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            type="text/xsl"?><rdf:RDF xmlns:rdf="http://www.w3.org/1999/02/22-rdf-syntax-ns#"><channel rdf:about="http://onlinelibrary.wiley.com/rss/journal/10.1002/(ISSN)1522-2624" xmlns="http://purl.org/rss/1.0/"><title>Journal of Plant Nutrition and Soil Science</title><description> Wiley Online Library : Journal of Plant Nutrition and Soil Science</description><link>http://dx.doi.org/10.1002%2F%28ISSN%291522-2624</link><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc</dc:publisher><dc:language xmlns:dc="http://purl.org/dc/elements/1.1/">en</dc:language><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/">Copyright © 2012 WILEY-VCH Verlag GmbH &amp; Co. KGaA, Weinheim</dc:rights><prism:issn xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">1436-8730</prism:issn><prism:eIssn xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">1522-2624</prism:eIssn><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><prism:coverDisplayDate xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">February, 2012</prism:coverDisplayDate><prism:volume xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">175</prism:volume><prism:number xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">1</prism:number><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">1</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">167</prism:endingPage><image rdf:resource="http://onlinelibrary.wiley.com/store/10.1002/jpln.v175.1/asset/cover.gif?v=1&amp;s=3aed3614789644e4a786303e576e5d8c874fbbfd"/><items><rdf:Seq><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100177"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100022"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201000434"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201000361"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100058"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100063"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100005"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201000046"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201000399"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201000358"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201290000"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201290007"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201290004"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201290005"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100075"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100076"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201000403"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201000438"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100072"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100186"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100253"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100097"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201000415"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100126"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201000348"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201000056"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201000390"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100127"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201000299"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100035"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201000426"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100141"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201100050"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201290001"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201290002"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201290003"/><rdf:li rdf:resource="http://dx.doi.org/10.1002%2Fjpln.201290006"/></rdf:Seq></items></channel><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100177" xmlns="http://purl.org/rss/1.0/"><title>Phosphorus forms and enzymatic hydrolyzability of organic phosphorus in soils after 30 years of organic and conventional farming</title><link>http://dx.doi.org/10.1002%2Fjpln.201100177</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Phosphorus forms and enzymatic hydrolyzability of organic phosphorus in soils after 30 years of organic and conventional farming</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Martina Keller</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Astrid Oberson</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Kathrin E. Annaheim</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Federica Tamburini</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Paul Mäder</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jochen Mayer</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Emmanuel Frossard</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Else K. Bünemann</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-13T08:42:02.034999-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100177</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100177</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100177</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Lower P-input levels in organic than conventional farming can decrease soil total and available P, which can potentially be resupplied from soil organic P. We studied the effect of 30 y of conventional and organic farming on soil P forms, focussing especially on organic P. Soil samples (0–20 cm) were taken in a field experiment with a nonfertilized control, two organic systems receiving P inputs as animal manure, and two conventional systems receiving only mineral P or mineral P and manure. Soils were analyzed for total, inorganic, organic, and microbial P, by sequential P fractionation and by enzyme additions to alkaline soil extracts. Samples taken prior to starting the experiment were also analyzed. Average annual P balances ranged from –20 to +5 kg ha<sup>–1</sup>. For systems with a negative balance, labile and moderately labile inorganic P fractions decreased, while organic and stable inorganic P fractions were hardly affected. Similar quantities and proportions of organic P extracted with NaOH-EDTA were hydrolyzed in all soils after addition of an acid phosphatase, a nuclease, and a phytase, and enzyme-stable organic P was also similar among soils. Thus, neither sequential fractionation nor enzyme addition to alkaline soil extracts showed an effect of the type of applied P (manure <em>vs.</em> mineral) on organic P, suggesting that organic P from manure has largely been mineralized. Thus far, we have no indication that the greater microbial activity of the organic systems resulted in a use of stable P forms.</p></div>]]></content:encoded><description>Lower P-input levels in organic than conventional farming can decrease soil total and available P, which can potentially be resupplied from soil organic P. We studied the effect of 30 y of conventional and organic farming on soil P forms, focussing especially on organic P. Soil samples (0–20 cm) were taken in a field experiment with a nonfertilized control, two organic systems receiving P inputs as animal manure, and two conventional systems receiving only mineral P or mineral P and manure. Soils were analyzed for total, inorganic, organic, and microbial P, by sequential P fractionation and by enzyme additions to alkaline soil extracts. Samples taken prior to starting the experiment were also analyzed. Average annual P balances ranged from –20 to +5 kg ha–1. For systems with a negative balance, labile and moderately labile inorganic P fractions decreased, while organic and stable inorganic P fractions were hardly affected. Similar quantities and proportions of organic P extracted with NaOH-EDTA were hydrolyzed in all soils after addition of an acid phosphatase, a nuclease, and a phytase, and enzyme-stable organic P was also similar among soils. Thus, neither sequential fractionation nor enzyme addition to alkaline soil extracts showed an effect of the type of applied P (manure vs. mineral) on organic P, suggesting that organic P from manure has largely been mineralized. Thus far, we have no indication that the greater microbial activity of the organic systems resulted in a use of stable P forms.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100022" xmlns="http://purl.org/rss/1.0/"><title>Effects of earthworms and plant growth–promoting rhizobacteria (PGPR) on availability of nitrogen, phosphorus, and potassium in soil</title><link>http://dx.doi.org/10.1002%2Fjpln.201100022</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Effects of earthworms and plant growth–promoting rhizobacteria (PGPR) on availability of nitrogen, phosphorus, and potassium in soil</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Fuyong Wu</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Judy Hon Chi Wan</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Shengchun Wu</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Minghung Wong</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-13T08:41:54.494513-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100022</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100022</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100022</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Both earthworms and plant growth–promoting rhizobacteria (PGPR) are ubiquitous and important for promoting circulation of plant macronutrients. Two series of laboratory experiments were conducted to investigate the effects of earthworm casts and activities on the growth of PGPR, and the inoculation of earthworms and PGPR on the availability of N, P, and K in soils, respectively. During a short incubation period (0–34 h), the extracts of earthworm (<em>Pheretima guillelmi</em>)-worked soil significantly (<em>p</em> &lt; 0.05) increased the abundance of the three species of PGPR, including N-fixing bacteria (NFB) (<em>Azotobacter chroococcum</em> HKN-5), phosphate-solubilizing bacteria (PSB) (<em>Bacillus megaterium</em> HKP-1), and K-solubilizing bacteria (KSB) (<em>B. mucilaginous</em> HKK-1), in Luria-Bertani (LB) broth. There were synergistic effects of dual inoculation of earthworms and PGPR on increasing the concentrations of NH<span class="math"><img alt="equation image" src="http://onlinelibrary.wiley.com/store/10.1002/jpln.201100022/asset/equation/tex2gif-ueqn-1.gif?v=1&amp;t=gyzvyb0h&amp;s=01f7eeb9eeaba418736c5ab3bb3a19d09b292d24" class="inlineGraphic"/></span>-N, (NO<span class="math"><img alt="equation image" src="http://onlinelibrary.wiley.com/store/10.1002/jpln.201100022/asset/equation/tex2gif-ueqn-2.gif?v=1&amp;t=gyzvyb0j&amp;s=ec671a959b007ef4a2a3307b28c7fd4a83be6c16" class="inlineGraphic"/></span> + NO<span class="math"><img alt="equation image" src="http://onlinelibrary.wiley.com/store/10.1002/jpln.201100022/asset/equation/tex2gif-ueqn-3.gif?v=1&amp;t=gyzvyb0k&amp;s=c4e6a43da0008811e860bc46ffef5444dcec2ac4" class="inlineGraphic"/></span>)-N, NaHCO<sub>3</sub>-extractable P, and NH<sub>4</sub>OAc-extractable K in the corresponding soils. Bioavailable N (the sum of NH<span class="math"><img alt="equation image" src="http://onlinelibrary.wiley.com/store/10.1002/jpln.201100022/asset/equation/tex2gif-ueqn-4.gif?v=1&amp;t=gyzvyb0n&amp;s=f2e9deabb8187a9fb328cddbbd800fc53d9355a1" class="inlineGraphic"/></span>-N and [NO<span class="math"><img alt="equation image" src="http://onlinelibrary.wiley.com/store/10.1002/jpln.201100022/asset/equation/tex2gif-ueqn-5.gif?v=1&amp;t=gyzvyb0o&amp;s=5eea5a17a30479bde9daffb03097ec99fb0ce72f" class="inlineGraphic"/></span> + NO<span class="math"><img alt="equation image" src="http://onlinelibrary.wiley.com/store/10.1002/jpln.201100022/asset/equation/tex2gif-ueqn-6.gif?v=1&amp;t=gyzvyb0p&amp;s=5fee61d8ae97b212e0d8d561c68ed0de84ed7d96" class="inlineGraphic"/></span>]-N) in the dual inoculation was 4 to 24 times those inoculated with earthworms or NFB alone, respectively. The significantly higher concentrations of bioavailable N and P in the dual inoculation of earthworms and NFB or PSB may be due to the higher abundance of PGPR and/or higher activities of urease and acid phosphatase than those of single inoculation of NFB or PSB, respectively. Dual inoculation of earthworms and PGPR would be most effective in reducing the need for chemical fertilizers in agriculture.</p></div>]]></content:encoded><description>Both earthworms and plant growth–promoting rhizobacteria (PGPR) are ubiquitous and important for promoting circulation of plant macronutrients. Two series of laboratory experiments were conducted to investigate the effects of earthworm casts and activities on the growth of PGPR, and the inoculation of earthworms and PGPR on the availability of N, P, and K in soils, respectively. During a short incubation period (0–34 h), the extracts of earthworm (Pheretima guillelmi)-worked soil significantly (p &lt; 0.05) increased the abundance of the three species of PGPR, including N-fixing bacteria (NFB) (Azotobacter chroococcum HKN-5), phosphate-solubilizing bacteria (PSB) (Bacillus megaterium HKP-1), and K-solubilizing bacteria (KSB) (B. mucilaginous HKK-1), in Luria-Bertani (LB) broth. There were synergistic effects of dual inoculation of earthworms and PGPR on increasing the concentrations of NH$ _4^+ $-N, (NO$ _3^- $ + NO$ _2^- $)-N, NaHCO3-extractable P, and NH4OAc-extractable K in the corresponding soils. Bioavailable N (the sum of NH$ _4^+ $-N and [NO$ _3^- $ + NO$ _2^- $]-N) in the dual inoculation was 4 to 24 times those inoculated with earthworms or NFB alone, respectively. The significantly higher concentrations of bioavailable N and P in the dual inoculation of earthworms and NFB or PSB may be due to the higher abundance of PGPR and/or higher activities of urease and acid phosphatase than those of single inoculation of NFB or PSB, respectively. Dual inoculation of earthworms and PGPR would be most effective in reducing the need for chemical fertilizers in agriculture.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201000434" xmlns="http://purl.org/rss/1.0/"><title>Glyphosate effects on photosynthesis, nutrient accumulation, and nodulation in glyphosate-resistant soybean</title><link>http://dx.doi.org/10.1002%2Fjpln.201000434</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Glyphosate effects on photosynthesis, nutrient accumulation, and nodulation in glyphosate-resistant soybean</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Luiz Henrique Saes Zobiole</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Robert John Kremer</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rubem Silvério de Oliveira Jr.</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jamil Constantin</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-13T08:41:47.080314-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201000434</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201000434</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201000434</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Previous greenhouse studies have demonstrated that photosynthesis in some cultivars of first- (GR1) and second-generation (GR2) glyphosate-resistant soybean was reduced by glyphosate. The reduction in photosynthesis that resulted from glyphosate might affect nutrient uptake and lead to lower plant biomass production and ultimately reduced grain yield. Therefore, a field study was conducted to determine if glyphosate-induced damage to soybean (<em>Glycine max</em> L. Merr. cv. Asgrow AG3539) plants observed under controlled greenhouse conditions might occur in the field environment. The present study evaluated photosynthetic rate, nutrient accumulation, nodulation, and biomass production of GR2 soybean receiving different rates of glyphosate (0, 800, 1200, 2400 g a.e. ha<sup>–1</sup>) applied at V2, V4, and V6 growth stages. In general, plant damage observed in the field study was similar to that in previous greenhouse studies. Increasing glyphosate rates and applications at later growth stages decreased nutrient accumulation, nodulation, leaf area, and shoot biomass production. Thus, to reduce potential undesirable effects of glyphosate on plant growth, application of the lowest glyphosate rate for weed-control efficacy at early growth stages (V2 to V4) is suggested as an advantageous practice within current weed control in GR soybean for optimal crop productivity.</p></div>]]></content:encoded><description>Previous greenhouse studies have demonstrated that photosynthesis in some cultivars of first- (GR1) and second-generation (GR2) glyphosate-resistant soybean was reduced by glyphosate. The reduction in photosynthesis that resulted from glyphosate might affect nutrient uptake and lead to lower plant biomass production and ultimately reduced grain yield. Therefore, a field study was conducted to determine if glyphosate-induced damage to soybean (Glycine max L. Merr. cv. Asgrow AG3539) plants observed under controlled greenhouse conditions might occur in the field environment. The present study evaluated photosynthetic rate, nutrient accumulation, nodulation, and biomass production of GR2 soybean receiving different rates of glyphosate (0, 800, 1200, 2400 g a.e. ha–1) applied at V2, V4, and V6 growth stages. In general, plant damage observed in the field study was similar to that in previous greenhouse studies. Increasing glyphosate rates and applications at later growth stages decreased nutrient accumulation, nodulation, leaf area, and shoot biomass production. Thus, to reduce potential undesirable effects of glyphosate on plant growth, application of the lowest glyphosate rate for weed-control efficacy at early growth stages (V2 to V4) is suggested as an advantageous practice within current weed control in GR soybean for optimal crop productivity.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201000361" xmlns="http://purl.org/rss/1.0/"><title>Effect of legume incorporation on solubization of Ogun phosphate rock on slightly acidic soils in SW Nigeria</title><link>http://dx.doi.org/10.1002%2Fjpln.201000361</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Effect of legume incorporation on solubization of Ogun phosphate rock on slightly acidic soils in SW Nigeria</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Olusola Olajumoke Adesanwo</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Michael Tunde Adetunji</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Sitapha Diatta</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-13T08:41:38.917744-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201000361</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201000361</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201000361</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Most soils in Nigeria are known to be slightly acidic and very low in plant-available P. These soils need to be fertilized for optimal crop production but cost and scarcity of mineral P fertilizers shifted attention to making direct application of indigenous phosphate rock viable alternative. Laboratory and greenhouse studies were carried out to monitor the effect of the decomposition of legume biomass on the solubilization of Ogun phosphate rock (OPR) on slightly acidic soils. Surface soil samples collected from three experimental sites in SW Nigeria were used. The fertilizer treatments were four rates of P as OPR (0, 30, 60, and 90 kg ha<sup>–1</sup>) and one rate of triple superphosphate (TSP, 40 kg P ha<sup>–1</sup>). The legume treatments were cowpea (<em>Vigna unguiculata</em> L Walp) and mucuna (<em>Mucuna puriens</em> L). Rice (<em>Oryza sativa</em>) was used in the greenhouse study as the test crop. Soil samples were analyzed for soluble P and pH after 2, 4, 6, and 10 months of incubation in the laboratory while plant tissues collected from greenhouse study were analyzed for P. In the incubation study, significant increase in water-soluble P was observed when legume biomass was incorporated with phosphate rock at <em>p</em> &lt; 0.05. Highest value in rice dry-matter yield was recorded with pots treated with mucuna and TSP, also treatment combination of cowpea and OPR significantly increased rice dry-matter yield by 16% over pots treated with cowpea biomass alone and 42% over control pot (no legume biomass and OPR in the green house (<em>p</em> &lt; 0.05). Thus incorporation of legume biomass significantly increased rate of OPR solubilization.</p></div>]]></content:encoded><description>Most soils in Nigeria are known to be slightly acidic and very low in plant-available P. These soils need to be fertilized for optimal crop production but cost and scarcity of mineral P fertilizers shifted attention to making direct application of indigenous phosphate rock viable alternative. Laboratory and greenhouse studies were carried out to monitor the effect of the decomposition of legume biomass on the solubilization of Ogun phosphate rock (OPR) on slightly acidic soils. Surface soil samples collected from three experimental sites in SW Nigeria were used. The fertilizer treatments were four rates of P as OPR (0, 30, 60, and 90 kg ha–1) and one rate of triple superphosphate (TSP, 40 kg P ha–1). The legume treatments were cowpea (Vigna unguiculata L Walp) and mucuna (Mucuna puriens L). Rice (Oryza sativa) was used in the greenhouse study as the test crop. Soil samples were analyzed for soluble P and pH after 2, 4, 6, and 10 months of incubation in the laboratory while plant tissues collected from greenhouse study were analyzed for P. In the incubation study, significant increase in water-soluble P was observed when legume biomass was incorporated with phosphate rock at p &lt; 0.05. Highest value in rice dry-matter yield was recorded with pots treated with mucuna and TSP, also treatment combination of cowpea and OPR significantly increased rice dry-matter yield by 16% over pots treated with cowpea biomass alone and 42% over control pot (no legume biomass and OPR in the green house (p &lt; 0.05). Thus incorporation of legume biomass significantly increased rate of OPR solubilization.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100058" xmlns="http://purl.org/rss/1.0/"><title>Acclimation of eggplant (Solanum melongena) to low boron supply</title><link>http://dx.doi.org/10.1002%2Fjpln.201100058</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Acclimation of eggplant (Solanum melongena) to low boron supply</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Georgios Liakopoulos</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Varvara Psaroudi</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Sotiria Stavrianakou</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Dimosthenis Nikolopoulos</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">George Karabourniotis</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-13T08:41:29.14718-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100058</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100058</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100058</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Root active uptake and remobilization of boron (B) have been accepted as mechanisms contributing to nutrient efficiency under low supply of boron. Here, we examined the existence of these mechanisms in eggplant (<em>Solanum melongena</em> L.) supplied either with luxury (100 μM, B+) or low (7.5 μM, B–) B in the growth medium <em>via</em> semihydroponic cultivation. Boron treatment was marginally not limiting growth thus avoiding side-effects and impairment of acclimation mechanisms of plants. The induction of a B-concentrating mechanism was evident in the roots as B concentration in the xylem sap was only decreased by 23% in B– compared to B+ plants, <em>i.e.</em>, B– roots concentrated B by a factor of 2.7 relative to the external solution. Leaf B concentration in the B– treatment decreased by 33% and 40% in young fully expanded and mature leaves, respectively. Larger differences were observed in the soluble B fraction that decreased by 65% in mature leaves. However, both total and soluble B concentrations in developing leaves were almost equal for both treatments exhibiting a pattern commonly observed in B-remobilizing plants. On the other hand, amounts of B export in the phloem sap were small compared to other species in which B is highly mobile. The B export rate from source leaves was slightly increased under low B supply while that of sucrose was not affected. We conclude that the root concentrating mechanism contributes to the alleviation of B deficiency in eggplant under low B supply while B remobilization may also contribute to a lower degree.</p></div>]]></content:encoded><description>Root active uptake and remobilization of boron (B) have been accepted as mechanisms contributing to nutrient efficiency under low supply of boron. Here, we examined the existence of these mechanisms in eggplant (Solanum melongena L.) supplied either with luxury (100 μM, B+) or low (7.5 μM, B–) B in the growth medium via semihydroponic cultivation. Boron treatment was marginally not limiting growth thus avoiding side-effects and impairment of acclimation mechanisms of plants. The induction of a B-concentrating mechanism was evident in the roots as B concentration in the xylem sap was only decreased by 23% in B– compared to B+ plants, i.e., B– roots concentrated B by a factor of 2.7 relative to the external solution. Leaf B concentration in the B– treatment decreased by 33% and 40% in young fully expanded and mature leaves, respectively. Larger differences were observed in the soluble B fraction that decreased by 65% in mature leaves. However, both total and soluble B concentrations in developing leaves were almost equal for both treatments exhibiting a pattern commonly observed in B-remobilizing plants. On the other hand, amounts of B export in the phloem sap were small compared to other species in which B is highly mobile. The B export rate from source leaves was slightly increased under low B supply while that of sucrose was not affected. We conclude that the root concentrating mechanism contributes to the alleviation of B deficiency in eggplant under low B supply while B remobilization may also contribute to a lower degree.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100063" xmlns="http://purl.org/rss/1.0/"><title>Soil-ecological evaluation of willows in a floodplain</title><link>http://dx.doi.org/10.1002%2Fjpln.201100063</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Soil-ecological evaluation of willows in a floodplain</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Dana Zimmer</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Christel Baum</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Ralph Meissner</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Peter Leinweber</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-24T06:10:39.227147-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100063</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100063</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100063</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Willows (<em>Salix</em> spp.) were supposed to be suitable candidates for the phytoremediation of polluted floodplain soils, but it is unknown how willow growth alters concentrations and mobility of pollutants under the conditions of ongoing periodically flooding. Therefore, effects of willow cropping on total concentrations and mobility of As and heavy metals and soil microbial properties were determined after three and four growing seasons under willows in comparison to native grassland in a flood channel of a River Elbe floodplain (Central Germany). After 4 y of willow coppice, the heavy metal concentrations (mg kg<sup>–1</sup>) were increased not only in the grass control plots (final Cu 274, Pb 276, Zn 935) but also under the willows (final Cu 248, Pb 251, Zn 779) compared to the initial concentrations (initial Cu 170, Pb 156, Zn 579). This increase might likely be caused by the ongoing sedimentation by flood events. The smaller increase under willows compared to grass might be related to an initial net effect of phytoextraction. The concentrations of the mobile fractions of Cd, Cu, Ni, and Zn were significantly lower under willows than under grass. Higher β-glucosidase activities under willows than under grass might indicate a starting net decomposition of organic matter. Therefore, the study of long-term and large-scale effects are recommend before an appropriate evaluation of willow short-rotation coppice for phytoremediation of polluted floodplains will be established.</p></div>]]></content:encoded><description>Willows (Salix spp.) were supposed to be suitable candidates for the phytoremediation of polluted floodplain soils, but it is unknown how willow growth alters concentrations and mobility of pollutants under the conditions of ongoing periodically flooding. Therefore, effects of willow cropping on total concentrations and mobility of As and heavy metals and soil microbial properties were determined after three and four growing seasons under willows in comparison to native grassland in a flood channel of a River Elbe floodplain (Central Germany). After 4 y of willow coppice, the heavy metal concentrations (mg kg–1) were increased not only in the grass control plots (final Cu 274, Pb 276, Zn 935) but also under the willows (final Cu 248, Pb 251, Zn 779) compared to the initial concentrations (initial Cu 170, Pb 156, Zn 579). This increase might likely be caused by the ongoing sedimentation by flood events. The smaller increase under willows compared to grass might be related to an initial net effect of phytoextraction. The concentrations of the mobile fractions of Cd, Cu, Ni, and Zn were significantly lower under willows than under grass. Higher β-glucosidase activities under willows than under grass might indicate a starting net decomposition of organic matter. Therefore, the study of long-term and large-scale effects are recommend before an appropriate evaluation of willow short-rotation coppice for phytoremediation of polluted floodplains will be established.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100005" xmlns="http://purl.org/rss/1.0/"><title>Evaluation of a local regression kriging approach for mapping apparent electrical conductivity of soil (ECa) at high resolution</title><link>http://dx.doi.org/10.1002%2Fjpln.201100005</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Evaluation of a local regression kriging approach for mapping apparent electrical conductivity of soil (ECa) at high resolution</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Wei Sun</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Brett M. Whelan</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Budiman Minasny</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Alex B. McBratney</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-01-24T03:20:54.161364-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100005</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100005</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100005</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Apparent electrical conductivity of soil (ECa) is a property frequently used as a diagnostic tool in precision agriculture, and is measured using vehicle-mounted proximal sensors. Crop-yield data, which is measured by harvester-mounted sensors, is usually collected at a higher spatial density compared to ECa. ECa and crop-yield maps frequently exhibit similar spatial patterns because ECa is primarily controlled by the soil clay content and the interrelated soil moisture content, which are often significant contributors to crop-yield potential. By quantifying the spatial relationship between soil ECa and crop yield, it is possible to estimate the value of ECa at the spatial resolution of the crop-yield data. This is achieved through the use of a local regression kriging approach which uses the higher-resolution crop-yield data as a covariate to predict ECa at a higher spatial resolution than would be prudent with the original ECa data alone. The accuracy of the local regression kriging (LRK) method is evaluated against local kriging (LK) and local regression (LR) to predict ECa. The results indicate that the performance of LRK is dependent on the performance of the inherent local regression. Over a range of ECa transect survey densities, LRK provides greater accuracy than LK and LR, except at very low density. Maps of the regression coefficients demonstrated that the relationship between ECa and crop yield varies from year to year, and across a field. The application of LRK to commercial scale ECa survey data, using crop yield as a covariate, should improve the accuracy of the resultant maps. This has implications for employing the maps in crop-management decisions and building more robust calibrations between field-gathered soil ECa and primary soil properties such as clay content.</p></div>]]></content:encoded><description>Apparent electrical conductivity of soil (ECa) is a property frequently used as a diagnostic tool in precision agriculture, and is measured using vehicle-mounted proximal sensors. Crop-yield data, which is measured by harvester-mounted sensors, is usually collected at a higher spatial density compared to ECa. ECa and crop-yield maps frequently exhibit similar spatial patterns because ECa is primarily controlled by the soil clay content and the interrelated soil moisture content, which are often significant contributors to crop-yield potential. By quantifying the spatial relationship between soil ECa and crop yield, it is possible to estimate the value of ECa at the spatial resolution of the crop-yield data. This is achieved through the use of a local regression kriging approach which uses the higher-resolution crop-yield data as a covariate to predict ECa at a higher spatial resolution than would be prudent with the original ECa data alone. The accuracy of the local regression kriging (LRK) method is evaluated against local kriging (LK) and local regression (LR) to predict ECa. The results indicate that the performance of LRK is dependent on the performance of the inherent local regression. Over a range of ECa transect survey densities, LRK provides greater accuracy than LK and LR, except at very low density. Maps of the regression coefficients demonstrated that the relationship between ECa and crop yield varies from year to year, and across a field. The application of LRK to commercial scale ECa survey data, using crop yield as a covariate, should improve the accuracy of the resultant maps. This has implications for employing the maps in crop-management decisions and building more robust calibrations between field-gathered soil ECa and primary soil properties such as clay content.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201000046" xmlns="http://purl.org/rss/1.0/"><title>Vertical distribution of soluble organic nitrogen, nitrogen mineralization, nitrification, and amidohydrolase activities in a manure-treated soil</title><link>http://dx.doi.org/10.1002%2Fjpln.201000046</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Vertical distribution of soluble organic nitrogen, nitrogen mineralization, nitrification, and amidohydrolase activities in a manure-treated soil</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Banafshe Khalili</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Farshid Nourbakhsh</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-12-01T08:21:21.554393-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201000046</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201000046</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201000046</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Recent studies indicate that soil soluble organic nitrogen (SON) plays an important regulatory role in the soil–plant N cycle. The aims of this study were to identify the vertical distribution of SON and its correlation with N mineralization, nitrification, and amidohydrolase activities, in a soil repeatedly amended with cow manure or chemical fertilizer. For this purpose, soil samples were collected from 0–20, 20–40, 40–60, 60–80, and 80–100 cm depths of a calcareous soil, which has been annually amended for 5 y with cow manure (CM) at two rates of 50 (CM<sub>50</sub>) and 100 (CM<sub>100</sub>) Mg CM ha<sup>–1</sup> y<sup>–1</sup>. Treatments with chemical fertilizer (CF) and a control (CT) were also included. Soluble organic N, N mineralization, nitrification rates, as well as L-glutaminase and L-asparaginase activities were determined. Both CM<sub>50</sub> and CM<sub>100</sub> enhanced SON content throughout the soil profile. Nitrogen-mineralization rate (N<sub>m</sub>) was increased at the 0–20 cm depth of the CM<sub>100</sub> treatment and remained unaffected at the deeper depths. Nitrification rate (N<sub>n</sub>) was significantly higher at the 0–60 cm depth of CM<sub>100</sub> compared to CF and CT. L-glutaminase and L-asparaginase activities were significantly increased at the 0–40 cm depth in both CM<sub>50</sub> and CM<sub>100</sub> compared to CF and CT. The amidohydrolase activities could not be detected below 40 cm, regardless of the fertilizer treatments. Our results suggest that SON makes a minor contribution to N mineralization in deep soil layers. It was also concluded that changes in the SON throughout the soil profile were not associated with changes in the N-transformation rates (N<sub>m</sub> and N<sub>n</sub>) and amidohydrolase activities. While we conclude that SON is a major N pool in the whole profile of the manure applied soil further investigation is required to characterize SON and to investigate the bioavailability of SON for microbial activity in different soil depths.</p></div>]]></content:encoded><description>Recent studies indicate that soil soluble organic nitrogen (SON) plays an important regulatory role in the soil–plant N cycle. The aims of this study were to identify the vertical distribution of SON and its correlation with N mineralization, nitrification, and amidohydrolase activities, in a soil repeatedly amended with cow manure or chemical fertilizer. For this purpose, soil samples were collected from 0–20, 20–40, 40–60, 60–80, and 80–100 cm depths of a calcareous soil, which has been annually amended for 5 y with cow manure (CM) at two rates of 50 (CM50) and 100 (CM100) Mg CM ha–1 y–1. Treatments with chemical fertilizer (CF) and a control (CT) were also included. Soluble organic N, N mineralization, nitrification rates, as well as L-glutaminase and L-asparaginase activities were determined. Both CM50 and CM100 enhanced SON content throughout the soil profile. Nitrogen-mineralization rate (Nm) was increased at the 0–20 cm depth of the CM100 treatment and remained unaffected at the deeper depths. Nitrification rate (Nn) was significantly higher at the 0–60 cm depth of CM100 compared to CF and CT. L-glutaminase and L-asparaginase activities were significantly increased at the 0–40 cm depth in both CM50 and CM100 compared to CF and CT. The amidohydrolase activities could not be detected below 40 cm, regardless of the fertilizer treatments. Our results suggest that SON makes a minor contribution to N mineralization in deep soil layers. It was also concluded that changes in the SON throughout the soil profile were not associated with changes in the N-transformation rates (Nm and Nn) and amidohydrolase activities. While we conclude that SON is a major N pool in the whole profile of the manure applied soil further investigation is required to characterize SON and to investigate the bioavailability of SON for microbial activity in different soil depths.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201000399" xmlns="http://purl.org/rss/1.0/"><title>Equivalence or complementarity of soil-solution extraction methods</title><link>http://dx.doi.org/10.1002%2Fjpln.201000399</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Equivalence or complementarity of soil-solution extraction methods</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Dominik Schlotter</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Helmer Schack-Kirchner</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Ernst E. Hildebrand</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Klaus von Wilpert</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-12-01T08:21:15.012988-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201000399</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201000399</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201000399</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Several methods are used for the extraction of soil solution. The objective of this study was to find out to what extent the different extraction methods yield complementary or equivalent information. Soil solutions were sampled once at 10 different forest sites in Germany, with 4 sampling points per site, using 5 different extraction methods. Concentrations of the major ions in the 1:2 extracts and the equilibrium soil-pore solutions (obtained from percolation of field-fresh soil cores) were generally lower than in desorption solutions, suction-cup solutions, and saturation extracts. Surprisingly, the latter three methods generally yielded equivalent results. However, possible systematic differences between these methods could have been masked by the high small-scale spatial variability within the sites.</p></div>]]></content:encoded><description>Several methods are used for the extraction of soil solution. The objective of this study was to find out to what extent the different extraction methods yield complementary or equivalent information. Soil solutions were sampled once at 10 different forest sites in Germany, with 4 sampling points per site, using 5 different extraction methods. Concentrations of the major ions in the 1:2 extracts and the equilibrium soil-pore solutions (obtained from percolation of field-fresh soil cores) were generally lower than in desorption solutions, suction-cup solutions, and saturation extracts. Surprisingly, the latter three methods generally yielded equivalent results. However, possible systematic differences between these methods could have been masked by the high small-scale spatial variability within the sites.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201000358" xmlns="http://purl.org/rss/1.0/"><title>Analysis of ammonia losses after field application of biogas slurries by an empirical model</title><link>http://dx.doi.org/10.1002%2Fjpln.201000358</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Analysis of ammonia losses after field application of biogas slurries by an empirical model</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Kang Ni</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Andreas Pacholski</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Dirk Gericke</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Henning Kage</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2011-11-22T09:10:48.76456-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201000358</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201000358</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201000358</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Due to energy crises and stricter environmental regulations, renewable energy sources like bio-methane produced by anaerobic digestion (biogas) become increasingly important. However, the application of slurries produced by biogas fermentation to agricultural land and subsequent ammonia emission may also create environmental risks to the atmosphere and to N-limited ecosystems. Evaluating ammonia loss from agricultural land by model simulation is an important tool of agricultural-systems analysis. The objective of this study was the systematical comparison of ammonia volatilization after application of two types of biogas slurries containing high amounts of energy crops in comparison with conventional animal slurries and to investigate the relative importance of factors affecting the emission process through an empirical model. A high number of ammonia-loss field measurements were carried out in the years 2007/08 in biogas cropping systems in N Germany. The study consisted of simultaneous measurement of NH<sub>3</sub> losses from animal and biogas slurries in multiple-plot field experiments with different N-fertilization levels. The derived empirical model for the calculation of NH<sub>3</sub> losses based on explanatory variables gave good predictions of ammonia emission for both biogas and pig slurries. The root mean square error (<em>RMSE</em>) and mean bias error (<em>MBE</em>) of the empirical model for validation data were 2.19 kg N ha<sup>–1</sup> (<em>rRMSE</em> 29%) and –1.19 kg N ha<sup>–1</sup>, respectively. Biogas slurries produced highest NH<sub>3</sub> emissions compared to the two animal slurries. In view of the explanatory variables included in the model, total NH<span class="math"><img alt="equation image" src="http://onlinelibrary.wiley.com/store/10.1002/jpln.201000358/asset/equation/tex2gif-ueqn-1.gif?v=1&amp;t=gyzvyb86&amp;s=2a981cf959f5b7037f9acc5cadfd013dedaa6d63" class="inlineGraphic"/></span> application rate, slurry type, temperature, precipitation, crop type, and leaf-area index were important for ammonia-volatilization losses.</p></div>]]></content:encoded><description>Due to energy crises and stricter environmental regulations, renewable energy sources like bio-methane produced by anaerobic digestion (biogas) become increasingly important. However, the application of slurries produced by biogas fermentation to agricultural land and subsequent ammonia emission may also create environmental risks to the atmosphere and to N-limited ecosystems. Evaluating ammonia loss from agricultural land by model simulation is an important tool of agricultural-systems analysis. The objective of this study was the systematical comparison of ammonia volatilization after application of two types of biogas slurries containing high amounts of energy crops in comparison with conventional animal slurries and to investigate the relative importance of factors affecting the emission process through an empirical model. A high number of ammonia-loss field measurements were carried out in the years 2007/08 in biogas cropping systems in N Germany. The study consisted of simultaneous measurement of NH3 losses from animal and biogas slurries in multiple-plot field experiments with different N-fertilization levels. The derived empirical model for the calculation of NH3 losses based on explanatory variables gave good predictions of ammonia emission for both biogas and pig slurries. The root mean square error (RMSE) and mean bias error (MBE) of the empirical model for validation data were 2.19 kg N ha–1 (rRMSE 29%) and –1.19 kg N ha–1, respectively. Biogas slurries produced highest NH3 emissions compared to the two animal slurries. In view of the explanatory variables included in the model, total NH$ _4^+ $ application rate, slurry type, temperature, precipitation, crop type, and leaf-area index were important for ammonia-volatilization losses.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201290000" xmlns="http://purl.org/rss/1.0/"><title>Cover Picture: J. Plant Nutr. Soil Sci. 1/2012</title><link>http://dx.doi.org/10.1002%2Fjpln.201290000</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Cover Picture: J. Plant Nutr. Soil Sci. 1/2012</dc:title><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201290000</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201290000</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201290000</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Cover Picture</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[]]></content:encoded><description/></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201290007" xmlns="http://purl.org/rss/1.0/"><title>Editorial Board: J. Plant Nutr. Soil Sci. 1/2012</title><link>http://dx.doi.org/10.1002%2Fjpln.201290007</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Editorial Board: J. Plant Nutr. Soil Sci. 1/2012</dc:title><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201290007</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201290007</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201290007</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Editorial Board</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">1</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">1</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[]]></content:encoded><description/></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201290004" xmlns="http://purl.org/rss/1.0/"><title>Impressum: J. Plant Nutr. Soil Sci. 1/2012</title><link>http://dx.doi.org/10.1002%2Fjpln.201290004</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Impressum: J. Plant Nutr. Soil Sci. 1/2012</dc:title><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201290004</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201290004</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201290004</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Impressum</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">2</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">2</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[]]></content:encoded><description/></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201290005" xmlns="http://purl.org/rss/1.0/"><title>Editorial J. Plant Nutr. Soil Sci. 1/2012</title><link>http://dx.doi.org/10.1002%2Fjpln.201290005</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Editorial J. Plant Nutr. Soil Sci. 1/2012</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Karl-Heinz Feger</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Sven Schubert</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201290005</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201290005</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201290005</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Editorial</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">3</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">3</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[]]></content:encoded><description/></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100075" xmlns="http://purl.org/rss/1.0/"><title>Physical properties of a Luvisol for different long-term fertilization treatments: I. Mesoscale capacity and intensity parameters</title><link>http://dx.doi.org/10.1002%2Fjpln.201100075</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Physical properties of a Luvisol for different long-term fertilization treatments: I. Mesoscale capacity and intensity parameters</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Dörthe Holthusen</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Markus Jänicke</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Stephan Peth</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rainer Horn</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100075</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100075</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100075</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">4</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">13</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The physical properties of a Luvisol derived from loess near Bonn, Germany, under different long-term fertilization treatments were examined. For the investigation of the impact of farmyard manure (FYM) on soil strength at the mesoscale (100 to 300 cm<sup>3</sup> soil cores), undisturbed samples were taken from two different depths (10 and 40 cm), either with no fertilization at all, with full mineral fertilization, with FYM only, and with both mineral and organic fertilization. We investigated hydraulic and mechanical parameters, namely precompression stress, pore-size distribution, saturated hydraulic and air conductivity, and calculated pore connectivity. Long-term organic fertilization resulted in significantly more and coarser pores which in addition were more conductant and mechanically stronger by trend. Mineral fertilization also increased pore volume by trend but not pore functionality. Mechanical strength generally increased with fertilization by trend, however, was reduced again when organic and mineral fertilization were combined. Nonetheless, FYM led to relatively higher soil strength as the FYM-treated plots with lower bulk density attained similar soil strength as the unfertilized but denser plots and thus supported the soil-improving impact of organic amendments. The subsoil physical properties were rather unaffected by fertilization, but were dominated by texture.</p></div>]]></content:encoded><description>The physical properties of a Luvisol derived from loess near Bonn, Germany, under different long-term fertilization treatments were examined. For the investigation of the impact of farmyard manure (FYM) on soil strength at the mesoscale (100 to 300 cm3 soil cores), undisturbed samples were taken from two different depths (10 and 40 cm), either with no fertilization at all, with full mineral fertilization, with FYM only, and with both mineral and organic fertilization. We investigated hydraulic and mechanical parameters, namely precompression stress, pore-size distribution, saturated hydraulic and air conductivity, and calculated pore connectivity. Long-term organic fertilization resulted in significantly more and coarser pores which in addition were more conductant and mechanically stronger by trend. Mineral fertilization also increased pore volume by trend but not pore functionality. Mechanical strength generally increased with fertilization by trend, however, was reduced again when organic and mineral fertilization were combined. Nonetheless, FYM led to relatively higher soil strength as the FYM-treated plots with lower bulk density attained similar soil strength as the unfertilized but denser plots and thus supported the soil-improving impact of organic amendments. The subsoil physical properties were rather unaffected by fertilization, but were dominated by texture.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100076" xmlns="http://purl.org/rss/1.0/"><title>Physical properties of a Luvisol for different long-term fertilization treatments: II. Microscale behavior and its relation to the mesoscale</title><link>http://dx.doi.org/10.1002%2Fjpln.201100076</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Physical properties of a Luvisol for different long-term fertilization treatments: II. Microscale behavior and its relation to the mesoscale</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Dörthe Holthusen</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Markus Jänicke</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Stephan Peth</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rainer Horn</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100076</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100076</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100076</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">14</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">23</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>We determined the impact of different fertilization, namely organic <em>vs.</em> mineral fertilization, on the mesoscale parameter cyclic compressibility as well as on rheology of soil samples as a microscale parameter and how these parameters are related. Therefore, undisturbed samples were taken from a long-term fertilization trial at the Dikop farm near Bonn (Germany) and tested for their mechanical and hydraulic properties. This paper examines the sensitivity of the soil towards cyclic loading (mesoscale) and oscillatory shearing at the microscale by means of an amplitude sweep test and the resulting parameter maximum shear stress. Fertilization increased cyclic compressibility and thus revealed structural weakness of fertilized soil samples, so did shear stress at the microscale. The main reason for this was a decrease in bulk density in the wake of fertilization. However, within the range of fertilized soil samples, the soil structure became less susceptible towards cyclic loading and oscillatory shearing, respectively, the more organic matter the soil contained (equivalent to the fertilization level). This was assumedly caused by enhanced cementation due to organic substances that could partly substitute the direct grain–grain contacts generally contributing to soil strength. The similar behavior of cyclic compressibility and maximum shear stress enabled a first approach to relate soil mechanical parameters at the microscale to those at the mesoscale.</p></div>]]></content:encoded><description>We determined the impact of different fertilization, namely organic vs. mineral fertilization, on the mesoscale parameter cyclic compressibility as well as on rheology of soil samples as a microscale parameter and how these parameters are related. Therefore, undisturbed samples were taken from a long-term fertilization trial at the Dikop farm near Bonn (Germany) and tested for their mechanical and hydraulic properties. This paper examines the sensitivity of the soil towards cyclic loading (mesoscale) and oscillatory shearing at the microscale by means of an amplitude sweep test and the resulting parameter maximum shear stress. Fertilization increased cyclic compressibility and thus revealed structural weakness of fertilized soil samples, so did shear stress at the microscale. The main reason for this was a decrease in bulk density in the wake of fertilization. However, within the range of fertilized soil samples, the soil structure became less susceptible towards cyclic loading and oscillatory shearing, respectively, the more organic matter the soil contained (equivalent to the fertilization level). This was assumedly caused by enhanced cementation due to organic substances that could partly substitute the direct grain–grain contacts generally contributing to soil strength. The similar behavior of cyclic compressibility and maximum shear stress enabled a first approach to relate soil mechanical parameters at the microscale to those at the mesoscale.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201000403" xmlns="http://purl.org/rss/1.0/"><title>Deformation damages in forest topsoils—An assessment based on Level-I soil monitoring data from Baden-Württemberg (SW Germany)</title><link>http://dx.doi.org/10.1002%2Fjpln.201000403</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Deformation damages in forest topsoils—An assessment based on Level-I soil monitoring data from Baden-Württemberg (SW Germany)</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Jürgen Schäffer</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Hermann Buberl</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Klaus von Wilpert</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201000403</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201000403</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201000403</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">24</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">33</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Acidification and eutrophication of soils had been the main activators for the implementation of forest soil monitoring in Central Europe. Thus, field and lab studies focused on gathering information that is essential for the evaluation of the chemical status and its trend. A systematic assessment of soil physical threats caused by machine use in forests has not been integrated yet into the soil-monitoring systems. In this study, a first approach to get a deeper insight into structure damages of forest topsoils was derived for 302 systematically distributed grid points in the Federal State of Baden-Württemberg (SW Germany) during the nation-wide soil survey performed from 2006 to 2008. We derived an approach to assess structure damage based on a key system using field information on structural and hydromorphic topsoil properties. It covers eight satellites surrounding the central monitoring soil pit at each grid point. Our survey focused on the mere stand area excluding visible damage and systematic skid trails. Analysis of structure-damage intensity and spatial distribution leads to the conclusion that damage caused by vehicle traffic off the skid trails is a wide-spread phenomena in Baden-Württemberg forests, where wheeling is not restricted by steepness of terrain. Although regulations to control machine use recommending vehicle traffic to skid trails and fortified roads have been in place since the early 1980s, soil-structure damages off these trails have reached significant levels. In the future, it will thus be indispensable to put more emphasis on the importance of soil-protection aims in the ranking of the economic objectives of forest organizations and forest owners.</p></div>]]></content:encoded><description>Acidification and eutrophication of soils had been the main activators for the implementation of forest soil monitoring in Central Europe. Thus, field and lab studies focused on gathering information that is essential for the evaluation of the chemical status and its trend. A systematic assessment of soil physical threats caused by machine use in forests has not been integrated yet into the soil-monitoring systems. In this study, a first approach to get a deeper insight into structure damages of forest topsoils was derived for 302 systematically distributed grid points in the Federal State of Baden-Württemberg (SW Germany) during the nation-wide soil survey performed from 2006 to 2008. We derived an approach to assess structure damage based on a key system using field information on structural and hydromorphic topsoil properties. It covers eight satellites surrounding the central monitoring soil pit at each grid point. Our survey focused on the mere stand area excluding visible damage and systematic skid trails. Analysis of structure-damage intensity and spatial distribution leads to the conclusion that damage caused by vehicle traffic off the skid trails is a wide-spread phenomena in Baden-Württemberg forests, where wheeling is not restricted by steepness of terrain. Although regulations to control machine use recommending vehicle traffic to skid trails and fortified roads have been in place since the early 1980s, soil-structure damages off these trails have reached significant levels. In the future, it will thus be indispensable to put more emphasis on the importance of soil-protection aims in the ranking of the economic objectives of forest organizations and forest owners.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201000438" xmlns="http://purl.org/rss/1.0/"><title>Gas diffusivity in soils compared to ideal isotropic porous media</title><link>http://dx.doi.org/10.1002%2Fjpln.201000438</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Gas diffusivity in soils compared to ideal isotropic porous media</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Anke Kühne</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Helmer Schack-Kirchner</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Ernst E. Hildebrand</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201000438</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201000438</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201000438</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">34</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">45</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Evidence of anisotropy is reported for advective air and water permeabilities in soils. Thus, anisotropy is likely to exist also for diffusive gas fluxes. Information about direction-dependent soil gas diffusivity is scarce and most modeling approaches assume isotropy. At hundreds of closely lying positions in a compacted and adjacent undisturbed forest soil, gas diffusivity (<em>D</em><sub>s</sub>/<em>D</em><sub>0</sub>) was measured either in vertical or horizontal direction. The volume-independent diffusion efficiency (<em>i.e.,</em> diffusivity divided by air-filled porosity) was fitted by a generalized additive model (GAM). Significant regressors were air-filled porosity (ϵ), soil depth, and the discrete diffusion direction. The model yields in all cases higher vertical diffusion efficiencies. The compaction factor did not yield a significant regressor of its own, <em>i.e.,</em> the reduction of diffusivity in the compacted soil was the same as in low-porosity samples of the undisturbed profile. To elucidate the role of sharing vertically and horizontally orientated pore space and a potential competition between diffusivity in different spatial directions, simple geometric models consisting of 3-dimensionally crossed pores have been parameterized. These models provided a good explanation of the typical nonlinear <em>D</em><sub>s</sub>/<em>D</em><sub>0</sub>(ϵ) relationship. By simple one-parameter correction (linear or power function), this mechanistic model could be fitted to the data. The one-parameter correction of the geometric model could be a straightforward approach to consider direction dependence of measured diffusivities. However, by applying this approach to the observations the anisotropy effect was not clearly evident, which could be attributed to a changing <em>D</em><sub>s</sub>/<em>D</em><sub>0</sub>(ϵ) relationship with depth. As a reason for the preference of the vertical gas diffusion the dominance of vertical stresses and the activity of anecic earthworms are discussed. Direction dependency of gas diffusivity seems to be a basic feature of natural pore systems and has to be considered for modeling gas fluxes in soils. Generally, a preferential vertical diffusion direction reduces horizontal balancing and increases the heterogeneity of gas concentrations in the soil air.</p></div>]]></content:encoded><description>Evidence of anisotropy is reported for advective air and water permeabilities in soils. Thus, anisotropy is likely to exist also for diffusive gas fluxes. Information about direction-dependent soil gas diffusivity is scarce and most modeling approaches assume isotropy. At hundreds of closely lying positions in a compacted and adjacent undisturbed forest soil, gas diffusivity (Ds/D0) was measured either in vertical or horizontal direction. The volume-independent diffusion efficiency (i.e., diffusivity divided by air-filled porosity) was fitted by a generalized additive model (GAM). Significant regressors were air-filled porosity (ϵ), soil depth, and the discrete diffusion direction. The model yields in all cases higher vertical diffusion efficiencies. The compaction factor did not yield a significant regressor of its own, i.e., the reduction of diffusivity in the compacted soil was the same as in low-porosity samples of the undisturbed profile. To elucidate the role of sharing vertically and horizontally orientated pore space and a potential competition between diffusivity in different spatial directions, simple geometric models consisting of 3-dimensionally crossed pores have been parameterized. These models provided a good explanation of the typical nonlinear Ds/D0(ϵ) relationship. By simple one-parameter correction (linear or power function), this mechanistic model could be fitted to the data. The one-parameter correction of the geometric model could be a straightforward approach to consider direction dependence of measured diffusivities. However, by applying this approach to the observations the anisotropy effect was not clearly evident, which could be attributed to a changing Ds/D0(ϵ) relationship with depth. As a reason for the preference of the vertical gas diffusion the dominance of vertical stresses and the activity of anecic earthworms are discussed. Direction dependency of gas diffusivity seems to be a basic feature of natural pore systems and has to be considered for modeling gas fluxes in soils. Generally, a preferential vertical diffusion direction reduces horizontal balancing and increases the heterogeneity of gas concentrations in the soil air.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100072" xmlns="http://purl.org/rss/1.0/"><title>Residence time of fine-root carbon using radiocarbon measurements of samples collected from a soil archive</title><link>http://dx.doi.org/10.1002%2Fjpln.201100072</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Residence time of fine-root carbon using radiocarbon measurements of samples collected from a soil archive</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Mats Fröberg</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100072</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100072</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100072</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Short Communication</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">46</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">48</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Fine roots from the soil archive of the Swedish National Forest Soil Inventory, collected in 1964, 1972, 1985, and 1998, were analyzed for <sup>14</sup>C contents. Two different methods of estimating residence time were compared. Residence time of root C was estimated to be 8 y using a steady state 1-pool model.</p></div>]]></content:encoded><description>Fine roots from the soil archive of the Swedish National Forest Soil Inventory, collected in 1964, 1972, 1985, and 1998, were analyzed for 14C contents. Two different methods of estimating residence time were compared. Residence time of root C was estimated to be 8 y using a steady state 1-pool model.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100186" xmlns="http://purl.org/rss/1.0/"><title>Simplified equations for the determination of the hydraulic properties of horticultural substrates by one-step outflow experiments</title><link>http://dx.doi.org/10.1002%2Fjpln.201100186</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Simplified equations for the determination of the hydraulic properties of horticultural substrates by one-step outflow experiments</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">John D. Valiantzas</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Paraskevi A. Londra</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100186</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100186</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100186</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Short Communication</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">49</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">52</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Simplified algebraic equations are derived to calculate directly the Brooks and Corey model parameters using data obtained from one-step outflow experiments and saturated hydraulic conductivity. The suggested method has been demonstrated only for horticultural substrates and is verified experimentally for four substrates with satisfactory agreement of the results.</p></div>]]></content:encoded><description>Simplified algebraic equations are derived to calculate directly the Brooks and Corey model parameters using data obtained from one-step outflow experiments and saturated hydraulic conductivity. The suggested method has been demonstrated only for horticultural substrates and is verified experimentally for four substrates with satisfactory agreement of the results.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100253" xmlns="http://purl.org/rss/1.0/"><title>Christian G. Ehrenberg and the birth of soil microbiology in the middle of the 19th century</title><link>http://dx.doi.org/10.1002%2Fjpln.201100253</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Christian G. Ehrenberg and the birth of soil microbiology in the middle of the 19th century</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Hans-Peter Blume</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Manfred Bölter</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Wolf-Henning Kusber</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100253</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100253</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100253</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">53</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">59</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Early in the 19th century, the German doctor and natural scientist Christian G. Ehrenberg (1795–1876) determined and classified through microscopic investigation the species and contents of microorganisms (bacteria, algae, diatoms, protozoa) of more than 1000 soil samples from all over the world. He identified phytoliths and minerals using a polarization microscope and described the morphology of the organic particles. Two of his soil descriptions were a Chernozem from Russia and an Ornithogenic Cryosol of the Maritime Antarctic. He further identified several soil-forming processes like the formation and decomposition of organic matter, mineral weathering, and new formation of carbonates, Fe oxides, and silicate under the influence of microorganisms long before other investigators. Although this was criticized during his time, it is still fully accepted today. Therefore, Ehrenberg can be regarded as the main founder of soil microbiology and as a pioneer in soil micromorphology.</p></div>]]></content:encoded><description>Early in the 19th century, the German doctor and natural scientist Christian G. Ehrenberg (1795–1876) determined and classified through microscopic investigation the species and contents of microorganisms (bacteria, algae, diatoms, protozoa) of more than 1000 soil samples from all over the world. He identified phytoliths and minerals using a polarization microscope and described the morphology of the organic particles. Two of his soil descriptions were a Chernozem from Russia and an Ornithogenic Cryosol of the Maritime Antarctic. He further identified several soil-forming processes like the formation and decomposition of organic matter, mineral weathering, and new formation of carbonates, Fe oxides, and silicate under the influence of microorganisms long before other investigators. Although this was criticized during his time, it is still fully accepted today. Therefore, Ehrenberg can be regarded as the main founder of soil microbiology and as a pioneer in soil micromorphology.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100097" xmlns="http://purl.org/rss/1.0/"><title>Soil sulfur fractions dynamics and distribution in a tropical grass pasture amended with nitrogen and sulfur fertilizers</title><link>http://dx.doi.org/10.1002%2Fjpln.201100097</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Soil sulfur fractions dynamics and distribution in a tropical grass pasture amended with nitrogen and sulfur fertilizers</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Fabiana Schmidt</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Fabiano Daniel De Bona</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Cristiane Prezotto Silveira</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Francisco Antonio Monteiro</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100097</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100097</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100097</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">60</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">67</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Soil sulfur (S) partitioning among the various pools and changes in tropical pasture ecosystems remain poorly understood. Our study aimed to investigate the dynamics and distribution of soil S fractions in an 8-year-old signal grass (<em>Brachiaria decumbens</em> Stapf.) pasture fertilized with nitrogen (N) and S. A factorial combination of two N rates (0 and 600 kg N ha<sup>–1</sup> y<sup>–1</sup>, as NH<sub>4</sub>NO<sub>3</sub>) and two S rates (0 and 60 kg S ha<sup>–1</sup> y<sup>–1</sup>, as gypsum) were applied to signal grass pastures during 2 y. Cattle grazing was controlled during the experimental period. Organic S was the major S pool found in the tropical pasture soil, and represented 97% to 99% of total S content. Among the organic S fractions, residual S was the most abundant (42% to 67% of total S), followed by ester-bonded S (19% to 42%), and C-bonded S (11% to 19%). Plant-available inorganic SO<sub>4</sub>-S concentrations were very low, even for the treatments receiving S fertilizers. Low inorganic SO<sub>4</sub>-S stocks suggest that S losses may play a major role in S dynamics of sandy tropical soils. Nitrogen and S additions affected forage yield, S plant uptake, and organic S fractions in the soil. Among the various soil fractions, residual S showed the greatest changes in response to N and S fertilization. Soil organic S increased in plots fertilized with S following the residual S fraction increment (16.6% to 34.8%). Soils cultivated without N and S fertilization showed a decrease in all soil organic S fractions.</p></div>]]></content:encoded><description>Soil sulfur (S) partitioning among the various pools and changes in tropical pasture ecosystems remain poorly understood. Our study aimed to investigate the dynamics and distribution of soil S fractions in an 8-year-old signal grass (Brachiaria decumbens Stapf.) pasture fertilized with nitrogen (N) and S. A factorial combination of two N rates (0 and 600 kg N ha–1 y–1, as NH4NO3) and two S rates (0 and 60 kg S ha–1 y–1, as gypsum) were applied to signal grass pastures during 2 y. Cattle grazing was controlled during the experimental period. Organic S was the major S pool found in the tropical pasture soil, and represented 97% to 99% of total S content. Among the organic S fractions, residual S was the most abundant (42% to 67% of total S), followed by ester-bonded S (19% to 42%), and C-bonded S (11% to 19%). Plant-available inorganic SO4-S concentrations were very low, even for the treatments receiving S fertilizers. Low inorganic SO4-S stocks suggest that S losses may play a major role in S dynamics of sandy tropical soils. Nitrogen and S additions affected forage yield, S plant uptake, and organic S fractions in the soil. Among the various soil fractions, residual S showed the greatest changes in response to N and S fertilization. Soil organic S increased in plots fertilized with S following the residual S fraction increment (16.6% to 34.8%). Soils cultivated without N and S fertilization showed a decrease in all soil organic S fractions.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201000415" xmlns="http://purl.org/rss/1.0/"><title>Effects of vegetation type on mercury concentrations and pools in two adjacent coniferous and deciduous forests</title><link>http://dx.doi.org/10.1002%2Fjpln.201000415</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Effects of vegetation type on mercury concentrations and pools in two adjacent coniferous and deciduous forests</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Daniel Obrist</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Dale W. Johnson</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Robert L. Edmonds</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201000415</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201000415</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201000415</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">68</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">77</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Vegetation type and ecosystem structure affect major aspects of the mercury (Hg) cycle in terrestrial ecosystems which serve as important storage pools for a long-term legacy of natural and anthropogenic Hg release to the environment. The goal of this study was to evaluate the integrated effects of 80 y of different vegetative type on Hg accumulation and partitioning in terrestrial ecosystems by comparing Hg concentrations and pools of two adjacent forests: a coniferous Douglas fir (<em>Pseudotsuga menziesii</em>) and a deciduous red alder (<em>Alnus rubra</em>) stand. These stands grew for &gt; 80 y in close proximity (200 m) with identical site histories, soil parent materials, and atmospheric exposure. Results showed that the Douglas fir stand was characterized by significantly higher Hg concentrations and Hg : C ratios in aboveground biomass compared to the deciduous red alder forest. For foliage, higher Hg concentrations (<em>plus</em> 43 μg kg<sup>–1</sup>) were expected due to foliage age, but Hg concentrations also were higher in woody tissues (by 2 to 18 μg kg<sup>–1</sup>) indicating increased uptake of atmospheric Hg by coniferous tissues. These differences were reflected—and further increased—in litter horizons where Hg-concentration differences increased in highly decomposed litter to &gt; 200 μg kg<sup>–1</sup>. In soils, no difference in concentrations of Hg was observed, but Hg : C ratios were consistently higher in the coniferous Douglas fir. Estimation of pool sizes of C and Hg in soils and at the whole ecosystem level showed that considerably smaller C pools in the coniferous stand as a result of faster C turnover and lower productivity did not lead to corresponding declines in Hg-pool sizes. The partitioning of Hg among ecosystem components—including distribution between aboveground and belowground components and distribution through the soil profile—was largely unaffected by forest type. Methyl-Hg concentrations observed in litter layers were also significantly higher in litter of Douglas fir, along with a higher proportion of methylated Hg of total Hg. In soils, methyl-Hg concentrations were similar in both stands. Comparison of these adjacent forest stands highlights that vegetation type affects concentrations of total Hg in otherwise equivalent sites and that differences also exist in respect to methylated Hg.</p></div>]]></content:encoded><description>Vegetation type and ecosystem structure affect major aspects of the mercury (Hg) cycle in terrestrial ecosystems which serve as important storage pools for a long-term legacy of natural and anthropogenic Hg release to the environment. The goal of this study was to evaluate the integrated effects of 80 y of different vegetative type on Hg accumulation and partitioning in terrestrial ecosystems by comparing Hg concentrations and pools of two adjacent forests: a coniferous Douglas fir (Pseudotsuga menziesii) and a deciduous red alder (Alnus rubra) stand. These stands grew for &gt; 80 y in close proximity (200 m) with identical site histories, soil parent materials, and atmospheric exposure. Results showed that the Douglas fir stand was characterized by significantly higher Hg concentrations and Hg : C ratios in aboveground biomass compared to the deciduous red alder forest. For foliage, higher Hg concentrations (plus 43 μg kg–1) were expected due to foliage age, but Hg concentrations also were higher in woody tissues (by 2 to 18 μg kg–1) indicating increased uptake of atmospheric Hg by coniferous tissues. These differences were reflected—and further increased—in litter horizons where Hg-concentration differences increased in highly decomposed litter to &gt; 200 μg kg–1. In soils, no difference in concentrations of Hg was observed, but Hg : C ratios were consistently higher in the coniferous Douglas fir. Estimation of pool sizes of C and Hg in soils and at the whole ecosystem level showed that considerably smaller C pools in the coniferous stand as a result of faster C turnover and lower productivity did not lead to corresponding declines in Hg-pool sizes. The partitioning of Hg among ecosystem components—including distribution between aboveground and belowground components and distribution through the soil profile—was largely unaffected by forest type. Methyl-Hg concentrations observed in litter layers were also significantly higher in litter of Douglas fir, along with a higher proportion of methylated Hg of total Hg. In soils, methyl-Hg concentrations were similar in both stands. Comparison of these adjacent forest stands highlights that vegetation type affects concentrations of total Hg in otherwise equivalent sites and that differences also exist in respect to methylated Hg.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100126" xmlns="http://purl.org/rss/1.0/"><title>Dissolved phosphorus composition of grassland leachates following application of dairy-slurry size fractions</title><link>http://dx.doi.org/10.1002%2Fjpln.201100126</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Dissolved phosphorus composition of grassland leachates following application of dairy-slurry size fractions</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Bárbara Fuentes</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Elizabeth Dixon</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">María de la Luz Mora</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Benjamin L. Turner</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Roland Bol</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100126</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100126</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100126</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">78</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">85</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Appropriate management of P from slurry can increase crop production and decrease nutrient loss to water bodies. The present study examined how the application of different size fractions of dairy slurry influenced the quantity and composition of P leached from grassland in a temperate climate. Soil blocks were amended (day 0 = start of the experiment) with either whole slurry (WS), the &gt; 425 μm fraction (coarse slurry fraction, CSF), the &lt; 45 μm slurry fraction (fine liquid slurry fraction, FLF), or not amended, <em>i.e.,</em> the control soil (CON). Deionized water was added to the soil blocks to simulate six sequential rainfall events, equivalent to 250 mm (day 0.2, 1.2, 4.2, 11.2) or 500 mm of rainfall (day 18.2 and 25.2), with leachates collected the following day. The results showed that total dissolved P (TDP), dissolved reactive P (DRP), dissolved unreactive P (DUP), orthophosphate, phosphomonoester, and pyrophosphate concentrations generally decreased with the increasing number of simulated rain events. Total dissolved P was leached in the following order WS &gt; FLF ≈ CSF &gt; CON. Dissolved organic C was correlated with TDP, DRP, and DUP in leachates of all treatments. The highest concentrations of dissolved phosphomonoesters and pyrophosphate (147 μg P L<sup>–1</sup> and 57 μg P L<sup>–1</sup>, respectively) were detected using solution <sup>31</sup>P-NMR spectroscopy in the WS leachates. Overall, there were significant differences observed between slurry treatments (<em>e.g.,</em> relative contributions of inorganic P <em>vs.</em> organic P of dissolved P in leachates). Differences were independent from the rate at which slurry P was applied, because the highest dissolved P losses per unit of slurry P applied were measured in the FLF, <em>i.e.,</em> the treatment that received the smallest amount of P. We conclude that the specific particle-size composition of applied slurry influences dissolved P losses from grassland systems. This information should be taken in account in farm-management approaches which aim to minimizing dissolved slurry P losses from grassland systems.</p></div>]]></content:encoded><description>Appropriate management of P from slurry can increase crop production and decrease nutrient loss to water bodies. The present study examined how the application of different size fractions of dairy slurry influenced the quantity and composition of P leached from grassland in a temperate climate. Soil blocks were amended (day 0 = start of the experiment) with either whole slurry (WS), the &gt; 425 μm fraction (coarse slurry fraction, CSF), the &lt; 45 μm slurry fraction (fine liquid slurry fraction, FLF), or not amended, i.e., the control soil (CON). Deionized water was added to the soil blocks to simulate six sequential rainfall events, equivalent to 250 mm (day 0.2, 1.2, 4.2, 11.2) or 500 mm of rainfall (day 18.2 and 25.2), with leachates collected the following day. The results showed that total dissolved P (TDP), dissolved reactive P (DRP), dissolved unreactive P (DUP), orthophosphate, phosphomonoester, and pyrophosphate concentrations generally decreased with the increasing number of simulated rain events. Total dissolved P was leached in the following order WS &gt; FLF ≈ CSF &gt; CON. Dissolved organic C was correlated with TDP, DRP, and DUP in leachates of all treatments. The highest concentrations of dissolved phosphomonoesters and pyrophosphate (147 μg P L–1 and 57 μg P L–1, respectively) were detected using solution 31P-NMR spectroscopy in the WS leachates. Overall, there were significant differences observed between slurry treatments (e.g., relative contributions of inorganic P vs. organic P of dissolved P in leachates). Differences were independent from the rate at which slurry P was applied, because the highest dissolved P losses per unit of slurry P applied were measured in the FLF, i.e., the treatment that received the smallest amount of P. We conclude that the specific particle-size composition of applied slurry influences dissolved P losses from grassland systems. This information should be taken in account in farm-management approaches which aim to minimizing dissolved slurry P losses from grassland systems.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201000348" xmlns="http://purl.org/rss/1.0/"><title>Classifying soils at the ultimate stage of weathering in the tropics</title><link>http://dx.doi.org/10.1002%2Fjpln.201000348</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Classifying soils at the ultimate stage of weathering in the tropics</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Eswaran Padmanabhan</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Hariharan Eswaran</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Ahmet R. Mermut</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201000348</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201000348</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201000348</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">86</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">93</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Oxisols cover ≈ 23% of the land surface in the tropics and are utilized extensively for agricultural purposes in the tropical countries. Under the variable input types of agricultural systems practiced locally, some of these soils still appear to have problems in terms of proper soil classification and subsequently hinder attempts to implement sustainable agro-management protocols. The definition for Oxisols in <em>Soil Survey Staff</em> (1999) indicates that additional input is still required to refine the definition in order to resolve some of the outstanding classification problems. Therefore, the objective of this study is to examine the properties of some Oxisols and closely related soils in order to evaluate the classification of these soils. Soils from Brazil, several countries in Africa, and Malaysia were used in this study. Field observations provided the first indication that some of the presently classified kandi-Alfisols and kandi-Ultisols were closer to Oxisols in terms of their properties. Water-retention differences and apparent CEC of the subsurface horizons also supported this idea. The types of extractable Fe oxides and external specific surface areas of the clay fractions showed that many kandic horizons have surface properties that are similar to the oxic horizons. Micromorphology indicated that the genetic transition from the argillic to the oxic involves a diminishing expression of the argillic. Properties, such as CEC, become dominant. The kandic horizon is therefore inferred as a transition to the oxic horizon. It is proposed that the Oxisols be keyed out based only on the presence of an oxic horizon and an iso–soil temperature regime. The presence of a kandic horizon will be reflected at lower levels in Oxisols. The Oxisols will now be exclusive to the intertropical belt with an iso–soil temperature regime. The geographic extend of the Oxisols would increase and that of kandi-Alfisols and Ultisols would decrease. A few kandi-Alfisols and Ultisols in the intertropical area will have low CEC which would fail the weatherable mineral contents. The kandic subgroups of some Alfisols and Ultisols will be transitional between the low (&lt; 16 cmol<sub>c</sub> [kg clay]<sup>–1</sup>)- and high (&gt; 24 cmol<sub>c</sub> [kg clay]<sup>–1</sup>)-activity clay soils. The proposed changes to classification will contribute to a better differentiation of the landscape units in the field. Testing of the proposed classification on some Malaysian soils showed that the new definition for Oxisols provides a better basis for the classification of the local soils and the development of meaningful soil-management groups for plantations.</p></div>]]></content:encoded><description>Oxisols cover ≈ 23% of the land surface in the tropics and are utilized extensively for agricultural purposes in the tropical countries. Under the variable input types of agricultural systems practiced locally, some of these soils still appear to have problems in terms of proper soil classification and subsequently hinder attempts to implement sustainable agro-management protocols. The definition for Oxisols in Soil Survey Staff (1999) indicates that additional input is still required to refine the definition in order to resolve some of the outstanding classification problems. Therefore, the objective of this study is to examine the properties of some Oxisols and closely related soils in order to evaluate the classification of these soils. Soils from Brazil, several countries in Africa, and Malaysia were used in this study. Field observations provided the first indication that some of the presently classified kandi-Alfisols and kandi-Ultisols were closer to Oxisols in terms of their properties. Water-retention differences and apparent CEC of the subsurface horizons also supported this idea. The types of extractable Fe oxides and external specific surface areas of the clay fractions showed that many kandic horizons have surface properties that are similar to the oxic horizons. Micromorphology indicated that the genetic transition from the argillic to the oxic involves a diminishing expression of the argillic. Properties, such as CEC, become dominant. The kandic horizon is therefore inferred as a transition to the oxic horizon. It is proposed that the Oxisols be keyed out based only on the presence of an oxic horizon and an iso–soil temperature regime. The presence of a kandic horizon will be reflected at lower levels in Oxisols. The Oxisols will now be exclusive to the intertropical belt with an iso–soil temperature regime. The geographic extend of the Oxisols would increase and that of kandi-Alfisols and Ultisols would decrease. A few kandi-Alfisols and Ultisols in the intertropical area will have low CEC which would fail the weatherable mineral contents. The kandic subgroups of some Alfisols and Ultisols will be transitional between the low (&lt; 16 cmolc [kg clay]–1)- and high (&gt; 24 cmolc [kg clay]–1)-activity clay soils. The proposed changes to classification will contribute to a better differentiation of the landscape units in the field. Testing of the proposed classification on some Malaysian soils showed that the new definition for Oxisols provides a better basis for the classification of the local soils and the development of meaningful soil-management groups for plantations.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201000056" xmlns="http://purl.org/rss/1.0/"><title>Driving factors determining the occurrence of sodic soils in dry subhumid Mediterranean areas</title><link>http://dx.doi.org/10.1002%2Fjpln.201000056</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Driving factors determining the occurrence of sodic soils in dry subhumid Mediterranean areas</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Fernando Manuel Monteiro</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Maria Madalena Fonseca</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Manuel Armando Madeira</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Adrien J. Herbillon</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201000056</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201000056</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201000056</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">94</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">100</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>An evaluation of the factors determining the occurrence and the properties of soils with low permeability occurring in vast areas in S Portugal was carried out taking into account the terrain morphology and the geology of the region. This paper deals with the variation patterns of the physical and chemical characteristics of soils from several soil toposequences that occur under different gradient slopes and on different parent rocks. Spatial variation of soil properties mainly depends on the composition of their cation-exchange complex, as the role of other factors, such as the mineralogy of the clay fraction, were of minor importance. There is often a stronger increment of Na and/or Mg than of Ca with depth, causing a variable degree of sodicity in some of these soils, to which waterlogging tendency of their upper horizons is related. Though the occurrence of these features is determined by the nature of the parent rock, their degree of expression varies primarily according to the topographic position of soils. Therefore, a catenary distribution including nonsodic Cambisols or Luvisols in the hillcrests and Stagnic Solonetz or Sodic Luvisols or Sodic Stagnosols in the topographic lows is common. Such soil characteristics are of utmost importance for irrigation suitability and management of these soils, and for environmental impacts assessment, as the region is vulnerable to desertification.</p></div>]]></content:encoded><description>An evaluation of the factors determining the occurrence and the properties of soils with low permeability occurring in vast areas in S Portugal was carried out taking into account the terrain morphology and the geology of the region. This paper deals with the variation patterns of the physical and chemical characteristics of soils from several soil toposequences that occur under different gradient slopes and on different parent rocks. Spatial variation of soil properties mainly depends on the composition of their cation-exchange complex, as the role of other factors, such as the mineralogy of the clay fraction, were of minor importance. There is often a stronger increment of Na and/or Mg than of Ca with depth, causing a variable degree of sodicity in some of these soils, to which waterlogging tendency of their upper horizons is related. Though the occurrence of these features is determined by the nature of the parent rock, their degree of expression varies primarily according to the topographic position of soils. Therefore, a catenary distribution including nonsodic Cambisols or Luvisols in the hillcrests and Stagnic Solonetz or Sodic Luvisols or Sodic Stagnosols in the topographic lows is common. Such soil characteristics are of utmost importance for irrigation suitability and management of these soils, and for environmental impacts assessment, as the region is vulnerable to desertification.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201000390" xmlns="http://purl.org/rss/1.0/"><title>Effects of combined application of vermicompost and mineral fertilizer on the growth of Allium cepa L. and soil fertility</title><link>http://dx.doi.org/10.1002%2Fjpln.201000390</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Effects of combined application of vermicompost and mineral fertilizer on the growth of Allium cepa L. and soil fertility</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Pankaj Kumar Srivastava</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Manjul Gupta</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rakesh Kumar Upadhyay</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Suresh Sharma</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Shikha</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Nandita Singh</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Sri Krishna Tewari</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Bajrang Singh</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201000390</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201000390</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201000390</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">101</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">107</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>The promotion of organic farming involves curtailing extensive use of mineral fertilizers. The present study was aimed to compare the effects of vermicompost (10 Mg ha<sup>–1</sup>), commercial mineral fertilizer (NPK—100:80:80), and their combination on (1) the growth of a major cash crop “onion” (<em>Allium cepa</em> L.) and (2) the changes that may have occurred in the amended soil. The experiment was a randomized complete block design with four replications during the crop-growing season of 2008/09. Results showed significantly higher plant growth in the combined/mix treatment of vermicompost and NPK, as measured by the vegetative growth of bulbs, number and length of tillers per bulb, and fresh weight of bulbs and by the biochemical characteristics of the onion tillers/leaves (total chlorophyll, caretenoids, protein, and total sugar contents). Comparison of the mixed treatment as compared to the control showed increases in bulb size (54%), total number of bulbs per bed (52%), and fresh weight of all bulbs (198%). The chemical properties and enzyme activity of the amended soil also improved significantly in the combined treatment as compared to the application of vermicompost or the mineral fertilizer alone. Total organic C, microbial biomass C, and sulfate content were significantly higher in the mix treatment, with increases of 60%, 127%, and 126%, respectively, as compared to those of the chemical-fertilizer-alone treatment. Similarly, β-glucosidase, alkaline phosphatase, and dehydrogenase were significantly higher by 145%, 91%, 71%, respectively, in the mix treatment as compared to those of fertilizer-alone application. This study indicates that application of a combination of mineral fertilizer and vermicompost in the field can positively influence the biological properties and fertility of soils, and support better plant growth, when compared to the application of mineral fertilizer or vermicompost alone. The study suggests that this combined application can reduce the quantity and cost of mineral-fertilizers application for bulbous-crop cultivation by 50%, while also sustaining soil biological activity of tropical and subtropical soils.</p></div>]]></content:encoded><description>The promotion of organic farming involves curtailing extensive use of mineral fertilizers. The present study was aimed to compare the effects of vermicompost (10 Mg ha–1), commercial mineral fertilizer (NPK—100:80:80), and their combination on (1) the growth of a major cash crop “onion” (Allium cepa L.) and (2) the changes that may have occurred in the amended soil. The experiment was a randomized complete block design with four replications during the crop-growing season of 2008/09. Results showed significantly higher plant growth in the combined/mix treatment of vermicompost and NPK, as measured by the vegetative growth of bulbs, number and length of tillers per bulb, and fresh weight of bulbs and by the biochemical characteristics of the onion tillers/leaves (total chlorophyll, caretenoids, protein, and total sugar contents). Comparison of the mixed treatment as compared to the control showed increases in bulb size (54%), total number of bulbs per bed (52%), and fresh weight of all bulbs (198%). The chemical properties and enzyme activity of the amended soil also improved significantly in the combined treatment as compared to the application of vermicompost or the mineral fertilizer alone. Total organic C, microbial biomass C, and sulfate content were significantly higher in the mix treatment, with increases of 60%, 127%, and 126%, respectively, as compared to those of the chemical-fertilizer-alone treatment. Similarly, β-glucosidase, alkaline phosphatase, and dehydrogenase were significantly higher by 145%, 91%, 71%, respectively, in the mix treatment as compared to those of fertilizer-alone application. This study indicates that application of a combination of mineral fertilizer and vermicompost in the field can positively influence the biological properties and fertility of soils, and support better plant growth, when compared to the application of mineral fertilizer or vermicompost alone. The study suggests that this combined application can reduce the quantity and cost of mineral-fertilizers application for bulbous-crop cultivation by 50%, while also sustaining soil biological activity of tropical and subtropical soils.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100127" xmlns="http://purl.org/rss/1.0/"><title>Compost and phosphorus amendments for stimulating microorganisms and growth of ryegrass in a Ferralsol and a Luvisol</title><link>http://dx.doi.org/10.1002%2Fjpln.201100127</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Compost and phosphorus amendments for stimulating microorganisms and growth of ryegrass in a Ferralsol and a Luvisol</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Khalid Saifullah Khan</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rainer Georg Joergensen</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100127</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100127</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100127</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">108</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">114</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>A greenhouse pot experiment was carried out to investigate the effects of different P-fertilizer application forms (triple superphosphate [TSP], compost + TSP, TSP-enriched compost) on the growth of ryegrass and the soil microbial biomass. The fertilizers were applied at equivalent doses for all nutrients to a neutral Luvisol in comparison with an acidic Ferralsol. Fertilizer application led to significantly increased contents of microbial biomass C, N, and P. Furthermore, yields of shoot C and root C, and concentrations of P, Ca, Mg, K, Fe, and Mn in shoots and roots were significantly increased. These increases always followed the order TSP &lt; compost + TSP &lt; TSP-enriched compost. Sole TSP application led only to maximum concentrations of N and S. In the Ferralsol, TSP had only minimal positive effect on the P concentration of the grass shoots. The positive effect of TSP-enriched compost, <em>i.e.,</em> incubating TSP together with compost for 24 h, did not differ between the neutral Luvisol and the acidic Ferralsol, <em>i.e.,</em> the effect is independent of the soil type. Consequently, soluble inorganic P fertilizer should generally be mixed into an organic fertilizer before application to soil.</p></div>]]></content:encoded><description>A greenhouse pot experiment was carried out to investigate the effects of different P-fertilizer application forms (triple superphosphate [TSP], compost + TSP, TSP-enriched compost) on the growth of ryegrass and the soil microbial biomass. The fertilizers were applied at equivalent doses for all nutrients to a neutral Luvisol in comparison with an acidic Ferralsol. Fertilizer application led to significantly increased contents of microbial biomass C, N, and P. Furthermore, yields of shoot C and root C, and concentrations of P, Ca, Mg, K, Fe, and Mn in shoots and roots were significantly increased. These increases always followed the order TSP &lt; compost + TSP &lt; TSP-enriched compost. Sole TSP application led only to maximum concentrations of N and S. In the Ferralsol, TSP had only minimal positive effect on the P concentration of the grass shoots. The positive effect of TSP-enriched compost, i.e., incubating TSP together with compost for 24 h, did not differ between the neutral Luvisol and the acidic Ferralsol, i.e., the effect is independent of the soil type. Consequently, soluble inorganic P fertilizer should generally be mixed into an organic fertilizer before application to soil.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201000299" xmlns="http://purl.org/rss/1.0/"><title>Late nitrogen fertilization affects nitrogen remobilization in wheat</title><link>http://dx.doi.org/10.1002%2Fjpln.201000299</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Late nitrogen fertilization affects nitrogen remobilization in wheat</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Teresa Fuertes-Mendizábal</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Carmen González-Murua</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Ma. B. González-Moro</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">José M. Estavillo</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201000299</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201000299</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201000299</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">115</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">124</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>A pot experiment with wheat plants was carried out to study how late application of nitrogen (N) fertilizer affects the use of pre-anthesis N reserves during the grain-filling period. Increasing doses of N fertilizer were applied (0, 40, and 52 mg N plant<sup>–1</sup>), either in two amendments (growth stages GS20 and GS30, according to Zadoks scale) or in three amendments (GS20, GS30, and GS37). The experiment was arranged in a complete randomized three-block design with 129 plants per treatment. The plants were watered daily, harvested every 2 d between anthesis and maturity, and were separated into roots, leaf sheaths, leaf blades, and ears for further N determination. Grain N concentration improved due to a late N application in GS37 by 14% (higher N dose) and by 7% (further splitting the same N-fertilizer dose, respectively). The higher the N-fertilizer dose applied, the greater was the amount of pre-anthesis reserves in vegetative organs, these reserves became later available for remobilization. Although splitting the same N dose in three amendments did not increase the N reserves, these reserves were more efficiently remobilized allowing an improvement in grain N concentration. The fertilizer management did not change the temporary pattern of N accumulation in the ear, but did induce a change in the amount of N remobilized and in the contribution of each organ (root, leaf sheath, leaf blade) to this remobilization. Late N amendment allowed a greater N availability of leaf blades and ear N reserves (from 20% up to 26% and from 19% up to 22%, respectively) for remobilization towards the grain, decreasing the root contribution from 28% down to 15%, while the contribution of leaf sheaths was maintained around 35% irrespective of the N applied.</p></div>]]></content:encoded><description>A pot experiment with wheat plants was carried out to study how late application of nitrogen (N) fertilizer affects the use of pre-anthesis N reserves during the grain-filling period. Increasing doses of N fertilizer were applied (0, 40, and 52 mg N plant–1), either in two amendments (growth stages GS20 and GS30, according to Zadoks scale) or in three amendments (GS20, GS30, and GS37). The experiment was arranged in a complete randomized three-block design with 129 plants per treatment. The plants were watered daily, harvested every 2 d between anthesis and maturity, and were separated into roots, leaf sheaths, leaf blades, and ears for further N determination. Grain N concentration improved due to a late N application in GS37 by 14% (higher N dose) and by 7% (further splitting the same N-fertilizer dose, respectively). The higher the N-fertilizer dose applied, the greater was the amount of pre-anthesis reserves in vegetative organs, these reserves became later available for remobilization. Although splitting the same N dose in three amendments did not increase the N reserves, these reserves were more efficiently remobilized allowing an improvement in grain N concentration. The fertilizer management did not change the temporary pattern of N accumulation in the ear, but did induce a change in the amount of N remobilized and in the contribution of each organ (root, leaf sheath, leaf blade) to this remobilization. Late N amendment allowed a greater N availability of leaf blades and ear N reserves (from 20% up to 26% and from 19% up to 22%, respectively) for remobilization towards the grain, decreasing the root contribution from 28% down to 15%, while the contribution of leaf sheaths was maintained around 35% irrespective of the N applied.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100035" xmlns="http://purl.org/rss/1.0/"><title>Responses of cucumber grown in recirculating nutrient solution to gradual Mn and Zn accumulation in the root zone owing to excessive supply via the irrigation water</title><link>http://dx.doi.org/10.1002%2Fjpln.201100035</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Responses of cucumber grown in recirculating nutrient solution to gradual Mn and Zn accumulation in the root zone owing to excessive supply via the irrigation water</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Constantinos Tzerakis</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Dimitrios Savvas</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Nick Sigrimis</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100035</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100035</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100035</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">125</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">134</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>A standard and a high manganese (Mn) level (10 and 160 μM) were combined with a standard and a high zinc (Zn) level (4 and 64 μM) in the nutrient solution supplied to cucumber in closed-cycle hydroponic units to compensate for nutrient uptake. The concentrations of all nutrients except Mn and Zn were identical in all treatments. The objectives of the experiment were to establish critical Zn and Mn levels in both nutrient solutions and leaves of cucumber grown hydroponically, to assess the impact of gradual Zn and/or Mn accumulation in the external solution on nutrient uptake and gas exchange, and to find whether Mn and Zn have additive effects when the levels of both ions are excessively high in the root zone. The first symptoms of Mn and Zn toxicity appeared when the concentrations of Mn and Zn in the leaves of cucumber reached 900 and 450 mg kg<sup>–1</sup> in the dry weight, respectively. Excessively high Mn or/and Zn concentrations in the leaves reduced the fruit biomass production due to decreases in the number of fruits per plant, as well as the net assimilation rate, stomatal conductance, and transpiration rate, but increased the intercellular CO<sub>2</sub> levels. Initially, the Mn or Zn concentrations in the recirculating nutrient solution increased rapidly but gradually stabilized to maximal levels, while the corresponding concentrations in the leaves constantly increased until the end of the experiment. The uptake of Mg, Ca, Fe, and Cu was negatively affected, while that of K and P remained unaffected by the external Mn and Zn levels. The combination of high Mn and Zn seems to have no additive effects on the parameters investigated.</p></div>]]></content:encoded><description>A standard and a high manganese (Mn) level (10 and 160 μM) were combined with a standard and a high zinc (Zn) level (4 and 64 μM) in the nutrient solution supplied to cucumber in closed-cycle hydroponic units to compensate for nutrient uptake. The concentrations of all nutrients except Mn and Zn were identical in all treatments. The objectives of the experiment were to establish critical Zn and Mn levels in both nutrient solutions and leaves of cucumber grown hydroponically, to assess the impact of gradual Zn and/or Mn accumulation in the external solution on nutrient uptake and gas exchange, and to find whether Mn and Zn have additive effects when the levels of both ions are excessively high in the root zone. The first symptoms of Mn and Zn toxicity appeared when the concentrations of Mn and Zn in the leaves of cucumber reached 900 and 450 mg kg–1 in the dry weight, respectively. Excessively high Mn or/and Zn concentrations in the leaves reduced the fruit biomass production due to decreases in the number of fruits per plant, as well as the net assimilation rate, stomatal conductance, and transpiration rate, but increased the intercellular CO2 levels. Initially, the Mn or Zn concentrations in the recirculating nutrient solution increased rapidly but gradually stabilized to maximal levels, while the corresponding concentrations in the leaves constantly increased until the end of the experiment. The uptake of Mg, Ca, Fe, and Cu was negatively affected, while that of K and P remained unaffected by the external Mn and Zn levels. The combination of high Mn and Zn seems to have no additive effects on the parameters investigated.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201000426" xmlns="http://purl.org/rss/1.0/"><title>Arsenic mobilization in rice (Oryza sativa) and its accumulation in the grains</title><link>http://dx.doi.org/10.1002%2Fjpln.201000426</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Arsenic mobilization in rice (Oryza sativa) and its accumulation in the grains</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Katja Bogdan</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Manfred K. Schenk</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201000426</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201000426</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201000426</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">135</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">141</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>Flooded rice (<em>Oryza sativa</em> L.) may contain high arsenic (As) concentrations compared to other grain crops. For the development of measures to reduce the As concentration of rice grains, knowledge about the mobility of As within the rice plant is required. Therefore, to investigate the mobilization of As within the plant, rice was grown in nutrient solution and exposed to As either before flowering, after flowering, or continuously until maturity. Furthermore, rice was grown in four soils under greenhouse and field conditions and the time course of As accumulation in grains during the grain-filling period was investigated. When grown in nutrient solution, As removal at flowering did not reduce As concentrations in polished rice compared to plants supplied with As continuously or after flowering. Plants that received As only after flowering had the same As concentrations in shoot and bran as plants receiving As only before flowering. However, continuous As supply resulted in doubling of As concentrations in both plant parts. In contrast to grain and shoot, the As concentration in the root decreased after As removal compared to the treatments receiving As only after flowering or continuously. The observations indicate that As was mobilized from root or shoot to the grain and that it was accumulated in the grain, although it was not available in nutrient solution during the grain-filling period. In soil experiments, the 1000-grain weight increased up to 2 weeks before harvest in the field as well as in the greenhouse. The As concentration in rice grain was constant during the whole grain-filling period. It was at a similar level under field and greenhouse conditions, and its variation among soils was in the same order indicating that soil was the decisive factor for As concentration in grains. Our results suggest that temporary cultural measures during the cultivation period, for example drainage, might be ineffective because of the mobilization capacity within the rice plant. Moreover, harvest before final maturity of grains would not reduce the As concentration since it remained constant during the grain-filling period.</p></div>]]></content:encoded><description>Flooded rice (Oryza sativa L.) may contain high arsenic (As) concentrations compared to other grain crops. For the development of measures to reduce the As concentration of rice grains, knowledge about the mobility of As within the rice plant is required. Therefore, to investigate the mobilization of As within the plant, rice was grown in nutrient solution and exposed to As either before flowering, after flowering, or continuously until maturity. Furthermore, rice was grown in four soils under greenhouse and field conditions and the time course of As accumulation in grains during the grain-filling period was investigated. When grown in nutrient solution, As removal at flowering did not reduce As concentrations in polished rice compared to plants supplied with As continuously or after flowering. Plants that received As only after flowering had the same As concentrations in shoot and bran as plants receiving As only before flowering. However, continuous As supply resulted in doubling of As concentrations in both plant parts. In contrast to grain and shoot, the As concentration in the root decreased after As removal compared to the treatments receiving As only after flowering or continuously. The observations indicate that As was mobilized from root or shoot to the grain and that it was accumulated in the grain, although it was not available in nutrient solution during the grain-filling period. In soil experiments, the 1000-grain weight increased up to 2 weeks before harvest in the field as well as in the greenhouse. The As concentration in rice grain was constant during the whole grain-filling period. It was at a similar level under field and greenhouse conditions, and its variation among soils was in the same order indicating that soil was the decisive factor for As concentration in grains. Our results suggest that temporary cultural measures during the cultivation period, for example drainage, might be ineffective because of the mobilization capacity within the rice plant. Moreover, harvest before final maturity of grains would not reduce the As concentration since it remained constant during the grain-filling period.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100141" xmlns="http://purl.org/rss/1.0/"><title>Alleviation of drought stress in winter wheat by late foliar application of zinc, boron, and manganese</title><link>http://dx.doi.org/10.1002%2Fjpln.201100141</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Alleviation of drought stress in winter wheat by late foliar application of zinc, boron, and manganese</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Md. Rezaul Karim</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Yue-Qiang Zhang</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Rong-Rong Zhao</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Xin-Ping Chen</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Fu-Suo Zhang</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Chun-Qin Zou</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100141</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100141</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100141</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">142</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">151</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>In many regions, drought during flowering and grain-filling inhibits micronutrient acquisition by roots resulting in yield losses and low micronutrient concentrations in cereal grains. A field and a greenhouse experiment were conducted to study the effect of foliar applications of zinc (Zn), boron (B), and manganese (Mn) at late growth stages of winter wheat (<em>Triticum aestivum</em> L.) grown with or without drought stress from booting to maturity. Foliar applications of Zn, B, and Mn did not affect grain yield in the absence of drought. However, under drought, foliar application of Zn and B in the field increased grain yield (15% and 19%, respectively) as well as raising grain Zn and B concentration, while Zn and Mn sprays in the greenhouse increased grain yield (13% and 10%, respectively), and also increased grain Zn and Mn concentrations. Furthermore, under drought stress both in the field and greenhouse experiment the rate of photosynthesis, pollen viability, number of fertile spikes, number of grains per spike, and particularly water-use efficiency (WUE) were increased by late foliar application of micronutrients. These results indicate that by increasing WUE foliar application of Zn, B, and Mn at booting to anthesis can reduce the harmful effects of drought stress that often occur during the late stages of winter wheat production. These findings therefore are of high relevance for farmers' practice, the extension service, and fertilizer industry.</p></div>]]></content:encoded><description>In many regions, drought during flowering and grain-filling inhibits micronutrient acquisition by roots resulting in yield losses and low micronutrient concentrations in cereal grains. A field and a greenhouse experiment were conducted to study the effect of foliar applications of zinc (Zn), boron (B), and manganese (Mn) at late growth stages of winter wheat (Triticum aestivum L.) grown with or without drought stress from booting to maturity. Foliar applications of Zn, B, and Mn did not affect grain yield in the absence of drought. However, under drought, foliar application of Zn and B in the field increased grain yield (15% and 19%, respectively) as well as raising grain Zn and B concentration, while Zn and Mn sprays in the greenhouse increased grain yield (13% and 10%, respectively), and also increased grain Zn and Mn concentrations. Furthermore, under drought stress both in the field and greenhouse experiment the rate of photosynthesis, pollen viability, number of fertile spikes, number of grains per spike, and particularly water-use efficiency (WUE) were increased by late foliar application of micronutrients. These results indicate that by increasing WUE foliar application of Zn, B, and Mn at booting to anthesis can reduce the harmful effects of drought stress that often occur during the late stages of winter wheat production. These findings therefore are of high relevance for farmers' practice, the extension service, and fertilizer industry.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201100050" xmlns="http://purl.org/rss/1.0/"><title>Response of cotton fiber quality to the carbohydrates in the leaf subtending the cotton boll</title><link>http://dx.doi.org/10.1002%2Fjpln.201100050</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Response of cotton fiber quality to the carbohydrates in the leaf subtending the cotton boll</dc:title><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Gao Xiangbin</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Wang Youhua</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Zhou Zhiguo</dc:creator><dc:creator xmlns:dc="http://purl.org/dc/elements/1.1/">Derrick M. Oosterhuis</dc:creator><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201100050</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201100050</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201100050</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Regular Article</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">152</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">160</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[<h3 xhtml="http://www.w3.org/1999/xhtml" xmlns:ol="http://www.wiley.com/namespaces/ol/xsl-lib">Abstract</h3><div class="para" xmlns="http://www.w3.org/1999/xhtml"><p>This study investigated the effect of nitrogen (N) fertilization on leaf and boll N and carbohydrate concentrations in the development of fiber quality. A two-year field study was conducted with two cotton (<em>Gossypium hirsutum</em> L.) cultivars, Kemian 1 (average fiber strength 35 cN tex<sup>–1</sup>) and NuCOTN 33B (average fiber strength 32 cN tex<sup>–1</sup>) at five (2008) and four (2009) N levels. The relationship between leaf and boll N and carbohydrate concentrations was assessed from measurements of N, carbohydrates, chlorophyll (based on SPAD readings), and free amino acids in the leaf subtending the boll, together with fiber carbohydrates and development of fiber quality. Results indicate that leaf N concentration more accurately reflected boll N status than the concentration of chlorophyll or free amino acids. Leaf sucrose and nonstructural carbohydrate had a quadratic relation with leaf N concentration (<em>p</em> &lt; 1%). The optimal leaf N concentration ranged from 3.0% to 2.4%. During 24–38 d post-anthesis (DPA), fiber sucrose was positively related to leaf sucrose and nonstructural carbohydrate (<em>p</em> &lt; 5%), but was not correlated with leaf starch or total soluble carbohydrates. Fiber strength was positively correlated with fiber sucrose before 38 DPA, and it appeared to be more easily influenced by the fiber sucrose concentration than fiber length, fineness, or maturity. These results suggest that 24–38 DPA is a crucial period for fiber development which might be significantly influenced by physiological and ecological factors. In addition, sucrose or nonstructural carbohydrates in the subtending leaf could be used as a monitoring index to evaluate sucrose levels in the developing fiber, and also for predicting the final fiber strength.</p></div>]]></content:encoded><description>This study investigated the effect of nitrogen (N) fertilization on leaf and boll N and carbohydrate concentrations in the development of fiber quality. A two-year field study was conducted with two cotton (Gossypium hirsutum L.) cultivars, Kemian 1 (average fiber strength 35 cN tex–1) and NuCOTN 33B (average fiber strength 32 cN tex–1) at five (2008) and four (2009) N levels. The relationship between leaf and boll N and carbohydrate concentrations was assessed from measurements of N, carbohydrates, chlorophyll (based on SPAD readings), and free amino acids in the leaf subtending the boll, together with fiber carbohydrates and development of fiber quality. Results indicate that leaf N concentration more accurately reflected boll N status than the concentration of chlorophyll or free amino acids. Leaf sucrose and nonstructural carbohydrate had a quadratic relation with leaf N concentration (p &lt; 1%). The optimal leaf N concentration ranged from 3.0% to 2.4%. During 24–38 d post-anthesis (DPA), fiber sucrose was positively related to leaf sucrose and nonstructural carbohydrate (p &lt; 5%), but was not correlated with leaf starch or total soluble carbohydrates. Fiber strength was positively correlated with fiber sucrose before 38 DPA, and it appeared to be more easily influenced by the fiber sucrose concentration than fiber length, fineness, or maturity. These results suggest that 24–38 DPA is a crucial period for fiber development which might be significantly influenced by physiological and ecological factors. In addition, sucrose or nonstructural carbohydrates in the subtending leaf could be used as a monitoring index to evaluate sucrose levels in the developing fiber, and also for predicting the final fiber strength.</description></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201290001" xmlns="http://purl.org/rss/1.0/"><title>Mitteilungen der Deutschen Bodenkundlichen Gesellschaft: J. Plant Nutr. Soil Sci. 1/2012</title><link>http://dx.doi.org/10.1002%2Fjpln.201290001</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Mitteilungen der Deutschen Bodenkundlichen Gesellschaft: J. Plant Nutr. Soil Sci. 1/2012</dc:title><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201290001</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201290001</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201290001</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Mitteilungen der Deutschen Bodenkundlichen Gesellschaft</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">161</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">162</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[]]></content:encoded><description/></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201290002" xmlns="http://purl.org/rss/1.0/"><title>News from the German Soil Science Society: J. Plant Nutr. Soil Sci. 1/2012</title><link>http://dx.doi.org/10.1002%2Fjpln.201290002</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">News from the German Soil Science Society: J. Plant Nutr. Soil Sci. 1/2012</dc:title><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201290002</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201290002</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201290002</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">News from the German Soil Science Society</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">163</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">165</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[]]></content:encoded><description/></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201290003" xmlns="http://purl.org/rss/1.0/"><title>Instructions for Authors: J. Plant Nutr. Soil Sci. 1/2012</title><link>http://dx.doi.org/10.1002%2Fjpln.201290003</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Instructions for Authors: J. Plant Nutr. Soil Sci. 1/2012</dc:title><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201290003</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201290003</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201290003</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Instructions for Authors</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">166</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">167</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[]]></content:encoded><description/></item><item rdf:about="http://dx.doi.org/10.1002%2Fjpln.201290006" xmlns="http://purl.org/rss/1.0/"><title>Contents: J. Plant Nutr. Soil Sci. 1/2012</title><link>http://dx.doi.org/10.1002%2Fjpln.201290006</link><dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Contents: J. Plant Nutr. Soil Sci. 1/2012</dc:title><dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">2012-02-01T00:00:00-05:00</dc:date><dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">doi:10.1002/jpln.201290006</dc:identifier><dc:rights xmlns:dc="http://purl.org/dc/elements/1.1/"/><dc:publisher xmlns:dc="http://purl.org/dc/elements/1.1/">John Wiley &amp; Sons, Inc.</dc:publisher><prism:doi xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">10.1002/jpln.201290006</prism:doi><prism:url xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">http://dx.doi.org/10.1002%2Fjpln.201290006</prism:url><prism:section xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">Contents</prism:section><prism:startingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:startingPage><prism:endingPage xmlns:prism="http://prismstandard.org/namespaces/1.2/basic/">n/a</prism:endingPage><content:encoded xmlns:content="http://purl.org/rss/1.0/modules/content/"><![CDATA[]]></content:encoded><description/></item></rdf:RDF>
