RESUMEN
The European black truffle is a mycorrhizal fungus native to Spanish Mediterranean forests. In most Spanish regions it was originally commercially harvested in the second half of the 20th century. Experts agree that wild truffle yields suffered a sharp decline during the 1970s and 1980s. However, official statistics for Spanish harvest are scarce and seemingly conflicting, and little attention has been paid to the regime for the exploitation of truffle-producing forests and its implications on the sustainability of this resource. Trends in harvest from 1969 to 2013 and current harvesting practices were analyzed as a case study, taking into account that Spain is a major truffle producer worldwide, but at the same time truffles have only recently been exploited. The available statistical sources, which include an increasing proportion of cultivated truffles since the mid-1990s, were explored, with estimates from Truffle Harvesters Federation showing higher consistency. Statistical sources were then compared with proxies for wild harvest (rents from truffle leases in public forests) to corroborate time trends in wild harvesting. Results suggest that black truffle production is recovering in recent years thanks to plantations, whereas wild harvest is still declining. The implications of Spanish legal and institutional framework on sustainability of wild truffle use are reviewed. In the current scenario, the decline of wild harvest is likely to continue and eventually make commercial harvesting economically unattractive, thus aggravating sustainability issues. Strengthening of property rights, rationalization of harvesting pressure, forest planning and involvement of public stakeholders are proposed as corrective measures.
Asunto(s)
Conservación de los Recursos Naturales , Producción de Cultivos/tendencias , Bosques , Micorrizas , Ascomicetos , Formulación de Políticas , EspañaRESUMEN
Abandoned charcoal hearths constitute a very particular habitat for spontaneous fruiting of Tuber melanosporum, leading some harvesters to hypothesise that the fungus could benefit from the alterations that these soils underwent. However, ecological mechanisms involved in this relation are not fully elucidated yet. As a first step to understand it, the influence of long-term soil alteration on the symbiotic stage of T. melanosporum and on selected soil properties considered key to fruiting was assessed by conducting a greenhouse bioassay and a field observational study. In the bioassay, percent root colonisation and relative abundance of T. melanosporum were significantly lower in hearth than in control soils. Hearth soils showed significantly lower resistance to penetration, larger temperature fluctuation, reduced plant cover and reduced herbaceous root abundance. The results do not support the hypothesis that soil from historical charcoal hearths currently enhances development of T. melanosporum mycorrhizas. However, whether this is due to increased infectivity of native ectomycorrhizal communities or to worse conditions for development of T. melanosporum mycorrhizas remains unresolved. Native ectomycorrhizal communities in hearths showed altered composition, although not a clear change in infectivity or richness. Direction of change in hearth soil properties is compared to alteration occurring in soils spontaneously producing T. melanosporum. The interest of these changes to improve T. melanosporum fruiting in plantations is discussed.
Asunto(s)
Ascomicetos/crecimiento & desarrollo , Carbón Orgánico , Micorrizas , Microbiología del Suelo , SueloRESUMEN
The ectomycorrhizal fungus Tuber melanosporum fruits in association with Quercus in natural forests of Spain. Some of these stands are managed to keep an open canopy and meet the habitat requirements of the fungus. However, there are few quantitative studies analysing in these forests the relationship between soil environment and T. melanosporum. Eight forest stands which produce T. melanosporum have been monitored for 6 years in order to characterise the below-ground ectomycorrhizal community and to assess its temporal dynamics after experimental canopy opening. The brûlé, the ground where T. melanosporum fruits, shows a distinct ectomycorrhizal community, characterised by lower density of active ectomycorrhizal tips, lower morphotype richness per soil volume, higher abundance of T. melanosporum and lower abundance of Cenococcum geophilum than soil closest to the trunk of the host Quercus ilex. Opening the canopy has not stimulated an increase in T. melanosporum, suggesting that a shift in the soil environment alone will not trigger the formation of new truffières in the short term. The dry climate of these truffières may be a factor as T. melanosporum abundance appears to be sensitive to annual weather conditions.
Asunto(s)
Ascomicetos/fisiología , Micorrizas/fisiología , Quercus/microbiología , Biodiversidad , Ecosistema , Microbiología del Suelo , Simbiosis , ÁrbolesRESUMEN
In the early years of a black truffle plantation, the field proliferation of the nursery-inoculated fungi can be hampered by native ectomycorrhizal fungi colonising the seedling roots. Reducing the soil ectomycorrhizal infectivity in the planting hole before introducing the inoculated seedling could be an effective strategy to reduce this problem. Three bioassays were conducted to evaluate the impact of several soil preparations on the ectomycorrhizal infectivity and richness of a Quercus ilex soil in a truffle-producing region. Microwaves, quicklime, and acetic acid significantly decreased the percent root colonisation and morphotype richness of the native ectomycorrhizal fungi. However, they also decreased seedling survival or growth. Peracetic acid, hydrogen peroxide, and sodium hypochlorite did not show a significant negative effect on the soil ectomycorrhizal community. The results support the potential of soil preparation for reducing the ectomycorrhizal infectivity of forest soils, thus being a promising strategy to reduce the early colonisation by native fungi in truffle plantations. However, the indications of damage to the seedling development must be addressed.
Asunto(s)
Ascomicetos/crecimiento & desarrollo , Desinfección/métodos , Micorrizas/efectos de los fármacos , Micorrizas/efectos de la radiación , Raíces de Plantas/microbiología , Quercus/microbiología , Microbiología del Suelo , Ácido Acético/toxicidad , Compuestos de Calcio/toxicidad , Bosques , Microondas , Óxidos/toxicidad , Desarrollo de la Planta/efectos de los fármacos , Desarrollo de la Planta/efectos de la radiación , Quercus/efectos de los fármacos , Quercus/crecimiento & desarrollo , Quercus/efectos de la radiaciónRESUMEN
Wildfires are a major threat to Mediterranean forests. Firebreaks are built as a prevention measure, but require a periodic and expensive maintenance. Cultivating the ectomycorrhizal mushroom Tuber melanosporum Vitt. in firebreaks could reduce costs and improve their sustainability. But firebreaks are built on forest soil, considered nonoptimum for T. melanosporum cultivation. A pot experiment was used to study the persistence of T. melanosporum in firebreak soils in the short term, as a first step to assess the viability of these plantations. The influence of seedlings, soil heating, and liming was also tested. During the 2 y after plantation, T. melanosporum mycorrhizas increased their number, showing its ability to proliferate. Percent root colonisation by native fungi importantly increased from month 12 to 22; although T. melanosporum remained dominant, with a colonisation level similar to those in standard truffle plantations. The age of seedlings at the time of planting influenced T. melanosporum proliferation, supporting a key role for nursery seedling quality in the performance of young plantations. Heating the soil before planting reduced the richness of native fungi, suggesting that this could increase plantation success. The results tend to support the viability of T. melanosporum cultivation in firebreaks, and encourage experimental field plantations.