Small understorey trees have greater capacity than canopy trees to adjust hydraulic traits following prolonged experimental drought in a tropical forest.

Future climate change predictions for tropical forests highlight increased frequency and intensity of extreme drought events. However, it remains unclear whether large and small trees have differential strategies to tolerate drought due to the different niches they occupy. The future of tropical forests is ultimately dependent on the capacity of small trees (<10 cm in diameter) to adjust their hydraulic system to tolerate drought. To address this question, we evaluated whether the drought tolerance of neotropical small trees can adjust to experimental water stress and was different from tall trees. We measured multiple drought resistance-related hydraulic traits across nine common neotropical genera at the world's longest-running tropical forest throughfall-exclusion experiment and compared their responses with surviving large canopy trees. Small understorey trees in both the control and the throughfall-exclusion treatment had lower minimum stomatal conductance and maximum hydraulic leaf-specific conductivity relative to large trees of the same genera, as well as a greater hydraulic safety margin (HSM), percentage loss of conductivity and embolism resistance, demonstrating that they occupy a distinct hydraulic niche. Surprisingly, in response to the drought treatment, small trees increased specific hydraulic conductivity by 56.3% and leaf:sapwood area ratio by 45.6%. The greater HSM of small understorey trees relative to large canopy trees likely enabled them to adjust other aspects of their hydraulic systems to increase hydraulic conductivity and take advantage of increases in light availability in the understorey resulting from the drought-induced mortality of canopy trees. Our results demonstrate that differences in hydraulic strategies between small understorey and large canopy trees drive hydraulic niche segregation. Small understorey trees can adjust their hydraulic systems in response to changes in water and light availability, indicating that natural regeneration of tropical forests following long-term drought may be possible.

Death from drought in tropical forests is triggered by hydraulics not carbon starvation.

Drought threatens tropical rainforests over seasonal to decadal timescales, but the drivers of tree mortality following drought remain poorly understood. It has been suggested that reduced availability of non-structural carbohydrates (NSC) critically increases mortality risk through insufficient carbon supply to metabolism ('carbon starvation'). However, little is known about how NSC stores are affected by drought, especially over the long term, and whether they are more important than hydraulic processes in determining drought-induced mortality. Using data from the world's longest-running experimental drought study in tropical rainforest (in the Brazilian Amazon), we test whether carbon starvation or deterioration of the water-conducting pathways from soil to leaf trigger tree mortality. Biomass loss from mortality in the experimentally droughted forest increased substantially after >10 years of reduced soil moisture availability. The mortality signal was dominated by the death of large trees, which were at a much greater risk of hydraulic deterioration than smaller trees. However, we find no evidence that the droughted trees suffered carbon starvation, as their NSC concentrations were similar to those of non-droughted trees, and growth rates did not decline in either living or dying trees. Our results indicate that hydraulics, rather than carbon starvation, triggers tree death from drought in tropical rainforest.

Gray Mold Caused by Botryotinia fuckeliana on Edible Pods of Pea in Brazil.

Gray mold on edible pods of snow pea (Pisum sativum Lam. [Fabaceae]) was observed in greenhouse-cultivated pea (cvs. Luana Gigante and Gigante Flor Roxa) in the city of Pelotas (Rio Grande do Sul, Brazil) in September and October 2012. The incidence of diseased pods was high (∼25% of immature pods) after up to 3 cloudy and rainy days that hindered the ventilation inside the greenhouse resulting in high relative humidity. Infection occurred first on senescing petals adhered to the forming pods, leading to pod abortion or rotting that began at the contact site with the infected petal. The first symptoms on pods included water soaked tissue that quickly turned light brown and progressed to necrosis. Conidia and conidiophores produced on profuse gray mycelium could be easily seen on infected tissue 2 to 3 days after the appearance of symptoms. Conidiophores were smooth-walled, 400 µm to over 1.5 mm long, hyaline to pale brown, and branched in their upper part; each branch ended with a hemispherical or spherical swelling, 5 to 9 µm in diameter with minute sterigmata. Macroconidia were globose, ellipsoidal, smooth, hyaline to pale brown, usually with protuberant hila, 7 to 15 × 5 to 9 µm. Microconidia were not observed. On potato dextrose agar (PDA), colonies were fast-growing, white, low, covering entire 10 cm petri plates in 4 to 5 days when they turned gray to brownish-gray. Conidiophores and conidia were often formed in sectors. Shield-like, elliptical, lenticular to irregular, black, 1.5 to 6.0 × 1.0 to 4.0 mm sclerotia developed in 10-day-old colonies incubated at room temperature. Genomic DNA was extracted from conidia, conidiophores, and mycelium and used to amplify both the internal transcribed spacer (ITS) (ITS1-5.8s-ITS2) region and the ß-tubulin gene using the ITS1/4 and Bt2a/b primers, respectively (1,4). The ITS (541 bp) and ß-tubulin (467 bp) sequences were deposited in GenBank under accessions KC683713 and KC683712, respectively. BLASTn searches revealed similarity of 100% (EF207415) and 99% (FQ790278) with Botryotinia fuckeliana (De Bary) Whetzel for the ITS and ß- tubulin sequences, respectively. Based on morphological characteristics and sequence analysis, the pathogen causing pod rot of peas was identified as B. fuckeliana. To fulfill Koch's postulates, 10 unwounded pods of P. sativum 'Luana Gigante' were inoculated by depositing PDA plugs (5 mm) colonized with fungal mycelium on their surface. Non-inoculated and mock-inoculated pods with sterile PDA plugs served as control. Inoculated and control pods were incubated inside a clear plastic box (11 × 11 × 3.5 cm) and over moistened filter paper under 12-h photoperiod at 25 ± 1°C. A surrounding water-soaked halo was visible only on pods inoculated with the fungus 48 h after inoculation (hai). Intense sporulation and necrosis were visible 96 hai. Botrytis spp. was previously detected, through standard blotter test, on seeds of P. sativum in Brazil, but without pathogenicity test nor its transmission through seeds (2,3). To our knowledge, this is the first report of B. fuckeliana causing epidemics on pea pods in Brazil. The high incidence of the disease in a protected environment has the potential to cause significant economic impact due to its damage to the pods, rendering them unmarketable. References: (1) N. L. Glass and G. Donaldson. Appl. Environ. Microbiol. 61:1323, 1995. (2) M. A. S. Mendes et al. Fungos em Plantas no Brasil. Embrapa-Cenargen, Brasília, 1998. (3) W. M. Nascimento and S. M. Cícero. Rev. Bras. Sementes 13:5, 1991. (4) T. J. White et al. PCR Protocols: A Guide to Methods and Applications. Academic Press, San Diego, 1990.

Quantifying the biodiversity value of tropical primary, secondary, and plantation forests.

Biodiversity loss from deforestation may be partly offset by the expansion of secondary forests and plantation forestry in the tropics. However, our current knowledge of the value of these habitats for biodiversity conservation is limited to very few taxa, and many studies are severely confounded by methodological shortcomings. We examined the conservation value of tropical primary, secondary, and plantation forests for 15 taxonomic groups using a robust and replicated sample design that minimized edge effects. Different taxa varied markedly in their response to patterns of land use in terms of species richness and the percentage of species restricted to primary forest (varying from 5% to 57%), yet almost all between-forest comparisons showed marked differences in community structure and composition. Cross-taxon congruence in response patterns was very weak when evaluated using abundance or species richness data, but much stronger when using metrics based upon community similarity. Our results show that, whereas the biodiversity indicator group concept may hold some validity for several taxa that are frequently sampled (such as birds and fruit-feeding butterflies), it fails for those exhibiting highly idiosyncratic responses to tropical land-use change (including highly vagile species groups such as bats and orchid bees), highlighting the problems associated with quantifying the biodiversity value of anthropogenic habitats. Finally, although we show that areas of native regeneration and exotic tree plantations can provide complementary conservation services, we also provide clear empirical evidence demonstrating the irreplaceable value of primary forests.

Decomposition and carbon cycling of dead trees in tropical forests of the central Amazon.

Decomposition rate constants were measured for boles of 155 large dead trees (>10 cm diameter) in central Amazon forests. Mortality data from 21 ha of permanent inventory plots, monitored for 10-15 years, were used to select dead trees for sampling. Measured rate constants varied by over 1.5 orders of magnitude (0.015-0.67 year-1), averaging 0.19 year-1 with predicted error of 0.026 year. Wood density and bole diameter were significantly and inversely correlated with rate constants. A tree of average biomass was predicted to decompose at 0.17 year-1. Based on mortality data, an average of 7.0 trees ha-1 year-1 died producing 3.6 Mg ha-1 year-1 of coarse litter (>10 cm diameter). Mean coarse litter standing-stocks were predicted to be 21 Mg ha-1, with a mean residence time of 5.9 years, and a maximum mean carbon flux to the atmosphere of 1.8 Mg C ha-1 year-1. Total litter is estimated to be partitioned into 16% fine wood, 30% coarse wood, and 54% non-woody litter (e.g., leaves, fruits, flowers). Decomposition rate constants for coarse litter were compiled from 20 globally distributed studies. Rates were highly correlated with mean annual temperature, giving a respiration quotient (Q 10) of 2.4 (10°C-1).

Risco e gravidez. II. Prontuario pre-natal orientado para rastreamento da gestacao de maior risco. Nota previa. / Risk and pregnancy. II. Oriented pre-natal record to search a righ-risk pregnancy.Preliminary note

No programa integrado de Saude Materno-Infantil e Familiar,sediado no Instituto de Pediatria e Puericultura da Universidade Federal do Rio de Janeiro sao utilizadas papeletas de anamnese obstetrica e exame clinico, orientados para apontar riscos de gravidez. Os autores discutem a importancia da sistematizacao de variavel como recurso primario para avaliacao de riscos e defendem a sua classificacao implementados em programas de assistencia materno-infantil, na identificacao do feto de maior risco