The Invasion of Native Forest by Phytophthora cinnamomi. II. Post-Infection Vegetation Patterns, Regeneration, Decline in Inoculum and Attempted Control

1973 ◽  
Vol 21 (1) ◽  
pp. 13 ◽  
Author(s):  
G Weste ◽  
D Cooke ◽  
P Taylor
Keyword(s):  
Phytophthora Cinnamomi ◽  
Soil Disturbance ◽  
Vegetation Patterns ◽  
Native Forest ◽  
Disease Symptoms ◽  
Sclerophyll Forest ◽  
Successful Control ◽  
Woody Shrubs ◽  
Spread Of Infection ◽  
Barrier Zone

Further investigations of die-back in sclerophyll forest have shown that the disease continued to spread, averaging 171 m per year over periods of 3 years. Soil disturbance and gravel removal did not result in disease when no P. cinnamomi was present. P. cinnamomi was isolated from areas showing disease symptoms, but not from unaffected areas. The pathogen was confined to the A horizon of the soil and did not penetrate the clay or B horizon. Susceptibility of eucalypts was experi- mentally demonstrated at germination, at the seedling stage, and at maturity. More than 40% of mature stringybarks (of three species) were killed on some severely diseased sites. The eucalypts of the area were rated in order of susceptibility or tolerance to the pathogen. A decline in the disease potential of infected soil with time was demonstrated, and was associated with decreased population density of the pathogen. Changes in both type and composition of the plant community were noted. The sclerophyll forest with its woody understorey became a grassy woodland. A number of woody shrubs disappeared and a variety of herbs, such as grasses, bulbs, and composites, colonized the space made available by the death of woody shrubs and die-back of the eucalypt canopy. The most successful control of the disease was achieved by injecting infected areas with Vapam. This killed everything, and a barrier zone 4 m wide injected with Vapam prevented the spread of infection over a period of 18 months.

The invasion of native forest by Phytophthora cinnamomi. I. Brisbane Ranges, Victoria

1971 ◽  
Vol 19 (3) ◽  
pp. 281 ◽  
Author(s):  
GM Weste ◽  
P Taylor
Keyword(s):  
Water Stress ◽  
Phytophthora Cinnamomi ◽  
Eucalyptus Species ◽  
Native Forest ◽  
Symptom Expression ◽  
Root Pathogen ◽  
Disease Symptoms ◽  
Sclerophyll Forest ◽  
Drainage Channels

Disease within an open sclerophyll forest dominated by Eucalyptus species of relatively low stature (15-20 m) was shown to be caused by Phytophthora cinnamomi Rands, an introduced root pathogen. Diseased sites were mapped and measured. The rate of advance of the pathogen over a period of 5 months was calculated at 4 m per month through moderately drained soils compared with 7 m per month through soils subject to waterlogging. Areas showing disease symptoms increased from 10.8 to 90%, the major extensions occurring along gullies. Spread of the fungus was associated with road-making activities, waterlogging, and the presence of drainage channels. Symptom expression in the different species was studied and shown to be similar to that associated with water stress. Most of the 42 species comprising the woody flora were susceptible to the disease, those particularly susceptible including the dominants. During a period of 8 months mortalities occurred in 50% of the species. Grasses, sedges, and Eucalyptus goniocalyx appeared to be field-resistant, but were uncommon in the Aora of the sites studied.

The Distribution of Phytophthora cinnamomi Rands at Two Sites in Southern Western Australia and at Durras in South-Eastern New South Wales.

1982 ◽  
Vol 30 (2) ◽  
pp. 139 ◽  
Author(s):  
WM Blowes ◽  
WA Heather ◽  
N Malajczuk ◽  
SR Shea
Keyword(s):  
Western Australia ◽  
Phytophthora Cinnamomi ◽  
New South ◽  
New South Wales ◽  
Native Forest ◽  
Prevention Strategies ◽  
South Eastern ◽  
Isolation Techniques ◽  
South Wales ◽  
Western Australian

Native forest at Durras in south-eastern New South Wales and Jarrahdale in south-western Western Australia was examined for the presence of Phytophthora cinnamomi by two sampling and isolation techniques. With the lupin seeding baiting technique, randomly selected samples of soil and fine roots collected from the New South Wales site yielded P. cinnamomi when baited, while similar baiting of comparable samples from Western Australia failed. Direct plating of samples of upper roots and root collars of recently dead Banksia grandis from Western Australian sites yielded P. cinnamomi, while this organism was not isolated from comparable samples of chlorotic Macrozamia communis collected at the New South Wales site. The results suggest that the form of occurrence of P. cinnamomi and its association with disease in Australia vary in different situations. Viewing each situation independently might ensure the adoption of control/prevention strategies appropriate to all.

Vegetation Changes as a Result of Invasion of Forest on Krasnozem by Phytophthora cinnamomi

1980 ◽  
Vol 28 (2) ◽  
pp. 139 ◽  
Author(s):  
G Weste
Keyword(s):  
Pinus Radiata ◽  
Phytophthora Cinnamomi ◽  
First Year ◽  
Acacia Dealbata ◽  
Sclerophyll Forest ◽  
Lower Height ◽  
Leaf Spot Fungus ◽  
Future Status ◽  
Reduced Water ◽  
Increased Susceptibility

Disease caused by Phytophthora cinnamomi was studied for 5 years in native and planted forest growing on krasnozem in the northern foothills of the Great Dividing Range at Narbethong, 100 km northwest of Melbourne. Changes in species composition were recorded for three sites carrying mature dry sclerophyll forest of Eucalyptus obliqua and Eucalyptus radiata, young plantations of E. obliqua, and young plantations of Pinus radiata. The mature ecualypts were diseased in 1974 and now are gradually dying. The young E. obliqua showed greater resistance than the older trees to the pathogen but infected trees were characterized by lower height, small leaves with reduced water potential, and an increased susceptibility to the leaf spot fungus Aulographina eucalypti. Susceptible understorey species such as Tetratheca ciliata and Epacris impressa died, but seedling regeneration of these has since occurred on one site. No species has disappeared from all three sites but T. ciliata and Daviesia latifolia almost disappeared from site 2, and the total number of plants was reduced. Species such as Leptospermum juniperinum and Platylobium formosum developed fluctuating cycles of chlorosis and die-back followed by either recovery or death. Resistant plants such as sedges, grasses and Acacia dealbata invaded the diseased forest. During the first year of the investigation 13% of the 4-year-old Pinus radiata died, but this particular site was well drained, warmer and drier than the others and the surviving pines later grew vigorously and crowded out other species. Symptoms are no longer evident on this site. The future status of the mature forest and the probable effects of disease on the young E. obliqua plantation are discussed.

Pathogenic Variability in Australian Isolates of Phytophthora cinnamomi

1993 ◽  
Vol 41 (6) ◽  
pp. 721 ◽  
Author(s):  
MJ Dudzinski ◽  
KM Old ◽  
RJ Gibbs
Keyword(s):  
Phytophthora Cinnamomi ◽  
Growth Period ◽  
Species Variation ◽  
Eucalyptus Marginata ◽  
Disease Symptoms ◽  
Horticultural Crops ◽  
Damage Reduction ◽  
Single Clone ◽  
Pathogenic Variability ◽  
Stable Characteristic

Forty-two isolates of Phytophthora cinnamomi were obtained from native vegetation and horticultural crops within Australia. They represented a broad spectrum of geographical and host origins, both mating types, and all identified Australian isozyme genotypes. All isolates were tested for their pathogenicity to a single clone of Eucalyptus marginata by inoculation of soil in which plants were growing. Differences in pathogenicity were expressed as extent of root damage, reduction of plant growth, period to first visible disease symptoms and time to plant death. Significant variation between isolates was detected. Pathogenicity was unrelated to mating type and isozyme properties. A subset of these 42 isolates encompassing a range of virulence gave generally consistent rankings for pathogenicity variates when re-inoculated twice into plants derived from the original clone. This suggests that pathogenicity is a relatively stable characteristic. Detection of differences in susceptibility to P. cinnamomi between three selected E. marginata. clones was influenced by the pathogenicity of isolates. Only the more pathogenic isolates were useful in this regard. Seedling stems of five eucalypt species were inoculated with virulent and less virulent isolates of P. cinnamomi. This method detected variation in both pathogenicity in the fungus and susceptibility in the host species. Variation in pathogenicity within Australian populations of P. cinnamomi should be taken into account by the choice of isolates of proven virulence when selecting for resistance in trees and other woody hosts.

Phytophthora cinnamomi: Population Densities in Forest Soils

1977 ◽  
Vol 25 (5) ◽  
pp. 461 ◽  
Author(s):  
G Weste ◽  
P Ruppin
Keyword(s):  
Environmental Factors ◽  
Soil Water ◽  
Phytophthora Cinnamomi ◽  
Soil Water Potential ◽  
Forest Community ◽  
Population Densities ◽  
Sclerophyll Forest ◽  
Soil Temperatures ◽  
Disease Extension ◽  
Pathogen Populations

Population densities of Phytophthora cinnamomi, associated disease and environmental factors were studied concurrently during a 2-year period in three different forest ecosystems. Pathogen populations showed seasonal variation, low values being obtained for winter months associated with soil temperatures less than 10°C. Populations increased with warmer temperatures for spring and summer, but declined during dry periods in late summer or early autumn when the soil water potential was lower than -9 bars, although at that period soil temperatures were favourable. High populations were recorded in autumn, then declined with decrease in soil temperatures during winter. Correlation coefficients indicated a highly significant relationship between pathogen populations and soil temperatures from autumn to early summer, and between soil moisture and pathogen population for summer and autumn, in the Brisbane Ranges independently of site. The same pattern was evident in wetter forests at Narbethong and savannah woodlands at Wilson's Promontory, although results were not significant. Disease was evident wherever the pathogen occurred among susceptible hosts. The savannah woodland, the dry shrubby sclerophyll forest and the wetter sclerophyll forest all contained susceptible dominants; consequently disease was associated with changes in the forest community such as early death of the understorey, later die-back and death of the trees, and an increase in sedges and in bare ground. Symptoms and deaths increased with time from invasion. The severity of disease and its rate of extension, apart from spread by free water, were associated with environmental factors such as shallow soil, poor drainage and low soil water-holding capacity. These were characteristic of the Brisbane Ranges, where destruction of the forest community was severe and the rate of disease extension rapid. In the deep krasnozem at Narbethong and the deep sands of Wilson's Promontory, destruction was confined to the most susceptible hosts, disease extension was continuous but slow, and deaths occurred in a mosaic throughout the infected zone.

Phytophthora cinnamomi in the Brisbane Ranges: Patterns of Disease Extension

1976 ◽  
Vol 24 (2) ◽  
pp. 201 ◽  
Author(s):  
G Weste ◽  
P Ruppin ◽  
K Vithanage
Keyword(s):  
Environmental Factors ◽  
Phytophthora Cinnamomi ◽  
Soil Characteristics ◽  
Drainage Water ◽  
Sclerophyll Forest ◽  
Disease Extension ◽  
Wavy Boundary ◽  
Active Disease

Three patterns of disease extension were observed in areas of uncultivated shrubby dry sclerophyll forest invaded by the pathogen Phytophthora cinnamomi. Environmental factors were found to determine which pattern developed. Where inoculum was spread downhill with drainage water, diseased areas were separated by clearly defined boundaries from unaffected vegetation. Where disease extension occurred uphill through soil or from root to root, a wavy boundary marked the active disease front. Investigations showed that absence of disease extension for 4 years in highly susceptible vegetation may be associated with differences in soil characteristics.

Field Resistance in Three Native Monocotyledon Species That Colonize Indigenous Sclerophyll Forest After Invasion by Phytophthora cinnamomi

1984 ◽  
Vol 32 (4) ◽  
pp. 339 ◽  
Author(s):  
D Phillips ◽  
G Weste
Keyword(s):  
Phytophthora Cinnamomi ◽  
Lateral Roots ◽  
Fungal Growth ◽  
Field Resistance ◽  
Root Production ◽  
Root Tip ◽  
Bare Ground ◽  
Rapid Reduction ◽  
Sclerophyll Forest ◽  
Disease Extension

Lepidosperma laterale (Cyperaceae), Gahnia radula (Cyperaceae) and Poa sieberana (Poaceae) colonize bare ground of dry sclerophyll forest after disease due to P. cinnamomi. To determine their resistance, plants grown in divided root boxes were inoculated with 150-200 zoospores of the pathogen. Infected roots ceased growth. In the small necrotic lesions produced, the pathogen remained viable and capable of providing a source of inoculum for disease extension. Fungal growth was usually limited to the lesion but in some cases a few hyphae were observed in adjacent tissue. Away from the lesion there was a rapid reduction of fungal material and of the associated cellular disintegration. Rates of root production and root growth were not stimulated by infection but uninfected lateral roots replaced the root tip in some plants; in others, a new root tip emerged from the necrotic zone, enabling the plant to outgrow the fungal attack.

Regeneration of Vegetation in the Brisbane Ranges After Fire and Infestation by Phytophthora cinnamomi

1985 ◽  
Vol 33 (1) ◽  
pp. 15 ◽  
Author(s):  
P Dawson ◽  
G Weste ◽  
D Ashton
Keyword(s):  
Population Density ◽  
Seed Production ◽  
Phytophthora Cinnamomi ◽  
Basal Area ◽  
First Record ◽  
Inoculum Density ◽  
Crown Cover ◽  
Bush Fire ◽  
Crown Density ◽  
Sclerophyll Forest

The distribution, population density and regeneration of some prominent spp. of understorey and overstorey (dominant Eucalyptus spp.) were monitored over a period of 20 yr in seasonally well drained dry sclerophyll forest. Changes varied with susceptibility to the pathogen and to fire. Changes in spp. composition and crown density of the overstorey were attributed to fire. Population density, basal area and crown cover of the Eucalyptus spp. which were associated with the pathogen, also declined in 1962-82. Both distribution and population density of Xanthorrhoea australis and Isopogon ceratophyllus declined markedly following the spread of infestation, whereas those of Hakea sericea and Lepidosperma semiteres increased. Regeneration of X. australis but not of I. Ceratophyllus was observed in certain areas of the infested plots 12-20 years after infection. This is the first record of such regeneration. It is postulated that a bush fire in 1967 both stimulated X. australis seed production and reduced further an already declining pathogen inoculum density.

scholarly journals Aggressiveness of Phytophthora cinnamomi in avocado seedlings and effect of pathogen inoculum concentration and substrate flooding periods on root rot and development of the plants

2020 ◽  
Vol 42 (6) ◽  
Author(s):  
Ivan Herman Fischer ◽  
Aloísio Costa Sampaio ◽  
Rosemary Marques de Almeida Bertani ◽  
Bruno Henrique Leite Gonçalves ◽  
Eduardo Feichtenberger
Keyword(s):  
Root Rot ◽  
Phytophthora Cinnamomi ◽  
Dry Mass ◽  
Area Index ◽  
Inoculum Concentration ◽  
Disease Symptoms ◽  
Two Factors ◽  
Number Of Leaves ◽  
Collar Diameter ◽  
Soilless Substrate

Abstract The present study evaluated the aggressiveness of Phytophthora cinnamomi isolates and the effect of pathogen inoculum concentration and periods of substrate flooding on root rot and plant development. Twelve pathogen isolates were inoculated on the collar region of avocado seedlings with or without wounding. Only 31.3% of the inoculated plants without wounding developed lesions, compared to 100% of the plants with wounding, while the isolates showed different aggressiveness levels. Avocado seedlings had their substrate inoculated with 0, 0.1% and 1.0% (m/v) wheat seeds colonized by the pathogen per pot, and four periods of 0, 12 and 24 h substrate flooding were produced at fortnightly intervals. The assessed parameters were number of leaves per plant, collar diameter, plant height, leaf area index, visual severity percentage of infected roots, fresh mass (%) of diseased roots and dry mass of shoot and roots. Both pathogen inoculation and substrate flooding caused root rot; however, combination of these two factors produced an additional effect on disease symptoms. Root rot severity was superior to 50% when soilless substrate had 0.1% (m/v) P. cinnamomi inoculum and flooded for 12-24 h after inoculation, conditions that can be recommended for pathogenicity and disease control studies using potted avocado plants.

New species of Glossoscolex and Fimoscolex earthworms (Oligochaeta: Glossoscolecidae) from Embrapa Forestry, Paraná, Brazil

Zootaxa ◽  
2018 ◽  
Vol 4496 (1) ◽  
pp. 492 ◽  
Author(s):  
ALEXANDER FEIJOO M. ◽  
GEORGE G. BROWN
Keyword(s):  
Land Use ◽  
New Species ◽  
Land Use Change ◽  
Soil Disturbance ◽  
Species Group ◽  
Southeastern Brazil ◽  
Native Forest ◽  
Fallow Land ◽  
Araucaria Forest ◽  
Native Grassland

Three new earthworm species in two genera of the Glossoscolecidae family, common in Southern and Southeastern Brazil, collected in the highland plateaus of Paraná, are described: Glossoscolex (Glossoscolex) maschio sp. nov. and Glossoscolex (Glossoscolex) embrapaensis sp. nov., and Fimoscolex nivae sp. nov. G. embrapaensis is a small, unpigmented endogeic belonging to the truncatus species group, having male pore on segment 17, while G. maschio is a large, pigmented epiendogeic species belonging to the giganteus species group, having male pore on segment 19. F. nivae is a very slender, small unpigmented endogeic species. All specimens were collected in native Araucaria forest on the grounds of Embrapa Forestry, but G. maschio was found exclusively associated with native forest, while G. embrapaensis and F. nivae were also collected in Eucalyptus, Pinus or Araucaria plantations, native grassland or fallow land, indicating their resistance to soil disturbance and land use change.

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