The last few decades have revealed the growing interest of industry and scientists in the research and development of composite materials based on organic materials originating from renewable sources. Lignocellulosic biomass has become a promising alternative source of raw materials for industrial applications because the main component―cellulose in most plants is inexhaustible [1]. Cellulose as one of the most important polysaccharides in the plant cell wall is widely used in the paper industry [2]. A large amount of cellulosic waste is generated yearly by the agro-industries [3].

Increasing importance of cellulosic materials utilization is due to their numerous advantageous properties for application in sustainable building constructions. Therefore, it is increasingly becoming crucial to accelerate the shift from classical to environmentally friendly materials, and so to contribute to the transition to equitable, sustainable, post fossil-carbon societies [4]. In this context, there are efforts centered upon bio-based economy based on sustainable production and consumption of renewable biological resources, as well as their conversion into bio-based products and energies. It is the possible way of achievement of sustainable development in the construction industry to shift from the limited and finite material resources to easily renewable raw material resources. The utilization of biomass in industry as a major strategic approach of 21st century is mainly focused on the development bio-based building materials. Eco-builders are interested in the utilization of natural biomass resources and recycled waste related materials/products contributing to regulation of the indoor moisture content and to greater levels of indoor air quality [5].

Ligno/cellulosic fibers obtained from biomass are attractive for their application into because of their positive environmental impact [2]. But cellulosic fibers obtained from wood are also a unique material reinforcing the cement composites. They are non-hazardous, renewable and readily available at relatively low cost compared to other commercially available fibers [6]. Due to the increasing scarcity of wood resources, the research is mainly concentrated on the utilization of cellulosic fibers obtained from waste paper as a possible and valuable resource of fibers for preparation sustainable building materials. From this point of view, recycled cellulosic fibers offer the economic advantage that can also reduce the environmental impact risks of primary production of fibers. This trend of incorporation of recycled cellulosic fibers and combination of natural and/or recycled fibers into composites with inorganic matrix is at the center of attention of researchers [7] [8] [9]. Maximizing their use in building materials and improving their performance can be achieved through properties characterization of cellulosic fibers by using adequate methods in order to reveal their chemical composition and physical properties because the composites require a strong fiber with good adhesion between matrix and fiber to enhance their final properties [6].

Fourier transform infrared spectroscopy (FTIR) is one of the most commonly used methods for identification different functional groups constituting a compound. FTIR is a rapid and non-destructive technique for the qualitative and quantitative determination of biomass components in the mid-IR region [10]. FTIR spectroscopy provides information about molecular fragments, the presence or absence of specific functional groups and can give an even deeper insight into the fibers structure. FTIR with ATR unit allows attenuation of the incident radiation and provides IR spectra without the water background absorbance [11].

The aim of this paper is comparative FTIR investigation of cellulosic fibers from wood pulp and recycled waste.

FTIR spectra of cellulose fibers from wood pulp and recycled waste paper are compared with reference sample in Figure 2 and Figure 3. The absorption bands are observed in two wave number regions of 3660 - 2800 cm⁻¹ and 1650 - 400 cm⁻¹. The presence of peaks on the spectra of cellulose samples coming from wood pulp corresponds to bands of microcrystalline cellulose (Figure 2), while differences in absorption bands intensities and appearance of new peaks in spectra of recycled cellulosic fibers are observed.

Identification of the absorption bands is following. The observed peaks in the wave number range of 3660 - 2900 cm⁻¹ is characteristic for stretching vibration of O-H and C-H bonds in polysaccharides. The broad peak at 3331 cm⁻¹ is characteristic for stretching vibration of the hydroxyl group in polysaccharides [3] [13]. This peak includes also inter- and intra-molecular hydrogen bond vibrations in cellulose [14]. The band at 2894 cm⁻¹ is attributed to CH stretching vibration of all hydrocarbon constituent in polysaccharides [3] [13]. Typical bands assigned to cellulose were observed in the region of 1630 - 900 cm⁻¹. The peaks located at 1633 cm⁻¹ correspond to vibration of water molecules absorbed in cellulose [3] [13]. The absorption bands at 1428, 1367, 1334, 1027 cm⁻¹ and 896 cm⁻¹ belong to stretching and bending vibrations of -CH₂ and -CH, -OH and C-O bonds in cellulose [10] [15]. The band at around 1420 - 1430 cm⁻¹ is

associated with the amount of the crystalline structure of the cellulose, while the band at 897 cm⁻¹ is assigned to the amorphous region in cellulose [1].

In Figure 2, visible differences were noted in the spectrum of G250WT sample. There are changes in intensities of the signals at 1428 cm⁻¹, 896, 875 cm⁻¹ and 712 cm⁻¹. A broad peak at 1428 cm⁻¹ includes -CH₂ and CH bonds vibrations coming from cellulose as well as the vibration of C = O bonds in the carbonate ion (CO₃²⁻). The CO bond vibrations in pure CaCO₃ are visible at 1475 cm⁻¹. The weak intensity peaks at 875 and 712 cm⁻¹ also belong to C=O bonds in carbonate anion. The FTIR spectra of the cellulosic fiber samples from waste paper in Figure 3 are very similar to spectrum of G250WT sample (Figure 2). This fact implies the presence of calcium carbonate [11] in cellulose samples as impurity deriving from the used filler in paper making what corresponds to cellulose purity (Table 1). However, further new peaks attributed to kaolinite in the spectra of recycled fibers were observed. The structure of this aluminosilicate mineral is two-layered, one silicon-oxygen tetrahedral layer (SiO₄) joined to Al(O,OH)₆ octahedral layer or expressed in other way, [Si₂O₅]₂-layer and [Al₂(OH)₄]₂-layer with pseudo-hexagonal symmetry [16]. The four absorptions at 3697, 3669, 3645 and 3620 cm⁻¹ are typical for kaolinite spectrum (amount aluminum in octahedral). The band at around 3620 cm⁻¹ has been ascribed to the inner hydroxyls, and the peaks at around the other three characteristic wave numbers are generally attributed to vibrations of the external hydroxyls. The absorption bands observed at 3420 - 3445 cm^-1 and at 2894 and 1633 cm^-1 could be assigned to the OH vibration mode, which are observed in almost all the natural hydrous silicates. However, the H-O-H bending of water is observed at 1620 - 1642 cm⁻¹ [17]. In the region of 1000-500 cm⁻¹, vibration of the main functional groups of Si-O and Al-OH were observed. The band at around 1100 - 1010 cm⁻¹ is assigned to Si-O stretching vibrations and the absorption bands at 914, 540 and 470 cm⁻¹ are attributed to Si-O-Si bending vibration.

The doublet at 780 - 798 cm⁻¹ is due to Si-O-Si inter tetrahedral bridging bonds in SiO₂. The peaks identified at 936-914 cm⁻¹ correspond to Al-OH bending vibration in kaolinite [17] [18] [19]. The above-mentioned facts about the presence of calcium carbonate and kaolinite as impurities in cellulose samples confirm their origin from the used filler in paper making what corresponds to cellulose purity (Table 1).

This work presents the results of FTIR spectroscopic comparative study of two kinds of cellulosic fibers with reference sample of microcrystalline cellulose. Studying the chemical composition and FTIR spectra of six samples of cellulosic fibers from wood pulp and waste paper showed differences in organic components contents such as cellulose, hemicelluloses and lignin as well as in the presence of inorganic impurities (calcite and kaolinite) originating from filler in paper making. More detail characterizations of cellulose samples by using XRD, TG/DSC and SEM will be a subject of further research work.

The authors are grateful to the Slovak VEGA Grant Agency for financial support of the project VEGA 1/0277/15.

Hospodarova, V., Singovszka, E. and Stevulova, N. (2018) Characterization of Cellulosic Fibers by FTIR Spectroscopy for Their Further Implementation to Building Materials. American Journal of Analytical Chemistry, 9, 303-310. https://doi.org/10.4236/ajac.2018.96023