<?xml version="1.0" encoding="ISO-8859-1"?><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance">
<front>
<journal-meta>
<journal-id>0871-018X</journal-id>
<journal-title><![CDATA[Revista de Ciências Agrárias]]></journal-title>
<abbrev-journal-title><![CDATA[Rev. de Ciências Agrárias]]></abbrev-journal-title>
<issn>0871-018X</issn>
<publisher>
<publisher-name><![CDATA[Sociedade de Ciências Agrárias de Portugal]]></publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S0871-018X2009000100029</article-id>
<title-group>
<article-title xml:lang="pt"><![CDATA[Produção de azoto mineral durante a compostagem de fracção sólida de chorume da pecuária leiteira intensiva]]></article-title>
<article-title xml:lang="en"><![CDATA[Production of mineral nitrogen during composting of dairy cattle slurry solid fraction]]></article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Brito]]></surname>
<given-names><![CDATA[L. M.]]></given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Mourão]]></surname>
<given-names><![CDATA[I.]]></given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Trindade]]></surname>
<given-names><![CDATA[H.]]></given-names>
</name>
<xref ref-type="aff" rid="A02"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[Coutinho]]></surname>
<given-names><![CDATA[J.]]></given-names>
</name>
<xref ref-type="aff" rid="A02"/>
</contrib>
</contrib-group>
<aff id="A01">
<institution><![CDATA[,Instituto Politécnico de Viana do Castelo (IPVC) Escola Superior Agrária de Ponte de Lima ]]></institution>
<addr-line><![CDATA[Ponte de Lima ]]></addr-line>
</aff>
<aff id="A02">
<institution><![CDATA[,Universidade de Trás-os-Montes e Alto Douro (UTAD) Departamento de Edafologia Centro de Ciência e Engenharia Agrícola (CECEA)]]></institution>
<addr-line><![CDATA[Vila Real ]]></addr-line>
</aff>
<pub-date pub-type="pub">
<day>00</day>
<month>01</month>
<year>2009</year>
</pub-date>
<pub-date pub-type="epub">
<day>00</day>
<month>01</month>
<year>2009</year>
</pub-date>
<volume>32</volume>
<numero>1</numero>
<fpage>323</fpage>
<lpage>334</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http://scielo.pt/scielo.php?script=sci_arttext&amp;pid=S0871-018X2009000100029&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://scielo.pt/scielo.php?script=sci_abstract&amp;pid=S0871-018X2009000100029&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://scielo.pt/scielo.php?script=sci_pdf&amp;pid=S0871-018X2009000100029&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="pt"><p><![CDATA[A fracção sólida do chorume (FSC) de duas explorações de pecuária leiteira intensiva foi compostada: (i) em 2004, sobre o solo, incluindo, ou não, palha, e com diferentes níveis de revolvimento; e (ii) em 2005, sobre uma tela de cobertura do solo, com e sem revolvimento, com diferentes coberturas e diferentes volumes. O teor de matéria seca (MS) da FSC da primeira exploração (30%) apresentou um valor superior, embora o rendimento da máquina separadora da FSC tenha sido inferior (1 m³ hora-1) relativamente ao observado na segunda exploração (4 e 3 m³ hora-1 correspondendo a 22% e 24% de MS, respectivamente, em 2004 e 2005). A FSC1 com 30% de MS atingiu elevadas temperaturas logo após a sua separação mas o mesmo não aconteceu com a FSC2 com menor teor de MS, particularmente quando foi compostada sem palha. O pH da FSC variou entre 8 e 9 durante a compostagem e a razão C/N foi semelhante entre tratamentos para o mesmo período de compostagem. O teor de N-NH4+ foi muito elevado durante a fase termófila da compostagem, após a qual diminuiu, acentuadamente, enquanto que o teor de N-NO3-foi mínimo naquela fase e aumentou após três meses de compostagem. O maior teor de MS inicial da FSC1 em comparação com a FSC2 e a mistura com palha associaram-se a concentrações mais baixas de azoto amoniacal (NNH4+). Considerando estas observações e, ainda, que as elevadas temperaturas durante a compostagem e o pH alcalino da FSC potenciam, eventualmente, a volatilização de amoníaco, a redução deste tipo de perdas de N poderá ser conseguida: (i) diminuindo o rendimento da máquina separadora da FSC; (ii) misturando a FSC com um material com elevada razão C/N; e (iii) diminuindo o número de revolvimentos.]]></p></abstract>
<abstract abstract-type="short" xml:lang="en"><p><![CDATA[Screw pressed dairy cattle slurry solid fraction (CSSF) was collected during 2004 and 2005 from two dairy farms with 30% and 22% -24% dry matter (DM) content and the effects of covered either with black polyethylene or with polypropylene, pile dimension, straw addition and of turning frequency on the fate of N were examined. The CSSF with 30% DM was collected at a rate of 1 m³ h-1 and the material with 22% 24% DM was collected at the rate of 4 and 3 3 h-1 min 2004 and 2005, respectively. Thermophilic temperatures were attained soon after separation of CSSF with 30% DM. In contrast, temperatures were much cooler in CSSF with 22% DM without straw. The pH ranged from 8 to 9 and C/N ratio was similar amongst treatments on each sampling occasion. Mineral N production was characterized - by high NH4+ and low NO3 contents during the thermophilic phase followed by a decrease of NH4+ and an increase of NO3 towards the end of composting. Higher DM, and straw addition were both associated with lower NH4+ compost concentrations. Therefore, to minimize the N loss as NH3 gas caused by the alkaline pH during the thermophilic phase of composting, it is suggested: i) to increase DM by slowing the rate of the screw dewatering mechanism; ii) to increase the C/N ratio of composting mixture; and iii) to reduce turning frequency.]]></p></abstract>
</article-meta>
</front><body><![CDATA[ <p align="center"><b>Produção de azoto mineral durante a compostagem de fracção    sólida de chorume da pecuária leiteira intensiva </b></p>     <p align="center"><b>Production of mineral nitrogen during composting of dairy    cattle slurry solid fraction </b></p>     <P align="center">L. M. Brito<Sup><a href="#1">1</a><a name="top1"></a></Sup>,    I. Mourão<Sup><a href="#1">1</a><a name="top1"></a></Sup>, H. Trindade<Sup><a href="#2">2</a><a name="top2"></a>    </Sup>&amp; J. Coutinho<Sup><a href="#2">2</a><a name="top2"></a> </Sup></P>     <p>&nbsp;</p>     <p align="center"><b>RESUMO</b></p>     <p>A fracção sólida do chorume (FSC) de duas explorações de pecuária leiteira    intensiva foi compostada: (i) em 2004, sobre o solo, incluindo, ou não, palha,    e com diferentes níveis de revolvimento; e (ii) em 2005, sobre uma tela de cobertura    do solo, com e sem revolvimento, com diferentes coberturas e diferentes volumes.    O teor de matéria seca (MS) da FSC da primeira exploração (30%) apresentou um    valor superior, embora o rendimento da máquina separadora da FSC tenha sido    inferior (1 m<Sup>3 </Sup>hora<Sup>-1</Sup>) relativamente ao observado na segunda    exploração (4 e 3 m<Sup>3 </Sup> hora<Sup>-1 </Sup>correspondendo a 22% e 24%    de MS, respectivamente, em 2004 e 2005). A FSC1 com 30% de MS atingiu elevadas    temperaturas logo após a sua separação mas o mesmo não aconteceu com a FSC2    com menor teor de MS, particularmente quando foi compostada sem palha. O pH    da FSC variou entre 8 e 9 durante a compostagem e a razão C/N foi semelhante    entre tratamentos para o mesmo período de compostagem. </P>     <p>O teor de N-NH4<Sup>+ </Sup>foi muito elevado durante a fase termófila da compostagem,    após a qual diminuiu, acentuadamente, enquanto que o teor de N-NO3<Sup>-</Sup>foi    mínimo naquela fase e aumentou após três meses de compostagem. O maior teor    de MS inicial da FSC1 em comparação com a FSC2 e a mistura com palha associaram-se    a concentrações mais baixas de azoto amoniacal (NNH4<Sup>+</Sup>). Considerando    estas observações e, ainda, que as elevadas temperaturas durante a compostagem    e o pH alcalino da FSC potenciam, eventualmente, a volatilização de amoníaco,    a redução deste tipo de perdas de N poderá ser conseguida: (i) diminuindo o    rendimento da máquina separadora da FSC; (ii) misturando a FSC com um material    com elevada razão C/N; e (iii) diminuindo o número de revolvimentos. </P>     <p>&nbsp;</p>     <p align="center"><b>ABSTRACT</b></p>     <p>Screw pressed dairy cattle slurry solid fraction (CSSF) was collected during    2004 and 2005 from two dairy farms with 30% and 22% -24% dry matter (DM) content    and the effects of covered either with black polyethylene or with polypropylene,    pile dimension, straw addition and of turning frequency on the fate of N were    examined. The CSSF with 30% DM was collected at a rate of 1 m<Sup>3 </Sup>h<Sup>-1    </Sup>and the material with 22% 24% DM was collected at the rate of 4 and 3    3 <Sub>h</Sub>-1 min 2004 and 2005, respectively. Thermophilic temperatures    were attained soon after separation of CSSF with 30% DM. In contrast, temperatures    were much cooler in CSSF with 22% DM without straw. The pH ranged from 8 to    9 and C/N ratio was similar amongst treatments on each sampling occasion. </P>     ]]></body>
<body><![CDATA[<p>Mineral N production was characterized - by high NH4<Sup>+ </Sup>and low NO3    contents during the thermophilic phase followed by a decrease of NH4<Sup>+ </Sup>and    an increase of NO3 towards the end of composting. Higher DM, and straw addition    were both associated with lower NH4<Sup>+ </Sup>compost concentrations. Therefore,    to minimize the N loss as NH3 gas caused by the alkaline pH during the thermophilic    phase of composting, it is suggested: i) to increase DM by slowing the rate    of the screw dewatering mechanism; ii) to increase the C/N ratio of composting    mixture; and iii) to reduce turning frequency. </P>     <p>&nbsp;</p>     <p>Texto completo disponível apenas em PDF.</p>     <p>Full text only available in PDF format.</p>     <p>&nbsp;</p>     <p align="center"><b>REFERÊNCIAS BIBLIOGRÁFICAS </b></p>     <p>Angelidaki, I. &amp; Ahring, B. K. 993. Thermophilic anaerobic digestion of    livestock waste: the effect of ammonia. <i>Appl. Microbiol. Biotechnol.</i>,    <b>38</b>: 560–564. </P>     <!-- ref --><p>Amon, B., Amon, T., Boxberger, J. &amp; Alt, C. 2001. Emissions of NH3, N2O    and CH4 from dairy cows housed in a farmyard manure tying stall. <i>Nutr. Cycl.    Agroecosyst.</i>, <b>60</b>: 103-113. &nbsp;&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;&nbsp;[&#160;<a href="javascript:void(0);" onclick="javascript: window.open('/scielo.php?script=sci_nlinks&ref=000020&pid=S0871-018X200900010002900001&lng=','','width=640,height=500,resizable=yes,scrollbars=1,menubar=yes,');">Links</a>&#160;]<!-- end-ref --><p>Bernal, M. P., Paredes, C., Sánchez-Monedero, M. A., &amp; Cegarra, J. 1998.    Maturity and stability parameters of compost prepared with a wide range of organic    wastes. <i>Bioresour. Technol.</i>, <b>63</b>: 91-99. </P>     <p>CEN, 1999. <i>European Standards - Soil Improvers and Growing Media.</i> European    Committee for Standardization. </P>     ]]></body>
<body><![CDATA[<p>Chadwick, D.R. 2005. Emissions of ammonia, nitrous oxide and methane from cattle    manure heaps: effect of compaction and covering. <i>Atmosph. Environ.</i>, <b>3</b>:    787–799. </P>     <p>Dewes, T. 1996. Effect of pH, temperature, amount of litter and storage density    on ammonia emissions from stable manure. <i>J. Agric. Sci.</i>, <b>127</b>:    501–509. </P>     <p>Ekinci, K., Keener, H.M. &amp; Elwell, D.L. 2000. Composting short paper fiber    with broiler litter and additives. Part I: effects of initial pH and carbon/nitrogen    ratio on ammonia emission. <i>Compost Sci. Util.</i>, <b>8</b>: 160–172. </P>     <p>Finstein, M.S. &amp; Miller, F.C. 1985. Principles of composting leading to    maximization of the decomposition rate, odour control, and cost effectiveness.    <i>In</i>. J.K.R. Gasser (eds) <i>Composting of Agricultural and Other Wastes</i>,    pp.13-26. Elsevier Applied Science, London. </P>     <p>Fukumoto, Y., Osada, T., Hanajima &amp; D., Haga, K. 2003. Patterns and quantities    of NH3, N2O and CH4, emissions during swine manure composting without forced    aeration-effect of compost pile scale. <i>Bioresour. Technol</i>, <b>89</b>:    109-14. </P>     <p>Gonçalves, M. S. &amp; Baptista, M. 2001. <i>Proposta de Regulamentação sobre    Qualidade do Composto para Utilização na Agricultura.</i> Laboratório Químico    Agrícola Rebelo da Silva, Instituto de Investigação Agrária, Ministério da Agricultura    do Desenvolvimento Rural das Pescas, Lisboa. </P>     <p>Hadas, A. &amp; Portnoy R. 1997. Rates of decomposition in soil and release    of available nitrogen from cattle manure and municipal waste compost. <i>Compost    Sci. Util.</i>, <b>53</b>: 48-54. </P>     <p>Hansen, M.N, Henriksen, K. &amp; Sommer, S.G. 2006. Observations of production    and emission of greenhouse gases and ammonia during storage of solids separated    from pig slurry: Effects of covering. <i>Atmosph. Environ.</i>, <b>4</b>: 4172–4181.</P>     <P>Eghball, B., Power, J. F., Gilley, J. E. &amp; Doran, J. W. 1997. Nutrient,    carbon, and mass loss during composting of beef cattle feedlot manure, <i>J.    Environ. Qual.</i>, <b>26</b>: 189-193. </P>     <p>Hao, X. &amp; Chang, C. 2001. Gaseous NO, NO2, and NH3 loss during cattle feedlot    manure composting. <i>Phyton-annales Rei Botanicae</i>, <b>41</b>(3): 81-93.  </P>     ]]></body>
<body><![CDATA[<p>Hellmann, B., L. Zelles, A. Palojarvi, &amp; Q. Bai. 1997. Emission of climate-relevant    trace gases and succession of microbial communities during open-windrow composting.    <i>Applied and Environ. Microbiol</i>,. <b>63</b>: 1011-18. </P>     <p>Houba, V.J.G., Van der Lee, J.J. &amp; Novozamsky, I. 1995. <i>Soil Analysis    Procedures – other procedures</i>, part 5B, 6<Sup>th </Sup>edition. Department    of Soil Science and Plant Nutrition, Wageningen Agricultural University, Netherlands.  </P>     <p>Kirchmann, H. 1985. Losses, plant uptake and utilisation during production    cycle. <i>Acta Agriculturae Scandinavia.</i> Suppl. 24, Stockholm, 72 p. </P>     <p>Michel, F., 1999. Managing compost piles to maximize natural aeration. <i>Biocycle</i>,    <b>40</b>(3): 56–58. </P>     <p>Peigné, J. &amp; Girardin, P. 2004. Environmental impacts on farm scale composting    practices. <i>Water, Air and Soil Pollut.</i>, <b>153</b>: 45–68. </P>     <p>Raviv, M., Medina, S., Krasnovsky, A. &amp; Ziadna, H. 2004. Organic matter    and nitrogen conservation in manure compost for organic agriculture. <i>Compost    Sci. Utiliz.</i>, <b>12</b>: 6-10. </P>     <p>Schelege, H.G. 1993. General <Sub>7</Sub>th Microbiology, ed. Cambrige University    Press, New York. </P>     <p>Sommer, S.G. 2001. Effect of composting on nutrient loss and nitrogen availability    of cattle deep litter. <i>Eur. J. Agric.</i>, <b>14</b>: 123–133. </P>     <p>Sommer, S.G. &amp; Moller, H.B. 2000. Emission of greenhouse gases during composting    of deep litter from pig production-effect of straw content. <i>J. Agric. Sci.,    Camb.</i>, <b>134</b>: 327-335. </P>     <p>Tchobanoglous, G., Theisen, H. &amp; Vigil, S. A. 1993. <i>Integrated Solid    Waste Management: Engineering Principles and Management Issues.</i> McGraw-Hill,    series in water resources and environmental engineering. </P>     ]]></body>
<body><![CDATA[<p>Tiquia, S.M. &amp; Tam, N.F. Y. 2000. Fate of nitrogen during composting of    chicken litter. <i>Environ. Pollution</i>, <b>110</b>: 535-541. </P>     <p>Webb, J., Chadwick, D. &amp; Ellis, S. 2001. Will storing farmyard manure in    compact anaerobic heaps be a simple and effective means of reducing ammonia    emissions?, <i>In</i> Sangiorgi, F. (ed.) <i>Technology Transfer.</i> Proceedings    of the 9th International RAMIRAN 2000 Workshop, Gargnano, Italy, 6–9 September    2000. Cemagref, France, pp. 161–166. </P>     <p>Zucconi, F. &amp; Bertoldi, M. 1987. Composts specifications for the production    and characterization of composts from municipal solid waste. <i>In</i> M. de    Bertoldi, M. P. Ferranti, P. L'Hermite, F. Zucconi (eds) <i>Compost: Quality    and Use</i>, pp. 30-50. Elsevier Applied Science, London. </P>     <p>&nbsp;</p>     <p><Sup><a href="#top1">1</a><a name="1"></a> </Sup>Escola Superior Agrária de    Ponte de Lima, Refóios, 4990-706 Ponte de Lima – Tel: (+351) 258 909 740 – Fax:    (+351) 258 909 779 – E-mail: <a href="mailto:miguelbrito@esa.ipvc.pt">miguelbrito@esa.ipvc.pt</a>;</P>     <P><Sup><a href="#top2">2</a><a name="2"></a> </Sup>CECEA, Departamento de Edafologia,    Universidade de Trás-os-Montes e Alto Douro, Apartado 1013, 5001-911 Vila Real  </P>      ]]></body><back>
<ref-list>
<ref id="B1">
<nlm-citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname><![CDATA[Amon]]></surname>
<given-names><![CDATA[B.]]></given-names>
</name>
<name>
<surname><![CDATA[Amon]]></surname>
<given-names><![CDATA[T.]]></given-names>
</name>
<name>
<surname><![CDATA[Boxberger]]></surname>
<given-names><![CDATA[J.]]></given-names>
</name>
<name>
<surname><![CDATA[Alt]]></surname>
<given-names><![CDATA[C.]]></given-names>
</name>
</person-group>
<article-title xml:lang="en"><![CDATA[Emissions of NH3, N2O and CH4 from dairy cows housed in a farmyard manure tying stall.]]></article-title>
<source><![CDATA[Nutr. Cycl. Agroecosyst.]]></source>
<year>2001</year>
<volume>60</volume>
<page-range>103-113</page-range></nlm-citation>
</ref>
</ref-list>
</back>
</article>
