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Thematische Bibliographien / Soil binding sites

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Auswahl der wissenschaftlichen Literatur zum Thema „Soil binding sites“

Autor: Grafiati

Veröffentlicht am 4. Juni 2021

Zuletzt aktualisiert am 20. Februar 2023

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Zeitschriftenartikel zum Thema "Soil binding sites"

1

Kogan, Marcelo, Alejandra Metz, and Rodrigo Ortega. "Adsorption of glyphosate in chilean soils and its relationship with unoccupied phosphate binding sites." Pesquisa Agropecuária Brasileira 38, no. 4 (April 2003): 513–19. http://dx.doi.org/10.1590/s0100-204x2003000400010.

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The objective of this work was to investigate glyphosate adsorption by soils and its relationship with unoccupied binding sites for phosphate adsorption. Soil samples of three Chilean soils series - Valdivia (Andisol), Clarillo (Inceptisol) and Chicureo (Vertisol) - were incubated with different herbicide concentrations. Glyphosate remaining in solution was determined by adjusting a HPLC method with a UV detector. Experimental maximum adsorption capacity were 15,000, 14,300 and 4,700 mg g¹ for Valdivia, Clarillo, and Chicureo soils, respectively. Linear, Freundlich, and Langmuir models were us

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2

Peng, Shimeng, Pei Wang, Lanfang Peng, Tao Cheng, Weimin Sun, and Zhenqing Shi. "Predicting Heavy Metal Partition Equilibrium in Soils: Roles of Soil Components and Binding Sites." Soil Science Society of America Journal 82, no. 4 (May 17, 2018): 839–49. http://dx.doi.org/10.2136/sssaj2018.03.0104.

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3

Gustafsson, Jon Petter, Charlotta Tiberg, Abubaker Edkymish, and Dan Berggren Kleja. "Modelling lead(II) sorption to ferrihydrite and soil organic matter." Environmental Chemistry 8, no. 5 (2011): 485. http://dx.doi.org/10.1071/en11025.

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Environmental contextLead(II) is a toxic metal pollutant with many anthropogenic sources. We show that lead(II) is bound more strongly to soil surfaces than previously understood. This knowledge may lead to better models for lead(II) dissolution from the soils, which will improve risk assessments for this metal. AbstractLead(II) adsorption to soil organic matter and iron (hydr)oxides is strong, and may control the geochemical behaviour of this metal. Here, we report the adsorption of Pb2+ (i) to 2-line ferrihydrite, and (ii) to a mor layer. The results showed that ferrihydrite has heterogeneou

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4

Naidu, R., S. Mcclure, NJ Mckenzie, and RW Fitzpatrick. "Soil solution composition and aggregate stability changes caused by long-term farming at four contrasting sites in South Australia." Soil Research 34, no. 4 (1996): 511. http://dx.doi.org/10.1071/sr9960511.

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The effect of long-term farming on the cation exchange capacity (CEC), organic carbon content, soil solution composition, and aggregate stability was investigated using contrasting soils from 4 sites in the Mid North of South Australia. Undisturbed and farmed profiles were characterised at each site. Farming led to a 10–50% decrease, approximately, in organic matter and CEC in the surface horizon. Scanning electron microscopic study of the surface and selected subsurface soils revealed poor aggregation, compaction, reduced porosity, and a decrease in aggregate particle size in the farmed surfa

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5

Ghabbour, Elham A., Geoffrey Davies, Nadeem K. Ghali, and Matthew D. Mulligan. "The effect of temperature on tight metal binding by peat and soil derived solid humic acids." Canadian Journal of Soil Science 81, no. 3 (August 1, 2001): 331–36. http://dx.doi.org/10.4141/s00-065.

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The brown biomaterials called humic acids (HA) in peats and soils retain water and bind metal cations and other solutes. Studies of the interactions of purified solid peat and soil-derived HA from different countries with metal cations in water probe HA microstructures and help to characterize the metal binding sites. Labile cations such as Caaq2+, Co aq2+, Cu aq2+, Fe aq3+, Mg aq2+ and Mn aq2+ tightly bind to solid HAs in sequential steps. The isotherms A vs. c are well fitted with the Langmuir model and plots of 1/A vs. 1/c are linear for each step. Here, A is mmol bound metal g–1 HA and c i

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6

Kayler, Z. E., M. Kaiser, A. Gessler, R. H. Ellerbrock та M. Sommer. "Application of <i>δ</i><sup>13</sup>C and <i>δ</i><sup>15</sup>N isotopic signatures of organic matter fractions sequentially separated from adjacent arable and forest soils to identify carbon stabilization mechanisms". Biogeosciences Discussions 8, № 2 (1 березня 2011): 1985–99. http://dx.doi.org/10.5194/bgd-8-1985-2011.

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Abstract. Identifying the chemical mechanisms behind soil carbon bound in organo-mineral complexes is necessary to determine the degree to which soil organic carbon is stabilized belowground. We used the δ13C and δ15N isotopic signatures from two organic matter (OM) fractions from soil to identify the likely binding mechanisms involved. We used OM fractions hypothesized to contain carbon stabilized through organo-mineral complexes: (1) OM separated chemically with sodium pyrophosphate (OM(PY)) and (2) OM stabilized in microstructures found in the chemical extraction residue (OM(ER)). Furthermo

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7

Burlakovs, Juris, Raimonds Kasparinskis, and Maris Klavins. "Leaching of Contamination from Stabilization/Solidification Remediated Soils of Different Texture." Scientific Journal of Riga Technical University. Environmental and Climate Technologies 9, no. 1 (September 1, 2012): 12–16. http://dx.doi.org/10.2478/v10145-012-0011-0.

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Abstract Development of soil and groundwater remediation technologies is a matter of great importance to eliminate historically and currently contaminated sites. Stabilization/solidification (S/S) refers to binding of waste contaminants to a more chemically stable form and thus diminishing leaching of contamination. It can be performed using cement with or without additives in order to stabilize and solidify soil with the contamination in matrix. A series of experiments were done to determine leaching properties of spiked soils of different texture bound with cement. Results of experiments sho

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8

Taillon, K. M., and W. H. Hendershot. "Measurement and modeling of surface charge and cation binding in agricultural soil." Canadian Journal of Soil Science 88, no. 5 (November 1, 2008): 749–59. http://dx.doi.org/10.4141/cjss07076.

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Models of metal adsorption have typically been developed and tested for soil components rather than whole soils and at cation concentrations higher than usual environmental conditions. This study investigates whether the non-ideal consistent competitive adsorption (NICA) model can be applied to ion binding in whole soils at low total metal concentrations. Surface charge was measured for 18 agricultural soils from southern Quebec over the pH range 3.5 to 8. The adsorption of Ca, Cd, Cu, Pb and Zn was also measured for three total metal concentrations of 2, 5 and 10 mg L-1 at pH 6 in a 0.005 M C

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9

Liu, Paiyu, Pei Wang, Yang Lu, Yang Ding, Guining Lu, Zhi Dang, and Zhenqing Shi. "Modeling kinetics of heavy metal release from field-contaminated soils: Roles of soil adsorbents and binding sites." Chemical Geology 506 (February 2019): 187–96. http://dx.doi.org/10.1016/j.chemgeo.2018.12.030.

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10

Peng, Lanfang, Zhenqing Shi, Pei Wang, Wei Li, Zhang Lin, Zhi Dang, and Donald L. Sparks. "A novel multi-reaction model for kinetics of Zn release from soils: Roles of soil binding sites." Journal of Colloid and Interface Science 514 (March 2018): 146–55. http://dx.doi.org/10.1016/j.jcis.2017.12.006.

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Dissertationen zum Thema "Soil binding sites"

1

Jeong, Chang-Yoon. "Modelling metal competition for adsorption sites on humic acid." Thesis, University of Nottingham, 1998. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.389363.

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2

Ryan, Gregory Lawrence, University of Western Sydney, of Science Technology and Environment College, and of Science Food and Horticulture School. "Mechanisms of phosphorus removal by constructed wetland systems." THESIS_CSTE_SFH_Ryan_G.xml, 2003. http://handle.uws.edu.au:8081/1959.7/532.

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The objective of this thesis is to provide a detailed investigation of phosphorus transformations in constructed wetlands. Five replicate Wetland Units were constructed adjacent the wastewater treatment plant in Richmond, Australia. Each wetland was supplied with secondary or tertiary sewage effluent and planted identically with species of schoenoplectus, Phragmites, and Triglochin. Detention times for each Unit were established at 5 or 15 days. Phosphorus concentrations were monitored routinely at the inlet and outlet of each Unit, with a number of specific studies conducted to investigate in

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Ryan, Gregory Lawrence. "Mechanisms of phosphorus removal by constructed wetland systems." Thesis, View thesis, 2003. http://handle.uws.edu.au:8081/1959.7/532.

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The objective of this thesis is to provide a detailed investigation of phosphorus transformations in constructed wetlands. Five replicate Wetland Units were constructed adjacent the wastewater treatment plant in Richmond, Australia. Each wetland was supplied with secondary or tertiary sewage effluent and planted identically with species of schoenoplectus, Phragmites, and Triglochin. Detention times for each Unit were established at 5 or 15 days. Phosphorus concentrations were monitored routinely at the inlet and outlet of each Unit, with a number of specific studies conducted to investigate in

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Bücher zum Thema "Soil binding sites"

1

Te shu di zhi sheng gong cheng: Vegetation engineering for specific sites. Taibei Shi: Wu nan tu shu chu ban gong si, 2012.

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Buchteile zum Thema "Soil binding sites"

1

Glüsenkamp, K.-H., H. Kosegarten, K. Mengel, F. Grolig, A. Esch, and H. E. Goldbach. "A fluorescein boronic acid conjugate as a marker for borate binding sites in the apoplast of growing roots of Zea mays L. and Helianthus annuus L." In Boron in Soils and Plants, 229–35. Dordrecht: Springer Netherlands, 1997. http://dx.doi.org/10.1007/978-94-011-5564-9_44.

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2

"Ion Binding to Minerals: Discrete Site Modeling." In Soil Colloids, 444–75. CRC Press, 2016. http://dx.doi.org/10.1201/b15349-17.

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3

"Ion Binding to Humic Substances: Distributed Site Modeling." In Soil Colloids, 476–507. CRC Press, 2016. http://dx.doi.org/10.1201/b15349-18.

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