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Com= posición y diversidad de especies forestales en el páramo Machay<= /span>- Chimborazo- Ecuador Tit= ulo (Tip= ografía: Time New Roman 18 en minúsculas)

 

TitCom= position and diversity of forest species in Machay param= o - Chimborazo-Ecuadorle (Typ= ography: Time New Roman 14 en = minúsculas y cursivas)

=  

= May= ra Janeth Paguay Tingo Autor. [1], = Dan= iel Arturo Román Robalino Autor. [2] &a= mp;, Jor= ge Patricio Cevallos Rodríguez Aut= or. <= /span>[3] & Dos nombres y apellidos. [4]

 

Recibido: 19-04-2019 / Revisado: 25-05-2019 /Aceptado: 28-06-2019/ Publicado: 15-07-2019

 

               Re= cibido: 10-02-2019 / Revisado: 15-02-209 /Aceptado: 04-03-2019/ Publicado: 14-06-20= 19=

=  

 Abstract.                   DOI: https://doi.org/10.33262/ci= enciadigital.v3i3.1.706

 =                                    DO= I: 

The present work aims to inventory the floristic diversity of the Machay paramo ecosystem, located in the Ilapo parish, = Guano Canton, Chimborazo Province, field trips were made to = georeference the territory and install five transitory plots of 25 m2 with 4 subplots of= 1 m2, from which the data record was obtained for the identification, quantification and analysis of floristic diversity. In the inventory were recorded: 40 samples of terrestrial vascular plants, corresponding to 16 botanical families, 36 genera and 40 species, in addition a sample of lichen and moss of unknown family, genus and species was collected, which adds 42 = plant samples. The inventory allowed to determine that the moss is the most representative species in all the plots and quadrants. According to the Sha= nnon index, plot five possesses high diversity that is corroborated with the res= ults obtained from the Simpson index, results that showed high values in relatio= n to the other plots. The results of Sorensen show that the plots (P3 vs P5 and = P1 vs P5) are very similar to each other. Concluding that this type of research contributes to the making of strategic decisions that allow the conservatio= n, protection, and management of the MACHAY paramo ecosystem through the flori= stic inventory.

 

Typography: Time New Roman 12 line spacing 1.= 15 (150 - 300 words).

 

Keywords: Indices, Inventory, Shannon-Weav= er, Simpson, Sorensen.<= /span>Typography: Time New Roman 12 line spacing 1.= 15. (4 – 6 words).

 

            Resumen.

 <= /span>

El presente trabajo tiene por objetivo invent= ariar la diversidad florística que posee el ecosistema páramo Machay, ubicado en la parroquia Ilapo, Cantón Guano, Provincia de Chimborazo, se realizaron salidas de campo para georreferencia= r el territorio e instalar cinco parcelas transitorias de 25 m2 con 4 subparcela= s de 1 m2, de las que se obtuvo el registró de datos para la identificación, cuantificación y análisis de la diversidad florística. En el inventario se registraron: 40 muestras de plantas vasculares terrestres, correspondientes= a 16 familias botánicas, 36 géneros y 40 especies, además se colectó una mues= tra de liquen y musgo de familia, género y especie no identificados lo que suma= n 42 muestras vegetales. El inventario permitió determinar que el musgo es la especie más representativa en todas las parcelas y cuadrantes. De acuerdo al índice de Shannon, la parcela cinco posee diversidad alta que se corrobora = con los resultados obtenidos del índice de Simpson, resultados que arrojaron valores altos en relación a las demás parcelas. Los resultados de Sorensen demuestran que las parcelas (P3 vs P5 y P1 v= s P5) son muy similares entre sí. Concluyendo que este tipo de investigaciones contribuyen a la toma de decisiones estratégicas que permitan la conservaci= ón, protección, y manejo del ecosistema páramo MACHAY a través del inventario florístico.

 =

Tipografía: T= ime New Roman 12, interlineado 1.15 (150 - 300 palabras).

 

Palabras claves: Tipografía: <= /b>Índ= ices, Inventario, Shannon-Weaver, Simpson, Sorensen.<= /ins>: T= ime New Roman 12, interlineado 1.15 (4 – 6 palabras).

 

Intro= ducción.

 =

Los páramos forman parte de una notable biodiversidad a escala de ecosistemas que se presentan en el Ecuador gracia= s a tres factores principales: la situación ecuatorial, la presencia de la cordillera de los Andes y otras sierras menores, la existencia de una fuente húmeda amazónica y de varias corrientes frías y cálidas frente a las costas (Medina & Mena, 2001).

Los páramos ecuatorianos se han caracterizado= por una elevada biodiversidad y un alto endemismo lo cual ayuda a la formación = de más de un ecosistema (Baquero, Sierra, Ordóñez, & Tipán, 2004).

Las mayores presiones sobre los páramos fuero= n a partir de los años de 1960, el agotamiento de las tierras y el fracaso de la redistribución de tierras con la reforma agraria en los años 1964 y 1973 que conllevo a ejercer una creciente presión demográfica especialmente de la población campesina sobre estos ecosistemas altos andinos.=

Es por esto que el páramo es un ecosistema, d= onde se desarrollan un sinnúmero de relaciones entre seres vivos y un medio ambi= ente con características especiales como: temperatura, humedad, radiación solar, presión atmosférica, otros (Bernal, Sánchez, & Zap= atta, 2000).

Hoy en día el ecosistema páramo no es valorado adecuadamente, en el caso particular del páramo Machay= perteneciente a la regional Ilapo-Guano, se con= oce que el territorio aporta principalmente agua para el consumo del ser humano= a través de los sistemas de agua entubada que beneficia a varias comunidades del Can= tón Guano. La Regional Ilapo-Guano en su afán de un= ir esfuerzos para la conservación del agua, se han aliado con juntas administradoras de agua potable de otras jurisdicciones parroquiales y han conformado la Pre-Corporación de Regionales en Defensa del Igualata que agrupa 20 comunidades, estas comunidades han reconocido la importancia = de este ecosistema como regulador hídrico. En este espacio cabe mencionar que = al momento de iniciar la investigación no se contaba con un monitoreo de la fl= ora de este páramo, mucho menos con el valor de importancia florística que este territorio presenta (Plan de Desarrollo y Ordenamiento Territorial de la Parroquia de ILAPO (PD Y OT), 2016).

Debido a la importancia= de este ecosistema y los pocos datos existentes, se ejecuta el presente trabajo de investigación con el fin de generar información sobre la diversidad de este lugar, y a partir de los resultados valorar la riqueza florística del sitio, para que sea un instrumento cuya información permita la toma de decisiones = y se pueda actualizar el Plan de Manejo existente.

 <= /span>

·Número de páginas del artículo entre 10 y 22 paginas

<= span class=3DmsoDel> 

= Tipografía= M= etodologia= .=

Car= acterizac= ión del lugar

El = Páramo Machay se encuentra ubicado en la Parroquia Ilapo - Cantón Guano - Provincia de Chimborazo este p= áramo se considera como una zona de recarga hídrica pues forma parte de la Region= al Ilapo – Guano, además este sitio de estudio pertenece= a la demarcación hidrográfica del Pastaza, sub cuenca del río Chambo.

 <= /span>

Tabla 1. = Ubicación geográfica

L= UGAR DE ESTUDIO=

L= ONGITUD=

L= ATITUD<= /span>

REGIONAL=

769488=

9817752<= /span>

Fue= nte: Inv= estigación primaria, 2018

 

Car= acterísticas climáticas. - La zona se caracteriza p= or tener la presencia de neblina, con poca precipitación.= Te= mperatura media: 11°C= , m= áxima: 25°C= y = mínima: 1°C<= /span>

Pen= dientes de 10% hasta 75%= (P= lan de Manejo de los Recursos Naturales de la Regional Ilapo<= /span>-Guano 2014, pg.11= ).

El = rango de precipitación en todo el páramo, está entre 700 y 3.000 mm por año.= La= humedad relativa tiene un rango entre 25 y 100%, con un promedio de 70-85%<= /span> <= /span>(Alvarado & Gavila= nes, 2012).

Cla= sificación ecológica. -= Según el <= /span>Sis= tema de Clasificación de los Ecosistemas del Ecuador, realizado por el Ministerio del Ambiente en= el año 2012 po= demos distinguir 3 zonas de vida:

Bos= que siempre verde montano: 2000 – 3000 msnm=

Bos= que siempre verde montano alto: 3000 – 3700 msnm

Mon= tano alto superior de páramo: 3700 – 4200 msnm., = (Ministerio del Ambien= te del Ecuador.[MAE], 2013).

Zon= ificación. - La georreferenciación se realizó en compañía de dirigentes de la Pre-Corporación, las coordenadas fueron tomadas con un GPS garmín. Las coordenadas registradas se ingresaron en el programa Arcgis 10.1 en el cual también se ingresó la Orto- foto Guano. Con todos los datos ingresados se dibujó el polígono de la zona de estudio y se ubicó las coordenadas de cada parcela.

 

Instalación de Parcelas

 =

Par= a la instalación de parcelas se tomó en cuenta la metodología propuesta por (Pauli, y otros, 2015)= para el Proyecto Gloria tomando en cuenta algunas modificaciones para adaptar a los páramos andinos= .

Fue= ron instaladas 5 parcelas transitorias de 5mx5m (25m2), = con una distancia de 300m cada de ellas. Cada cuadrante se dividió en sub-cuadrantes de 1m X 1m, las observaciones de veget= ación se llevaron a cabo únicamente en los cuadrantes de las esquinas ya que los = otros se alteran con el pisoteo, en la recolección de las muestras y datos. Se ob= tuvo datos de vegetación de los 20 cuadrantes de 1m X 1m.

5 m

5 m

5 m

 

 =


1 m =

 

 

 

 

 

 =

 =

 


Figura  1 .- = División de parcelas<= span style=3D'font-size:8.0pt !msorm;line-height:115% !msorm;font-family:"Calibr= i",sans-serif !msorm; mso-bidi-font-family:Calibri !msorm'>

En = la figura 1. Se indica cada uno de los cuadrantes de 1m x 1m, los mismos que se subdividieron en celdillas de 0.1m x 0.1m para lo cual se utilizó un armazó= n de madera y un enrejado de hilos que delimitaron un total de 100 celdillas esto permitió la toma de datos de cada subparcela para su posterior análisis.

&nb= sp;

&nb= sp;

 =

1 m

0.1 m

 =


1= <= o:p>

2= <= o:p>

3= <= o:p>

4= <= o:p>

5= <= o:p>

6= <= o:p>

7= <= o:p>

8= <= o:p>

9= <= o:p>

1= 0<= o:p>

2= <= o:p>

3= <= o:p>

4= <= o:p>

5= <= o:p>

6= <= o:p>

<= span style=3D'mso-spacerun:yes'> 7<= o:p>

8= <= o:p>

9= <= o:p>

1= 0<= o:p>

                                                 =                                                      

Figura  2.- <= /b>Diseño de cuadrantes<= b>

Extracción de especies y herborización

Las= especies vegetales que se recolectaron en la zona de estudio fueron herborizadas en = el mismo lugar con papel periódico y a su vez prensadas para su transportación, las especies fueron secadas manualmente bajo sombra y prensadas, se cambió = de papel periódico cada día para evitar putrefacción de las muestras o que est= as se llenen de hongos.

Las= muestras fueron identificadas en el herbario de la ESPOCH, a su vez el herbario emit= ió un certificado de reconocimiento de muestras vegetales.=

 =

Tab= ulación de datos

Se = procedió a contar y registrar los datos en el cuaderno de campo; se registró el número= de individuos, altura y cobertura de cada especie, con el fin de obtener datos cuantitativos de la vegetación. Las especies que no se pudieron identificar= en el campo fueron registradas con códigos e identificadas en el herbario de l= a ESPOCH. Ya reconocidas las especies se procedió a realizar el listado con sus respectivos datos para los cálculos respectivos.=

 

Cál= culo de datos

Con= la información obtenida se determinaron valores de importancia por especie y familia, densidad relativa, frecuencia relativa e índices de diversidad.

IVI= : (Índice de valor de importancia)

IVI= =3D DR + FR

DR = =3D Densidad Relativa

DR= =3D (Número de individuos de una especie /<= /ins> nú= mero total de individuos en el muestreo) X <= /ins>100= .

FR = =3D Frecuencia Relativa

FR = =3D (Número de unidades de muestreo con la especie / <= /ins>Sum= atoria de las frecuencias de todas las especies) X <= /ins>100=

Par= a este estudio el número de unidades de muestreo son 20 cuadrantes de 1 m2.<= o:p>

D = =3D áre= a de cobertura de la especie / ár= ea muestreada

Dr<= /ins> = =3D (Áre= a de cobertura de la especie / <= /ins>áre= a de cobertura de todas las especies) X 10= 0

Índ= ice de Shannon - Weaver

Don= de:

H=3D Índice de Shannon =

S =3D Número de especie= s

Pi = =3D Proporción del número total de individuos que constituyen la especie<= /span> (Velásquez, 1997).

Índ= ice de Simpson

Donde:

ISD=3D Índice de Simpso= n

Pi =3D Proporción del n= úmero total de individuos que constituyen la especie.

Los índices de Shannon y Simpson toman en consideración tanto la riqueza como la equitividad de especies.  <= /span>

 

Tabla 2. Interpretación de la diversidad:

Valores <= span style=3D'mso-prop-change:Admin 20190722T2207'>

Interpretación <= /b><= span style=3D'mso-prop-change:Admin 20190722T2207'>

0,00 – 0,35<= o:p>

Diversidad baja= <= o:p>

0.36 – 0.75<= o:p>

Diversidad mediana<= o:p>

0.76 – 1,00<= o:p>

Diversidad alta= <= o:p>

Fuente:

Índice de = Sorensen

Donde:

Iss= =3DÍndice de Sorensen

A =3D Número de especie= s en el sitio 1

B =3D Número de especie= s en el sitio 2

C = =3D Número de especies similares presentes en ambos sitios A y B.

&nb= sp;

&nb= sp;

 =

Tab= la 3. Interpretación de Similitud

V= alores<= o:p>

I= nterpretación<= o:p>

0= ,00 – 0,35<= o:p>

Disimiles=

0= ,36 – 0,70<= o:p>

Medianamente similares<= /span>

0= .71 – 100<= o:p>

Muy similares

Fue= nte: <= w:Sdt Citation=3D"t" ID=3D"-859037317" w:insAuthor=3D"Admin" w:insDate=3D"2019-0= 7-22T22:03:00Z" w:endInsAuthor=3D"Admin" w:endInsDate=3D"2019-07-22T22:03:00Z">.

Tipografía<= span style=3D'font-size:11.0pt !msorm;line-height:115% !msorm;font-family:"Baske= rville",serif !msorm; mso-bidi-font-family:"Times New Roman" !msorm;mso-bidi-theme-font:minor-bid= i !msorm'>: T= ime New Roman 12, interlineado 1.15

R= esultados.= <= span class=3DmsoIns>

Esp= ecies registradas en el área de estudio

Tabla 4. Vegetación Registrada= en el Páramo Machay

FAMILIA<= /span>

NOMBRE <= /span>C= IENTÍFICO

Ge

Sp

1=

Apiaceae=

Azorella= = pedunculata = (Spreng.= ) Mathias<= /span> = & Constance.=

2=

Apiaceae=

Daucus  montanus= = Humb = et= Bonpl.= ex spreng

3=

3=

3=

Apiaceae=

Eryngium= = humile<= span style=3D'mso-spacerun:yes'>  Cav

4=

Rosaceae=

Lachemilla = orbiculata = (Ruiz & P= av.= ) Rydb.=

1=

1=

5=

Fabaceae=

Lupinus<= /span><= span style=3D'mso-spacerun:yes'>  sp.=

2=

2=

6=

Fabaceae=

Trifolium = repens = L.

7=

Poaceae<= /span>

Festuca<= /span> = cf

8=

Poaceae<= /span>

Calamagrostis = intermedia (J. Presl) Steud.=

9=

Poaceae<= /span>

Bromus = pitensis= <= span style=3D'mso-spacerun:yes'>  Kunth<= /span>

10

Poaceae<= /span>

Holcus = lanatus<= /span> = L.

5=

6=

11

Poaceae<= /span>

Dactylis= = glomerata = L.

12

Poaceae<= /span>

Festuca<= /span> = sp.=

13

Cyperaceae

Carex = bonplandii = Kunth

1=

1=

14

Plantaginaceae<= /span>

P= lantago = linearis= = var.=

1=

2=

15

Plantaginaceae<= /span>

Plantago= = seríce= a = Ruíz = & Pav.

16

Asteraceae

Hypochaeris = sessiliflora = Kunth

17

Asteraceae

Baccharis = caespitosa = (Lam.) Pers<= o:p>

18

Asteraceae

Gnaphalium = elegans<= /span> = Kunth.

19

Asteraceae

Taraxacum = officinale = Weber

20

Asteraceae

Werneria= = nubigena= = Kunth

21

Asteraceae

Lasiocephalus = ovatus = Schltdl<= /span>.=

11

11

22

Asteraceae

Gynoxys<= /span> = buxifolia = (Kunth) Cass<= o:p>

23

Asteraceae

Bidens = andicola= = Kunth

24

Asteraceae

Casiocaptalus<= span style=3D'mso-spacerun:yes'>  (Schltdl<= /span>.= ) B. Nord

25

Asteraceae

Erigeron= <= span style=3D'mso-spacerun:yes'>  ecuadoriensis<= span style=3D'mso-spacerun:yes'>  Hieron

26

Asteraceae

Asteracea

27

Melastomataceae=

Brachyotum = ledifolium = (Desr.) Triana

1=

1=

28

Ericaceae

Pernettya = prostrata<= span style=3D'mso-spacerun:yes'>  (Cav.= ) DC

29

Ericaceae

Vaccinium = floribundum = Kunth

3=

3=

30

Ericaceae

Disterigma = empetrifolium = (Kunth) Drude.

31

Hypericaceae

Hipericum = laricifolium = Juss.=

1=

1=

32

Lycopodiaceae

Huperzia= = crassa = (Humb.= & Bonpl.= Ex Willd.= )

1=

1=

33

Polygonaceae

Rumex = acetosella = L.

1=

1=

34

Geraniaceae

Geranium= = laxicaule = R. Knuth

1=

2=

35

Geraniaceae

Geranium= = L.

36

Ranunculaceae

Ranunculus = praemorsus = Humb.= , Bonpl.= & Kunth ex DC.

1=

1=

37

Gentianaceae

Gentiana= <= span style=3D'mso-spacerun:yes'>  sedifolia = Kunth

38

Gentianaceae

Gentianella = cerastioides = (K= unth)= F= abris.

2=

2=

39

Caprifoliaceae<= /span>

Phyllactis = rigida = (Ruiz & P= av.= ) Pers.

2=

2=

40

Caprifoliaceae<= /span>

Valeriana microphylla = Kunth

41

Liquen

Indeterminada 1=

1=

1=

42

Musg= o

Indeterminada

1=

1=

TOTAL 18=

36

40

Fue= nte: Inv= estigación primaria, 2018.

 

En = el estudio realizado se registraron los datos de las especies vegetales de 20 cuadrant= es de 1m2 <= /ins>cad= a uno, estos cuadrantes están ubicados en 5 parcelas transitorias de 5m X 5m las cuales están distribuidas al azar en la zona de estudio. Se colectó 40 mues= tras de plantas vasculares terrestres, correspondientes a 16 familias botánicas,= 36 géneros y 40 especies, además también se colectó 1 liquen y 1 musgo de fami= lia, género y especie no identificado lo que suman 42 muestras vegetales las cua= les han sido identificadas en el Herbario de la ESPOCH.

 

Tabla 5.= Resumen de la composición Florí= stica de las 5 parcelas=

Parcelas

P. - 01

P. - 02

P. - 03

P. - 04

P. - 05

Familias

1= 5<= o:p>

1= 4<= o:p>

1= 6<= o:p>

1= 4<= o:p>

1= 4<= o:p>

Géneros =

2= 4<= o:p>

2= 3<= o:p>

3= 0<= o:p>

2= 5<= o:p>

2= 7<= o:p>

Especies=

2= 7<= o:p>

2= 3<= o:p>

3= 0<= o:p>

2= 5<= o:p>

2= 9<= o:p>

Fue= nte: Inv= estigación primaria, 2018.

 =

En = la tabla 5, se aprecia mayor riqueza en la parcela 03. Con 16 familias, 30 géneros y= 30 especies. Se acota a este resultado lo que el autor Pujos, (2013) menciona = que los sitios menos perturbados son más ricos en especies, en los resultados obtenidos la parcela 03 presenta 16 familias y 30 especies lo que según los resultados es la parcela con más familias y especies. Por otro lado, la par= cela 02 presenta 14 familias y 23 especies siendo la parcela que menos diversidad tiene lo cual se explica por la presencia de ganado vacuno, incendios y otr= as perturbaciones provocadas por el hombre. No obstante, la parcela 05 también presenta 14 familias, pero el número de especie es mayor que en las parcelas 01, 02, 04, lo cual cumple con la lógica de menor perturbación mayor divers= idad mencionada anteriormente. Cabe reconocer que esta zona de estudio se encuen= tra en proceso de recuperación por las actividades antrópicas del hombre mencionadas anteriormente.

 

Des= cripción del Índice de Valor de Importancia (I.V.I) de especies de las cinco parcela= s

Las= especies con mayor valor de importancia en este caso es el Musgo (Indeterminada) con= un 30% esta especie se encuentra en forma de un tipo de colchón en asociación = con la mayoría de especies y sola formando grandes cubiertas esponjosas sobre el suelo de páramo, la especie Bra= chyotum led= ifolium (<= /ins>Des= r.) = Triana, y Gyn= oxys bux= ifolia (K= unth) Cass con= 5 %y 4,25 % es la segunda especie dominante en este ecosistema lo cual concuerda con = el estudio realizado por (Caluña V, 2017) quien concuerdan con lo dicho por Freire F, 2004 en tercer lugar tenemos a = Cal= amagrostis in= termedia (J.P= resl) <= /ins>Ste= ud co= n el 3.18% est= a especie es propia de los páramos de pajonal según la clasificación de Proyecto Pára= mo (1999). Por otra parte, la especie Las= iocephalus ova= tus Sch= ltdl, es= propia de los páramos sin embargo en este sitio de estudio los individuos son muy poc= os, a la igual que otras especies también registradas en este ecosistema.=

 =

Índ= ice Shannon-Weaver

Tabla 6. Descripción del índice de Shannon-Weaver=

-= de Parcela<= o:p>

V= alor Calculado<= o:p>

V= alor Referencial<= o:p>

I= nterpretación

01

0.613

0.36 – 0.75

Diversidad Media

02

0.127

0.0 – 0.35

Diversidad Baja=

03

0.652

0.36 – 0.75

Diversidad Media

04

0.229

0.0 – 0.35

Diversidad Baja=

05

1.0

0.76 – 1.00

Diversidad Alta=

Fuente: Inv= estigación secundaria, 2018.

 

Descripción de resultados Índice de Diversida= d de Shannon-Weaver

Los resultados obtenidos del Índice de diversidad de Shannon-Weaver en las 5 parcelas demuestran que la parcela 02 y 04 tienen una diversidad baja de acuerdo a la tabla de interpretación mencionada por (Smith & Smith, 200= 7) el cual tiene un rango de 0.0 – 0.35 el cual conc= uerda con los resultados obtenidos. Mientras que las parcelas 01 = y 03 tienen una diversidad media de acuerdo a la tabla de interpretación mencion= ada por (Sm= ith & Smith, 2007) el cual tiene un rango de 0.36 – 0.75valores que = se encuentran como extremos de los resultados obtenidos luego de aplicar la fórmula mencionada por (Londo,J. 2018). La parc= ela 05 fue la parcela que mayor índice de diversidad tuvo pues según los resultados obtenidos y comparados con la tab= la de interpretación mencionada por (Smith & Smith, 200= 7) es una parcela que posee una diversidad alta dentro de esta zona de estudio.

 =

Índ= ice de Simpson

Tabla 7. Des= cripción del Índice de Simpson

- de Parcela<= o:p>

Valor Calculado= <= o:p>

Valor Referencial<= o:p>

Interpretación<= /span><= o:p>

1= <= o:p>

0.25<= o:p>

0.0 – 0.35<= o:p>

Diversidad Baja= <= o:p>

2= <= o:p>

0.034<= o:p>

0.0 – 0.35<= o:p>

Diversidad Baja= <= o:p>

3= <= o:p>

0.222<= o:p>

0.0 – 0.35<= o:p>

Diversidad Baja= <= o:p>

4= <= o:p>

0.073<= o:p>

0.0 – 0.35<= o:p>

Diversidad Baja= <= o:p>

5= <= o:p>

0.456<= o:p>

0.36 - 0.75<= o:p>

Diversidad Media<= o:p>

Fue= nte: Investigación secundaria, 2018.

 

Des= cripción de Resultados del Índice de diversidad de Simpson

Los resultados obtenidos del Índice de Simpson en las 5 parcelas son similares a los obtenidos en el índice se Shannon – Weaver o que dé demuestra que este ecosistema tiene un ecosistema de una diversidad media según los resultados obtenidos tanto en Simpson como en Shannon – Weaver se acercan a 1 valor má= ximo de la tabla de interpretación mencionada por (Smith & Smith, 200= 7) aplica para los dos índices de diversidad dieron como resultado que la parc= ela - 05 es la más diversa dentro del estudio. Los resu= ltados además se corroboran con la observación directa que se realizó en el sitio = de estudio.

 =

Sim= ilitud de acuerdo al Índice de Sorensen

Tab= la 8. Resultados Índice de Similitud de Sorensen=

-= de Parcela

E= species comunes

V= alor Calculado

V= alor Referencial

I= nterpretación

P1 vs P2= <= o:p>

17<= o:p>

68%<= o:p>

0.36 – 0.70<= o:p>

Medianamente similare= s<= o:p>

P1 vs P3= <= o:p>

19<= o:p>

66.67%<= o:p>

0.36 – 0.70<= o:p>

Medianamente similare= s<= o:p>

P1 vs P4= <= o:p>

13<= o:p>

50%<= o:p>

0.36 – 0.70<= o:p>

Medianamente similare= s<= o:p>

P1 vs P5= <= o:p>

22<= o:p>

78.57%<= o:p>

0.71 – 1.00<= o:p>

Muy similares<= o:p>

P2 vs P3= <= o:p>

17<= o:p>

64.15%<= o:p>

0.36 – 0.70<= o:p>

Medianamente similare= s<= o:p>

P2 vs P4= <= o:p>

15<= o:p>

62.5%<= o:p>

0.36 – 0.70<= o:p>

Medianamente similare= s<= o:p>

P2 vs P5= <= o:p>

17<= o:p>

65.38%<= o:p>

0.36 – 0.70<= o:p>

Medianamente similare= s<= o:p>

P3 vs P4= <= o:p>

17<= o:p>

61.82%<= o:p>

0.36 – 0.70<= o:p>

Medianamente similare= s<= o:p>

P3 vs P5= <= o:p>

23<= o:p>

77.97%<= o:p>

0.71 – 1.00<= o:p>

Muy similares<= o:p>

P4 vs P5= <= o:p>

14<= o:p>

51.85%<= o:p>

0.36 – 0.70<= o:p>

Medianamente similare= s<= o:p>

Fue= nte: Investigación secundaria, 2018.<= /span>

 

Descripción de resultados del Índice de Simil= itud de Sorensen

El = índice de similitud de Sorensen ayuda a determinar la pre= sencia o ausencia de las especies (Smith & Smith. 2001). Al comparar los valor= es de similitud entre parcelas se observa que la vegetación es medianamente simil= ar en más del 50 % lo que quiere decir que la mayoría de las especies se pueden encontrar en toda la zona de estudio. La comparación que se realizó entre l= as parcelas P3 vs P5 y = P1 vs P5 dieron como resultado = que las parcelas son muy similares de acuerdo la tabla de comparación propuesta por= (Mostacedo, 2000).

 =

Pre= sencia de especies de las 5 parcelas

Tabla 9. Des= cripción de la presencia de especies entre las 5 parcelas

FAMILIA<= /span>

NOMBRE CIENTÍFICO

1=

2=

3=

4=

5=

1=

Apiaceae=

Azorella= = pedunculata = (Spreng.= ) Mathias<= /span> = & Constance.=

X= <= o:p>

 

X=

X=

X=

2=

Apiaceae=

Daucus  montanus= = Humb = et Bonpl.= ex spreng

X=

 

 

X=

 

3=

Apiaceae=

Eryngium= = humile<= span style=3D'mso-spacerun:yes'>  Cav

X=

X=

X=

 

X=

4=

Rosaceae=

Lachemilla = orbiculata = (Ruiz & P= av.= ) Rydb.=

X=

X=

X=

X=

X=

5=

Fabaceae=

Lupinus<= /span><= span style=3D'mso-spacerun:yes'>  sp.=

X=

X=

X=

 

X=

6=

Fabaceae=

Trifolium = repens = L.

 

 

X=

X=

 

7=

Poaceae<= /span>

Festuca<= /span> = cf

X=

X=

X=

 

X=

8=

Poaceae<= /span>

Calamagrostis = intermedia (J. Presl) Steud.=

X=

X=

X=

X=

X=

9=

Poaceae<= /span>

Bromus = pitensis= <= span style=3D'mso-spacerun:yes'>  Kunth<= /span>

X=

X=

X=

 

X=

10

Poaceae<= /span>

Holcus = lanatus<= /span> = L.

X=

 

X=

X=

X=

11

Poaceae<= /span>

Dactylis= = glomerata = L.

 

 

X=

 

 

12

Poaceae<= /span>

Festuca<= /span> = sp.=

X=

 

 

 

 

13

Cyperaceae =

Carex = bonplandii = Kunth

X=

 

X=

 

X=

14

Plantaginaceae<= /span> =

P= lantago = linearis= = var.=

X=

 

X=

 

X=

15

Plantaginaceae<= /span> =

Plantago= = serícea<= /span> = Ruíz = & Pav.

X=

 

 

 

X=

16

Asteraceae

Hypochaeri= s = sessiliflora = Kunth

X=

X=

X=

X=

X=

17

Asteraceae

Baccharis = caespitosa = (Lam.) Pers<= o:p>

X=

X=

X=

X=

X=

18

Asteraceae

Gnaphalium = elegans<= /span> = Kunth.

X=

 

 

 

X=

19

Asteraceae

Taraxacum = officinale = Weber

 

X=

X=

 

X=

20

Asteraceae

Werneria= = nubigena= = Kunth

 

 

X=

X=

X=

21

Asteraceae

Lasioce= phalus = ovatus = Schltdl<= /span>.=

 

 

 

X=

 

22

Asteraceae

Gynoxys<= /span> = buxifolia = (Kunth) Cass<= o:p>

 

 

X=

X=

 

23

Asteraceae

Bidens = andicola= = Kunth

 

 

X=

X=

X=

24

Asteraceae

Casiocaptalus<= span style=3D'mso-spacerun:yes'>  (Schltdl<= /span>.= ) B. Nord

 

X=

 

X=

X=

25

Asteraceae

Erigeron= <= span style=3D'mso-spacerun:yes'>  ecuadoriensis<= span style=3D'mso-spacerun:yes'>  Hieron

 

 

X=

 

X=

26

Asteraceae

Ast= eracea =

 

X=

X=

X=

X=

27

Melastomataceae= =

Brachyotum = ledifolium = (Desr.) Triana

 

X=

X=

X=

 

28

Ericaceae

Pernettya = prostrata<= span style=3D'mso-spacerun:yes'>  (Cav.= ) DC

X=

X=

X=

X=

X=

29

Ericaceae

Vaccinium = floribundum = Kunth

X=

X=

 

X=

 

30

Ericaceae

Disterigma = empetrifolium = (Kunth) Drude.

 

X=

 

X=

 

31

Hypericaceae

Hipericum = laricifolium = Juss.=

X=

X=

 

X=

 

32

Lycopodiaceae

Huperzia= = crassa = (Humb.= & Bonpl.= Ex Willd.= )

X=

X=

 

X=

X=

33

Polygonaceae

Rumex = acetosella = L.

X=

 

X=

 

X=

34

Geraniaceae

Geranium= = laxicaule = R. Knuth

X=

X=

X=

 

X=

35

Geraniaceae

Geranium= = L.

X=

 

 

X=

X=

36

Ranunculaceae =

Ranunculus = praemorsus = Humb.= , Bonpl.= & Kunth ex DC.

 

X=

X=

X=

 

37

Gentianaceae =

Gentiana= <= span style=3D'mso-spacerun:yes'>  sedifolia = Kunth

X=

X=

X=

 

X=

38

Gentianaceae =

Gentianella = cerastioides = (K= unth)= F= abris.

 

 

 

 

X=

39

Caprifoliaceae<= /span>

Phyllactis = rigida = (Ruiz & P= av.= ) Pers.

X=

X=

X=

 

X=

40

Caprifoliaceae<= /span>

Valeriana microphylla = Kunth

X=

X=

X=

X=

 

41

Liquen

Indeterminada 1=

 

 

X=

X=

 

42

Musgo

Indeterminada

X=

X=

X=

X=

X=

Fuente: Investigación Primaria, 2018.

 

: T= ime New Roman 12, interlineado 1.15

 

Los Gráficos, Tablas y Figuras deberán centrarse en el texto. Es necesario numerarlos. Tipografía: Arial 10 negrita.

 

 =

Figura 1. = Ciencia Digital

Fuente: Elaboración propia.

 

 =

 =

 =

 =

 =

 =

 =

Conclusiones.

·      =    La = vegetación de la zona de estudio es representativa del ecosistema páramo en el análisis realizado se muestran familias como (Apiaceae, = Asteraceae, Caprifoliaceae, Cyperaceae, Ericaceae, Fabaceae, Gentianaceae, <= span class=3DSpellE>Geraniaceae, Hypericaceae, Liquen, Lycopodiaceae, Mel= astomataceae, Musgo, Plantaginaceae, Poa= ceae, Polygonaceae, Ranunculacea= e, Rosaceae) y especies (Azor= ella pedunculata (Spreng= .) Mathias & Constance, = Baccharis caespitosa (Lam= .) Pers, Calamagrostis intermedia (= J.Presl) Steud, Daucus  montanus Humb et Bonpl. ex spreng, Disterigma empetrifolium (Kunth) Drude, Erigeron  ecuadoriensis  Hieron, Eryngium humile  Cav, Gentiana  sedifolia K= unth, Gentianella cerastioides = (Kunth) Fabris, Gnaphalium elegans= Kunth, Gynoxys buxifolia (Kunth) Cass, Lachemilla o= rbiculata  (Ruiz & Pav.) Rydb, Lasiocephalus ovatus Schltdl, Plantago serícea Ruíz & Pav<= /span>, Werneria nubigena Kunth.entre otras), típicas de estos ecosistemas a pe= sar de que este páramo ha tenido gran influencia antrópica en años anteriores y el ecosistema se encuentre en proceso de recuperación.

·      =    El = Musgo (Indeterminada) se encontró en todas las parcelas y cuadrantes teniendo may= ores individuos en la Parcela 2, esta especie forma una autentica alfombra viva = que cubre el suelo del páramo, la especie se encuentra en perfecta asociación c= on los demás individuos y no impide el desarrollo de las demás especies a su alrededor.

·      =    La composición florística no presenta una tendencia pronunciada de disminución= o incremento en su vegetación, pese a que las parcelas no se encuentran en a = la misma altura lo que hace pensar que la altura no tiene gran influencia en e= sta zona de estudio.

·      =    La = mayoría de especies se encuentran en todas las parcelas, aunque en diferente número de individuos, es decir la vegetación es casi homogénea en este páramo.<= /span>

<= del cite=3D"mailto:Admin" datetime=3D"2019-07-22T22:32">·      =       Tipografía: Time New Roman 12, interlineado 1.15

·&nb= sp;           De tres a cinco conclusiones las más relevantes=

 

 

Referencias bibliográficas.<= /p>

<= del cite=3D"mailto:Admin" datetime=3D"2019-07-22T22:34">·      =       Tipografía: Time New Roman 12, interlineado 1.15

·      =       Referencias ordenadas alfabéticamente y de acuerdo con la normativa APA.

Alv= arado, E., & Gavilanes, A. (2012). Línea base de los cinco humedales de la comunid= ad Chocaví- páramo del Igualata. (Te= sis de grado. de Ingeniero Forestal). Escuela Superior Politécnica de Chimborazo. Riobamba. .

Baq= uero, E., Sierra, R., Ordóñez, M., & Tipán, L. (2004). La = Vegetación de los Andes del Ecuador. Qu= ito: Memoria explicativa de los mapas de vegetación: potencial y remanente.=

Ber= nal, F., Sánchez, & Zapatta. (2000). Man= ejo de Páramos y Zonas de Altura. Quito-Ecuador: CAMAREN-IEDECA. Quito.=

Londo, J. (2017). Inventario= y Morfología de las Especies Forestales del  Bosque Nativo Sachafilo, Ubicado en la Parroquia San Antonio de Pasa, Cantón Ambato, Provincia de Chimborazo. Tesi= s de grado. Escuela Superior Politécnica de Chimborazo- Riobamba.

Med= ina, & Mena . (2001). Los páramos en el Ecuador.

Min= isterio del Ambiente del Ecuador.[MAE]. (2013). <= span style=3D'font-size:11.0pt !msorm;line-height:115% !msorm;font-family:"Calib= ri",sans-serif !msorm; mso-ascii-theme-font:minor-latin !msorm;mso-hansi-theme-font:minor-latin !m= sorm; mso-bidi-font-family:Calibri !msorm;mso-bidi-theme-font:minor-latin !msorm'= >Sis= tema de clasificación de los ecosistemas del = Ecu= ador continental. (S= . d. Natural., Ed.) Quito- Ecuador .

Ord= oñez, J. (1999). Cap= tura de carbono en un bosque templado: el caso de San Juan Nuevo, Michoacán. México= DF. Mé= xico: SEMARNAP.

Pau= li, H., Gottfried, M., Lamprecht, A., Niessner, Rumpf, S., Winkler, M., . . . Grabherr,. (2015). Man= ual para el trabajo de campo del proyecto GLORIA. Aproximación al estudio de las cim= as. Métodos básicos, complementarios y adicionales.<= /i> 5ª= edición. GLORIA - Coordinación, Academia Austriaca de Ciencias y Universidad de Recu= rsos Naturales y Ciencias de la Vida, Viena, Austria. Edición en español a cargo= de Benito, J.L. & Villar, L., Jaca,. Obtenido de https://www.researchgate.net/profile/Jose_Luis_Benito_Alonso/publication/28= 2567915_Manual_para_el_trabajo_de_campo_del_proyecto_GLORIA_Aproximacion_al= _estudio_de_las_cimas_Metodos_basico_complementarios_y_adicionales_5_edicio= n/links/5615380308ae4ce3cc6526=

Pla= n de Desarrollo y Ordenamiento Territorial de la Parroquia de ILAPO (PD Y OT). (2016). Gob= ierno Autónomo Desentralizado de = la parroquia Rural Ilapo . Gu= ano -Ecuador .

Puj= os. (2013). Mét= odos para el análisis de datos: una aplicación para resultados provenientes de caracterizaciones de biodiversidad. .=

Velásquez, A. (1997). <= /ins>Mét= odos para el análisis de datos: una aplicación para resultados provenientes de caracterizaciones de biodiversidad. . Re= cuperado el 12 de 02 de 2019, de http://www.bio-nica.info/biblioteca/humboldtanalisisdatos.pdf<= /span>

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

PARA CITAR EL ARTÍCULO INDEXADO.=

 

 

 

Paguay Tingo, M., Ro= mán Robalino, D., & Cevallos Rodríguez, J. (2019). Composición y diversidad= de especies forestales en el páramo Machay- Chimbo= razo- Ecuador. Ciencia Digital3(3.1), 326-340.= https://doi.org= /10.33262/cienciadigital.v3i3.1.706

 

 


 

 

 

= El artículo que se pub= lica es de exclusiva responsabilidad de los autores y no necesariamente reflejan el pensamiento de la Revista Ex= plorador= Digital.

 

El= articulo 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 o editor de la Revista Explorador Digital.<= /o:p>

 

 

=  


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

 

El= artículo 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.

 

 

=  

 



[1] Escuela Superior Polité= cnica de Chimborazo, Carrera de Ingeniería Forestal, Riobamba, Ecuador. Tesista Afi= liación (Universidad, Carrera o Facultad), Ambato, Ecuador, email (preferente institucional)mayra201223@hotmail.com

[2] Escuela Superior Politécnica de Chimborazo, Facul= tad de Recursos Naturales. Riobamba, Ecuador. daniel.roman@espoch.edu.ec=

[3] Escuela Superior Politécnica de Chimborazo, Facultad de Recursos Naturales. Riobamba, Ecuador. jorge.cevallos@espoch.edu.ec

[4] Universidad Técnica de Amato, Facultad de Cie= ncias de la Educación, Carrera de Cultura Física. Ambato, Ecuador. xxxxxx@uta.edu= .ec

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      =                                                       =         Vol. 3, N°3.1 p. 326-340, julio - septiembre, 2019

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                                                                        =                                                ISSN: 2602-8085

                                                                        =            Vol. 3, N°2, p. 78-97, abril - junio, 2018

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