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Swamp ecosystems

Cu + Co deficit Especially in Swamp ecosystems Low content of Cu and Co in Podsoluvisols, Podzols, Arenosols and Histosols. Declining contents of Cu and Co in forage species (Cu from 3 to 0.7 ppm, Co < 5 ppb) Depressed synthesis of BJ2 vitamin and oxidation ferments. Cobalt-deficiency and B12 vitamin-deficiency complicated by Cu deficiency. The prevalent diseases of sheep and cattle... [Pg.40]

Swamp ecosystems are placed both in watershed and subordinate relief positions. The elevated content of metals is monitored in the latter case (Table 14). [Pg.164]

Table 14. The comparative estimation of average content of trace metals in surface waters of Swamp ecosystems, pg/L (after Shvartsev, 1999 and Dobrovolsky, 1994). Table 14. The comparative estimation of average content of trace metals in surface waters of Swamp ecosystems, pg/L (after Shvartsev, 1999 and Dobrovolsky, 1994).
The characteristic biogeochemical feature inherent in all Steppe and Desert ecosystems is the most intensive cycling of different chemical species in comparison with forest ecosystems. For a Steppe ecosystem the biogeochemical cycle is 2-3 years and this means that the complete renewal of all ecosystems biomass takes place over this period. Remember that in Forest ecosystems the biogeochemical cycling is about 3->25 years and even about 50 years in Forest Swamp ecosystems. The turnover is the highest in Ephemeral Desert and gradually decreases to the north. [Pg.168]

The plant precursors that eventually formed coal were compacted, hardened, chemically altered, and metamorphosed by heat and pressure over geologic time. It is suspected that coal was formed from prehistoric plants that grew in swamp ecosystems. When such plants died, their biomass was deposited in anaerobic, aquatic environments where low oxygen levels prevented their reduction (rotting and release of carbon dioxide). Successive generations of this type of plant growth and death formed deep deposits of unoxidized organic matter that were subsequently covered by sediments and compacted into carboniferous deposits such as peat or bituminous or anthracite coal. Evidence of the types of plants that contributed to carboniferous deposits can occasionally be found in the shale and sandstone sediments that overlie coal deposits. [Pg.1]

Moran, M.A., Wicks, R.J., and Hodson, R.E. (1991) Export of dissolved organic matter from a mangrove swamp ecosystem evidence from natural fluorescence, dissolved lignin phenols, and bacterial secondary production. Mar. Ecol. Prog. Ser. 76, 175-184. [Pg.633]

The remarkable part of the forested area is swampy. In certain regions, like the vast West Siberian plain, swamp and waterlogged ecosystems occupy about 30% of the total area. The biogeochemical cycling in these ecosystems is very complex and specific. The slow rates of biogeochemical turnover, typical for all Boreal Forest ecosystems are more depressed in Swamp ecosystems. For instance, in the Sphagnum Swamp ecosystem, the most widespread type of Swamp ecosystems, the annual NPP... [Pg.260]

Trace metals Swamp ecosystem relief position ... [Pg.273]

Lakes, rivers, swamps, and marshes - common in temperate areas - contribute little to the diversity of natural products. Abundant dull-green grass and dull-colored fish and moUusks characterize lakes and rivers, in contrasts with the vivid colors of tropical fish and seaweeds. Haplosclerid sponges are occasionally abundant in freshwater, but their secondary metabolism is limited to demospongic acids (Dembisky 1994), in contrast with the variety of metabolites from marine sponges in the same order. Where not for cyanobacteria (which are as rich of unusual metabolites as the marine strains), tropical amphibians, and aquatic fimgi, freshwater ecosystems would have passed unnoticed in this book. [Pg.27]

This major input of DOM from macrophytes is not restricted to lakes, but is also realized in other aquatic ecosystems. DOM export from watersheds in lotic ecosystems is directly related to annual runoff, but significantly greater in swamp-draining streams compared with upland-draining streams (Mulholland and Kuenzler, 1979 see Chapter 2 and 6). In the Hudson Estuary, planktonic bacterial production is 3 to 6 times greater than primary production (Findlay et al., 1992). DOC derived from submerged aquatic plants in part supports the difference in bacterial carbon uptake and planktonic primary production. [Pg.18]

Mulholland, P. J. 1981. Organic carbon flow in a swamp stream ecosystem. Ecological Monographs 51 307—322. [Pg.66]

Malaysia is blessed with a rich tropical rain forest, which is one of the most diverse and complex ecosystems in the world. The forest contributes to 95% of the land covers in Malaysia providing rich timber and other forest products. The coastal regions are generally covered with peat swamp (3.3%) and the ecologically sensitive mangroves (1.8%) (UNEP/ EAP-AP, 1999). In 2003, Malaysia exported 13.97 million m3 of timber and timber products (MTC, 2006). [Pg.632]

Two species of buffalo fish, smallmouth buffalo (Ictiobus bubalus) and bigmouth buffalo (Ictiobus cyprinellus), were collected from a contaminated (multiple metals and organic chemicals) Mississippi River Basin ecosystem, DS, and a control site, Tunica Swamp, both near Baton Rouge, LA [17], The buffalo fish... [Pg.443]

Biomes are a group of closely related ecosystems (see below). Terrestrial biomes include tundras, taigas, temperate forests, deserts, grasslands, and tropical rain forests. Major aquatic biomes are freshwater swamps, marshes and bogs, lakes and rivers, estuaries, inter-tidal zones, coastal oceans and open oceans. [Pg.144]

Benner R., Morgan M. A., and Hodson R. E. (1985) Effects of pH and plant source on lignocellulose biodegradation rates in two wetland ecosystems, the Okefenokee Swamp and a Georgia salt marsh. Limnol. Oceanogr. 30, 489-499. [Pg.3681]

Surface freshwater ecosystems consist of wetlands (e.g., bogs, fens, marshes, swamps, prairie potholes, etc.), streams, lakes (and artificial reservoirs), and rivers. Surface freshwater ecosystems receive most of their Nr from their associated watersheds, from atmospheric deposition, and from BNF within the system. There is hmited potential for Nr to accumulate within surface-water ecosystems, because the residence time of Nr within surface waters, like the water itself, is very brief. Residence times may be relatively longer in the sediments associated with wetlands and some larger lakes but are still short when compared to terrestrial ecosystems or the oceans. [Pg.4440]

Ecosystems of the World, Vols. 4A and 4B, Mires Swamp, Bog, Fen and Moor, General Studies, editors A. D. J. Gore and David W. Goodall, Elsevier Scientific Publishing, Amsterdam, 1983. [Pg.672]


See other pages where Swamp ecosystems is mentioned: [Pg.153]    [Pg.159]    [Pg.164]    [Pg.268]    [Pg.363]    [Pg.153]    [Pg.159]    [Pg.164]    [Pg.268]    [Pg.363]    [Pg.68]    [Pg.236]    [Pg.162]    [Pg.164]    [Pg.287]    [Pg.31]    [Pg.154]    [Pg.443]    [Pg.415]    [Pg.2066]    [Pg.2846]    [Pg.3681]    [Pg.445]    [Pg.91]    [Pg.58]    [Pg.592]    [Pg.594]    [Pg.600]    [Pg.630]    [Pg.3]    [Pg.271]   
See also in sourсe #XX -- [ Pg.153 , Pg.159 , Pg.164 , Pg.168 ]

See also in sourсe #XX -- [ Pg.260 , Pg.273 , Pg.274 , Pg.344 ]




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