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Flessa, Heiner
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Flessa, Heiner
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Flessa, Heiner
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Flessa, H.
Flessa, Heinz
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2002Journal Article [["dc.bibliographiccitation.firstpage","307"],["dc.bibliographiccitation.issue","3-4"],["dc.bibliographiccitation.journal","Geoderma"],["dc.bibliographiccitation.lastpage","325"],["dc.bibliographiccitation.volume","105"],["dc.contributor.author","Flessa, H."],["dc.contributor.author","Ruser, R."],["dc.contributor.author","Schilling, R."],["dc.contributor.author","Loftfield, N."],["dc.contributor.author","Munch, J. C."],["dc.contributor.author","Kaiser, E. A."],["dc.contributor.author","Beese, F."],["dc.date.accessioned","2018-11-07T10:32:10Z"],["dc.date.available","2018-11-07T10:32:10Z"],["dc.date.issued","2002"],["dc.description.abstract","The large temporal variation in nitrous oxide (N2O). methane (CH4) and carbon dioxide (CO2) flux rates is a major source of error when estimating cumulative fluxes of these radiative active trace gases. We developed an automated system for near-continuous, long-term measurements of N2O, CH4 and CO2 fluxes from cropland soils and used it to study the temporal variation of N2O and CH4 fluxes from potato (Solanum tuberosum L.) fields during the crop periods of 1997 and 1998, and also to determine the effects of management practices and weather. Additionally, we evaluated the error of other common methods, namely, weekly or monthly measurements, used for estimating cumulative fluxes. ne fluxes were quantified separately for the ridges, uncompacted interrows and tractor-compacted interrows. Total N2O-N emission from the potato field during the growing period (end of May to September) was 1.6 kg ha(-1) in 1997 and 2.0 kg ha(-1) in 1998; emissions were highest for the tractor-compacted soil. Periods of increased N2O losses were induced by heavy precipitation (in particular in compacted soil) and by the killing of potato tops (on the ridges) by herbicide application. The total CH4-C uptake in the potato field during the growing period was 295 g ha(-1) in 1997 and 317 g ha(-1) in 1998. The major fraction of the total CH, uptake (approximate to 86%) occurred on the ridges. Weekly measurements of N2O fluxes complemented by additional event-related flux determinations provided accurate estimates of total emissions. The monthly flux determination was not adequate for determining the temporal variation of the N2O emission rates. Weekly measurements were sufficient to provide reliable estimates of the cumulative CH4 uptake. (C) 2002 Elsevier Science B.V. All rights reserved."],["dc.identifier.doi","10.1016/S0016-7061(01)00110-0"],["dc.identifier.isi","000173148400010"],["dc.identifier.uri","https://resolver.sub.uni-goettingen.de/purl?gro-2/44283"],["dc.notes.status","zu prüfen"],["dc.notes.submitter","Najko"],["dc.publisher","Elsevier Science Bv"],["dc.relation.issn","0016-7061"],["dc.title","N2O and CH4 fluxes in potato fields: automated measurement, management effects and temporal variation"],["dc.type","journal_article"],["dc.type.internalPublication","yes"],["dc.type.peerReviewed","yes"],["dc.type.status","published"],["dspace.entity.type","Publication"]]Details DOI WOS2008Journal Article [["dc.bibliographiccitation.firstpage","891"],["dc.bibliographiccitation.issue","6"],["dc.bibliographiccitation.journal","Biology and Fertility of Soils"],["dc.bibliographiccitation.lastpage","895"],["dc.bibliographiccitation.volume","44"],["dc.contributor.author","Potthoff, Martin"],["dc.contributor.author","Dyckmans, Jens"],["dc.contributor.author","Flessa, Heinz"],["dc.contributor.author","Beese, Friedrich"],["dc.contributor.author","Joergensen, Rainer Georg"],["dc.date.accessioned","2018-11-07T11:13:13Z"],["dc.date.available","2018-11-07T11:13:13Z"],["dc.date.issued","2008"],["dc.description.abstract","A 28-day incubation experiment at 12 degrees C was carried out on the decomposition of maize leaf litter to answer the questions: (1) Is the decomposition process altered by chemical manipulations due to differences in the colonization of maize leaf litter? (2) Do organisms using this maize material contribute significantly to the soil microbial biomass? The extraction of the maize straw reduced its initial microbial biomass C content by 25%. Fumigation and extraction eliminated the microbial biomass by 88%. In total, 17% of added maize straw C was mineralized to CO(2) during the 28-day incubation at 12 degrees C in the treatment with non-manipulated straw. Only 14% of added C was mineralized in the treatment with extracted straw as well as in the treatment with fumigated and extracted straw. The net increase in microbial biomass C was 79 mu g g(-1) soil in the treatment with non-manipulated straw and an insignificant 9 mu g g(-1) soil in the two treatments with manipulated straw. However, the net increase did not reflect the fact that the addition of maize straw replaced an identical 58% (approximate to 180 mu g g(-1) soil) of the autochthonous microbial biomass C(3)-C in all three straw treatments. In the two treatments with manipulated straw, the formation of maize-derived microbial biomass C(4)-C was significantly reduced by 25%. In the three straw treatments, the ratio of fungal ergosterol-to-microbial biomass C ratio showed a constant 60% increase compared to the control, and the contents of glucosamine and muramic acid increased by 18%. The average fungal C/bacterial C ratio was 3.6 in the soil and 5.0 in the recovered maize straw, indicating that fungal dominance was not altered by the initial chemical manipulations of the maize straw-colonizing microorganisms."],["dc.identifier.doi","10.1007/s00374-007-0266-y"],["dc.identifier.isi","000257201600010"],["dc.identifier.uri","https://resolver.sub.uni-goettingen.de/purl?gro-2/53840"],["dc.notes.status","zu prüfen"],["dc.notes.submitter","Najko"],["dc.publisher","Springer"],["dc.relation.issn","0178-2762"],["dc.title","Decomposition of maize residues after manipulation of colonization and its contribution to the soil microbial biomass"],["dc.type","journal_article"],["dc.type.internalPublication","yes"],["dc.type.peerReviewed","yes"],["dc.type.status","published"],["dspace.entity.type","Publication"]]Details DOI WOS2000Conference Paper [["dc.bibliographiccitation.firstpage","63"],["dc.bibliographiccitation.issue","1"],["dc.bibliographiccitation.journal","Isotopes in Environmental and Health Studies"],["dc.bibliographiccitation.lastpage","78"],["dc.bibliographiccitation.volume","36"],["dc.contributor.author","Dyckmans, Jens"],["dc.contributor.author","Flessa, H."],["dc.contributor.author","Shangguan, Z."],["dc.contributor.author","Beese, F."],["dc.date.accessioned","2018-11-07T11:07:45Z"],["dc.date.available","2018-11-07T11:07:45Z"],["dc.date.issued","2000"],["dc.description.abstract","A continuous dual (CO2)-C-13 and (NH4NO3)-N-15-N-15 labelling experimental set-up is presented that was used to investigate the C and N uptake and allocation within 3-year old beech (Fagus sylvatica L.) during one growing season. The C and N allocation pattern was determined after six, twelve and eighteen weeks of growth. The carbon uptake was distinctly different in the three phases examined: The first six weeks after budbreak were dedicated to leaf growth with a RIS (root to shoot) ratio of 0.14 for the new carbon. The second growth phase showed a balanced RIS ratio of C allocation and after week 13, the root compartment was the main carbon sink (R/S = 6.97). Nitrogen allocation was more basipetal as compared to carbon. In the second growth phase, R/S of N-new was 5.57 but fell to 3.54 for the third growth phase probably due to formation of reserves in buds and stem."],["dc.identifier.doi","10.1080/10256010008032933"],["dc.identifier.isi","000088914000007"],["dc.identifier.pmid","11022326"],["dc.identifier.uri","https://resolver.sub.uni-goettingen.de/purl?gro-2/52642"],["dc.notes.status","zu prüfen"],["dc.notes.submitter","Najko"],["dc.publisher","Gordon Breach Sci Publ Ltd"],["dc.publisher.place","Reading"],["dc.relation.conference","22nd Annual Meeting of the German Working Group on Stable Isotopes (ASI)"],["dc.relation.eventlocation","UNIV GOTTINGEN, GOTTINGEN, GERMANY"],["dc.relation.issn","1025-6016"],["dc.title","A dual C-13 and N-15 long term labelling technique to investigate uptake and translocation of C and N in beech (Fagus sylvatica L.)"],["dc.type","conference_paper"],["dc.type.internalPublication","yes"],["dc.type.peerReviewed","yes"],["dc.type.status","published"],["dspace.entity.type","Publication"]]Details DOI PMID PMC WOS2000Journal Article [["dc.bibliographiccitation.firstpage","113"],["dc.bibliographiccitation.issue","1"],["dc.bibliographiccitation.journal","Plant Biology"],["dc.bibliographiccitation.lastpage","120"],["dc.bibliographiccitation.volume","2"],["dc.contributor.author","Dyckmans, J."],["dc.contributor.author","Flessa, H."],["dc.contributor.author","Polle, Andrea"],["dc.contributor.author","Beese, F."],["dc.date.accessioned","2018-09-18T09:51:53Z"],["dc.date.available","2018-09-18T09:51:53Z"],["dc.date.issued","2000"],["dc.description.abstract","A continuous dual 13CO2 and 15NH415NO3 labelling experiment was undertaken to determine the effects of ambient (350μmol mol‐1) or elevated (700μmol mol‐1) atmospheric CO2 concentrations on C and N uptake and allocation within 3‐year‐old beech (Fagus sylvatica L.) during leafing. After six weeks of growth, total carbon uptake was increased by 63 % (calculated on total C content) under elevated CO2 but the carbon partitioning was not altered. 56 % of the new carbon was found in the leaves. On a dry weight basis was the content of structural biomass in leaves 10 % lower and the lignin content remained unaffected under elevated as compared to ambient [CO2]. Under ambient [CO2] 37 %, and under elevated [CO2] 51 %, of the lignin C of the leaves derived from new assimilates. For both treatments, internal N pools provided more than 90 % of the nitrogen used for leaf‐growth and the partitioning of nitrogen was not altered under elevated [CO2]. The C/N ratio was unaffected by elevated [CO2] at the whole plant level, but the C/N ratio of the new C and N uptake was increased by 32 % under elevated [CO2]."],["dc.identifier.doi","10.1055/s-2000-9153"],["dc.identifier.uri","https://resolver.sub.uni-goettingen.de/purl?gro-2/15729"],["dc.language.iso","en"],["dc.notes.status","final"],["dc.title","The Effect of Elevated [CO2] on Uptake and Allocation of13C and15N in Beech (Fagus sylvatica L.) during Leafing"],["dc.type","journal_article"],["dc.type.internalPublication","unknown"],["dspace.entity.type","Publication"]]Details DOI2000Journal Article [["dc.bibliographiccitation.firstpage","77"],["dc.bibliographiccitation.issue","2"],["dc.bibliographiccitation.journal","ACTA HYDROCHIMICA ET HYDROBIOLOGICA"],["dc.bibliographiccitation.lastpage","82"],["dc.bibliographiccitation.volume","28"],["dc.contributor.author","Ludwig, B."],["dc.contributor.author","Heil, B."],["dc.contributor.author","Flessa, H."],["dc.contributor.author","Beese, F."],["dc.date.accessioned","2018-11-07T10:04:32Z"],["dc.date.available","2018-11-07T10:04:32Z"],["dc.date.issued","2000"],["dc.description.abstract","Dissolved organic carbon (DOC) in seepage water can combine with organic pollutants, with Al and heavy metal ions and transport them through the soil profile with a potential to contaminate groundwater. We studied the production of DOC in aerobic decomposition experiments at 8 degrees C and moisture close to field capacity in soils from two sites with different microbial activities (spodic dystric Cambisols with moder (SLB) and mor-moder (SLS) layers) using C-13-depleted plants of differing decomposability (Epilobium angustifolium and Calamagrostis epigeios). Additionally, we investigated the DOC transformation during soil passage in decomposition experiments and in the field for the sites SLB and SLS. For SLS, decomposition of Epilobium resulted in a cumulative CO2 production of 14% of the added C within 128 days. Priming effects were negligible. CO2: production for the experiments using Calamagrostis was less with 11% for SLB and 10% for SLS. Cumulative DOC production was markedly high in the Epilobium decomposition experiment, being 25 g m(-2), out of which 11 g m(-2) were Epilobium-derived (2% of the added C). For the Calamagrostis experiments, cumulative productions of DOC and Calamagrostis-derived DOC (0.1% of the added C for SLS and SLB) were much less. During the soil passage, much of the DOC was removed by sorption or decomposition processes. Field studies at SLS and SLB using C-13 natural abundance showed that C-13 distribution of soil organic matter increased with depth, probably mainly due to a discrimination of C isotopes by decomposing microorganisms. DOG, however, showed a depletion of C-13 from -28 parts per thousand PDB to -29 parts per thousand (SLB at 40 cm) or --28 to -30 parts per thousand (SLS at 20 cm) with depth, owing to preferential decomposition of C-13-enriched substances or preferential adsorption. This study indicates that DOC production is strongly affected by litter composition and that significant changes in DOC composition may occur during its passage through a soil depth of 40 cm."],["dc.identifier.doi","10.1002/(SICI)1521-401X(20002)28:2<77::AID-AHEH77>3.0.CO;2-V"],["dc.identifier.isi","000087121600002"],["dc.identifier.uri","https://resolver.sub.uni-goettingen.de/purl?gro-2/38713"],["dc.notes.status","zu prüfen"],["dc.notes.submitter","Najko"],["dc.publisher","Wiley-v C H Verlag Gmbh"],["dc.relation.issn","0323-4320"],["dc.title","Dissolved organic carbon in seepage water - Production and transformation during soil passage"],["dc.type","journal_article"],["dc.type.internalPublication","yes"],["dc.type.peerReviewed","yes"],["dc.type.status","published"],["dspace.entity.type","Publication"]]Details DOI WOS2002Journal Article [["dc.bibliographiccitation.artnumber","PII S0167-8809(01)00234-1"],["dc.bibliographiccitation.firstpage","175"],["dc.bibliographiccitation.issue","1-3"],["dc.bibliographiccitation.journal","Agriculture Ecosystems & Environment"],["dc.bibliographiccitation.lastpage","189"],["dc.bibliographiccitation.volume","91"],["dc.contributor.author","Flessa, H."],["dc.contributor.author","Ruser, R."],["dc.contributor.author","Dorsch, P."],["dc.contributor.author","Kamp, T."],["dc.contributor.author","Jimenez, M. A."],["dc.contributor.author","Munch, J. C."],["dc.contributor.author","Beese, F."],["dc.date.accessioned","2018-11-07T10:03:28Z"],["dc.date.available","2018-11-07T10:03:28Z"],["dc.date.issued","2002"],["dc.description.abstract","Agricultural practices contribute to emissions of the greenhouse gases CO2, CH4 and N2O. The aim of this study was to determine and discuss the aggregate greenhouse gas emission (CO2, CH4 and N2O) from two different farming systems in southern Germany. Farm A consisted of 30.4 ha fields (mean fertilization rate 188 kg N per ha), 1.8 ha meadows, 12.4 ha set-aside land and 28.6 adult beef steers (year-round indoor stock keeping). Farm B followed the principles of organic farming (neither synthetic fertilizers nor pesticides were used) and it consisted of 31.3 ha fields, 7 ha meadows, 18.2 ha pasture, 5.5 ha set-aside land and a herd of 35.6 adult cattle (grazing period 6 months). The integrated assessment of greenhouse gas emissions included those from fields, pasture, cattle, cattle waste management, fertilizer production and consumption of fossil fuels. Soil N2O emissions were estimated from 25 year-round measurements on differently managed fields. Expressed per hectare farm area, the aggregate emission of greenhouse gases was 4.2 and 3.0 Mg CO2 equivalents for farms A and B, respectively. Nitrous oxide emissions (mainly from soils) contributed the major part (about 60%) of total greenhouse gas emissions in both farming systems. Methane emissions (mainly from cattle and cattle waste management) were approximately 25% and CO2 emissions were lowest (circa 15%). Mean emissions related to crop production (emissions from fields, fertilizer production, and the consumption of fossil fuels for field management and drying of crops) was 4.4 and 3.2 Mg CO2 equivalents per hectare field area for farms A and B, respectively. On average, 2.53% of total N input by synthetic N fertilizers, organic fertilizers and crop residues were emitted as N2O-N. Total annual emissions per cattle unit (live weight of 500 kg) from enteric fermentation and storage of cattle waste were about 25% higher for farm A (1.6 Mg CO2 equivalents) than farm B (1.3 Mg CO2 equivalents). Taken together, these results indicated that conversion from conventional to organic farming led to reduced emissions per hectare, but yield-related emissions were not reduced. (C) 2002 Elsevier Science B.V. All rights reserved."],["dc.identifier.doi","10.1016/S0167-8809(01)00234-1"],["dc.identifier.isi","000178112700015"],["dc.identifier.uri","https://resolver.sub.uni-goettingen.de/purl?gro-2/38473"],["dc.notes.status","zu prüfen"],["dc.notes.submitter","Najko"],["dc.publisher","Elsevier Science Bv"],["dc.relation.issn","0167-8809"],["dc.title","Integrated evaluation of greenhouse gas emissions (CO2, CH4, N2O) from two farming systems in southern Germany"],["dc.type","journal_article"],["dc.type.internalPublication","yes"],["dc.type.peerReviewed","yes"],["dc.type.status","published"],["dspace.entity.type","Publication"]]Details DOI WOS2002Journal Article [["dc.bibliographiccitation.firstpage","66"],["dc.bibliographiccitation.issue","1"],["dc.bibliographiccitation.journal","Biology and Fertility of Soils"],["dc.bibliographiccitation.lastpage","71"],["dc.bibliographiccitation.volume","36"],["dc.contributor.author","Vor, T."],["dc.contributor.author","Dyckmans, Jens"],["dc.contributor.author","Flessa, H."],["dc.contributor.author","Beese, F."],["dc.date.accessioned","2018-11-07T10:11:59Z"],["dc.date.available","2018-11-07T10:11:59Z"],["dc.date.issued","2002"],["dc.identifier.doi","10.1007/s00374-002-0510-4"],["dc.identifier.isi","000177885700009"],["dc.identifier.uri","https://resolver.sub.uni-goettingen.de/purl?gro-2/40151"],["dc.notes.status","zu prüfen"],["dc.notes.submitter","Najko"],["dc.publisher","Springer"],["dc.relation.issn","0178-2762"],["dc.title","Use of microcalorimetry to study microbial activity during the transition from oxic to anoxic conditions"],["dc.type","journal_article"],["dc.type.internalPublication","yes"],["dc.type.peerReviewed","yes"],["dc.type.status","published"],["dspace.entity.type","Publication"]]Details DOI WOS2003Journal Article Discussion [["dc.bibliographiccitation.firstpage","126"],["dc.bibliographiccitation.issue","2"],["dc.bibliographiccitation.journal","Biology and Fertility of Soils"],["dc.bibliographiccitation.lastpage","127"],["dc.bibliographiccitation.volume","38"],["dc.contributor.author","Vor, T."],["dc.contributor.author","Dyckmans, Jens"],["dc.contributor.author","Flessa, H."],["dc.contributor.author","Beese, F."],["dc.date.accessioned","2018-11-07T10:37:51Z"],["dc.date.available","2018-11-07T10:37:51Z"],["dc.date.issued","2003"],["dc.identifier.doi","10.1007/s00374-003-0625-2"],["dc.identifier.isi","000184878100012"],["dc.identifier.uri","https://resolver.sub.uni-goettingen.de/purl?gro-2/45665"],["dc.notes.status","zu prüfen"],["dc.notes.submitter","Najko"],["dc.publisher","Springer"],["dc.relation.issn","0178-2762"],["dc.title","Reply of the authors to the comments of Dr. N. Barros"],["dc.type","journal_article"],["dc.type.internalPublication","yes"],["dc.type.peerReviewed","yes"],["dc.type.status","published"],["dc.type.subtype","letter_note"],["dspace.entity.type","Publication"]]Details DOI WOS2000Conference Paper [["dc.bibliographiccitation.firstpage","35"],["dc.bibliographiccitation.issue","1"],["dc.bibliographiccitation.journal","Isotopes in Environmental and Health Studies"],["dc.bibliographiccitation.lastpage","47"],["dc.bibliographiccitation.volume","36"],["dc.contributor.author","Heil, B."],["dc.contributor.author","Ludwig, B."],["dc.contributor.author","Flessa, H."],["dc.contributor.author","Beese, F."],["dc.date.accessioned","2018-11-07T11:07:40Z"],["dc.date.available","2018-11-07T11:07:40Z"],["dc.date.issued","2000"],["dc.description.abstract","The study of natural isotopic abundance signatures is useful to gain further insights in the processes resulting in depthwise changes in the composition of soil organic matter (SOM). Objectives were to describe the delta(13)C and delta(15)N abundances of SOM with depth in soils from a 153-year old beech (B1), a 119-year old spruce (F1) and a 61-year old spruce (F2) stand at Selling, north-west Germany, and to study, how podzolisation affects the isotopic abundances of C-13 and N-15 in the SOM. The degree of podzolisation decreased in the order F1 > B1 > F2. At the surface of the humus layer of all three sites, delta(13)C values are approximately 1 to 4 parts per thousand higher than in the leaves and needles, probably mainly due to the discrimination of C-13 by microbial decomposition. C-13 abundances in the organic layers of Fl and F2 increased only slightly from -27.6 parts per thousand PDB (B1, L) to -27.2 parts per thousand PDB (B1, Oh) and from -26.3 parts per thousand PDB (F2, L) to -25.9 parts per thousand PDB (F2, Oh), suggesting that biotic activity resulted in mixing of organic matter. At Fl, however, C-13 abundance increased from -27.5 parts per thousand PDB (L) to -26.0 parts per thousand PDB (Oh) which reflects the lack of mixing by animals. In the upper 2-4 cm of the mineral soil, i.e., in the eluvial horizons Aeh, C-13 values showed a minimum at the spruce sites which was presumably related to a translocation of C-13 enriched fulvic acids. Depthwise changes in delta(15)N values were not related to podzolisation processes. At all three sites, a N-15 enrichment with depth occurred in the mineral soil which is the result of the discrimination of N-15 by microbial decomposition."],["dc.identifier.doi","10.1080/10256010008032931"],["dc.identifier.isi","000088914000005"],["dc.identifier.pmid","11022324"],["dc.identifier.uri","https://resolver.sub.uni-goettingen.de/purl?gro-2/52616"],["dc.notes.status","zu prüfen"],["dc.notes.submitter","Najko"],["dc.publisher","Taylor & Francis Ltd"],["dc.publisher.place","Abingdon"],["dc.relation.conference","22nd Annual Meeting of the German Working Group on Stable Isotopes (ASI)"],["dc.relation.eventlocation","UNIV GOTTINGEN, GOTTINGEN, GERMANY"],["dc.relation.issn","1477-2639"],["dc.relation.issn","1025-6016"],["dc.title","C-13 and N-15 distributions in three spodic dystric cambisols under beech and spruce"],["dc.type","conference_paper"],["dc.type.internalPublication","yes"],["dc.type.peerReviewed","yes"],["dc.type.status","published"],["dspace.entity.type","Publication"]]Details DOI PMID PMC WOS2000Journal Article [["dc.bibliographiccitation.firstpage","262"],["dc.bibliographiccitation.issue","1"],["dc.bibliographiccitation.journal","Journal of Environmental Quality"],["dc.bibliographiccitation.lastpage","268"],["dc.bibliographiccitation.volume","29"],["dc.contributor.author","Flessa, H."],["dc.contributor.author","Beese, F."],["dc.date.accessioned","2018-11-07T11:09:13Z"],["dc.date.available","2018-11-07T11:09:13Z"],["dc.date.issued","2000"],["dc.description.abstract","Applying cattle slurry to soil may induce emissions of the greenhouse gases N2O and CH4. Our objective was to determine the effects of different application techniques (surface application and slit injection) of cattle (Bostaurus) slurry on the decomposition of slurry organic matter and the emissions of N2O and CH4. The effects of slurry application (43.6 m(3) ha(-1)) were studied for 9 wk under controlled laboratory conditions using a soil microcosm system with automated monitoring of the CO2, N2O, and CH4 fluxes, The soil used was a silty loam (Ap horizon of a cambisol) with a constant water-filled pore space of 67% during the experiment. About 38% of the organic matter applied with the slurry was decomposed within 9 wk. Production of CO2 was not affected by the application technique. Emissions of N2O and CN4 from the injected slurry were significantly higher than from the surface-applied slurry, probably because of restricted aeration at the injected-slurry treatment. Total N2O-N emissions were 0.2% (surface application) and 3.3% (slit injection) of the slurry N added, Methane emission occurred only during the first Few days followimg application. The total net nux of CH4-C for 2 wk was -12 g ha(-1) for the control (CH4 uptake), 2 g ha(-1) far the surface-applied slurry, and 39 g ha(-1) for the injected slurry. Slurry injection, which is recommended to reduce NH3 volatilization, appears to increase emissions of the greenhouse gases N2O and CH4 from the fertilized fields."],["dc.identifier.isi","000084885800034"],["dc.identifier.uri","https://resolver.sub.uni-goettingen.de/purl?gro-2/52960"],["dc.notes.status","zu prüfen"],["dc.notes.submitter","Najko"],["dc.publisher","Amer Soc Agronomy"],["dc.relation.issn","0047-2425"],["dc.title","Laboratory estimates of trace gas emissions following surface application and injection of cattle slurry"],["dc.type","journal_article"],["dc.type.internalPublication","yes"],["dc.type.peerReviewed","yes"],["dc.type.status","published"],["dspace.entity.type","Publication"]]Details WOS