Deforestation and Biomass Production in Miombo Forest

Deforestation and Biomass Production in Miombo Forest: Comparison

Please note this is a comparison between Version 2 by Rita Xu and Version 1 by David Ariza-Mateos.

Miombo is one of the most widely distributed ecosystems in Angola, with a great social and environmental value. Thus, the rural population uses the biomass as fuel and miombo provides important ecosystem services, such as its carbon sequestration capacity. The objectives of this work were (i) to assess deforestation in miombo forest in Huambo province (Angola) during the last 20 years, (ii) to evaluate carbon storage capacity of miombo, and (iii) to calculate the charcoal productive capacity of those forests. From 2000 to 2019, 359,130 ha (12.96%) were deforested in Huambo province. Thirty-six woody species were identified as major components of miombo forest, the most frequent being Albizia anthunesiana, Brachystegia spiciformis, Julbernardia paniculata, Monote spp., Brachystegia boemii, Isoberlinea angolensis, Anisophyllea boehmii, Syzygium guineense, and Erythrophleum africanum. The total biomass estimated in miombo forest was 195.05 Mg ha−1 (55.02 Mg ha−1 radical and 140.04 Mg ha−1 area), with a total wood volume of 78.57 m3 ha−1. This represents values of 91.67 Mg ha−1 of accumulated carbon and 336.13 Mg ha−1 of CO2 equivalent. The potential charcoal productivity was 15,359.9 kg ha−1, corresponding to 24.78 trees ha−1. The Annual Allowable Cutting Volume was 10.77 m3 ha−1 year−1, 14.13 m3 ha−1 year−1, 21.17 m3 ha−1, and 32.85 m3 ha−1 year−1 for rotation lengths of 55, 40, 25, and 15 years, respectively, corresponding to a potential annual charcoal productivity of 2107.08 Kg ha−1 year−1, 2762.96 Kg ha−1 year−1, 4139.21 Kg ha−1, and 422.56 Kg ha−1 year−1. However, deforestation rates in the last 19 years and low charcoal productive capacity could compromise the sustainability of the Miombo ecosystem and its value as an ecosystem service provider in the province if appropriate management strategies are not developed.

miombo
deforestation
charcoal
biomass

1. Introduction

Miombo is one of the most important forest ecosystems in southern Africa, covering large areas of Angola, Mozambique, Tanzania, Zimbabwe, Zambia, and the Democratic Republic of Congo, covering between 2.5 to 3.6 million km

^[1]. This ecosystem includes mosaics of dry forests and wooded savannahs, with a high diversity of flora and fauna ^[2], with medium productivity and high social value in terms of woody fuel, building materials, pasture, food, and medicinal plants ^[3]. Miombo usually has a multistrata structure: an upper stratum with adult trees between 15 and 18 m tall and a density around 65 trees ha

⁻¹

; an intermediate stratum with trees between 8 and 12 m tall and a density of 80 trees ha

⁻¹

; and the lower stratum with saplings, shrubs, and grassland with a height lower than 8 m and a density range between 375 and 500 trees ha

⁻¹ [4,5]. The volume varies between 14 and 59 m

^[4][5]. The volume varies between 14 and 59 m

⁻¹

in dry Miombo and between 41 and 100 m

⁻¹ in wet Miombo [4], with higher productivity in wet Miombo forests [6].

More than 55% of Angola’s land area is forested, amounting to about 69 Mha, of which 58.6 Mha is Miombo lands, 3.6 Mha correspond to other native forest and plantation forest, and 2.1 Mha of other lands with scattered trees [7,8]. Angolan Miombo is characterized by species of the genus Brachystegia, Julbernardia, and Isoberlinia, [9]. This ecosystem provides many ecosystem services to the rural population, including timber and nontimber products biomass for household energy production (firewood and charcoal), fodder for livestock, medicinal plants, and wild fruits. Water cycle regulation, the reduction of erosion, and the diversity of habitats favoring a high biodiversity are also important ecosystem services of Miombo lands [9]. Estimated data confirm that Miombo forest in Angola has an annual harvest capacity of 326,000 m

in wet Miombo ^[4], with higher productivity in wet Miombo forests ^[6].

More than 55% of Angola’s land area is forested, amounting to about 69 Mha, of which 58.6 Mha is Miombo lands, 3.6 Mha correspond to other native forest and plantation forest, and 2.1 Mha of other lands with scattered trees ^[7][8]. Angolan Miombo is characterized by species of the genus Brachystegia, Julbernardia, and Isoberlinia, ^[9]. This ecosystem provides many ecosystem services to the rural population, including timber and nontimber products biomass for household energy production (firewood and charcoal), fodder for livestock, medicinal plants, and wild fruits. Water cycle regulation, the reduction of erosion, and the diversity of habitats favoring a high biodiversity are also important ecosystem services of Miombo lands ^[9]. Estimated data confirm that Miombo forest in Angola has an annual harvest capacity of 326,000 m

and an average annual commercial timber productivity of 0.3 m

⁻¹

year

⁻¹

^[7]. In addition, Miombo forests play an important role in atmospheric CO

₂

sequestration with fixation rates of up to 39.6 MgC ha

⁻¹ in above-ground biomass [10]. Thus, under sustainable management criteria, the Miombo could be an important source of economic income and employment, especially in rural areas. However, at present, this ecosystem is under great pressure from the local population, which puts its sustainability at risk, mainly due to some specific deforestation drivers.

In general, there is a differentiation between proximate causes (or drivers) and driving forces (or indirect drivers). Proximate causes are human activities that have a direct influence on the deforestation while driving forces are complex interactions of key social, economic, political, cultural, and technological processes [11]. Several works have assessed deforestation drivers as a tool for decision-making to reduce emissions from deforestation [12]. The main drivers identified in tropical forests are the agriculture expansion [13], urban expansion, infrastructural development, mining activity, and commercial timber exploitation or as fuel (firewood and charcoal), grazing, and forest fires [14].

Studies carried out in sub-Saharan Africa have concluded that the subsistence agriculture is the main driver in the poorest rural populations, often associated with deforestation for charcoal production and/or forest fires [15,16]. Thus, some authors link deforestation to food security, with the most frequent causes being agriculture [17] and exploitation of biomass as fuel [18]. In Angola, the main proximate drivers are the overextraction of timber resources, clearing for agricultural purposes, unregulated burning, and overgrazing [19]. This has led to an increase in deforestation rate from 0.2% in 2000 to 0.8% in the period 2000–2019 [7], compromising the current and future ecosystem services of the Miombo.

Charcoal production is a very important activity in Miombo and is increasingly becoming a lucrative business. Charcoal production in rural areas causes large environmental impact, especially in comparison with that generated by fuelwood, mainly in periurban areas [7]. This activity, which is continuously growing in Africa, is one of the main causes of deforestation and forest degradation both in Africa and Angola [18,20]. One of the main problems related to charcoal production in the Angolan Miombo is the lack of data about the potential productive capacity of this ecosystem. This leads to a lack of tools for assessing admissible annual cut values and, thus, for sustainable management. Some of the tools often used for assessing productive capacity, such as dendrochronology, have not often been used in such studies in tropical forests due to the great diversity of species and the difficulty in assessing annual growth [21]. Previous works have assessed annual growth in Miombo species to determine the annual allowable cutting volume [22]. Therefore, study of the productivity of the Miombo ecosystem is an important tool to increase knowledge about the charcoal production capacity and the annual allowable cutting volume, including the variables in forest management plans to increase the sustainability of this activity.

The aim of this study was to assess the productivity of Miombo ecosystem in Huambo (Angola) to estimate C sequestration and charcoal production capacity. The specific objectives were (i) to assess deforestation in miombo forest in Huambo province (Angola) during the last 20 years, (ii) to evaluate carbon storage capacity of miombo, and (iii) to calculate the charcoal productive capacity of those forests and compare them with the carbon storage capacity. The results obtained will provide information about the charcoal production for the management of miombo woodland resources in Huambo province, ensuring the sustainability of the activity and ecosystem services and improving forest management in a context of vulnerability of the local population. This information could also open up new funding opportunities, facilitating the engagement of rural communities with initiatives for reducing emissions from deforestation, forest degradation, and forest management (REDD+) or Clean Development Mechanisms (CDM) [1,23].

in above-ground biomass ^[10]. Thus, under sustainable management criteria, the Miombo could be an important source of economic income and employment, especially in rural areas. However, at present, this ecosystem is under great pressure from the local population, which puts its sustainability at risk, mainly due to some specific deforestation drivers.

In general, there is a differentiation between proximate causes (or drivers) and driving forces (or indirect drivers). Proximate causes are human activities that have a direct influence on the deforestation while driving forces are complex interactions of key social, economic, political, cultural, and technological processes ^[11]. Several works have assessed deforestation drivers as a tool for decision-making to reduce emissions from deforestation ^[12]. The main drivers identified in tropical forests are the agriculture expansion ^[13], urban expansion, infrastructural development, mining activity, and commercial timber exploitation or as fuel (firewood and charcoal), grazing, and forest fires ^[14].

Studies carried out in sub-Saharan Africa have concluded that the subsistence agriculture is the main driver in the poorest rural populations, often associated with deforestation for charcoal production and/or forest fires ^[15][16]. Thus, some authors link deforestation to food security, with the most frequent causes being agriculture ^[17] and exploitation of biomass as fuel ^[18]. In Angola, the main proximate drivers are the overextraction of timber resources, clearing for agricultural purposes, unregulated burning, and overgrazing ^[19]. This has led to an increase in deforestation rate from 0.2% in 2000 to 0.8% in the period 2000–2019 ^[7], compromising the current and future ecosystem services of the Miombo.

Charcoal production is a very important activity in Miombo and is increasingly becoming a lucrative business. Charcoal production in rural areas causes large environmental impact, especially in comparison with that generated by fuelwood, mainly in periurban areas ^[7]. This activity, which is continuously growing in Africa, is one of the main causes of deforestation and forest degradation both in Africa and Angola ^[18][20]. One of the main problems related to charcoal production in the Angolan Miombo is the lack of data about the potential productive capacity of this ecosystem. This leads to a lack of tools for assessing admissible annual cut values and, thus, for sustainable management. Some of the tools often used for assessing productive capacity, such as dendrochronology, have not often been used in such studies in tropical forests due to the great diversity of species and the difficulty in assessing annual growth ^[21]. Previous works have assessed annual growth in Miombo species to determine the annual allowable cutting volume ^[22]. Therefore, study of the productivity of the Miombo ecosystem is an important tool to increase knowledge about the charcoal production capacity and the annual allowable cutting volume, including the variables in forest management plans to increase the sustainability of this activity.

2. MaSterial and Methodudy Sites

The study site is located in Huambo province (Angola), which covers an area of 34,270 km

² on the Central Plateau (Figure 1). Huambo is the province with the second-highest stock of biomass in Angola [24]; however, it is one of three provinces with the highest loss of forest cover in the country [25] and has the fifth-highest emissions [26]. In this case, it is not only the number of trees removed that threatens the stability of Miombo forests, but also the deforestation patterns associated with the demand for charcoal and firewood production for cooking and heating [20].

on the Central Plateau (Figure 1). Huambo is the province with the second-highest stock of biomass in Angola ^[23]; however, it is one of three provinces with the highest loss of forest cover in the country ^[24] and has the fifth-highest emissions ^[25]. In this case, it is not only the number of trees removed that threatens the stability of Miombo forests, but also the deforestation patterns associated with the demand for charcoal and firewood production for cooking and heating ^[20].

The climate—according to the Thornthwaite classification—is characterized as humid mesotherm, with cold and dry winters from May to September and hot and rainy summers from October to April [27]. The climatology is conditioned by a high altitude (more than 95% of its surface above 1500 m) with an average temperature of 20 °C, maximum temperatures of 25–27 °C, and minimum of 11–13 °C, precipitation of 1366 mm, and relative humidity that varies between 60 and 70% in January and 35 and 70% in August [27]. The predominant soils are of the ferralitic type. According to the Angolan Phytogeographic Chart [28], the province of Huambo is dominated by savanna-type Miombo forests with a high presence of Julbernardia and Brachystegia species with patches of low-density miombo on mesoplanaltic slopes (between the valleys of the Keve and Kwanza rivers) and high-elevation meadows (anharas) on ferralitic and thin soils.

Forty-nine permanent plots were established according to stratified sampling into the Huambo province. At each stratum, plots were randomly distributed based on the forest cover phytogeographic map of the Huambo province by Jaxa in 2015 [29], the soil map of Angola [28], and Huambo roads with a buffer of 500 m per side (Open Street Map, 2016). Each plot was georeferenced taking the central coordinates (GPS Garmin MAP 60 csx) and projected according to the UTM projection system. Once each plot was located, a circular plot following the N–S direction of 10 m-radius (314 m²) was laid out using a handheld compass (Suunto KB-14/360R G Compass; Finland) and a 50-m measuring tape (Lufkin^®, Mexico) (Figure 1).

Figure 1. Distribution of miombo plots in the Huambo province (Angola). Forest area corresponds to the year 2000.

The climate—according to the Thornthwaite classification—is characterized as humid mesotherm, with cold and dry winters from May to September and hot and rainy summers from October to April ^[26]. The climatology is conditioned by a high altitude (more than 95% of its surface above 1500 m) with an average temperature of 20 °C, maximum temperatures of 25–27 °C, and minimum of 11–13 °C, precipitation of 1366 mm, and relative humidity that varies between 60 and 70% in January and 35 and 70% in August ^[26]. The predominant soils are of the ferralitic type. According to the Angolan Phytogeographic Chart ^[27], the province of Huambo is dominated by savanna-type Miombo forests with a high presence of Julbernardia and Brachystegia species with patches of low-density miombo on mesoplanaltic slopes (between the valleys of the Keve and Kwanza rivers) and high-elevation meadows (anharas) on ferralitic and thin soils.

3. Deforestation

The forest area in Huambo province in 2000 was 2,770,205 ha, of which 359,130 ha (12.96%) were deforested during the period 2000–2019 (Figure 2). The highest levels of deforestation occurred in the municipalities of Caála (20.67%), Bailundo (15.17%), and Longonjo (13.16%); the lowest levels occurred in the municipalities of Huambo and Ecunha, with 8.02% and 8.68% of deforested area, respectively (Table 1).

Figure 2. Deforestation in Huambo province. Forest area in 2000 (treecover2000); deforested area and non-deforested area from 2000 to 2019.

Table 1. Deforestation in Huambo province. Forest area in 2000 (ha); deforested area from 2000 to 2019 expressed in ha and as a percentage.

Municipality	Forest Area 2000 (ha)	Deforestation (ha)	Deforestation (%)
Bailundo	662,026	100,449	15.17
359,130
12.96

4. Composition and Structure

Forty tree species were found in the study area, of which 36 were identified by their scientific name and 33 by their local name. Two species were not identified by either their local name or scientific name, although they were perfectly discriminated from the rest, so they were identified as independent species. The species with the highest frequencies were Albizia anthunesiana (12.94%), Brachystegia spiciformis (12.28%), Julbernardia paniculata (8.44%), Monote spp. (8.42%), Brachystegia boemii (7.85%), Isoberlinea angolensis (5.88%), Anisophyllea boehmii (5.86%), Syzygium guineense (4.84%), and Erythrophleum africanum (4.50%). The average density of adult trees was 3616.38 trees ha⁻¹. Caála and Tchicala have the highest densities (4747.35 trees ha⁻¹ and 4313.09 trees ha⁻¹, respectively) and Ukuma and Bailundo have the lowest densities (3151.26 trees ha⁻¹ and 3226.16 trees ha⁻¹, respectively).

5. Accumulated Carbon and CO₂ Equivalent

Total biomass was 195.05 Mg ha⁻¹ (55.02 Mg ha⁻¹ below-ground biomass and 140.04 Mg ha⁻¹ above-ground biomass (Table 2)). The highest biomass values were found in Ukuma and Bailundo (289.85 Mg ha⁻¹ and 218.18 Mg ha⁻¹, respectively), and the lowest in Tchicala and Longonjo (113.03 Mg ha⁻¹ and 157.69 Mg ha⁻¹, respectively) (Table 3).

Table 2. Biomass, accumulated Carbon, and CO₂ equivalent in the Miombo of Huambo province expressed in Mg ha⁻¹.

Variable	Above-Ground	Below-Ground	Total
Biomass	¹

₂ eq., and below-ground CO₂ eq. expressed in Mg ha⁻¹. For each variable, the mean value and standard deviation of all plots of Huambo province are included; further, maximum and minimum values found in plots are included.

Table 3. Biomass, volume, accumulated Carbon, and CO₂ equivalent by municipality. Mean values expressed in Mg ha⁻¹ and standard deviation are presented in the table.

Municipality	Total Biomass	¹	Volume	²	Accumulated C	³	CO2eq	⁴
140.04 ± 108.59	(24.68–716.41)	55.02 ± 31.69
Bailundo		(14.68–209.55)	218.18 ± 214.35	195.05 ± 140.14 (39.36–925.96)	79.09 ± 36.01	102.55 ± 100.75	376.00 ± 369.40
Caála	270,146	55,826	20.67
Accumulated Carbon	²	65.82 (11.60–336.71)	25.86 ± 14.89
Caála		(6.90–98.48)	177.10 ± 75.42	91.67 (18.50–435.20)	92.39 ± 46.73	Cathiungo	225,175	26,568
83.24 ± 35.45	305.21 ± 129.98	CO2 equivalent	11.80
³	241.32 (42.53–1234.61)	94.81
Ekunha		(25.30–361.12)	212.01 ± 49.72	336.13 (67.84–1595.74)	Ecunha	113,311	9837	8.68
Huambo	205,780	16,511	8.02
72.86 ± 27.16	99.65 ± 23.37	365.37 ± 85.68
Katchiungo	178.48 ± 46.66	83.87 ± 5.49	83.88 ± 21.93	307.58 ± 80.42
Londuimbale	181.23 ± 42.11	70.88 ± 12.14	85.18 ± 19.79	312.32 ± 72.57
Longonjo	157.69 ± 55.75	77.24 ± 17.73	74.11 ± 26.20	271.75 ± 96.08
Tchicala	113.03 ± 58.74	56.44 ± 23.15	53.12 ± 27.61	194.79 ± 101.23
Tchingenje	184.29 ± 112.72	70.62 ± 26.28	86.62 ± 52.98	317.59 ± 194.26
Ukuma	289.85 ± 6.74	96.71 ± 10.48	136.23 ± 3.17	499.51 ± 11.62

¹ Total biomass, expressed in Mg ha⁻¹. ² Wood volume, expressed in m³ ha⁻¹. ³ Total accumulated Carbon, expressed in Mg ha⁻¹. ⁴ Total CO₂ eq., expressed in Mg ha⁻¹. For each variable, the mean value and standard deviation by municipality are included.

The mean wood volume in the Miombo forest was 78.57 m³ ha⁻¹, with the highest values in Ukuma and Caála (96.71 m³ ha⁻¹ and 92.39 m³ ha⁻¹, respectively) and the lowest in Tchingenje and Loundimbale (70.62 m³ ha⁻¹ and 70.88 m³ ha⁻¹, respectively) (Table 3).

The above-ground accumulated C was 65.82 Mg ha⁻¹ and the below-ground accumulated C was 25.86 Mg ha⁻¹; total accumulated C was 91.67 Mg ha⁻¹ (Table 2). The highest values were found in Ukuma and Bailundo (136.23 Mg ha⁻¹ and 102.55 Mg ha⁻¹, respectively) and the lowest values in Tchicala and Longonjo (53.12 Mg ha⁻¹ and 74.11 Mg ha⁻¹, respectively) (Table 3). These values correspond to a CO₂ equivalent of 336.13 Mg ha⁻¹ (94.81 Mg ha⁻¹ of above-ground CO₂eq and 241.32 Mg ha⁻¹ of below-ground CO₂eq) (Table 2). The highest values were found in Ukuma and Bailundo (499.51 Mg ha⁻¹ and 376.00 Mg ha⁻¹, respectively) and the lowest values in Tchicala and Longonjo (194.79 Mg ha⁻¹ and 271.75 Mg ha⁻¹, respectively) (Table 3).

6. Productive cCapacity

The Potential Charcoal Productivity (PCP) was 15,359.9 kg ha

6.1. Potential Charcoal Productivity (PCP)

The PCP was 15,359.9 kg ha

⁻¹

, although the variability between municipalities was very high, ranging from 11,034.87 Kg ha

⁻¹

for (Tchicala) to 18,907.60 Kg ha

⁻¹ for (Ukuma).

The Allowable Cutting Value (ACV) was 24.78 trees ha⁻¹, with the lowest values in Londuimbale (22 trees ha⁻¹) and the highest values in Caála (31.57 trees ha⁻¹).

for (Ukuma) (Table 4).

Table 4. Potential Charcoal Productivity (PCP) and Allowable Cutting Value (ACV) by municipality. Mean values and standard deviation of PCP expressed in Kg ha⁻¹ are included. Mean values and standard deviations of ACV expressed in number of trees ha⁻¹ are included.

Municipality	¹ PCP (Kg ha⁻¹)	² ACV (N. Trees ha⁻¹)

Bailundo	15,461.62 ± 7040.92	23.06 ± 5.41
Bailundo	15,461.62 ± 7040.92	23.06 ± 5.41
Caála	18,061.42 ± 9136.63	31.57 ± 21.69
Caála	18,061.42 ± 9136.63	31.57 ± 21.69
Ekunha	14,245.06 ± 5310.49	25.50 ± 3.54
Ekunha	14,245.06 ± 5310.49	25.50 ± 3.54
Katchiungo	16,395.84 ± 1073.17	24.75 ± 4.79
Kacthiungo	16,395.84 ± 1073.17	24.75 ± 4.79
Londuimbale	13,857.53 ± 2373.48	22.00 ± 1.00
Londuimbale	13,857.53 ± 2373.48	22.00 ± 1.00	Londuimbali	241,025
Longonjo
30,931	12.83
15,100.04 ± 3465.85		25.00 ± 4.24
Longonjo	15,100.04 ± 3465.85	25.00 ± 4.24	Longonjo	177,232	23,325	13.16
Tchicala	27.50 ± 11.12
Tchicala
	11,034.87 ± 4525.17
11,034.87 ± 4525.17	27.50 ± 11.12	Mungo	280,719
Tchingenje
25,533	9.10
13.806.39 ± 5136.87		22.43 ± 5.91
Tchingenje	13.806.39 ± 5136.87	22.43 ± 5.91	Tchikala	358,482	44,211	12.33
Ukuma	22.67 ± 4.51
Ukuma
	18,907.60 ± 2048.33
18,907.60 ± 2048.33	22.67 ± 4.51	Tchinjenje	82,765	10,788	13.03
Ukuma	153,543	15,151	9.87
Total	2,770,205

¹ Total biomass, above-ground biomass, and below-ground biomass expressed in Mg ha⁻¹. ² Total accumulated Carbon, above-ground Carbon, and Below-ground Carbon expressed in Mg ha⁻¹. ³ Total CO₂ eq., above-ground CO

Mean values and standard deviations of PCP expressed in Kg ha

⁻¹

²Mean values and standard deviation of ACV expressed in number of trees ha

Mean values and standard deviation of ACV expressed in number of trees ha⁻¹.

6.2. Allowable Cutting Value (ACV)

The ACV was 24.78 trees ha⁻¹, with the lowest values in Londuimbale (22 trees ha⁻¹) and the highest values in Caála (31.57 trees ha

⁻¹.

When comparing the biomass carbon storage with the potential charcoal productivity, there is a correlation at the extreme values (Tchicala and Ukuma) despite the correlation coefficient not being very high (0.5).

For a rotation period of 55 years, the Annual Allowable Cutting (ACV) was 14.31 ± 5,61 trees ha

) (Table 4).

6.3. Annual Allowable Cutting (AAC)

For a rotation period of 55 years, the ACV was 14.31 ± 5,61 trees ha

⁻¹

year

⁻¹

, increasing for shorter periods (40 years, 19.68 ± 7.72 trees ha

⁻¹

year

⁻¹

; 25 years, 31.5 ± 12.35 trees ha

⁻¹

year

⁻¹

; 15 years, 52.5 ± 20.58 trees ha

⁻¹

year

⁻¹).

Values of AAC corresponding to values of Annual Allowable Cutting Volume (AACV) of 10.77 ± 6.05 m

6.4. Annual Allowable Cutting Volume (AACV)

Values of AAC corresponding to values of AACV of 10.77 ± 6.05 m

⁻¹

year

⁻¹

, 14.13 ± 7.96 m

⁻¹

year

⁻¹

, 21.17 ± 11.93 m

⁻¹

year

⁻¹

, and 32.85 ± 18.51 m

⁻¹

year

⁻¹ (55, 40, 25, and 15 years, respectively).

The Potential Annual Allowable Charcoal Productivity (PAACP) were 2107.08 ± 1183.53 kg ha

(55, 40, 25, and 15 years, respectively).

6.5. Potential Annual Allowable Charcoal Productivity (PAACP)

The PAACP were 2107.08 ± 1183.53 kg ha

⁻¹

year

⁻¹

, 2762.96 ± 1557.41 kg ha

⁻¹

year

⁻¹

, 4139.21 ± 2333.17 kg ha

⁻¹

year

⁻¹

, and 6422.56 ± 3620.24 kg ha

⁻¹

year

⁻¹ for the rotation lengths considered (55, 40, 25, and 15, respectively).

for the rotation lengths considered (55, 40, 25, and 15, respectively).

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1. Introduction

2. MaSterial and Methodudy Sites

3. Deforestation

4. Composition and Structure

5. Accumulated Carbon and CO2 Equivalent

6. Productive cCapacity

6.1. Potential Charcoal Productivity (PCP)

15,461.62 ± 7040.92

23.06 ± 5.41

Caála

18,061.42 ± 9136.63

31.57 ± 21.69

14,245.06 ± 5310.49

25.50 ± 3.54

16,395.84 ± 1073.17

24.75 ± 4.79

13,857.53 ± 2373.48

22.00 ± 1.00

15,100.04 ± 3465.85

25.00 ± 4.24

27.50 ± 11.12

11,034.87 ± 4525.17

13.806.39 ± 5136.87

22.43 ± 5.91

Ukuma

22.67 ± 4.51

18,907.60 ± 2048.33

6.2. Allowable Cutting Value (ACV)

6.3. Annual Allowable Cutting (AAC)

6.4. Annual Allowable Cutting Volume (AACV)

6.5. Potential Annual Allowable Charcoal Productivity (PAACP)

References

5. Accumulated Carbon and CO₂ Equivalent