assessed by this committee to date.
|
| Saskatchewan |
Tree species are protected in forests managed on crown lands and in protected areas through an in situ approach |
- Objectives: To conserve native biological diversity in representative areas (to serve as ecological benchmark) To preserve biological diversity in wilderness parks To protect wildlife habitat on wildlife development lands
|
| Alberta |
Provincial Tree Gene Conservation Program |
- Maintains adequate samples of genetic resources of forest tree species in each ecozone of Alberta
- Offers a reservoir of natural genetic variation for use in tree improvement, scientific and botanical studies
- Provides benchmarks for improved forest and genetic diversity
- Maintains ex situ plantations, clone banks, and seed banks for native tree species
|
| Alberta Forest Genetic Resources Council |
- Objective: To support conservation of forest genetic resources through advice and recommendations to the minister
|
| British Columbia |
Provincial Gene Resource Management and Resource Inventory (Data Conservation) programs (Ministry of Forests and Range, Ministry of Agriculture and Lands, Ministry of Environment) |
- Hosted Canadian Tree Improvement Association Conference, Climate Change and Forest Genetics, in Kelowna, July 2004
- Undertakes provincial breeding and genecology programs including ex situ plantations, provenance trials, breeding arboreta, and clone banks for more than 15 native tree species
- Maintains provincial Tree Seed Centre
- Maintains provincial Data Conservation Centre (coordinated nationally through NatureServe Canada)
- Develops provincial gene resource management plans, including in situ and ex situ gene conservation (in progress)
- Supports provincial gene resource management (mountain pine beetle, climate change) initiatives
- Order establishing provincial nonspatial old-growth objectives (June 2004)
- Defines parks, ecological reserves, and protected areas in Ecological Reserve Act
- Supports effectiveness evaluation under Forest Resource Evaluation Program, Timber Value - Genetic Diversity
|
| Forest Genetics Council of British Columbia |
- Supports an in situ documentation program through the Centre for Forest Gene Conservation (UBC). Information is incorporated into FGC strategic plans, and species-based annual business planning.
- Gene conservation identified as a strategic goal in the Forest Genetics Council of British Columbia Strategic Plan (2004/2008)
|
| Centre for Forest Gene Conservation (University of British Columbia) |
- Inventories and catalogues forest tree gene resources (Hamann et al. 2004)
- Supports information and expertise related to forest gene conservation
- Develops and advances gene conservation theory through research and collaboration with other agencies worldwide
|
| Yukon |
Tree species are protected in forests managed on crown lands and in protected areas through an in situ approach |
- Reexamining protected areas
- Conservation of genetic diversity through natural regeneration, seed banks, and provenance tests
|
| Northwest Territories |
No tree species conservation program |
- No perceived threat to loss of genetic diversity in native trees at this time or in the foreseeable future
|
| Nunavut |
Gene conservation is through an in situ approach in protected areas |
|
|