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Chemistry and Materials Research
ISSN 2224- 3224 (Print) ISSN 2225- 0956 (Online)
Vol.3 No.12, 2013

www.iiste.org

Properties of Plastic Bounded Agricultural Waste
Composites II: Physical Properties of Some Composites.
1*

Akinyele S.A. and 2Adeosun, B, O.
Federal Polytechnic, Ado-Ekiti, Nigeria
2
Federal University of Technology Akure (FUTA) Nigeria.
1*
Corresponding author : kinyelesa@yahoo.com.
1

ABSTRACT
Twenty six (26) plastic bounded composites, one unfilled and five each filled separately with varying
contents of cement, limestone, silica-sand, drainage san granite have been formulated and compounded. Their
percentage water absorption was determined. Composites % water absorption was determined. Composites %
shrinkage range from (0.86-8.00) % and % water absorption from (1.03-15.00) %. These results suggest that the
composites under study meet the allowable American Standard for Test Measurement (ASTM) for floor and wall
tile tiles maximum 15% shrinkage and maximum 16% water absorption. If these composites are examined for
mechanical strength, they may be found useful in the building industry for the manufacture of floor and wall
tiles. Using spent pure water (thermoplastic) may result in the control of environmental pollution caused by the
non-biodegradable spent plastic. Key word: plastic bonded composite, floor tile, wall tile, % shrinkage, % water
absorption allowable ASTM.
1.0

INTRODUCTION
The ideal of incorporating agricultural wastes into a composite matrix is not novel; straw was used in a
clay matrix to strength bricks in Egypt long time ago. The by-products of rice, groundnut, cowpea and maize
have been used to produce particle boards which find utility in internal partitioning, celling covering and soundproof Enclosure-building (sampathrajan et al). Today’s composites have move through high technology and has
emerged as engineering materials and as advanced structural composite (Premomony 1990). These recent
composites consist of metal-metal, metal ceramics, plastic-metal-non metal and ceramics-agricultural wastes
particle and fibre boards. They are heterogeneous solid consisting of two or more different materials that may be
mechanically, metallurgically or chemically bonded together (Deganro et al 1980).
The properties of wood cement –bounded particle board have been studied extensively (Sanderinann et
al, 1960; weather wax et al 1964; Bibls et al 1968; Mosleni et al 1983; Oyagade 1992; paramesmeran et al 1978;
Dinwoodie, 1990; 1991. Problems associated with the production of wood cement particle board in tropical
countries are (i) non-compatibility of tropical hardwoods with cement (ii) the large quantity of cement per unit
weight of wood employed in the board manufacture not only makes the resultant board to be heavy, but also
makes cement constitute an costly components of the board. The characteristically high density of the board is a
possible limitation to its use particularly in area where weight saving is essential-like site handling and in
application in situations such as ceiling panels (Bison-Werke, 1974).
The major consumption of synthetic polymers is as plastic materials in the form of molded objects.
After the expiry of the economic use of most plastic materials they constitute environmental pollution
consequent upon the non-biodegradability of plastics. As a means of controlling environmental pollution caused
by spent plastics, spent plastics is now being recycled and filled with agricultural waste and some locally
available material into composites. Some physical properties of the in the present work for possible manufacture
of building materials which has been the exclusion reserve of cement bounded composites.
2.0
Experimental
Material-spent plastic (thermoplastics), spent pure water sachets, collected from the dungs, washed and
sundried. Fillers-limestone was collected were separately collected, died, ground, and sieved to an appropriate
size with the endecotte sieve. drainage sand was also collected, dried and sieved. Silica sand was likewise sieved
(to the same particle size for limestone and drainage sand) after collection, washing and sun drying. For granite
the commercial size was further reduced by a factor of about 1/8 while cement was used as bought. Twenty six
(26) composites were formulated as shown in Table
1Curing –Spent plastics were melted and filled separately with the fillers according to Table 1. The resultant
composite was introduced into cylindrical and rectangular moulds, allowed to cool, removed from the moulds
and kept in cold water for 24 hours before the determination of properties.
3.0
Property determination
Methods for determination of percentage water absorption and percentage shrinkage have been reported
(Samuel and Adeyemi 2004.)

55
Chemistry and Materials Research
ISSN 2224- 3224 (Print) ISSN 2225- 0956 (Online)
Vol.3 No.12, 2013

www.iiste.org

4.0

Result and discussion
The physical properties determined for the twenty six composites as shown in table 1 and 2. It is
observed that the control comrade (plastic only) shows % shrinkage of 1.12%. The composite of drainage sand,
silica sand, limestone, cement and granite shows % shrinkage range of (1.80-2.86)%, (4.00-8.00)%, (2.304.00)% (1.00-4.00)% and (0.86-1.67)% respectively.
The control composite shows % water absorption, while the other composites show the following
values; drainage sand (4.30-14.22)% silica sand (1.03-6.40)%, limestone (1.90-53)% cement (10.60-15.00)% and
granite (2.74-6.65)%. Comparing the values of % water absorption and % shrinkage with the America standard
for test and measurement (ASTM) for floor and wall tiles, all the five composites seem to meet the ASTM.
However, apart from these physical properties the ASTM contains standard for mechanical of these
mechanical properties is the focus of an on-going research effort. It is after the conclusion of this part of the
research that a categorical scientific statement could be made on the suitability of these composites for the
production of floor and wall tiles.
5.0
Conclusion
The result of this work has shown conclusively that all composites examined meet the (ASTM) standard
for the physical properties (% water absorption and % shrinkage) of floor and wall tiles. These are examined for
mechanical strength they may be found useful in the manufacture of industry building materials like tiles and
particle-boards and even compete favourably with wood cement composites. The use of spent thermoplastics this
way would result in the control of environmental pollution caused by this non-biodegrable waste.
Table 1: Compounding formulation of composite
Composite
Components
code no
Thermoplastic
2
62.5
3
62.5
4
62.5
5
62.5
6
62.5
7
62.5
8
62.5
9
62.5
10
62.5
11
62.5
12
62.5
13
62.5
14
62.5
15
62.5
16
62.5
17
62.5
18
62.5
19
62.5
20
62.5
21
62.5
22
62.5
23
62.5
24
62.5
25
62.5
26
62.5

56

filler
28 cement
56 cement
84 cement
112 cement
140 cement
35 limestone
52.5 limestone
70.0 limestone
105 limestone
125 limestone
25 silica sand
50 silica sand
62.5 silica sand
75 silica sand
87.5 silica sand
25 drainage sand
37.5 drainage sand
50 drainage sand
62.5 drainage sand
75 drainage sand
31 granite
46.5 granite
62 granite
77.5 granite
93 granite
Chemistry and Materials Research
ISSN 2224- 3224 (Print) ISSN 2225- 0956 (Online)
Vol.3 No.12, 2013

www.iiste.org

Table 2: Properties examined for the composites
Composite
% shrinkage
1 unfilled
1.12
2 cement
4.00
3 cement
3.00
4 cement
2.90
5 cement
1.00
6 cement
1.15
Range
(1.00-4.00)
7 limestone
4.00
8 limestone
3.33
9 limestone
2.30
10 limestone
2.33
11 limestone
2.73
Range
(2.30-4.00)
12 silica-sand
8.00
13 silica-sand
6.00
14 silica-sand
5.00
15 silica-sand
5.50
16 silica-sand
4.00
Range
(4.00-8.00)
17 drawing sand
2.86
18 drawing sand
2.50
19 drawing sand
2.00
20 drawing sand
2.50
21 drawing sand
1.80
Range
(1.80-2.86)
22 Granite filled
1.62
23 Granite filled
1.40
24 Granite filled
1.10
25 Granite filled
1.00
26 Granite filled
0.86
Range
(0.86-1.67)

% water absorption
1.95
12.7
11.9
15.0
10.6
11.2
(10.6.15.00)
3.70
5.00
1.90
5.30
5.30
(1.90-5.3)
6.40
5.10
1.03
3.80
3.31
(1.03-6.40)
5.4
4.3
13.50
13.90
14.22
(4.30-14.22)
2.79
6.65
5.98
2.33
2.74
(2.74-6.65)

Table 3: American standard for testing and measurement (ASTM) allowable values for floor and wall tiles.
Compressive strength % water absorption
% total shrinkage
Mpa
Floor tile
22.1 (minimum)
16.% (maximum
15% (maximum)
Wall tile
17.2 minimum
16% maximum
15% maximum
References
1.
Sampathrajam A; Vijayraghavan, N. C and Swamniathen K.R (1991): Bio-resource Technology, 35,
67-71.
2.
Premomony, G (1990): Polymer science and Technology of plastic rubber’s Mc Graw- Hill N. 44 pp.
252
3.
Degarmo, P.E, Temple B. J and Ronald K. O (1980); Materials and processing 9th Edn. Macmillan, N4
pp. 193-195.
4.
Sanderman W. presusser, H.J and Schween, W (1960): studies on mineral bonded wood materials. The
effect of wood extractives on the settings of cement-bouded wood materials, Holzforch ung 14 (3); 7077
5.
Weather max R. and Terknow, H. (1964) Effect of wood on the setting of Portland cement forest
products journal 14 (12): 567-570.
6.
Bibles, E.J and Lo, C.F (1968) Sugar and other wood extractives: effect on the setting of southern purecement mixtures. Forest products Journal 18 (8) 28-34.
57
Chemistry and Materials Research
ISSN 2224- 3224 (Print) ISSN 2225- 0956 (Online)
Vol.3 No.12, 2013

7.
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www.iiste.org

Moslemi A.A. (1989): Wood –cement particle products; coming of age in fibre and particle boards
bonded with inorganic binders, conference proceedings. Idaho pp 12-18
Oyagade, A.O. (1992): A preliminary investigation of the influence of some treatments on the
compressive strength on Gmelina arborea wood cement composite, Nigerian Journal of Forestry 22
(1&2): 41-44.
Paramerwaran, N. and Broker, F. W. (1979): Micromorphological investigation on woo-cement
composite after long term use, Holzforeschung 33:97-102.
Dinwoodie J.M (1978): Wood-cement particle board, BRE information building research establishment
no. 1S2/98 2pp
Dinwoodie J.M and Paxton, B.H (1990): A technical assessment of cement-bounded wood particle
boards in fibre and particle boards bonded with inorganic binders. Conference proceedings Idaho pp
115-112
Dinwoodie J.M (1991): Characterising the performance of chipboard in the United Kingdom.
Proceedings 15th Washington State University International Symposium on particle board, T. M
Maloney (Ed) Washingtone State University, pullmanto, Wa pp. 57-78.
Bison-werke (1977): Cement bonded particle board F.A.O portfolio of small-scale wood-based panel
plants 22pp.
Deppe, H.J (1974): on the production and application of cement wood chipboards. Proceedings 8th
Washington State University International Symposium on particle board T.M Maloney (Ed)
Washington State University, Pullmanot, Wa. Pp. 267-287.
Samuel, J.O and M.B Adeyemi (2004): Effects of Silica/clay types and compositions on the properties
of ceramic tiles, JORMAR (1) 42-53.
Oyagade, A.O (1997): Wood-cement composite sheet element for the building construction industries
in Nigeria, The Journal of techno-Science vol.1, 4, 21-30

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Properties of plastic bounded agricultural waste

  • 1. Chemistry and Materials Research ISSN 2224- 3224 (Print) ISSN 2225- 0956 (Online) Vol.3 No.12, 2013 www.iiste.org Properties of Plastic Bounded Agricultural Waste Composites II: Physical Properties of Some Composites. 1* Akinyele S.A. and 2Adeosun, B, O. Federal Polytechnic, Ado-Ekiti, Nigeria 2 Federal University of Technology Akure (FUTA) Nigeria. 1* Corresponding author : kinyelesa@yahoo.com. 1 ABSTRACT Twenty six (26) plastic bounded composites, one unfilled and five each filled separately with varying contents of cement, limestone, silica-sand, drainage san granite have been formulated and compounded. Their percentage water absorption was determined. Composites % water absorption was determined. Composites % shrinkage range from (0.86-8.00) % and % water absorption from (1.03-15.00) %. These results suggest that the composites under study meet the allowable American Standard for Test Measurement (ASTM) for floor and wall tile tiles maximum 15% shrinkage and maximum 16% water absorption. If these composites are examined for mechanical strength, they may be found useful in the building industry for the manufacture of floor and wall tiles. Using spent pure water (thermoplastic) may result in the control of environmental pollution caused by the non-biodegradable spent plastic. Key word: plastic bonded composite, floor tile, wall tile, % shrinkage, % water absorption allowable ASTM. 1.0 INTRODUCTION The ideal of incorporating agricultural wastes into a composite matrix is not novel; straw was used in a clay matrix to strength bricks in Egypt long time ago. The by-products of rice, groundnut, cowpea and maize have been used to produce particle boards which find utility in internal partitioning, celling covering and soundproof Enclosure-building (sampathrajan et al). Today’s composites have move through high technology and has emerged as engineering materials and as advanced structural composite (Premomony 1990). These recent composites consist of metal-metal, metal ceramics, plastic-metal-non metal and ceramics-agricultural wastes particle and fibre boards. They are heterogeneous solid consisting of two or more different materials that may be mechanically, metallurgically or chemically bonded together (Deganro et al 1980). The properties of wood cement –bounded particle board have been studied extensively (Sanderinann et al, 1960; weather wax et al 1964; Bibls et al 1968; Mosleni et al 1983; Oyagade 1992; paramesmeran et al 1978; Dinwoodie, 1990; 1991. Problems associated with the production of wood cement particle board in tropical countries are (i) non-compatibility of tropical hardwoods with cement (ii) the large quantity of cement per unit weight of wood employed in the board manufacture not only makes the resultant board to be heavy, but also makes cement constitute an costly components of the board. The characteristically high density of the board is a possible limitation to its use particularly in area where weight saving is essential-like site handling and in application in situations such as ceiling panels (Bison-Werke, 1974). The major consumption of synthetic polymers is as plastic materials in the form of molded objects. After the expiry of the economic use of most plastic materials they constitute environmental pollution consequent upon the non-biodegradability of plastics. As a means of controlling environmental pollution caused by spent plastics, spent plastics is now being recycled and filled with agricultural waste and some locally available material into composites. Some physical properties of the in the present work for possible manufacture of building materials which has been the exclusion reserve of cement bounded composites. 2.0 Experimental Material-spent plastic (thermoplastics), spent pure water sachets, collected from the dungs, washed and sundried. Fillers-limestone was collected were separately collected, died, ground, and sieved to an appropriate size with the endecotte sieve. drainage sand was also collected, dried and sieved. Silica sand was likewise sieved (to the same particle size for limestone and drainage sand) after collection, washing and sun drying. For granite the commercial size was further reduced by a factor of about 1/8 while cement was used as bought. Twenty six (26) composites were formulated as shown in Table 1Curing –Spent plastics were melted and filled separately with the fillers according to Table 1. The resultant composite was introduced into cylindrical and rectangular moulds, allowed to cool, removed from the moulds and kept in cold water for 24 hours before the determination of properties. 3.0 Property determination Methods for determination of percentage water absorption and percentage shrinkage have been reported (Samuel and Adeyemi 2004.) 55
  • 2. Chemistry and Materials Research ISSN 2224- 3224 (Print) ISSN 2225- 0956 (Online) Vol.3 No.12, 2013 www.iiste.org 4.0 Result and discussion The physical properties determined for the twenty six composites as shown in table 1 and 2. It is observed that the control comrade (plastic only) shows % shrinkage of 1.12%. The composite of drainage sand, silica sand, limestone, cement and granite shows % shrinkage range of (1.80-2.86)%, (4.00-8.00)%, (2.304.00)% (1.00-4.00)% and (0.86-1.67)% respectively. The control composite shows % water absorption, while the other composites show the following values; drainage sand (4.30-14.22)% silica sand (1.03-6.40)%, limestone (1.90-53)% cement (10.60-15.00)% and granite (2.74-6.65)%. Comparing the values of % water absorption and % shrinkage with the America standard for test and measurement (ASTM) for floor and wall tiles, all the five composites seem to meet the ASTM. However, apart from these physical properties the ASTM contains standard for mechanical of these mechanical properties is the focus of an on-going research effort. It is after the conclusion of this part of the research that a categorical scientific statement could be made on the suitability of these composites for the production of floor and wall tiles. 5.0 Conclusion The result of this work has shown conclusively that all composites examined meet the (ASTM) standard for the physical properties (% water absorption and % shrinkage) of floor and wall tiles. These are examined for mechanical strength they may be found useful in the manufacture of industry building materials like tiles and particle-boards and even compete favourably with wood cement composites. The use of spent thermoplastics this way would result in the control of environmental pollution caused by this non-biodegrable waste. Table 1: Compounding formulation of composite Composite Components code no Thermoplastic 2 62.5 3 62.5 4 62.5 5 62.5 6 62.5 7 62.5 8 62.5 9 62.5 10 62.5 11 62.5 12 62.5 13 62.5 14 62.5 15 62.5 16 62.5 17 62.5 18 62.5 19 62.5 20 62.5 21 62.5 22 62.5 23 62.5 24 62.5 25 62.5 26 62.5 56 filler 28 cement 56 cement 84 cement 112 cement 140 cement 35 limestone 52.5 limestone 70.0 limestone 105 limestone 125 limestone 25 silica sand 50 silica sand 62.5 silica sand 75 silica sand 87.5 silica sand 25 drainage sand 37.5 drainage sand 50 drainage sand 62.5 drainage sand 75 drainage sand 31 granite 46.5 granite 62 granite 77.5 granite 93 granite
  • 3. Chemistry and Materials Research ISSN 2224- 3224 (Print) ISSN 2225- 0956 (Online) Vol.3 No.12, 2013 www.iiste.org Table 2: Properties examined for the composites Composite % shrinkage 1 unfilled 1.12 2 cement 4.00 3 cement 3.00 4 cement 2.90 5 cement 1.00 6 cement 1.15 Range (1.00-4.00) 7 limestone 4.00 8 limestone 3.33 9 limestone 2.30 10 limestone 2.33 11 limestone 2.73 Range (2.30-4.00) 12 silica-sand 8.00 13 silica-sand 6.00 14 silica-sand 5.00 15 silica-sand 5.50 16 silica-sand 4.00 Range (4.00-8.00) 17 drawing sand 2.86 18 drawing sand 2.50 19 drawing sand 2.00 20 drawing sand 2.50 21 drawing sand 1.80 Range (1.80-2.86) 22 Granite filled 1.62 23 Granite filled 1.40 24 Granite filled 1.10 25 Granite filled 1.00 26 Granite filled 0.86 Range (0.86-1.67) % water absorption 1.95 12.7 11.9 15.0 10.6 11.2 (10.6.15.00) 3.70 5.00 1.90 5.30 5.30 (1.90-5.3) 6.40 5.10 1.03 3.80 3.31 (1.03-6.40) 5.4 4.3 13.50 13.90 14.22 (4.30-14.22) 2.79 6.65 5.98 2.33 2.74 (2.74-6.65) Table 3: American standard for testing and measurement (ASTM) allowable values for floor and wall tiles. Compressive strength % water absorption % total shrinkage Mpa Floor tile 22.1 (minimum) 16.% (maximum 15% (maximum) Wall tile 17.2 minimum 16% maximum 15% maximum References 1. Sampathrajam A; Vijayraghavan, N. C and Swamniathen K.R (1991): Bio-resource Technology, 35, 67-71. 2. Premomony, G (1990): Polymer science and Technology of plastic rubber’s Mc Graw- Hill N. 44 pp. 252 3. Degarmo, P.E, Temple B. J and Ronald K. O (1980); Materials and processing 9th Edn. Macmillan, N4 pp. 193-195. 4. Sanderman W. presusser, H.J and Schween, W (1960): studies on mineral bonded wood materials. The effect of wood extractives on the settings of cement-bouded wood materials, Holzforch ung 14 (3); 7077 5. Weather max R. and Terknow, H. (1964) Effect of wood on the setting of Portland cement forest products journal 14 (12): 567-570. 6. Bibles, E.J and Lo, C.F (1968) Sugar and other wood extractives: effect on the setting of southern purecement mixtures. Forest products Journal 18 (8) 28-34. 57
  • 4. Chemistry and Materials Research ISSN 2224- 3224 (Print) ISSN 2225- 0956 (Online) Vol.3 No.12, 2013 7. 8. 9. 10. 11. 12. 13. 14. 15. 16. www.iiste.org Moslemi A.A. (1989): Wood –cement particle products; coming of age in fibre and particle boards bonded with inorganic binders, conference proceedings. Idaho pp 12-18 Oyagade, A.O. (1992): A preliminary investigation of the influence of some treatments on the compressive strength on Gmelina arborea wood cement composite, Nigerian Journal of Forestry 22 (1&2): 41-44. Paramerwaran, N. and Broker, F. W. (1979): Micromorphological investigation on woo-cement composite after long term use, Holzforeschung 33:97-102. Dinwoodie J.M (1978): Wood-cement particle board, BRE information building research establishment no. 1S2/98 2pp Dinwoodie J.M and Paxton, B.H (1990): A technical assessment of cement-bounded wood particle boards in fibre and particle boards bonded with inorganic binders. Conference proceedings Idaho pp 115-112 Dinwoodie J.M (1991): Characterising the performance of chipboard in the United Kingdom. Proceedings 15th Washington State University International Symposium on particle board, T. M Maloney (Ed) Washingtone State University, pullmanto, Wa pp. 57-78. Bison-werke (1977): Cement bonded particle board F.A.O portfolio of small-scale wood-based panel plants 22pp. Deppe, H.J (1974): on the production and application of cement wood chipboards. Proceedings 8th Washington State University International Symposium on particle board T.M Maloney (Ed) Washington State University, Pullmanot, Wa. Pp. 267-287. Samuel, J.O and M.B Adeyemi (2004): Effects of Silica/clay types and compositions on the properties of ceramic tiles, JORMAR (1) 42-53. Oyagade, A.O (1997): Wood-cement composite sheet element for the building construction industries in Nigeria, The Journal of techno-Science vol.1, 4, 21-30 58
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