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	<journal>
		<journal_title>Biogeosciences</journal_title>
		<journal_url>www.biogeosciences.net</journal_url>
		<issn>1726-4170</issn>
		<eissn>1726-4189</eissn>
		<volume_number>6</volume_number>
		<issue_number>10</issue_number>
		<publication_year>2009</publication_year>
	</journal>
	<doi>10.5194/bg-6-2181-2009</doi>
	<article_url>http://www.biogeosciences.net/6/2181/2009/</article_url>
	<abstract_html>http://www.biogeosciences.net/6/2181/2009/bg-6-2181-2009.html</abstract_html>
	<fulltext_pdf>http://www.biogeosciences.net/6/2181/2009/bg-6-2181-2009.pdf</fulltext_pdf>
	<start_page>2181</start_page>
	<end_page>2192</end_page>
	<publication_date>2009-10-14</publication_date>
	<article_title content_type="html">Measuring and modelling seasonal variation of gross nitrification rates in response to long-term fertilisation</article_title>
	<authors>
		<author numeration="1" affiliations="1,2">
			<name>C. F. Stange</name>
			<email>florian.stange@ufz.de</email>
		</author>
		<author numeration="2" affiliations="1,2">
			<name>H.-U. Neue</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Helmholtz Centre for Environmental Research &amp;ndash; UFZ, Theodor-Lieser-Str. 4, 06120 Halle, Germany</affiliation>
		<affiliation numeration="2" content_type="html">Martin-Luther-University Halle-Wittenberg, Weidenplan 14, 06108 Halle/Saale, Germany</affiliation>
	</affiliations>
	<abstract content_type="html">The formation of nitrate (nitrification) in soils is an important process
that influences N availability for plant uptake and potential N losses as
well. Gross nitrification is an effective measure by which to test
mechanistic ecosystem models for predictability because gross rates can
widely differ between sites, even if net production is similar between these
sites.

&lt;br&gt;&lt;br&gt;

A field experiment was designed to (i) determine gross nitrification rates
in response to fertilisation and (ii) to verify the idea that seasonal
variations of gross rates in soils can be readily predicted by soil moisture
and soil temperature.

&lt;br&gt;&lt;br&gt;

Gross nitrification rates were measured by a Barometric Process Separation
(BaPS). The BaPS measurements were validated with the commonly used &lt;sup&gt;15&lt;/sup&gt;N
pool dilution technique measurements at six times. In general, the rates
determined from both measurement approaches were in the same order of
magnitude and showed a good correlation.

&lt;br&gt;&lt;br&gt;

The effects of 100 years of fertilisation (mineral fertiliser, manure and
control) on gross nitrification rates were investigated. During 2004 soil
samples from the long-term &quot;static fertilisation experiment&quot; at Bad
Lauchstädt were sampled weekly and were measured in the laboratory under
field conditions and subsequently under standardised conditions (16&amp;deg;C
soil temperature and &amp;minus;30 kPa matrix potential) with the BaPS system. Gross
nitrification rates determined under standardised conditions did not show
any seasonal trend but did, however, reveal a high temporal variability.
Gross nitrification rates determined by the BaPS-method under field
conditions showed also a high temporal variability and ranged from 5 to 77 μg N h&lt;sup&gt;&amp;minus;1&lt;/sup&gt; kg&lt;sup&gt;&amp;minus;1&lt;/sup&gt;
dry mass, 2 to 74 μg N h&lt;sup&gt;&amp;minus;1&lt;/sup&gt; kg&lt;sup&gt;&amp;minus;1&lt;/sup&gt;
dry mass and 0 to 49 &amp;mu;g N h&lt;sup&gt;&amp;minus;1&lt;/sup&gt; kg&lt;sup&gt;&amp;minus;1&lt;/sup&gt; dry mass with respect to
manure, mineral fertiliser, and control. The annual average was 0.34, 0.27
and 0.19 g N a&lt;sup&gt;&amp;minus;1&lt;/sup&gt; kg&lt;sup&gt;&amp;minus;1&lt;/sup&gt; dry mass for the manure site, mineral
fertiliser site and control site, respectively. On all sites gross
nitrification revealed a strong seasonal dynamic. Three different models
were applied for reproducing the measured results. Test models could explain
75% to 78% of variability at the manure site, 66% to 77% of
variability at the mineral fertiliser site, and 39% to 63% of
variability at the control site. The model parameterisation shows that the
temperature sensitivity of gross nitrification differs between the three
neighbouring sites. Hence, a temperature response function in an ecosystem
model has to consider the site specificity in order to adequately predict
the effects of future climate change on the soil N cycle.</abstract>
	<references>
		<reference numeration="1" content_type="text"> Abbasi, M. K. and Adams, W. A.: Loss of nitrogen in compacted grassland soil by simultaneous nitrification and denitrification, Plant and Soil, 200, 265–277, 1998. </reference>
		<reference numeration="2" content_type="text"> Altermann, M., Rinklebe, J., Merbach, I., Korschens, M., Langer, U., and Hofmann, B.: Chernozem – Soil of the Year 2005, J. Plant Nutrition Soil Sci., 168, 725–740, 2005. </reference>
		<reference numeration="3" content_type="text"> Ambus, P.: Relationship Between Gross Nitrogen Cycling and Nitrous Oxide Emission in Grass-clover Pasture, Nutr. Cycl. Agroecosys., 72, 189–199, 2005. </reference>
		<reference numeration="4" content_type="text"> Booth, M. S., Stark, J. M., and Rastetter, E.:. Controls on nitrogen cycling in terrestrial ecosystems: A synthetic analysis of literature data, Ecol. Monogr., 75, 139–157, 2005. </reference>
		<reference numeration="5" content_type="text"> Breuer, L., Kiese, R., and Butterbach-Bahl, K.: Temperature and moisture effects on nitrification rates in tropical rain-forest soils, Soil Sci. Soc. Am. J., 66, 834–844, 2002. </reference>
		<reference numeration="6" content_type="text"> Cookson, W. R., Cornforth, I. S., and Rowarth, J. S.: Winter soil temperature (2–15 degrees C) effects on nitrogen transformations in clover green manure amended or unamended soils; a laboratory and field study, Soil Biol. Biochem., 34, 1401–1415, 2002. </reference>
		<reference numeration="7" content_type="text"> Cookson, W. R. and Murphy, D. V.: Quantifying the contribution of dissolved organic matter to soil nitrogen cycling using 15N isotopic pool dilution, Soil Biol. Biochem., 36, 2097–2100, 2004. </reference>
		<reference numeration="8" content_type="text"> Cookson, W. R., Marschner, P., Clark, I. M., Milton, N., Smirk, M. N., Murphy, D. V., Osman, M., Stockdale, E. A., and Hirsch, P. R.: The influence of season, agricultural management, and soil properties on gross nitrogen transformations and bacterial community structure, Aust. J. Soil Res., 44, 453–465, 2006. </reference>
		<reference numeration="9" content_type="text"> Corre, M. D., Schnabel, R. R., and Stout, W. L.: Spatial and seasonal variation of gross nitrogen transformations and microbial biomass in a Northeastern US grassland, Soil Biol. Biochem., 34, 445–457, 2002. </reference>
		<reference numeration="10" content_type="text"> Currie, W. S., Aber, J. D., McDowell, W. H., Boone, R. D., and Magill, A. H.: Vertical transport of dissolved organic C and N under long-term N amendments in pine and hardwood forests, Biogeochemistry, 35, 471–505, 1996. </reference>
		<reference numeration="11" content_type="text"> Davidson, E. A. and Janssens, I. A.: Temperature sensitivity of soil carbon decomposition and feedbacks to climate change, Nature, 440, 165–173, 2006. </reference>
		<reference numeration="12" content_type="text"> Fierer, N., Allen, A. S., Schimel, J. P., and Holden, P. A.: Controls on microbial CO&lt;sub&gt;2&lt;/sub&gt; production: a comparison of surface and subsurface soil horizons, Global Change Biology, 9, 1322–1332, 2003. </reference>
		<reference numeration="13" content_type="text"> Fierer, N., Craine, J. M., and McLauchlan, K.: Litter quality and the temperature sensitivity of decomposition, Ecology, 86, 320–326, 2005. </reference>
		<reference numeration="14" content_type="text"> Firestone, M. K. and Davidson, E.: Microbiological basis of NO and N2O production and consumption in soil, in: Exchange of trace gases between terrestrial ecosystems and the atmosphere, edited by: Andreae, M. and Schimel, D., John Wiley and Sons, New York, p. 7–21, 1989. </reference>
		<reference numeration="15" content_type="text"> Hoyle, F. C., Murphy, D. V., and Fillery, I. R. P.: Temperature and stubble management influence microbial CO&lt;sub&gt;2&lt;/sub&gt;-C evolution and gross N transformation rates, Soil Biol. Biochem., 38, 71–80, 2006. </reference>
		<reference numeration="16" content_type="text"> Ingwersen, J., Butterbach-Bahl, K., Gasche, R., Richter, O., and Papen, H.: Barometric process separation: new method for quantifying nitrification, denitrification, and nitrous oxide sources in soils, Soil Sci. Soc. Am. J., 63, 117–128, 1999. </reference>
		<reference numeration="17" content_type="text"> Ingwersen, J., Schwarz, U., Stange, C. F., Ju, X. T., and Streck, T.: Shortcomings in the commercialized barometric process separation measuring system, Soil Sci. Soc. Am. J., 72, 135–142, 2008. </reference>
		<reference numeration="18" content_type="text"> Jamieson, N., Barraclough, D., Unkovich, M., and Monaghan, R.: Soil N dynamics in a natural calcareous grassland under a changing climate, Biol. Fert. Soils, 27, 267–273, 1998. </reference>
		<reference numeration="19" content_type="text"> Khalil, M. I. and Baggs, E. M.: CH4 oxidation and N2O emissions at varied soil water-filled pore spaces and headspace CH4 concentrations, Soil Biol. Biochem., 37, 1785–1794, 2005. </reference>
		<reference numeration="20" content_type="text"> Kirkham, D. and Bartholomew, W. V.: Equations for following nutrient transformations in soil, utilizing tracer data, Soil Sci. Soc. Am. Proceedings, 18, 33–34, 1954. </reference>
		<reference numeration="21" content_type="text"> Klimanek, E. M.: Die Wirkung von Düngungsänderungen auf die mikrobielle Aktivität von Löss-Schwarzerde nach 96 Jahren differenzierter organischer und mineralischer Düngung im \mbox,,Statischen Düngungsversuch&quot; Bad Lauchstädt, Archives of Agromomy and Soil Science, 45, 381–397, 2000. </reference>
		<reference numeration="22" content_type="text"> Malhi, S. S. and McGill, W. B.: Nitrification in three Alberta soils: Effect of temperature, moisture and substrate concentration, Soil Biol. Biochem., 14, 393–399, 1982. </reference>
		<reference numeration="23" content_type="text"> Mathieu, O., Leveque, J., Henault, C., Ambus, P., Millouxl, M. J., and Andreux, F.: Influence of N-15 enrichment on the net isotopic fractionation factor during the reduction of nitrate to nitrous oxide in soil, Rapid Commun. Mass Sp., 21, 1447–1451, 2007. </reference>
		<reference numeration="24" content_type="text"> Müller, C., Abbasi, M. K., Kammann, C., Clough, T. J., Sherlock, R. R., Stevens, R. J., and Jager, H. J.: Soil respiratory quotient determined via barometric process separation combined with nitrogen-15 labeling, Soil Sci. Soc. Am. J., 68, 1610–1615, 2004a. </reference>
		<reference numeration="25" content_type="text"> Müller, C., Stevens, R. J., and Laughlin, R. J.: A 15N tracing model to analyse N transformations in old grassland soil, Soil Biol. Biochem., 36, 619–632, 2004b. </reference>
		<reference numeration="26" content_type="text"> Murphy, D. V., Recous, S., Stockdale, E. A., Fillery, I. R. P., Jensen, L. S., Hatch, D. J., and Goulding, K. W. T.: Gross nitrogen fluxes in soil: Theory, measurement and application of N-15 pool dilution techniques., 69–118 pp, 2003. </reference>
		<reference numeration="27" content_type="text"> Murphy, D. V., Stockdale, E. A., Poulton, P. R., Willison, T. W., and Goulding, K. W. T.: Seasonal dynamics of carbon and nitrogen pools and fluxes under continuous arable and ley-arable rotations in a temperate environment, European J. Soil Sci., 58, 1410–1424, 2007. </reference>
		<reference numeration="28" content_type="text"> Nozhevnikova, A. N., Simankova, M. V., Parshina, S. N., and Kotsyurbenko, O. R.: Temperature characteristics of methanogenic archaea and acetogenic bacteria isolated from cold environments, Water Sci. Technol., 44, 41–48, 2001. </reference>
		<reference numeration="29" content_type="text"> Recous, S., Aita, C., and Mary, B.: In situ changes in gross N transformations in bare soil after addition of straw, Soil Biol. Biochem., 31, 119–133, 1998. </reference>
		<reference numeration="30" content_type="text"> Robertson, G. P. and Tiedje, J. M.: Nitrous oxide sources in aerobic soils: Nitrification, denitrification and other biological processes, Soil Biol. Biochem., 19, 187–193, 1987. </reference>
		<reference numeration="31" content_type="text"> Russow, R., Spott, O., and Stange, C. F.: Evaluation of nitrate and ammonium as sources of NO and N&lt;sub&gt;2&lt;/sub&gt;O emissions from black earth soils (Haplic Chernozem) based on $^15$N field experiments, Soil Biol. Biochem., 40, 380–391, 2008. </reference>
		<reference numeration="32" content_type="text"> Russow, R., Stange, C. F., and Neue, H.-U.: Role of nitrite and nitric oxide in the processes of nitrification and denitrification in soil: results from $^15$N tracer experiments, Soil Biol. Biochem., 41, 785–795, 2009. </reference>
		<reference numeration="33" content_type="text"> Silva, R. G., Jorgensen, E. E., Holub, S. M., and Gonsoulin, M. E.: Relationships between culturable soil microbial populations and gross nitrogen transformation processes in a clay loam soil across ecosystems, Nut. Cycl. Agroecosys., 71, 259–270, 2005. </reference>
		<reference numeration="34" content_type="text"> Spott, O., Russow, R., Apelt, B., and Stange, C. F.: A N-15-aided artificial atmosphere gas flow technique for online determination of soil N-2 release using the zeolite Kostrolith SX6 (R), Rapid Commun. Mass Sp., 20, 3267–3274, 2006. </reference>
		<reference numeration="35" content_type="text"> Stange, C. F.: A novel approach to combine response functions in ecological process modeling, Ecol. Model., 204(3–4), 547–552, 2007. </reference>
		<reference numeration="36" content_type="text"> Stange, C. F., Spott, O., Apelt, B., and Russow, R. W. B.: Automated and rapid online determination of $^15$N abundance and concentration of ammonium, nitrite, or nitrate in aqueous samples by the SPINMAS technique, Isotopes in Environmental and Health Studies, 43, 227–236, 2007. </reference>
		<reference numeration="37" content_type="text"> Stange, F. and Döhling, F.: N-15 tracing model SimKIM to analyse the NO and N2O production during autotrophic, heterotrophic nitrification, and denitrification in soils, Isot. Environ. Health S., 41, 261–274, 2005. </reference>
		<reference numeration="38" content_type="text"> Stark, J. M. and Firestone, M. K.: Kinetic characteristics of ammonium-oxidizer communities in a California oak woodland-annual grassland, Soil Biol. Biochem., 28, 1307–1317, 1996. </reference>
		<reference numeration="39" content_type="text"> Stevens, R. J., Laughlin, R. J., Burns, L. C., Arah, J. R. M., and Hood, R. C.: Measuring the contributions of nitrification and denitrification to the flux of nitrous oxide from soil, Soil Biol. Biochem., 29, 139–151, 1997. </reference>
		<reference numeration="40" content_type="text"> Vitousek, P. M., Gosz, J. R., Grier, C. C., Melillo, J. M., Reiners, W. A., and Todd, R. L.: Nitrate losses from disturbed ecosystems, Science, 204, 469–474, 1979. </reference>
		<reference numeration="41" content_type="text"> Watson, C. I. and Mills, C. L.: Gross nitrogen transformations in grassland soils as affected by previous management intensity, Soil. Biol. Biochem., 30, 743–753, 1998. </reference>
		<reference numeration="42" content_type="text"> Wolf, I. and Russow, R.: Different pathways of formation of N2O, N-2 and NO in black earth soil, Soil Biol. Biochem., 32, 229–239, 2000. </reference>
		<reference numeration="43" content_type="text"> Zaman, M. and Chang, S. X.: Substrate type, temperature, and moisture content affect gross and net N mineralization and nitrification rates in agroforestry systems, Biol. Fert. Soils, 39, 269–279, 2004. </reference>
		<reference numeration="44" content_type="text"> Zaman, M., Di, H. J., Cameron, K. C., and Frampton, C. M.: Gross nitrogen mineralization and nitrification rates and their relationships to enzyme activities and the soil microbial biomass in soils treated with dairy shed effluent and ammonium fertilizer at different water potentials, Biol. Fert. Soils, 29, 178–186, 1999. </reference>
	</references>
</article>

