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Registro Completo |
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Biblioteca(s): |
Embrapa Florestas. |
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Data corrente: |
16/01/2019 |
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Data da última atualização: |
16/01/2019 |
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Autoria: |
WALTER, L. S.; SANTOS, C. A. dos; OLIVEIRA, L. dos S.; SILVA, E. C. A. da. |
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Título: |
Influência de tratamentos pré-germinativos e crescimento inicial de plântulas de Libidibia ferrea. |
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Ano de publicação: |
2018 |
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Fonte/Imprenta: |
Pesquisa Florestal Brasileira, Colombo, v. 38, e201801684, 2018. 6 p. |
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DOI: |
10.4336/2018.pfb.38e201801684 |
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Idioma: |
Português |
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Notas: |
Nota científica. |
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Conteúdo: |
Objetivou-se verificar a influência de tratamentos pré-germinativos no vigor de germinação e crescimento inicial de mudas de Libidibia ferrea. Foram utilizados 5 tratamentos: controle; ácido sulfúrico; água por 24 h; água quente e escarificação. Para a germinação, avaliou-se a porcentagem (%E), o índice de velocidade (IVE) e o tempo médio de emergência (TME) e para o crescimento inicial, avaliou-se a altura das mudas, diâmetro do caule, número de folhas, matéria seca das folhas, caule e das raízes, e razão raiz/parte aérea. O tratamento com ácido sulfúrico resultou em maior %E e IVE e menor TME, apresentando, também, o melhor crescimento das plantas. |
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Palavras-Chave: |
Libidibia ferrea; Seedlings production. |
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Thesagro: |
Dormência; Germinação; Muda; Produção. |
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Thesaurus Nal: |
Dormancy; Germination. |
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Categoria do assunto: |
K Ciência Florestal e Produtos de Origem Vegetal |
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URL: |
https://ainfo.cnptia.embrapa.br/digital/bitstream/item/190733/1/1684-18678-1-PB.pdf
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Marc: |
LEADER 01516naa a2200277 a 4500
001 2104337
005 2019-01-16
008 2018 bl uuuu u00u1 u #d
024 7 $a10.4336/2018.pfb.38e201801684$2DOI
100 1 $aWALTER, L. S.
245 $aInfluência de tratamentos pré-germinativos e crescimento inicial de plântulas de Libidibia ferrea.$h[electronic resource]
260 $c2018
500 $aNota científica.
520 $aObjetivou-se verificar a influência de tratamentos pré-germinativos no vigor de germinação e crescimento inicial de mudas de Libidibia ferrea. Foram utilizados 5 tratamentos: controle; ácido sulfúrico; água por 24 h; água quente e escarificação. Para a germinação, avaliou-se a porcentagem (%E), o índice de velocidade (IVE) e o tempo médio de emergência (TME) e para o crescimento inicial, avaliou-se a altura das mudas, diâmetro do caule, número de folhas, matéria seca das folhas, caule e das raízes, e razão raiz/parte aérea. O tratamento com ácido sulfúrico resultou em maior %E e IVE e menor TME, apresentando, também, o melhor crescimento das plantas.
650 $aDormancy
650 $aGermination
650 $aDormência
650 $aGerminação
650 $aMuda
650 $aProdução
653 $aLibidibia ferrea
653 $aSeedlings production
700 1 $aSANTOS, C. A. dos
700 1 $aOLIVEIRA, L. dos S.
700 1 $aSILVA, E. C. A. da
773 $tPesquisa Florestal Brasileira, Colombo$gv. 38, e201801684, 2018. 6 p.
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Registro original: |
Embrapa Florestas (CNPF) |
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Biblioteca |
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Registro |
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Registro Completo
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Biblioteca(s): |
Embrapa Suínos e Aves. |
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Data corrente: |
16/04/2015 |
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Data da última atualização: |
05/08/2019 |
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Tipo da produção científica: |
Artigo em Anais de Congresso |
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Autoria: |
OLIVEIRA, P. A. V. de; ANGNES, G.; NICOLOSO, R. da S.; HIGARASHI, M. M. |
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Afiliação: |
PAULO ARMANDO VICTORIA DE OLIVEIRA, CNPSA; UFSC; RODRIGO DA SILVEIRA NICOLOSO, CNPSA; MARTHA MAYUMI HIGARASHI, CNPSA. |
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Título: |
Greenhouse gas emissions on the treatment of swine slurry by composting. |
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Ano de publicação: |
2013 |
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Fonte/Imprenta: |
In: INTERNATIONAL SYMPOSIUM ON EMISSIONS OF GAS AND DUST FROM LIVESTOCK, 2012, Saint-Malo. [Proceedings?]. Saint-Brieuc: INRA; Le Rheu: IFIP-Institut du Porc, 2013. EMILI 2012. |
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Idioma: |
Inglês |
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Notas: |
Edited by Mélynda Hassouna and Nadine Guingand. |
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Conteúdo: |
The treatment of swine manure through composting is seen as an alternative to minimize environmental impact and im prove nutrient recycling. However, the degradation of organic matter during the composting process promotes greenhouse gas emissions (GHG: CO2, CH4, N2O), NH3 and water vapor. The objective of this study was to measure the flux of these gases to perform the mass balance (DM, TN, C and P) of composting piles. Three compost piles (3 m3, initial mass .935 kg of sawdust and slurry) were mounted inside PVC tunnels with controlled ventilation (flow 1.526 m3 /h). We evaluated temperatures and humidity (Datalogger TESTO 174H) inside and outside the tunnels and inside the biomass (TESTO Mod. 926, Type T), performed physical-chemical analysis of compost and measured GHG, NH3 and water vapor emissions every 4 min through infra red photoacoustic spectroscopy (INNOVA 1412). The average temperature observed in the biomass during composting was 45.53 ± 5.48ºC. The average H2O balance error (between input and output) recorded was 5.52%. Gaseo us losses of N-NH3 and N-N2O totaled 1.21 kg, representing 10.4% of the original 11.63 kg of N applied in the compost piles. NH3represented 78% of measured total N gaseous losses(NH3+N2O). The total C emitted as CH4 and CO2 gases totaled 80.96 kg, representing 40.2% of the original 201.28 kg of TOC in compost piles (sawdust+slurry). CO2 emission accounted for 97% of total C losses. Considering the global warming potential (GWP) of each GHG, 615.3 kg of CO2 eq were emitted duringcomposting. CO2 emissions accounted for 46.8% of total CO2 eq emission, while CH4 and N2O represented 11.1 and 42.2%, respectively. Mitigation of CH4, and especially N2 O emissions, during composting is critical due to the higher GPW of the se gases. The presence of pathogenic microorganisms (Escherichia coli and coli form bacteria) was observed in the input slurry, but those microorganisms were not detected in the final compost. It was possible to accurately measure and verify gas emissions with the association of direct measurements and mass balance. MenosThe treatment of swine manure through composting is seen as an alternative to minimize environmental impact and im prove nutrient recycling. However, the degradation of organic matter during the composting process promotes greenhouse gas emissions (GHG: CO2, CH4, N2O), NH3 and water vapor. The objective of this study was to measure the flux of these gases to perform the mass balance (DM, TN, C and P) of composting piles. Three compost piles (3 m3, initial mass .935 kg of sawdust and slurry) were mounted inside PVC tunnels with controlled ventilation (flow 1.526 m3 /h). We evaluated temperatures and humidity (Datalogger TESTO 174H) inside and outside the tunnels and inside the biomass (TESTO Mod. 926, Type T), performed physical-chemical analysis of compost and measured GHG, NH3 and water vapor emissions every 4 min through infra red photoacoustic spectroscopy (INNOVA 1412). The average temperature observed in the biomass during composting was 45.53 ± 5.48ºC. The average H2O balance error (between input and output) recorded was 5.52%. Gaseo us losses of N-NH3 and N-N2O totaled 1.21 kg, representing 10.4% of the original 11.63 kg of N applied in the compost piles. NH3represented 78% of measured total N gaseous losses(NH3+N2O). The total C emitted as CH4 and CO2 gases totaled 80.96 kg, representing 40.2% of the original 201.28 kg of TOC in compost piles (sawdust+slurry). CO2 emission accounted for 97% of total C losses. Considering the global warming potential (GWP) of each GHG... Mostrar Tudo |
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Palavras-Chave: |
Global warming potential; Manure treatment; Swine manure. |
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Thesaurus NAL: |
gas emissions. |
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Categoria do assunto: |
-- |
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URL: |
https://ainfo.cnptia.embrapa.br/digital/bitstream/item/122452/1/final6699.pdf
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Marc: |
LEADER 02880nam a2200205 a 4500
001 2013711
005 2019-08-05
008 2013 bl uuuu u00u1 u #d
100 1 $aOLIVEIRA, P. A. V. de
245 $aGreenhouse gas emissions on the treatment of swine slurry by composting.$h[electronic resource]
260 $aIn: INTERNATIONAL SYMPOSIUM ON EMISSIONS OF GAS AND DUST FROM LIVESTOCK, 2012, Saint-Malo. [Proceedings?]. Saint-Brieuc: INRA; Le Rheu: IFIP-Institut du Porc, 2013. EMILI 2012.$c2012
500 $aEdited by Mélynda Hassouna and Nadine Guingand.
520 $aThe treatment of swine manure through composting is seen as an alternative to minimize environmental impact and im prove nutrient recycling. However, the degradation of organic matter during the composting process promotes greenhouse gas emissions (GHG: CO2, CH4, N2O), NH3 and water vapor. The objective of this study was to measure the flux of these gases to perform the mass balance (DM, TN, C and P) of composting piles. Three compost piles (3 m3, initial mass .935 kg of sawdust and slurry) were mounted inside PVC tunnels with controlled ventilation (flow 1.526 m3 /h). We evaluated temperatures and humidity (Datalogger TESTO 174H) inside and outside the tunnels and inside the biomass (TESTO Mod. 926, Type T), performed physical-chemical analysis of compost and measured GHG, NH3 and water vapor emissions every 4 min through infra red photoacoustic spectroscopy (INNOVA 1412). The average temperature observed in the biomass during composting was 45.53 ± 5.48ºC. The average H2O balance error (between input and output) recorded was 5.52%. Gaseo us losses of N-NH3 and N-N2O totaled 1.21 kg, representing 10.4% of the original 11.63 kg of N applied in the compost piles. NH3represented 78% of measured total N gaseous losses(NH3+N2O). The total C emitted as CH4 and CO2 gases totaled 80.96 kg, representing 40.2% of the original 201.28 kg of TOC in compost piles (sawdust+slurry). CO2 emission accounted for 97% of total C losses. Considering the global warming potential (GWP) of each GHG, 615.3 kg of CO2 eq were emitted duringcomposting. CO2 emissions accounted for 46.8% of total CO2 eq emission, while CH4 and N2O represented 11.1 and 42.2%, respectively. Mitigation of CH4, and especially N2 O emissions, during composting is critical due to the higher GPW of the se gases. The presence of pathogenic microorganisms (Escherichia coli and coli form bacteria) was observed in the input slurry, but those microorganisms were not detected in the final compost. It was possible to accurately measure and verify gas emissions with the association of direct measurements and mass balance.
650 $agas emissions
653 $aGlobal warming potential
653 $aManure treatment
653 $aSwine manure
700 1 $aANGNES, G.
700 1 $aNICOLOSO, R. da S.
700 1 $aHIGARASHI, M. M.
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