MIME-Version: 1.0 Content-Type: multipart/related; boundary="----=_NextPart_01D7857A.7CFDC870" Este documento es una página web de un solo archivo, también conocido como "archivo de almacenamiento web". Si está viendo este mensaje, su explorador o editor no admite archivos de almacenamiento web. Descargue un explorador que admita este tipo de archivos. ------=_NextPart_01D7857A.7CFDC870 Content-Location: file:///C:/9E85C06C/818-GALERADA-FINAL.htm Content-Transfer-Encoding: quoted-printable Content-Type: text/html; charset="windows-1252" Jorge Mendoza Cedeño, Antonio Campos Cedeño

 

 

 

 

https://doi.org/10.37815/rt= e.v33n1.818

Artículos originales=

 

Reacción al Fuego de Tres Maderas Angiospermas Impregnadas con Sales de Boro<= /b><= /o:p>

Reaction to fire of three angiosperm woods impregnated with boron sa= lts=

 

Javier Ramón Sotomayor Castellanos1 https://orcid.org/0000-= 0002-1527-8801 <= o:p>

Luz Elena Alfonsina Ávila Calderón1<= /span> https://orcid.org/0000-0003-2646-2= 142 =                                 

 

1 Universidad Michoacana de San Nicolás de Hidalgo, Morelia, México

madera999= @yahoo.com

lea.avilacalderon@gmail.com

 =

Enviado:   =        2021/04/27

Aceptado:  =       2021/05/20

Publicado: =        2021/06/30                             

Resumen

L= a madera es un material combustible, motivo por el cual es importante investigar técnicas para aumentar su resistencia al fuego. La retención de sales de bo= ro en la madera mide la idoneidad del tratamiento de impregnación y la aptitud= que tiene una especie para su preservación y reacción al fuego. Los objetivos d= e la investigación fueron, por una parte, determinar su densidad aparente y su capacidad de retención de sales de boro y, por otra, medir el tiempo de ign= ición y la pérdida de masa en pruebas de reacción al fuego. La investigación comp= robó la capacidad de retención de sales de boro de Spathodea campanu= lata (Tulipán africano), Fraxinus americana (Fresno blanco) y Albizia plurijuga= (Tepehuaje). Para cada especie, se impregnaron cuarenta probetas de pequeñas dimensiones con el método de baño caliente-frío con una solución de ácido bórico y borato de sodio con concentraciones de uno, dos y tres por ciento.= Se determinaron la densidad y el contenido de humedad de la madera.  Se realizaron pruebas de reacción al fu= ego con duración de dos minutos y se midieron el tiempo de ignición y la pérdid= a de masa. El impregnado de la madera con sales de boro aumenta la resistencia aparente de la madera a la exposición al fuego. A medida que la densidad de= la madera aumenta, los tiempos de ignición se incrementan y, a la vez, se disminuye la pérdida de masa.

 

Palabras clave: = impregnación de la madera, retención, densidad aparente, tiempo de ignición, pérdida de = masa.

Sumario: 1 Introdu= cción, 2 Materiales y Métodos, 3 Resultados y Discusión, 4 Conclusiones.=

 

Como citar= : Sotomayor Castellanos, J. R., & Ávila Calderón, L. E.  A. (2021). Reacción al Fuego de Tres Maderas Angiospermas Impregnadas con Sales de Boro. Revista Tecnoló= gica - Espol, 33(1), 35-48. http://www.rte.espol.edu.ec/index.php/tecno= logica/article/view/818


 

Abstract=

Wo= od is a combustible material; therefore, it is important to investigate techniques = to increase its resistance to fire. The retention of boron salts in wood measu= res the suitability of the impregnation treatment and the aptitude of one speci= es for its preservation and reaction to fire. The objectives of this research = are, on one hand, to determine the apparent density of this kind of wood and its capacity to retain boron salts and on the other hand, to measure ignition t= ime and mass loss in reaction to fire tests. The investigation verified the capacity of retention of boron salts of Spathodea campanulata (Tulipán africano), Fraxinus americana (Fresno blanco) and Albizia plurijuga= (Tepehuaje). For each species, forty small spec= imens were impregnated with the hot-cold bath method with a solution of boric acid and sodium borate with concentrations of one, two, and three percent. The density and moisture content of the wood were determined. Fire reaction tes= ts were conducted lasting two minutes and the ignition time and mass loss were measured. Impregnated wood with boron salts increases the apparent resistan= ce of wood to fire exposure. The density of the wood increases with the increa= se of ignition time whereas mass loss decreases.

 

Keywords: Wood impregnation, retention, apparent density, ignition time, mass loss.

 

      =             &nb= sp;            =             &nb= sp;            =             &nb= sp;            =          1.    Introducción

La madera e= s un material combustible, motivo por el cual arquitectos, diseñadores de elemen= tos de construcción y fabricantes de muebles se han preocupado por indagar sobre las técnicas que permiten aumentar la resistencia de esta al fuego (Atar et al., 2011; Bartlett et al., 2019). Para tal propósito, se han desarrollado diferentes enfoques de investigación. Por ejemplo, aquel que efectúa pruebas con configuraciones que simulan condiciones reales de incendio para así pod= er recomendar criterios de diseño y cálculo estructural (= Östman, 2017; Ali et al., 2019).  Otro enfo= que, en cambio, prefiere realizar pruebas de laboratorio con pequeñas probetas, = con el objetivo de estudiar las variables que intervienen en la fenomenología d= e la reacción de la madera al fuego (Harada, 2001; <= span class=3DSpellE>Osvaldová, 2018). Otra perspectiva alude a las sustan= cias preservantes y los métodos de impregnación con el fin de, a partir de la caracterización del fenómeno de ignición de la madera, disminuir su deterio= ro cuando se expone al fuego (Tondi et al., 2012; = Wang et al., 2017 Gaff et al., 2019).

 =

La medición= de los niveles de retención de sales de boro en la madera facilita establecer la idoneidad de un determinado tratamiento de impregnación y la aptitud que ti= ene una especie para preservarse del fuego (Koumbi-Mounang= a et al., 2015, Pereira et al., 2017). Existe evidencia empírica de que, si u= na probeta de madera de pequeñas dimensiones es impregnada con sales de boro y expuesta al fuego, el tiempo de ignición y la pérdida de masa disminuyen (<= span class=3DSpellE>Sogutlu et al., 2011; Uner et al., 2016; Jin & Chung, 2018). En este proceso intervienen, entre otros factores, la especie, su densidad aparente, la retención de la sustancia preservante, así como las condiciones de laboratorio en las cuales se reali= zan las pruebas de reacción al fuego (Babrauskas, 2= 002; Osvaldová et al., 2016). La información revisada sobr= e el tema en la literatura es amplia y los resultados hallados en esta son diferentes en cada caso.

 =

Como ya se mencionó, uno de los factores que influye en el momento de evaluar el comportamiento de la madera expuesta al fuego es la densidad aparente, porq= ue cuando esta aumenta el tiempo de ignición también se incrementa (Osvaldová, 2018). Por su parte, el tiempo de ignición= , que es un factor importante para evaluar el comportamiento de combustión de los materiales, se define como el lapso requerido para percibir la flama sosten= ida en la superficie de una muestra expuesta a un flujo de calor incidente, y, cuanto más corto sea el tiempo de ignición, más inflamable será el material= (Boonmee & Quintiere, = 2002; Xu et al., 2015).

 =

Entre tanto= , la pérdida de masa, como resultado de la exposición de la madera al fuego, pue= de servir como indicador de la vocación de una especie para su empleo en estructuras y productos. La literatura sobre el comportamiento de la madera expuesta al fuego establece que la pérdida de masa es proporcional a la densidad de la madera (Friquin, 2011; Rocha &am= p; Landesmann, 2016) y que la pérdida de masa depende, principalmente, del tipo de especie maderable, de la temperatura y el tiemp= o de exposición al calor ígneo (Ragan et al., 2016).=

 =

P. Beauv ha estudiado las características tecnológicas de la especie Spathodea campanulata. Britton y Rose, además de otros auto= res, como Silva et al. (2010), Sotomayor (2015) y Tamarit y López (2017), han estudia= do las especies Fraxinus americana y= Albizia plurijuga (Standl.). Sin embargo, no se detectó información sobr= e su reacción al fuego en un contexto en el que estas especies hayan sido impregnadas previamente con sales de boro. Los objetivos de la investigación fueron, por una parte, determinar su densidad aparente y su capacidad de retención de sales de boro y, por otra, medir el tiempo de ignición y la pérdida de masa en pruebas de reacción al fuego.

 

   &nbs= p;            &= nbsp;           &nbs= p;            &= nbsp;           &nbs= p;            &= nbsp;           2.    Materiales y Métodos

Las piezas de madera de S. campan= ulata, F. americana y A. plurijuga se recolectaron en aserraderos del Estado de Michoacán, México. Para cada especie se prepararo= n 40 probetas, con dimensiones de 0,02 m x 0, 02 m de sección y 0,4 m de largo, orientadas, respectivamente, en las direcciones radial, tangencial y longit= udinal de la madera, tal como lo estipula la norma ISO 3129:2012 (International Organization for Standardization, 2012). Las probetas contenían solo m= adera de duramen, libre de defectos de crecimiento. Se almacenaron en una cámara = de acondicionamiento durante 12 meses, con una temperatura de 20 °C (± 1 °C) y= una humedad relativa del aire de 65 % (± 2 %) hasta que su peso alcanzó un valor constante. El material experimental de esta investigación corresponde al mi= smo tipo que Sotomayor y Ávila utilizaron y reportaron (2019) en experimentos q= ue se realizaron de manera paralela a la presente investigación.

 

El contenido de humedad se calculó en un grupo adicion= al de 20 muestras, obtenidas del recorte que se efectuó, después de las pruebas, = en un extremo de las probetas, con dimensiones de 0,02 m × 0,02 m × 0,06 . El contenido de humedad se determinó por el métod= o de diferencia de pesos, que realiza su cálculo de acuerdo con la norma ISO 13061-1:2014 (International Organization for Standardization, 2014= a). La densidad aparente de la madera se determinó de acuerdo con la norma ISO 13061-2:2014 (International Organization for Standardization, 2014= b). Cabe señalar que, para aligerar el texto cuando conviene, se ha utilizado el tér= mino “́densidad̀́” en lugar del concepto “densidad aparente”.

 

Proceso de impregnación

Las probetas se impregnaron con el método baño caliente-frío, siguiendo el protocolo propuesto por Ávila et al. (2012). Se prepararon 30 litros de solución de trihidróxido de boro (ácido bórico, 39,4 %) y tetraborato de so= dio (borato de sodio, 60,6 %) con tres concentraciones: 1 %, 2 % y 3 %, tal com= o lo establece la norma NMX-C-178-ONNCCE-2014 (Organismo Nacional de Normalizaci= ón y Certificación de la Construcción y Edificación, 2014). La madera se sumergió durante 8 h en un baño de agua con temperatura de 60 º= C y presión atmosférica. A continuación, las probetas se sumergieron durante = 16 h en un baño frío, con la solución de sales de boro a temperatura de 23 °C y presión atmosférica.

 

La retención se determinó con la fórmula (1) (Simsek et al., 2013):

 

 

(1)<= /span>

 

Donde:

R =3D Retención (kg m-3)<= /span>

PDT =3D Peso después del tratamiento= de impregnación (kg)

PAT =3D Peso antes del tratamiento de impregnación (kg)

C =3D Concentración de sales de boro (%)

VDT =3D Volumen después del tratamie= nto de impregnación (m3)

 

P= ruebas de reacción al fuego

Las pruebas de reacción al fuego se llevaron a = cabo según el protocolo reportado por Sotomayor y Carrillo (2017). La metodología implementada para dichas pruebas se dividió en las siguientes etapas:<= /o:p>

1.&n= bsp;     Se midieron el peso y las dimensiones de = la probeta antes del tratamiento.

2.&n= bsp;     La probeta se posicionó en el dispositivo= para las pruebas de comportamiento al fuego (Figura 1).= Su orientación siguió la dirección radial, lo que coincidió con el flujo verti= cal de la flama.

3.&n= bsp;     La probeta se expuso durante 2 minutos al fuego directo de la flama de un mechero de laboratorio tipo Meker-Fisher, con regulación de aire y de gas, quemador de 0,03 m de diámetro y temperatu= ra máxima de 1300 °C.

4.&n= bsp;     Con un cronómetro se midió el tiempo de ignición (tign) definido de acuerdo con el tiem= po que transcurrió hasta que la ignición apareció en al menos tres de las caras de= la probeta expuestas a la flama.

5.&n= bsp;     La probeta se retiró de la flama y se interrumpió su combustión en una cama de arena.

6.&n= bsp;     La masa de la zona carbonizada se retiró = y, luego, se procedió a medir el peso de la probeta después del tratamiento.

<= o:p> 

Figura <= /span>1<= /span>

Dispositivo para las pruebas de comportamiento al fuego=

=

 

L= a pérdida de masa se determinó con la fórmula (2) (Gaff e= t al., 2019):

<= o:p> 

(2)<= /span>

<= o:p> 

Donde:

Δm =3D Pérdida de masa (%)

PAT =3D Peso antes de la exposición = al fuego (kg)

PDT =3D Peso después de la exposició= n al fuego (kg)

<= o:p> 

<= o:p> 

Diseño experimental

Se examinaron tres unidades experimentales, que se organizaron en torno a cada una de las siguientes especies: S. campanulata, F. americana y A. plurijuga. El factor de variación fue el tratamie= nto de impregnación con cuatro niveles de concentración de sales de boro: 1 %, 2 %= , y 3 %. El grupo de control fue el del nivel cero, y no se le dio tratamiento. Para cada especie y cada concentración, se efectuaron muestras independient= es de diez probetas cada una, por lo que en total se analizaron 120 probetas (= 3 x 4 x 10). Las variables de respuesta fueron la densidad aparente (ρCH), la retención de sales de boro (R), el tiempo de ignición (tign) y la pérdida de masa (Δm). El contenido de humedad (CH) se consideró variable de referencia y no inter= vino en los resultados.

 

Para cada variable se calculó su media (= ), su desviación estándar (σ) y su coeficiente de variación porcentual (CV =3D σ/ ). Se determinó su normalidad en la distribución con el criterio de demarcación para el sesgo estandarizado (SE= ) y para el apuntamiento estandarizado (AE): [-2 < SE y/o AE < +2]; se verificaron la igualdad de varianzas (Ver-var) = con la hipótesis nula: , con un nivel de significancia de 5 % (α =3D 0,05).  Luego, se pract= icaron análisis de varianza (Anova) con la hipótesis n= ula:  = , con un nivel de significancia de 5 % (α =3D 0,05). El criterio de demarcac= ión fue aceptar una diferencia estadísticamente significativa para valores P(α =3D 0,05) < 0,05. Cu= ando no se confirmó la normalidad en la distribución de las muestras, se realizaron pruebas no paramétricas de Kruskal-Wallis de diferencia de medianas ( ) para un nivel de confiabilidad del 95 %. Para las pruebas no paramétricas, las hipótesis resultaron similares, pero = se emplearon las medianas.

<= o:p> 

   &nbs= p;            &= nbsp;           &nbs= p;            &= nbsp;           &nbs= p;            &= nbsp;         3.    Resultados y Discusión

Las mad= eras de S. campanulata, F. americana y A. plurijuga alcanzaron un contenido de humedad equilibrado, con un promedio de 10 %, un coeficiente de variación de 8 %. E= stos parámetros indican que la madera se acondicionó a un estado de humedad seco= y homogéneo, de tal forma que la variación en el contenido de humedad de la madera no intervino de modo significativo en los resultados.

&n= bsp;

El impr= egnado de la madera con sales de boro sí aumentó la resistencia aparente de la madera= a la exposición del fuego. A medida que la concentración de sales de boro se incrementó, la pérdida de masa en la zona de combustión disminuyó (<= !--[if supportFields]> REF _Ref75539942 \h  \* MERGEFORMAT= Figura 2).

&n= bsp;

Figura <= /span>2<= /span>

Disminución de la sección transversal en función de la concent= ración (C) en probetas de A. plurijuga

=

&n= bsp;

Densidad

Las magnitudes de las densidades de la madera s= in tratamiento (C =3D 0 %) de S. campanulata, F. americana y A. plurijuga (Tabla 1) = son similares a las reportadas en la bibliografía (Silva et al., 2010; Sotomayor, 2015; Tamarit & López, 2017). En el siguiente cuadro (Tabla 1),= las densidades correspondientes a cada especie siguen el ordenamiento: S. campanulata > F. americana > A. plurijuga. Además, evidencia que los coeficientes de variación de la densidad de la madera sin tratamiento aumentan o disminuyen dependiendo de la especie o de la concentración. No se observa una tendencia definida hacia la disminución, p= ero tampoco se advierte un aumento desproporcional ocasionado por el tratamient= o.

&n= bsp;

Tabla 1<= /span>

Resultados de las pruebas de exposición al fuego

C

 

ρCH

R

tign<= /b>

Δm

(%)

 

(kg m-3)

(kg m-3)

(s)

(%)

 

S. <= span class=3DSpellE>campanulata

0

351

0

12,7

6,0

 

CV

(6,3)

-

(36,2)

(30,2)

1

351

2,3

11,3

6,4

 

CV

(6,4)

(4,6)

(30,1)

(26,5)

2

336

4,2

12,6

6,4

 

CV

(3,9)

(4,8)

(21,6)

(9,3)

3

340

6,4

11,1

6,4

 

CV

(8,5)

(6,4)

(10,8)

(4,6)

 

F. a= mericana

0

654

0

11,6

6,2

 

CV

(5,6)

-

(13,6)

(6,7)

1

616

1,6

13,7

5,8

 

(CV

(3,6)

(9,5)

(1,6)

(9,1)

2

619

3,3

17,0

5,7

 

CV

(7,5)

(6,3)

(11,1)

(13,7)

3

610

5,3

21,5

5,5

 

CV

(4,8)

(10,2)

(7,7)

(10,0)

 

A. plurijuga

0

830

0

15,0

4,4

 

CV

(2,7)

-

(15,7)

(8,8)

1

831

1,3

19,3

3,9

 

CV

(2,2)

(9,8)

(14,7)

(6,7)

2

846

2,7

20,6

4,1

 

CV

(5,0)

(5,9)

(12,8)

(7,8)

3

816

3,7

25,3

3,9

 

CV

(2,8)

(7,3)

(5,9)

(2,5)

ρCH =3D Densidad; R =3D Retención; tign =3D Tiempo de ignición; Δm =3D Pérdida d= e masa; C =3D Concentración;  =3D Media; CV =3D Coeficiente de varia= ción en porciento y entre paréntesis.

Fuente: Elabo= ración propia

Las distribuciones de todas las muestras result= aron normales (Tabla 2),= con excepción de las de S. campanulata sin tratamiento (C =3D 0 %: SE y AE &= gt; 2). Las pruebas de verificación y análisis de varianza no muestran diferencias estadísticamente significativas (P(α =3D 0,05) > 0,05) para S. = campanulata y A. plurijuga (Tabla 3).= Un caso diferente corresponde a las densidades de F. americana, las cuales muestran una diferencia significativa (P(α =3D 0,05) < 0,05). L= as pruebas de grupos homogéneos indican que, para S. campanulata, las densidades, seg= ún las concentraciones (grupos de muestras en la Tabla 3), son homogéneas entre el= las. En cambio, para F. americana y = A. plurijuga se agrupan y combinan en diferentes concentraciones.

<= o:p> 

Tabla 2<= /span>

Resultados de las pruebas de normalidad

 

C =3D 0 %

C =3D 1 %

C =3D 2 %

C =3D 3 %

 

 

SE

AE

SE

AE

SE

AE

SE

AE

 

 

S. campanulata

 

ρCH

2,6840

2,8500

-0,5667

-0,5415

-0,0072

0,3682

0,5001

0,0054

 

R

-

-

-0,1245

0,4658

-0,6149

-0,4818

0,0429

1,3880

 

tign

1,6960

1,2850

-0,0591

-1,1030

0,5755

-0,7850

-0,3009

-0,2379

 

Δm

1,7510

0,5705

-0,8481

0,3336

1,3910

1,4280

0,7590

0,4514

 

 

F. americ= ana

 

ρCH

0,2382

-1,2460

0,4932

-0,2227

0,2952

-0,6957

-0,8263

-0,9480

 

R

-

-

-0,2723

0,1108

-0,2013

-0,6870

0,7573

-0,6038

 

tign

-0,2959

-0,5296

0,0393

-0,4225

-0,8023

1,1660

1,0780

0,9941

 

Δm

1,8630

0,3033

-0,0572

-0,5249

0,9110

-0,1152

0,2073

-0,7578

 

 

A. plurijuga

 

ρCH

-0,0899

-0,8442

-0,5070

-0,5870

0,0227

-0,1543

-0,8722

0,5468

 

R

-

-

-0,1431

-0,7043

0,5075

-0,6602

-1,6640

1,1280

 

tign

1,725

0,6590

1,0740

0,1032

1,3510

0,6334

-0,8252

-0,6403

 

Δm

-0,3254

-0,1120

-0,6241

-0,7839

-0,7292

1,2100

-0,7764

0,2558

 

C = =3D Concentración; SE =3D Sesgo estandarizado; AE =3D Apuntalamiento estandar= izado; ρCH =3D Densidad; R =3D Retención; = tign =3D Tiempo de ignición; Δm =3D Pérdida de masa.

 

Fuente: Elabo= ración propia

 

Retención

Los resultados de las retenciones de sales de b= oro obtenidos en esta investigación (Tabla 1) = son similares a los reportados en la bibliografía sobre especies mexicanas en l= as que se han aplicado protocolos experimentales parecidos a los de esta investigación. Sotomayor y Correa (2016) reportan para S. campanulata (ρCH =3D 357 kg m-3) una retención de 14,31 kg m-3= ; para A. religiosa (ρCH =3D 419 kg m-3), una retención de 7,23 %; y para G. ulmifolia (ρCH =3D 739 kg m-3), una retención de 9,7 %. Por su parte, Sotomayor y Villaseñor (2016) reportan valores de reten= ción que varían en el intervalo de 4,07 % hasta 14,18 % para diez especies mexicanas: Tilia mexicana, Cupressu= s lindley, Alnus<= /span> acuminata, Cedrela<= /i> odorata, Fraxinus uhdei, Lysiloma= bahamensis, Fagus mexicana, Caesalpinia granadillo<= /i>, Platymiscium dimorphan= drum y Quercus spp. Los coeficientes de variación de las retenciones aumentan a medida que las concentraciones se incrementan para S. campanulata, F. americana y A. plurijuga, (Tabla 1).= No se observa en estos una disposición relacionada con la especie o con la densid= ad.

Tabla 3<= /span>

Resultados de las pruebas estadísticas

 

Ver-var

Anova

K-W

C

Grupos homogéneos

 

P(<= b>α =3D 0,05)

P(<= b>α =3D 0.05)

P(<= b>α =3D 0.05)

(%)

 

 

S. campanulata

ρCH

0,4344

-

0.2996

0

X

 

 

 

 

-

-

-

1

X

 

 

 

 

-

-

-

2

X

 

 

 

 

-

-

-

3

X

 

 

 

R

0,1111

< 0.0001

-

0

X

 

 

 

 

-

-

-

1

 

X

 

 

 

-

-

-

2

 

 

X

 

 

-

-

-

3

 

 

 

X

tign

0,1080

0.5679

-

0

X

 

 

 

 

-

-

-

1

X

 

 

 

 

-

-

-

2

X

 

 

 

 

-

-

-

3

X

 

 

 

Δm

0,0703

0.8787

-

0

X

 

 

 

 

-

-

-

1

X

 

 

 

 

-

-

-

2

X

 

 

 

 

-

-

-

3

X

 

 

 

 

F. americ= ana

ρCH

0,1451

0.0312

-

0

X

 

 

 

 

-

-

-

1

X

 

 

 

 

-

-

-

2

X

 

 

 

 

-

-

-

3

 

X

 

 

R

0,0003

-

< 0.0001

0

X

 

 

 

 

-

-

-

1

 

X

 

 

 

-

-

-

2

 

 

X

 

 

-

-

-

3

 

 

 

X

tign

0,9857

< 0.0001

-

0

X

 

 

 

 

-

-

-

1

 

X

 

 

 

-

-

-

2

 

 

X

 

 

-

-

-

3

 

 

 

X

Δm

0,2446

0.0718

-

0

X

 

 

 

 

-

-

-

1

X

X

 

 

 

-

-

-

2

X

X

 

 

 

-

-

-

3

 

X

 

 

 

A. plurijuga

ρCH

0,1162

0.1403

-

0

X

 

 

 

 

-

-

-

1

X

X

 

 

 

-

-

-

2

X

X

 

 

 

-

-

-

3

 

X

 

 

R

0,0244

-

< 0.0001

0

X

 

 

 

 

-

-

-

1

 

X

 

 

 

-

-

-

2

 

 

X

 

 

-

-

-

3

 

 

 

X

tign

0,4610

< 0.0001

-

0

X

 

 

 

 

-

-

-

1

 

X

 

 

 

-

-

-

2

 

X

 

 

 

-

-

-

3

 

 

X

 

Δm

0,0849

0.0017

-

0

X

 

 

 

 

-

-

-

1

X

 

 

 

 

-

-

-

2

X

X

 

 

 

-

-

-

3

 

X

 

 

Ver= -var=3D Pruebas de verificación de varianza; Anova =3D Prueba de análisis de varianza; K-W =3D P= ruebas de Kruskal-Wallis; C =3D Concentración; ρCH =3D Densidad; R =3D Retención; tign =3D Tiem= po de ignición; Δm =3D Pérdida de masa.

Fuente: Elabo= ración propia

 

Las distribuciones de los resultados de las retenciones del grupo de control y de las muestras de las tres concentracio= nes resultaron normales, con excepción de la retención alcanzada con la concentración de 2= % para A. plurijuga (Tabla 2).= Sin embargo, los valores medios de la retención presentan diferencias estadísticamente significativas de acuerdo con el nivel de concentración de sales de boro y entre especies (Tabla 3).= En el mismo contexto, las pruebas de rangos múltiples indican que, para las tres especies en estudio, existen diferencias entre los cuatro grupos analizados= .

 

Las retenciones de sales de boro en S. campanulata, F. americana y A. plurijuga disminuyen con relació= n a la densidad de la madera (Figura 3a), además, se observa una tendencia al agrupamiento en las magnitudes de las retenciones a medida que la densidad aumenta, como es el caso para A. plurijuga. Al respecto, es importante mencionar que las retenciones correspondientes a= un valor R =3D 0 (Figura 5a)= se refieren a las probetas sin tratamiento, es decir, una concentración de boro igual a cero (C =3D 0 %). Por el contrario, en las tres especies del estudi= o, las retenciones aumentan en función de la concentración utilizada y, cabe señal= ar, que lo hacen con fuertes coeficientes de determinación (R2 =3D 0= ,99) (Figura 4a). Estos resultados corroboran los reportados por Toker et al. (2009) para maderas de <= span class=3DSpellE>Pinus brutia (ρCH =3D 532 kg m-3) y Fagus orientalis (ρCH = =3D 520 kg m-3), sobre las cuales también se impregnaron concentraciones similares de sales de boro. Igualmente, las magnitudes de las retenciones, = considerando las concentraciones utilizadas en esta investigación, son del mismo orden q= ue las encontradas por Temiz et al. (2008) para madera de Alnus glutinosa (ρCH = =3D 503 kg m-3) y Pinus sylvestris (ρCH =3D 520 kg m-3).

 

Figura <= /span>3<= /span>

Dispersiones de a), la re= tención (R); b), del tiempo de ignición (tign); y c), de la pérdida de masa (Δm), en función de la densidad aparente (ρ<= sub>CH) para las concentraciones de 1 %, 2 % y 3 % de sales de boro

Fuente: Elabo= ración propia<= /o:p>

Figura 4=

Correlaciones y coeficien= tes de determinación (R2): de a) la retención (R); b) del tiempo de ignición (tign); y c) de la pérdida = de masa (Δm), en función de las concentraciones de 1%, 2% y 3 % de sales de boro

Fuente: Elabo= ración propia

 

Figura <= /span>5<= /span>

Dispersiones de los tiemp= os de ignición (tign) en función de las densidades aparentes (ρCH) y sus correlaciones, detalladas en la Tabla 4

 Fuente: Elaboración propia<= /o:p>

T= iempo de ignición

Los tiempos promedio de ignición medidos, para = S. campanulata, F. americana y A. plurijuga (Tabla 1),= son similares a los reportados en la bibliografía (Tabla 5) para maderas mexica= nas cuyos protocolos experimentales fueron similares a los utilizados en esta investigación (Sotomayor & Carrillo, 2017; Sotomayor et al., 2018; Sotomayor & Gallegos, 2018; Sotomayor & Giraldo, 2017; Sotomayor & Osvaldová, 2017)= . Sin embargo, a diferencia de lo reportado en la bibliografía, en la madera no impregnada, no se observa una tendencia al aumento del tiempo de ignición a medida que la densidad de la madera aumenta (Harada, 2001; Shi & Chew, 2019; Rocha & Landesmann, 2016). Estas tendencias se muestran en la Figura 3b con modelos lineales empíricos (Tabla 4), calculados a partir de los resultados obtenidos en esta investigación y de = la bibliografía (ambos enlistados en la Tabla 5).= El coeficiente de determinación de la correlación ti= gn =3D f(ρCH) = se calculó con los resultados de esta investigación (Tabla 4);= su resultado estableció que este es 64 % menor, en promedio, en comparación con los coeficientes R2 de la bibliografía.

<= o:p> 

Tabla 4<= /span>

Correlaciones de las Figuras 5 y 6

Autor

Correlación tign =3D f(ρCH)<= /span>

Esta investigación (2= 019)

tign =3D 0,0034 ρCH + 11,28

0,28

Sotomayor et al. (2017-2018)

tign =3D 0,041 ρCH - 6,54

0,71

Shi y Chew (2012)

tign =3D 0,037 ρCH - 7,18

0,75

Rocha y Landesmann (2016)

tign =3D 0,065 ρCH - 3,53

0,76

Harada (2001)

tign =3D 0,059 ρCH - 5,66

0,92

Autor

Correlación Δm =3D f(ρCH)

Esta investigación (2= 019)

Δm =3D -0,0029 <= span lang=3DPT style=3D'font-size:8.0pt;mso-bidi-font-size:9.0pt;line-height:1= 02%; color:black;mso-ansi-language:PT;mso-fareast-language:ES-MX'>ρC= H + 7,31

0,51

Sotomayor et al. (2017-2018)

Δm =3D -0,019 ρC= H + 27,12<= o:p>

0,89

Sotomayor y Carrillo (2017)

Δm =3D -0,0085 <= span lang=3DPT style=3D'font-size:8.0pt;mso-bidi-font-size:9.0pt;line-height:1= 02%; color:black;mso-ansi-language:PT;mso-fareast-language:ES-MX'>ρC= H + 10,15<= o:p>

0,94

Sotomayor y Gallegos (2018)

Δm =3D -0,0244 <= span lang=3DPT style=3D'font-size:8.0pt;mso-bidi-font-size:9.0pt;line-height:1= 02%; color:black;mso-ansi-language:PT;mso-fareast-language:ES-MX'>ρC= H + 322,46=

0,85

tign =3D Tiempo de ignición; Δm =3D Pérdida de masa; ρCH =3D = Densidad; R2 =3D Coeficiente de determinación.

Fuente: Elaboración propia<= /o:p>

 

Tabla 5<= /span>

Densidades aparentes, tiempos de ignición y pérdidas de masa p= ara maderas no impregnadas en la bibliografía

Especies mexicanas

ρCH

tign

Δm

Espe= cies internacionales

ρCH

tign

 

(kg = m-3)

(s)<= o:p>

(%)<= o:p>

 

(kg = m-3)

(s)<= o:p>

Sotomayor= y Carrillo (2017)

Harada (2001)

Tabebuia rosea

613<= /o:p>

8

5,3<= /o:p>

Cryptomeria japonica

299<= /o:p>

13

Andira inermis

737<= /o:p>

12

3,6<= /o:p>

Thujopsis dolabrata

422<= /o:p>

18

Juglans pyriformis

773<= /o:p>

23

3,5<= /o:p>

Pinus densiflora

433<= /o:p>

19

Quercus spp,

866<= /o:p>

30

2,6<= /o:p>

Larix leptolepsis

524<= /o:p>

22

Cordia elaeagnoides

996<= /o:p>

34

2,0<= /o:p>

Paulownia tomentosa=

266<= /o:p>

14

Sotomayor= et al, (2018)<= /p>

Juglans soeboldiana

547<= /o:p>

23

Tabebuia donnell-smithii

448<= /o:p>

17

20,8=

Fagus crenata

581<= /o:p>

32

Enterolobium cyclocarpum

504<= /o:p>

17

18,7=

Zelkova serrata

703<= /o:p>

36

Tabebuia rosea

604<= /o:p>

24

15,9=

Quercus mongolica

772<= /o:p>

44

Swietenia humilis

655<= /o:p>

28

14,9=

Shi y Chew (2012)

Lysiloma acapulcensis

685<= /o:p>

31

10,4=

Pinus contorta<= /span>

447<= /o:p>

11

Cordia elaeagnoides

1130=

37

7,8<= /o:p>

Fagus grandifolia

632<= /o:p>

13

Tabebuia chrysantha

1234=

49

4,2<= /o:p>

Prunus serotina

558<= /o:p>

11

Sotomayor= y Gallegos (2018)

Quercus rubra

897<= /o:p>

24

Enterolobium cyclocarpum

458<= /o:p>

10

11,8=

Acer nigrum

748<= /o:p>

26

Tabebuia rosea

624<= /o:p>

16

5,7<= /o:p>

Fraxinus, americana

680<= /o:p>

19

Juniperus pyriformis

711<= /o:p>

12

6,1<= /o:p>

Rocha y <= span class=3DSpellE>Landesmann (2016)

Sotomayor= y Osvaldová (2017)

Joannesia princeps

352<= /o:p>

23

Abies religiosa=

431<= /o:p>

10

5,4<= /o:p>

Cedrela, lilloi

422<= /o:p>

25

Sotomayor= y Giraldo (2017)

Schizolobium parahyba

347<= /o:p>

16

Gyrocaupus americanus

375<= /o:p>

10

9,0<= /o:p>

Ocotea porosa

584<= /o:p>

43

-

-

-

-

Capsicodendron dinisii

471<= /o:p>

20

-

-

-

-

Peltophorum dubium

627<= /o:p>

33

-

-

-

-

Zanthoxylum chiloperone

739<= /o:p>

44

-

-

-

-

Pinus caribaea

484<= /o:p>

31

ρCH =3D Densidad; R =3D Retención; = tign =3D Tiempo de ignición; Δm =3D Pérdida de masa.

 

Fuente: Elabo= ración propia

Los tiempos de ignición, para S. campanulata, F. americana y A. plurijuga, aumentan a medida que la densidad de la madera se incrementa, tanto para el grupo de referencia (C =3D 0 %) como pa= ra las tres concentraciones de sales de boro (Figura 3b)= . Se observa igualmente una tendencia a la dispersión de los valores del tiempo = de ignición a medida que la concentración aumenta. Además, los tiempos de igni= ción, para F. americana y A. plurijuga, aumentan conforme la concentración de sales de boro se incrementa, con fuertes coeficientes de determinación (Figura 4b). Estos resultados coinciden con l= os reportados por Toker et al. (2009) para maderas de Pinus brutia (ρCH = =3D 532 kg m-3) y Fagus orientalis (ρCH =3D 520 kg m-3), las cuales se impregnaron con concentra= ciones de sales de boro similares a las que se utilizaron en esta investigación.  S. campanulata es un caso diferente, ya que muestra = una ligera tendencia a disminuir del tiempo de ignición y un coeficiente de determinación muy débil.

 

P= érdida de masa

Las magnitudes de la pérdida de masa observadas= en S. campanulata, F. americana y A. plurijuga (Tabla 1) = son similares a las que se reportan en la bibliografía para maderas mexicanas (= Tabla 5).= Las pruebas de normalidad en las distribuciones de las muestras de las tres especies, así como de las tres concentraciones de sales de boro y del grupo= de control (C =3D 0 %) fueron normales. Igualmente, para cada especie, en las pruebas de verificación y análisis de varianza hay diferencias estadísticam= ente significativas entre el grupo de control y las tres concentraciones estudia= das (Tabla 3).= Sin embargo, con excepción de S. campanulata, tanto las densidades como los tiempo= s de ignición y la pérdida de masa resultaron no homogéneos entre las cuatro concentraciones.

 

La Figura 3c evidencia que la pérdida de masa disminuye a medida que la densidad de la madera aumenta (Figura 3c)= . Debido a que el protocolo experimental utilizado en esta investigación es diferent= e al reportado en la bibliografía, su contrastación es compleja. Sin embargo, es= ta tendencia coincide con las que se muestran en la Figura 6. = En la Tabla 4 se detallan las correlaciones y coeficientes de determinación, así como las correlaciones lineales construidas con datos recolectados en la literatura = (Tabla 5).=

 

Estos corolarios coinciden con los de Toker et al. (2009) para maderas de Pinus brutia (ρCH =3D 532 kg m-3) y Fagus orientalis (ρCH =3D 520 kg m-3), impre= gnadas con concentraciones de sales de boro similares a las que se utilizaron en e= sta investigación. A partir de esta coincidencia se deduce que la pérdida de ma= sa disminuye cuando la densidad de la madera aumenta. El coeficiente de determinación correspondiente a la correlación calculada, tomando como base= los resultados de esta investigación (Tabla 4),= es en promedio 57 % menor que los coeficientes reportados por los autores mencion= ados en esta tabla. Respecto a la pérdida de masa en función de la concentración= de sales de boro, para F. americana y A. plurijuga, se observan ligeras tendencias a la disminución. Un caso diferente muestra = S. campanulata, cuya regresión es positiva (Figura 4c)= .

 

Figura <= /span>6<= /span>

Dispersiones de la pérdid= a de masa (Δm) en función de las densidades apa= rentes (ρCH) y sus correlaciones, deta= lladas en la Tabla 4

Fuente: Elabo= ración propia

 

   &nbs= p;            &= nbsp;           &nbs= p;            &= nbsp;           &nbs= p;            &= nbsp;           &nbs= p;           4.    Conclusiones

El método baño caliente-frío permite impregnar con sal= es de boro las maderas de S. campanulata, F. american= a y A. plurijuga. El tratamiento con concentraciones d= e 1 %, 2 % y 3 % no altera de manera significativa las densidades de estas tres especies. El impregnado aumenta la resistencia aparente de la madera a la exposición al fuego. Además, retarda los tiempos de ignición y disminuye la pérdida de masa cuando la madera es expuesta al fuego en condiciones de laboratorio.

 

La madera de S. campanulata impregnada con las sales de boro al 3 % presenta las retenciones (6,4 kg m-= 3) y la pérdida de masa (6,4 %) más altas y el tiempo de ignición menor (11,1 s)= .

 

Con todo, las magnitudes de las retenciones, los tiemp= os de ignición y la pérdida de masa son diferentes para cada especie y concentrac= ión. Las retenciones fueron proporcionales a la concentración e inversamente proporcional a la densidad. Los tiempos de ignición se incrementan a medida que la densidad de la madera aumenta y la concentración de sales de boro aumenta. La pérdida de masa disminuye en fun= ción de la densidad aparente de la madera. No se observa tendencias claras respe= cto a la pérdida de masa en función de la concentración de sales de boro. Estos resultados encuentren aplicación práctica en la selección e impregnado de la madera para su uso en la industria de la construcción.

 

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8

Javier Sotomayor Castellanos, Luz Elena Ávila Calderón

7

Reacción al Fuego de Tres Maderas Angiospermas Impregnadas con Sales de Boro

 

Escuela Superior Politécn= ica del Litoral. ESPOL

 

Revista Tecnológica Espol= – RTE Vol. 33, N° 1 (Junio, 2021)

 

Revista Tecnológica Espol= – RTE Vol. 33, N° 1 (Junio, 2021)

 

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