Efecto de la fertilización orgánica y mineral en las propiedades del suelo, la emisión de los principales gases de efecto invernadero y en las diferentes fases fenológicas del cultivo de café (Coffea arabica L.)

El cultivo de café es de gran importancia a nivel mundial (ICO, 2011), y en el Ecuador ha sido uno de los cultivos más importantes en la generación de divisas (COFENAC, 2011). Sin embargo en los sistemas productivos de este país se puede apreciar el uso inapropiado de fertilizantes, lo que conlleva a una pérdida de nutrientes, por lo que es importante estudiar las dosis adecuadas para la fertilización tanto mineral como orgánica. El objetivo del trabajo fue evaluar el efecto de la fertilización mineral y orgánica en diferentes dosis en un monocultivo de café en la provincia de Loja, sobre las propiedades del suelo, la emisión de los principales gases que provocan el efecto invernadero y la fenología y productividad del cultivo. En la provincia de Loja (Ecuador) se seleccionó un área de 2.520 m2 en la que se establecieron 21 parcelas de café arábigo (Coffea arabica L.) var. caturra y se aplicó tres tratamientos con tres repeticiones de fertilización mineral y tres orgánicos con dosis: bajas minerales (MIN 1= 157 Kg NPK ha-1 año-1 para el primer año y 425 Kg NPK ha-1 año-1 para el segundo año), medias minerales (MIN 2= 325 Kg NPK ha-1 año-1 para el primer año y 650 Kg NPK ha-1 año-1 en el segundo año) y altas minerales (MIN 3= 487 y 875 Kg NPK ha-1 año-1 para el primer y segundo año respectivamente), bajas orgánicas (ORG 1= 147 Kg NPK ha-1 año-1 en el primer año y 388 Kg NPK ha-1 año-1 en el año dos), medias orgánicas (ORG 2= 265 Kg NPK ha-1 año-1 para el primer año y 541 Kg NPK ha-1 año-1 en el segundo año), altas orgánicas (ORG 3= 368 Kg NPK ha-1 año-1 para el primer año y 727 Kg NPK ha-1 año-1 en el segundo año) y fertilización cero (TES = sin fertilización). Se usó urea, roca fosfórica y muriato de potasio en la fertilización mineral y humus (Bioabor) en la orgánica, más un tratamiento testigo, cada tratamiento tuvo tres repeticiones. El tiempo de evaluación de los fertilizantes aplicados fue de dos años consecutivos, la fertilización se la realizó dos veces por año y en base a análisis del suelo y demandas nutricionales del cultivo. para determinar las características del suelo se realizó muestreos de suelos en cada parcela a una profundidad de 20 cm de estas muestras los parámetro iniciales determinados fueron: color (Munsell), textura (método del hidrómetro), pH (relación 1:2,5 suelo-agua), Materia orgánica (Walkey y Black), Nitrógeno (Micro Kjendahl), Fósforo (Bray y Kurtz), Potasio (Olsen), estos procesos se repitieron cada seis meses para poder evaluar los cambios de que se producen debido a la fertilización mineral y orgánica en el cultivo. Las emisiones de gases efecto invernadero desde el suelo al ambiente se determinaron por el método de cámara cerrada (Rondón, 2000) y la concentración por cromatografía de gases. Las mediciones fisiológicas (altura de planta, ancho de copa, grosor de tallo y producción) se las evaluó cada dos meses, a excepción de la producción que fue anual al término de cada cosecha. Además se realizó el análisis económico de la productividad del cultivo. El análisis estadístico de datos se lo realizó con el programa SPSS v. 17.0. Las medias fueron comprobadas mediante ANOVAS de un factor con test de Tukey (P < 0,05). El beneficio económico se estimó en términos de ingresos y gastos totales que se presentaron en el ensayo. Los resultados obtenidos al término del ensayo indican que los tratamientos MIN 2 y MIN 3 produjeron cambios más significativos en comparación con los otros tratamientos establecidos en la mejora de fertilidad del suelo, el pH ha sido menos afectado en la acidificación en comparación con los tratamientos orgánicos que se han acidificado mayormente; la materia orgánica (MO) tuvo incrementos considerablemente bueno en estos dos tratamientos, sin embargo fueron superados por los tratamientos de fertilización orgánica; el nitrógeno total (Nt )y el potasio (K) también presentaron mejores valores al termino del ensayo y el fósforo (P) mostro incrementos buenos aunque un poco menores que los de los tratamientos ORG 2 y ORG 3. En lo que respecta a las emisiones de gases efecto invernadero, los flujos acumulados de óxido nitroso (N2O) en los dos años han aumentado en todos los tratamientos en comparación con el tratamiento Testigo, pero de manera considerable y con mayores flujos en el tratamiento MIN 3 y MIN 2 que se podrían considerarse los de mayor contaminación por N2O al ambiente lo que se le atribuye a las dosis de fertilización mineral aplicadas en el periodo de investigación, los tratamiento MIN 1 y todos los tratamientos orgánicos muestran menores emisiones al ambiente. Las emisiones de metano (CH4) no muestran mayores diferencias de emisiones entre tratamientos, siendo los mayores emisores los tratamientos ORG 3 y ORG 2 posiblemente debido al abono orgánico y añadido al suelo; para las emisiones de dióxido de carbono (CO2) de manera similar al CH4 el tratamiento ORG 3 fue el que presento mayores emisiones, los flujos de CO2 al ambiente de los otros tratamientos fueron menores y no presentaron diferencias significativas entre ellos. La variables fisiológicas en todos los casos apoyaron al desarrollo de las plantas de café, esto al ser comparadas con el tratamiento Testigo, sin embargo las que alcanzaron las mayores altitudes, anchos de copas y diámetro de tallo fueron las plantas del tratamiento MIN 3, seguido del MIN 3, no mostrando significancia entre ellos, y para los tratamientos orgánicos el que presento muy buenos resultados en estas variables ha sido el ORG 3, el cual no presento diferencias significativas con el MIN 2, lo cual comprueba que la fertilización mineral es más efectiva en este caso frente a la orgánica. Para el primer año de producción el tratamiento mineral con fertilización MIN 3 es el que obtuvo mayor producción no presentando diferencia estadística con el tratamiento con el MIN 2, no obstante fueron significativamente mayores que los otros tratamientos. Vale indicar que también el tratamiento MIN 1 y el tratamiento ORG 3 han presentado una producción considerable de café no mostrando diferencias estadísticas entre ellos. Para el segundo año la producción el cultivo mostró mayores rendimientos que el primer año de evaluación en todos los tratamientos, esto debido a la fisiología propia del cultivo y por otra parte se atribuye a la adición de fertilizantes que se ha realizado durante todo el ensayo; de manera similar al anterior los tratamientos MIN 3 y MIN 2 obtuvieron mejores rendimientos, no enseñando diferencias estadísticas significativas entre ellos, no obstante el tratamiento mineral dosis MEDIA no presentó significancia estadística con el ORG 3. El benéfico económico ha resultado mayor en el tratamiento MIN 3 y MIN 2, aunque el tratamiento MIN 2, es el que obtiene la mejor relación costo-beneficio; los tratamientos ORG 2 y ORG 3 y Testigo has producido beneficios negativos para el productor. En cuanto a la parte ambiental se considera que los mejores tratamientos en cuanto ha cuidado ambiental serían los tratamientos MIN 1 y ORG 1, sin embargo a nivel de producción y rentabilidad para el productor baja. ABSTRACT Coffee growing has great importance worldwide (ICO, 2011), and in Ecuador, it has been one of the most important crops to generate income (COFENAC, 2011). However, in the productive systems of this country, the inappropriate use of fertilizers has been observed which produces loss of nutrients, thus it is important to study suitable doses for mineral and organic fertilizing. The purpose of the study was to evaluate the effect of mineral and organic fertilizing at different doses in a coffee monoculture in the province of Loja on soil characteristics, emission of the main gasses that produce the greenhouse effect and the phenology and productivity of crops. In the province of Loja (Ecuador) an area of 2.520 m2 was chosen, where 21 plots of Arabica coffee (Coffea arabica L.), the caturra variety were cultivated and three treatments with three repetitions each one for mineral and organic fertilization were used with doses that ranged from: mineral low (MIN 1= 157 Kg NPK ha-1 año-1 for the first year y 425 Kg NPK ha-1 año-1 for the second year), mineral medium (MIN 2= 325 Kg NPK ha-1 año-1 for the first year y 650 Kg NPK ha-1 año-1 I the second year) y mineral high (MIN 3= 487 y 875 Kg NPK ha-1 año-1 for the first and second year respectively), organic low (ORG 1= 147 Kg NPK ha-1 año-1 in the first year y 388 Kg NPK ha-1 año-1 in the second year), organics medium (ORG 2= 265 Kg NPK ha-1 año-1 for the first year y 541 Kg NPK ha-1 año-1 in the second year), organics high (ORG 3= 368 Kg NPK ha-1 año-1 for the first year and 727 Kg NPK ha-1 año-1 in the second year) y fertilization zero (TES = no fertilization).; urea, phosphoric rock and muriate of potash were used in the mineral fertilization and humus (Bioabor) in the organic, plus a blank treatment. Time to evaluate the applied fertilizers was for two consecutive years, fertilization was done twice per year based on soil analysis and nutritional requirements of the crops. In order to determine the characteristics of the soil, samples of soil in each plot with a depth of 20 cm were done; from these samples, the determined initial parameters were: color (Munsell), texture (hydrometer method), pH (soil-water 1:2,5 relation), organic matter (Walkey y Black), nitrogen (Micro Kjendahl), phosphorus (Bray y Kurtz), potassium (Olsen); these processes were repeated each six months in order to evaluate the changes that are produced due to mineral and organic fertilization in the crops. The emissions of greenhouse gasses from the soil to the atmosphere were determined by using enclosure method (Rondón, 2000) and the concentration, by using gas chromatography during the whole testing. The physiological measures (plant height, width of the top of the tree, thickness of the stem and production) were evaluated each two months, except for production which was annual at the end of each harvest. Moreover, the economic analysis of the productivity of the crops was done. The statistical analysis of the data was done using SPSS v. 17.0. The means were proved by ANOVAS with a factor of a Tukey test (P < 0,05). The economic benefit was estimated in terms of incomes and total expenses which were presented in the essay. The results obtained at the end of the essay show that the MIN 2 and MIN 3 treatments produced more meaningful changes in comparison with the other treatments used to improve soil fertility; pH was less affected in the acidification compared with the organic treatments which were greatly acidified; organic matter (MO) had increased considerably in these two treatments; however, they were surpassed by the organic treatments of fertilization; total nitrogen (Nt) and potassium (K) also presented better results at the end of the essay and phosphorus (P) showed good increasing figures although a little lower compared with ORG 2 and ORG 3 treatments. Regarding the emission of the greenhouse gasses, the fluxes accumulated from nitrous oxide (N2O) in two years increased in all the treatments in comparison with the blank treatment, but in a greater form and with higher fluxes in the MIN 3 and MIN 2 treatments which can be considered as the ones with greater contamination of N2O in the atmosphere, this can be due to the applied mineral doses to fertilize during the process; MIN 1 treatments and all the organic ones showed lower emission to the atmosphere. Methane emissions (CH4) did not show major differences in emissions in the treatments, being the greater emissions the ORG 3 and ORG 2 treatments; this is possibly due to the organic compost added to the soil; regarding carbon dioxide (CO2) emissions, in a similar way to CH4, the ORG 3 treatment was the one that presented greater emissions, the CO2 emissions to the atmosphere in the other treatments were lower and did not present meaningful differences among them. The physiological variables in all the cases helped coffee crops grow, this was observed when compared with the blank treatment; however, plants that reached the greatest height, width of top and diameter of stem were the plants of the MIN 3 treatment, followed by MIN 3, which did not show much significance among them, and for the organic treatments, the one that presented great results in these variables was ORG 3, which did not show meaningful differences compared with MIN 2, which proves that mineral fertilization is more effective in this case compared with the organic. In the first year of production, the mineral treatment with MIN 3 fertilization obtained greater production and thus did not show statistical difference with MIN 2 treatment, although the other treatments were greater. It is worth mentioning that MIN 1 treatment and ORG 3 treatment presented a meaningful production of coffee, not showing statistical differences among them. For the second year, the production of the crops showed greater profits than in the first year of evaluation in all the treatments, this was due to the physiological properties of the crops and on the other hand, it might be due to the addition of fertilizers during the whole essay; in a similar way, MIN 3 and MIN 2 performed better, not showing greater statistical differences among them, although the mineral treatment MEDIUM doses did not show statistical difference compared with ORG 3. The economic benefit was greater in the MIN 3 and MIN 2 treatments, although MIN 2 treatment is the one that shows the best cost-benefit ratios; ORG 2 and ORG 3 treatments and the blank produced negative benefits for the producer. Regarding the environment, the best treatments to care for the atmosphere are considered to be MIN 1 and ORG 1 treatments; however, regarding production volume and profitability they were low for the producer.

Isotopic ratios and concentrations for mineral-associated and particulate organic fractions of sediment core Wilson_Lake samples

The flux of sediment and organic carbon from continents to the coastal ocean is an important factor governing organic burial in coastal sediments, and these systems preserve important records of environmental and biogeochemical conditions during past global change events. Burial of organic materials in coastal systems can be promoted by chemical resilience or through protection by association with mineral surfaces, but the role and influence of these processes on organic records from ancient sediments is poorly known. We studied sediment and organic matter burial as particulate organic matter (POM) and mineral-bound organic matter (MOM) in near-shore marine sediments from the Wilson Lake core (New Jersey, USA) that span the Paleocene-Eocene thermal maximum (PETM), a climatic perturbation 55.9 Myr ago. Our results show that distinct POM and MOM fractions can be isolated from sediments. Both fractions appear to be dominated by terrestrial material, but POM consisted primarily of recently synthesized material whereas MOM included a significant fraction of pre-aged organic matter from soils or ancient sediments. Variation in organic burial through the PETM is associated with changes in inorganic nitrogen burial, clay mineralogy, and clastic grain size that we associate with enhanced continental weathering, erosion and redeposition of ancient kaolinites, and eustatic sea level variation, respectively. These results provide a new perspective on factors governing carbon burial and carbon isotope records in ancient marine margin settings and offer information on rate and phasing of late Paleocene/early Eocene Earth system changes that may constrain interpretations of the cause of the PETM climate change event.

Hydrothermal control on organic matter alteration and illite precipitation, Mt Isa Basin, Australia

Abundant illite precipitation, in Proterozoic rocks from Northern Lawn Hill Platform, Mt Isa Basin, Australia, occurred in organic matter-rich black shales rather than in sandstones, siltstones and organic matter-poor shales. Sandstones and siltstones acted as impermeable rocks, as early diagenetic quartz and carbonate minerals reduced the porosity-permeability. Scanning and transmission electron microscopy (SEM and TEM) studies indicate a relation between creation of microporosity-permeability and organic matter alteration, suitable for subsequent mineral precipitation. K-Ar data indicate that organic matter alteration and the subsequent illite precipitation within the organic matter occurred during the regional hydrothermal event at 1172 +/- 150 (2sigma) Ma. Hot circulating fluids are considered to be responsible for organic matter alteration, migration and removal of volatile hydrocarbon, and consequently porosity-permeability creation. Those rocks lacking sufficient porosity-permeability, such as sandstones, siltstones and organic matter poor shales, may not have been affected by fluid movement. In hydrothermal systems, shales and mudstones may not be impermeable as usually assumed because of hydrocarbons being rapidly removed by fluid, even with relatively low total organic carbon.

Piggery pond sludge as a nitrogen source for crops. 1. Mineral N supply estimated from laboratory incubations and field application of stockpiled and wet sludge

Piggery pond sludge (PPS) was applied, as-collected (Wet PPS) and following stockpiling for 12 months ( Stockpiled PPS), to a sandy Sodosol and clay Vertosol at sites on the Darling Downs of Queensland. Laboratory measures of N availability were carried out on unamended and PPS-amended soils to investigate their value in estimating supplementary N needs of crops in Australia's northern grains region. Cumulative net N mineralised from the long-term ( 30 weeks) leached aerobic incubation was described by a first-order single exponential model. The mineralisation rate constant (0.057/week) was not significantly different between Control and PPS treatments or across soil types, when the amounts of initial mineral N applied in PPS treatments were excluded. Potentially mineralisable N (N-o) was significantly increased by the application of Wet PPS, and increased with increasing rate of application. Application of Wet PPS significantly increased the total amount of inorganic N leached compared with the Control treatments. Mineral N applied in Wet PPS contributed as much to the total mineral N status of the soil as did that which mineralised over time from organic N. Rates of CO2 evolution during 30 weeks of aerobic leached incubation indicated that the Stockpiled PPS was more stabilised (19-28% of applied organic C mineralised) than the Wet PPS (35-58% of applied organic C mineralised), due to higher lignin content in the former. Net nitrate-N produced following 12 weeks of aerobic non-leached incubation was highly correlated with net nitrate-N leached during 12 weeks of aerobic incubation (R-2 = 0.96), although it was

Between-tree variation in fruit quality and fruit mineral concentrations of Hass avocados

Inconsistent internal fruit quality in Hass avocados affects consumer confidence. To determine the influence of individual trees on fruit quality, Hass avocado fruit were harvested from adjacent trees of similar external appearance in 3 commercial orchards in 1998 and 1 orchard in 1999. The trees in each orchard were grown with similar commercial practices and in similar soil types. Within each location, there were significant (P < 0.05) differences in the mean ripe fruit quality between trees with respect to fruit body rot severity ( mainly anthracnose) with and without cold storage, internal disorders severity due to diffuse discolouration and vascular browning ( after cold storage), days to ripen, percentage dry matter, and the percentage of the skin area with purple-black colour when ripe. These effects were also noted in the same orchard in 1999. There were significant (P < 0.05) differences in fruit flesh calcium, magnesium, potassium, boron and zinc concentrations between trees. Significant (P < 0.05) correlations were observed between average fruit mineral concentrations in each tree ( particularly calcium, magnesium and potassium) and body rot severity, percentage dry matter and fruit mass. There was little conclusive evidence that characteristics such as the growth of the non-suberised roots or the degree of scion under- or overgrowth was involved in these tree effects; however, differences between trees with respect to other rootstock characteristics may be involved. The inconsistency of the correlations across sites and years suggested that other factors apart from tree influences could also affect the relationship between fruit minerals and fruit quality.

Zinc deposits and related mineralization of the Burketown mineral field, including the world-class Century Deposit, Northern Australia: Fluid inclusion and stable isotope evidence for basin fluid sources

The stratiform Century Zn-Pb deposit and the discordant Zn-Pb lode deposits of the Burketown mineral field, northern Australia, host ore and gangue minerals with primary fluid inclusions that have not been affected by the Isan orogeny, thus providing a unique opportunity to investigate the nature of the ore-forming brines. All of the deposits are hosted in shales and siltstones belonging to the Isa superbasin and comprise sphalerite, pyrite, carbonate, quartz, galena, minor chalcopyrite, and minor illite. According to Pb model ages, the main ore stage of mineralization at Century formed at I575 Ma, some 20 m.y. after deposition of the host shale sequence. Microthermometry on undeformed, primary fluid inclusions hosted in porous sphalerite shows that the Zn at Century was transported to the deposit by a homogeneous, Ca2+- and Na+-bearing brine with a salinity of 21.6 wt percent NaCl equiv. delta D-fluid of the fluid inclusion water ranges from -89 to -83 per mil, consistent with a basinal brine that evolved from meteoric water. Fluid inclusion homogenization temperatures range between 74 degrees and 125 degrees C, which are lower than the 120 degrees to 160 degrees C range calculated from vitrinite reflectance and illite crystallinity data from the deposit. This discrepancy indicates that mineralization likely formed at 50 to 85 Mpa, corresponding to a depth of 1,900 to 3,100 m. Transgressive galena-sphalerite veins that cut stratiform mineralization at Century and breccia-filled quartz-dolomite-sphalerite-galena veins in the discordant Zn-Pb lodes have Pb model ages between 1575 and 1485 Ma. Raman spectroscopy and microthermometry reveal that the primary fluid inclusions in these veins contain Ca2+, Na+. but they have lower salinities between 23 and 10 wt percent NaCl equiv and higher delta D-fluid values ranging from -89 to -61 per mil than fluid inclusions in porous sphalerite from Century. Fluid inclusion water from sphalerite in one of the lode deposits has delta O-18(fluid) values of 1.6 and 2.4 per mil, indistinguishable from delta O-18(fluid) values between -0.3 to +7.4 per mil calculated from the isotopic composition of coexisting quartz, dolomite, and illite. The trend toward lower salinities and higher delta D-fluid values relative to the earlier mineralizing fluids is attributed to mixing between the fluid that formed Century and a seawater-derived fluid from a different source. Based on seismic data from the Lawn Hill platform and paragenetic and geochemical results from the Leichhardt River fault trough to the south, diagenetic aquifers in the Underlying Calvert superbasin appear to have been the most likely sources for the fluids that formed Century and the discordant lode deposits. Paragenetically late sphalerite and calcite cut sphalerite, quartz, and dolomite in the lode deposits and contain Na+-dominated fluid inclusions with much lower salinities than their older counterparts. The isotopic composition of calcite also indicates delta O-18(fluid) from 3.3 to 10.7 per mil, which is larger than the range obtained from synmineralization minerals, supporting the idea that a unique fluid source was involved. The absolute timing of this event is unclear, but a plethora of Pb model, K-Ar, and Ar-40/Ar-39 ages between 1440 and 1300 Ma indicate that a significant volume of fluid was mobilized at this time. The deposition of the Roper superbasin from ca. 1492 +/- 4 Ma suggests that these late veins formed from fluids that may have been derived from aquifers in overlying sediments of the Roper superbasin. Clear, buck, and drusy quartz in veins unrelated to any form of Pb-Zn mineralization record the last major fluid event in the Burketown mineral field and form distinct outcrops and ridges in the district. Fluid inclusions in these veins indicate formation from a low-salinity, 300 degrees +/- 80 degrees C fluid. Temperatures approaching 300 degrees C recorded in organic matter adjacent to faults and at sequence boundaries correspond to K-Ar ages spanning 1300 to 1100 Ma, which coincides with regional hydrothermal activity in the northern Lawn Hill platform and the emplacement of the Lakeview Dolerite at the time of assemblage of the Rodinia supercontinent.

(Table 1) Mineral phosphorus contents in bottom sediments and interstitial waters of the Southeast Atlantic

Concentrations of mineral phosphorus in interstitial waters from sediments of the Southeast Atlantic generally increases from the ocean bed to the continental slope and shelf. In diatomaceous oozes of the Southwest Africa shelf, phosphorus concentration in fresh interstitial waters reaches 2.5 mg/l in absence of phosphorite concretions and 0.1-0.7 mg/l in their presence. After prolonged storage of samples concentration of dissolved mineral phosphorus sometimes increases up to 7-8 mg/l. The key factor regulating phosphorus content of solid and liquid phases of unaltered sediments are content and composition of organic matter.

(Table 2-3) Radiocarbon datings of organic matter from sediments of Core PSh-4510

Core PSh-2510 (4.76 m long) recovered mud and clay of the Baltic Ice Lake and of all subsequent stages of the Baltic Sea. Grain size, mineral and chemical compositions, as well as physical properties of sediments were studied. Biostratigraphic (diatoms and foraminifers), lithostratigraphic, and chemical (26 elements) methods, as well as radiocarbon datings were used to subdivide core sections into stratigraphic units.