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Propagaci= ón de árboles de Bursera graveolens (Kunt) Triana & Planch, por estacas

Propagation of Bursera graveolens (Kunt) Triana & Planch trees, by cuttings

¹	Raúl Armando Ramos Veintimilla	<= /o:p>	https://orcid.org/0000-0001-5181-1039=
	Docent= e, Escuela Superior Politécnica de Chimborazo, Riobamba, Ecuador.= raul.ramos@espoch.edu.ec
= ²	Ana Alexandra Yagual González	<= /o:p>	https://orcid.org//0000-0002-6787-8868
	Egresada, Escuela Superior Politécnica= de Chimborazo, Riobamba, Ecuador. ana.yagual@espoch.edu.ec
= ³	Carlos Francisco Carpio Coba	<= /o:p>	https:= //orcid.org/000= 0-0002-7361-7664
	Docent= e, Escuela Superior Politécnica de Chimborazo, Riobamba, Ecuador.= ccarpio@espoch.edu.ec
= ⁴	Mario Rolando Ramos Veintimilla	<= /o:p>	https://orcid.org/0000-0003-2264-2808=
	Invest= igador Instituto Nacional de Investigaciones Agropecuarias, INIAP, Ecuador.= mario.ramos@iniap.gob.ec

	Artículo de Investigación Científica y Tecnológica Enviado: 16/07/2022 Revisado: 26/08/2022 Aceptado: 02/09/2022 Publicado:15/09/2022 DOI: https://doi.org/10.33262/= ap.v4i3.2.276 = =
=
Cítese:		&= nbsp; Ramos Veintimilla , R. A., Yagual González, A. A., Carpio Coba, C. F., & Ra= mos Veintimilla, M. R. (2022). Propagación de árboles de Bursera graveolens (Kunt) Triana & Planch, por estacas. AlfaPublicaciones, 4(3.2), 40–55. https://doi.org= /10.33262/ap.v4i3.2.276
		*ALFA PUBLICACIONES,* es una Revista Multidisciplinar, Trimestral, que se publicará en soporte electrónico tiene como misión contribu= ir a la formación de profesionales competentes con visión humanística y crítica que sean capaces de exponer sus resultados investigativos y científicos en la misma medida que se promueva mediante su intervención cambios positivos en la sociedad. https://al= fapublicaciones.com La revista es editada por la Editorial Ciencia Digital (Editorial de prestigio registra= da en la Cámara Ecuatoriana de Libro con No de Afiliación 663) www.celibr= o.org.ec
		Esta revista está protegida bajo una licencia Creative Commons AttributionNonCommercialNoDerivatives 4.0 International. Copia de la licencia: http://creativecommons.org/licenses/by-nc-nd/4.0= /
Palabras claves: Bursera graveolens, propagación asexual, auxina, ácido indol-butíri= co, bosque seco, vivero.		Resumen Introd= ucción. Bursera graveolens (Kunt) Triana & Planch, especie forestal nativa de bosques sec= os del Ecuador, mantiene un equilibrio en ecosistemas xerofíticos frágiles lo que incide en proteger esta especie en su desarrollo vegetativo, el probl= ema radica en su propagación sexual debido a que presenta un porcentaje bajo = de germinación de las semillas, y a su vez la limitada información generada sobre propagación asexual. Objeti= vo. Determinar el tratamiento con el que obtienen mejores comportamient= os las variables de crecimiento inicial de B. graveolens. Metodología. El presente trabajo de investigación se desarrolló en vivero, donde se aplic= ó un Diseńo de Bloques Completamente Aleatorizados con dos factores: i) tipo de sustrato (A1: tierra = negra + tamo de arroz + arena de río, A2: tierra negra + estiércol de ganado va= cuno y A3: tierra negra + arena de río) y ii) Concentraciones de Auxinas (AIB) (B1: 6.000 ppm, B2: 8.000 ppm, B3: 10.000 ppm y B4: agua destilada); generando 12 tratamientos, con 10 observaciones cada uno. Se realizó análisis paramétrico para las variables que cumplían= los supuestos de normalidad y homocedasticidad y análisis no paramétrico a las variables que no cumplen. Las variables evaluadas fueron: prendimiento, número, altura y diámetro de brotes. Result= ados. No se evidenció interacciones entre el tipo de sustrato y las concentraciones de auxina, sí un efecto de sustratos. El prendimiento promedio de estacas de B. graveol= ens fue de 36,9%, mostrando el mayor porcentaje (51,88 %) el sustrato A3, la longitud de brotes a los 45 días fue de 2,04 cm. Conclu= siones. No existió un efecto en la interacción sustrato con auxina (AIB) en= las variables estudiadas, se observó un efecto del factor tipo de sustrato, d= onde el sustrato A3 experimentó un mayor porcentaje en prendimiento y longitud= de brotes.
Keywords:= Bursera graveolens, asexual propagation, auxin, indole-butyric ac= id, dry forrest, seedbed.		Abstract Introd= uction. Bursera graveolens (Kunt) Triana & Planch, a forest species native to dry forests of Ecuador, maintains a balance in fragile xerophytic ecosystems, which affects the protection of this species in its vegetative development, the problem lie= s in its sexual propagation since it presents a percentage low seed germinatio= n, and in turn the limited information available on its asexual propagation.= Objective. To determine the tre= atment with which the initial growth variables of B. graveolens obtain better behavior. Methodology. The present research work was developed in a seedbed, where a Completely Randomized Block Design was applied with two factors: i) type of substrate= (A1: black earth + rice chaff + river sand, A2: black earth + cattle manure be= ef and A3: black earth + river sand) and ii) Auxin Concentrations (AIB) (B1: 6,000 ppm, B2: 8,000 ppm, B3: 10,000 ppm = and B4: distilled water); generating 12 treatments, with 10 observations each. Parametric analysis was performed for the variables that met the assumpti= ons of normality and homoscedasticity and non-parametric analysis for the variables that did not. The variables evaluated were setting, number, hei= ght, and diameter of shoots. Results.= There was no evidence of interactions between the type of substrate and a= uxin concentrations, but an effect of substrates. The average taking of B. graveolens cuttings was 36.9%, showing the highest percentage (51.88%) in the A3 substrate, the sprout length at 45 days was 2.04 cm. C= onclusions. There was no effect on the substrate interaction with auxin (AIB) in the variables studied, an effect of the substrate type factor was observed, w= here the A3 substrate experienced a higher percentage in setting and sprout length.

Introducción

Ecuador es uno de los países a nivel mundial que posee una gran diversidad de flora= y fauna (Grijalva et al., 2016; Ramos et al., 2017), existen estimaciones que indican que cerca del 35% de la superficie de bosque en el Ecuador correspo= nde a los bosques secos, del cual se ha perdido el 50%, considerando que el 75%= son especies caducifolias que presentan una época estacionaria, es decir, pierd= en sus hojas durante un periodo corto (Aguirre, 2012).

En Ecuador la tala indiscriminada de los bosques, y en particular el bosque se= co en los últimos ańos, ha sido cada vez más notoria, una de las causas es la obtención de recursos maderables y no maderables de especies representativas económicamente realizando una extracción selectiva de especies maderables, ocasionando la degradación de éste ecosistema, ampliación de la frontera agrícola y pérdida de la base genética forestal y particularmente en B. graveolens, especie que se encuentra en peligro de extinción (Vázquez et al., 2005).

Los bosques deciduos o también llamados bosques secos, son ecosistemas frágiles= y únicos que albergan especies endémicas y aportan beneficios económicos, sociales, culturales y ambientales (Aguirre et al., 2016); por ello, el cui= dado y la conservación se ha convertido en una prioridad. Este ecosistema ha sido fuertemente perturbado y degradado por la actividad humana, para cambiar de= uso del suelo a agricultura convencional; de esta manera, retiran la cobertura forestal, mueven el suelo, este se erosiona y además utilizan agroquímicos indiscriminadamente. Otras de las causas que ocasionan dańo este ecosistema= es la explotación de recursos forestales madereros, expansión urbana, aumento = de industrias camaroneras (Estrella et al., 2005).

Una de las especies forestales, nativa de bosques secos del Ecuador y de interés socioeconómico es la conocida como palo santo, Bursera graveolens= (Kunt) Triana & Planch, pertenece a la familia Burseraceae, crece en zo= nas bajas del perfil costanero, su distribución oscila entre 0 a 2000 m.s.n.m. (Aguirre, 2012). Por otro lado, es un árbol aromático que tiene múltiples beneficios, siendo éste utilizado principalmente como medicinal natural y ancestral, se aplica para dolores en todo el cuerpo, reumatismo y como remedio para dolores estomacales (Manzano, 2007).

La especie forestal B. graveolens, es considerada una madera sagrada de= bido a su utilización en rituales espirituales y ceremonias, creando un ambiente= de armonía y paz en el entorno. En la industria es utilizada para la elaboraci= ón de aceites esenciales, jabones e incienso; debido a esto, es inminente busc= ar estrategias para conservar este ecosistema natural, restaurar y repoblar con ésta especie de alto valor social y económico, como lo busca el decenio de = las Naciones Unidas sobre la restauración de los ecosistemas 2021 – 2030 que es= un llamado a la protección y reactivación de los ecosistemas en todo el mundo,= en beneficio de las personas y la naturaleza, de esta forma alcanzar objetivos= globales (Organización de las Naciones Unidas para la Alimentación [FAO], 2021).

B. graveolens es un árbol de hojas caducifolias que vive en asociación con otras especies y mantiene un equilibrio en estos ecosistemas xerofíticos frágiles y poco apreciados. Es una especie forestal difícil de propagar p= or reproducción sexual o semilla, debido a que por alguna razón física o fisiológica presenta un porcentaje extremadamente bajo de germinación de la semilla y regeneración natural. Los datos reportados en la literatura sobre= la germinación de la semilla están alrededor del 20 %; siendo esta una seria limitante para la multiplicación de la especie a nivel de vivero y los programas de repoblación (Morillo et al., 2016).

La propagación asexual en especies leńosas permite obtener una nueva planta con características similares a la planta madre en períodos relativamente corto= s y a su vez conservar las especies que estén en peligro de extinción y es la alternativa para la multiplicación de especies leńosas que experimentan problemas de baja germinación de sus semillas o producciones estacionales (= Mero et al., 2017).

El desconocimiento de métodos y protocolos de propagación asexual y sustratos apropiados para el desarrollo vegetativo de B. graveolens es un limitante para que esta especie sea implementada en planes de reforestac= ión y programas de manejo forestal a nivel de la provincia de Santa Elena y la = zona de bosque seco como tal. En esta línea Mero et al. (2017), en la comuna Quimis-Manabi, condujeron un estudio donde evaluaron el comportamiento de B. graveolens= al efecto de reguladores de crecimiento tipo auxínico, la variable respuesta fue la regeneración de tej= ido vegetal. En la experiencia reportan que el tratamiento compuesto por ácido indolbutírico a 8000 ppm + tierra de guaba y arena de río alcanzó la mayor presentación de brotes y callos por estaca, así como el menor porcentaje de mortalidad.

En este contexto, nuestra investigación pretendió propagar vegetativamente por estacas arboles de B. graveolens (palo santo) en condiciones de vive= ro, que ayuda con información para la generación de protocolos de multiplicació= n, misma que servirá para los diferentes programas de restauración y repoblaci= ón con esta especie en bosque seco que desarrollarán la presente y futuras generaciones.

Metodología

La presente investigación se realizó en el vivero agroforestal Dos Mangas de la parroquia Manglaralto, cantón Santa Elena, provincia de Santa Elena-Ecuador. El vivero agroforestal Municipal se encue= ntra ubicadas a 1° 49' 36.9984'' Sur, 80° 41' 48.1200'' Este de latitud sur y Bo= sque Seco Tropical (bs-T) (Yagual, 2022).

El vivero agroforestal se encuentra a 12 m.s.n.m. = con un rango de precipitación anual en la zona de 31,7 a= 350,6 mm distribuida en dos épocas, lluviosa (diciembre-marzo) y seca (abril-novi= embre). La temperatura promedio es de 24 ^oC y la humedad de 87% (Instit= uto Nacional de Meteorología e Hidrología [INAMHI], 2019).

Metodológicamente la investigación ejecutada correspondió a: diseńo experimental de tipo cuasiexperimental y nivel de tratamientos múltiples, como se detalla a continuación:

Los factores estudiados fueron: 1. Tipos de sustrato A1: Tierra negra (50%) + Tamo de arroz (25%) + Arena de río (25%); A2: Tierra negra (50%) + Estiércol de ganado vacuno (50%)= ; A3: Tierra negra (50%) + Arena de río (50%) y 2. Dosis de Auxinas AIB: B1: 6.000 ppm; B2: 8.000 ppm; B3= : 10.000 ppm; B4: Agua Destilada

Los tratamientos estudiados fueron 12, producto de la combinación de los nivele= s de los factores en estudio (3x4), como se muestra en la Tabla 1.

Tabla 1

Tratamientos en estudio

Tratamiento	Factor A<= o:p>	Factor B<= o:p>	Código	Descripci= ón
T1	A1	B1	A1B1	Tierra negra (50%) + Tamo de arroz (25%) + Ar= ena de río (25%) + 6.000 ppm de AIB
T2	A2	B1	A2B1	Tierra negra (50%) + Estiércol de ganado vacu= no (50%) + 6.000 ppm de AIB
T3	A3	B1	A3B1	Tierra negra (50%) + Arena de río (50%) + 6.0= 00 ppm de AIB
T4	A1	B2	A1B2	Tierra negra (50%) + Tamo de arroz (25%) + Ar= ena de río (25%) + 8.000 ppm de AIB
T5	A2	B2	A2B2	Tierra negra (50%) + Estiércol de ganado vacu= no (50%) + 8.000 ppm de AIB
T6	A3	B2	A3B2	Tierra negra (50%) + Arena de río (50%) + 8.0= 00 ppm de AIB
T7	A1	B3	A1B3	Tierra negra (50%) + Tamo de arroz (25%) + Ar= ena de río (25%) + 10.000 ppm de AIB
T8	A2	B3	A2B3	Tierra negra (50%) + Estiércol de ganado vacu= no (50%) +10.000 ppm de AIB
T9	A3	B3	A3B3	Tierra negra (50%) + Arena de río (50%) + 10.= 000 ppm de AIB
T10	A1	B4	A1B4	Tierra negra (50%) + Tamo de arroz (25%) + Ar= ena de río (25%) + Agua Destilada
T11	A2	B4	A2B4	Tierra negra (50%) + Estiércol de ganado vacu= no (50%) + Agua Destilada
T12	A3	B4	A3B4	Tierra negra (50%) + Arena de río (50%) + Agua Destilada

Nota: T=3D Tratamiento; A=3D Sustratos, B=3D Concentración de AIB<= /o:p>

Fuente: Yagual (2022)=

El ensayo se ejecutó con un total de 12 tratamient= os, la unidad observacional fue una estaca plantada, el número de observaciones= por tratamiento fue n=3D10 y finalmente el número de bloques fueron 4; por lo q= ue, el número total de unidades observacionales fue 480 estacas plantadas, como se muestra en la figura 1.

Figura 1

Representación del diseńo de bloques completos al= azar, tratamientos y unidades experimentales para la evaluación

Nota: T1…T12 =3D Tratamientos; 1…10=3D observaciones por tratamiento

Fuente= : Yagual (2022)<= span style=3D'mso-bookmark:_Toc112181557'><= /o:p>

Preparación de concentraciones de ácido indolbutírico (AIB)

Para cada uno de los niveles del factor Auxinas se diluyó en un litro de agua destilada las siguientes concentraciones: B1: 6000 ppm que equivale a 1,225 g., se le agregó 18 gotitas de hidróxido de sodio hasta formar una me= zcla homogénea y luego se diluyó en agua destilada. B2: 8000 ppm que equi= vale a 1,633 g., se le agregó 22 gotitas de hidróxido de sodio hasta formar una mezcla homogénea y luego se diluyó en agua destilada. B3: 10000 ppm = que equivale a 2,041g., se le agregó 30 gotitas de hidróxido de sodio hasta for= mar una mezcla homogénea y luego se diluyó en agua destilada (Yagual, 2022).

Preparación de los sustratos

Los sustratos evaluados se prepararon como componente principal tierra negra proveniente de la capa superficial del bosque donde se desarrolla la especi= e. Para el primer nivel del factor sustratos se utilizó tres porciones de cada componente conformando la siguiente proporción 2:1:1 (50% tierra negra + 25= % tamo de arroz + 25 % arena de río), el segundo nivel estaba compuesto en una proporción 1:1 (50% tierra negra + 50% estiércol descompuesto de ganado vacuno), y finalmente el tercer nivel se conformó con una proporción 1:1 de= los materiales en estudio (50% de tierra negra + 50% de arena de río) (Yagual, 2022).

Desinfección de sustratos

Una vez preparados los tres sustratos en estudio, se procedió a desinfectar; pa= ra lo cual, se humedeció el sustrato con agua, posterior a ello se aplicó una solución de Vitavax® 300 con una concentración de 17g en 10 litros de agua = y se empezó a encharcar completamente los sustratos. Luego de dos días se realiz= ó un movimiento de los sustratos, de una forma individual, con el fin de que expulsen los gases que se pudieron haber generado como efecto de la acción = del desinfectante (Yagual, 2022).

Enfundado de sustrato

Se enfundó cada uno de los sustratos A1 (tierra negra + tamo de arroz + arena = de río), A2 (tierra negra + estiércol de ganado) y A3 (tierra negra + arena de río) en fundas de polietileno 6 x 8 cm de acuerdo con los tratamientos propuestos a evaluar y se les ubicó en cada uno de los bloques (Yagual, 202= 2).

Identificación de plantas madre= de B. graveolens

Las plantas madre de B. graveolens se identificaron en la comuna Aguadit= a, parroquia Colonche provincia de Santa Elena, para lo cual se seleccionaron árboles con excelentes características morfológicas, mayores a 10 ańos y que encuentren sanos, libre de problemas sanitarios (Yagual, 2022).<= /span>

Recolección de estacas

Se recolectaron 480 estacas apicales e intermedias de palo santo (B. graveo= lens) con una longitud entre 35 a 40 cm y un diámetro entre 1 a 5 cm, teniendo al menos 1 o 2 yemas que no muestren (Yagual, 2022).

Repique de especie forestal B. graveolens<= o:p>

Se colocó la estaca en los contenedores de cada uno en los tratamientos (aleto= rizados) T1, T2, T3 T4, T5, T6, T7, T8, T9, T10, T11 y T12 a una profundidad aproxim= ada de 5 cm, y a su vez se compactó el sustrato dejando sin cámaras de aire (Yagual, 2022).

Vari= ables evaluadas

Prendimiento. - Para= el cálculo del porcentaje de prendimiento de las estacas se registró datos a l= os 50 días después de la instalación del experimento (ddie), y se aplicó la fórmula propuesta por Narváez (2021):

Supervivencia. - Para el cálculo del porcentaje de supervivencia de las estacas se registró los datos a los 50 días después de la instalaci= ón del experimento, se aplicó la sig= uiente fórmula:

Número de= brotes. -= Se realizaron evaluaciones a los 15, 30 y 45 días después de la instalación de= l experimento. Se realizó mediante observación directa a cada una de las unidades experimentales (estacas).

Longitud del brote

Se registró información a los 15, 30 y 45 días después de la instalación del experimento<= /span>, del brote de mayor vigor de la estaca con el calibrador venier y/o pie de r= ey, se tomó como referencia la base del brote hacia arriba, esta variable se registró en cm

Diámetro del cuello del brote<= /span>

Se recolectó información a los 15, 30 y 45 días después de la instalación del experimento<= /span>, tomando el dato al brote de mayor vigor de la estaca, con el calibrador ven= ier y/o pie de rey, se realizó la medición del cuello del brote, esta variable = se registró en mm.

Análisis estadístico

A los datos de las variables respuesta evaluada= s en los respectivos periodos de acuerdo con el protocolo de investigación, se realizó la comprobación de los supuestos de normalidad y homocedasticidad, luego se aplicaron pruebas paramétricas (ANOVA univariado de dos factores: sustrato y AIB, considerándoles como efectos fijos) a las variables respues= ta que cumplieron los supuestos, y pruebas no paramétricas para las variables = que no cumplieron dichos supuestos. En el proceso de análisis se utilizó el software estadístico InfoStat.

Resultados y discusión

Prendimiento

Los tipos de sustratos y las dosis de la auxina (Ácido indobutírico) no interac= tuaron estadísticamente (pv =3D 0,7068); al igual que, el factor auxina (pv =3D 0,= 6025); mientras que, los tipos de sustrato afectó significativamente en el prendimiento (p-valor =3D 0,0003). El promedio general de prendimiento (%) = de B. grabelens, a los 50 días despué= s del trasplante, fue de 36,9, como se muestra en la tabla 2). =

Tabla 2

Cuadrados Medios, significancias y promedios de variables respuesta de crecimiento temprano de Bursera graveolens a los 45 de evaluación=

Fuente de Variación

gl

Prendimie= nto (%)

Supervive= ncia (%)

Número de brotes por estaca

Longitud = del brote (mm)

50 ddie

15 ddie

35 ddie

15 ddie

30 ddie

45 ddie

Bloque      &nb= sp;

3

0,62

47,86

0,01

0,96

0,16



0,45



0,1=



Sustrato      &= nbsp;

2

8,03

**

518,61

*

0,08

*

0,29

n.s.

1,71

**

2,64

**

2,17

**

Auxina      &nb= sp;

3

0,47

n.s.

202,47

n.s.

0,01

n.s.

0,48

n.s.

0,38

n.s.

0,15

n.s.

0,38

n.s.

Sustrato*Auxina

6

0,47

n.s.

73,12

n.s.

0,01

n.s.

0,3=

n.s.

0,48

*

0,22

n.s.

0,33

n.s.

Error      &nbs= p;

33<= /span>

0,75

110,61

0,01

0,27

0,18



0,30

0,35

Total      &nbs= p;

47<= /span>



   &nb= sp;

Promedio

36,90

68,80

1,48̴= 3;

1,35=

15,5̴= 3;

16,3=

16,2̴= 3;

Nota: gl: grados de libertad; **: altamente significativo (pv<0,01); *: significativo (pv<0,05); ns: no significa= tivo (pv˃0,05).

Se observa que el sustrato tierra negra (50%) + arena de río (50%) (A3) presen= tó el mejor promedio de brotación a los 50 días después de la instalación del ensayo (51,88%) siendo diferente estadísticamente a los sustratos tierra ne= gra (50%) + tamo de arroz (25%) + arena de río (25%) (A1) y tierra negra (50%) + estiércol de ganado vacuno (50%) (A2), que presentaron los menores promedios 24,38 y 34,38%, respectivamente como se muestra en la figura 2a.

Figura 2

Media de pre= ndimiento y sobrevivencia de B. graveolens, a los 50 días después de la instalación del experimento

Figura 2a. Medias de prendimiento

Figura 2b. Media de supervivencia

Fuente: Yagual (2022)

Supervivencia=

No hubo diferencias estadísticas significativas para la interacción Sustrato*Auxina= (pv =3D 0,6813), ni para el factor Auxina (pv =3D 0,1608); mientras que, para e= l factor Sustrato encontró diferencias estadísticas altamente significativas (p-valo= r =3D 0,0160). El promedio general de Supervivencia (%) a los 50 días después de = la instalación del ensayo fue de 60,80 como se muestra en la tabla 2.

El mayor promedio (63,15%) de supervivencia observado en las estacas de B. graveolens experimentaron las plantadas en el sustrato tierra negra (50%) + arena de río (50%) (A3), en comparación con los otros sustratos, presentando el menor promedio (52,25%)= de supervivencia las estacas plantadas en tierra negra (50%) + tamo de arroz (= 25%) + arena de río (25%) (A1), como se muestra en la figura 2b.

Número de brot= es por estaca

Los tipos de sustrato y las dosis de AIB no generaron efecto importante en el número de brotes por estaca, observado a los 45 días después de la instalac= ión del experimento. La prueba de Friedman desarrollada presentó un p-valor de = 0,7185. El promedio general fue 1,2 brotes por estaca, como se muestra en la tabla = 3.

Tabla 3

Prueba no paramétrica Friedman para número de br= otes por estaca y diámetro (mm) del cuello a la base del brote de B. graveolens a los 45 días de instalado el experimento (ddie)

Variables respuesta

T1 &= #8203;

T2&= nbsp;

T3&= nbsp;

T4&= nbsp;

T5&= nbsp;

T6&= nbsp;

T7&= nbsp;

T8&= nbsp;

T9&= nbsp;

T10 =

T11 =

T12 =

T˛&= nbsp;

p-valor

Número de brotes a los 45 ddie

6,33

6,83

10,00

4,17

6,33

5,67

4,17

6,33

7,50

7,00

6,00

7,67

0,71

0,7185

n.s.

Diámetro del cuello del brote (mm) a los 45 d= ías ddie

4,17

2,67

11,00

4,50

6,00

9,17

4,67

6,50

7,33

6,83

5,50

9,67

1,82

0,1108

n.s.

Promedio de Número de brotes a los 45 ddie =3D 1,2

Promedio Diámetro del cuello del brote (= mm) a los 45 días ddie =3D 11,4 mm

Fuente: Yagual (2022)

Longitud del b= rote

A diferencia de las dosis de auxinas AIB, los tipos de sustratos generaron un efecto significativo (pv< 0,005) en la longitud del brote de B. graveolens en las tres evaluaciones realizadas (15, 30 y 45 días de instalado el experimento), pre= sentaron promedios generales de 1,55; 1,63 y 1,62 cm, por evaluación respectivamente= como se muestra en la tabla 2.

La longitud de los brotes de las estacas plantadas en el sustrato tierra negra= 50% + arena de río 50% (A3) mostraron el mayor promedio (2,04 cm), a los 45 días después de instalado el experimento, siendo diferente estadísticamente que = la longitud de los brotes de las estacas plantadas en los sustratos tierra neg= ra 50% + estiércol de ganado vacuno 50% (A2) y tierra negra 50% + tamo de arroz 25% + arena de río 25% (A1) cuyos valores fueron de 1.38 y 1,46 cm respectivamente, siendo éstos últimos similares entre ellos, como se muestr= a en la figura 3.

Figura 3=

Medias de longitud del brote de B. graveolens, a los 50 días después de la instalación del experimento

Fuente: Yagual (2022)

Diámetro del cuello de los brotes

Al igual que en la variable número promedio de brotes por estaca, en diámetro = del cuello de los brotes, los tipos de sustrato y las dosis de AIB estudiados no generaron efecto importante a los 45 días después de la instalación del ens= ayo. La prueba de Friedman desarrollada presentó un p-valor de 0,1108. El promed= io general fue 11,4 mm de diámetro, como se muestra en la tabla 3.<= /span>

Discusión=

Durante el tiempo de la conducción de la investigación (50 días luego de la instala= ción del ensayo), no se observó una interacción clara entre el tipo de sustrato y las concentraciones de AIB en las variables de crecimiento evaluadas, así c= omo también no se observó efecto alguno de los niveles del factor axina, probab= lemente con un mayor tiempo de evaluación experimental se pueda encontrar dicha int= eracción y efecto, éste hallazgo es congruente con los reportados por Morillo et al. (2016), quienes utilizaron productos enraizantes de nombre comercial (Hormonagro 1 y Enraizador H.V) para la propagación asexual de B. graveolens, donde no lograron e= fecto alguno; así como también C= arranza et al. (2012), en su estudio de propagación de Tabebuya donnell-smithii. Si nos referimos al efecto de los tip= os de sustratos como factor individual, el mejor porcentaje de estacas prendid= as de B. graveolens alcanzado en e= sta investigación (sustrato tierra negra 50%+arena de río 50%) fue 23% menor a = los promedios presentados por Sánchez (2019), quien reportó un porcentaje de prendimiento= del 67%, a los 60 días después de establecer el ensayo de prendimiento de B. graveolens en etapa de vivero, usando una combinación de sustrato y enraizante natural en Portoviejo-Manabí. Los resultados alcanzados en esta investigación para la longitud del brote (cm), de estacas plantadas en sust= rato tierra negra 50%+arena de río 50%, son congruentes y superiores a los reportados por Mero et al. (2017), quienes en su estudio de la misma especi= e indican haber alcanzado una longitud media de brote de 1,45 cm con el tratamiento tierra de campo + tierra de guabo + arena de río + 8.000 ppm de auxina, dic= ho promedio es similar a las longitudes de brote de estacas plantadas en sustrato tierra negra 50%+estiércol de v= acuno 50% de esta investigación. En razón de que las evaluaciones de ésta investigación finalizaron a 45 y 50 días del establecimiento del experiment= o, es posible que el porcentaje de prendimiento de las estacas hubiera incrementado al evaluar un mayor tiempo, al igual que la longitud del brote, probablemente en un mayor tiempo de investigación su pueden observar interacciones entre los tipos de sustrato y las concentraciones de la auxin= a, experimentando diferencias estadísticas en las variables respuesta como acc= ión de las concentraciones de la hormona en los procesos fisiológicos del crecimiento inicial de B. graveolen= s. Los resultados alcanzados en esta investigación dan cierta orientación para= el diseńo y conducción de nuevos derroteros en investigaciones, donde se exami= nen concentraciones de auxinas y se prueben otras fuentes de fitohormonas que contribuyan al proceso de multiplicación clonal de B. graveolens, debido a que los porcentajes de prendimiento de estacas siguen siendo bajos, muy poco interesante para los viveristas.

Conclusiones<= /b>

ü No se evidenció un efecto claro de interacción entre el tipo de sustrato y las concentraciones de aux= inas (AIB), así como también del factor auxina en las variables de crecimiento d= asométrico temprano estudiadas.

ü El prendimiento promedio de estacas de Bursera graveolens (Kunt) Triana & Planch (Palo Santo= ) en el vivero agroforestal Dos Mangas del cantón Santa Elena, fue de 36,9 %, presentando el mayor porcentaje (51,88%) de esta variable el sustrato tierr= a negra 50% + arena de río 50%.

ü Se observó un efecto del factor tipo de sustrato, donde el sustrato tierra negra (50%) + arena de río (50%), experimentó un mayor promedio, sendo éste 50 y 100% superior con respecto a los sustratos tierra negra (50%) + estiércol de ganado vacuno (5= 0%) y tierra negra (50%) + arena de río (50%) respectivamente; así como también, presentó la mayor longitud del brote, superando entre el 40 y 54 % a los br= otes de las estas plantadas en los sustratos tierra negra (50%) + tamo de arroz (25%) + arena de río (25%) y tierra negra (50%) + estiércol de ganado vacuno (50%), respectivamente.

Referencias bibliográficas

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Yagual, A (2022). Evalu= ación de tres tipos de sustrato y tres dosis de auxinas en la propagación de esta= cas de Bursera graveolens (Kunt) Triana & Planch. [Tesis para obtener el título de Ingeniero Forestal, Escuela Superior Politécnica de Chimborazo]. Riobamba Ecuador.

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

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El artíc= ulo queda en propiedad de la revista y, por tanto, su publicación parcial y/o t= otal en otro medio tiene que ser autorizado por el director de la Revista Ciencia Digital.

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&nb= sp;

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file:///C:/715B22A1/03RaulRamos-Propagaciondearbolesdebursera_archivos/header.htm Content-Transfer-Encoding: quoted-printable Content-Type: text/html; charset="windows-1252"

= ISSN: 2773-7330

= Vol. 4 No. 3.2 pp= . 40 – 55. septiembre 2022

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Eureka Págin= a 40 | 1=

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Nota: T=3D Tratamiento; A=3D Sustratos, B=3D Concentración de AIB<= /o:p>

Fuente: Yagual (2022)=

Preparación de concentraciones de ácido indolbutírico (AIB)

Preparación de los sustratos

Desinfección de sustratos

Enfundado de sustrato

Identificación de plantas madre= de B. graveolens

Recolección de estacas

Repique de especie forestal B. graveolens<= o:p>

Vari= ables evaluadas

Prendimiento. - Para= el cálculo del porcentaje de prendimiento de las estacas se registró datos a l= os 50 días después de la instalación del experimento (ddie), y se aplicó la fórmula propuesta por Narváez (2021):

Supervivencia. - Para el cálculo del porcentaje de supervivencia de las estacas se registró los datos a los 50 días después de la instalaci= ón del experimento, se aplicó la sig= uiente fórmula:

Longitud del brote

Diámetro del cuello del brote<= /span>

Análisis estadístico

Prendimiento

Supervivencia=

Número de brot= es por estaca

Longitud del b= rote

Diámetro del cuello de los brotes

Fuente de Variación	gl	Prendimie= nto (%)	Supervive= ncia (%)	Número de brotes por estaca	Longitud = del brote (mm)
50 ddie	15 ddie	35 ddie	15 ddie	30 ddie	45 ddie
Bloque &nb= sp;	3	0,62		47,86		0,01		0,96		0,16		0,45		0,1=
Sustrato &= nbsp;	2	8,03	**	518,61	*	0,08	*	0,29	n.s.	1,71	**	2,64	**	2,17	**
Auxina &nb= sp;	3	0,47	n.s.	202,47	n.s.	0,01	n.s.	0,48	n.s.	0,38	n.s.	0,15	n.s.	0,38	n.s.
Sustrato*Auxina	6	0,47	n.s.	73,12	n.s.	0,01	n.s.	0,3=	n.s.	0,48	*	0,22	n.s.	0,33	n.s.
Error &nbs= p;	33<= /span>	0,75		110,61		0,01		0,27		0,18		0,30		0,35
Total &nbs= p;	47<= /span>									&nb= sp;
Promedio	36,90	68,80	1,48̴= 3;	1,35=	15,5̴= 3;	16,3=	16,2̴= 3;

Variables respuesta	T1 &= #8203;	T2&= nbsp;	T3&= nbsp;	T4&= nbsp;	T5&= nbsp;	T6&= nbsp;	T7&= nbsp;	T8&= nbsp;	T9&= nbsp;	T10 =	T11 =	T12 =	T˛&= nbsp;	p-valor
Número de brotes a los 45 ddie	6,33	6,83	10,00	4,17	6,33	5,67	4,17	6,33	7,50	7,00	6,00	7,67	0,71	0,7185	n.s.
Diámetro del cuello del brote (mm) a los 45 d= ías ddie	4,17	2,67	11,00	4,50	6,00	9,17	4,67	6,50	7,33	6,83	5,50	9,67	1,82	0,1108	n.s.
Promedio de Número de brotes a los 45 ddie =3D 1,2
Promedio Diámetro del cuello del brote (= mm) a los 45 días ddie =3D 11,4 mm