Semo Mogeia (email), Alberto A. Manhiça, Andrade F. Egas

Wood ash content variation in Eucalyptus grandis clones in Mozambique

Mogeia S., Manhiça A. A., Egas A. F. (2023). Wood ash content variation in Eucalyptus grandis clones in Mozambique. Silva Fennica vol. 57 no. 1 article id 10767. https://doi.org/10.14214/sf.10767

Highlights

  • Eucalyptus grandis heartwood produces better fuel than sapwood, if assuming ash content as energy quality parameter
  • Younger individuals have higher ash content in sapwood, and older individuals in the heartwood
  • There was not significant stem end variation of ash content in heartwood and sapwood.

Abstract

The sustainability of native forests in Sub-Saharan Africa depends on the diversification of sources to generate bioenergy, and Eucalyptus spp. wood has been highlighted. However, the determination of energy quality parameters has been a challenge to enable plantation wood to generate energy. The research assessed the ash content of radial and longitudinal samples of Eucalyptus grandis (Hill) clone with different ages and growth sites. Samples were collected in three pre-established plots in the center of Mozambique. Five trees were cut down in each plot and six discs were removed from each tree. Grinded samples with <0.5 mm particle size were generated from the heartwood and sapwood of each disk to determine the ash content. Wood from 7-year-olds had a higher ash content compared to 9-year-olds. The two sample plots differed from each other in terms of wood ash content. Heartwood samples had smaller ash content than sapwood samples. In general, the ash content of the intermediate positions was lower than those from the base and top of the stem, for both radial sections. No conclusive differences were found between samples from the base and the top of the trees, indicating that the material from the top of the trees can also be used as wood fuel. Ash content can be a considerable parameter to assess the quality of the wood of Eucalyptus spp. as a fuel.

Keywords
sapwood; heartwood; base-top; bioenergy quality; woody fuel

Author Info
  • Mogeia, Universidade Lúrio, Faculdade de Ciências Agrárias, Departamento de Silvicultura e Maneio [Lurio University, Faculty of Agricultural Sciences, Department of Forestry and Management], Campus de Wanaango, EN733, Km 42, Unango, Niassa, Mozambique E-mail smogeia@unilurio.ac.mz (email)
  • Manhiça, Centro de Investigação Florestal, [Forestry Research Center], Marracuene, EN1, Maputo província, Mozambique E-mail albertomanhica@gmail.com
  • Egas, Universidade Eduardo Mondlane, Faculdade de Agronomia e Engenharia Florestal, Departamento de Florestas, [Eduardo Mondlane University, Faculty of Agronomy and Forestry Engineering, Department of Forests], Av. Julius Nyerere, Maputo cidade, Mozambique E-mail aegas8@gmail.com

Received 30 June 2022 Accepted 25 January 2023 Published 3 February 2023

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Available at https://doi.org/10.14214/sf.10767 | Download PDF

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1 Introduction

Worldwide, firewood, through direct consumption, and charcoal are the main ways of using energy from forests (Fundo Nacional de Energia 2014; Monjane and De Barros 2015). Wood fuels production makes a significant contribution to the energy needs of the African continent. Sub-Saharan Africa produces around 600 million m3 of wood fuel per year, which covers 60–80% of energy needs, depending on the country. Mozambique is in fifth position with 4% of the ten largest charcoal producers globally (Steierer 2011). It should be noted that this value falls on natural forest, including the harvest of species protected by local law (Nhancale 2008; Afonso 2012; Atanassov-Andrade et al. 2012).

Although Mozambique is one of the few countries in Southern Africa that still has a considerable area of natural forests (Sitoe et al. 2012), the deforestation rate and forest degradation continues to increase, from 0.58% in 2007 to 0.77% in 2018 (Direcção Nacional de Florestas 2018). The harvest for energy production is one of the main drivers of deforestation (Cuamba et al. 2016; Egas et al. 2016). In 2008, annual consumption of wood fuels was estimated at 16 million m3 year–1. Ten years later, the volume of wood extracted from natural forests has increased to 20 million m3 year–1 (Nhancale 2008; Bila 2018). It is estimated that 95% of deforestation is caused by firewood and charcoal, which supply the energy needs of communities, bakeries, tea and tobacco drying (Bila 2018). Thus, over the years there has been no significant evolution regarding the dependence of the urban and rural population on the use of wood fuels in Mozambique (Ministério da Energia 2012, 2013). However, the availability of natural forests with the potential to continue to supply energy demand tends to decrease (Atanassov et al. 2012; DNF 2018) due to population growth, especially in rural areas, where about 85% of the population depends on biomass from forests for cooking, heating and as a source of income (Nhancale 2008).

As a way of guaranteeing the perpetuation of natural forests, environmental policies have been increasingly directed towards the protection of native forests. This emerges the need to use raw materials from reforestation (Varma and Behera 2009; Republic of Mozambique 2016). Eucalyptus spp. are the most widely planted exotic genus (Souza et al. 2004). Its rapid volumetric growth is pointed out as one of the important characteristics for energy generation (Goulart et al. 2003; Castro et al. 2013). However, wood is a heterogeneous and anisotropic material, with variations in its composition depending on the provenance, age of the trees, among other factors (Goulart et al. 2003; Castro et al. 2013), which alter the wood’s energy qualifiers and quantifiers.

In the use of wood as fuel, physical properties such as wood density and moisture content; energetic properties (heating value); and chemical characteristics such as volatile material content, fixed carbon and ash content are important specific factors to be taken into account (Afonso 2012; Carneiro et al. 2014; Simetti et al. 2015).

Ash content is one of the most important parameters to evaluate the energy potential of wood. Ash originates from inorganic materials (silicone, aluminum, iron, calcium, magnesium, sodium, potassium, titanium and manganese) and does not participate in energy production (Frederico 2009; Santos 2010; Afonso 2012; Kajda-Szcześniak 2014). As it is an inorganic material, ash corresponds to the residues of the complete wood combustion. There is an inverse correlation between ash content, volatile materials content and heating value, and a positive correlation between heating value and fixed carbon content (Vale et al. 2002). Higher heating value is generally associated with material with higher levels of fixed carbon (Frederico 2009; Santos 2010; Castro 2011). On the other hand, high ash content in wood increase cleaning frequency and reduce the useful life of combustion equipment (Oliveira et al. 2010). Ash content also contributes to the particles emission through boiler chimneys, making it necessary to install separator particles equipment from combustion gases (Hytönen and Nurmi 2015; Čubars and Poiša 2017). The increase of particles in boilers causes corrosion of combustion equipment, cracks and fissures formation (Santos 2010). In domestic consumption, high ash content reduces heat propagation and energy value.

Studies on the determination of ash content directly in wood are scarce. However, several studies have been carried out on the immediate chemical analysis of charcoal, including the determination of ash content in charcoal (Vale et al. 2002; Andrade 2009; Barros et al. 2009; Afonso 2012; Zanuncio et al. 2014). However, the quantification and qualification of energy parameters is not linear in wood due to anisotropy. The heterogeneity of wood is manifested through the variation of its anatomical characteristics, physical and mechanical properties, and chemical characteristics between-species and within-species, growing under different ecological conditions (Vidaurre et al. 2012, 2013; Braz et al. 2014).

The data on wood energy quality of exotic species planted in Mozambique would allow the identification of Eucalyptus spp. with better quality for energy generation, and to understand the provenance variation of firewood energy quality in two important regions for forest plantation to maximize its domestic and industrial use. In this way, the ash content becomes a strong parameter to assess the quality and potential of woody fuels (Pereira et al. 1997; Calonego et al. 2005; Castro 2011; Johnson 2012; Hytönen and Nurmi 2015).

Recognizing the importance of ash content in wood to quantify wood quality, and the relevance of understanding variations in ash content at different ages, tree positions and growing regions, the research evaluated the ash content of radial and longitudinal samples of Eucalyptus grandis (Hill) with ages of 7 and 9 years. The study sites were plantations in Bandula and Penhalonga, the two important sites of reforestation in Austral Africa, center region of Mozambique.

2 Material and methods

2.1 Sample collection sites

The samples were collected in the localities of Bandula (19°20´S, 33°10´E) and Penhalonga (18°51´S, 32°50´E) in Manica province. Manica is located in the center of Mozambique, Sub-Saharan Africa (Fig. 1). As the results may be subject to climate and soil variations, the values for soil characteristics, temperature and precipitation for Bandula and Penhalonga were compiled (Table 1).

1

Fig. 1. Sites collection of Eucalyptus grandis discs samples. Africa (1a), Mozambique (1b), and Manica district boundaries highlighted (1c). The full black dots indicate discs’ collection site in Bandula plantation and the white dot indicates Penhalonga plantation.

Table 1. Edaphic-climatic characteristics of the Eucalyptus grandis plantation sites. Data relating to geographic location, average temperatures, average cumulative amount of rainfall, elevation and soil typology of the sites.
Species Age Provenance Temperature Precipitation Altitude Soil depth Soil type
Eucalyptus grandis 7 years Bandula 24.06 °C 1138 mm 698 m 16.20 cm Sandy clay franc
7 years Penhalonga 22.94 °C 1000 mm 813 m 16.00 cm Sandy clay franc
9 years Penhalonga 22.94 °C 1000 mm 813 m 22.20 cm Sandy clay
Sources: Instituto de Investigação Agronómica de Moçambique (1995) [Mozambique Agricultural Research Institute]; MAE (2005); Mina Alumina (2006); WorldClim (2020)

2.2 Samples collection

Eucalyptus grandis wood, aged 7 and 9-years, were used. The samples were collected from three blocks pre-established by the IFLOMA Company (Industria Florestal de Moçambique). Five trees were felled randomly at each location. Four 50-mm thick discs were removed from each tree: at the base (0.30 m from the ground), at 25%, 50%, and 75% of the commercial height of the tree (Trugilho et al. 2005; Castro 2011; Pereira et al. 2012; Simetti et al. 2015). Commercial height was considered to be the height which minimum diameter with bark was 60 mm.

2.3 Samples preparation for laboratory analysis

The discs obtained from the different sections of the trees were sliced into four wedges according to the TAPPI T 605 om-92 (1992) standard. Two opposite wedges were used to determine the ash content. For each disk, four specimens (prisms) were produced with 20 × 20 × 50 mm dimensions (thickness × width × length), where the length corresponded to the thickness of the disk (Fig. 2). In each wedge, a prism was obtained in both heartwood and sapwood radial position. The prisms were reduced to chips. Chips originating from the five samples trees were mixed separated from each radial and axial position.

2

Fig. 2. Scheme of reduction of discs into laboratory test specimens. Sapwood (2a), heartwood (2b), transversal section of prism 20×20 mm (2c), and thickness of the disc (2d).

The samples were grinded using a Wiley-type knife mill into particles that passed through a 0.5 mm sieve. The particles were subjected to a Retsch sieve, and the sample that passed through the 0.5 mm sieve again, was used to determine the ash content, as described in the standard (ASTM D1102 – 84 2013).

2.4 Assessment of ash content

The samples should be free of moisture. Two grams of the 0.5 mm diameter compound was weighed in 25 and 30 mL volume crucibles. The crucibles were previously heated in the Carbolite Gero muffle at a 600 °C temperature to stabilized mass. The samples in triplicate, and the respective crucibles were submitted in the oven at (103 ± 2) °C until the stabilization of the mass before being submitted to the muffle. The muffle was previously heated to approximately 100 °C, considered the initial temperature. The assessment of ash of wood followed the procedure described in the ASTM D1102 – 84 2013 standard. The effective time from the submission of the specimens to the total burning of the organic compounds in the wood and assessing ash was approximately 5 hours. The heating time of the samples in the muffle until the stabilization of the maximum temperature of the process (580 °C) was 1 hour and 10 minutes, with a heating rate of 7 °C min–1. The ash was obtained after the complete combustion of the samples at 580 °C. The ash content was considered as the residual mass in relation to the anhydrous powder mass.

2.5 Statistical analyses

The ash content of wood was calculated separately for both heartwood and sapwood radial position, for each one of longitudinal section. The provenance, radial variance, and age mean were compared using Student’s LSD test at a significance level p < 0.05. Longitudinal variance in both heartwood and sapwood, as well as age groups, were compared using ANOVA Tukey test at a significance level p < 0.05. The analysis was confined at four longitudinal positions: base (at 0.30 m of height from the ground), at 25%, 50% and 75% of commercial height. All analyses were carried out using the STATISTICA 8.0 program.

3 Results

Table 2 shows the mean ash contents and respective variation coefficients obtained for Eucalyptus grandis wood, according to age, provenance, radial and longitudinal position of the trees.

Table 2. Summary of the mean ash content of Eucalyptus grandis wood. The values in parentheses correspond to the variation coefficients. S1 indicates samples collected at 0.30 m height from the ground, and S2, S3 and S4 samples collected from 25%, 50%, and 75% of the commercial height of the tree, respectively. The data is grouped according to two test sites, two age groups, and two radial positions.
Site Species Age Radial position Mean ash wood content (%)
S1 S2 S3 S4
Bandula Eucalyptus grandis 7-year Sapwood 2.11 (3.00) 0.64 (22.31) 0.57 (6.43) 0.78 (4.95)
Heartwood 0.33 (23.95) 0.33 (17.39) 0.36 (26.83) 0.34 (22.74)
Penhalonga Eucalyptus grandis 7-year Sapwood 0.65 (31.47) 0.49 (12.76) 0.59 (15.56) 0.46 (4.60)
Heartwood 0.34 (0.03) 0.15 (51.78) 0.26 (11.67) 0.47 (2.97)
9-year Sapwood 0.52 (7.46) 0.35 (10.29) 0.31 (8.52) 0.34 (8.13)
Heartwood 0.39 (5.69) 0.31 (9.34) 0.33 (4.51) 0.39 (15.14)

3.1 Age of the trees

Significant differences were observed between ash contents of 7 and 9-year-old E. grandis wood from Penhalonga plantations for both radial positions: heartwood (t = 3.52; P = 0.02) and sapwood (t = 3.49; P = 0.03).

3.2 Samples provenance

Analyzes were performed for section S2 only, at 25% of commercial height of 7-year-old samples. The wood from Bandula plantation showed higher ash content than the one from Penhalonga, both for heartwood and sapwood samples. The provenance had a significant effect on variation of ash content in heartwood samples (t = 3.38; P = 0.03). However, no differences in ash content were detected in the sapwood samples of E. grandis between Bandula and Penhalonga.

3.3 Sample position in the tree

3.3.1 Radial position

The ash content was higher in sapwood than in heartwood at all sampling sites and stem heights (Fig. 3). Significant differences were detected between heartwood and sapwood samples in all sections studied from 7-year-old trees, except at 75% section from Penhalonga samples. Differences between 9-year-old heartwood and sapwood samples were detected only for S1 from Penhalonga plantation (t = 1.37; P = 0.01).

3

Fig. 3. Effect of radial position on ash content in 7 and 9-year-old Eucalyptus grandis wood. Radial variation of ash content of 7-years-old Bandula samples (3a), 7-year-old (3b), and 9-year-old (3c) both from Penhalonga samples; round symbol stands for the samples extracted at 0.30 m height from the ground, quadrangular symbol for the samples extracted at 25% height, lozenge symbol for the samples extracted at 50% height, and triangular symbol for samples extracted at 75% height, in relation to the commercial length of the stem.

3.3.2 Longitudinal position

Higher ash contents were found in samples from the base and the top of the trees, with the base showing higher contents. The lowest ash contents were found in intermediate samples (at S2 and S3) (Fig. 4). ANOVA found significant differences in ash content only in the E. grandis sapwood samples of 7-year-old collected in Bandula (F = 214.48; P < 0.00). However, the Tukey test did not find differences in the sapwood samples at 25% and 50% of commercial height from same plantation. For the 7-year-old samples from Penhalonga, only the heartwood samples were statistically different along the longitudinal axis (F = 27.90; P < 0.00). Tukey’s test showed differences in mean ash content between S1 and S2 (P = 0.01), and S2 and S4 (P < 0.00). In 9-year-old individuals, ANOVA showed differences along the length of the trees only in the radial sapwood position (F = 25.88; P < 0.00). However, just sapwood samples extracted at 0.30 m from the ground differed from all other longitudinal positions.

4

Fig. 4. Variation of ash content at different heights of 7 and 9-year old Eucalyptus grandis stems. 4a: 7-year-old sapwood samples; 4b: 9-year-old sapwood samples; 4c: 7-year-old heartwood samples; 4d: 9-year-old heartwood samples; round symbol stands for the Bandula site and rectangular symbol for the Penhalonga site. View larger in new window/tab.

4 Discussion

4.1 Effect of age on ash content variation

The results show that for sapwood, the ash content decreases with the age of the trees, which corroborates with the findings of several authors. Carvalho (1997) analyzing a hybrid Eucalyptus grandis × E. urophylla of ages 4, 7 and 9 years, Castro (2011) analyzing clones of Eucalyptus urophylla (S. T. Blake) and hybrids of E. grandis × E. urophylla with ages of 3, 4, 5 and 7 years, and Soares et al. (2015) studying the same hybrids with ages of 3, 5 and 7 years found a decrease in ash content with increasing age. Previously, ash content ranging from 0.70 to 0.22% was observed for Eucalyptus saligna (Smith) from 1 to 4-year-old, respectively (Trugilho et al. 1996). De Morais et al. (2017) found that a 1-year-old E. grandis × E. urophylla hybrid had a higher ash content than the 8-year-old did. On the other hand, the present study indicates that the ash content of core samples from 7-year-old individuals is lower than that of 9-year-old individuals. However, the difference in ash content between 7- and 9-year-old individuals is not conclusive, especially as the difference in heartwood and sapwood ash content in older trees is minimal (Table 2). Using the same origin samples of these study, Varela (2019: unpublished) did not find a significant difference in wood density for 7 and 9-year-old, both for the heartwood and sapwood radial position. That fact needs further research.

4.2 Effect of the provenance of the species

The influence of planting location on ash content was observed by some authors. The lowest ash content (0.73%) for a 3-year-old E. grandis clone was found in samples from Santa Bárbara and the highest in clones from other regions of Guanhães (0.99%) and (1.26%) in Ipaba, Brazil (Frederico 2009). Precipitation and altitude proved to be important for the amount of ash in the wood. A similar pattern was observed in the present study: trees from Penhalonga region, a mountainous area, had a lower ash content than trees from Bandula that is a plain region. However, both 7-year-old E. grandis plantation sites have similar soil types and depths (Table 1). Thus, the altitude had a greater contribution to low ash contents in Penhalonga than the precipitation, once the precipitation in Bandula region is 138 mm higher. However, other factors may be associated with the findings, too. For example, the change in the nutritional status of the plant is one of the factors that determine variations in the ash content of wood (Castro 2011; Castro et al. 2013; Hytönen et al. 2018). Analyzing E. grandis × E. urophylla hybrids from 1 and 8-year-old plantations, it was concluded that the change in plant metabolism was influenced by the characteristics of climate, soil, and topography of the site (Santos 2010; De Morais et al. 2017).

4.3 Effect of the sample radial position

In general, lower ash content was found in the region closest to the pith (heartwood) in relation to the region close to the bark (sapwood). Similar behavior was found in Eucalyptus spp. when determining high values of density and ash content as it advanced from the pith to the bark (Trugilho et al. 2005). Woods with high density generally have thick cell walls and accumulate more cellulosic material and minerals per unit volume as they grow (Ciolkosz 2010). Studying the density at the 1.3-metre-height of the same trees used in the present study, it was observed that sapwood’s basic density was higher than that of heartwood (Varela 2019). There is a strong negative correlation between ash content and cell lumen diameter, indicating an increase in ash content for woods with small lumen and higher density (Santos 2010). Sapwood is the physiologically active part of wood, composed of living cells, where all types of compounds are transported before being stored in the heartwood (Pereira et al. 2013; Silveira et al. 2013). The ash content in samples from plantation with 9-year-old individuals was not significantly affected by the radial position, regardless of the longitudinal position. This fact may probably result from a decrease in the metabolic activity of sapwood with increasing age (Castro 2011; Castro et al. 2013).

4.4 Variation of ash content along the longitudinal axis

Studies of ash content variation in the radial (bark-to-pith) and longitudinal (bottom-to-top) directions are extremely important to determine the quality and location of extraction of wood for energy (Brito et al. 1983). These variations result from anatomical differences between heartwood and sapwood, as well as changes in the growth rings (Vale et al. 2009). The highest values of ash content were verified for the positions of the base and at 75% of the commercial height. In a similar study, the lowest ash contents were found at 25% height (0.15%) and 50% height (0.19%) in relation to the commercial length of the stem (Simetti et al. 2015). The authors observed that the ash content at 25% height was lower than at the other positions in the tree. In another study, lower ash contents were found at the 1.3-metre-height (0.50%) and at 50% height (0.42%), and higher at base (0.71%), 25% (0.74%), 75% (0.72) and at 100% height (0.65 %) in five 8-year-old E. grandis × E. urophylla clone hybrids, without, however, finding statistical differences in ash content between any of the positions of the sampled trees (Coelho et al. 2018). In the present research, a generalized trend of ash content along the longitudinal axis was not found. However, in most cases the intermediate sections S2 and S3 had lower ash content in relation to the other positions along the height of the trees. Similar trends were observed by (Simetti et al. 2015; Dibdiakova et al. 2017; Coelho et al. 2018). On the other hand, for all cases, the ash content decreases from the S1 section (base, at 0.30 m from the ground) to the S2 section, which indicates that the base wood has a lower quality for energy, if considered the ash content as a quality parameter, particularly considering the ash content of 7-year-old E. grandis collected in Bandula (2.11%).

5 Conclusions

Considering the ash content of Eucalyptus grandis wood as a quality indicator in energy production, the heartwood material produces better fuel than the sapwood material. Younger individuals have a higher content of ash in the sapwood than in the heartwood. Although the ash content of E. grandis is mostly within the admissible amounts for domestic or industrial use, samples from Penhalonga plantations have better energy quality than those from Bandula plantations. No conclusive differences were found between samples from the bottom and top of the trees. This means that the samples from the tops of the trees can also be used as wood fuel, yet the bottom and intermediate wood is commonly given supremacy. The ash content proved to be a considerable parameter to evaluate the quality of Eucalyptus spp. as a woody fuel in center region of Mozambique, as it allows the selection of the best age, ideal regions for growth and position of trees capable of providing wood with a lower ash content. However, the results of the analyzes showed the need to include other variables that can better explain the reasons and patterns of ash content variation in Eucalyptus spp. wood.

Acknowledgments

The authors are grateful to Eduardo Mondlane University, in particular the Faculty of Agronomy and Forestry, for providing funds and a laboratory to carry out the research. The authors are thankful too to Swedish University of Agricultural Sciences (Department of Forest Products) and Luleå University of Technology (Division of Engineering and Wood Science), for technical and academicals support. Thanks are also extended to the IFLOMA company for allowing the extraction of the samples. Special thanks also go to Neri, Indira, Wate and Langa for their fieldwork, and Angelo Natalino by the proofreading of the English language.

Availability of research materials and data

The data and other research supplementary material required will be available for Silva Fennica, and other databases where Silva Fennica is listed when registering the DOI of the article.

Authorsʼ contributions

The contributions of the authors are as follow:

Semo Mogeia: conception of research question and design of the work; acquisition, analysis and interpretation of the data and results; scientific writing; final approval of the version to be published; and accountable for all aspects of the work in ensuring that questions related to the accuracy are appropriately investigated and solved. Alberto A. Manhiça and Andrade F. Egas: The acquisition, analysis and interpretation of the data and results; revising it critically for sound and intellectual content; final approval of the version to be published; and integrity of any part of the work are appropriately investigated and solved. Andrade F. Egas also contributed as general supervision of the research group.

References

Afonso CI (2012) Uso da antracologia como instrumento de fiscalização do carvão vegetal em Moçambique. [Use of anthracology as a tool for charcoal inspection in Mozambique]. Universidade Federal do Paraná.

Andrade CR (2009) Espectroscopia no infravermelho próximo para predizer propriedades da madeira e do carvão vegetal de plantio clonal de Eucalyptus sp. [Near infrared spectroscopy to predict wood and charcoal properties of clonal planting of Eucalyptus sp.]. Universidade Federal de Lavras. http://repositorio.ufla.br/jspui/handle/1/2365.

Atanassov B, Egas A, Falcao M, Fernandes A, Mahumane G (2012) Mozambique urban biomass energy analysis 2012. Mozambique Ministry of Energy. https://www.biofund.org.mz/wp-content/uploads/2019/01/1548673665-Final%20Report%20Mozamique%20Urban%20Biomass%202012.pdf.

Barros SV dos S, Pio N da S, Do Nascimento CC, Costa S de S (2009) Avaliação do potencial energético das espécies florestais Acacia auriculiformis e Ormosia paraensis cultivadas no município de Iranduba. [Evaluation of the energetic potential of forest species Acacia auriculiformis and Ormosia paraensis cultivated in Iranduba]. Madera y Bosques 15: 59–69. https://doi.org/10.21829/myb.2009.1521191.

Bila A (2018) Componente: Cadeia de valor da madeira derivada de plantações florestais (Projecto UTFMOZ123MOZ e GCP MOZ124MOZ). [Component: value chain of wood derived from forest plantations]. Maputo.

Braz RL, Oliveira JTS, Rosado AM, Vidaurre GB, Paes JB, Fomazelo-Filho M, Loiola G (2014) Caracterização Anatômica, Física e Química da Madeira de Clones de Eucalyptus Cultivados em Áreas Sujeitas à Ação de Ventos. [Anatomical, physical and chemical characterization of the wood of Eucalyptus clones cultivated in areas subject to the action of winds]. Rev Ciência da Madeira - RCM 5: 127–137. https://periodicos.ufpel.edu.br/ojs2/index.php/cienciadamadeira/article/view/4790.

Brito JO, Barrichelo LEG, Seixas F (1983) Análise da produção energética e de carvão vegetal de espécies de eucalipto. [Analysis of energy and charcoal production of Eucalyptus species]. IPEF 23: 53–56. https://www.ipef.br/publicacoes/scientia/nr23/cap08.pdf.

Calonego FW, Severo ETD, Perrechil MV de A, Rezende MA, Latorraca JV de F(2005) Efeito da vaporização no poder calorífico de Eucalyptus grandis. [Effect of vaporization on the calorific value of Eucalyptus grandis]. Floresta & Ambient 12: 30–35. https://doi.org/10.1590/S0100-67622006000300016.

Carneiro A de CO, Castro AFNM, Castro RVO, Santor, RC, Ferreira LP, Damásio RAP, Vital BR (2014) Potencial energético da madeira de Eucalyptus sp. em função da idade e de diferentes materiais genéticos. [Energy potential of Eucalyptus sp. depending on age and different genetic materials]. Revista Árvore 38: 375–381. https://doi.org/10.1590/S0100-67622014000200019.

Carvalho HG de (1997) Efeito da idade de corte da madeira e de variáveis de refino nas propriedades da celulose Kraft branqueada de eucalipto. [Effect of wood cutting age and refining variables on the properties of bleached Eucalyptus Kraft pulp]. Universidade Federal de Viçosa. http://www.celso-foelkel.com.br/artigos/outros/Arquivo 01_TESE- HUBEMAR.pdf.

Castro AFNM (2011) Efeito da idade e de materiais genéticos de Eucalyptus sp. na madeira e carvão vegetal. [Effect of age and genetic materials of Eucalyptus sp. on wood and charcoal]. Universidade Federal de Viçosa. https://www.locus.ufv.br/handle/123456789/3082.

Castro AFNM, Castro RVO, Carneiro A de CO, Lima JE, Santos RC, Pereira BLC, Alves ISN (2013) Análise multivariada para seleção de clones de eucalipto destinados à produção de carvão vegetal. [Multivariate analysis for selection of Eucalyptus clones for charcoal production]. Pesquisa Agropecuaria Brasileira 48: 627–635. https://doi.org/10.1590/S0100-204X2013000600008.

Ciolkosz D (2010) Characteristics of biomass as a heating fuel. Renewable and Alternative Energy Fact Sheet. https://extension.psu.edu/characteristics-of-biomass-as-a-heating-fuel.

Coelho SR de S, Sampaio J da S, Andrade FWC (2018) Características químicas da madeira de Eucalyptus urophylla × Eucalyptus grandis no sentido base-topo. [Chemical characteristics of Eucalyptus urophylla × Eucalyptus grandis wood in the base-top direction]. In: XVI Encontro Brasileiro em Madeira e em Estruturas da Madeira e III Congresso Latino-Americano de Estruturas da Madeira, pp 1–9. EESC-USP, São Carlos

Cuamba GC, Chenene ML, Egas AF, Vaz K (2016) The environmental, social and economic co-benefits of charcoal substitution in Mozambique: report biofuels policy study in Mozambique. Maputo.

Čubars E, Poiša L (2017) Analysis of ash content in composite biomass fuels. In: Tehnologija. resursi – environment, technology, resources. Rezekne Higher Education Institution, pp 31–36.

De Morais PHD, Longue Júnior D, Colodette JL, Morais ELC, Jardim CM (2017) Influence of clone harvesting age of Eucalyptus grandis and hybrids of Eucalyptus grandis × Eucalyptus urophylla in the wood chemical composition and in Kraft pubpability. Ciência Florestal 27: 237–248. https://doi.org/10.5902/1980509826462.

Dibdiakova J, Wang L, Li H (2017) Heating value and ash content of downy birch forest biomass. Energy Procedia 105: 1302–1308. https://doi.org/10.1016/j.egypro.2017.03.466.

Direcção Nacional de Florestas (2018) Inventário Florestal Nacional: Relatório Final. [National forest inventory: final report]. Maputo. https://www.biofund.org.mz/wp-content/uploads/2019/01/1548412245-Relato%CC%81rio%20do%20%20IV%20Inventa%CC%81rio%20Florestal%20Nacional.pdf.

Egas AF, Fernandes AM, Bila NF, Júnio EU, Nube TG, Wilsone A (2016) Estudo das causas de desmatamento e da degradação florestal nos distritos abrangidos pelo Programa de Gestão Integrada de Paisagens de Cabo Delgado. [Study of the causes of deforestation and forest degradation in the districts covered by the Cabo Delgado Integrated Landscape Management Program]. Maputo. https://docplayer.com.br/64611888-Fundo-do-ambiente-funab.html.

Frederico PGU (2009) Efeito da região e da madeira de eucalipto nas propriedades do carvão vegetal. [Effect of region and Eucalyptus wood on charcoal properties]. Universidade Federal de Viçosa. https://locus.ufv.br/handle/123456789/3024.

Fundo Nacional de Energia (2014) Atlas das Energias Renováveis de Moçambique: Recursos e Projectos para Produção de Electricidade. [Atlas of renewable energies of Mozambique: resources and projects for electricity production]. Maputo. https://www.instituto-camoes.pt/images/cooperacao/atlas_energia_mz.pdf.

Goulart M, Haselein CR, Hoppe JM, Farias JÁ, Pauleski DT (2003) Massa específica básica e massa seca de madeira de Eucalyptus sob efeito do espaçamento de plantio e da posição axial no tronco. [Basic specific mass and dry mass of Eucalyptus wood under the effect of planting spacing and axial position on the trunk]. Ciência Florestal 13: 167–175. https://doi.org/10.5902/198050981753.

Hytönen J, Beuker E, Viherä-Aarnio A (2018) Clonal variation in basic density, moisture content and heating value of wood, bark and branches in hybrid aspen. Silva Fenn 52, article id 9938. https://doi.org/10.14214/sf.9938.

Hytönen J, Nurmi J (2015) Heating value and ash content of intensively managed stands. Wood Research 60(1): 71–82. https://www.researchgate.net/publication/272356163_Hytonen_J_Nurmi_J_2015_Heating_value_and_ash_content_of_intensively_managed_stands_Wood_Research_60171-82.

Johnson NG (2012) Village energy system dynamics of an isolated rural West African village. Digitital Repository Graduate Theses Dissertation Iowa State Univsity. https://doi.org/10.31274/etd-180810-2210.

Kajda-Szcześniak M (2014) Characteristics of ashes from fireplace. Archives of Waste Management and Environmental Protection 16: 73–78. https://bibliotekanauki.pl/articles/357504.pdf.

Ministério da Administração Estatal (2005) Perfil do distrito da Manica, província de Manica. [Profile of the Manica district, Manica province]. Republica de Moçambique.

Ministério da Energia (2013) Estratégia de conservação e uso sustentável da energia da biomassa. [Strategy for conservation and sustainable use of biomass energy]. Maputo. https://www.biofund.org.mz/wp-content/uploads/2019/01/1548670181-2015%2010%2008%20ECUSEB%20-%20Estrategia%20de%20Conservacao%20e%20Uso%20Sustentavel%20da%20Energia%20de%20Biomassa%202.pdf.

Monjane AAR, De Barros JAP (2015) Potencialidades Bioenergéticas em Moçambique. [Bioenergetic potentialities in Mozambique]. Revista Electrônica de Energia 5: 5–12. https://revistas.unifacs.br/index.php/ree/index.

Nhancale CC (2008) Carvão e pobreza: Impacto social e económico local. [Coal and poverty: local and social economic impact]. In: International Conference on charcoal and African communities, 16th to 18th June. Maputo. https://energypedia.info/images/e/e3/PT-CARVÃO_E_POBREZA_IMPACTO_SOCIAL_E_ECONÓMICO_LOCAL-Camilo_Correia_Nhancale.pdf.

Oliveira AC, Carneiro A de CO, Vital BR, Almeida W, Pereira BLC, Cardoso MT (2010) Parâmetros de qualidade da madeira e do carvão vegetal de Eucalyptus pellita F. Muell. [Quality parameters of Eucalyptus pellita F. Muell wood and charcoal]. Scientia Forestalis 38: 431–439. https://www.ipef.br/publicacoes/scientia/nr87/cap10.pdf.

Pereira BLC, Oliveira AC, Carvalho AMML, Carneiro ACO, Santos LC, Vital BR (2012) Quality of wood and charcoal from Eucalyptus clones for ironmaster use. Int J For Res 2012, article id 523025. https://doi.org/10.1155/2012/523025.

Pereira BLC, Oliveira AC, Carvalho AMML, Colodette JL, Oliveira AC (2013) Correlações entre a relação cerne/alburno da madeira de eucalipto, rendimento e propriedades do carvão vegetal. [Correlations between the heartwood/sapwood ratio of Eucalyptus wood, yield and properties of charcoal]. BioResources 41: 217–225. https://www.ipef.br/publicacoes/scientia/nr87/cap10.pdf.

Pereira JCD, Schaitza EG, Higa AR (1997) Caracterização dos resíduos da madeira de Eucalyptus dunnii como fonte de energeia. [Characterization of Eucalyptus dunnii wood residues as a source of energy]. Embrapa Florestas. https://core.ac.uk/reader/15427768.

Republic of Mozambique (2016) Improving business climate for planted forests. Washington D.C.

Santos RC dos (2010) Parâmetros de qualidade da madeira e do carvão vegetal de clones de eucalipto. [Quality parameters of wood and charcoal from eucalyptus clones]. Lavras. http://repositorio.ufla.br/jspui/handle/1/2775.

Silveira LHC, Rezende AV, Vale AT do (2013) Teor de umidade e densidade básica da madeira de nove espécies comerciais amazônicas. [Moisture content and basic wood density of nine Amazonian commercial species]. Acta Amazônica 43: 179–184. https://doi.org/10.1590/S0044-59672013000200007.

Simetti R, Mayer SLS, Pelandra KA, Andrade C, Silva DA (2015) Características energéticas de duas espécies do gênero Eucalyptus em função do ponto de amostragem. [Energy characteristics of two species of the Eucalyptus genus according to the sampling point]. Enciclopédia Biosfera 11: 364–371. https://conhecer.org.br/ojs/index.php/biosfera/article/view/175.

Sitoe A, Salomão A, Wertz-Kanounnikoff S (2012) O contexto de REDD+ em Moçambique: causas actores e instituições. [The context of REDD+ in Mozambique: causes actors and institutions]. Bogor, Indonésia. https://www.cifor.org/publications/pdf_files/OccPapers/OP-76.pdf.

Soares VC, Bianchi ML, Trugilho PF, Höfler J, Pereira AJ (2015) Análise das propriedades da madeira e do carvão vegetal de híbridos de eucalipto em três idades. [Analysis of the properties of wood and charcoal from eucalyptus hybrids at three ages]. Cerne 21: 191–197. https://doi.org/10.1590/01047760201521021294.

Souza CR de, Rossi LMB, Azevedo CP de, Lima RMB de (2004) Comportamento da Acacia magium e de clones de Eucalyptus grandis × Eucalyptus urophylla em plantios experimentais da Amazónia Central. [Behavior of Acacia magium and Eucalyptus grandis × Eucalyptus urophylla clones in experimental plantations in Central Amazonia]. Sci Florestalis 65: 95–101. https://www.ipef.br/publicacoes/scientia/nr65/cap09.pdf.

Steierer B (2011) Highlights on wood charcoal: 2004–2009. https://www.yumpu.com/en/document/read/49844045/highlights-on-wood-charcoal-2004-2009-faostat.

Trugilho FP, Lima TJ, Mendes ML (1996) Influência da idade nas características físico-químicas e anatômicas da madeira de Eucalyptus saligna. [Influence of age on the physical-chemical and anatomical characteristics of Eucalyptus saligna wood]. Cerne 2: 1–15. http://www.bibliotecaflorestal.ufv.br/handle/123456789/18347.

Trugilho FP, Da Silva RMJ, Mori AF, Lima JT, Mendes LM, Mendes LFB (2005) Rendimentos e caracteríscas do carvão vegetal em função da posição radial de amostragem em clones de Eucalyptus. [Charcoal yield and characteristics as a function of the radial sampling position in Eucalyptus clones]. Cerne 11: 178–186. https://www.agencia.cnptia.embrapa.br/Repositorio/carvaovegetal1_000g7due97f02wx5ok0wtedt3bhzxro3.pdf.

Vale AT do, Brasil MAM, Leão AL (2002) Quantificação e caracterização energética da madeira e casca de espécies do Cerrado. [Quantification and energy characterization of wood and bark of Cerrado species] Ciência Florestal 12: 71–80. https://doi.org/10.5902/198050981702.

Vale AT do, Rocha LR, Del Menezzi CHS (2009) Massa específica básica da madeira de Pinus caribaea var. hondurensis cultivado em Cerrado. [Basic specific mass of Pinus caribaea var. hondurensis grown in Cerrado]. Scientia Forestalis 37: 387–394. https://www.ipef.br/publicacoes/scientia/nr84/cap06.pdf.

Varela N (2019) Influência da posição radial, idade e local de crescimento nas propriedades físicas de 5 espécies de Eucalyptus. [Influence of radial position, age and growth site on the physical properties of 5 Eucalyptus species] Dissertação de Mestrado/FAEF/Universidade Eduardo Mondlane. Maputo.

Varma A, Behera B (2009) Green energy: biomass processing and technology. Capital Publishing Company, New Dehli. ISBN 8185589135.

Vidaurre GB, Carneiro A de CO, Vital BR, Santos RC, Valle, MLA (2012) Propriedades energéticas da madeira e do carvão de Pericá (Schizolobium amazonicum). [Energetic properties of wood and coal from Pericá (Schizolobium amazonicum)]. Revista Árvore 36: 365–371. https://doi.org/10.1590/S0100-67622012000200018.

Vidaurre GB, Lombardi LR, Nutto L, França FJN, Oliveira JTS, Arantes MDC (2013) Propriedades da madeira de reação. [Reaction wood properties]. Floresta e Ambiente 20: 26–37. https://doi.org/10.4322/floram.2012.041.

Zanuncio AJV, Carvalho AG, Trugilho PF, Monteiro TCM (2014) Extractives and energetic properties of wood and charcoal. Revista Árvore 38: 369–374. https://doi.org/10.1590/S0100-67622014000200018.

Total of 52 references.


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