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Propuesta de un esquema de aprovechamiento para la producción subordinada del Pinus maestrensis Bisse caso de estudio Colón, Guisa

Determination of the potential for sustain=
able use of the biomass of Pinus maestrensis Bisse as a su=
bordinate production of forestry exploitation case study Colón, Guisa<=
/o:p>
 

3D"Interfaz1

Alexey Rosabal Quintana

 

 

 <= /span>

Master en Gestión Ambiental, Facultad de Ciencias Agrícolas, Universidad de Gran= ma. Km 17 carretera Manzanillo

arosabalq@udg.co.cu <= /span>

= 2=

Yudemir Cruz Pérez

 

 

 <= /span>

Dr. en Ciencias Forestales, Universi= dad de la Habana. Correo electrónico cruzperezyudemir@gmail.com  

= 3=

Alberto Vidal Corona

 <= /span>

 

 

 <= /span>

Dr. en Ciencias Forestales UCTB Estación Experimental Agroforestal Camagüey, = Ave. Ignacio Agramonte # 178, Rpto. Los Coquitos, Camagüey

 vi= dal56@nauta.cu

4

Imilsi Virelles Espinosa<= /span>

Master en Educación Facultad de Ciencias Agrícolas, Universidad de Granma. Km 17 carretera Manzanillo

iverellese@udg.co.cu =

5

Dayana Rosabal González

Ingeniera forestal. Universidad de Granma. Km 17 carretera Manzanillo,

drosabalg@udg.co.cu

 

 <= /span>

Artículo de Investigación Científica y Tecnológica

Enviado: 05/10/2023=

Revisado: 17/11/2023

Aceptado: 09/12/2023

Publicado:05/01/2024

https://doi.org/10.33262/exploradordigi= tal.v8i1.2846         =         <= /o:p>

 

 

 =

 

Cítese= :

&= nbsp;

 

Rosabal Quintana, A., Cruz Pérez, Y., Vidal Corona, A., Virelles Espinosa, I., & Rosabal González, D. (2024). Propuesta de un esquema = de aprovechamiento para la producción subordinada del Pinus maestrensis Bisse caso de estudio Colón, Guisa. Explorador Digital, 8(1), 58-71. https://doi= .org/10.33262/exploradordigital.v8i1.2846

 

 

&= nbsp;

&= nbsp;

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Esta revista está protegida bajo una licencia Creative Commons en la = 4.0 International. Copia de la licencia: http://creativec= ommons.org/licenses/by-nc-nd/4.0/.=

 

Palabr= as claves: producción subordinada, surtidos, tocón

 =

 =

Resumen

El trabajo se desarrolló en la comunidad de “Colón” perteneciente al municipio Guisa, provincia Granma, con el objetivo de Proponer un esquema de aprovechamien= to para la producción subordinada del Pinus maestrensis Bisse. Que disminuirá las pérdidas de madera. Para ello se levantaron, parcelas rectangulares de (500m 2), que se distribuyeron de forma aleatoria. Fueron medidos 101 árboles de ellos fueron objeto de tala 41 árboles, a los que se les midieron los parámetros dasométricos, se determ= inó el volumen de madera dejada en el campo y su utilización como diferentes surtidos las perdidas por concepto de tocón y trozas dejadas en el campo = alcanzan un valor de 0,124m3 /ha y 11.06 m3 /ha respectivamente, de estos solo se aprovechó el fuste quedando en el campo madera que puede= ser aprovechada como cujes, bolitos de madera, postes y rolliza. Por lo que se hace necesario proyectar medidas preventivas mediante un programa o un control periódico

 =

 

Keywor= ds: subordinate production, assortments, stump

&= nbsp;

Abstract

The work was carried out in the community of &qu=
ot;Colón" belonging to the Guisa municipality, Granma province, with t=
he objective of Proposing a utilization scheme for the subordinate producti=
on of Pinus maestrensis Bisse. That will decrease wood losses. For this, re=
ctangular plots of (500m 2 ) were raised, which were distributed randomly. =
101 trees were measured, of which 41 trees were felled, to which the dasome=
tric parameters were measured, the volume of wood left in the field was det=
ermined and its use as different assortments, the losses due to stumps and =
logs left in the field. field reach a value of 0.124m3 /ha and 11.06 m3 /ha=
 respectively, of these only the stem was used, leaving wood in the field t=
hat can be used as cujes, wooden pellets, poles and logs. Therefore, it is =
necessary to project preventive measures through a program or periodic cont=
rol

&= nbsp;

 

 

Introducción

Los residuos forestales primarios, son los restos procedentes del aprovechamiento maderable de los bosques y de los tratamien= tos silvícolas que en ellos se practican, tales como: cortas, podas, desbroces, apertura de vías, acciones para prevención de incendios, cortas intermedias= , de saneamiento entre otras; estos residuos forestales pueden ir del orden del = 10 al 18% en especies de coníferas y de un 30 a 48% en especies de bosques tropicales (Carrillo et al., 2018).

Los residuos forestales son una fuente de dendroenergía que se pueden utilizar como leña, carbón vegetal, licor negro, metanol y aceite pirolítico. De acuerdo a la FAO, 2017 más de 2,000 millone= s de personas dependen de la dendroenergía para cocinar y/o calentarse, especialmente en los hogares de los países en desarrollo.

Según García, (2020) la utilización de esta fuente= de biomasa ofrece ventajas como: la emisión neutra de CO2 a la atmósfera durante su combustión, reducción de incendios forestales y la presencia de plagas forestales. Pese a las ventajas, que tiene el aprovechamiento de los residu= os forestales, aún existen inconvenientes como su elevada dispersión territori= al y su baja densidad energética, por lo cual, el conocimiento de su disponibili= dad resulta prioritario para determinar la viabilidad técnica económica de los proyectos que pretendan utilizarlos.

Para realizar un adecuado aprovechamiento se tiene= que tomar en cuenta variables como la cantidad de biomasa, distribución en fren= tes de corta y áreas con tratamientos silvícolas; sin dejar de lado los criteri= os de tipo técnico, ecológico y económico.

La extracción de los residuos forestales está condicionada a las características y la existencia de diversas variables, q= ue influyen de manera directa en la logística de extracción, costos económicos= e impactos ambientales, una de ellas es la cantidad de biomasa forestal, que = está relacionada con la superficie forestal y el tipo de vegetación presente (García, et al., 2021).

Ante el creciente interés sobre la utilización de = la biomasa de residuos provenientes del aprovechamiento forestal, es necesario realizar estudios que permitan conocer la disponibilidad, distribución, así como la factibilidad para la gestión de los mismos.

Brañas, (2020) es de la opinión que todas estas circunstancias han llevado a que, en las últimas décadas, el número e importancia de estudios sobre la producción de biomasa forestal haya crecid= o de forma continuada, hasta alcanzar cada vez más relevancia, y abarcar un gran número de especies y estructuras de masas diferentes. Bajo esta perspectiva= de posible aprovechamiento de fracciones de biomasa arbórea, se hace necesario aportar información que permita elaborar criterios de sostenibilidad de nuestras masas forestales, especialmente en lo que se refiere a especies de crecimiento rápido manejadas de forma intensiva. Por lo que el objetivo que llevo la presente investigación fue Proponer un esquema de aprovechamiento = para la producción subordinada del Pinus maestrensis Bisse

 

Materiales y métodos:

Caracterización del área de estudio

La comunidad de Colón se encuentra a 53 km de la cabecera municipal, en pleno corazón de la Sierra Maestra elevándose de 700= a 1200 metros sobre el nivel del mar, con terrenos irregulares su surgimiento data de mitad del siglo XIX, a partir de 1830, La misma se encuentra ubicada entre las coordenadas longitud: 76º 38´14´´ y latitud: 20º 8´7´´. Cubre tod= a la zona de la localidad de Colón.

Los bosques que más abundan son pinares de Pinus maestrensis Bisse y Pinus caribaea Morelet var. Caribaea Barret & Golfari y en una menor escala, bosques naturales compuestos por difer= entes especies, dentro de la categoría de bosque se destacan los productores.

Según la Ley 85 o Ley Forestal de Cuba, en el capí= tulo 15, los bosques de producción son aquellos cuya función principal es satisf= acer las necesidades de la economía nacional maderera y productos forestales no madereros, mediante su aprovechamiento y uso racional.

 Evalua= ción del área

Para la evaluación del área se realizó un análisis detallado de las características propias de la misma como su ubicación y características (suelo, relieve, clima), la superficie del área, la vegetac= ión existente, el volumen de madera a aprovechar. Se elaboró un mapa topográfic= o, del área a aprovechar, precisando los límites de la zona, los cursos de agu= a, los caminos existentes y otros detalles de interés con el software QGIS 3.2= 6.3

Estos resultados permitieron determinar la superfi= cie efectiva de tala, y la superficie no objeto de tala.

Determinación del tamaño de la muestra<= /span>

El tamaño de la muestra se calculó en función del error estándar  <= /p>

Donde:

n =3D número de muestras

t =3D se obtiene de la tabla de Student y su valor= de la magnitud de la muestra

E =3D error de muestreo

CV=3D coeficiente de variación

Como no se disponía de información relativa a la variabilidad de la población, mediante la varianza o en forma relativa a tr= avés del coeficiente de variación, se desarrolló un muestreo piloto. Una de las ventajas del coeficiente de variación, es que permite comparar la variabili= dad de poblaciones que tienen diferentes unidades de medida.<= /p>

Debido a que la plantación es homogénea en todo su aspecto (masa coetánea y mono especie) el tamaño de la muestra fue de 16 parcelas por rodal significativas para llevar a cabo la investigación.

Muestreo empleado

Para determinar los parámetros dasomètricos de los árboles que están dentro del rodal se aplicó un muestreo aleatorio simple; = en él, la muestra es tomada directamente de la población, de acuerdo a los requisitos de aleatoriedad. Después de talados los árboles y medido los parámetros dasomètricos se clasificaron los surtidos para determinar a part= ir de la producción preferente los usos de la producción subordinada para ello= se empleó la tabla de surtido del manual de trabajo Servicio Estatal Forestal = de Cuba

Tabla 1.

Tabla de surtido del manual de trabajo servicio estatal forestal

GRUPOS DE ESPECIES

SURTIDOS

LONGITUD

(m)

DIÁMETRO RABIZA (cm)

TIPO DE SURTIDO

Tod= as

Bol= os

1,8= o más

25 = y más

Gru= eso

Dur= as, Semiduras, Eucaliptos y pinos

Pos= tes

2,9= a 5,5 y más

14 = a 24

Med= io

Dur= as y Eucaliptos

Pos= tes servicio público

5,5= a 11,5

más= de 11,5

12 = a 32

Med= io Especial

Dur= as, coníferas

Tra= viesas

1,8= 3; 2,13; 2,44

11 = a 24

Med= io

Tod= as

Bol= itos

1 a= 4

8

Med= io

Dur= as y Semiduras

Rol= lizas uso directo

1,8= a 10,0 y más

5 a= 13

Fin= o

Dur= as y Semiduras

Pal= os tutores

0,9= a 1,3

3

Fin= o

Dur= as y Semiduras

Cuj= es

1,4= a 3,6 y más

3 a= 13

Fin= o

Table I. State Forest Service Workbook Assortment Table

 

En las áreas taladas se midieron todas las partes aprovechables de los árboles que quedaron en el campo y la altura de los tocones que fueran superior a un tercio del diámetro tomado a 1.30 metros a partir de esto se determinó las pérdidas en volumen de madera. <= /span>

CAPÍTULO III.- ANÁLISIS Y DISCUSIÓN DE LOS RESULTA= DOS

Evaluación del área

En el mapa topográfico Figura 1 elaborado con el software QGIS 3.26.3, del área a aprovechar, se precisan los límites de la zona, los cursos de agua, los caminos existentes y otros detalles de interé= s.

Figura 2. Mapa del área

Fuente: elaboración propia

Figure 2. Area map

Source: Own El= aboration

La toma de datos se realizó en tres rodales donde el número de árboles que se = midieron para la realización del estudio fueron 101, alcanzándose diversos resultados como el diámetro mínimo que posee un valor de 0,1cm y diámetro máximo 0,6m = aproximadamente, cuya altura varia de 8 m hasta 39 m los árboles se encuentran en la etapa de latizal (bajo) a fustal donde hay un crecimiento más acelerado en dependenc= ia de las características que posea cada especie. Estos resultados se expresan= en la tabla 2.  Valores semejantes en = cuanto a la dispersión de las alturas fueron encontrados por Perez-Miranda, (2022)=

 

Tabla 2.

 Análisis de los parámetros dasomètricos<= o:p>

Números de árboles  101

altura =

volumen

variables estadíst= icas

Diámetro promedio = (m)

0.350

altura mínima (m)<= o:p>

8

volumen m3/ha

168,01<= /span>

varianza (m)<= /o:p>

0.01

Diámetro mínimo(m)=

0.100

altura máxima (m)<= o:p>

39

volumen total de l= os rodales m3

521,22<= /span>

desviación estándar (m)

0.1

Diámetro máximo(m)=

0.650

altura promedio (m= )

26

 <= /span>

volumen del árbol medio m3

0,998

Correlación altura diámetro

0.72

Diámetro Weise(m)<= o:p>

0.390

altura Lorey  (m)

26

Fuente: elaboración propia.

Table 2. Analysis of dasometric parameters

Source: Own Elaboration.

Análisis de las pérdidas de madera por la altura d= el tocón

Según Dourojeanni (2021), el manejo forestal sostenible no estaría garantizado si se respetan las normas actuales por es= o y otros motivos es necesario proponer nuevas políticas que traigan un cambio progresivo, lo que implicaría cambios drásticos en la gestión forestal  que vayan encaminado a evitar pérdidas = en los procesos  productivos

La altura del tocón se debe de talar a un tercio del diámetro del árbol= a uno 1.30m diámetro a la al= tura del pecho (DAP), en árboles de pequeños diámetro= s, quedan no menos de 10 cm de altura del tocón. De un total de 41 árboles que fueron objetos de tala, las pérdidas ascendieron= a 0.12m 3, el análisis estadístico de los resultados de las pérdidas de madera se refleja en la tabla 3

Tabla 3:

Análisis estadístico de las pérdidas de madera

Análisis de las pérdidas de madera

Volumen dejado por tocón metros cúbicos

0.124

V en trozas dejado= en metros cúbicos

11.620

altura máxima cm <= o:p>

46.00

Troza mayor dejada= en metros

5.280

altura mínima cm <= o:p>

10.00

Troza menor dejada= 0

0.000

promedio altura cm=

24.44

promedio en metros=

2.700

 

 

Tabla 3:

Análisis estadístico de las pérdidas de madera (continuación)

Análisis de las pérdidas de madera

varianza

77.74

correlación entre = las alturas y diámetros

0.960

Desviación estánda= r

8.82

moda

25.00

Table 3: Statistical analysis of wood losses<= /o:p>

Source: Own Elaboration.

Miranda (2022) es del criterio que la abundancia de árbole= s de las categorías de menor tamaño (< de 9,9cm de DAP),  = presentan poca o mínima especies valiosas.

El total del volumen perdido en trozas dejadas en = el campo mencionado por Valdés, (2019) en el Norte de Bolivia es de 2,5m3= siendo este inferior al obtenido en la tabla, donde los volúmenes dejados e= n el campo por este concepto sobrepasan los 11m3.

Lo cual demuestra que para obtener una producción determinadas se talen más árboles. Moreno, (2021) es de la opinión que los<= span style=3D'mso-spacerun:yes'>   volúmenes de madera que se acumulan son materiales combustibles que pueden servir para propagar los incendios forestales.  

La troza mayor dejada en el sitio fue de 5,28m pudiendo emplearse en diferentes fines como postes, traviesas o rollizas us= o directo lo que demuestra la importancia de la reducción de las pérdidas en el aprovechamiento forestal.

Análisis de las pérdidas de madera dejada en la ra= biza

La rabiza es la parte del árbol que queda, una vez= que ha sido cubicado y aprovechado los volúmenes de surtido de los árboles y que generalmente, en la planta, es la que en realidad asume esta categoría, est= á en dependencia del diámetro que presente el mismo.

Esta porción del árbol, rara vez (en nuestras cond= iciones), es empleada desde el punto de vista industrial. Aunque, son conocidos los u= sos que pueden tener estas porciones, sobre todo para producciones industriales= de poco diámetro y longitud.

Pero, la utilidad que generalmente se le da a la rabiza, es para la producción de leña y carbón, dos renglones que ocupan un importante peso dentro de la economía.

Clasificar los surtidos totales de la biomasa producida en la cosecha

En este estudio los surtidos de la especie de P= inus maestrensis Bisse quedan en el campo en forma de rabiza, y partes del tronco, así como la masa foliar que pueden tener diferentes usos, el no aprovechamiento de estos esta dado en muchas ocasiones por el carro donde se transporta la madera solo admite una cantidad de la misma además de existir otras causas como la madera que es talada sobre lugares que dificulta su extracción, árboles dañado por el derribo de otros.

 En árbole= s de 35m se obtuvieron cinco trozas de seis metros quedando en el bosque cinco metros los cuales no fueron aprovechados dado a que la capacidad del carro = era inferior resultando que quedarán cinco metros pudiendo ser comercializado c= omo postes.

Otro surtido que quedo en el campo fueron los bolo= s o bolitos los mismos cuentan con una longitud de 1 a 4m clasificándose como u= n surtido medio, estos bolos que se pierden podrían ser aprovechados y darle diferent= es usos como leña a la hora de cocinar, sin necesidad de tener que talar pinos innecesariamente y solo usar la madera en bolo que se pierde en el campo.

La rolliza, se pierde en el campo ya que no se cue= nta con un camión especializado para el traslado de esta, esté surtido se clasi= fica como un surtido fino y comienza a utilizarse cuando el diámetro es superior= a los 5 cm y su longitud superior a 1,8 m.

 Este tipo= de surtido es poco aprovechado en nuestro país debido a que los campesinos no tienen las costumbres de recolectar estas partes de los árboles después de = la tala. Teniendo importantes y diferentes formas de emplearse, en la figura 3= se puede observar estructuras para cubiertas, estructuras para techos, techos = de madera, pórticos para pérgolas de madera, quioscos en madera, cerchas en madera, sus uniones son generalmente con elementos metálicos como varillas roscadas, tirafondos y tornillos especializados.

Figura 3.

Usos de la madera rolliza y cujes=

El surtido de cujes es afectado de manera continua= ya que el mismo cuenta con una longitud de 1,4 a 3,6m para su uso, este es un = tipo de surtido que se clasifica como fino el cuál  se desperdicia y se pierde, sin embargo se le puede dar un uso principalmente en edificaciones, techos, jaulas, carpintería menor

Valoración económica en función de los surtidos

Los análisis económicos han tendido a ignorar los costos ambientales y la disminución de los recursos naturales. La justifica= ción económica de la diversidad biológica puede jugar un papel primordial en los debates sobre el uso de los recursos naturales. Los beneficios económicos q= ue obtiene la humanidad de la biodiversidad son difíciles de valorar, una de l= as metas de la economía ecológica es desarrollar métodos de valoración de los componentes de la diversidad biológica.

En este estudio de pérdida de madera de la especie= de Pinus maestrensis Bisse se obtuvieron datos los cuales se reflejan en la tabl= a 4. Valores económicos perdidos en madera no aprovechada.

Tabla 4.

Valores económicos perdidos en madera = no aprovechada

Volumen Perdido de=

volumen=

árboles=

Pérdida=

madera<= /span>

promedio

Volumen por

económica ($)=

de los 41

hectárea (m 3 /ha)=

Volumen de cujes n= o

0.173

0.692

307.48

aprovechado

volumen de bolitos= no

0.222

0.888

100.34

aprovechado

volumen de postes = no

1.681

6.724

492.87

aprovechado

volumen de madera rolliza

0.62

2.48

1463.72

no aprovechado

Table 4. Economic values ​​lost in woo= d

Source: Own Elaboration.

Diseño del esquema

Para el caso de estos lugares que cuentan con una excesiva pendiente donde existe la presencia de suelos frágiles y bosques tropicales con abundantes especies, se propone evitar en estas áreas de tal= as la hermeticidad de equipos de combustibles o equipos de diésel y trabajar solamente con el tractor Dt-429, ya que tiene como beneficio la eliminación= de la carga manual, su poca compactación del suelo y la facilidad de extraer grandes trozas a largas distancia.

En la figura 4 se observa la realización del proce= so de corta de árboles, donde se emplean operaciones como la tala, extracción, desrame, troceado, apilado y carga. Para ser iniciado este, se plantea que = los árboles deben ser talados de un modo seguro, cayendo en la dirección correc= ta, esto evita que el tronco sea dañado más de lo necesario.<= /p>

 

Figura 4

Variante Tecnológica mediante el diagr= ama de OTIDA

Todo esto se somete a la operación de carga, donde= es llevada desde los acopiaderos superiores hasta los intermedios en los cuale= s se puede realizar algún tipo de tratamiento a la madera para después comercializarla o para ser transportada a los centros de consumo, en estos acopiaderos es de suma importancia llevar a cabo una correcta SST (Segurida= d y salud en el trabajo) debido a la cantidad de riesgos a los que se someten l= os trabajadores en estas operaciones

Se debe de llevar a cabo un procedimiento para la identificación, evaluación y control de riesgos. identificando las situacio= nes peligrosas las cuales se ubican principalmente en el acopiaderos donde se encuentren las operaciones de alto riesgo como son la extracción, desrame, troceado y apilado en las mismas se ven riesgos a la hora de desramar un pi= no o trocearlo por lo que hay que tener  cuidado con la motosierra, hacha o cualquier medio de cortar utilizado, además a la hora de apilar la madera es necesario usar todos los medio de protección co= mo guantes, cascos, botas de gomas, overoles y gafas o caretas esto va a evitar que ocu= rran accidentes o algún trabajador salga gravemente lastimado en todos los proce= sos.

Si se logran evaluar todos estos riesgos cuantitativamente mediante mediciones o análisis se va a lograr disminuir múltiples consecuencias por lo que hace necesario proyectar medidas prevent= ivas mediante un programa o un control periódico.

Kometter, (2019) opina que un a<= /span>náli= sis de las prácticas de aprovechamiento son la base para lograr u= n mane= jo sostenible del recurso en las concesiones forestales y son el fundamen= to para evitar accidentes y aumentar la rentabilidad empresarial

 

Conclusiones

·&nb= sp;        De un total de 101 árboles que fueron inventariados en el área de estudio se talaron 41, de los cuales no se aprovechan cujes, bolitos de madera, postes y rolliza todo est= o es dejado en el campo lo que provoca pérdidas económicas

·&nb= sp;        El esquema que se pro= pone agrupa las operaciones de troceo, desrame, apilado y caga en el acopiadero = para agrupar los surtidos y evitar las pérdidas de madera 

Conflicto de intereses

Los autores deben declarar si existe o no conflict= o de intereses en relación con el artículo presentado.

Bibliografía

BRAÑAS, J.; GONZÁLEZ-RÍO, F.; MERINO, A. Contenido y distribución de nutrientes en plantaciones de Eucalytus globulus del Noroeste de la Península Ibér= ica. Investigaciones. Agraria, 2020, (9): 316-335.

Carrillo-Ávila, N., Fuentes-López, M. E., Aguilar-Sánchez., P., Flores-Velázquez, R., Ordóñez-Prado, C., Buendía-Rodríguez, E. Uso de los residuos forestales en = la producción de bioenergía. Instituto Nacional de Investigaciones Forestales, Agrícolas y Pecuarias. Campo Experimental San Martinito Tlahuapan, Puebla. = 2018.  30 p.

FAO. Dendroenergía. Disponible  [Consult= ada el19 de octubre de 2017,] en:http://www.fao.org/forestry/energy/es/http://w= ww.fao.org/forestry/energy/ es/..

García, A., García, D., Pascual, J., De la Riva., Pérez, C. F., Montorio, R. Determinación de zonas adecuadas para laextracción de biomasa residual fore= stal en la provincia de Teruel mediante SIG y teledetección, Revista GeoFocus= (Artículos), 2021, No. 11. ISSN: 1578-5157. España. pp. 19-50

Moreno Ruiz, Juan Pablo. Adaptación de la evaluación de la peligrosidad a los flujos de escombros en zonas forestales incendiadas: incendios forestales de Robledo de Chavela (2 y 29/08/2020) y, en el sitio pronóstico Valle de Lozo= ya, Comunidad de Madrid.Tesis en opción de Master en Ingeniería Geológica. = 2021

Rodríguez García Encarna. Biomasa, Biocombustibles y Sostenibilidad. In c. T. A. y. A. ITAGRA.CT (Ed.) 2020, pp. 216.

Valdés. Madera residual en un bosque aprovechado en el Norte de Bolivia. Evaluac= ión de 6 especies. Tesis de Maestría. 2019

Dourojeanni, M. J.; Malleux, J.; Sabogal, C.; Lombardi, I.; Tarazona, R.; Rincón, C.: Helmut, S. & Barriga, C. A. (2021). Fundamentos de una nueva política forestal par= a el Perú. Revista Fore= stal del Perú, 36(2), 118-17 Univ. Nac. Agraria La Molina  http://dx.doi.org/10.21704/rfp.v36i2.1796

Caballero Miranda, Melina Lisbet. Análisis Estadístico Del Aprovechamiento Forestal E= n La Estructura Y Composición Florística Del Bosque Productivo De La Comunidad Nativa Chamiriari, Perú Revista Investigacion Operacional Vol. 43 , = NO. 1, 120-129, 2022

Kometter R. Análisis de las prácticas de manejo y la sostenibilidad del recurso en las concesiones forestales con fines maderables. Proyecto: USAID – US FOREST. 80 pp . = 2019

Pérez-Miranda et al, Ramiro. Análisis de contingencia de la distribución natural de pinos mexicanos en categoría de riesgo. Terra Latinoamericana, vol. 40, , 2022, Enero-Diciembre.ISSN: 2395-8030

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El artículo que se publica es de exclusiva responsabilidad de los autores y no necesariamente reflejan el pensamiento = de la Revista Explorador Digital.

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El artículo queda en propiedad de la revista y, por tanto, su publicación parcial y/o total en otro medio tiene que ser autoriz= ado por el director de la Revista Expl= orador Digital.

 

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