CO2 emissions from a municipal site for final disposal of solid waste in Gualeguaychu, Entre Rios Province, Argentina
This paper estimates CO2 fluxes in a municipal site for final disposal of solid waste, located in Gualeguaychu, Argentina. Estimations were made using the accumulation chamber methods, which had been calibrated previously in laboratory. CO2 fluxes ranged from 31 to 331 g m-2 day-1. Three different p...
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2012
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| LEADER | 15130caa a22014177a 4500 | ||
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| 003 | AR-BaUEN | ||
| 005 | 20230518203936.0 | ||
| 008 | 190411s2012 xx ||||fo|||| 00| 0 eng|d | ||
| 024 | 7 | |2 scopus |a 2-s2.0-84860363024 | |
| 040 | |a Scopus |b spa |c AR-BaUEN |d AR-BaUEN | ||
| 100 | 1 | |a Sanci, R. | |
| 245 | 1 | 0 | |a CO2 emissions from a municipal site for final disposal of solid waste in Gualeguaychu, Entre Rios Province, Argentina |
| 260 | |c 2012 | ||
| 270 | 1 | 0 | |m Sanci, R.; Instituto de Geocronología y Geología Isotópica, Univ. de Buenos Aires,Consejo Nacional de Investigaciones Cientificas y Tecnicas,Pabellon INGEIS, Ciudad Universitaria, C1428EHA Ciudad Autónoma de Buenos Aires, Argentina; email: romina@ingeis.uba.ar |
| 506 | |2 openaire |e Política editorial | ||
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| 520 | 3 | |a This paper estimates CO2 fluxes in a municipal site for final disposal of solid waste, located in Gualeguaychu, Argentina. Estimations were made using the accumulation chamber methods, which had been calibrated previously in laboratory. CO2 fluxes ranged from 31 to 331 g m-2 day-1. Three different populations were identified: background soil gases averaging 46 g m-2 day-1, intermediate anomalous values averaging 110 g m-2 day-1 and high anomalous values averaging 270 g m-2 day-1. Gas samples to a depth of 20 cm were also taken. Gas fractions, XCO2 <0.1, XCH4 <0.01, XN2 ~0. 71 and XO2 ~0. 21, δ13C of CO2 (-34 to -18‰), as well as age of waste emplacement, suggest that the study site may be at the final stage of aerobic biodegradation. In a first approach, and following the downstream direction of groundwater flow, alkalinity and δ13C of dissolved inorganic carbon (-15 to 4‰) were observed to increase when groundwater passed through the disposal site. This suggests that the CO2 generated by waste biodegradation dissolves or that dissolved organic matter appears as a result of leachate degradation. © 2011 Springer-Verlag. |l eng | |
| 536 | |a Detalles de la financiación: PICT, 12243 | ||
| 536 | |a Detalles de la financiación: Acknowledgments This research was supported by the Instituto de Geocronología y Geología Isotópica (UBA-CONICET) and PICT 2002 No 12243. The authors are grateful to Eduardo Llambías, Anibal Tricarico and Gabriel Giordarengo for their collaboration in the field. | ||
| 593 | |a Instituto de Geocronología y Geología Isotópica, Univ. de Buenos Aires,Consejo Nacional de Investigaciones Cientificas y Tecnicas,Pabellon INGEIS, Ciudad Universitaria, C1428EHA Ciudad Autónoma de Buenos Aires, Argentina | ||
| 593 | |a Departamento de Geología, Facultad de Ciencias Exactas y Naturales, Universidad de Buenos Aires, Pabellón II, Ciudad Universitaria, C1428EHA Ciudad Autónoma de Buenos Aires, Argentina | ||
| 690 | 1 | 0 | |a CARBON ISOTOPES |
| 690 | 1 | 0 | |a CO2 FLUXES |
| 690 | 1 | 0 | |a DIC GROUNDWATER |
| 690 | 1 | 0 | |a SOLID WASTE |
| 690 | 1 | 0 | |a AEROBIC BIODEGRADATION |
| 690 | 1 | 0 | |a CARBON ISOTOPES |
| 690 | 1 | 0 | |a DISPOSAL SITES |
| 690 | 1 | 0 | |a DISSOLVED INORGANIC CARBON |
| 690 | 1 | 0 | |a DISSOLVED ORGANIC MATTERS |
| 690 | 1 | 0 | |a GAS FRACTION |
| 690 | 1 | 0 | |a GAS SAMPLES |
| 690 | 1 | 0 | |a LEACHATES |
| 690 | 1 | 0 | |a SOIL GAS |
| 690 | 1 | 0 | |a STUDY SITES |
| 690 | 1 | 0 | |a WASTE BIODEGRADATION |
| 690 | 1 | 0 | |a BIODEGRADATION |
| 690 | 1 | 0 | |a GROUNDWATER |
| 690 | 1 | 0 | |a GROUNDWATER FLOW |
| 690 | 1 | 0 | |a ISOTOPES |
| 690 | 1 | 0 | |a MUNICIPAL SOLID WASTE |
| 690 | 1 | 0 | |a SOLID WASTES |
| 690 | 1 | 0 | |a CARBON DIOXIDE |
| 690 | 1 | 0 | |a BIODEGRADATION |
| 690 | 1 | 0 | |a CALIBRATION |
| 690 | 1 | 0 | |a CARBON DIOXIDE |
| 690 | 1 | 0 | |a CARBON EMISSION |
| 690 | 1 | 0 | |a CARBON FLUX |
| 690 | 1 | 0 | |a CARBON ISOTOPE |
| 690 | 1 | 0 | |a DISSOLVED INORGANIC CARBON |
| 690 | 1 | 0 | |a DISSOLVED ORGANIC MATTER |
| 690 | 1 | 0 | |a GROUNDWATER FLOW |
| 690 | 1 | 0 | |a LEACHATE |
| 690 | 1 | 0 | |a MUNICIPAL SOLID WASTE |
| 690 | 1 | 0 | |a SOIL GAS |
| 690 | 1 | 0 | |a WASTE DISPOSAL |
| 690 | 1 | 0 | |a GUALEGUAYCHU |
| 651 | 4 | |a ARGENTINA | |
| 651 | 4 | |a ARGENTINA | |
| 651 | 4 | |a ENTRE RIOS | |
| 700 | 1 | |a Panarello, H.O. | |
| 700 | 1 | |a Ostera, H.A. | |
| 773 | 0 | |d 2012 |g v. 66 |h pp. 519-528 |k n. 2 |p Environ. Earth Sci. |x 18666280 |t Environmental Earth Sciences | |
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