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Organic matter in soil

There are several environmentally significant mercury species. In the lithosphere, mercury is present primarily in the +II oxidation state as the very insoluble mineral cirmabar (HgS), as a minor constituent in other sulfide ores, bound to the surfaces of other minerals such as oxides, or bound to organic matter. In soil, biological reduction apparently is primarily responsible for the formation of mercury metal, which can then be volatilized. Metallic mercury is also thought to be the primary form emitted in high-temperature industrial processes. The insolubility of cinnabar probably limits the direct mobilization of mercury where this mineral occurs, but oxidation of the sulfide in oxygenated water can allow mercury to become available and participate in other reactions, including bacterial transformations. [Pg.407]

Apart from its use in studies of nitrogen fixation, N-labeled substrates have been used to assess the association of contaminants with organic matter in soil, and in metabolism. [Pg.286]

Association with organic matter in soil to produce nonextractable residues (Thorn and Kennedy 2002). [Pg.509]

Lesser tendency to partition to organic matter in soil (soil adsorption coefficient). [Pg.992]

The behavior of technetium in soils is important from an ecological viewpoint, but is quite complicated and depends on many factors. Stalmans et al. [27] stated that it is ruled by a combination of chemical, physicochemical and biological factors and understanding of it is needed on two main accounts bioavailability and geochemical mobility . They also noticed that organic matter in soils and sediments play a significant role as a geochemical sink for technetium. [Pg.29]

REACTIONS OF TRACE ELEMENTS WITH ORGANIC MATTER IN SOILS... [Pg.131]

Dissolved organic matter can be thought of, for simplicity, as soluble organic matter present in soil solution. However, although some workers have measured dissolved organic matter in soil leachates or extracted soil solutions, many use the extract from a 1 2 w/v soil/water extraction... [Pg.208]

Chan KY, Heenan DP (1999) Microbial-induced soil aggregate stability under different crop rotations. Biol Fertil Soils 30 29-32 Chantigny MH (2003) Dissolved and water-extractable organic matter in soils a review on the influence of land use and management practices. Geoderma 113 357-380... [Pg.225]

Janzen HH, Campbell CA, Brandt SA, Lafond GP, Townley-Smith L (1992) Light-fraction organic matter in soils from long-term crop rotations. Soil Sci Soc Am J 56 1799-1806... [Pg.227]

Watt BE, Clark NWE, Hayes MHB, Chipman JK, Skjemstad JO, Swift RS (1996) Aquatic humic substances from Pristine watersheds chemistry and postchlorination mutagenicity. In Clapp CE, Hayes MHB, Senesi N, Griffith SM (eds) Humic substances and organic matter in soil and water environments characterization, transformations and interactions. Proceedings of the 7th international conference IHSS, St. Augustine, Trinidad and Tobago, pp 389-390... [Pg.301]

Sediments can also serve as potential exposure routes for aquatic food chains through the bioaccumulation of contaminants by benthic organisms. The potential of sediment contaminants to expose organisms in sediments and the water column is determined by their bioavailability. The bioavailability or bioaccessibility of nonpolar organic contaminants is determined by how strongly they are bound to organic matter in soil and sediment [31, 32]. This fact should be taken into account in a realistic assessment of the environmental risks of these contaminants (Fig. 13). [Pg.401]

The share of a substance adsorbed by DOC is calculated by the partition coefficient of equilibrium partitioning between DOC and the dissolved phase /docKdoc- In this context it is assumed that the DOC fraction is 1% of total organic matter in soil... [Pg.397]

Diagram the breakdown of organic matter in soil and give the products of this decomposition process. [Pg.107]

Any low-molecular-weight organic compounds are normally a gas at standard temperature and pressure (STP) may also be found in the soil solution. These compounds will be produced as a result of the decomposition of organic matter in soil. Many of these will be readily taken up and used by microorganisms and thus their life spans in the soil solution are short. [Pg.117]

Figure 5.11. Equations for Kd and Kom , kg is kilogram L is liter of the soil solution. For Kom applied to soil, the numerator would be kg organic matter in soil. Figure 5.11. Equations for Kd and Kom , kg is kilogram L is liter of the soil solution. For Kom applied to soil, the numerator would be kg organic matter in soil.
Koopmans GF, Groenenberg JE. Effects of soil oven-drying on concentrations and speciation of trace metals and dissolved organic matter in soil solution extracts of sandy soils. Geoderma 2011 161 147-158. [Pg.174]

APHA (1979) Method 62. Organic Matter in Soil. The Analysis of Agricultural Materials, RB 247, 2nd edn., London. [Pg.375]

The Analysis of Agricultural Materials, 2nd edn, R.B. 427. HMSO, London, (1979) Method 2, p. 6. Preparation of Samples of soil Method 8, p. 21. Boron, water soluble in soil Method 57, p. 134. Nitrogen in soil Method 62, p. 148. Organic matter in soil Method 63, p. 151. Particle size distribution in soil... [Pg.507]


See other pages where Organic matter in soil is mentioned: [Pg.581]    [Pg.168]    [Pg.101]    [Pg.160]    [Pg.166]    [Pg.177]    [Pg.542]    [Pg.401]    [Pg.437]    [Pg.38]    [Pg.134]    [Pg.245]    [Pg.286]    [Pg.338]    [Pg.448]    [Pg.38]    [Pg.209]    [Pg.220]    [Pg.223]    [Pg.299]    [Pg.68]    [Pg.196]    [Pg.22]    [Pg.32]    [Pg.86]    [Pg.89]    [Pg.105]    [Pg.106]    [Pg.125]    [Pg.221]    [Pg.300]    [Pg.180]   
See also in sourсe #XX -- [ Pg.2 , Pg.73 ]

See also in sourсe #XX -- [ Pg.2 , Pg.73 ]




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Organic soils

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