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BEN # 221



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No. 221                              April 14, 1999

aceska@freenet.victoria.bc.ca        Victoria, B.C.
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 Dr. A. Ceska, P.O.Box 8546, Victoria, B.C. Canada V8W 3S2
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PLANT DIVERSITY IN BARKLEY SOUND [Part 2 of 3]
From: Martin L. Cody <mlcody@ucla.edu>

DISPERSAL AND COLONIZATION

On  smaller  islands where both colonization and extinction both
play a role, there  is  much  lower  predictability  in  species
numbers,  with  area  (e.g. r**2 = 0.3-0.5). This is expected if
colonization rates are isolation-specific, with a minor role  of
island  size  via  a  "target"  effect.  Four  common  dispersal
syndromes are represented on the islands:

 1. FERNS  ARE  DISPERSED VIA DUST-LIKE HAPLOID SPORES that give
    rise to a tiny short-lived gametophyte  which  produces  an-
    theridia  or  archegonia or both; after gametic union, it is
    replaced  by  the  often  large   and   long-lived   diploid
    sporophyte  whose  sori  in turn are the source of a further
    generation of spores (e.g.Stebbins 1950). To date 9  species
    have been encountered on the islands, but several others are
    possibilities  (Cody  [W.J.]  &  Britton 1989). Of the eight
    focal species, half are typical of shaded and moist  forest-
    floor  sites, but some are rather more habitat specific; one
    (Polypodium  scouleri)  occurs  on  coastal  rocks,  another
    (Adiantum  pedatum)  on damp interior rocks, bracken (Pteri-
    dium aquilinum) prefers  dry,  sunny  banks,  and  a  fourth
    (Polypodium  glycyrhiza),  perennial but with annual fronds,
    is largely epiphytic on tree trunks. All of the fern species
    have rather regular and sigmoidal incidence functions (plots
    of proportion of islands occupied versus island  size)  well
    fitted  by  logistic  regression,  but  island size at which
    incidence begins to decline varies  among  species,  and  in
    particular only those species with high leaf-specific weight
    and  minimal frond dissection (e.g., P. scouleri) persist on
    the smaller islands.

 2. At  the  opposite  end  of  the vegetation gradient from the
    forest ferns are PLANTS RESTRICTED TO  THE  SHORELINE  ROCKS
    AND  BEACHES,  of  which  there  are  some 30 characteristic
    species  (Cody   1998).   Examples   are   Atriplex   patula
    (Chenopodiaceae), Honkenya peploides and Sagina crassicaulis
    (Caryophyllaceae), Triglochin maritimum (Juncaginaceae), and
    four  grasses  (Poaceae):  Festuca  rubra, Hordeum brachyan-
    therum, Poa annua, Puccinnellia  pumila.    They  differ  in
    habitat  preference  and  are representative of the range of
    shoreline sites; most are of  wide  Holarctic  distribution,
    and  annual  and  perennial species are about equally repre-
    sented in the guild. Most of these  shoreline  species  dis-
    perse  by  floating  propagules,  but  in  the  two dry-rock
    grasses wind, or possibly animals such  as  shoreline  birds
    may  effect  dispersal ("ectozoochory"), though they are but
    modestly awned; of  the  two,  Festuca  is  rhizomatous  and
    Hordeum  is  not.  Incidence  functions  for  some shoreline
    species are reasonably monotonic with area, but  others  are
    not.

 3. A  third  guild  is WOODY SHRUBS that occupy the ecotone be-
    tween the forest and the shoreline. There is a  choice  from
    perhaps  two  dozen  species for this category, and examples
    include  four  species  of  Rosaceae  (Rosa,  Rubus),  2  of
    Caprifoliaceae (Lonicera, Sambucus), Grossulariaceae (Ribes)
    and  several  Ericaceae  (Arctostaphylos,  Gaultheria,  Vac-
    cinium, Menziesia), among many others of narrower  distribu-
    tion  (e.g.  in  Rosaceae,  Amelanchier,  Aruncus, Crategus,
    Holodiscus, Physocarpus,  Sorbus,  Spiraea).  These  species
    produce  variously  succulent  berries  and disperse via en-
    dochory,  using  the   locally   common   thrushes   (Turdus
    migratorius,  Ixoreus  naevius,  Catharus ustulatus, C. gut-
    tatus) and crows (Corvus) as dispersal agents. The fruits in
    this guild span a range of  sizes,  colors,  and  maturation
    phenologies,  as  in  the  three  Rubus species which differ
    conspicuously in timing and color of mature fruit: R.  spec-
    tabilis  matures  early  (mid-June)  with  orange  fruit, R.
    parviflorus 2-3 weeks later with red fruit, and  R.  ursinus
    later  still  with  blackish  fruit (Cody unpubl). Two other
    Rubus spp., the alien R. procerus [=R.  armeniacus]  and  R.
    laciniatus, are rare on the islands. Incidence functions for
    berry-producing  shrubs  decline  with  island  area  but at
    different rates in different species. For examples, Lonicera
    shows no effects of increased isolation, while  the  effects
    are  strong in Sambucus, which has much reduced incidence on
    distant islands. The  three  Rubus  species  are  ranked  in
    decreasing incidence spectabilis-parviflorus-ursinus, in all
    cases  with lower incidence on more distant islands; habitat
    availability among these edge shrubs is not likely  to  vary
    over  island  isolation,  indicating perhaps a role for dif-
    ferential dispersal and colonization.

 4. Between the shoreline and the forest edge is a  zone  a  few
    meters  wide  where  WEEDY  HERBACEOUS PLANTS form a nearly-
    continuous cover. This is the largest component of the flora
    (ca. 100 species), with representatives of such families  as
    Apiaceae,   Brassicaceae,   Onagraceae,   Polygonaceae,  and
    species of Asteraceae are especially  common.  Studies  have
    focussed  on  the latter family; most are short-lived peren-
    nials, some are biennials and some annual. Some species have
    distinct substrate and exposure preferences,  and  most  are
    anemochorous  and disperse via achenes borne on a parachute-
    like pappus. However, the most widely distributed species on
    these islands, Achillea millefolia,  matures  later  in  the
    season  that do others in the guild and apparently disperses
    as an ectozoochore when migrating shorelbirds fill the Sound
    in late August. Two other composite species,  Anaphalis  and
    Aster,  also have non-anemochorous (and non-obvious) disper-
    sal  means.  Incidence  functions  generally  decline   with
    decreasing  island  size, but in widely variable fashion. At
    the extremes, it is gradual in Achillea and  precipitous  in
    Sonchus.  Incidence  in  the  three non-anemochorous species
    (Achillea, Anaphalis, Aster) show little  or  no  effect  of
    island  isolation,  but  in the anemochores all show reduced
    incidence on the more distant islands in line with  expecta-
    tions  of  declining colonization rates with increasing dis-
    tance from source. The variety  of  incidence  functions  is
    further   extended  by  other  species  such  as  Matricaria
    matricaroides , which occurs  only  on  very  small  islands
    (near  and  far),  and  is  a  good  example of a supertramp
    (Diamond 1975).
[Conclusion in BEN # 222]


VEGETATION CLASSIFICATION AND MAPPING IN THE ROCKY MOUNTAINS
   SYMPOSIUM AND FIELD EXCURSION
From: Spribille_Toby/r1_kootenai@fs.fed.us

FIRST PRE-REGISTRATION NOTICE

Sponsored  by  the  International  Association   of   Vegetation
Science,  North American Chapter, Glacier National Park, and the
Kootenai National Forest Botany/Ecology Programme.

Symposium - 29-30 June 1999 - Kalispell, Montana
Excursion - 1-2 July 1999

In recent years there has been a flurry of activity in the arena
of vegetation classification  and  vegetation  mapping,  ranging
from  the introduction of a new vegetation classification system
by the Federal Geographic Data Commission and The Nature Conser-
vancy to advances being made in on-the-ground applications, from
Alaska to Colorado. Much of this work reflects an ongoing effort
to establish baseline data about vegetation, departing from  the
past  emphasis on site potential and concentrating on the exist-
ing vegetation in direct relationship to processes and  environ-
ment.  Unfortunately,  much of this work is not very well known.
Even many vegetation scientists do not  know  about  work  being
carried  out  in other areas, and the users of vegetation class-
ifications have been confused  about  the  relationship  of  the
newer  vegetation  classifications  to  habitat  types and other
vegetation work done up until the present.

Against this background, vegetation scientists from  across  the
Rocky  Mountains  and  Pacific  Northwest  have  been invited to
present recent work on vegetation classification at a  symposium
in  Kalispell,  Montana  on the 29th and 30th of June, 1999. The
objectives  of  the  meeting  are  to  facilitate  communication
amongst  vegetation  scientists,  familiarize  natural  resource
managers with the existing vegetation classification systems  as
well as recent developments in vegetation science in our region,
and  solicit  feedback from users on the ground, in a structured
but informal setting. The target  audience  includes  vegetation
ecologists,  foresters, botanists, wildlife biologists and other
professionals who use  vegetation  classifications  on  a  daily
basis.  We  hope  this  exchange  will shed light on some of the
following general topics:

Current issues:
--do new directives for natural resource management require  new
   perspectives of vegetation?
--taking  stock  of disturbance-dependent vegetation: do we have
   an information void?
--acquiring the information needed in natural resource  planning
   (NEPA, Forest Practices Code)

Classifying vegetation:
--classification   of   all  vegetation:  aims  and  methods  of
   phytosociology
--field methods and table sorting: how results are arrived at
--syntaxonomy:  bringing  different  vegetation   classification
   efforts ``onto the same page''
--relationship of phytosociology to habitat typing
--the National Vegetation Classification System
--landscape  vegetation  classification:  aggregating vegetation
   units at larger scales
--state of knowledge:  what  recent  classifications  have  been
   completed in the west?
--potential natural vegetation: new thoughts on old ideas

Applying classifications on the ground:
--how  are  vegetation  classifications used in resource manage-
   ment?
--vegetation inventory; what  vegetation  attributes  should  be
   routinely collected for conservation and management purposes?
--how  can baseline existing vegetation inventory be achieved by
   land management agencies with limited budgets?
--vegetation mapping; integration of  field  inventory  and  GIS
   techniques
--where do we need to go from here?

Two  days of presentations will be followed by two days of field
excursions (limited to 25 people). On the 1st of July, Christian
Damm will show us alpine tundra vegetation in  Glacier  National
Park  which he recently classified using Braun-Blanquet methods,
while on the second day (2 July) we will examine forest  vegeta-
tion on the Kootenai National Forest, recently classified by Dan
Leavell on the basis of existing vegetation. We will discuss how
Glacier National Park and the Forest Service, respectively, will
be  using  these  classifications, and how they could change the
way we view vegetation in these different environments.

In the course of the symposium, we will also  learn  about  work
recently  completed  in  Colorado, Alaska, British Columbia, and
other parts of the west. We will  have  a  chance  to  pose  our
questions  to  a panel of senior vegetation scientists including
members of the Ecological Society of America  Vegetation  Class-
ification Panel.

The  organizing  committee  needs to get initial feedback on the
number of people interested in attending the symposium.  If  you
are intending to attend this meeting, please send an e-mail to:
Jack Triepke, Kootenai National Forest,
jtriepke/r1_kootenai@fs.fed.us (IBM: jtriepke/r1,kootenai). Your
name  will be added to a mailing list to receive future mailings
about this symposium.

A DRAFT AGENDA  listing  the  scheduled  presentations  will  be
forthcoming  and will be mailed out to those who respond to this
posting.  Individuals  interested  in  presenting   posters   or
scheduling  brief  presentations,  please contact Toby Spribille
at 406.882.4451 or e-mail: <tspribille/r1_kootenai@fs.fed.us> as
soon  as  possible.  Formal  registration  in the symposium will
carry a modest fee, not expected to exceed US$60.00 per person.


WORLD WEEDS DATABASE ON CD-ROM
From: "P. Bacon" <phil.bacon@plant-sciences.oxford.ac.uk>

The World Weeds Database is based on the  information  contained
in the book "A Geographical Atlas of World Weeds" by Leroy Holm,
Juan  V.  Pancho,  James  P.  Herberger and Donald L. Plucknett,
which was published in 1979.

The book is a comprehensive list of weed species  of  the  world
and  their distribution after a research-work of ten years. Even
though it does not include all the species for any  geographical
region  it  is  a good information source for workers and scien-
tists.

The purpose of the database is to make it possible  to  retrieve
valuable  information  from  this book and make it available for
foresters or any other person who might be interested in knowing
the distribution of the most common and worst weeds.  The  World
Weeds  Database displays information on nearly 7000 weed species
around the world  according  of  its  rank  of  importance.  The
database  contains  Genus,  Family  and Species names as well as
taxonomic authorities.

This database is a development of work originally done  in  1994
and  1995,  supported  by  The Natural Resources Institute, Long
Ashton Research Station, The Forestry Research Program (OFI) and
the UK Overseas Development Administration.

We've now got this copied to CD-ROM. Full spec can be viewed at:
   http://w3.to/weeds/

Copies available from here at 27 British Pounds  or  equivalent.
Please pass this message on to anyone who might be interested.

   Dr.  P.  Bacon, Oxford Forestry Institute
   Department of Plant Sciences, University of Oxford
   South Parks Road,  Oxford OX2 3RB -  UK
   fax: 01865 271036  phone: 01865 271035
   email: pbacon@ermine.ox.ac.uk

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