McCoy, Stephane Guy
Description
Ultramafics cover extensive areas of New Caledonia and present a
variety of unique nutritional and metal toxicity problems for plant growth.
The flora of these substrates is highly diverse and occurs as vegetation types
ranging from a low sclerophyllous maquis (heath) to rainforest. These
substrates have been the focus of intensive nickel mining over the last
century and are often devoid of vegetation for several decades. This lack of
plant establishment is a major environmental concern...[Show more] in New Caledonia
and has been the focus of revegetation research. The genus Gymnostoma
has received particular attention because of its nitrogen fixing association
with Frankia and dominance in vegetation types which might be
interpreted as a reflecting successional progression after fire. An
understanding of the mechanisms surrounding these successional patterns
might assist in solving practical issues of mine site revegetation with native
species.
This thesis set out to firstly determine whether vegetation types
containing Gymnostoma are successional communities, secondly to
examine certain key processes which appear to be driving vegetation
patterns, and thirdly, to identify the role of Gymnostoma in ultramafic
vegetation. Key processes associated with vegetation were examined
experimentally to determine their influence on plant growth on a range of
ultramafic substrates.
Field surveys exammmg vegetation patterns and processes were
carried out on three ultramafic soil types supporting Gymnostoma
vegetation: iron crust oxisol, eroded oxisol and hypermagnesian soil. These
three soil types have distinct chemical and physical properties which may
affect plant growth. Floristic records from each soil type were firstly
examined using MDS to determine floristic associations and subsequently
with a successional index constructed from a PCA ordination of vegetation
structure. The successional indices explained much of the variation on
MDS axes which suggested that ultramafic vegetation patterns primarily
reflects a post-fire succession. Fire records, annual growth rings of fire
sensitive Dacrydium araucarioides and demographic trends in species
composition also support a post-fire succession pattern. The succession
pattern was found to be composed of an early successional group of maquis species which either (i) decline or (ii) persist, and (iii) a late successional
group of forest species. Another important pattern revealed in surveys is
that early ultramafic successional stages progress more slowly than tropical
vegetation on other soil types. More importantly, certain processes appear
to be critical at early successional stages and predetermine later successional
development.
Surveys of abandoned mine sites set out to determine what processes
appear to be influencing plant establishment at early successional stages.
The evidence implies that most species are dispersal limited and show an
abrupt decline in abundance away from adjacent vegetation. Primary
colonist establishment is more abundant on crevice sites which trap seed,
and seedlings show higher rates of survival in such areas. The primary
colonists eventually generate a micro-environment providing shade and
litter which supports all of the subsequent colonisation of bare ground.
Shade and litter levels were regarded as important factors driving succession
on ultramafics and their effects at both the community and plant level were
examined.
Measures of light regimes in successional vegetation indicated that
light (PAR) declined with the development of vegetation cover over time.
These changes in incident solar radiation effect the community composition
depending on species light requirements for photosynthesis. Chlorophyll
fluorescence measurements of plants in natural vegetation and in field
experiments indicated that seedlings on bare ultramafic soil experienced
chronic photoinhibitive stress from a combination of high light and
substrate conditions. Seedlings under shade cloth and underneath tree
canopies potentially received less light for photosynthesis but exhibited less
stress indicative of photoinhibition. Therefore, shade may be crucial for
seedling survival at early successional stages. Furthermore, plant species
responded to high light conditions depending on their successional status.
Maquis species generally overcame photoinhibitive effects of bare ground
environments once they attained a certain age. In contrast, forest species
continued to exhibit photoinhibitive stress on bare ground environments.
Measures of soil and litter nutrient content indicate that N, P, Kand
Ca content increased with successional progression. Gymnostoma plays a
key role in the development of later successional phases by providing a
major source of nitrogen through its Frankia association. This nitrogen is
released along with other nutrients as an abundant litterfall that gradually increases soil nutrient pools over time through slow decay. Glasshouse
experiments indicated that leachates arising from slow cladode decay had no
allelopathic effect on plant growth. However, litter build up in late maquis
phases physically excluded large seeded species from establishing.
A fire susceptibility index was constructed from litter and vegetation
properties of successional vegetation. It indicates that Gymnostoma may
raise the susceptibility of maquis because its open canopy allows litter beds to
remain dry and flammable. However, Gymnostoma deplancheanum and
G. chamaecyparis are able to persist on their respective soil types even at
high fire frequencies because rocky terrain reduces fire spread and protects
patches of vegetation. In contrast, G. intermedium appears to have been
excluded from early successional vegetation on eroded oxisol by a
continuous cover of woody sedge maquis which is highly flammable. The
eventual dominance of broad leafed vegetation at later succession forest
stages decreases the fire susceptibility of these communities.
Results of field experiments indicate that slow maquis species growth
is primarily due to the low nutrient status of ultramafic soils. Plants which
received low doses of fertiliser and/ or litter showed a significant positive
response in terms of height and relative shoot growth. Fertiliser
applications also raised the total Frankia nodule weight per plant, indicating
that Frankia responds positively to slight increases in phosphorus. Contrary
to expectation, lime applications had no effect on maquis species shoot
growth. Lime additions resulted in fewer Frankia nodules and more
extensive root systems in Gymnostoma seedlings by reducing the
availability of other nutrients.
In summary, it is concluded that Gymnostoma dominated maquis
represents a post-fire succession. Colonisation at early successional stages is
dispersal limited and highly dependent upon the availability of crevices.
Once pioneer plants have established, litter and shade levels become crucial
factors in facilitating further succession. The relative abundance of
Gymnostoma determines the rate and direction of this successional change.
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