Gerardo Begué QuialaUsuario de Windows2842017-04-11T20:17:00Z2021-03-14T04:31:00Z2021-07-02T15:26:00Z1135341943901614522928153082-10.2.0.5871

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del arbolado urbano en el centro de la ciudad de GuantánamoBehavior of the urban woodland at Guantánamo downtown

Ernesto Henry Ferrer; Yuris Rodríguez-Matos; Yoandris Tamayo Santoya

Reserva Ecológica de

Hatibonico

, Guantánamo, Cuba. Universidad de Guantánamo, Cuba. Empresa Agroforestal Guantánamo UEB Guantánamo, Cuba.Correo(s) electrónico(s) ORCID: https: //orcid.org/: 0000-0003-1137-4211 https: //orcid.org/: 0000-0002-5032-6362 https: //orcid.org/: 0000-0002-8968-1329 Recibido: 20 de octubre de 2020 Aceptado: 26 de noviembre de 2020

Resumen

El trabajo se desarrolló en el centro de la ciudad de Guantánamo, con el objetivo de evaluar el comportamiento del arbolado urbano. Se realizó un inventario florístico mediante un muestreo aleatorio simple, donde

se utilizaron transeptos variables, evaluándose las especies de árboles existentes en el estrato arbustivo y arbóreo. Se evalúo el diámetro, altura, área basal, volumen, estructura horizontal, índice de valor importancia ecológica y secuestro de carbono.

e identificaron 21 familias, 33 especies y 835 individuos, las familias de mayor riqueza fueron:

Boraginaceae

Bignonaceae

y las especies de mejor comportamiento en CO

son:

Ehretia

tinifolial

L.,

Tabebuia

angustata

Britt

Palabras clave:

Arbolado urbano;

Estrategia;

Transeptos variables;

Muestreo aleatorio; Inventario florísticos.

Abstract

The work

was developed

in downtown of Guantánamo, with the objective of evaluating the urban behavior of the tree-lined one. He/she was carried out an inventory

florísti

, by means of a simple random sampling, where variable

transeptos

was used, being evaluated the species of existent trees in the stratum

arbustivo

and arboreal. You evaluate the diameter, height, basal area, volume, structures horizontal, index of value

ecological importance and kidnapping of carbon. 21 families, 33 species and 835 individuals were identified, the families of more wealth were:

Boraginaceae

Bignonaceae

, and the species of better behavior in CO

are:

Ehretia

tinifolial

L.,

Tabebuia

angusta

Britt.

Key word:

tree-lined urban, strategy, variable

transeptos

, random sampling and inventory

florísticos

Introducción

Las zonas urbanas en el mundo presentan enormes problemas ambientales y cada vez se hacen más agudos y están poniendo en duda la sostenibilidad de su desarrollo. Es por ello, que los árboles plantados en pueblos y ciudades, principalmente del tercer mundo, hacen un aporte positivo a las condiciones de vida actual y su potencial puede ser todavía mayor de acuerdo con la explicación de Jiménez (2009).

La silvicultura urbana tiene como finalidad el cultivo y ordenación de árboles para aprovechar la contribución actual y potencial que éstos puedan aportar al bienestar de la población urbana, desde el punto de vista fisiológico, sociológic

o y económico. Esta actividad representa una fusión entre la arboricultura, la horticultura ornamental, la arquitectura del paisaje y la ordenación forestal, en correspondencia con lo que aborda Sánchez (2003).

Moll

Gangloff

(2007), afirman que en la ac

tualidad se plantan árboles en las ciudades sin la debida planificación, sin una correcta preparación del suelo, sin una adecuada selección de especies, entre otras deficiencias. Todo ello, trae consigo árboles débiles y/o enfermos, mal anclados al terreno

que caen en cuanto se producen vientos fuertes, árboles podados drásticamente porque sus ramas estorban a los edificios y viviendas colindantes, raíces que invaden conducciones de agua, levantan pavimentos o agrietan muros; problemas éstos que podían ser

perfectamente previstos y subsanados con una adecuada planificación.

Cuba comienza a dar los primeros pasos en esta disciplina, y tiene como principal fortaleza la voluntad política para implementar un sistema sostenible, por lo que es uno de los aspectos importantes tratados en la Ley Forestal No 85 de 1998, su reglamento

y contravenciones. Existe un reglamento para la poda y la tala del arbolado urbano, regulaciones urbanísticas y ambientales que protegen al árbol en el entorno urbano; su proyección y protección forman parte de las estrategias urbanísticas territoriales. S

in embargo, todavía existen muchos caminos que recorrer, el árbol urbano necesita amor, protección y financiamiento, de acuerdo con lo que plantean Sosa,

et al.

(2011).

Las aéreas urbanas de la ciudad de Guantánamo no escapan a estas realidades, las espec

ies forestales muchas veces no reúnen las características necesarias para alcanzar la sostenibilidad en las diferentes zonas urbanas, de ahí que el objetivo esté orientado a evaluar el comportamiento del arbolado urbano de la ciudad centro de Guantánamo.

Desarrollo

Los datos fueron tomados en las arterias (calles) que comprende la zona central del municipio Guantánamo con una superficie de 167 462 m2; se levantaron 20 transeptos variables, según la metodología de Foster, et al. (1995), citado por Mostacedo y Fredericksenm (2000).El inventario fue realizado mediante un muestreo aleatorio simple, donde se utilizaron transeptos variables, evaluándose las especies de árboles existentes en el área que componen el estrato arbustivo, 1 a 4,99 m, y arbóreo mayor de 5 m, según Álvarez y Varona (2006), evaluando el diámetro, altura de la planta, área basal, volumen y la estructura horizontal, abundancia relativa, dominancia relativa, frecuencia relativa, índice de valor de importancia ecológica (IVIE) y secuestro de carbono.Diámetro (m): se midió a la altura del pecho con una cinta diamétrica.Altura (m): se le determinó la altura por el método ocular.Área basal (m2): se determinó mediante la forcipulación total de los árboles en las parcelas de pruebas y el cálculo se realizó por las fórmulas:

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Donde:

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= volumen medio de madera.

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= diámetro medio.

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= altura media.

H4sIAAAAAAAEC52RsUoDQRCG/5lc1FwCBisRkdNCY6GIvkBeQAuTWoxwouAZIYHjmnCPEFsfwKew uCqdta0QSGvAdELOmcmiIgHBPXbv35nZb2dnXp4HD7CRcZ1RUnl/RioKmwQw1s1blLXEKlUxicsU cZ7npvZp1dnKX3EVYWa8IvbthWWsQWJzoCr7TNSjzFRiRwIru5gKjlvdq2ZyFwLndvcHF6dD8QJ9 vZTlqzaS6KJ9g7guhonn10bZJH6TqQHAATxZ92SzJP9Dv0dHUE8t0bf8xRt6/sZ8Hhl3/IO7w8rd ddxA3qajb9XxJM/mdRR2gpMwDk7bUesW87lwXHL5vlLPCKHjptP/cX/nm9K71eEy8QWoHfGtI/oG uFpXsWi7J+shMW81kk43jNSop7SyszE79V1r9Ywl74K5PwFqTUirWAIAAA==

= coe

ficiente mórfico empírico.

Estructura horizontal del arbolado urbano

individuos de una especie

Abundancia relativa = ------------------------------------------------------------- x 100

# Total de individuos de todas las especies

Área basal de una especie

Dominancia relativa = ------------------------------------------------ x 100

Área basal de todas las especies

# De parcelas en la que ocurre una especie

Frecuencia relativa = ---------------------------------------------------------------- x 100

Total de ocurrencia en todas las parcelas

IVIE = Abundancia relativa + Dominancia relativa + Frecuencia relativa

Se determinó el total de individuos por clases

diamétricas

de las especies, agrupadas en clases

diamétricas

con su intervalo, ajustado a la metodología de Hoyos (2003).La información registrada se utilizó para estimar la biomasa y retención de carbono siguiendo la metodología descrita por Mercadet y Álvarez (2009). Todos los datos obtenidos fueron procesados con un fichero confeccionado en Microsoft Office Excel 2003, siguiendo los pasos siguientes:Carbono retenido en la biomasa:

Se realizó la conversión del volumen de madera en pie a biomasa del fuste, empleando la densidad de la madera seca reportada por especies.

BMF (t) = Volumen (m3) x Densidad básica de la especie (kg/m3) /1000 (1)

La biomasa correspondiente a las ramas y follaje (biomasa aérea), se calculó utilizando el Factor de Expansión de la Biomasa (FEB), la que tendrá como valor mínimo 1,74 y máximo 3,00, quedando:

BMA (t) = BMF (t) x FEB (FEB = e (3,213-0,506 ln BMF) (2)

La biomasa de las raíces (BMR) se estimó multiplicando la biomasa aérea por el valor por defecto 0,3.

BMR (t) = BMA x 0,3 (3)La biomasa total (BMT) fue calculada como la suma de los siguientes componentes:

BMT (t) = BMA (t) + BMR (t) (4)

El carbono retenido en la biomasa total (CRBT) se calculó utilizando la fracción de contenido de carbono en la madera (FCCM) determinada para las condiciones de Cuba.

CRBT (t) = BMT (t) x FCCM (5)

Esta operación (1, 2, 3, 4, 5) se realizó para cada especie y se promediaron los valores de todos los árboles. Conversión del carbono calculado a carbono equivalente (CO2e):

Para calcular cuánto representó el carbono retenido en toneladas de CO2 removido de la atmósfera, se multiplicó por 44/12 (3,67 t CO2), que es la relación existente entre el peso total de la molécula de CO2 (44) y del átomo de carbono (12), según Ramírez y Gómez (1999).

Los datos se procesaron a partir de programas estadísticos

BioDiversity

Pro, para realizar el anál

isis del Clúster y para introducir los datos, la confección de tablas y figuras se empleó el Microsoft Excel, además para la interpretación de los resultados obtenidos, Microsoft Word.

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La Figura 1 representa la cantidad de individuos por estratos, donde se puede apreciar que el estrato arbustivo es donde existe mayor riqueza con 637 y el arbóreo 198, además, la escasa presencia en el estrato arbóreo está dado por la poda que se le realiz

a en función de controlar la altura que alcanzan estos árboles para que sirva de mejoramiento y embellecimiento de la ciudad.

Figura 1.Total de individuos presentes en el arbolado urbano Fuente: Elaboración propiaEstos resultados coinciden con Jiménez (2009), al plantear que el manejo de árboles debe ser uno de los componentes principales de un programa de silvicultura urbana de las comunidades, donde los planes de manejo de árboles deben complementar las metas totales del programa de los árboles urbanos y de los parques de una comunidad, además se integran completamente las actividades de plantación y mantenimiento de los árboles, y los programas de emergencia.La tabla 1 muestra las familias de mayor y menor individuos de cada especies en el centro de la ciudad, donde se aprecia que las mayores son: Apoynaceae con 327 individuos, Rubiaceae 107, Euphorbiaceae 95; Magnonaceae 54, Bignonaceae 40 y Rutaceae con 28 y las menores: Sapotaceae, Myrtaceae, Akaniaceae, Combretaceae, todos con 1, y Moraceae con 2.

Familias

Especies

Mayor individuos

Familias

Especies

Menor individuos

Apocynaceae

327

Bignoniaceae

Rubiaceae

107

Clusiaceae

Euphorbiacea

Moringaliaceae

Magnonaceae

Euphorbiacea

Bignonaceae

Mimosaceae

Rutaceae

Arecaceae

Boraginaceae

Papillonaceae

Annonaceae

Moraceae

Rutaceae

Combretaceae

Malvaceae

Akaniaceae

Anacardiaceae

Myrtaceae

Simarubaceae

Sapotaceae

1Tabla 1. Familias de mayor y menor individuosFuente: Elaboración propia

Estas familias de mayor riqueza tienen efectos sobre el clima, situación que crea condiciones favorables para el bienestar humano proporcionando temperaturas más agradables y belleza escénica, haciendo contraste con un lugar desprovisto de vegetación. También Hoyos (2003), alcanzó resultados similares al plantear que estos árboles sirven para la protección contra la radiación solar al generar sombra, sus copas están diseñadas para captar la luz solar y al extenderse sombrean el piso, protegen la fauna, la flora inferior y al ser humano del impacto directo de los rayos solares, además, permiten la regulación de temperatura, donde las áreas verdes y los árboles son un elemento protector contra fluctuaciones de temperatura en los microclimas, ayudan a regularla, mantenerse fresco en verano y bloqueando el frío en invierno.

En la tabla 2 se observan las especies de mayor y menor índice de valor de importancia ecológica, donde las mayores están representada por:

Aleuritis

moluccana

35, 32 %,

Thevetia

peruviana

33, 41 %,

Ficus benjamina

16,91 %,

Morinda

citrifolia

15,29 %,

Salix

longipes

13,98 %,

Mangifera

indica

11,53 %,

Calophyllum

antillanum

10, 58 % y las menores:

Psidium

guajava

1,70 %,

Akania

belizensis

1,71 %,

Citrus

grandis

1,74 %.

El interés en el mane

jo de árboles riesgo en los bosques urbanos ha aumentado en años recientes debido a la seguridad y responsabilidad que resulta de prevenir accidentes. Reconocer árboles peligrosos y tomar acciones apropiadas

pueden

proteger propiedades y salvar vidas.

Mayor Índice de Valor

Importancia Ecológica (%)

Menor Índice de Valor de Importancia Ecológica (%)

Gossypium

barbadense

7,09

Akania

belizensis

1,71

Thevetia

peruviana

33,41

Annona

muricata

1,89

Salix

longipes

13,98

Psidium

guajava

1,70

Aleuritis

moluccana

35,32

Ficus

havanensis

1,86

Ficus benjamina

16,91

Citrus

reticulata

1,86

Citrus

reticulata

10,52

Citrus

grandis

1,74

Mangifera

indica

11,53

Manilkara

zapotilla

1,89

Citrus

aurantium

8,79

Jatropha

curcas

1,97

Morinda

citrifolia

15,29

Erythrina

glauca

1,80

Calophyllum

antillanum

10,58

Tamarindus

indica

1,88

Ehretia

tinifolial

9,50

Tabla 2. Especies leñosas de mayor y menor índice de valor ecológico en el arbolado urbano.Fuente: Elaboración propiaTambién coinciden con estos resultados Chiesura (2004), al dejar claro que los beneficios que proveen las áreas verdes urbanas pueden ser clasificados en ambientales, económicos y sociales, en materia ambiental se destaca la funcionalidad de los ecosistemas urbanos, lo cual incluye el hábitat de la fauna silvestre y la biodiversidad enriquecida, la regulación del microclima, el control de la erosión, de la contaminación del aire, del ruido y el incremento de la biodiversidad; en lo económico sirven como medio de subsistencia o de generación de ingresos y de materiales como alimento, leña, forraje, fibra, e incrementan el valor de la propiedad inmueble y en el ámbito social, contribuyen con la salud física y mental, reflejada en sensaciones como relajación, libertad, felicidad, inspiración, entre otras.

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En la Figura 2 se observa el total de individuos por clases

diamétrica

en el arbolado urb

ano, donde los diámetros mayores: la 34 (92 individuos), 36 (90), 30 (80), 24 (80), 22 (60), 32 (60), 30 (50), 38 (47), 2 (42), 4 (30), 20 (20) y 6 (20) y las menores son: la 14 (8), 8 (10), 12 (10), 10 (13) y 16 (15).Figura 2.Total de individuos por clases diamétricas en el arbolado urbanoFuente: Elaboración propia

Estos valores se deben a que no se manejan adecuadamente los árboles de mayor porte, dado a que no se realiza una debida planificación, sin una correcta preparación del suelo, sin la adecuada selección de especies, coincidiendo con estos resultados, Moll y Gangloff (2007), al plantear que cuando no se trabaja organizadamente, trae consigo, árboles débiles y/o enfermos, mal anclados al terreno que caen en cuanto se producen vientos fuertes, árboles podados drásticamente porque sus ramas estorban a los edificios y viviendas colindantes.

En la Figura 3 se observan los índices

dasométricos

medios de las especies de valor económico en el arbolado urbano, donde los mejores volúmenes de madera en m

on:

Ehretia

tinifolia

14,34 m

Tabebuia

angustata

9,72 m

Simaruba glauca

9,38 m3,

Calophyllum

antillanum

5,87 m

Peltophorum

ferrugineum

3,94 m

Delonix

regia

3,76 m

Albizia

lebbeck

2,60 m

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Figura 3. Comportamiento del volumen de las especies forestales de valor económicoFuente: Elaboración propiaCon estos resultados coinciden Sosa,

et al. (2011), al plantear que la finalidad del ordenamiento de los árboles para aprovechar la contribución actual y potencial que estos pueden adoptar al bienestar de la población urbana, tanto desde el punto de vista fisiológico como sociológico y económico, donde incluye también los hábitats de las especies animales silvestres, además de las oportunidades de esparcimiento al aire libre, el diseño del paisaje, la recuperación de desechos en el ámbito municipal, el cuidado de los árboles en general y la producción de fibra de madera como materia prima.

Las especies del estudio, tabla 3, retienen un total de 6 496

,48 t de carbono, a razón de 6,74 t por individuo, sobresaliendo en su aporte el falso nogal, roble prieto y roble blanco con una retención de 2 106,32, 1 065,39 y 598,89 t de carbono respectivamente. El resto de las especies mantiene una retención entre l

as 0,65 y 307,59 t, constituyendo estas especies en su conjunto, un almacén de carbono, lo que a su vez permite se les considere como una estrategia de conservación y de reducción de CO

Nombres Científicos

Total de especies

Volumen

)

Densidad

(kg / m

)

Biomasa

Fuste (t)

FEB

Biomasa

aérea (t)

Biomasa

raíces (t)

Biomasa

Total (t)

Fracción de Carbono

Carbono total en

la Biomasa (t)

Albizia

lebbeck32,604901,271,742,220,662,8846,37133,54

Gossypium

barbadense120,024900,011,740,010,000,0247,080,90

Terminalia

catappa10,818300,671,741,160,351,5147,3871,69

Annona

cherimola80,074900,031,740,060,020,0847,083,54

Azadirachta

indica70,516100,311,740,540,160,7049,7435,04

Thevetia

peruviana3260,774900,381,740,660,200,8647,0840,28

Pieris

cubensis650,114500,051,740,090,030,1247,085,50

Akania

belizensis10,024900,011,740,020,010,0247,081,06

Juglans

jamaicensis9141,3749020,271,7435,2710,5845,8545,942106,32

Peltophorum

ferrugineum33,947362,901,745,051,516,5646,88307,59

Delonix

regia33,767132,681,744,671,406,0746,88284,50

Simarouba

glauca109,385955,581,749,712,9112,6346,88592,01

Annona

muricata40,166500,111,740,190,060,2447,0811,42

Psidium

guajava10,004900,001,740,000,000,0047,080,14

Crescentia

cujete70,166330,101,740,180,050,2346,8810,78

Ficus

crocata30,233900,091,740,160,050,2046,889,50

Ficus benjamina540,086500,051,740,090,030,1247,085,57

Citrus

limon150,014900,011,740,010,000,0247,080,75

Citrus

reticulata50,074900,031,740,060,020,0847,083,54

Mangifera

indica113,475501,911,743,321,004,3247,08203,33

Moringa

oleifera50,324900,161,740,270,080,3547,0816,64

Citrus

aurantium130,027100,011,740,020,010,0347,081,31

Citrus

sinensis20,015900,011,740,010,000,0147,080,65

Manilkara

zapotilla10,819100,731,741,270,381,6647,0878,03

Morinda

citrifolia420,904900,441,740,770,231,0047,0847,12

Calophyllum

antillanum75,877594,451,747,752,3310,0848,75491,16

Roystonea

regia31,939601,851,743,220,974,1946,88196,25

Jatropha

curcas40,313000,091,740,160,050,2146,889,89

Erythrina

crista30,056120,031,740,060,020,0746,883,50

Tabebuia

angustata409,725555,401,749,392,8212,2049,07598,89

Ehretia

tinifolia1814,346939,941,7417,295,1922,4847,421065,79

Tamarindus

indica10,557500,411,740,720,210,9347,0843,80

Cordia

alliodora50,946990,661,741,140,341,4946,0268,44

Total

769

103,3127

60,6564

105,54

31,66

137,2

6448,47

Por individuo

0,1077

0,0634

0,11

0,03

0,14

6,74Tabla 3. Cálculo de carbono retenido en el arbolado urbano del centro de la ciudad de Guantánamo Fuente: Elaboración propiaLeyenda: FEB (Factor de expansión de la biomasa)Se ha estimado que las plantaciones han originado una absorción de 6 496,48t de carbono, contribuyendo con ello a disminuir el exceso de CO2 de la atmósfera, reflejado este tributo en 23 842,08 t CO2 equivalente, no emitidas a la atmósfera. Estos resultados permiten validar el criterio universal de que los bosques son sumideros naturales de carbono, como lo ha defendido Brown (2002), quedando demostrada la importancia de las especies forestales, por su aporte a la retención de carbono.

Conclusiones

Las familias de mayor riqueza de especies fueron:

Apoynaceae

Rubiaceae

Euphorbiaceae

Magnonaceae

Bignonaceae

Rutaceae

Las especies de mejor comportamiento en CO

son:

Ehretia

tinifolia

Tabebuia

angustata

Calophyllum

antillanum

Simarouba

lauca,

Peltophorum

ferrugineum

Delonix

regia

Juglans

jamaicensis

, en el centro de la ciudad de Guantánamo.

Referencias bibliográficas Álvarez, P. A. y Varona, J. C. (2006). Silvicultura. La Habana: Editorial Félix. Brown, S. (2002). Measuring carbon in forests: current status and future challenges. Environmental Pollution 116: 363-372 Disponible en: http: /www.winrock.org/ecosystems/files/2002ForestCarbon.pdfGaceta Oficial de la República de Cuba. (1998). Ley Forestal No 85. La Habana, Cuba. Chiesura, A. (2004). The role of urban parks for the sustainable city. Review Landscape and Urban Planning.Hoyos, M. F. (2003). Propuesta metodológica para la valoración económica del árbol urbano. Trabajo de diploma. Universidad Nacional de Colombia.Jiménez, M. (2009). Desarrollo de la Silvicultura Urbana en Cuba. Perspectivas. Revista Agricultura Orgánica Vol. 3. Disponible: http://

www.actaf.co.cu/revistas/revista_ao_95...3/18%20Perspect

ivas.pdf. Mercadet, A. y A. Álvarez. (2009). Metodología para establecer la línea base de retención de carbono en las Empresas Forestales Integrales de Cuba, efecto de cambios globales sobre el ciclo de carbono. RED CYTED 406RT0285. Efecto cambios globales sobre los humedales de Ibero América. Moll, G y Gangloff, D. (2007): Silvicultura urbana en los Estados Unidos. Disponible en: http://www.fao.org/documents/show_cdr.asp?url_file=/docrep/s1930S/s1930s05.htm. Moll, G y Gangloff, D. (2007): Silvicultura urbana en los Estados Unidos. Disponible en: http://www.fao.org/documents/show_cdr.asp?url_file=/docrep/s1930S/s1930s05.htm. Mostacedo, B. y Fredericksenm, T. S. (2000). Manual de Métodos Básicos de Muestreo y Análisis en Ecología Vegetal. Proyecto de Manejo Forestal Sostenible, Santa Cruz, Bolivia: Editorial El País.Ramírez, O. A y M. Gómez. (1999). Estimación y valoración económica del almacenamiento del carbono. Revista Forestal Centroamérica 27 (2), pp. 17 -22, julio-septiembre.Sánchez, J. M. (2003). Algunas consideraciones sobre el árbol en el diseño urbano. La Habana: Editorial Félix Varela.Sosa, A., Yenia, M., Pérez, A., Valdez, E. (2011). Diagnóstico de la situación del arbolado urbano en la Ciudad de Guisa. Revista Forestal Baracoa vol. 30 (1), p.12.

PAGE

Ernesto Henry,

Yuris

Rodríguez,

Yoandris

Tamayo: Comportamiento del arbolado urbano en el centro de la

PAGE Vol. 6, No. 12, abril-junio, año 2021 PAGE \* MERGEFORMAT96

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http://cienciayprogreso.cug.co.cu Vol. 6, No. 12, abril-junio, año 2021 PAGE \* MERGEFORMAT86