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Carbono en el sue= lo de bosque secundario y pasturas=

Soil Carbon in secondary forest a= nd grass

¹	Raúl Armando Ramos Veintimilla	https://orcid.org/0000-0001-5181-1039
	Docente, Facultad de Recursos Naturales, Carrera Ingeniería Fores= tal, Escuela Superior Politécnica de Chimborazo (ESPOCH), Riobamba-Ecuador. raul.ramos@espoch.edu.ec
²	Roy Vera Vélez	https://orcid.org//0000-0002-4716-4390
	Departmen= t of Plant Sciences, University of Saskatchewan. 51 Campus Drive, Saskatoon, S= K. S7N 5A8-Canada roy.vera@usask.ca=
³	Jorge Eduardo Grijalva Olmedo	https://orcid.org/0000-0001-8301-531X
	Docente, Universidad Central del Ecuador. Quito-Ecuador jgrijalva@uce.edu.ec
⁴	Mario Rolando Ramos Veintimilla	https://orcid.org/0000-0003-2264-2808
	Investigador Instituto Nacional de Investigaciones Agropecuarias, INIAP, Ecuador. mario.ramos@iniap.gob.ec

<= o:p>	Artículo de Investigac= ión Científica y Tecnológica Enviado: 09/07/2022 Revisado: 24/08/2022 Aceptado: 05/09/2022 Publicado:16/09/2022 DOI: https://doi.org/10.33262/c= oncienciadigital.v5i3.2.2322

Cítese:		Ramos Veintimilla , R. = A., Vera Vélez, R., Grijalva Olmedo, J. E., & Ramos Veintimilla, M. R. (2022). Carbono en el suelo de bosque secundario y pasturas. ConcienciaDigital, 5(3.2), 91-106. https://d= oi.org/10.33262/concienciadigital.v5i3.2.2322
	&= nbsp;	CONCIENCIA DIGITAL, = es una revista multidisciplinar, trimestral, que se publicará en soporte electrónico tiene como misión contribuir a la formació= n de profesionales competentes con visión humanística y crítica que sean capac= es de exponer sus resultados investigativos y científicos en la misma medida= que se promueva mediante su intervención cambios positivos en la sociedad.&nb= sp;https://concienciadigital.org<= span style=3D'font-size:8.0pt;line-height:115%;mso-fareast-language:ES'> La rev= ista es editada por la Editorial Ciencia Digital (Editorial de prestigio registrada en la Cámara Ecuatoriana de Libro con No de Afiliación 663) www.celibro.org.ec<= /o:p>
	&= nbsp;	Esta revista está protegida bajo una licencia Creative Commons Attribution Non Commercial No Derivatives 4.0 International. Copia de la licencia: http:/= /creativecommons.org/licenses/by-nc-nd/4.0/
Palabras claves: Fraccionamiento del carbono orgánico, pasivo, lento, lábil, suelo, sumidero.		Resumen Introducción: El suelo contiene la mayor reserva de carbono orgánico de los ecosistemas terrestr= es y quizá es el recurso natural de mayor vulnerabilidad al cambio climático. = Objetivo: Determinar cómo influ= ye el cambio de uso de la tierra en el secuestro de carbono orgánico y su fraccionamiento en el suelo de bosque secundario y pasturas. Metodología: La investigación= se condujo en San Miguel de Barranca, Puntarenas, Costa Rica, a un rango altitudinal de 150 a 200 m.s.n.m. precipitación de 2043 mm ańo^{-1, relieve quebrado y fuertes pendientes (23-55%). Estudiamos pasturas mejor= adas más árboles (PmA), pasturas degradadas (Pd) y bosque secundario (Bs). En = cada repetición del sistema evaluado se hicieron nueve puntos de muestreo, tres calicatas (1x1x1 m) centrales en dirección a la pendiente y seis mini-calicatas (0.5x0.5x0.5 m) distribuidas equidistantemente a 20 m entre ellas. En laboratorio el fraccionamiento fue físico químico y se determin= ó en autoanalizador modelo Flash EA 1112. Resultados: El mayor valor de carbono orgánico almacenado en suelo, hasta 0,8 m de profundidad, presentó el sistema PmA (141,79 Mg ha^-1), seguido del Pd (133,22 Mg ha^-1) y= el menor valor registró el Bs (85,80 Mg ha^-1); de los cuales, los sistemas con pasturas presentaron el 68,2 % carbono pasivo y el 65% el bo= sque secundario. Discusión: La tendencia PmA > Pd > Bs probablemente se deba algún fenómeno biofís= ico, topográfico y acompańado de las fuertes precipitaciones pudo haber influenciado cíclicamente para que el carbono en el suelo de bosque secun= dario sea menor. Conclusiones: Entre 0 y 20 cm de profundidad del suelo, se encuentra el 50% del carbono orgánico total secuestrado, y en gran medida en la forma lábil por lo que probablemente = se libere debido a la deforestación o al cambio climático. Esto nos intuye en la necesidad de preservar las áreas bosc= osas y restaurar áreas degradadas.}
Keywords: Fractioning of organic carbon, passive, slow, labile, soil, carbon sink.		Abstract Introduction: = Soil contains the largest = reserve of organic carbon in terrestrial ecosystems, and it is the natural resour= ce with the greatest vulnerability to climate change. Objective= : To determine to what extent land use change influences carbon sequestration = and fractioning in secondary forests and pastures soil. Methodol= ogy: This study was conducted in San Miguel de Barranca, Puntarenas, Costa Rica. Elevation at this location range from 150 to 200 m.a.s.l., average annual rainfall of 2043 mm, and rough terrain with 23-55% steep slopes. We investigated three systems, mixed improved pastures with trees (PmA), degraded pastures (Pd), and secondary forest (Bs). Each replication had n= ine sampling points: three main trial pits (1x1x1m) across the slope and six mini-trial pits (0.5 x0.5 x0.5m) evenly spaced along a 20m transect. Laboratory analysis consisted of soil physical-chemical fractioning with a Flash EA 1112 autoanalyzer. Results: PmA system stored the highest value of organic carbon in the soil (141.79 Mg ha-1) u= p to 0.8 m deep, followed by Pd (133.22 Mg ha-1) and Bs (85.80 Mg ha-1). Pastu= re systems displayed 68.2% passive carbon and 65% in secondary forests. = ;Discussion: The carbon storage trend PmA > Pd > Bs is likely due to biophysical and topographical phenomena linked to heavy rainfall. Precipitation could have influenced the carbon cycle in the secondary forest floor to have the low= est value. Conclusions: 50% of the total organic carbon is stored between 0 and 20 cm deep in the soil and, to a considera= ble extent, in the labile form. Carbon is released due to deforestation or ecological anomalies associated with climate change. Our results show the need to preserve forested areas and restore degraded areas.

Introducción

A nivel mundial= y en América Latina, en particular, durante las últimas décadas la deforestac= ión, entendida como la transformación de tierras forestales para otros usos como: pastizales para ganadería y agricultura, origina los procesos de degradació= n y perdida del potencial de servicios ecosistémicos de los bosques (Alonso, 20= 22). Desde 1950 se estima que alrededor de 250 millones de hectáreas de bosque húmedo y su biodiversidad asociada se han perdido, y a escala global el val= or se incrementa a 420 millones de hectáreas (Organización de las Naciones Uni= das para la Alimentación [FAO], 2001; Programa de las Naciones Unidas para el M= edio Ambiente [PENUMA], 2020).

Los sistemas de producción ganadero que sobresalen en estas áreas están basados principalme= nte en pastizales, con una escasa integración de cultivos (FAO, 2001; Rocha, 20= 02; Ramos, 2003; Ramos et al., 2020). La sustentabilidad de estos sistemas ha s= ido amenazada por diversos factores como la degradación de los pastizales (liga= da al impacto en los suelos), la estacionalidad de la producción forrajera y l= as condiciones climáticas adversas. Las consecuencias inmediatas han sido la reducción de la productividad, el aumento de costos de producción y la degradación ambiental (FAO, 2001).

Varios investigadores, entre ellos: Steinfeld et al. (2009) y Hernánd= ez et al. (2020), manifiestan que la producción pecuaria es uno de los protagonistas de la problemática ambiental a nivel global. Sánchez et al. (= 2020), indican que a nivel mundial la producción de ca= rne y leche de bovino es responsable de la mayoría de las emisiones de Gases Efec= to Invernadero (GEI), pues contribuye con el 41 y el 29 %, respectivamente, de= las emisiones del sector, aportan gases efecto invernadero como el dióxi= do de carbono (CO₂), el metano (CH₄) y óxido nitroso (N<= sub>2O) a la atmósfera. El CO₂ es un gas de mucha importancia desde el p= unto de vista del calentamiento global, debido al volumen producido todos los ań= os, con un aumento en su concentración y por el tiempo de residencia en la atmósfera (Mora, 2001). El CO₂ es responsable del 50% del calentamiento global a través de la absorción de la radiación térmica emiti= da por la superficie de la tierra (Veldkamp, 1993; Lorenz & Lal, 2018).

Los bosques almacenan grandes cantidades de carbono tanto en la bioma= sa vegetal como en el suelo (De Oliveira et al., 2017). El mismo autor manifie= sta que el carbono del suelo debajo de los bosques tiene un papel importante en= el cambio global, lo que hace que la información sobre las formas y profundida= des de estas existencias sea de considerable interés en los esfuerzos para cuantificar las emisiones cuando la deforestación convierte estos bosques en pastizales u otros usos de la tierra.

En el suelo se encuentra la reserva de carbono orgánico terrestre más grande de la Tierra y es una fuente importante y sumidero de CO₂ atmosférico en la mitigación del efecto invernadero (Lehmann & Kleber, 2015). El carbono orgánico del suelo (COS) es un indicador clave para evalu= ar la calidad del suelo debido a sus propiedades fisicoquímicas, procesos biológicos y funciones ecológicas (Wu et al., 2022), y por su manejo inadec= uado es probablemente uno de los recursos naturales más vulnerables al cambio climático.

En los últimos ańos, avances conceptuales y metodológicos sugieren un concepto clave sobre= el carbono orgánico en el suelo, entre ellos Parton et al. (1987), indican que existen tipos o fracciones de carbono en el suelo con diferentes tasas de recambio (1,5 a más de 1000 ańos). Por su parte Meléndez (1997), indican que la dinámica del carbono en el suelo p= uede dividirse en tres fracciones: la fracción activa o carbono microbiano el cu= al representa entre 1-2% del carbono orgánico total (CO total), la fracción de carbono orgánico lento (CO lento) y el carbono orgánico pasivo (CO pasivo).=

Conocer la diná= mica de estas reservas es importante para evaluar el riesgo de liberación a la atmósfera que tiene el carbono en los escenarios climáticos proyectados. El carbono en fracciones lábiles es el más susceptible de liberarse si se expo= ne a estas perturbaciones, y es más probable que se libere carbono en cualquier forma ubicada cerca de la superficie del suelo que el carbono en capas más profundas (Ramos, 2003; De Oliveira et al., 2017).

En este contexto nuestra investigación pretendió determinar cómo influye el cambio de uso de= la tierra en el secuestro de carbono orgánico y su fraccionamiento en el suelo= de bosque secundario y pasturas en el trópico, información relevante para ayud= ar a entender mejor cómo la deforestación impacta el potencial que tiene el suelo como sumidero de carbono y promover estrategias para su manejo sostenible.<= span style=3D'mso-fareast-language:EN-US;mso-bidi-language:SI-LK;mso-bidi-font-w= eight: bold'>

Metodología

Esta investigac= ión se realizó en el sector San Miguel de Barranca perteneciente a la provincia Puntarenas, Costa Rica. Las fincas estudiadas se encuentran ubicadas a 10o 09` de latitud norte y Bosque Sub-húmedo Tropical (bh-T), el relieve = es quebrado con fuertes pendientes que se encuentran entre 23-55%.

Este estudio se realizó en un suelo Typic Rhodustalfs que pertenece al orden de los Alfisol= es (Mapa de suelos de Costa Rica). Los suelos en la zona son superficiales compactados, arcillosos y baja conductividad hidráulica (Camargo, 1999).

La precipitación media anual en la zona es de 2043 mm distribuida en dos épocas, lluviosa (mayo-noviembre) y seca (diciembre-abril). La temperatura promedio es de 27= .2 ^oC (Chinchilla, 1987).

El área de influencia del proyecto “Enfoques integrados silvopastoriles para el manejo= de ecosistemas” esta entre 0 y 600 m.s.n.m., las fincas en estudio se encuentr= an de 150 y 200 m.s.n.m, con topografía irregular y fuertes pendientes.

Metodológicamen= te la investigación ejecutada correspondió a: Diseńo experimental de tipo cuas= iexperimental y nivel de tratamientos múltiples, como se detalla a continuación: Los tratamientos estudiados fueron pasturas mejoradas más árboles (PmA), pastur= as degradadas (Pd) y bosque secundario (Bs).

Las pasturas mejoradas más árboles fueron apartos o potreros con Brachiaria brizantha de 3 ańos y varias especies leńosas disper= sas. Las pasturas degradadas fueron apartos que tenían como pasto principal jara= gua (Hyparrhenia rufa Stapf.) y var= ias gramíneas nativas, presentaron una población de árboles muy baja, además se observó un alto porcentaje de arvenses y de suelo descubierto. El bosque secundario en las tres fincas estudiadas está estimado en una edad entre 15= y 25 ańos (Ramos, 2003).

Se utilizó un diseńo Irrestricto al azar con parcelas divididas con muestreo, donde la parcela grande estaba conformada por el tipo de uso de la tierra y la parce= la pequeńa por la profundidad del suelo. Las repeticiones fueron cinco.

En cada repetic= ión del sistema de uso de la tierra evaluado se hicieron nueve puntos de muestr= eo, tres calicatas (hoyos de 1x1x1 m) que se ubicaron en la parte central del aparto distribuidas equidistantemente a 20 m entre ellas y en dirección a la pendiente del terreno y seis mini-calicatas (hoyos de 0.5x0.5x0.5 m) distribuidas en forma paralela a 20 m de distancia de las calicatas, igualm= ente en sentido de la pendiente, como se observa en la figura 1. En cada punto de muestreo y a tres profundidades de suelo 0-20 cm, 20,1-40 cm y 60-80 cm, se midieron las siguientes variables: densidad aparente, fertilidad, textura, biomasa de raíces finas y carbono orgánico, tema del presente artículo científico (Ramos, 2003).

Los datos obten= idos se analizaron con la ayuda de Statistical Analysis Systems para Wind= ows V8 (SAS V8). El nivel de significancia utilizado en las pruebas estadísticas realizadas fue 95% (p=3D0.05). Para comparar las medias de las variables se realizaron pruebas de rangos múltiples de Duncan.

Figura 1

Croquis de distri= bución de los puntos de muestreo de suelo en el campo, en fincas ganaderas de San Miguel de Barranca, Puntarenas-Costa Rica

Fuente: Ramos (2003)

En los nueve pu= ntos de muestreo con la ayuda de un barreno se tomaron muestras de suelo sin disturbar a tres profundidades (0-20, 20,1-40 y 60-80 cm), ubicando el cili= ndro muestreador en el tercio medio de cada profundidad en estudio, luego el sue= lo se pasó a una bolsa plástica bien etiquetada y se llevó al Laboratorio de Suelos del CATIE a realizar el respectivo procesamiento y análisis (Ramos, 2003).

En el laborator= io las muestras de suelo fresco fueron pasadas por un tamiz de 2 mm y se divid= ió en tres submuestras. En una submuestra se determinó la humedad, secando el suelo a una temperatura de 105 ^oC durante 24 horas en una estufa= de aire forzado. Otra submuestra fue secada al aire libre y se analizó carbono orgánico total por el analizador de carbono y nitrógeno, y en la tercera submuestra se realizó el fraccionamiento y análisis del carbón pasivo como = se explica en la figura 2 (Ramos, 2003).

Figura 2

Fraccionamiento d= el carbono orgánico de suelo basado en el tamańo de partículas, de muestras tomadas en fincas ganaderas de San Miguel de Barranca, Puntarenas-Costa Ric= a

Fuente: = Ramos (2003)

El fraccionamie= nto del carbono orgánico como se indica en la figura 2 se realizó combinando un método de dispersión química de suelo seguido de una separación física basa= da en el tamańo de partículas (Cambardella & Elliot, 1992).

De cada submues= tra se pesó 10 g de suelo fresco en tubos plásticos de agitación de 100 ml, lue= go se adicionó 30 ml de solución de hexametafosfato de sodio Na (PO_{3)₆
de concentración 5g L^-1 y se agitó durante 1 hora en un agitador
horizontal a una velocidad de 120 rPmA. Luego del periodo de agitación se p=
asó
la suspensión por un tamiz de 53 µm,
pasando todas las partículas del tubo al tamiz; utilizando una peseta y con
pequeńas alícuotas de agua se lavaron las partículas de suelo adheridas al =
tubo
y con una espátula de hule se desprendieron ligeramente los agregados que
quedaron encima del tamiz (Ramos, 2003).}

La fracción de arena más la macro materia orgánica retenida sobre el tamiz de >53 µm (carbón lento= ) y la fracción de materia orgánica <53 µm (carbón pasivo) asociada a limos y arcillas, fueron recolectados en vasos de precipitación pre-pesados, luego se puso a secar ambas fracciones a 50 şC h= asta obtener el peso seco. Cuando los vasos estaban secos se determinaron las cantidades de material en cada uno de ellos (Cambardella & Elliot, 1992= ). La fracción de suelo <53 µm fue morterizada, tamizada a 250 µm y finalmente se analizó el carbono orgánico total en un autoanalizador mode= lo Flash EA 1112. El funcionamiento de este equipo se basa en una oxidación completa de la muestra dentro de un reactor de alta temperatura (aproximadamente 1800°C), transformando la muestra en una mezcla de gases. = Los gases se separan a través de una columna cromatográfica la misma que está conectada a un detector de conductividad térmica (TERMO QUEST) (Ramos, 2003= ).

La población fue compuesta por fincas de productores ganaderos que manejan los sistemas de u= so de la tierra con al menos una de las tres formas de uso en estudio. La selección de las parcelas a evaluar se realizó considerando los siguientes criterios:

1. Que las fincas a evaluar se encuentren en un rango de altitud máximo de 100 m.

2. Que en las fincas se practique el mismo tipo= de explotación ganadera.

3. Que las parcelas a estudiar se encuentren en= un mismo orden de suelo.

4. Que las parcelas no hayan sufrido quemas dur= ante los últimos 15 ańos.

5. Que el manejo de la pastura en términos de especie, edad, fertilización, malezas, carga animal, tiempos de utilización= y recuperación de la pastura sean lo más parecidos posibles.

6. Que el bosque secundario (comparador) tenga = al menos 15 ańos.

La ubicación de las fincas se realizó con apoyo de información (base = de datos, mapas y fotografías aéreas 1:40000) disponible en el proyecto antes mencionado e información secundaria (mapa de clasificación).

Resultados y discusión =

La evaluación d= e CO total y CO pasivo se realizó a través de un análisis de varianza para un di= seńo de parcelas divididas con muestreo, donde la parcela grande fue el sistema = y la parcela pequeńa las profundidades. En este análisis se encontraron diferenc= ias estadísticas significativas (p< 0.0001) para sistemas de uso de la tierr= a y profundidades. No se encontró diferencias estadísticas para la interacción sistemas*profundidad, como se observa en la tabla 1.

Tabla 1

Análisis de varianza para carbono orgá= nico total (CO total) y carbono orgánico pasivo (CO pasivo) a tres profundidades= de suelo en tres sistemas de uso de la tierra

Fuentes de Variación<= /p>	gl	CO total	CO pasivo
Sistemas de uso del= suelo	2	11259,95	*=	4951,64	*=
Error a (R*S)<= /o:p>	12	2420,56		793,18
Profundidad	2	25289,38	**	6303,84	**
Tratamiento*Profund= idad	4	694,13	ns	133,24	ns
Error b. (RSP)&nb= sp;	24	620,76		255,39
Error de Muestreo	360	449,96		160,39
Total &n= bsp;	404

Nota: R= =3D Repetición; S=3D Sistema (PmA=3D Pastura mejorada, Pd=3D Pastura degradada,= Bs=3D Bosque secundario); P=3D Profundidad; *=3D Significativo (p˂0,05); **= =3D Altamente Significativo (p˂0,01); ns =3D No significativo (p˃0,05= )

La comparación múltiple de Duncan al 5% para sistemas de uso del suelo en la variable contenido de CO total, encontró que PmA (64.44 t ha^-1) y Pd (63.= 11 t ha^-1) fueron significativamente mayores que Bs (41.41 t ha^-=
1) en la profundidad superficial de suelo (0-20 cm). En la profundidad de 20,1= -40 cm, PmA superó un 15% a Pd y 49.15% a Bs. En la tercera profundidad 40,1-60 cm,= PmA superó 11% a Pd y 35% a Bs y finalmente en la cuarta profundidad (60,1-80 c= m) PmA fue 15% mayor que Pd, y 29.9% superior que Bs, como se muestra en la fi= gura 3a. La fracción CO pasivo presentó una tendencia similar, como se muestra e= n la figura 3b.

Figura 3

Promedios de CO t= otal y la fracción CO pasivo en suelo bajo pasturas mejoradas más árboles, pasturas degradadas y bosque secundario en fincas ganaderas de San Miguel de Barranc= a, Puntarenas-Costa Rica.

a. Promedio en sistemas de= uso de la tierra.

b. Fraccionamiento de carb= ono en suelo.<= /o:p>

Nota: Letras iguale= s en cada profundidad no difieren significativamente Duncan p<0.05=

La figura 4 mue= stra el CO lento y CO pasivo en los tres tipos de uso de la tierra y a las cuatro profundidades en estudio. Aquí se puede observar una relación directa entre= el contenido de CO pasivo y la profundidad de suelo, aunque no muy clara en Bs= . La baja tendencia en Bs puede estar dado por la posible erosión laminar que su= fre el suelo bajo este sistema, lo cual probablemente hizo que las muestras se hayan tomado a una profundidad mayor dentro del perfil y los cuatro puntos = de evaluación se encuentren en un mismo horizonte.

Figura 4

Fraccionamiento de carbono orgánico en cuatro profundidades de suelo, bajo pasturas mejoradas = más árboles (PmA), pasturas degradadas (Pd) y bosque secundario (Bs) en fincas ganaderas de San Miguel de Barranca, Puntarenas Costa Rica.<= /p>

La profundidad = 0-20 cm tiene una tendencia a contener un mayor porcentaje de CO lento en comparación a las tres profundidades restantes (20,1-40, 40,1-60 y 60,1-80 = cm), esto posiblemente se debe a una mayor cantidad de raíces, material vegetal = en descomposición y probablemente una mayor cantidad de arenas en la parte superficial del perfil, aunque un poco más acentuado en Pd que posiblemente al estar el sue= lo menos protegido hay una mayor acción de las variables climáticas lo que conlleva a una descomposición más rápida de la materia orgánica, como muest= ra la figura 4.

Discus= ión

En esta investigación se determinó t analizó únicamente la fracción de CO pasivo y = el CO total. Los datos de la fracción de carbono orgánico lento (CO lento) se estimaron por diferencia entre el CO total y el CO pasivo.

Las tendencias observadas en esta investigación sobre el carbono orgá= nico del suelo son parecidas a las reportadas por López et al. (1999) y Ruiz (20= 02), y superior en 30% el CO total en bosque secundario al reportado por Rojas-Solano et al. (2021), en estudios de suelo bajo sistemas silvopastoriles en Turrialba, Costa Rica. El comportamiento del CO total del suelo en las diferentes profundidades se relaciona con el comportamiento de biomasa de raíces finas; es decir, tiene= una tendencia a disminuir con el incremento en profundidad lo cual era de esper= arse ya que una de las principales entradas de carbono al suelo está dado por la constante muerte de raíces finas (MacDiken, 1997; FAO, 2018).

En la figura 3a= se observa también que en la profundidad de, suelo de 0-20 cm se encontró alrededor del 45% de carbono y en la profundidad de 20-80 cm se encontró alrededor del 55% del carbono secuestrado en el suelo. Estos datos muestran= que en un perfil de 0.8 m de profundidad, en estas condiciones bioclimáticas, aproximadamente el 60% de carbono secuestrado se encontró en una profundidad mayor a los 0.2 m, esta característica hace que éste carbono esté menos expuesto a procesos de oxidación y por tanto su perdida como gas efecto invernadero (Fisher et al., 1994; Rojas, 2021).

El sistema de P= mA presentó el mayor promedio de CO total almacenado en las tres profundidades= de suelo, aunque no difiere estadísticamente con Pd, pero sí con Bs. Estos promedios bajos, no esperados, de contenido de CO total en suelo de Bs puede estar dado por que las pendientes de los bosques secundarios en estudio fue= ron mayores (23-55%) que en PmA y Pd (28-30%), este factor combinado con las fuertes precipitaciones provoca arrastre del material orgánico depositado e= n el sistema como producto de la senescencia y muerte de órganos vegetales. Situación que no ocurre en PmA y Pd dado que una de las principales entrada= s de carbono al suelo es producido por el cambio permanente y de intensidad peri= ódica de raíces de los pastos y que directamente se quedan atrapadas en el suelo (MacDiken, 1997; Wiesmeier et al., 2019),<= /span> que indican que las características topogr= áficas desempeńan un papel importante para el almacenamiento de carbono en suelo.<= /span>

Es importante considerar también que los sistemas de bosque tienen la biomasa aérea como fuente principal de almacenamiento de carbono, además existe carbono almace= nado en la biomasa radicular que va mucho más allá de la profundidad que se está evaluando en este estudio, por lo cual es necesario realizar la comparación= en términos de sistema. Dixon et al. (1994), indican que la mitad del carbono almacenado por el sistema bosque se encuentra en la parte sobre el suelo. Por su parte Richter & Markewitz (2001), indican que encontraron en el Calhoun Forest, Carolina del Norte, un incremento de 165 t ha^-1 de carbono, donde el 65% se acumuló en = la biomasa y el 35% en la hojarasca, las raíces y el suelo.

Los porcentajes promedios de la fracción de CO pasivo encontrados en esta investigación fue= ron parecidos a los citados por Meléndez (1997), en su trabajo realizado en un Typic Humitropept de Turrialba-Costa Rica bajo diferentes sistemas de uso d= e la tierra. Esto se dio posiblemente porque la fracción mineral esta menos suje= ta a los cambios causados por el manejo debido a su complejidad química y/o a su protección física con las arcillas (Cambardella & Elliott, 1992; Melénd= ez, 1997; De Oliveira et al., 2017).

Es importante también indicar que las partículas con las cuales está ligado este tipo de carbono (arcilla y limo) principalmente la arcilla, tiene una relación dire= cta con la profundidad, en los suelos tropicales.

Conclu= siones

·&nb= sp;        El almacenamiento de carbono orgánico total en el suelo presentó la siguiente tendencia PmA > Pd > Bs. La baja diferenc= ia en almacenamiento de carbono entre los sistemas bajo pasturas, posiblemente= se debe a que las parcelas de PmA son muy jóvenes (3 ańos). Algún fenómeno bio= físico, topográfico y acompańado de las fuertes precipitaciones en la zona de estud= io pudo haber influenciado cíclicamente para que el carbono en el suelo de bos= que secundario haya experimentado dicha tendencia.

·&nb= sp;        La profundidad del suelo fue un factor determinant= e en el almacenamiento de carbono en el suelo. El patrón de comportamiento de es= ta variable fue inversamente proporcional con la profundidad, es decir la mayor cantidad de carbono (50 %) se encontró en la capa superficial (0-20cm), esto nos intuye en la necesidad de preservar las áreas boscosas, que el carbono = en suelo se encuentra mayormente en la parte superficial, en gran medida en la forma lábil por lo que probablemente se libere debido a la deforestación o = al cambio climático.

·&nb= sp;        El CO pasivo presentó una relación directamente proporcional con la profundidad de suelo, probablemente porque este tipo de carbono se encuentra en la parte mineral del suelo ligado a las partículas = de arcilla y limo.

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Conflicto de intereses<= /o:p>

Los autores declaran que no existe conflicto de intereses en relación= con el artículo presentado.

                                                                     =                                                                    <= /p>

El artículo qu= e se publica es de exclusiva responsabilidad de los autores y no necesariamente reflejan el pensamiento de la Revi= sta Conciencia Digital.

El artículo qu= eda en propiedad de la revista y, por tanto, su publicación parcial y/o total en o= tro medio tiene que ser autorizado por el director de la Revista Conciencia Digital.

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                                     Juegos Didácticos                Página 91 | 1<= /span>

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