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Electrical Conductivity of Lignocellulose Composites Loaded with Copper powders

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This article is concerned with synthesis and characterization of electroconductive composite materials prepared by the compression molding of mixtures of lignocellulose and electrochemically deposited copper powder under different pressures, and investigation of the influence of particle size on conductivity and percolation threshold of obtained composites. Electrodeposited copper powder content was varied from 2.0-29.8 vol%. Analysis of the most significant properties of individual components and prepared composites included structural and morphological analysis and measurements of hardness and electrical conductivity. Hardness of the investigated composites, as expected, increased with the increase of the processing pressure, as well as lowering the particle size compared to previous work. The significant increase of the electrical conductivity can be observed as the copper powder content reaches the percolation threshold. The packaging effect and more pronounced interpartical contact with smaller, highly porous, highly dendritic particles with high values of specific area lead to “movement” of percolation threshold towards lower filler content, which for the particles
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Electrical Conductivity of Lignocellulose Composites Loaded with Copper powders Tailoring new composites within a perspective of sustainable development is applied to more and more materials. Ecological concerns have resulted in a renewed interest in natural, renewable resources-based and compostable materials, and therefore issues such as materials elimination and environmental safety are becoming important. For these reasons, material components such as natural fibers, biodegradable polymers obtained from biomass can be considered as ‘‘interesting’’ – environmentally safe – alternatives for the development of new biodegradable composites (biocomposites). Biomass is defined as consisting of all plant and plant- derived materials including livestock manures. The main classification of biodegradable polymers in different families is: agro-polymers (e.g., polysaccharides) obtained from biomass by fractionation; polyesters, which are obtained by fermentation from biomass or from genetically modified plants (e.g., polyhydroxyalkanoate: PHA); polymers synthesized from monomers obtained from biomass (e.g., polylactic acid: PLA); and polyesters synthesized by petrochemical process (e.g., polycaprolactone: PCL, polyesteramide: PEA, aliphatic or aromatic copolyesters), from fossil resources [1]. A large number of these biodegradable polymers are commercially available. They show a large range of properties and at present, they can compete with
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Tailoring new composites within a perspective of sustainable development is applied to more and more materials

Electrical Conductivity of Lignocellulose Composites Loaded with Copper powdersTailoring new composites within a perspective of sustainable development is applied to more and more materials. Ecological concerns have resulted in a renewed interest in natural, renewable resources-based and compostable materials, and therefore issues such as materials elimination and environmental safety are becoming important. For these reasons, material components such as natural fibers, biodegradable polymers obtained from biomass can be considered as interesting environmentally safe alternatives for the development of new biodegradable composites (biocomposites).

Biomass is defined as consisting of all plant and plant-derived materials including livestock manures. The main classification of biodegradable polymers in different families is: agro-polymers (e.g., polysaccharides) obtained from biomass by fractionation; polyesters, which are obtained by fermentation from biomass or from genetically modified plants (e.g., polyhydroxyalkanoate: PHA); polymers synthesized from monomers obtained from biomass (e.g., polylactic acid: PLA); and polyesters synthesized by petrochemical process (e.g., polycaprolactone: PCL, polyesteramide: PEA, aliphatic or aromatic copolyesters), from fossil resources [1]. A large number of these biodegradable polymers are commercially available. They show a large range of properties and at present, they can compete with non-biodegradable polymers in different industrial fields (e.g., packaging, agriculture, hygiene, and cutlery) [2].

Lignocellulosic biomass is the nonstarch, fibrous part of plant material and is an attractive resource because it is renewable and abundant [3]. Lignocellulose-based fibers are the most widely used. Intrinsically, these fibers have a number of interesting mechanical and physical properties [4-6]. The structural and chemical composition of lignocellulosic feedstocks is highly variable because of genetic and environmental influences and their interactions (Table 1). Table 1 lists general characteristics of agriculture-derived biomass, specifically crop residues from corn and small grains and dedicated perennial grasses, and other potential biomass resources [2].

Chemical composition of lignocellulosic feedstocks is a key factor affecting properties of this biodegradable polymer and its composites [7, 8]. With their environmentally friendly character and some techno-economical advantages, these fibres motivate more and more different industrial sectors (automotive) to replace common fibreglass, for example. Biocomposites are obtained by the combination of biodegradable polymer as the matrix material and fillers [1].

Lignocellulose is the term used to describe the three-dimensional polymeric composites formed by plants as structural material. It consists of variable amounts of cellulose, hemicellulose, and lignin [2]. Lignocellulosic feedstocks are composed primarily of carbohydrate polymers (cellulose and hemicellulose) and phenolic polymers (lignin). Lower concentrations of various other compounds, such as proteins, acids, salts, and minerals, are also present. Cellulose, the most abundant naturally occurring plant polysaccharide, consists of long chains of anhydro--D-glukopyranose units (AGU) with each cellulose molecule having three hydroxyl groups per AGU, with the exception of the terminal ends, whereas hemicellulose is the second most abundant plant polysaccharide readily available, especially from annual plants and agriculture crop residues such as corn cobs, corn grain, wheat stems, seed coats, and sugar cane stalks. Polysaccharides associated with hemicellulose constitute the cell wall of land plants; D-glucoronic acid, L-arabinose, and D-xylose are present in the cell wall of corn cobs in the approximate ratio of 2:7:19, respectively [9]. Lignin (1525% of total feedstock dry matter) is polyphenolic structural constituent of plants. It is the largest non-carbohydrate fraction of lignocellulose. Unlike cellulose and hemicellulose, lignin cannot be utilized in fermentation processes; however, it may be useful for other purposes. Other compounds present in lignocellulosic feedstocks are known as extractives. These include resins, fats and fatty acids, phenolics, phytosterols, salts, minerals, and other compounds [2].

Cellulose and hemicellulose typically make up two-thirds of cell wall dry matter and can be hydrolyzed to sugars and then fermented to ethanol. Also, both cellulose and hemicelluloses have properties for potential use in the biomedical area, as they have the ability to pass through the digestive tract unchanged. Owing to their resistance to digestion, they are eligible as potential excipients that could be used in the pharmaceutical industry [10].

The research effort on electrically conducting polymer composites filled with metallic powders has had a great development in the last two decades. The addition of metals fillers into a polymer matrix allows enables the preservation of the mechanical properties of the polymer while exploiting the electrical conduction properties of the metal [11]. The conductivity of filled polymers is usually strongly dependent on the nature of the contact between the conductive filler elements and depends critically on the volume fraction of the conducting filler particles, and is well explained by percolation theory [12-14].

Table 1: Composition of different natural lignocellulosic feedstocks [2].CelluloseHemi-

celluloseLigninAcid

detergent

ligninCrude

ProteinAsh

Crop residues

Corn stover382619456

Soybean3314-1456

Wheat straw382915946

Rye straw3125-336

Barley straw4228-7711

Warm-season grasses

Switchgrass372919636

Big bluestem372818666

Indiangrass3929-638

Little bluestem3531---7

Prairie cordgrass4133-636

Miscanthus432419-32

Cool-season grasses

Intermediate wheatgrass3529-636

Reed canarygrass2436-2108

Smooth bromegrass3236-6148

Timothyb2830-576

Tall fescue252514-1311

Other crops

Alfalfa2712-8179

Forage sorghum341716--5

Sweet sorghum231411--5

Pearl millet2535-3109

Sudangrass3327-81212

Information about numerous existing possibilities of polymers containing dispersed conductive fillers and various methods of manufacture of such materials have been reported widely in the literature for the last years [1522]. Metal-filled conducting polymer composites have found uses in electromagnetic shielding of computers and electronic equipment, as conducting adhesives in electronics packaging, underfill for flip chips, cold solders, switching devices, static charge dissipating materials and devices for surge protection [11, 23-26]. Also they found numerous technological applications as self regulating heater, photothermal optical recording, direction finding antennas, chemical detecting sensors used in electronic noses, chemical and electrochemical catalysts and adsorbents [27-33].

These polymer-based electrically conducting composites have several advantages over their pure metal counterparts, including lower cost, ease of manufacture, high flexibility, reduced weight, mechanical shock absorption ability, corrosion resistance, and conductivity control [11].The method most often employed to alter the electrical properties of a polymer is an extrinsic approach whereby the insulating polymer is combined with a conductive additive. It is known that, in general, the percolation theory is used to describe the nonlinear electrical conductivity of extrinsic conductive polymer composites. Hence, the electrical conductivity of polymer composites does not increase continuously with increasing electroconductive filler content. The conducting additive is incorporated into polymers at levels that allow the composite to maintain its electrically insulative qualities, as well as at higher levels, which allow the composite to become electrically semiconductive. As the volume fraction of the conducting filler particles increases, the particles come into contact with one another to form the conduction paths through the composite. As the result there is a critical composition (percolation threshold) at which the conductivity increases by some orders of magnitude from the insulating range to values in the semiconductive or metallic range [12,13,16].For efficiency and in order to decrease the difficulty of the process and economic costs, the amount of the conductive phase for achieving materials with high conductivity should be usually as small as possible. The percolation threshold is typically 1530 vol.% for dense spherical micron size particles [11, 16, 23, 25] A huge number of different models have been proposed for the estimation of the conductivity (or inverse resistivity) vs. filler concentration curves [34 - 39].

The aim of this work was to investigate electrical properties of copper powder filled lignocellulose matrix composites produced under different pressures, as well to compare the obtained results with previous research in this field and percolation theories.Materials and methods

Given that one of the most abundant sources of lignocellulose is corn cob, the matrix natural polymer used in experiments was a commercial grade lignocellulose produced by Maize Research Institute "Zemun Polje" [15]. Celgran C fraction was used, with particle size below 88 m. Chemical composition of Celgran C fraction including moistrue, ash, oil, protein and nitrogen free extracts content is given in Table 2. Composition of lignocellulose complex of cob fraction is given in Table 3. All presented data were statistically analysed using variance analysis (LSD) for unifactorial experiment with randomized block design [15].Table 2. Chemical composition of Celgran ( C fraction [15]Fraction Moisture

(%)Ash

(%)Oil

(%)Protein

(%)NFE

(%)

C11.201.210.064.3165.10

LSD 0.010.3140.3140.3140.3140.314

NFE nitrogen free extractsTable 3. Lignocellulose complex of cob fraction [15]FractionCellulose (%)Hemicellulose

(%)Lignin

(%)NDF (%)ADF (%)

C29.4039.706.6079.439.7

LSD 0.010.4440.3140.3140.5440.314

NDF - neutral detergent fiber

ADF - acidic detergent fiber

Table 4. Physical and chemical properties of Celgran ( C fraction [15]FractionCLSD0.01

Solubility - %

Water11.150.314

Ethanol5,00 0,314

Acetone10,99 0,314

Sodium hydroxide25,96 0,314

Absorption - %

Water580,16 24,64

Oil129,27 0,623

Oil after water absorption (moist sample)24,79 0,314

Oil after water absorption (dry sample)286,22 0,314

Thermal stability of the lignocellulose was investigated by thermogravimetry using TA Instruments Q600 thermal analyzer at 10oC/min heating rate under dynamic argon atmosphere. Obtained TGA curve, presented on Fig.1, illustrates thermal behavior (stability) of used lignocellulose and characteristic temperatures of the observed thermal events confirm presence of the main constituents (Table 3.).

Fig. 1. Results of thermogravimetric analysis of lignocellulose - fraction Celgran C

The mass loss below 100oC can be attributed to the evaporation of water (moisture) originally present in the sample (Table 2.). The mass loss increases with temperature gradually up to approximately 200oC while in the region between 200 and 400oC more significant mass loss occurs. On the obtained DTGA curve (Fig.1) two distinct peaks can be observed within this temperature interval, suggesting the existence of two separate thermal events. According to the literature data [20-22], the first event that occurs at 210-300oC can be associated with the decomposition of hemicellulose and the slow degradation of lignin, while the second event (275-350oC) can be attributed to the degradation of cellulose. Possible discrepancies between literature data and the DTGA results may be associated with the amount of cellulose and lignin in the lignocellulose material (Table 3.), given that Shebani etal.3 and DAlmeida etal.14 demonstrated that higher cellulose and lignin content in lignocellulosic materials leads to a greater thermal stability.

Bakarni prah korien kao elektro provodni punioc dobijen je elektrohemijskim putem, programiranim strujno-naponskim reimom - reversnom strujom [16,17]. Amplitudna gustina struje je imala vrednost 3600 A/m2. Vreme katodnog taloenja je iznosilo 40 s, a vreme anodnog rastvaranja 0.2s. Vreme narastanja praha (r=15 min, protok elektrolita, Q=0.11 dm3/min, temperatura elektrolita, t=(50(2)oC, koncentracija bakra, C(Cu+2) = 15 g/dm3 i koncentracija sumporne kiseline, C(H2SO4) = 140 g/dm3. Bakarni prah je stabilizovan rastvorom pogodne povrinski aktivne materije [18].

Particle size of used lignocellulose and copper powder was analysed using Malvern Instruments laser diffractometer Mastersizer 2000 with the Scirocco 2000 module. Obtained particle size distributions are presented on Fig.2. The mean particle sizes of lignocellulose powder and copper powder determined by laser diffractometry are d(0.5) = 60.544 m and d(0.5) = 27.219 m, respectively.

a)

b)

Fig 2. Particle size distribution of used matrix and conductive filler powders: a) lignocellulose and b) copper

Morphology of matrix (lignocellulose) and conductive filler (copper) powders was analysed using scanning electron micrscopy (SEM). The size and the shape of the matrix and filler particles are illustrated in Fig.3.

a)

b)

Fig. 3. SEM micrographs of pure matrix and filler powders a) lignocellulose and b) copper

Investigated lignocellulose and copper powder composites were prepared with filler contents in the range 10 wt.% - 90 wt.% with the 10 wt.% increment, while pure lignocellulose and copper samples were prepared as reference materials. The samples were produced from thoroughly homogenized powder mixtures that were pressed into 16 mm diameter tablets at ambient temperature (t = 25oC) under pressure of 10, 20 and 27 MPa. Morphology of the investigated composites was analyzed using scanning electron microscopy (SEM).

Fig. 4. SEM micrograph of the obtained lignocellulose-copper powder composite

Sample thicknesss (necessary for the calculation of porosity and conductivity) was determined using micrometer, to an accuracy of 0.01 mm. Several thickness measurements were taken per sample and then averaged.

Theoretical density of composites t was calculated according to relation [2,19]:

(1)

where V is volume fraction, density while f and m indexes correspond to filler (copper powder) and matrix (lignocellulose), respectively.

Porosity of the investigated composites was determined by comparison of experimental and theoretical densities of the samples according to relation [19]:

(2)

where e is experimentally obtained value of composite density.

Electrical conductivity measurements were carried out by DC U/I-characteristic measurements of the samples using Digital Multimeter, Model 464, Simpson Elec. Company. Geometry of the instrument contacts (rings) used is such that it minimizes edge effects thus it can be assumed that they do not exist. Electrical conductivity was determined according to relation:

(3)

where is electrical conductivity, I current through sample, U potential difference, l length and S cross-sectional area of the sample.

Hardness of the samples was determined at ambient temperature (t = 25oC) using Shore D hardness testing method in acordance with ASTM D 2240-68 standard. Five data points were taken for each sample and no difference was found between values obtained for both faces of each sample.Results and discussion

The theoretical density of the composite (dt) was calculated from the relation

(1)[pinto, jahorina, tara]where V is the volume fraction, d is the density, and m and f stand for the matrix and filler, respectively.

Porosity of the investigated composites, , was determined by comparison of experimental and theoretical densities of the samples according to relation:

(2)where de represents the experimental density.

Figure 4 represents the porosity rate of different composites as function of the filler volume fraction at various processing pressures. It can be seen that, as expected, the porosity decreases with the increase of pressure, due to higher packaging effect. On the other hand, as the volume fraction of the very porous natural matrix decreases, the porosity decreases too. In all cases, the porosity is still rather high around percolation threshold and it is between 24% and 30%. These results show that although the quality of the obtained composites was good, some changes in the preparation processes can lead to lover porosity composites.

Figure 4: Porosity of the copper powder filled lignocellulose matrix composites at various pressures.

Figure 5 shows the dependence of hardness measured as shore D values, in various composite of lignocelluloses matrix and copper powder filler prepared under various pressures. As expected with pressure molding under low temperatures (25C), the hardness decreases with the increase of the filler fraction and it increases with the increase in processing pressure.

Figure 5: Hardness of lignocelluloses matrix and copper powder filler composites prepared under various pressures. Measurements are shown as Shore D values.

The electrical conductivity of the composites as a function of filler content for the samples was measured as stated in Materials section. The conductivity measurements showed typical S-shaped dependency with three regions (dielectric, transition, and conductive; Fig. 6). These measurements were performed on all the samples prepared under three different pressures: 10 MPa, 20 MPa and 27 MPa. As expected, samples with low filler content were almost nonconductive. However, the electrical conductivity of the composites increased dramatically as the copper content reached the percolation threshold at 14.4% (v/v) filler for all the processing pressures. The value of the percolation threshold was obtained from of the maximum of the derivative of the conductivity as a function of filler volume fraction (Fig. 6). According to Flandin et al.[4], values of 2040% (v/v) are typical for spherical particles of filler. This much lower percolation threshold can be explained by much higher specific area of the highly dendritic copper powder particles used as filler. The statistical percolation theory is usually used to relate the electrical conductivity of the composite to the existence of clusters of connected particles, which give rise to the so-called conducting infinite cluster above the threshold. With highly porous, highly dendritic particles with high values of specific area, more interparticle connections can be obtained at lower filler content. Above the percolation threshold, the conductivity of composite increased by much as fourteen orders of magnitude. The increase in the conductivity is higher than stated by Pinto et all. due to filler with high specific area. It can be seen from the Figure 6 that under investigated range of pressures there is no change in the percolation threshold. However, in the conductive region, composites with the same volume fraction of copper powder prepared under higher pressure have higher values of conductivity.

Figure 6: Variation of electrical conductivity, as a function of filler content, of lignocellulose composites filled with copper powder under different processing pressures.For percolation theory, the relationship between the electrical conductivity of the mixture and the volume fraction of the conductive filler was given by Kirkpatrick:

(4)where is the electrical conductivity of the mixture, 0 is the electrical conductivity of the fillers particles, Vf is the volume fraction of the filler, Vf* is the critical volume concentration at the threshold of percolation, and t is an exponent that determines the increase in the conductivity above Vf*. This theory provided a good description of the experimental results near the transition point. However, discrepancies were observed between the critical parameters (Vf*, t) resulting from eq. (4) and the experimental values, since this theory does not include the shape of the conductive filler and it does not consider several other parameters. Although the experimental results show that the electrical conductivity depended strongly on the viscosity and the surface tension of the filled polymers, it also depended on the filler particles geometrical parameters and the filler matrix interactions. These parameters were considered by Mamunya et al.[15,16]. A model they developed consideres specific parameters for each composite and it is given in the basic theory:

(5)

where m is the maximal conductivity of composites, F is the filler packing density coefficient (equivalent to the maximal value of the filler volume fraction), and teff is given by the relation

(6)

where t1 is equivalent to the t parameter in the basic eq. (4). t1 usually has a value around 1.7, and t2 depends on the specific composite. Thus, teff could have higher values depending on the fillerpolymer interactions.

Treba da resim jednacinu, potom da zavrsim poslednji pasus.

Equation (4) will be used in this study to interpret experimental results. The fit, above the percolation threshold, of the electrical conductivity as function of the volume fraction of Zn filled in urea formaldehyde embedded in cellulose powder is given in Figure 5. The agreement between the experiment and the theory was fairly good. The deduced parameters were Vf* 18.5%, teff 2.25, and F 0.45.

The determined packing density coefficient was in good agreement with the prediction of eq. (4).25 The teff obtained value was close to 2, which represented the accepted theoretical value for three-dimensional lattices.26,27 This theoretical value was independent of the exact composition of the random composites.26 On the other hand, the critical threshold percolation value obtained was in good agreement with that determined by experience, Vf* 18.9%. Elsewhere, this result was also close to the 18% found in Zn-filled nylon 6.22 Indeed, the random composites electrical conductivity was already shown to depend on several parameters, 1823,28,29 such as the viscosity and the polymers surface tension, especially in the case of mixes in which the conductive powder is dispersed; the size, shape, and surface energy of the filling particles; and the powder dispersion procedure, that is, the type, duration, and strength of shear. In this study, the particle sizes and shape of Zn filled in nylon 6 and ureaformaldehyde were the same, and the dispersion procedure was maintained uniformly. Consequently, the small difference in threshold values observed between nylonZn and ureaformaldehyde/Zn composites was probably due to the specific matrixfiller interaction and viscosity effects.

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