1. Introduction
Biomass resources in arid and semiarid lands are scarce due to lack of water and poor soil quality. Prickly pear (
Opuntia ficus-indica (L.) Miller) is a member of the cactaceae family that shows great capability to grow in these harsh environments based on several morphological and physiological adaptations: the adoption of the Crassulacean acid metabolism (CAM) which allows nocturnal uptake of CO
2 (thus avoiding the opening of stomata during the warmer hours of the day), the presence of a complex hydrocolloid (mucilage) capable of storing great amounts of water in the parenchyma tissues, and a vegetative form consisting of a succession of flat photosynthetic stems (cladodes) with low density of stomata and covered by an almost impermeable epicuticular wax layer [
1,
2].
Prickly pear is mainly cultivated for the production of edible fruits (the prickly pears, sensu stricto) but also to obtain tender cladodes for human consumption (nopalitos) and mature cladodes employed as forage for cattle, among other uses. There are two main approaches for the cultivation of prickly pear. Traditional management implies the extensive cultivation of prickly pear in wastelands with poor quality soils where no other crop can succeed and almost without any further agricultural practices or inputs. Biomass yields achieved in these conditions are very limited (typically below 5 MgDM/ha·year, depending primarily on rainfall, soil fertility, and specific management [
1]) and so are the fodder resources and fruit yields obtained.
Modern intensive prickly-pear plantations are designed to achieve higher production yields and may be applied in lands with a certain degree of water availability. Under these circumstances, a more diligent management of the crop is carried, usually involving the use of large amounts of fertilizers and phytochemicals to reach productivities up to 50 Mg DM/ha·year [
2,
3].
The use of prickly pear as an energy crop can follow both approaches, but an improved version of the traditional management (in terms of appropriate fertilization and weeding) could allow for reaching the potential yields for the existing rainfall levels, while improving the energy balance of the bio-system. Furthermore, it implies a reduced competition for the land between crops destined to food and those destined to energy, as none of the essential rainfed crops can stand such harsh rainfed environments as prickly pear.
Consistent with a composition rich in mucilage carbohydrates and starch, while poor in lignin, research on energy applications for prickly-pear biomass has focused on the production of biogas and bioethanol. Biogas production from this feedstock has gathered certain scientific attention since the 1980s, and conclusions reported in literature [
4,
5,
6,
7,
8,
9,
10] encourage the industrial development of prickly-pear anaerobic digestion. Bioethanol from prickly-pear cladodes has been less investigated and, though it seems promising (with obtained yields up to 163 L/Mg DM), it still faces uncertainties related to the low fermentation yields of carbohydrates (many of the pentoses present in the mucilage and hemicellulose hydrolysis), the low concentration of ethanol in the brew, and the energy balance of the process [
1,
9,
11,
12,
13,
14].
The use of prickly pear directly as a solid fuel for thermal applications (either direct combustion, gasification, or pyrolysis) has not been reported in the scientific literature, and it is very rarely described in practice. This is mainly due to its high moisture content, limited availability, and due to its more valuable use as animal fodder in water-deprived environments. However, new business initiatives looking into alternative fuels in arid and semiarid locations are starting to show interest in this type of biomass whose yields in sustainably managed crops may be sufficient for domestic and commercial exploitation. To evaluate the fuel potential of this biomass, information needs to be available about its heating values, ash content, composition, and most importantly, its drying behavior. Extended knowledge about moisture elimination may also be of interest to promote the use of this type of biomass in other potential applications, such as animal feeding.
The drying of prickly-pear tender cladodes aimed for human consumption has been investigated in some research papers [
15,
16,
17,
18,
19,
20,
21]. However, no information is available regarding the drying of fully developed cladodes, which may be more suitable for use as a solid biofuel. Besides size and weight, mature cladodes differ from tender ones in their lower protein and ash contents and higher fiber contents [
22], although the most important issue related to drying kinetics is the progressive development as the cladode grows older of a waxy cuticle over its epidermis [
23]. This cuticle reduces transpiration and avoids the dehydration of the plant, becoming a major obstacle in the drying of this material. It has been reported that exposing the internal tissues of tender cladodes facilitates their drying process [
18], and the same may occur when drying mature cladodes.
The aim of this paper is to characterize prickly-pear mature cladodes in terms of chemical, proximal, and fuel properties, as well as to study the drying kinetics of this biomass after a pretreatment destined to expose the internal tissues of mature cladodes to different drying temperatures.
3. Results
3.1. Characterization of Prickly-Pear Cladodes
The prickly-pear cladodes from the B1 batch (small mature cladodes) had fresh weight of 471.53 ± 69.7 g, diameter at the wider point of 15.5 ± 1.2 cm, and length of 31.5 ± 6.0 cm. The cladodes from the B2 batch (large mature cladodes) had fresh weight of 788.5 ± 95.6 g, diameter at the wider point of 19.2 ± 1.5 cm, and length of 40.5 ± 2.9 cm.
Table 3 shows the elemental composition of the prickly-pear cladodes. When compared to lignocellulosic biomass, the prickly-pear elemental composition shows a lower C content and a significantly higher concentration of alkaline (primarily K) and alkaline earth (primarily Ca) elements. Due to the low boiling temperatures of alkaline salts, the presence of K and Cl typically implies a high potential for the formation of slagging and/or fouling in boilers, while Cl and S may create major corrosion problems. This biomass also showed a high content in Ca that may be able to partly mitigate the negative effects of K [
47]. This Ca content was associated with the presence of high amounts of calcium oxalates and free calcium in the parenchyma tissues [
48,
49]. Chlorine (Cl) content was also very high and may lead to the production of chlorinated aromatics (dioxins and furans) and corrosive HCl during combustion [
50]. Nitrogen content was also higher than those typically reported for woody materials but low when compared to proteinaceous biomasses.
When compared to literature, Ca and K values were at the top of the ranges reported by other authors for prickly-pear cladodes (2.8–7.8 wt% dmb and 0.4–4.7 wt% dmb, respectively). Regarding P, the content observed in the samples investigated was higher (400–1800 ppm), while Mg content was lower (1900–24,000 ppm) (various authors, in [
9]). The reported literature showed a significant variability in the elemental composition of prickly-pear biomass, especially regarding minor components. This has been attributed primarily to differences in soil composition which are, in turn, related to the agricultural practices as explained in the introduction of this work. The composition of plants cultivated using traditional management is poor in proteins (and, therefore, in N) and depends primarily on the elemental composition of the soil. On the contrary, cladodes produced in profusely fertilized intensive prickly-pear plantations usually accumulate a wider range of inorganic elements brought in by the fertilizer.
If intended for use directly for thermal applications, the management of prickly-pear plantations should try to find an equilibrium between the level of fertilization required to achieve high biomass yields and the limited amount of mineral elements tolerable in boilers and furnaces.
As expected from their elemental composition, proximate analyses of prickly-pear cladodes revealed a high ash content (25.8 ± 2.0%, as shown in
Table 4), even compared to values reported in literature (10–23 wt%, dmb). The variability in the proximate composition of the samples (including small B1 and large B2 cladodes) was limited, evidencing the homogeneous nature of the material. The high ash and oxygen contents (1.26 O/C ratio) and the low lignin concentration were responsible for the limited calorific value of this biomass. The fiber contents of the employed cladodes fall within the ranges published in literature for hemicellulose (4–23 wt%, dmb) and lignin (2–7 wt%, dmb), while they were comparatively lower for cellulose (10–22 wt%, dmb) and starch (8–23 wt%, dmb) (various authors in [
9]). This may suggest the presence of high amounts of mucilages, compounds rich in carbohydrates that could represent more than 20 wt% of dry cladodes [
51,
52].
Figure 4 shows the TGA/DTG analyses of the three separated cladode tissues (parenchyma, chlorenchyma, and epidermis) and the ground/milled cladode sample. The results showed three main areas of weight loss. The first one takes place at temperatures below 200 °C and corresponded to the elimination of free moisture and the chemical dehydration of polysaccharides. The second one, at temperatures between 200 °C and 400 °C, was attributable primarily to the thermal degradation of polysaccharides. DTG plots for parenchyma and epidermis showed two differentiated peaks in this step. The first one corresponded to the maximum degradation rate of hemicellulose at 255 °C in the parenchyma tissue and 261 °C in the epidermis. The second one was mainly associated with the degradation of cellulose and appeared at 291 °C in parenchyma tissue, 297 °C in the chlorenchyma, and 309 °C in the epidermis [
53]. The first peak in the chlorenchyma is almost indistinguishable, which suggests a limited hemicellulose content in this tissue.
Finally, the gradual mass reduction in the solid fraction observed at temperatures between 400 °C and 700 °C was attributable to the progressive carbonization of thermally resilient components (lignin), as well as to the degradation and volatilization of heavy tars and inorganic compounds. Mass losses associated with the transformation of oxalates into carbonate may be responsible for the peaks observed at 450–459 °C [
54,
55], while peaks at 672–702 °C could be related to the volatilization of chlorinated salts and the degradation of carbonates [
54].
The TGA/DTG plots of the unfractionated cladode biomass appeared as a combination of the three tissues. Moisture loss in this sample was comparatively higher (with DTG maxima at 59 °C) due to the hydrophilic nature of this material that led to water absorption when the ground/milled biomass was stored at room conditions.
3.2. Drying of Prickly-Pear Cladodes
The equilibrium moisture contents (Xe) of the samples at 50 °C, 60 °C, and 70 °C were determined as 0.04 ± 0.003, 0.03 ± 0.001, and 0.03 ± 0.001 (kg H
2O/kg DM), respectively. These values were similar, though slightly lower, to the ones reported by [
17,
21] for tender prickly-pear cladodes at similar temperatures and relative ambient moisture contents (0.05–0.06 kg H
2O/kg DM). This was probably due to the osmotic pressure provided by the higher content of soluble components in tender cladodes when compared to mature ones.
Figure 5 shows the drying curves of prickly-pear cladodes (cut into straps and cubes) at different temperatures. Similar patterns were found for both cutting geometries. Regarding curves at 60 °C and 70 °C, a rapid moisture loss could be observed in the first hours represented by parallel and almost linear tendencies with noticeable slopes. As the process moved forward, the curves tendency turned asymptotic towards Rx ≈ 0. Drying curves at 50 °C showed a more progressive tendency, even at the first hours, resulting in significantly higher drying times.
The variability between results obtained at each experimental condition (expressed as the average standard deviation of the moisture ratio—Rx) was 0.02, 0.01, and 0.01 for straps dried at 50, 60, and 70 °C, respectively, and 0.04, 0.02, and 0.04 for cubes dried at 50, 60, and 70 °C, respectively.
When cutting the cladodes into straps, the exposed surface of parenchyma and chlorenchyma tissues (expressed as the exposed surface to fresh-weight ratio) represented between 49 and 57% of the total cladode’s surface subjected to drying, while this value increased to 70–74% when cladodes were cut into cubes (
Table 5). Exposed surfaces and moisture-loss rates were, respectively, 2.0–2.3 and 1.6–2.3 times higher when cladodes were cut into cubes than when they were cut into straps. The highest moisture-loss rate (31.9 g/h) was found for cladodes cut into cubes and dried at 70 °C, being 26% higher than the one found for the same cutting geometry at 60 °C, and 9.4 times higher than the one determined for cladode cubes dried at 50 °C. Whole cladodes dried at 70 °C showed the lowest moisture-loss rate, representing 11% of the one found for cladodes cut into straps and dried at the same temperature and 81% of the one determined for cladode cubes dried at 50 °C.
Figure 6 (left) shows the drying rates (expressed as moisture loss per unit of dry matter and time) of the prickly-pear cladodes cut into different geometries and dried at different temperatures, along with their tendency lines. Whole cladodes showed the lowest drying rates followed by cladode straps and cubes dried at 50 °C. At the other end of the spectrum, cubes dried at 70 °C and 60 °C reached the highest drying rates. The results showed how it was increasingly difficult to reach high drying rates when the moisture content in the cladode diminished. The tendency lines of the experimental results followed a power tendency (y = axb) when mild conditions were employed, although the asymptotic range of the function at the determined moisture-weight to dry-weight ratios (MW/DW), was only visible for the one representing the drying of whole cladodes. This implies that when the internal tissues of the cladodes are exposed to drying air, there is a clear response of the drying rate to the MW/DW ratio. At more severe drying conditions (cubes and straps at 60 °C and 70 °C), this phenomenon was utmost clear, as the tendency lines fitted into linear functions (R2 = 0.96–0.99) even better than into power ones (R2 = 0.93–0.96). According to [
15,
19], this predominance of the falling rate period implies that the drying process was mainly controlled by water diffusion (same as what happens when drying tender cladodes, as reported by the cited authors) while the constant-rate period observed at high MW/DW values for whole cladodes dried at 70 °C is governed by convection.
To study the effect of temperature over the moisture-loss rates without considering the effect of the cutting geometry,
Figure 6 shows the rates of moisture loss per unit of exposed tissues surface (along with their tendency lines). If rates were compared at the maximum common value for MW/DW (10.1), the rates of moisture loss per unit of exposed tissues surface increased with temperatures from ca. 0.03 g/(cm
2 h) at 50 °C to ca. 0.1 g/(cm
2 h) at 70 °C.
3.3. Drying Modeling
The determination coefficients (R2) and the adjustment errors of the different drying models tested were included in
Appendix A (see
Table A1). All models fitted quite well with the experimental data (R2 ≥ 0.94, SEE ≤ 0.06, MAE ≤ 0.05) with the exception of the Wang and Sing model when applied to data from straps dried at 50 °C (R2 = 0.74–0.87). On average (considering the three tested temperatures), the double exponential with three parameters and the Midilli models achieved the higher determination coefficients for straps (0.997) and cubes (0.999), respectively. The coefficients belonging to these models that allowed us to build the empirical functions that best represent the drying kinetics of prickly-pear cladodes under the tested conditions are shown in
Table 6.
The modeling of the drying kinetics of tender cladodes had been previously reported in literature. López et al. [
18] found the best fit for the double exponential (four parameters) model when drying whole and partially peeled cladodes at temperatures between 35 and 60 °C, while both Díaz-Ayala et al. [
15], and Taouil et al. [
21] found better fits for the Midilli model when drying cladode straps (thickness = 0.4 cm) and cubes (1 × 1 cm), respectively, at the same temperatures. These results, together with the ones obtained in the present work, suggest that optimum results are achieved with functions that include at least three parameters when a wide range of models are tested to describe the drying kinetics of cladodes.
The diffusion coefficient values (
Table 7) increased along with drying temperatures and the surface area of exposed tissues. The obtained values were significantly lower than those obtained for tender prickly-pear cladodes by [
20] (0.82 × 10
−7–3.25 × 10
−7 m
2/s) but fell within the range compiled by [
56] for vegetables and foodstuff (10
−12–10
−8 m/s). When drying cladodes at 60 °C and 70 °C, the obtained values (2.0 × 10
−9–6.5 × 10
−9 m/s) were similar to those found for thyme biomass dried at 50–60 °C (3.4 × 10
−9–6.0 × 10
−9 m/s) [
57], spinach dried at 60–70 °C (1.0–1.5 × 10
−9 m/s) [
58], and Chenopodium ambrosioides L. dried at 60 °C (4.5 × 10
−9 m/s) [
59]. Diffusion coefficients obtained for cladodes dried at 50 °C are similar to those found for another succulent species, Aloe barbadensis Mill., dried at 50–70 °C (5.3–11.3 × 10
−10 m/s) [
60].
3.4. Bulk Density of Prickly-Pear Dry Cubes
The average bulk density of dry cladode cubes was 150 ± 3.6 kg/m
3. This value is higher than the ones found for different milled herbaceous biomasses (60–82 kg/m
3) by [
61], while similar to those reported for pine sawdust [
62] and milled
Phalaris arundinacea L. [
63]. These values are much lower than the ones commonly determined in commercial quality pellets (≥600 kg/m
3), suggesting the need of further densification of this biomass to avoid disproportionate transportation costs.