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Evaluación de la densidad y manejo forestal del piptocoma discolor (Pigüe) y= otras especies en la provincia de Pastaza – Ecuador

Density assessment and for= est management of piptocoma discolor (Pigüe) and other species in the province = of Pastaza – Ecuador

^{Erika Clara Casco G.}

https://orcid.org/0000-0002-6603-6837

^{Corporación de Desarrollo Integral Rashellbella (CORDEIR). Bolívar,
Ecuador claracasco369@gmail.co=
m}

^{Juan Elías González              =

                             https://orcid.org/0000-0002-0674-7741}

Universidad Estatal Amazónica, Pastaza, Ecuador =

jgonzalez@uea.edu.ec <= o:p>

^{Rubén Darío Ledesma <=
/span>https://orcid.org/0000-0002-2086-0185}

Privado, Pastaza, Ecuador =

lard0385@gmail.com =

^{Billy Coronel Espinoza https://orcid.org/0000-0003-2389-5751}

Universidad Estatal Amazónica, Pastaza, Ecuador =

bcoronel@uea.edu.ec

^{Luis Enrique Guerrero Naranjo https://o=
rcid.org/0000-0003-4745-4483}

Universidad Estatal Amazónica, Pastaza, Ecuador =

luenguna21@gmail.com <= o:p>

^{Santiago Homero Cuichan P http=
s://orcid.org/0000-0003-0572-9880}

Privado, Sucumbíos, Ecuador =

sant_pau84@hotmail.com

<= /span>

<= /span>	Artículo de Investigación Científica y Tecnológica Enviado: 08/07/2022= Revisado: 23/08/2022 Aceptado: 01/09/2022 Publicado:16/09/2022 DOI: https://doi.org/10.33262/c= oncienciadigital.v5i3.2.2321 <= /span>
	=
Cítese= :	&= nbsp;	= Casco G, E. C., González= , J. E., Ledesma, R. D., Espinoza, B. C., Guerrero Naranjo, L. E., & Cuichan P., S. H. (2022). Evaluación de la densidad y manejo forestal del piptocoma discolor (Pigüe) y otras especies en la provincia de Pastaza – Ecuador. ConcienciaDigital, 5(3.2), 67-90. https://d= oi.org/10.33262/concienciadigital.v5i3.2.2321 =
<= /o:p>		*CONCIE= NCIA DIGITAL,* es una revista multidisciplinar, trimestral, que se publicará en soporte electrónico tiene como misión contribuir a la formación de profesionales competentes con visión humanística y crítica q= ue sean capaces de exponer sus resultados investigativos y científicos en la misma medida que se promueva mediante su intervención cambios positivos e= n la sociedad. https://concienci= adigital.org <= /span> 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.e= c
<= /o:p>		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:Bosque secundario; condición, crecimiento; sostenibilidad ambiental.<= o:p>		Resumen Introducción: la política mundial y nacional consider= a la clave de la conservación de especies, para las sinergias de los ecosistem= as naturales, con la importancia de mantener el equilibrio frente a las actividades del hombre como los recursos sostenibles y sustentable del ecosistema. Objetivo: evaluar la densidad y el manejo forestal del manejo de las especies del piptocoma discolor (Pigüe) y otras especi= es en la provincia de Pastaza – Ecuador. Metodología: el estudio se llevó a cabo en los cantones: Pastaza, Mera, Santa Clara y Arajuno de la Provincia de Pastaza. Consider= ando las condiciones de altitud de cada cantón, mediante la aplicación de un muestreo al azar en 48 propiedades de un área de 10.400 m² del bosque secundario se logrando un análisis estadístico como Resultados:= las relaciones entre las categorías del fuste con 54,94 %, con un coeficiente= de variabilidad de 7,13 %, con probabilidad del 0,01 %, una confiabilidad del 99% y con una prueba de Tukey al 0,01 %. Se determinó el potencial actual= de las siguientes especies: Piptoco= ma discolor, Cecropia peltata L., Inga edulis Mart, Jacaranda mimosifolia D. Don., Miconia = Ruiz & Pav., Myrica pubescens Humb. & Bonpl. ex Willd., Piptocoma Cass, Ocotea Aub= l., Vismia baccifera L. Triana & Planch., Joosia umbellifera H. Karst= . Conclusione= s: según la evaluación el 70% del bosque no cuenta con un manejo forestal, y en el= 30% se evidencia aclareos de manera rudimentaria, debido a la ausencia de man= ejo técnico forestal existe el desequilibrio de la biodiversidad en la Amazon= ía del Ecuador.
Keywords: secondary forest; condition, growth; environmental sustainability		Abstract Introduction: the world and national policy consider= the key to the conservation of species, for the synergies of natural ecosyste= ms, with the importance of maintaining the balance against the activities of = man as sustainable and sustainable resources of the ecosystem. Goal. Evaluate= the density and forest management of the species of Piptocoma discolor (Pigüe) and other species in the province of Pastaza - Ecuador. Methodology: the study was conducted in the cantons: Pastaza, Mera, Santa Clara and Arajun= o of the Province of Pastaza. Considering the altitude conditions of each cant= on, through the application of a random sampling in forty-eight properties of= an area of 10,400 m2 of secondary forest, a statistical analys= is was achieved as Results: the relationships between the categories = of the stem with 54.94%, with a variability coefficient of 7.13%, with a probability of 0.01%, a reliability of 99% and with a Tukey test at 0.01%. The current potential of the following species was determined: Piptocoma discolor, Cecropia peltata L., Inga edulis Mart, Jacaranda mimosifolia D. Don., Miconia Ruiz & Pav., Myrica pubescens Humb. & Bonpl. ex Willd., Piptocoma Cass, Ocotea Aubl., Vismia baccifera L. Triana & Planch., Joosia umbellifer= a H. Karst. Conclus= ions: according to the evaluation, 70% of the forest does not have forest management, and in 30% there is evidence of rudimentary thinning, due to the absence of technical forest management, there is an imbalance of biodiversity in the Ecuadorian Amazon=

&n= bsp;

Introdu= cción

La política a nivel mundial busca la conservación, producción, ordenación, cultivo, manejo y aprovechamiento de = los ecosistemas forestales. Ecuador considera que el medio ambiente y los recur= sos naturales son patrimonio natural de gran importancia económica y social del país. Un elemento clave para favorecer el manejo forestal, es conocer las compensaciones, sinergias y relaciones de los servicios ecosistémicos gener= ados por los bosques (González et al., 2015). El uso de las maderas convencionales y no convencionales permite a las personas con bajos recursos ingresos para mejo= rar sus estilos de vida, la biomasa forestal, se puede convertir en productos y subproductos de valor agregado. Es importante buscar un equilibrio en la naturaleza y las actividades del hombre frente a los recursos forestales pa= ra su aprovechamiento.

La Amazonía ecuatoriana tiene una diversidad forestal importante para el desarrollo de la sociedad. En la provincia de Pas= taza, Piptocoma discolor (pigüe), se con= sidera como una especie nativa de la zona, su crecimiento es rápido, frente a las otras especies. La mayor densidad de estos árboles, se presenta en los claros del bosque secundario, crecen de= sde una altitud de los 500 hasta los 1500 m s. n. m., en una temperatura media = de 18°C y 25°C (Garrido et al., 2013). La dispersión de semillas es natural de forma anemócora, es decir por el viento, gracias a las escamas florales típ= icas de la familia Asterácea, el contenido de semillas por kilogramo son aproximadamente de 3 571 428 a 3 731 343 (Merino, 2010), y su germinación presenta un promedio del 95% en forma natural, muestra una supervivencia de 95,8% al ser trasplantad= as, en estudios previos de la sobrevivencia de las plántulas, a los 2,5 ańos su altura se aproxima a los 3.21 m, con un diámetro de 7.2 cm, descrito por Aguirre et al. (2019). El conocimiento del manejo forestal de e= sta especie es limitado, permitiendo la deforestación de los bosques para subsistir, según estas características se puede llegar a la conservación, sostenibilidad y aprovechamiento.

Mediante la estima= ción de la densidad en los bosques de especies nativas endémicas y su distribuci= ón geográfica se evalúa los términos diamétricos de crecimiento relativo y acumulado, de especies forestales dominantes y asociadas, dando a conocer que los ecosist= emas amazónicos y la diversidad biológica forestal es extraordinaria, pues conti= enen bienes y servicios como provisiones que deben ser conservadas para el futur= o de la sociedad, en los pueblos indígenas de la región la naturaleza es sagrada pues provee de vivienda, medicina y complacencia. Es transcendental conocer= las especies arbóreas con una tasa de natalidad alta, de crecimiento rápido de estas especies nativas de cada región para mantener un equilibrio ecológico= que permita un desarrollo económico social, la evaluación de la densidad en los puntos de muestreo en la provincia indica que la especie Piptocoma disco= lor, posee estas características de recuperación en un bosque intervenido en corto plazo (González et al., 2015).

En la región andina del Ecuador existen especies forestales de sucesión natural bajo plantaciones como P. radiata D. Don, P. patula Schlect. = et Cham. y Eucalyptus globulus Labill (Aguirre et al., ADDIN ZOTERO_ITEM CSL_CITATION {"ci= tationID":"smkwK6aj","properties":{"formatted= Citation":"(2019)","plainCitation":"(2019)&qu= ot;,"dontUpdate":true,"noteIndex":0},"citationItem= s":[{"id":84,"uris":["http://zotero.org/users= /local/eLIiInmM/items/L6TAELDD"],"uri":["http://zotero.= org/users/local/eLIiInmM/items/L6TAELDD"],"itemData":{"= id":84,"type":"article-journal","container-ti= tle":"Arnaldoa","DOI":"10.22497/arnaldoa.263.= 26306","ISSN":"2413-3299","issue":"= 3","note":"publisher: Universidad Privada Antenor Orrego","page":"943-964","source":"= SciELO","title":"Sucesión natural bajo plantaciones de Pinus radiata D. Don (Pinaceae) y Eucalyptus globulus Labill. (Myrtaceae), en el sur del Ecuador","volume":"26","author":[{"= family":"Aguirre Mendoza","given":"Zhofre"},{"family":&qu= ot;Díaz Ordońez","given":"Elvis"},{"family":&quo= t;Muńoz Chamba","given":"Johana"},{"family":&quo= t;Muńoz Chamba","given":"Luis"}],"issued":{"= ;date-parts":[["2019",9]]}},"suppress-author":true= }],"schema":"https://github.com/citation-style-language/sche= ma/raw/master/csl-citation.json"} 2019). En zonas de la provincia de Cotopaxi, mediante la aplicación de un manejo forestal adecuado, existen grandes extensiones de árboles que proporciona servicios ecosistémicos importantes = como la regulación, estabilidad e incluso mejoras en los caudales de agua además= de brindar trabajo a las personas locales (Natalini et al., 2016). Dentro del estudio, el objetivo fue eval= uar a la especie Piptocoma discolor (pigüe), especies asociadas de baja densidad arbórea del bosque secundario en manejo y calidad actual forestal, reactivando, conservando y regulando los servicios ecosistémicos, aprovecha= ndo el potencial de biomasa forestal debido a su importante uso energético para= la Amazonía ecuatoriana.

Metodología

El estudio se llevó a cabo en la provincia de Past= aza, en los cantones Pastaza, Mera, Arajuno y Santa Clara; para una mejor visualización a continuación en la figura 1, se detalla la ubicación de las fincas y cada una de las muestras donde se realizó aplicando la guía las instalaciones y evaluaciones de parcelas permanentes (PMP), de acuerdo a la Norma Técnica 248/98, tal como menciona (Acosta et al., 2014), donde se levantaron los datos de campo según los puntos celestes son bosque protectores o primarios.

<= /span>

Figura 1

Ubicación de las parcelas = en la provincia Pastaza

La investigación experimental se realizó en difere= ntes fincas de la provincia de Pastaza, de la parroquia Canelos, sector Cruz Lom= a, Cantón Mera, sector Pindo Mirador, Cantón Santa Clara, sector Comunidad Rey= de Oriente y, Cantón Arajuno, sector Nushino Ishpingo de la Provincia de Pasta= za, en el ańo 2016, las áreas mencionadas son las de mayor aprovechamiento de l= as especies en la parroquia de Canelos y Cantón Arajuno donde se establecieron= las parcelas de los finqueros donde se evaluaron mediante un cronograma de actividades, tal como se muestra en la tabla 1.

Tabla 1

Fincas y parcelas del área= de estudio de los cantones de la provincia

=	Cantón=	Fincas/Prov.<= /span>	Parcelas	Área (m˛)	%
1	Pastaza	8	20	20000,00	44,44<= /p>
2	Mera	2	6	6000,00	13,33<= /p>
3	Arajuno	2	7	7000,00	15,56<= /p>
4	Santa Clara	4	12	12000,00	26,67<= /p>
Total	16	45	45000,00	100,00=

Se identificaron un total de 16 fincas distribuidas en los 4 cantone= s de la provincia de Pastaza, distribuidas en 13 fincas se logró hacer 3 parcela= s y en las otras 3 fincas fueron 2 parcelas dando un total de 45 parcelas de evaluación, sumando un total de 45 000 m˛ lo que equivale a 4,5 ha; del tot= al del área muestreada el 44,44% corresponde al cantón Pastaza, seguido del ca= ntón Santa Clara con el 26,67% y por último se ubican los cantones Arajuno y Mera con 15,56 y 13,33% respectivamente. y se realizaron 290 encuestas del manejo forestal de las especies de acuerdo con el tamańo de la población 83 933 habitantes con una precisión del 17%, según la fórmula para muestras pequeńas al azar. Las variables dasométricas consideradas para el inventario de las medidas son: longitud d= el árbol, diámetro del tronco de la base y fuste, la intensidad del muestreo y= la relación de la superficie de la muestra, que se encuentran establecidas en = la tabla 2.

Tabla 1=

Intensidad de mues= tro y número de parcelas por hectárea

Estrato o plantación por ha según DAP (cm)	Muestreo (% área total)	N° de parcelas por ha
6,1 a 10	1,5	0,37 =3D 1 c= ada 3 ha
10,1 a 20	1<= /o:p>	0,25 =3D 1 cada 4 ha
20,1 a 50	0,75	0,19 =3D 1 c= ada 5.5 ha
>50	0,5	0,12 =3D 1 cada 8 ha

Fuente: Pinelo (2016)

A continuación, se= presenta los datos esquematizados en la figura 2.

Figura 2

Distribución de ha muestreadas por cantón

Los criterios técn= icos para la identificación y recolección de datos primarios, fueron mediante reuniones con productores y socios de la madera del (Pigüe), de la provinci= a de Pastaza, utilizando instrumentos, equipo técnico como funcionarios del MAE = y la UEA, para determinar la densidad forestal y evaluar la calidad del bosque mediante encuestas sobre el manejo forestal, de la cobertura vegetal con fo= rmaciones pioneras de (Pigüe) y otras especies; fueron de forma in situ (fincas) segú= n el tamańo de la muestra definida para la biomasa forestal.

Aplicaciones de las encuestas a finqueros

Se determino media= nte acercamientos a los propietarios con metodología participativa y la recopilación de datos, mediante encuestas a cada uno de los finqueros elabo= rada con anterioridad relacionados al campo de estudio: Este instrumento, permit= ió obtener la información para conocer el estado del bosque mediante parcelas = circulares de cada sitio (Tamayo et al., 2020).

Establecimiento de parcelas circulares

Las parcelas circulares fueron como unidad de evaluación para cada una de las especies presentes en ella, fue la estimación del diámetro (1.30 m del suelo) y a una altura comercial de cada uno de los individuos. Los materiales utilizados fueron cinta métrica y la forcípula métrica, para instalar las parcelas circulares tomando como centro un radio de 17,85 cm en cruz esto fue en terrenos planos, donde identificaron 4 cuadrantes. La estimación del DAP de cada uno de los individuos, fueron evaluados con parámetros dasométricos lo= que permitió el levantamiento de la información del bosque nativo secundario de= la Provincia de Pastaza.

El estudio experimental, se realizó usando criterios de diámetros de la base y fuste d= el árbol, a la misma altura de la base de 1.30 m y otros, con igual similitud presentado (González et al., 2019). Con la siguiente categorización estudiados y con características morfológicas semejantes (Escoto et al., 2017).

Densidad arbórea de las especies del bosque secundario

Se realizó emplean= do los métodos alométricos con tala asistida y criterios diamétricos, identificando 48 árboles en los cuatro cantones según la categorización de = los diámetros (10 - 33 cm), mediante la visión ocular con técnicos, dentro de l= as parcelas establecidas, con características morfológicas semejantes de 5 cm = de amplitud, mediante la Norma Reglamento y Directrices de estilo TAPPI – cm-8= 5 de 1985, se obtuvo el peso completo del árbol expresado en Kg de biomasa fresc= a, y su producción se estimó de acuerdo a la metodología (Navarro et al., 2020). La determinación del volumen de biomasa = fue según promedios de altura y utilizando la siguiente ecuación volumétrica pa= ra conos truncados (Aristizábal, 2011). (Ecuación 1)

= (1)

Dónde:

=3D volumen del fuste (m³).

=3D radio mayor al cuadrado (m²)

<= /span> =3D radio menor al cuadrado (m²)

=3D Radio mayor por radio menor (m²)

=3D altura del fuste hasta = el diámetro superior aparente (m)

En base a los datos del inventario se validó la ecuación (1), de la simulación del árbol y el cálculo del potencial de biomasa fresca con el programa software Autodesk Inventor 2017.

Valoración de la calidad

Esta metodología f= ue según las patologías de los árboles que fueron valoradas la incidencia de s= us factores antrópicos de la condición climática, asignada a la comparación de= su dominio de la producción probada y con rango de calificaciones de 1 a 5 de = las cualidades del estado de los árboles, las variables experimentales cualitat= ivas de excelente 5, muy bueno 4, bueno 3, regular 2 y ninguno 1. Y las variable= s de calidad, posición sociológica (asociación con otras especies), bifurcación (número de ramas o brazos), reiteración (número de veces que se repiten las ramas), inclinación, rectitud del fuste, dańo mecánico, grosor de ramas, án= gulo de inserción de ramas, estados fitosanitarios, gambas y aletones, grano en espiral, madera libre de nudos y control de malezas para generar una información útil del Pigüe. Se midieron las variables cuantitativas: diámet= ro normal del fuste (DN, en cm); altura total (m); diámetro de copa (DC, en m), considerando dos diámetros; posición sociológica de copas. Además, se registraron datos de sitio: altitud (m) y exposición, pendiente (%) (García= et al., 2017). Las características del manejo o raleo de los árboles en el bosque, como la regeneración de las especies, su crecimiento y la relación entre todas las especies del bosque secundario, su condición de producción y destino del producto final lo que hace de interés para la aplicación industrial = (Food and Agricultura Organization of the United Nations [FAO], 2020).

Valoración de la tasa de crecimiento y raleo para la conservación

Fue basado en la información de la tasa de crecimiento de los estudios anteriores en el caso= de la producción de la especie Piptocoma discolor (Pigüe) (González et al., 2018).

Procesamiento de datos

La información recolectada en campo se realizó mediante la aplicación de GPS, analizando l= os datos mediante el Software como Word, Excel, Arcview Gis 3.2 y se procedió = a la tabulación e interpretación.

<= /span>

Resultados y discusión=

Densidad arbórea Piptocoma discolor (Pigüe) y otras especies

El estrato de la vegetación encontrados concuerda con la información del Ministerio del Ambi= ente en el ańo 2014, el área de estudio fue de 29 068 km²de los cuat= ro cantones de la provincia de Pastaza, se consideró desde una altitud de 550 a 960 m.s.n.m., humedad relativa del 80 y 90 %, temperatura de 22şC. En el estudio se determinó la abundancia del Pigüe y otras especies que correspon= de a 90 variedades forestales, tal como se puede observar en la siguiente tabla = 3.

Tabla 3=

Número de especies identificadas en la provincia de Pastaza<= /p>

Cód.	Nombre común	Nombre Científico	Familia	No ind.	%
1	pigüe	Piptocoma discolor.	Asteraceae	1322,0= 0	46,52<= /span>
2	guarumo	Cecropia peltata L.	Urticaceae	158,00	5,56
3	guabo	Inga edulis = Mart.	Fabaceae	129,00=	4,54
4	jacaranda	Jacaranda mimosifolia D.Don.	Bignoniaceae	111,00	3,91
5	colca	Miconia Ruiz & Pav.	Melastomatac= eae	90,00<= /span>	3,17
6	laurel	Myrica pubescens Humb. & Bonpl. ex Willd.	Myricaceae	78,00	2,74
7	pigüe de pan= tano	Piptocoma sp. Cass.<= /span>	Asteraceae	76,00<= /span>	2,67
8	canelo	Ocotea Aubl.	Lauraceae	65,00	2,29
9	achotillo	Vismia bacci= fera L. Triana & Planch.	Hypericaceae=	57,00<= /span>	2,01
10	intachi	Joosia umbellifera H. Karst.	Rubiaceae	54,00	1,90
11	roble blanco=	Quercus alba= L.	Fagaceae	47,00<= /span>	1,65
12	balsa blanca	Ochroma pyramidale Cav. ex Lam Urb.	Malvaceae	47,00	1,65
13	anona	Annona macroprophyllata Donn.Sm.	Annonaceae	46,00<= /span>	1,62
14	doncel	Otoba parvifolia Mgf. M.Gently.	Yristicaceae	44,00	1,55
15	guarango	Macrolobium acaciafolium Benth.=	Fabaceae	42,00<= /span>	1,48
16	uva	Pourouma cecropiifolia Mart.	Urticaceae	27,00	0,95
17	cedrillo	Trichilia sp= . P. Browne.	Meliaceae	27,00<= /span>	0,95

Tabla 3=

Número de especies identificadas en la provincia de Pastaza (continuación)

Cód.	Nombre común	Nombre Científico	Familia	No ind.<= /o:p>	%<= /o:p>
18	Calun	Hieronyma alchorneoides L.<= /o:p>	Phyllanthaceae	26,00<= /span>	0,91
19	higuerón	Ficus citrifolia Mill.	Moraceae	24,00	0,84
20	manzano=	Clethra L.	Clethraceae	22,00<= /span>	0,77
21	cuero de sapo	Guarea guidonia L. Sleumer.	Meliaceae	20,00	0,70
22	corcho<= /o:p>	Quercus humboldtii Bonpl.	Fagaceae	19,00<= /span>	0,67
23	sangre de drago	Croton lechleri Muell. Arg	Euphorbiaceae	17,00	0,60
24	avío	Micropholis = chrysophyllum L.	Sapotaceae <= o:p>	17,00<= /span>	0,60
25	caimito	Pouteria caimito caimito Ruiz & Pav. Radlk.	Sapotaceae	15,00	0,53
26	pata de vaca=	Bauhinia forficata Link.<= /o:p>	Fabaceae	15,00<= /span>	0,53
27	capulí	Vallea stipularis L.f.	Elaeocarpaceae	13,00	0,46
28	tamburo=	Vochysia spp= . Print.	Vochysiaceae=	12,00<= /span>	0,42
29	zapote	Quararibea cordata Bonpl.	Malvaceae	12,00	0,42
30	payas	Miconia pilgeriana Ule.	Melastomatac= eae	12,00<= /span>	0,42
31	matapalo	Ficus mutisii Dugand.	Moraceae	11,00	0,39
32	copal	Dacryodes olivifera Cuatrec.<= o:p>	Burceraceae<= o:p>	10,00<= /span>	0,35
33	palo prieto	Lysiloma divaricatum (Jacq.) J.F. Macbr.	Fabaceae	9,00	0,32
34	pumamaqui	Oreopanax ecuadorensis Seem.<= o:p>	Araliaceae	9,00	0,32
35	sapán	Clathrotropis brunnea Amshoff.	Fabaceae	9,00	0,32
36	sande	Brosimun uti= le Kunth.	Moraceae	9,00	0,32
37	tilo	Tilia platyphyllos Scop.	Malvaceae	8,00	0,28
38	carahuasca	Trema integerrima Beurl.	Ulmaceae	8,00	0,28
39	motilón	Hieronyma asperifolia Pax y K. Hoffm.	Euphorbiaceae	7,00	0,25
40	barbasquillo=	Lonchocarpus nicou Aubl. J. F= .	<= span style=3D'font-size:10.0pt;line-height:150%;mso-bidi-font-family:"Times Ne= w Roman"; mso-ansi-language:ES-EC;font-weight:normal;text-decoration:none;text-unde= rline: none'>Fabaceae	7,00	0,25

Tabla 3=

Número de especies identificadas en la provincia de Pastaza (continuación)

Cód.	Nombre común	Nombre Científico	Familia	No ind.<= /o:p>	%<= /o:p>
41	naranjillo	Citronella mucronata Ruiz et Pav= ón D. Don.	Cardio= pteridaceae	6,00	0,21
42	paso	Gustavia macarenensis Philipson.	Lecythidaceae	6,00	0,21
43	tachuelo	Zanthoxylum rhoifolium Lam.	Rutaceae	6,00	0,21
44	atamba	Cecropia sp. Loefl.	Urticaceae	6,00	0,21
45	cedro	Cedrela odor= ata L.	Meliaceae	5,00	0,18
46	pitón	Grias neuberthii J.F.	Lecythidaceae	5,00	0,18
47	aguacatillo<= o:p>	Persea caeru= lea Ruiz & Pav Mez.	Lauraceae	5,00	0,18
48	chicle	Manilkara zapota L. P. Royen	Sapotaceae	4,00	0,14
49	cabo de hach= a	Trichilia hi= rta L.	Meliaceae	4,00	0,14
50	guambula	Bougain= villea Comm. ex Juss.	Nyctaginaceae	3,00	0,11
51	guayabo=	Psidium guaj= ava L.	Myrtaceae	3,00	0,11
52	limoncillo	Melicoccus bijugatus Jacq.	Sapindaceae	3,00	0,11
53	Pariachi	Calycophyllum candidissimum Vahl DC.=	Rubiaceae	3,00	0,11
54	Quila	Chusquea quila Kunth.	Poaceae	3,00	0,11
55	Uvilla<= /o:p>	Pourouma spp= . Aubl.	Urticaceae	3,00	0,11
56	Bálsamo	Myroxylum balsamum L.	Fabaceae	2,00	0,07
57	barbasco	Lonchocarpus= nicou Aubl. DC.	Fabaceae	2,00	0,07
58	guayabillo	Psidium sartorianum O. Berg Nied.	Myrtaceae	2,00	0,07
59	peine de mon= o	Apeiba glabra Aubl.	Malvaceae	2,00	0,07
60	árbol de maní	<= span style=3D'font-size:10.0pt;line-height:150%;mso-bidi-font-family:"Times Ne= w Roman"; mso-ansi-language:ES-EC;font-weight:normal;text-decoration:none;text-unde= rline: none'>Sterculia quadrifida R. Br.	Malvaceae	2,00	0,07

Tabla 3=

Número de especies identificadas en la provincia de Pastaza (continuación)

Cód.	Nombre común	Nombre Científico	Familia	No ind.<= /o:p>	%<= /o:p>
61	santa m= aría	Calophyllum brasiliense L. Cambess.=	Calophyllaceae	2,00	0,07
62	pechuga de gallina	Hasseltia floribunda Kunth.	Salicaceae	2,00	0,07
63	Sauco	Sambucus canadensis Linneo	Adoxaceae	2,00	0,07
64	Sisín	Podocarpus oleifolius D. Don.	Podocarpaceae	2,00	0,07
65	Lispungo	Couroupita guianensis Aubl.	Lecythidacea= e	2,00	0,07
66	algodoncillo	Alchornea iricurana Casar.	Euphorbiaceae	2,00	0,07
67	caracaspi	Anacardium excelsum L.	Anacardiaceae	1,00	0,04
68	carańa	Bursera graveolens Kunth Triana & Planch.	Burseraceae	1,00	0,04
69	chilca<= /o:p>	Baccharis L.	Asteraceae	1,00	0,04
70	chilco	Ageratina tinifolia Kunth R= .M. King & H. Rob.	Asteraceae	1,00	0,04
71	chincha=	Geonoma unda= ta Klotzsch.	Arecaceae	1,00	0,04
72	chontacaspi	Mouriri oligantha Pilg.	Melastomataceae	1,00	0,04
73	perillo=	Couma macroc= arpa Barb. Rodr.	Apocynaceae<= o:p>	1,00	0,04
74	dunduna	Eugenia florida DC.	Myrtacea	1,00	0,04
75	higueron	Ficus aurea<= /span> Nutt.	Moraceae	1,00	0,04
76	guabiduco	Piper carpunya Ruiz & Pav.	Piperaceae	1,00	0,04
77	gualis<= /o:p>	Musa velutina H. Wendl. &= amp; Drude	Musácea	1,00	0,04
78	ishpingo	Ocotea quixos Lam. Kosterm.	Lauraceae	1,00	0,04
79	laurel de ce= ra	Morella pubescens Humb. & Bonpl. Wilbur	Myricaceae	1,00	0,04
80	malva	Malva arborea L. Webb & Berthel.	Malvaceae	1,00	0,04
81	mango de mon= te	Mangifera L.	Anacardiacea= e	1,00	0,04
82	moral fina	Maclura tinctoria L. Steud	Moracea= e	1,00	0,04
83	lluvia de or= o	Cassia fistu= la L.	Fabaceae	1,00	0,04

Tabla 3=

Número de especies identificadas en la provincia de Pastaza (continuación)

Cód.	Nombre común	Nombre Científico	Familia	No ind.<= /o:p>	%<= /o:p>
84	cacao de mon= te	Herrania Evans.	= Malvaceae	1,00	0,04
85	nimbo	Azadirachta indica A. Juss.	= Meliaceae	1,00	0,04
86	árbol del pa= n	Artocarpus altilis Parkinson Fosberg.	Moraceae<= o:p>	1,00	0,04
87	maría	Ficus jacobii V.zq. Avila	Moraceae	1,00	0,04
88	yapit	Ficus pertus= a L.f.	Moraceae	1,00	0,04
89	yunyún	terminalia oblonga Ruiz & Pav.	Combretaceae	1,00	0,04
90	desconocido<= o:p>	desconocido =	desconocido =	1,00	0,04
Total				2842,00	100

Número de individu= os por cantones

Se identificaron 2= 842 individuos que representa el 100% de la provincia de Pastaza distribuidos de siguiente manera: Arajuno 507, Mera 346, Pastaza 1 116 y Santa Clara 873 del estudio realizado (figura 3).

Figura 3

Total, de individuos id= entificados por cantón de la provincia Pastaza

Realizado en las á= rea antes mencionadas y localizadas en los cuatro cantones de la provincia. Del 100% de individuos, el 39,27% corresponde al cantón Pastaza con 1116 individuos, cantón Santa Clara con el 30,72%, cantón Arajuno 17,84% y por último el cantón Mera con el 12,17%. Esto se llevó a cabo en función de los criterios del tipo de finca y número de parcelas por cantón, razón por la q= ue varían significativamente los datos presentados.

Figura 4

Total, de individuos en la provincia de Pastaza

Las especies encontradas fueron 90 especies, de las cuales se eliminaron 81 especies, porque tienen un bajo % de representatividad, quedando solo con 9 especies forestales, por su potencial productivo como una ventaja para el manejo forestal de árboles o arbustos sostenible y sustentable (Natalini et al., 2016). Si bien es cierto que utilizan el conteo= de anillos para algunos árboles, que representan las temporadas de crecimiento= del árbol y permite desarrollar los planes de manejo forestal (Rojas-García et al., 2020), se observaron anillos de crecimiento distintos en algunos individuos (Fontana et al., 2019). En la figura 4 se presenta el número de individuos y su predominancia o abundancia.

Análisis estadístico del fuste de los árboles Piptocoma discolor (pigüe)

De acuerdo a su categoría de diámetro de la base de crecimiento del árbol, se ajusta a la g= uía matemática según (González et al., 2018). Por lo tanto, de igual similitud, guarda concordancia con el fuste superior de los árboles de las otras especies, de igual manera se presenta la gráfica de los datos en forma conjunta del estu= dio de acuerdo con su categoría, donde se observa las diferencias altamente significativas, de la incidencia de las condiciones climatológicas y de sue= lo, en base a su diámetro obtenido de las medias de los cuatro cantones de la Provincia de Pastaza. Desde el punto de vista forestal y necesidad urgente = de un manejo forestal sostenible donde se incorporen las acciones biológicas (= Murillo, Rivera y Castizo, 2018) (tabla 4).

Tabla 4=

Análisis de varianzas al 99 % de confiabilidad del fuste inferior<= /i>

Fuente de variación

Suma de Cuadrados

Grados de libertad

Cuadrados medios Esperados

Fisher

p-valor

Modelo<= /o:p>

1920,01

17

112,941654

48,6037674

0

Categoría

1915,03=

15=

127,668= 431

54,9413= 477

0<= /o:p>

Repetición

4,98

2

2,49083= 333

1,07191527

0,35510303

Caso

0<= /o:p>

0<= /o:p>

0<= /o:p>

Error

69,71

30

2,32372222

Total

1989,72=

47=

CV=3D

7,13

Las categorías de su simbología de los cuatro cantones de la provincia de Pastaza: M =3D Mera, A =3D Arajuno, S =3D Santa= Clara y C =3D Canelos-Pastaza.

Tabla 5=

Test de Tukey Alfa=3D0,01 DMS=3D5,45661 confiabilidad del fuste inferior

Categoría

Media

n=

E.E.

Col5

Col6

Col7

Col8

Col9

Col10<= o:p>

Col11<= o:p>

Col12<= o:p>

Col13<= o:p>

MA

12,60<= o:p>

3=

0,9

A

AA

13,33<= /p>

3

0,9

A

B

SA

13,40<= o:p>

3=

0,9

A

B

CA

13,67<= /p>

3

0,9

A

B

CB

17,67<= o:p>

3=

0,9

A

B

C

SB

18,00<= /p>

3

0,9

A

B

C

D

MB

18,47<= o:p>

3=

0,9

B

C

D

AB

19,20<= /p>

3

0,9

C

D

E

CC

22,77<= o:p>

3=

0,9

C

D

E

F

SC

23,30<= /p>

3

0,9

D

E

F

MC

24,17<= o:p>

3=

0,9

E

F

G

AC

25,03<= /p>

3

0,9

F

G

H

AD

29,50<= o:p>

3=

0,9

G

H

I

MD

29,87<= /p>

3

0,9

H

I

SD

30,30<= o:p>

3=

0,9

H

I

CD

30,90<= /p>

3

0,9

I

Según los resultados obtenidos de las tablas 4 y 5 del análisis de varianza del fuste del crecimiento Piptocoma discolor existen diferencias altamente significativas entre los métodos de manejo tradicional del bosque en forma natural, con una prueba estadística de Fisher de 48,66%= , (tabla 4), y su relación con categorías que le corresponde a su diámetro analizados por los cuatro cantones de 54,94 %, con coeficiente de variabilidad de 7,13= % y con una probabilidad de ocurrencia menor al 0,01 % y con una confiabilidad = del 99 %, con una prueba de Tukey al 0,01 % (tabla 5) con una Diferencia Mínima Significativa (DMS) 5,45 %; entre los cantones, esto hace la referencia a su base del tronco del árbol, en relación a su crecimiento lo que cumple el mo= delo matemático propuesto.

Tabla 6=

Análisis de varianzas al 99% de Confiabilidad del fuste superior

Fuente= de variación

Sumas = de cuadrados

Grados= de libertad

Cuadra= dos medios

Fisher=

p-valo= r

Modelo=

1785,8= 3

17

105,04= 9

40,758=

0,000<= o:p>

Categoría

1784,85

15

118,990

46,167=

0,000<= /p>

Repetición

0,98

2=

0,489<= o:p>

0,190<= o:p>

0,828<= o:p>

Caso

0

0

0,000<= /p>

Error<= /p>

77,32<= o:p>

30

2,577<= o:p>

Total<= /p>

1863,15

47

CV=3D<= /p>

10,22<= /p>

<= /span>

Tabla 7=

Test de Tukey alfa 0,01DMS =3D 5,75 confiabilidad del fuste superior<= /span>

Categoría

Medias=

N=

E.E.

Col5

Col6

Col7

Col8

Col9

Col10<= /p>

SA

8,26

3=

0,94

A

MA

8,77

3

0,94

A

B

SC

9,36

3=

0,94

A

B

AA

9,5

3

0,94

A

B

CA

9,5

3=

0,94

A

B

CB

12,33<= /p>

3

0,94

A

B

C

SB

13,26<= o:p>

3=

0,94

A

B

C

AB

13,97<= /p>

3

0,94

A

B

C

MB

14,5

3=

0,94

B

C

D

AC

16,5

3

0,94

C

D

CC

17,07<= o:p>

3=

0,94

C

D

E

Tabla 7=

Test de Tukey alfa 0,01DMS =3D 5,75 confiabilidad del fuste superior (continuaci= ón)

Categoría

Medias=

N

E.E.

Col5

Col6

Col7

Col8

Col9

Col10<= /span>

MC

20,17<= o:p>

3=

0,94

D

E

AD

22,33<= /p>

3

0,94

E

F

SD

22,75<= o:p>

3=

0,94

E

F

<= /span>

= Figura 5

= Análisis de varianza del diámetro del fuste

=

El análisis de varianza del fuste de los árboles P= iptocoma discolor (pigüe) en relación al a la DAP de crecimiento, se demuestra e= n el modelo de Fisher el 40,76% de diferencias altamente significativas, las categorías corresponde al diámetro= en sus cuatro cantones con el 46,17 %, su coeficiente de variabilidad es de 10= ,22 %, con una probabilidad de ocurrencia menor al 0,01 % y una confiabilidad d= el 99 % (tabla 6); Con una prueba de Tukey al 0,01 %, con una diferencia mínim= a significativa (DMS) 1,78 (tabla 7). Esta referencia se hace en base a la DAP del tronco d= el árbol, su influencia de las condiciones climáticas y del suelo en cada cantón muestra las diferencias de crecimiento del fuste (figura 5). Lo = que se asemeja con los estudios planteados de la modelación matemática del crecimiento de la especie (González et al., 2018). Existen otras especies que debido a su dinámica de crecimiento y bifurcación, manifiestan una supervivencia con un mayor crecimiento dentro de la región amazónica, estas son: Nectandra sp., Terminalia oblonga, Apeiba asp= era, Guarea kunthiana, Caryodendron orinocense, Terminalia Amazonía, Albizia sp., Ochroma pyramidale, Piptocoma discolor, Heliocarpus americanus, Aspidosperma laxiorum, Pouteria capasífolia, Clarisia racemosa y Cedrela odorata, estas especies se han desarrollado después de las actividades = como la deforestación, degradación forestal y al cambio del uso de la tierra ( Food and Agricultura Organization of the United Nations [FAO] & Programa de las Naciones Unidas para el medio ambiente = [PNUMA], 2020)

La abundancia está dada en función del número de individuos por hectárea y del área basal/ha; = El porcentaje más alto obtenido en este estudio Piptocoma discolor, se debe a su diámetro mayor en relación con= las otras especies del bosque secundario como se muestra en la figura 5, donde = se estiman las condiciones del potencial de biomasa. Sin embargo, se consideró= el acuerdo No. 0125, por sus características diamétricas para el manejo forest= al sostenible de los bosques, en el artículo 11, literal a), inciso 3 detalla = que un árbol no puede ser cortado si la especie tiene una baja abundancia con D= AP igual o superior a 30 centímetros, por lo tanto, no podrán ser incluidos en= un aprovechamiento forestal (FAO & PNUMA, 2020).

Derivado de este análisis, se observó que de manera general existe una dominancia debido a s= us relaciones de crecimiento y la sinergia entre Piptocoma discolor y las otras especies (tabla 3), para = el manejo forestal (producción de madera). Los resultados por su gran diversid= ad de especies sugieren una relación sinérgica entre las 9 especies (Lee & Lautenbach, 2016). Dado que encontraron pocos estudios acer= ca del flujo de biomasa y agua de las especies forestales, al menos en este ca= so la compensación, en el corto plazo que se obtiene de algunas especies es po= co, a diferencia del (pigüe), que por su crecimiento rápido puede contribuir al desarrollo económico y social de la Amazonía ecuatoriana (González et al., = 2015).

Con resp= ecto a las condiciones de crecimiento y la dominancia las diferencias son significativas en algunas especies como (pigüe de pantano, guarumo, canelo, jacaranda, doncel, uva, avío y naranjillo); A pesa= r de su importancia, la dominancia es mayor con respecto a la abundancia de las otras especies que presentaron diámetros mayores, como es el caso de guarum= o y uva que no es tan común encontrar en realces en pasto y realces en chacra. = Esto tiene que ver con relación a sus condiciones climáticas y de altitud, en ra= ngos comprendidos entre 901-1100 m.s.n.m., lo que equivale a 1.8 ha, seguido del rango altitudinal entre 500-700 m.s.n.m. con 16 parcelas de evaluación y finalmente están los rangos >1100 y de 701-900 m.s.n.m. con 7 y 4 parcel= as respectivamente lo que confirman sus estudios (Ordóńez, 2020).

Considerando las Normas para el Manejo Forestal Sustenta= ble del aprovechamiento de la madera en bosque húmedo que están constituidos por especies heliófitas, tales como el niguito o frutillo (Mantingia sp.= ) el pigüe (Pallalesta discolor), la= balsa o boya (Ochroma spp), el guarum= o (Cecropia spp), el sapan de paloma = (Trema spp), el pichingo chillalde = (Trichospermum spp), la balsa del o= riente (Eliocarpus americanus), el ali= so (Alnus acuminata), Laurel de cera (= Myrica pubescens), guasimo o guasm= o (Guasmo ulmifolia) según el acuerdo 0125 del Ministerio del Ambiente del Ecuador (MAE, 2015). Las especies pioneras de rápido crecimie= nto pigüe y balsa, muestran alta demanda a nivel nacional y considerando que su manejo requiere de bajos costos de inversión, es necesario considerar su potencial para pequeńos productores de la Costa y la Amazonía (Pinelo, 2016).

Tabla 8=

Calidad del Manejo forestal Piptocoma discolor (pigüe) y otras espe= cies

Descripción

E5

E4

E3

E2

E1

Porcentaje

Manejo

0

0

0

27,08

72,92

100

Control

0

0

0

27,08

72,92

100

Raleo

0

0

0

0

100

100

Limpieza

0

0

0

35,42

64,58

100

Promedio de la calidad del Manejo

22,39

77,61

100

Nota: Las condiciones del manejo de la calidad de = la especie significan: E1 malo,

E2 regular, E3 Bueno, E4 Muy bueno, E5 excelente.<= o:p>

Los resultados de = las encuestas realizadas del crecimiento fue en base a las frecuencias absoluta= y relativa, en los cuatro cantones que se presentan en la (tabla 8), se obser= va que son diferentes los promedios de sus porcentajes de la fase de crecimiento, en relación al “diámetro de la base y superior del árbol”(cm), “altura, copa y raíz” del árbol (m); Los árboles medidos in situ y los tumbados, lograron obtener datos fidedignos de la calidad del manejo forestal, con una calificación regular (E2) con un promedio del 22,39% y sin manejo (E1) el 77,61%, definido para su aprovechamiento como recurso maderable y que un fu= turo aplicando el manejo cambiara este sistema tradicional para su aprovechamien= to. Siendo un desafío de mejorar las condiciones del manejo forestal ADDIN ZOTERO_ITEM CSL_CITATION {"citationID":"A34A0Edf","properties":{"= formattedCitation":"(Rojas 2020)","plainCitation":"(Rojas 2020)","noteIn= dex":0},"citationItems":[{"id":60,"uris"= :["http://zotero.org/users/local/eLIiInmM/items/HSM79KZZ"],"= uri":["http://zotero.org/users/local/eLIiInmM/items/HSM79KZZ"= ;],"itemData":{"id":60,"type":"article-j= ournal","abstract":"Resumen: el presente artículo tiene como objetivo primario reflexionar sobre cómo la= bioética pue-de dar luces para un desarrollo forestal más comprometido con la vida en general. El estudio se focaliza en el Perú; sin embargo, se toma en cuenta","container-title":"Revista Latinoamericana de Bioética","DOI":"https://doi.org/10.18359/rlbi.4536&quo= t;,"ISSN":"2462-859X","issue":"1",&= quot;language":"spa","page":"107-122",&q= uot;source":"www.academia.edu","title":"Aprox= imaciones para el desarrollo de una bioética forestal a partir del caso peruano","volume":"20","author":[{"= family":"Rojas","given":"Rodrigo Severo Arce"}],"issued":{"date-parts":[["2020"]= ]}}}],"schema":"https://github.com/citation-style-language/s= chema/raw/master/csl-citation.json"} (Rojas 2020).

En el estudio las otras especies sin identificación, Cecropia peltata L. Ocotea Aubl, Croton lechleri Muell. Arg, Vismia baccifera L. Triana & Planch y Morella p= ubescens Humb. & Bonpl. Wilbur son las= que presentan una abundancia y dominancia directamente proporcional al número de individuos; aunque en algunas especies como Quercus alba L., Vismia baccifera L. Triana & Planch, Myrica pubescens Humb. & Bonpl. ex Willd, Brosimun utile Kunth, Trema integerrima Beurl, Calophyllum brasiliense L. Cambess, sin la dominancia presenta porcentajes mayores, debido a que los individuos encontrados tienen diámetr= os mayores.

<= /span>

<= /span>

Tabla 9=

Condiciones del crecimiento Piptocoma discolo= r (pigüe) y otras especies

Descripción

E5

E4

E3

E2

E1

%

F1-F2-F3-Limpio

40,63

31,25

18,75

9,37

0

100

Condición actual de la producción

Condición

10,42

47,91

25

16,67

0

100

Destino de la producción

Descripción

Madera

Construcción

Cajas

Leńa

Muebles

Destino

16,67

31,25

37,5

14,58

0

100

Evaluación de calidad del dominio de las especies en relación con las otras

Descripción

Dominante

Codominante

Intermedio

Suprimido

Ninguno

Posición sociológica

50

50

0

0

0

100

El crecimiento, producción, dominancia y posición sociológica según el estudio se muestra e= n la (tabla 9). Se considera en orden de importancia y jerarquía que encuentra en estos ejemplares que han alcanzado una dominancia debido a sus diámetros, crecimiento rápido y su abundancia, por su participación en la estructura horizontal y vertical, aunque en todos los casos las especies antes mencion= ada por sus términos triplica las restantes especies vegetales que se caracteri= zan por su asociación, lo que permite visualizar de acuerdo con el peso ecológi= co de las especies dentro de la comunidad vegetal.

Conclusiones

·      =    Dentro= de la provincia de Pastaza, se evidencia Piptocoma discolor y las 9 especies descritas se pueden considerar por su crecimiento rápido como posibles especies para el aprovec= hamiento con fines sostenibles y sustentables ayudando de esta manera al mejoramiento del nivel de vida de la población de la zona, por su riqueza y extensión territorial y diversidad forestal, sin embargo, hasta la actualidad no cuen= ta con estrategias de conservación.

·      =    La asociación dominante de especies de la zona de estudio está integrada por <= /span>Piptocoma discolor, Cecropia peltata L., Inga edulis M= art, Jacaranda mimosifolia D. Don., Miconia Ruiz & Pav., Myrica pubescens Humb. & Bonpl. ex Willd., Piptocoma Cass, Ocotea Aubl.= , Vismia baccifera L. Triana & Planch., Joosia umbellifera H. Karst. La regeneración natural de las mismas adquiere importancia financiera para la provincia de Pastaza, debido a rápi= da adaptación en los bosques secundarios, mediante un manejo forestal adecuado= se beneficiarán a las familias económicamente.

·      =    En relación con su densidad y manejo forestal hasta la actualidad no se cuenta= con planes de manejo forestal, por esta razón se prevé que esta información, se= rá útil para las condiciones de desarrollo y crecimiento de esta vegetación co= n el fin de impulsar esta actividad con los gobiernos locales de la provincia de Pastaza.

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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 autorizado por el director de la R= evista Conciencia Digital.

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ISSN: 2600-5= 859

Vol. 5 No 3.2,<= span style=3D'mso-spacerun:yes'> pp. 67 – 90 , septiembre 2022<= /o:p>

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Fuente de variación	Suma de Cuadrados	Grados de libertad	Cuadrados medios Esperados	Fisher	p-valor
Modelo<= /o:p>	1920,01	17	112,941654	48,6037674	0
Categoría	1915,03=	15=	127,668= 431	54,9413= 477	0<= /o:p>
Repetición	4,98	2	2,49083= 333	1,07191527	0,35510303
Caso	0<= /o:p>	0<= /o:p>	0<= /o:p>
Error	69,71	30	2,32372222
Total	1989,72=	47=		CV=3D	7,13

Fuente= de variación	Sumas = de cuadrados	Grados= de libertad	Cuadra= dos medios	Fisher=	p-valo= r
Modelo=	1785,8= 3	17	105,04= 9	40,758=	0,000<= o:p>
Categoría	1784,85	15	118,990	46,167=	0,000<= /p>
Repetición	0,98	2=	0,489<= o:p>	0,190<= o:p>	0,828<= o:p>
Caso	0	0	0,000<= /p>
Error<= /p>	77,32<= o:p>	30	2,577<= o:p>
Total<= /p>	1863,15	47		CV=3D<= /p>	10,22<= /p>

Categoría	Medias=	N=	E.E.	Col5	Col6	Col7	Col8	Col9	Col10<= /p>
SA	8,26	3=	0,94	A
MA	8,77	3	0,94	A	B
SC	9,36	3=	0,94	A	B
AA	9,5	3	0,94	A	B
CA	9,5	3=	0,94	A	B
CB	12,33<= /p>	3	0,94	A	B	C
SB	13,26<= o:p>	3=	0,94	A	B	C
AB	13,97<= /p>	3	0,94	A	B	C
MB	14,5	3=	0,94		B	C	D
AC	16,5	3	0,94			C	D
CC	17,07<= o:p>	3=	0,94			C	D	E

Descripción	E5	E4	E3	E2	E1	Porcentaje
Manejo	0	0	0	27,08	72,92	100
Control	0	0	0	27,08	72,92	100
Raleo	0	0	0	0	100	100
Limpieza	0	0	0	35,42	64,58	100
Promedio de la calidad del Manejo	22,39	77,61	100

Descripción	E5	E4	E3	E2	E1	%
F1-F2-F3-Limpio	40,63	31,25	18,75	9,37	0	100
Condición actual de la producción
Condición	10,42	47,91	25	16,67	0	100
Destino de la producción
Descripción	Madera	Construcción	Cajas	Leńa	Muebles
Destino	16,67	31,25	37,5	14,58	0	100
Evaluación de calidad del dominio de las especies en relación con las otras
Descripción	Dominante	Codominante	Intermedio	Suprimido	Ninguno
Posición sociológica	50	50	0	0	0	100