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Book of Abstracts (PDF) - International Mycological Association

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IMC7 Main Congress Theme IV: POPULATION DYNAMICS AND ECOLOGY Posters<br />

the BNR-7 and BP-7 yrs sites, and rapidly increased from<br />

November to January. At the BNR-7 yrs site the number<br />

gradually decreased from 400 in July to 200 in January. At<br />

the BP-7 yrs site, on the other hand, the number gradually<br />

increased from below 100 in July to 200/10 g dry soil in<br />

January. 3. Number <strong>of</strong> sporangiocarps at the BNR-22 yrs<br />

site was always higher than those at the BNR-7 and BP-7<br />

yrs sites, in the range <strong>of</strong> 70-110/10 g dry soil, and showed<br />

the higher level in January. At the BNR-7 and BP-7 yrs<br />

sites the number is always very low (below 10/10g dry<br />

soil). 4. At the BNR-7 and BP-7 yrs sites Gigaspora and<br />

Scutellospora types, at the BNR-22 yrs site Glomus and<br />

Sclerocystis types were typically observed.<br />

988 - Seasonal changes in an ectomycorrhizal<br />

community associated with beech (Fagus sylvatica)<br />

R. Kjøller<br />

Department <strong>of</strong> Mycology, Botanical Institute, University <strong>of</strong><br />

Copenhagen, Øster Farimagsgade 2D, DK-1353,<br />

Denmark. - E-mail: rasmusk@bot.ku.dk<br />

The seasonal fluctuations <strong>of</strong> species abundances in an<br />

ectomycorrhizal (EM) community associated with beech<br />

(Fagus sylvatica) are being studied. Throughout 2001<br />

intensive sampling was performed in a 15 x 15 m plot in<br />

Lille Bøgeskov, located in mid Zealand. Soil cores were<br />

taken at eight harvest times covering the growing season<br />

from March to November. The sampling in this plot will be<br />

continued in 2002-2003. Fungal species forming EM on the<br />

beech roots are sorted by morphotyping and ITS-RFLP and<br />

then identified by sequencing. In the fall 2001,<br />

basidiocarps <strong>of</strong> EM species were sampled in the plot<br />

(collected and identified by Morten Christensen, KVL,<br />

Denmark). The basidiocarps are being sequenced in order<br />

to create a reference sequence database to aid in the<br />

identification <strong>of</strong> the root tips. As other EM communities<br />

the beech community turns out to be species rich. So far,<br />

the two harvests from March and May 2001, which has<br />

been most thoroughly worked through, has yielded approx.<br />

40 species. Some <strong>of</strong> the more abundant species found are<br />

Cortinarius species, Russulaceae spp., chanterelloid spp.<br />

including Clavulina cristata, Cenococcum geophilum,<br />

thelophoroid spp. and Piloderma spp. While some species<br />

e.g. Lactarius subdulcis are present throughout the growing<br />

season others e.g. a yet unidentified chanterelloid sp. are<br />

absent in the spring harvests but are then becoming<br />

dominant in the fall. Possible explanations for the observed<br />

seasonal trends will be discussed.<br />

298<br />

<strong>Book</strong> <strong>of</strong> <strong>Abstracts</strong><br />

989 - Rhizopogon spore bank communities: Species<br />

distribution within and among Californian pine forests<br />

R. Kjøller 1* & T.D. Bruns 2<br />

1 Department <strong>of</strong> Mycology, Botanical Institute, University<br />

<strong>of</strong> Copenhagen, Øster Farimagsgade 2D, DK-1353,<br />

Denmark. - 2 Department <strong>of</strong> Plant and Microbial Biology,<br />

University <strong>of</strong> California Berkeley, 321C Koshland Hall, CA<br />

94720-3102, U.S.A. - E-mail: rasmusk@bot.ku.dk<br />

In this study we examine the distribution <strong>of</strong> Rhizopogon<br />

species in spore banks from five Californian pine forests.<br />

Four <strong>of</strong> the forest sites were discontinuous populations <strong>of</strong><br />

Pinus muricata while the last was a Pinus ponderosa stand<br />

in the Sierra National Forest. Rhizopogon species were<br />

isolated from a soil-bioassay using Pinus muricata as host<br />

followed by isolation from individual root tips with typical<br />

Rhizopogon ectomycorrhizal morphology. The cultures<br />

were screened by ITS-RFLP and from each site unique<br />

patterns were sequenced. These sequences were then<br />

compared with sequences derived from identified<br />

sporocarp material. Bioassaying proved to be an efficient<br />

way to bring Rhizopogon species into culture as 50% <strong>of</strong> the<br />

pots contained ectomycorrhizal tips with Rhizopogon like<br />

morphology and half <strong>of</strong> these pots then resulted in axenic<br />

Rhizopogon cultures. Members <strong>of</strong> all the major pineassociated<br />

sections were represented within the isolates.<br />

Our results showed that Rhizopogon spores are<br />

homogeneously distributed within local forest areas while<br />

there is significant structuring at the regional scale. High<br />

spore longevity and homogenization by soil and water<br />

movement may explain their distribution within local forest<br />

areas while the latter observation fits with an expectation <strong>of</strong><br />

limited dispersal because <strong>of</strong> the hypogeous fruiting <strong>of</strong><br />

Rhizopogon species.<br />

990 - Monitoring <strong>of</strong> white-rot fungus during<br />

bioremediation <strong>of</strong> dioxin-contaminated soils<br />

R. Kondo * , H. Suhara & C. Daikoku<br />

Fac. <strong>of</strong> Agriculture, Kyushu University, Hakozaki,<br />

Fukuoka, 812-8581, Japan. - E-mail: kondo@brs.kyushuu.ac.jp<br />

Bioremediation is a low-cost treatment alternative for the<br />

cleanup <strong>of</strong> dioxin-contaminated soils and -fly ashes, when<br />

pollution spread broad-ranging. An interesting fungus was<br />

isolated from white rotten wood <strong>of</strong> a broadleaf tree from<br />

Kyushu Island in Japan, named strain MZ-340. This isolate<br />

has high ability to degrade dioxin. We have tried to use the<br />

strain MZ-340 for bioremediation <strong>of</strong> dioxin-contaminated<br />

soil on site. On the other hand, we have to consider that<br />

this trial has potential problems to bring biohazard on<br />

natural ecosystem, when this organism has been<br />

naturalized. Therefore, we have to develop a monitoring<br />

system for the introduced fungus with the examination <strong>of</strong><br />

bioremediation. The bioremediation <strong>of</strong> the dioxincontaminated<br />

soils by the fungus MZ-340 has been

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