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Herbaceous Biomass (herbaceous + biomass)
Selected AbstractsSpatial pattern of dry rainforest colonizing unburnt Eucalyptus savannaAUSTRAL ECOLOGY, Issue 2 2004R. J. Fensham Abstract The spatial pattern of dry rainforest and savanna tree species was analysed in a 1.56-ha plot within an unburnt eucalypt savanna woodland in north Queensland, Australia. Rainforest colonization constituted only 1.3% of the basal area and mostly consisted of individuals less than 3 m high. The distribution of rainforest trees was highly clumped around the large savanna eucalypt trees. Ecological mechanisms generating the clumped distribution are discussed in light of evidence from this study and the literature. Herbaceous biomass was not reduced under trees, suggesting that relief from grass competition has not favoured rainforest colonization under tree crowns. Edaphic facilitation through nutrient enrichment under savanna tree crowns appears to be only minor on the moderate fertility soils of the area. The highly clumped pattern of colonizing dry rainforest may be a consequence of seeds dropped from birds roosting in savanna trees. [source] Spatial pattern of dry rainforest colonizing unburnt Eucalyptus savannaAUSTRAL ECOLOGY, Issue 2 2004R. J. FENSHAM Abstract The spatial pattern of dry rainforest and savanna tree species was analysed in a 1.56-ha plot within an unburnt eucalypt savanna woodland in north Queensland, Australia. Rainforest colonization constituted only 1.3% of the basal area and mostly consisted of individuals less than 3 m high. The distribution of rainforest trees was highly clumped around the large savanna eucalypt trees. Ecological mechanisms generating the clumped distribution are discussed in light of evidence from this study and the literature. Herbaceous biomass was not reduced under trees, suggesting that relief from grass competition has not favoured rainforest colonization under tree crowns. Edaphic facilitation through nutrient enrichment under savanna tree crowns appears to be only minor on the moderate fertility soils of the area. The highly clumped pattern of colonizing dry rainforest may be a consequence of seeds dropped from birds roosting in savanna trees. [source] Abiotic constraints on the establishment of Quercus seedlings in grasslandGLOBAL CHANGE BIOLOGY, Issue 2 2003Brett T. Danner Abstract High evaporative demand and periodic drought characterize the growing season in midwestern grasslands relative to deciduous forests of the eastern US, and predicted climatic changes suggest that these climatic extremes may be exacerbated. Despite this less than optimal environment for tree seedling establishment, deciduous trees have expanded into adjacent tallgrass prairie within the last century leading to a dramatic land cover change. In order to determine the role of light and temperature on seedling establishment, we assessed carbon and water relations and aboveground growth of first-year Quercus macrocarpa seedlings exposed to one of three conditions: (1) intact tallgrass prairie communities (control), (2) aboveground herbaceous biomass removed (grass removal), and (3) shade plus biomass removal to reduce light (PFD) to levels typical of the grassland-forest ecotone (shade). In the 2000 growing season, precipitation was 35% below the long-term average, which had a significant negative effect on oak seedling carbon gain at midseason (photosynthesis declined to 10% of maximum rates). However, net photosynthesis and stomatal conductance in the shade treatment was ca. 2.5 and 1.5 times greater, respectively, than in control treatment seedlings during this drought. During this period, leaf and air temperatures in control seedlings were similar whereas leaf temperatures in the shade treatment remained below air temperature. A late-season recovery period, coincident with decreased air temperatures, resulted in increased net photosynthesis for all seedlings. Increased photosynthetic rates and water relations in shaded seedlings compared to seedlings in full sun suggest that, at least in dry years, high light and temperature may negatively impact oak seedling performance. However, high survival rates for all seedlings indicate that Q. macrocarpa seedlings are capable of tolerating both present-day and future climatic extremes. Unless historic fire regimes are restored, forest expansion and land cover change are likely to continue. [source] Variant of estimation method of aboveground plant biomass in grassland with the gamma model.GRASSLAND SCIENCE, Issue 2 2006Abstract A modified method with visual observation for estimating biomass distribution on grasslands is proposed. This labor-saving technique facilitates surveys for estimating herbaceous biomass distribution for grasslands. It is based on the principle of Shiyomi's visual observation method. The procedure is performed as follows. (i) Set two points with biomass of c1 g and c2 g used as criteria in a pasture (c1 < c2). (ii) In the first visual observation, divide herbaceous biomass in the pasture into two classes that are more or less than c1 g. (iii) In the second visual observation, divide herbaceous biomass in the same pasture into two classes that are more or less than c2 g. Then, match the trial numbers obtained in the first and second observations. (iv) Measure the biomass weights of c1 and c2 with cutting. (v) From the data obtained above, infer the herbaceous biomass distribution using the gamma model. The procedure was conducted in a Zoysia grazed pasture. The following are discussed: advantages and regulations of the current method with a gamma model; some problems of the cutting method, as viewed from the shape of herbaceous biomass distribution; and the influence of grazing pressure on herbaceous biomass distribution. [source] |