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Q)Explain the role of mycorrhizae in the ecosystem
INTRODUCTION:
Most land plants form associations with mycorrhizal fungi. Mycorrhizas aremutualistic associations between fungi and plant roots. They are described as symbioticbecause the fungus receives photosynthetically derived carbon compounds and the planthas increased access to mineral nutrients and sometimes water. The two most commonassociations are the arbuscular endomycorrhizas (AM) formed by Zygomycete fungi, andthe ectomycorrhizas (ECM) formed by Basidiomycetes, Ascomycetes, and a fewZygomycetes. Other mycorrhizal associations include the orchid, ericoid, arbutoid,monotropoid and ectendo- mycorrhizas (Brundrett et al., 1996).Mycorrhizal associations predominate in most natural terrestrial ecosystems(Brundrett, 1991). Whereas the AM fungi are widespread geographically and have a veryextensive host range, the ECM fungi are more restricted, forming associationspredominantly with genera of important woody plants. Nevertheless, ECM fungi aredominant components of the ground-dwelling macro-fungi in ecosystems where membersof the following plant families abound: Betulaceae, Dipterocarpaceae, Fagaceae,Myrtaceae, Pinaceae, Ulmaceae, Salicaceae. ECM fungi are common in tropical forests ofAsia but are uncommon in many forests in Africa and South America. In Asia, the numberof host species tends to increase with altitude and at higher latitudes.
ROLES IN ECOSYSTEMS:
The ecology of mycorrhizal fungi is not well documented (Abbott
and Gazey,1994; Francis and Read, 1995). Hence, in the discussion
that follows, conclusions aremostly drawn from short-term studies
with a small range of partnerships, often underexperimental
conditions. In nature, the situation is far more complex as a
single tree mayhave fungal partners which can vary in time and
space. The study by Moyersoen et al.,(1998), on the co-occurrence
of AM and ECM fungi in rainforest in Cameroon, provides a
good example of a field study exploring possible functional roles
of mycorrhizal fungi.More studies of this type are needed to
elucidate the dynamics of mycorrhizal fungi inecosystems and the
impact of disturbance. Carbon transport The fungal/plant interface
provides a conduit for the movement of carbon fromthe plant to the
fungus, and for movement between plants linked by mycelia (Francis
andRead, 1984; Simard et al., 1997; Wu et al., 2001). The nature of
the interface and its modeof regulation are still being elucidated
(Hall and Williams, 2000). It is generally believedthat mycorrhizal
plants direct more of their photosynthates into the soil
thannonmycorrhizal plants. This extra carbon accumulates in patches
and at the edge of hyphalmats (Finlay and Read, 1986), and boosts
the energy supply to the detrital food web,benefiting saprohytic
microbes and other soil organisms (Barea, 2000). Because
thechemical (Dieffenbach and Matzner, 2000) and physical
environment around mycorrhizas(the mycorrhizosphere) differs from
nonmycorrhizas, presumably it provides microhabitatsfor soil biota
that are not present in the rhizospere of nonmycorrhizal roots.
Mycorrhizal fungi are estimated to consume from 15 to 50% of net
primaryproduction (Fogel and Hunt, 1979; Vogt et al., 1982).
Nutrient cycling and nutrient conservation Fungi are crucial
components of ecosystems as they transport, store, release andcycle
nutrients. A good example of the potential of mycorrhizal fungi to
capture anddeliver nutrients to their host comes from studies using
inoculated eucalypts in field trialsin sub-tropical China.
Generally, trees in this region grow well below their potential.
Themain constraint to productivity appears to be low soil fertility
(Dell and Malajczuk, 1994;Xu and Dell, 1998). Most of the land
available for plantation forestry have been degradedover recent
centuries with extensive loss of the A horizon caused by population
pressure,inadequate management and over-harvesting (Xu, 1996).
Topsoil crusting is common,contributing to enhanced erosion,
reduced soil water storage, compaction and poor rootdevelopment (Xu
et al., 2000). Low soil organic matter (SOM) content (<2%)
alsorestrains productivity. As most soils for plantation eucalypts
in southern China have losttheir Ao layer, we need urgently to
consider how to recover microbial biodiversity as thereis no doubt
that this will be important for improving long-term soil fertility.
The capacityof some ECM fungi to promote both early growth and
survival of eucalypts is veryimportant for commercial plantations
on these disturbed and difficult sites. Significanteffects of ECM
fungal inoculation on growth of plantation eucalypts were obtained
at twosites in southern China (Xu et al., 2001). Effects were
isolate dependent with someisolates stimulating tree growth and
some isolates depressing tree growth. Similar resultswere obtained
in a trial in the Philippines where two isolates increased survival
while oneisolate decreased survival of Eucalyptus urophylla
(Aggangan et al., 1999). Theimprovement in growth could be
attributed to the acquisition of P as other essentialmineral
nutrients were supplied at establishment. Generally, inoculation
only increasedstand volume under P-limiting soil conditions. In
forests, litter is an important nutrient reservoir. ECM fungi can
mobilise P, N
and other nutrients from litter to tree roots (Attiwill and Adams,
1993; Perez-Moreno andRead, 2000). Fogel (1980) estimated that ECMs
account for 43% of the annual turnoverof N in a Pseudotsuga
menziesii forest in Oregon. Litter type can affect the diversity
andfunction of ECMs (Conn and Dighton, 2000). Buscot et al., (2000)
propose that the highdiversity of fungal partners that a tree may
have allows optimal foraging and mobilisationof various N and P
forms from organic soil layers. Soil structure It is obvious from
the examination of ECM mycelial mats, that mycorrhizal fungihave a
big impact on soil structure. Yet, there is scant information in
the literatureregarding soils in tropical ecosystems. In
agricultural soils, AM fungi increase theformation of soil
aggregates (Bethlenfalvay et al., 1999). Food for animals
Long-distance dispersal of spores from ECM fungi with hypogeal
(truffle-like)sporocarps depends largely on mammal mycophagy
(Kotter and Farentinos; Claridge andMay, 1994). Mycophagy is
widespread and has been demonstrated in Europe, Australasiaand
North America. Mycophagy serves to maintain populations of ECM
fungi andprovides nourishment to small mammals (Malajczuk et al.,
1987). Sporocarps are goodsources of water, protein, carbohydrates
and minerals (Johnson, 1994; Claridge et al.,1999). The tripartite
relationship between truffles/truffle-like fungi, vertebrates such
assquirrels and many ground-dwelling marsupials, and the host
trees, are well known. Lesswell known is the role that mycorrhizal
fungi play as a food source for invertebrates andthe role of
invertebrates in dispersal of ECM and AM fungal spores.
Q) Explain the key differences between bryophyte, gymnosperm, and angiosperm reproductive life-cycles.
Key Differences Between Angiosperms and Gymnosperms
Following are the substantial key differences between angiosperms and gymnosperms:
Angiosperms are also the source of the world’s hardwoods. Flowering plants are economically important as they serve as a source of pharmaceuticals, timber, ornamentals, fiber products, and other commercial uses, whereas gymnosperms are known for providing softwoods such as pine, fir and use to make paper, lumber, and plywood.
The defining features of bryophytes are:
Answer all questions below. You should give your sources used, and they should be primarily our book/videos/notes. Feel...