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 Elaboración de productos de fibrocemento a partir de residuos de cuero.

 

Fiber cement products fabrication from leather residues.

Calderón Segundo Hugo.[1= ], Parada Rivera Mabel Mariela.[2], Andrade Avalos Mónica Lilián[3] &= amp; Borja Mayorga Danielita Fernanda[4]

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Recibido: 27-05-2019 / Revisado= : 25-06-2019 /Aceptado: 24-07-2019/ Publicado: 30-07-2019

 

Abstract.          =                       DOI: https://doi.org= /10.33262/cienciadigital.v3i3.2.763

 

Substitution of chrysotile in fibro cement boar= ds becomes relevant because it may be included as a dangerous product in the E= cuadorian legislation, due to its possible carcinogenic effects. The incorporation of leather residues (LR) in fibro cement boards were studied elaborating test probes containing 5%, 6%, 7%, 10% and 13.66% of leather residues.  The quality properties considered were: modulus of rupture (MOR), bulk density (Bd) and absorption of water % (Abs = %). The requirements were MOR > 4MPa (NTE INEN 2080:1996), Bd > 1, 37 g/ml and % Abs <2= 8% (Tubasec C.A. own standard). The 10% LR mix satisfied t= he máximum quality requirements (MOR=3D6,46  MPa, Bd=3D1,46 g/ml, %Abs=3D27,88 %), including  the Chi-square test of statistical significance (CHI2= =3D0,666). The 13,66%  LR mix had the best perform= ance with respect to the modulus of rupture, but it did not satisfied the bulk density nor the  absorption of wate= r% (MOR=3D6,53  MPa, Bd=3D1,33 g/ml, %= Abs=3D34 %).

Keywords= : Fiber cement, chrysotile, leather resid= ues, construction material.

Resumen       

                =                    

El estudio de la sustitución del crisotilo, que se utiliza en láminas de fibro cemento, se hace pertinente ante la posibilidad= de que dicho material sea incluido como producto peligroso dentro de la Normat= iva Ecuatoriana, por sus posibles efectos cancerígenos. Para estudiar la incorp= oración de residuos de cuero (RC) en las láminas= se fabricaron probetas con 5%, 6%, 7%, 10%  y 13,66% de residuos de cuero.  Las propiedades de calidad evaluadas fueron: módulo de rotura (MOR), densidad aparente (Da) y % de absorción de agua (%Abs). =  Los requisitos a cumplir fu= eron MOR >4MPa (NTE INEN 2080:1996), Da >1,37g/ml y %= Abs <28% (Norma interna Tubasec C.A.). La mezcla con 10% de RC  fue la que cumplió con la mayor cantida= d de requisitos de calidad (MOR=3D6,46  = MPa, Da=3D1,46 g/ml, %Abs=3D27,88 %), incluyendo la = prueba que verifica la significancia estadística (CHI2=3D0,666). La mezcla con 13,66%  de RC tuvo el mejor desempeńo con respecto al módulo de rotura, pero estuvo fuera del rango referencial, tanto de la densidad aparente como del % absorción de agua (MOR=3D6,53  MPa,= Da=3D1,33 g/ml, %Abs=3D34 %).

Palabras clave<= /span>: Fibro cemento, cr= isotilo, residuos cuero, material construcción.

Introducción.

Los residuos sólidos de la industria del cuero aparecen como una alternativa al crisotilo en las láminas de fibrocemento, utilizadas en la construcción de viviendas como paredes interiores. El crisolito brinda a los productos de fibrocemento mayor resistencia, durabilidad y acabado. El crisotilo es un mineral que cristal= iza en el sistema monoclínico o triclínico formando fibras. Su fórmula química es = Mg3(Si2O5)(OH)4 y se le conoce con el nombre de amianto o asbesto. = La búsqueda de un material sustituto al crisotilo = se debe a que se ha demostrado que es un material cancerígeno y existe la posibilidad que sea prohibido su uso en Ecuador.

En los ańos anteriores a 1988, los estudios realizados en personas q= ue trabajaban en las minas o en fábricas, para relacionar el crisotilo como causante del mesotelioma, no había sido confirmado de manera categóric= a (Dunningan, 1988). Ahora bien, en estudios más recient= es se estableció que los asbestos con crisotilo eran = la causa de asbestosis y cáncer de pulmón (Smith y col., 1996) y también la ca= usa de mesotelioma (Frank y col., 1998; Yano y col., 2009; Egilman y col., 2011). Otros estudios tam= bién confirmaron que en la fabricación de textiles, donde se usaba 100% crisotilo, el riesgo de desarrollar cáncer de pulmón = era muy alto (Dement y col., 1994). <= /b>

Entre los usos del crisotilo se pueden mencionar: aislante para tuberías y equipos, techos, lámina para paredes, pastillas de freno, aislante para cables eléctricos, pinturas antifuego, textiles, entre otros (Ro= wson, 1978; Virta, 2006). Los residuos de cuero han sido investigados para ser usados, en combinación con yeso, en la producción de láminas para cielos rasos (Faim y col., 2002). El uso de los residuos de cuero p= ara ser incorporados en ladrillos de arcilla también ha sido estudiado (Aguiar y col., 2002). Aunque los ladrillos resultaron menos resistentes, su menor pe= so y mayor porosidad les permitiría ser usados como aislantes. Senthil y col., 2015 estudiaron la combinación de residuos de cuero con goma natural de latex para producir láminas, cuyo uso sería en suelas de zapatos y otros productos para recubie= rtas interiores del hogar.

Adicionalmente, debe mencionarse que los residuos de la industria del cuero pueden contener restos de cromo hexavalente el cual es peligroso para= el medio ambiente. Por lo tanto, la incorporación de estos residuos en materia= les de construcción o en fibras poliméricas, ayudaría a disminuir este problema= de su eliminación (Sekaran y col., 2017; Lakraia y col., 2012; El-Sabbagh y col., 2010).

En el afán de promover la mejora continua y la innovación,  la  búsqueda  de  nuevos  materiales que  puedan  servir  como sustitutos del = crisotilo, se hace pertinente ante la posibilidad de = que éste último sea incluido como material peligroso dentro de la Normativa Ecuatoriana.=

En este orden = de ideas, se plantea el estudio de la sustitución del crisotilo, que se utiliza en láminas= de fibro cemento en la siguiente proporción en peso: 7% = crisotilo, 76% cemento y 17% aditivos, por residuos de la industria del cuero.

Procedimiento Experimental=

Materiales y métodos

Cemento Portland

Cemento Chimbo= razo Portland Puzolánico Tipo IP producido con Clinker, adiciones minerales y sulfato de calcio. Sus características técnicas se muestran en la Tabla 1.<= /span> =

Tabla 1. Características técnicas cemento Portland

Requisitos Químicos

 

MgO (%)

1,99

SO3(%)

1,75

Pérdida por ignición(%)

2,14

Requisitos Físicos

 =

Peso específico(g/ml)

2,85

Expansión en autoclave(%)

0,0013=

Fraguado Vicat Inicial(minuto)<= /b>

160

Fraguado Vicat Final(minuto)

240

Resistencia a Compresión

 =

3 días (MPa)

18

7 días (MPa)

26

28 días (MPa)

37

Toba o roca volcánica

Roca ígnea volcánica molida a un tamiza= do de malla N°200.

Residuos o virutas de cuero

Residuos sólidos de cuero provenientes = de la empresa Curtiem= bre TUNGURAHUA. S.A., Riobamba, Ecuador. En la Figura 1 se muestra el material utilizado= .

Figura 1. Virutas o residuos de cuero.

Aditivos

Compuestos químicos confidenciales de la Empresa Tubasec C.A., Riobamba, Ecuador. La mez= cla denominada estándar posee crisotilo (±7%) entre= los aditivos.

 

Elaboración de las probetas

Para estudiar la posibilidad de sustitu= ir el crisotilo por residuos de cuero en las lámin= as de fibrocemento, se elaboraron probetas con las diferentes proporciones de residuos o virutas de cuero y se compararon las semejanzas en  calidad con las manufacturadas por la E= mpresa TUBASEC C.A. El procedimiento utilizado en la fabricación de las probetas se muestra en la Figura 2.

 

 

Figura 2. Procedimiento para la elaboración de las probetas.

 

El tamańo de las probetas fue fabricado= de acuerdo a la norma NTE INEN 2080:1996. Las dimensiones de las mismas fue 250x250x20 mm.

 

 

Composición de las mezclas

Las mezclas a ser estudiadas se muestra= n en la Tabla 2.

 

Tabla 2. Composición de las mezclas a ser estudiadas

 

 

% Cemento=

% Toba

% Res. Cu= ero

% Aditivo= s

Estándar<= span style=3D'mso-bidi-font-weight:bold'>

76,17<= o:p>

3,58

20,25<= o:p>

Mezcla 1<= span style=3D'mso-bidi-font-weight:bold'>

76,17<= o:p>

3,58

5=

15,25<= o:p>

Mezcla 2<= span style=3D'mso-bidi-font-weight:bold'>

76,17<= o:p>

3,58

6=

14,25<= o:p>

Mezcla 3<= span style=3D'mso-bidi-font-weight:bold'>

76,17<= o:p>

3,58

7=

13,25<= o:p>

Mezcla 4<= span style=3D'mso-bidi-font-weight:bold'>

76,17<= o:p>

2,09

10

11,74<= o:p>

Mezcla 5<= span style=3D'mso-bidi-font-weight:bold'>

76,17<= o:p>

2,58

13,66<= o:p>

7,59

 

Propiedades físicas y mecánicas

Una vez preparadas las probetas (siguie= ndo el procedimiento mostrado en la Figura 2) se procedió a seleccionar aquellas que no tuvieran grietas y que fueran las más uniformes en su espesor. Las propiedades de calidad evaluadas fueron: módulo de rotura, densidad aparent= e y absorción de agua (NTE INEN 2080, 1996; NTE INEN 208= 2, 1996). El módulo de rotura se midió utilizando u= na Máquina Universal de Ensayos (NESTOR) a una tasa de extensión de 5 mm/min. = (Ver Figura 3). La densidad aparente de la probeta  se calculó con el peso seco de la probeta (secado a 105°C por 24hr) = y su volumen medido por desplazamiento de líquido. La absorción de agua se deter= minó mediante la diferencia entre el peso seco y el peso saturado (después de 24= hr sumergido en agua).

 

 

Figura 3. Máquina Universal de Ensayos

Se considera una relación factible de l= as variables de calidad, aquellas mezclas que mantengan las mismas tendencias = en el tiempo de fraguado, con respecto a la mezcla estándar o patrón (con crisotilo).

 

Normativa a cumplir

Las probetas deben cumplir con las especificaciones que se muestran en la Tabla 3.

 

Tabla 3. Especificaciones a cumplir

 

NTE INEN = 2080

TUBASEC C= .A.

Módulo de Rotura (MPa) Min.

4=

10 <= b>

Densidad Aparente (g/ml) Min.

 =

1,37

Absorción de Agua (%) Max.

 =

28

    

 

Población de estudio

Se seleccionaron 162 probetas, luego de descartar aquellas defectuosas, para las pruebas de calidad, 27 para cada mezcla y estándar (27x6). Se seleccionaron las 27 mejores para cada grupo; = sin grietas, lo más planas posibles y espesor constante medido en varios puntos= . Se escogieron nueve probetas para  los distintos tiempos de fraguado, 7, 14 y 21 días respectivamente.

 

Análisis Estadístico

Se presentan los valores promedios y desviación estándar de las variables medidas. Se aplicó la prueba Chi Cuadrado (p<0,5 y 2 grados de libertad) a los valores de la MOR de las probetas estándar (7, 14 y 21 días= ) en conjunto con cada una de las composiciones de residuos de cuero, para la verificación de la independencia de dos variables y así verificar el cumpli= miento de la normativa NTE INEN 2084:1996.

 

 

Resultados y Discusión

 

La primera prueba que se le realiza a las probetas es su resistencia= a la flexión o módulo de rotura (MOR), el cual se calcula a través de la Ecua= ción 1:

 

P=3D Carga promedio(N)

L=3DDistancia entre apoyos (0,215 m NTE INEN 2080:1996)

A=3D Ancho de la probeta (0,25 m NTE INEN 2080:1996)

e=3D Espesor de la probe= ta (m)

 

El MOR se calcula para las probetas estándar y para cada una de las probetas con las mezclas consideradas (5%,6%,7%,10% y 13,66% de residuos de cuero, mezclas 1, 2, 3, 4 y 5 respectivamente). Las Figuras 4 y 5 muestran = los valores del MOR en función de los días de fraguado considerados para los ca= sos estudiados. Adicionalmente, se incluye el valor de la norma NTE INEN 2084:1= 996.

Figura 4. MOR de las probetas en función de los días de fraguado para= las probetas estándar, Norma, 5%, 6% y 7% de residuos de cuero.

 

Figura 5. MOR de las probetas en función de los días de fraguado para= las probetas estándar, Norma, 10% y 13,66% de residuos de cuero.

 

El primer aspecto a destacar al ver las Figuras 4 y 5 es la tendencia creciente del MOR a medida que aumenta el tiempo de fraguado, tanto para la probeta estándar como para todas las mezclas con cuero, lo cual es razonable debido a que mientras más seca la probeta mayor es la fuerza necesaria para romperla. Otro aspecto resaltante es que el MOR de la probeta patrón o está= ndar es mayor que todas las mezclas con residuos de cuero en todos los tiempos de fraguado, duplicándola en algunos casos. Finalmente, también se puede obser= var que todas las probetas de las mezclas cumplen con la Norma de 4 MPa, except= o 2 probetas de la mezcla de 7%.

 

Los valores promedio y su desviación estándar para el MOR de todas l= as probetas se muestran en la Tabla 4. Como puede observarse en la Tabla 4, to= dos los valores promedio obtenidos cumplen con la norma NTE INEN 2084:1996, cuyo valor para láminas de fibrocemento Categoría 1, Tipo B es 4 MPa.=

 

 

Tabla 4. Valores promedio y desviación estándar del MOR

 

MOR<= /o:p>

Desviació= n

Probetas<= span style=3D'mso-bidi-font-weight:bold'>

Promedio,= MPa

Estándar<= o:p>

Estándar<= o:p>

10,12<= o:p>

1,186<= o:p>

Mezcla 1<= o:p>

5,85

0,510<= o:p>

Mezcla 2<= o:p>

6,02

1,077<= o:p>

Mezcla 3<= o:p>

4,70

0,558<= o:p>

Mezcla 4<= o:p>

6,46

0,531<= o:p>

Mezcla 5<= o:p>

6,53

0,692<= o:p>

 

Adicionalmente, la prueba estadística CHI2 se aplicó a la serie de datos de todas las mezclas, tomando como relación la serie de dato= s de las probetas estándar, que cumple en forma excedida, con la norma NTE INEN 2084:1996. Las filas (3) de datos considerados fueron los tiempos de fragua= do (7, 14 y 21 días) y las columnas (2) los MOR de las probetas estándar  y los MOR de las probetas con residuos = de cuero. Se consideró como hipótesis nula, H0, el cumplimiento con= la norma NTE INEN 2084 y como hipótesis 1, H1, el no cumplimiento c= on la norma. El valor de CHI2 teórico para 2 grados de libertad y u= na probabilidad mayor de 50%  es 1,386= 3. Si CHI2 calculado< CHI2 teórico, se rechaza H1. Si CHI2 calculado> CHI2 teórico, se rechaza = H0. En la Tabla 5 se enseńa el análisis CHI2.

 

Tabla 5. Prueba CHI2 para los datos de = los distintos contenidos de residuos de cuero

 

CHI2=

 

CHI2=

Calculado=

 

Teórico

Mezcla 1<= o:p>

1,827<= o:p>

> 

1,3863=

Mezcla 2<= o:p>

1,761<= o:p>

> 

1,3863=

Mezcla 3<= o:p>

1,457<= o:p>

> 

1,3863=

Mezcla 4<= o:p>

0,666<= o:p>

< 

1,3863=

Mezcla 5<= o:p>

2,659<= o:p>

> 

1,3863=

 

La Tabla 5 muestra, que al usar la prueba estadística CHI2= , la única mezcla que cump= le con la norma NTE INEN 2084:1996 es la Mezcla 4, que corresponde a un conten= ido de residuos de cuero de 10%.

La densidad aparente de las láminas de fibrocemento debe ser reportada por el fabricante. Para el caso = que nos concierne, la empresa TUBASEC C.A. ha establecido un valor de referencia mínimo de 1,37 g/ml. Las Figuras 6 y 7 enseńan la densidad aparente de las probetas estándar, la norma y para cada una de las probetas con las mezclas consideradas (5%, 6%, 7%, 10%  y 13= ,66% de residuos de cuero, mezclas 1, 2, 3, 4 y 5 respectivamente).

La densidad aparente (Da) = se calculó utilizando la ecuación 2, con la masa en gramos y el volumen desplazad= o en mililitros.

 

 

En la Figura 6 se puede observar que la tendencia de la densidad de las probetas estándar es decreciente con el tiempo de fraguado. Las tendencias de las mezclas de 5%,= 6% y 7% de cuero son crecientes, lo que es contrario al comportamiento del pat= rón. En relación al cumplimiento del valor referencial de 1,37 g/ml, todas las mezclas lo cumplen.

Figura 6. Densidad Aparente de las probetas en función de los días de fraguado para las probetas estándar, Norma, 5%, 6% y 7% de residuos= de cuero.

En la Figura 7 se puede observar que las tendencias de las Da de las mezclas de 10% y 13,66% de cue= ro son decrecientes al igual que la tendencia de las probetas estándar, lo cua= l es el comportamiento deseado. Las probetas de 10% cumplen con la norma referen= cial de 1,37 g/ml mientras las de 13,66%, en su mayoría no cumplen. Se especula = que la densidad del cuero estaría afectando los límites sugeridos al llegar a d= icha proporción.

           

Figura 7. Densidad Aparente de las probetas en función de los días de fraguado para las probetas estándar, Norma, 10% y 13,66% de residuo= s de cuero

 

En la Tabla 6 se observan los valores promedio y su desviación estándar= de las densidades. Los datos muestran que en promedio la única mezcla que no cumple con el valor referencial es la de 13,66% de cuero. Todas las mezclas resultan más livianas que la estándar y eso se explica por el contenido de cuero cuya densidad es menor.

Tabla 6. Valores promedi= o y desviación estándar de la densidad aparente de las probetas

 

Densidad Aparente

Desviació= n

Probetas<= span style=3D'mso-bidi-font-weight:bold'>

Promedio, g/ml

Estándar<= o:p>

Estándar<= o:p>

1,58

0,036<= o:p>

Mezcla 1<= o:p>

1,48

0,031<= o:p>

Mezcla 2<= o:p>

1,48

0,032<= o:p>

Mezcla 3<= o:p>

1,46

0,044<= o:p>

Mezcla 4<= o:p>

1,46

0,033<= o:p>

Mezcla 5<= o:p>

1,33

0,046<= o:p>

 

 

La cantidad de agua absorbida (%Abs) por las probetas, luego de sumergida por 24 horas, se midió como otra variable de calidad de las láminas de fibrocemento. Esta propiedad está relacionada con= la impermeabilidad y flexibilidad del material. La cantidad de agua se determinó como el porcentaje absorbido y se calculó mediante la ecuación 3.=

 

 

En la Figura 8 se puede observar que la tendencia del % de absorción de agua de las probetas estánd= ar es creciente con el tiempo de fraguado. Las tendencias de las mezclas de 5%= , 6% y 7%  de cuero son decrecientes, lo= que es contrario al comportamiento del patrón, esto significa que estas proporciones de cuero se podrían estar consolidando de tal forma que su porosidad es menor con el paso del tiempo y por lo tanto absorben menos agu= a.

 

 

Figura 8. Absorción de agua de las probetas en función de los días de fraguado para las probetas estándar, Norma, 5%, 6% y 7% de residuos de cuer= o.

 

En la Figura 9 se puede observar que las tendencias del % de absorción = de agua de las mezclas de 10% y 13,66%  de cuero son crecientes, igual al comportamiento del patrón, lo cual es la res= puesta deseada.

Figura 9. Absorción de agua de las probetas en función de los días de fraguado para las probetas estándar, Norma, 10% y 13,66% de residuos de cue= ro.

 

En la Tabla 7 se muestran los valores promedio y su desviación estándar= del % de absorción de agua. El valor referencial a cumplir es un % de absorción máximo de 28%. Los datos enseńan que en promedio la única mezcla que no cum= ple con el valor referencial es la de 13,66% de cuero (mezcla 5). Sin embargo, también puede notarse, que los valores promedio de las demás mezclas están = muy cerca del valor referencial (0,12% a 0,82% por debajo).

 

Tabla 7. Valores promedio y desviación estándar = de la absorción de agua de las probetas

 

Absorción=

Desviació= n

Probetas<= o:p>

Promedio,= %

Estándar<= o:p>

Estándar<= o:p>

23,51<= o:p>

1,378<= o:p>

Mezcla 1<= o:p>

27,68<= o:p>

1,422<= o:p>

Mezcla 2<= o:p>

27,08<= o:p>

1,669<= o:p>

Mezcla 3<= o:p>

27,78<= o:p>

2,896<= o:p>

Mezcla 4<= o:p>

27,88<= o:p>

1,623<= o:p>

Mezcla 5<= o:p>

34,18<= o:p>

2,488<= o:p>

 

Conclusiones

Se pudo demostrar la factibilidad de utilizar residuos o virutas de la industria de cuero ecuatoriana como componente de las láminas de fibrocemen= to fabricadas en la empresa Tubasec C.A.

Aunque todas las mezclas cumplieron con el requisito del módulo de rotu= ra (MOR>4 MPa, NTE INEN 2084:1996), las mezclas 5%, 6% y 7% presentaron tendencias opuestas a la mezcla estándar (con crisotil= o) tanto en la densidad aparente como en el % absorción de agua, por lo cual quedaron descartadas por no cumplir con los criterios de calidad establecid= os.

Las mezclas 4 (10% cuero) y 5 (13,66% de cuero) fueron las que cumplier= on con los requisitos de calidad.

La mezcla 4, fue la que cumplió con la mayor cantidad de requisitos de calidad (MOR=3D6,46 MPa, Da=3D1,46 g/ml >1,37 g/ml, %Abs=3D27,88% <28%), incluyendo la prueba que verifica la significancia estadísti= ca (CHI2=3D0,666<1,3863).

La mezcla 5 tuvo el mejor desempeńo con respecto a la resistencia a la flexión o módulo de rotura, pero estuvo fuera del rango referencial, tanto = de la densidad aparente como del % absorción de agua (MOR=3D6,53 MPa, Da=3D1,3= 3 g/ml <1,37 g/ml, %Abs=3D34% >28%). Cabe mencio= nar que la norma NTE INEN 2080 solo exige reportar la densidad aparente y el % de absorción de agua. Los valores mostrados son normas internas de la empresa = Tubasec C.A.

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PARA CITAR EL ARTÍCULO INDEXADO.=

 

 

Calderón, S. H., Parada Rivera, M., Andrade Lilián, M., & Bor= ja Mayorga, D. (2019). Elaboración de productos de fibrocemento a partir de residuos de cuero. Ciencia Digital, 3(3.2), 314-331. https://doi.org= /10.33262/cienciadigital.v3i3.2.763

 


 

 

 

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

El artículo queda en propiedad de la revista y, por tanto, su publicación parc= ial y/o total en otro medio tiene que ser autorizado por el director de la Revista Ciencia Digital.

 

 



[1= ] Escuela Superior Politécnica de Chimb= orazo, Facultad de Ciencias, Chimborazo, Ecuador hcalderon@espoch.edu.ec.

[2= ] Escuela Superior Politécnica de Chimb= orazo, Facultad de Ciencias, Chimborazo, Ecuador, mparada@espoch.edu.ec.

[3= ] Escuela Superior Politécnica de Chimb= orazo, Facultad de Ciencias, Chimborazo, Ecuador, moandrade@espoch.edu.ec.

[4= ] Escuela Superior Politécnica de Chimb= orazo, Facultad de Ciencias, Chimborazo, Ecuador, dborja@espoch.edu.ec.

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