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Article

Soil Properties of a Tef-Acacia decurrens-Charcoal Production Rotation System in Northwestern Ethiopia

by
Miftha Beshir
1,2,*,
Fantaw Yimer
2,
Nicolas Brüggemann
3,* and
Menfese Tadesse
2
1
College of Agriculture and Environmental Science, Arsi University, Asela P.O. Box 193, Ethiopia
2
Wondo Genet College of Forestry & Natural Resources, Hawassa University, Shashemane P.O. Box 128, Ethiopia
3
Forschungszentrum Jülich GmbH, Institute of Bio- and Geosciences-Agrosphere (IBG-3, Agrosphere), 52425 Jülich, Germany
*
Authors to whom correspondence should be addressed.
Soil Syst. 2022, 6(2), 44; https://doi.org/10.3390/soilsystems6020044
Submission received: 18 March 2022 / Revised: 16 April 2022 / Accepted: 26 April 2022 / Published: 1 May 2022
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Abstract

:
A tef-Acacia decurrens-charcoal production rotation system, a unique indigenous climate-smart agricultural technology of northwest Ethiopia, is increasingly seen as a promising strategy for improving soil properties. This study investigated the effect of the tef-Acacia decurrens-charcoal production rotation system on soil properties. In total, 112 soil samples (7 treatments × 4 depths × 4 replicates) were collected and analyzed inside and outside randomly selected charcoal production spots in the tef-Acacia decurrens-charcoal production rotation system and from an adjacent tef monocropping system. The soil properties examined generally exhibited significant variation between the tef monocropping system and the tef-Acacia decurrens-charcoal production rotation system, and between soil depths, as well as with respect to charcoal production spots in the system. The system resulted in a significant increase in SOC, TN, available phosphorus, available sodium, available nitrate and ammonium in general, and in total contents of K, P and Mn in the 0–20 cm depth. Charcoal production in the system significantly increased the total content of P, Al, and Fe, as well as the available nitrate and sulfate in the charcoal production spot. The variation in soil proprieties between the land use types and with respect to charcoal production spots in the TACP system were possibly due to the effect of the Acacia decurrens trees, and fire and fine charcoal residues from charcoal production, indicating the capacity of the tef-Acacia decurrens-charcoal production rotation system to improve soil properties.

1. Introduction

Poor land management and plant nutrient depletion are increasingly seen as a fundamental biophysical causes of declining food security among smallholder farm households in sub-Saharan Africa (SSA) [1,2,3,4]. In addition, anthropogenic climate change, the increasing costs of mineral fertilizers and land grabbing are continuously exacerbating this situation [5,6]. In Ethiopia, the problems are even more severe. The majority of Ethiopian farmers are living on land prone to degradation due to low nutrient inputs, soil erosion and droughts, the extent of which is increasing due to an increasing population density [7,8]. Moreover, due to the associated loss of soil fertility and resilience to climate change, soil degradation is one of the most serious constraints limiting crop productivity in Ethiopia [9,10,11].
The most prevalent land management activities for fighting these problems and improving food security in smallholder crop farming are the expansion and intensification of agricultural practices [12,13,14]. However, the increased expansion and intensification of agricultural practices could result in declining soil fertility due to severe soil disturbance, thus increasing the decomposition of soil organic matter (SOM) and soil nutrient depletion [15,16]. A feasible option for addressing this problem may be the adoption of climate-smart agricultural technologies (CSAT) [17,18]. Climate-smart agriculture (CSA) is an approach that helps to guide the actions needed to transform and reorient agricultural systems to effectively support development and ensure food security in a changing climate [17,19]. The three pillars of CSA are: to sustainably increase agricultural productivity and improve the income and livelihood of farmers; to build resilience and adaptation to climate change; and to reduce and/or remove greenhouse gas (GHG) emissions, where possible [19].
Smallholder farmers in SSA have developed a number of alternative CSAT that they can use either alone or in combination to build resilience against climate-induced calamities such as severe drought [20,21,22,23]. Agroforestry is one of the paradigmatic alternatives to climate-smart agriculture [22]. It is a land use practice that introduces trees and/or shrubs to croplands and/or livestock [24,25]. It is one of the beneficial land management practices for increasing soil carbon (C) storage, potentially mitigating GHG emissions [26,27] and improving soil fertility [28,29] in agricultural landscapes. In SSA, agroforestry practices can increase crop yields by 2 to 4 times compared with monocropping [30]. In their reviews, [31] found that the absolute rate of soil organic carbon (SOC) sequestration of agroforestry systems in SSA was up to 14 Mg C ha−1 y−1.
The tef-Acacia decurrens-charcoal production rotation system (referred hereafter as the TACP system) is a unique (and rapidly expanding) agroforestry system in the Fagita Lekoma district of the northwestern highlands of Ethiopia. It involves the intercropping of a tef crop, A. decurrens (a fast-growing acacia tree species that is adapted to acidic soil conditions [32]) and the production of charcoal on the same piece of land in rotation. The TACP system has been adopted by the local farmers in the study area for the last 30 years; it is one of the two agricultural systems in the study area, along with a tef monocropping system (TM system), from which the TACP system was developed. The charcoal is produced using traditional mound kilns. In this system, the charcoal is produced for marketing by burning wood of A. decurrens by a method explained in detail by [33]. In the TACP system, charcoal residues and charred biomass left on the kiln sites could help to ameliorate and improve the fertility of the soils by direct addition and retention of nutrients [34].
The application of charcoal (biochar) to soil is an emerging strategy for sequestering carbon, reducing GHG emissions and improving soil quality in recent years [35,36,37,38]. Evidence has shown that the application of biochar can play a significant role in enhancing SOC content and hence carbon sequestration [39], water-holding capacity [40,41], soil aeration, base saturation, nutrient retention and availability; decreasing fertilizer needs and nutrient leaching [37]; stimulating microbial biomass and activity [42]; enhancing crop yield and reducing anthropogenic GHG fluxes [35,43]. Significant changes in soil properties, such as soil pH, base saturation, electrical conductivity, exchangeable Ca, Mg, K, Na, and available P (Pav) in the soil were also observed in studies carried out to investigate the effect of charcoal production at kiln sites in agricultural and forestry systems in different parts of the world [44,45,46,47]. Furthermore, biochar can reduce the risk of environmental pollutants (organic and inorganic) in soils by forming complexes or through sorption of heavy metals and/or organic compounds [48,49,50]. Nonetheless, biochar may contain contaminates itself, either introduced by its feedstock (e.g., heavy metals) or co-produced during pyrolysis.
In general, trees can exert positive, negative or neutral effects on soil properties and plant communities in agroforestry systems, depending on the local environmental conditions and the position in the landscape. The inclusion of nitrogen-fixing trees, such as A. decurrens, in the TACP system can potentially improve the physicochemical and biological soil conditions through numerous processes, including biological N2 fixation, maintenance of or increases in SOM, uptake of nutrients from below the reach of crop roots, increased water infiltration and storage, reduced loss of nutrients by erosion and leaching, improved the soil’s physical properties, reduced soil acidity and improved soil biological activity [25,51]. Several authors have reported on the effect of trees on soil fertility and the associated crop yields in Ethiopia [52,53,54,55,56]. For example, the effect of Acacia trees on the soil’s physical, chemical and biological properties have been studied extensively in different settings [57,58,59].
While much is known about the independent effects of biochar and nitrogen-fixing trees on soil properties, few studies have examined the synergetic effect of charcoal production and nitrogen-fixing trees such as A. decurrens for modification of the soil properties in agroforestry. This study was designed (1) to assess the impact of the TACP system (in three rotations) on soil properties as compared with the TM system and (2) to evaluate the influence of charcoal production on soil properties in the TACP system under the charcoal production spots.

2. Materials and Methods

The study site is located in the Fagita Lekoma district in the Awi zone of the Amhara region of northwestern Ethiopia (10°57′23″ N to 11°11′21″ N, 36°40′01″ E to 37°05′21″ E, between 1800 and 2900 m above mean sea level) (Figure 1). The mean monthly rainfall between 2007 to 2017 was 1328 mm [60] with an estimated average annual temperature of 17.5 °C [61] (Figure 2). The area is part of the moist subtropical agro-ecological zone of the northwestern highlands of Ethiopia. Farmers in the district practice mixed subsistence cropping–livestock farming systems. The major crops grown are tef (Eragrostis tef Zucc.), barley (Hordeum vulgare L.), wheat (Triticum aestivum L.) and potato (Solanum tuberosum L.). The predominant soil types are Nitisols and Acrisols, according to the World Reference Base for Soil Resources (WRB), which are characterized by moderately and strongly acidic conditions, respectively [10,62]. The soil textural fractions of the study area are presented in Table 1. The area is characterized by flatlands and a moderately steep rolling topography, which covers 65% of the district [63]. The major land use categories of the district are agriculture (60.8%) and forestry (19.5%), while the remaining area is used for grazing land and settlement [64].
The main fertilizers used in the TM system are urea and diammonium phosphate (DAP). Both are applied mostly at a rate of about 50 kg ha−1, but the rate varies (40–60 kg ha−1) depending on the socioeconomic status of the farmers [63,64]. In the TACP system, A. decurrens trees are planted in the fields at about 25–50 cm spacing immediately after tef is cultivated. The tef is harvested after 3 to 5 months, whereas A. decurrens is grown for about 4 to 5 years. Thereafter, the trees are harvested to produce charcoal in the same field (Figure 3).

2.1. Soil Sampling and Laboratory Analysis

The soil samples were taken from the TM and the TACP system (in the first, second and third rotations) with four replicates from four depths (0–20, 20–40, 40–60 and 60–100 cm). In the TACP system, the subsoil samples containing charcoal debris (biochar) from charcoal production were taken from inside and outside six randomly selected charcoal production spots at the end of the cropping period. The six subsoil samples were combined into a single composite soil sample for each depth and replication. The sampling design covered seven different areas (treatments) (1) the TM system with no charcoal production, plus (2) the first rotation inside a charcoal production spot, (3) the first rotation outside a charcoal production spot, (4) the second rotation inside a charcoal production spot, (5) the second rotation outside a charcoal production spot, (6) the third rotation inside a charcoal production spot and (7) the third rotation outside a charcoal production spot in the TACP system, resulting in a total of 112 soil samples (7 treatments × 4 depths × 4 replicates).
Soil samples for chemical analysis were passed through a 2 mm soil sieve. Soil texture was determined using the hydrometric method, after removing the SOM using hydrogen peroxide and thereafter dispersing the soil with sodium hexametaphosphate [66]. The USDA particle size classes, viz. sand (2.0–0.05 mm), silt (0.05–0.002 mm) and clay (<0.002 mm), were used for assigning the textural classes. Bulk density was determined by the core method [66]. Soil pH was measured with combined electrodes in a 1:2.5 soil/water suspension. Soil organic carbon (SOC) was determined by the Walkley–Black oxidation method [67]. Total nitrogen (TN) was measured by the Kjeldahl digestion method [68]. Available phosphorus (Pav), available potassium (Kav), available nitrate (NO3−), available magnesium (Mgav), available sulfate (SO42−), available ammonium (NH4+) and available phosphate (PO43−) were extracted by the calcium acetate lactate (CAL) method [69]. Total nutrients (Na, K, P, Mg, Ca, Al, Fe and Mn) were extracted by the aqua regia (concentrated HCl:HNO3 3:1) digestion method, followed by ICP-OES analysis [70]. The soil samples were analyzed at the Central Analytical Laboratory (ZEA-3) of the Forschungszentrum Jülich, Jülich, Germany.

2.2. Data Analysis

The data were then grouped according to the land use types (the TM and the TACP system, with three rotations) and soil depth classes. Two comparisons were conducted: (i) a comparison of the soil properties under the TACP system in the first, second and third rotations with those under the TM system, and (ii) a comparison of soil properties inside the charcoal production spots with the area outside them in the TACP system.
Statistical differences were tested using one-way analysis of variance (ANOVA) following the general linear model (GLM) procedure of SPSS version 20.0 for Windows [71]. Tukey’s honestly significance difference (HSD) test was used for means separation when the analysis of variance showed statistically significant differences (p < 0.05). Linear regression analysis was performed to examine the relationship between TN and SOC content.

3. Results

3.1. Variation in the Soil Properties with the TACP and TM Systems and Soil Depth

3.1.1. Soil Organic Carbon, Total Nitrogen, C:N Ratio and Bulk Density

Soil organic carbon (SOC) content varied significantly with the land use type and soil depth (Table 2). Generally, SOC content was higher under the TACP system than under the TM system, and it was higher in the first rotation than in the two other rotations. SOC content was higher overall (up to 225%) in the topsoil than in the adjacent subsurface soil layer for all land use types (Table 2). In the 0–20 cm soil layer, SOC was significantly higher in the first and the second rotations than in the TM system.
The total nitrogen content of the soil showed significant differences between land use type and soil depth (Table 2). Soil TN was 91.7% higher in the first rotation of the TACP system than under the TM system, while it did not show significant differences from the second and third rotations of TACP system. Depthwise, soil TN was higher by up to 255% in the topsoil than in the other depths under both the TM and TACP systems. TN was significantly and positively correlated with SOC content (r2 = 0.96) (Figure 4).
The carbon to nitrogen (C/N) ratio varied with land use type and soil depth (Table 2). The C/N ratio was higher in the first rotation of the TACP system than under the TM system. Under both the TACP and TM systems, the C/N ratio was higher in the topsoil compared with the other soil depths. In the 0–20 cm and 40–60 cm soil layers, the C/N ratio was significantly higher under the TACP system than under the TM system.
There was a significant variation in Bd with land use type and soil depth (Table 2). The Bd was 15% higher in the first rotation of the TACP system than under the TM system. It declined with depth in all rotations of the TACP system.

3.1.2. Soil pH, Pav, Kav, Naav and Mgav

Significant differences in pH were observed between land use types (Table 2). There was no significant difference in soil pH with soil depth under the TACP system, in contrast to the TM system (Table 2). Under the TM system, the soil pH was higher compared with that under the TACP system and declined with soil depth (Table 2). The soil pH under the TACP system and the TM system was within the medium to strongly acidic range (Table 2).
Available phosphorus varied significantly with land use type (Table 3), and was 159.1% and 77.8% higher in the first and second rotations of the TACP system, respectively, compared with the TM system. Variation in Pav was also observed across soil depths under the TACP system but not under the TM system (Table 3). Available phosphorus was higher in the topsoil compared with the other depths under the TACP system. In the 0–20 cm soil layer, Pav was significantly higher in the first and second rotations of the TACP system than that under the TM system.
There was a significant variation in available potassium (Kav) with land use type and soil depth (Table 3). Kav decreased by about 56.7% in the third rotation of the TACP system compared with the TM system. The mean Kav in the topsoil (0–20 cm) was higher than in the soil depth immediately below it (20–40 cm) under both the TM and TACP systems.
The ANOVA for available sodium (Naav) and available magnesium (Mgav) revealed that they were significantly affected by land use type but not by soil depth (Table 3). Available Na increased by 152.1% and 184.7% in the first and third rotations, respectively, whereas Mgav decreased by 66.0% and 44.1% in the first and second rotations of the TACP system, respectively, compared with the TM system.

3.1.3. Available Ammonium, Nitrate, Phosphate and Sulfate

Available ammonium (NH4+), available nitrate (NO3−) and available sulfate (SO42−) varied significantly with land use type but not with soil depth, except in the 20–40 cm and 40–60 cm soil layers of the TM system (Table 3). Available NH4+ and NO3− increased by up to 300% and 10% in the TACP system in different rotations, while available sulfate (SO42−) decreased by up to 77%. Available phosphate (PO43−) was below the detection limit under both the TM and TACP systems across all depths (Table 3).

3.1.4. Total Contents of Soil Na, K, P, Mg, Ca, Al, Fe and Mn

Total soil contents of K, Mg, Ca, Fe, P and Al overall varied significantly between the TM and the TACP system, and with soil depth (Table 4). In the TACP system, the mean total contents of Ca were higher after three rotations, whereas K, Mg and P decreased with increasing number of rotations; while Mn remained unaffected. In contrast, total Na, Fe and Al contents showed an inconsistent pattern. The total contents of K, Mg and Mn were higher overall in the 0–20 cm depth of the third rotation of the TACPA system, whereas for other elements and rotations of the TACPA system no clear pattern could be found. In the 0–20 cm soil layer, the total Na content was significantly higher in the second and the third rotations of the TACP system than in the TM system. The total content of P (20–40 cm layer) was significantly higher in the first rotation of the TACP system than in the TM system. The total content of Mn was significantly higher in the 0–20 soil layer of the third rotation of the TACP system than in the TM system.

3.2. Variation of Soil Properties between Areas inside and outside Charcoal Production Spots

3.2.1. Soil Organic Carbon and Bulk Density, Total Nitrogen and C:N Ratio

There was no difference in soil SOC, TN or C:N ratio between the soils inside and outside charcoal production spots in the three rotations of the TACP system (Table 5). Moreover, no significant differences were observed in Bd between the soils from inside and outside charcoal production spots under the TACP system (Table 5).

3.2.2. Soil pH, and Available Phosphorus, Potassium, Magnesium and Sodium

No significant differences were observed in soil pH (Table 5), Pav and Kav (Figure 5a,b) between soils inside and outside the CPS. Available Na varied significantly between soils inside and outside the charcoal production spots of the TACP system (Figure 5) and was up to 139% higher inside the charcoal production spots compared with outside them.

3.2.3. Available Ammonium, Sulfate, Nitrate and Phosphate

Available ammonium (NO3−) and available sulfate (SO42−) increased significantly inside the CPS of the TACP system compared with outside them in different rotations by up to 88% and 75%, respectively; no statistical difference was observed for available ammonium (NH4+) (Table 5). Available phosphate (PO43−) was less than 0.0008 mg kg−1 inside the CPS of all the three rotations of the TACP system.

3.2.4. Total Soil Element Contents

Our results showed that total P varied significantly between soils inside and outside charcoal production spots in the TACP system (Table 5). It was 19% higher inside the charcoal production spots compared with outside them. No significant difference was observed in the total contents of Na, K, B, S, Mg, Ca, Mn and Cu.
Our results also showed that total Al and Fe varied significantly between soils inside and outside the charcoal production spots in the TACP system (Table 5). Total Al was up to 7% higher in the second rotation and 25% higher in the third rotation, while the total Fe was up to 11% higher in the second rotation and up to 14% higher in the third rotation.

4. Discussion

4.1. Variation in the Soil Properties between the TACP and TM Systems and with Soil Depth

We found that SOC, TN, the C/N ratio, Bd, and the contents of Al, K, Mg, Ca, Fe, Pav, Pav, Naav, available NO3− and NH4+ were significantly higher under the TACP than under the TM system; SOC, TN, the C/N ratio, Pav and Kav were higher in topsoil than in the rest of the soil depths (Table 2 and Table 3, Figure 5).
The significant improvement in SOC and TN under the TACP system could be explained by the progressive accumulation of litter [72] and root biomass [73,74] under the canopy of A. decurrens and probably the effects of tef crop residues left after harvest. Many authors have reported higher SOC levels and TN concentrations under the canopy of trees and in topsoil for other species, which is in concert with the present investigation (e.g., [66,67,68]). For instance, a study on the impacts of Millettia ferruginea on soil fertility [75] observed significantly higher SOC and TN beneath the canopy compared with the open field outside the canopy.
Soil enrichment in terms of SOC and TN in soils under trees in an agricultural system is concentrated in a few centimeters of the soil, especially under leguminous trees [76,77,78,79], which is in agreement with the increases in SOC and TN of up to 225% and 255% in the topsoil of the TACP system in the present study, respectively. For instance, [75] found significantly higher soil SOC and TN in both the topsoil and subsoil under the canopy of Millettia ferruginea compared with the open area outside the canopy zone of M. ferruginea. The increase in SOC and TN under the TACP system could also be explained by the addition of charcoal debris to the soil [80,81]. In several studies, adding biochar when cultivating the soil of farmland has been shown to significantly increase SOC [81,82,83] and TN [84,85] in the surface soil.
The C/N ratio in the studied soils was higher under the TACP system and in the topsoil under both the TM and TACP systems, probably due to the input of litter from the A. decurrens trees, which could have a high C/N ratio, and/or due to the formation of recalcitrant nitrogen compounds in the soil during charcoal production [86]. Tree litter and biochars with high C/N ratios are low in quality [82]. The C/N ratios of the current study are contradictory to the findings of different authors [75,82]. For instance, [75,87] observed a lower C/N ratio under M. ferruginea than in open areas and in soil treated with biochar, which they attributed to the high quality of the litter of M. ferruginea trees and biochar.
Contrary to our expectations, the TACP system brought about a significant increase in terms of Bd in the first and second rotations, as well as with depth. The result is, however, not entirely surprising. Several previous studies have found that biochar does not always rapidly improve Bd and other physical soil properties, depending on the management (e.g., [88,89]) or because of the slower decomposition rate of wood-derived biochar, such as that of A. decurrens, as a result of its high C content [90,91].
The accumulation of aboveground biomass and the associated cation uptake by the tree component of agroforestry systems are among the possible indirect causes of the decreased pH in soils [92]. Studies have also indicated the rise of soil pH due to application of biochar (e.g., [84,93,94]). On the contrary, in our study, soil pH was found to be higher under the TM system compared with the TACP system, which may be an indication of overcultivation leading to prolonged uptake of basic cations [95]. The relatively higher pH under the TACP system could also be due to other mechanisms that release H+ ions, such as soil base cation uptake (or depletion) by the decomposition of organic matter to organic acids and CO2, root respiration and nitrification. The findings of this research are in agreement with [77], who found a higher pH under the canopy of Balanites aegyptiaca.
The observed higher Pav in the soil of rotation 1 of the TACP system compared with the soil under TM, and in the topsoil could be due to higher SOM accumulation from litterfall from A. decurrens and due to the charcoal debris in the soil. The increase in Pav could also be associated with the relatively higher pH under the TACP system, which could make phosphorus more available in the soil [96]. Higher Pav content was also reported by [97] and [98] as result of the presence of trees in the agricultural land use systems, and by [96] in soil treated with biochar, which confirms the relatively higher P found here.
Trees in an agroforestry system can potentially improve nutrient availability via nutrient-enriched litterfall [25,51]. In the present study, however, Kav was observed to be higher under the TM system compared with the TACP system in the 0–20 cm depth. This could be due to the application of K fertilizer in the TM system by the local farmers. In contrast, Naav was higher under the TACP system, which could be attributed to the ability of the fine charcoal residues in the soil of the TACP system to retain nutrients [35,99]. Contrary to our study, [55,100] reported a significant decrease in Naav in soil treated with charcoal debris.
The increased availability of NO3− and NH4+ in the TACP system could be due to change in microbial abundance [63] and the increased nitrification and oxidation of ammonia [96] as result of the charcoal residues. The high capacity of the charcoal residues to absorb nutrients enables their effective absorption of ammonia (NH3), reducing its loss through volatilization [34,101]. The higher SO42− under the TACP system compared with the TM system in the present study could also be attributed to the effect of the microbially mediated transformation of nutrients in the soil by the addition of the charcoal residue [96]. Our findings of higher NO3− and NH4+ in the soil of TACP corroborate the findings of previous studies that compared soil nutrients in agroforestry systems versus agricultural fields [102,103,104].
In our study, the TACP system increased the total contents of K, Mg and Ca overall, while it decreased the total content of P and Al in the different rotations. However, notice that due to charcoal production, the total content of P and Al was significantly higher inside the charcoal production spots under the TACP system compared with outside them (see Table 4). Previous studies revealed that application of biochar in agroforestry systems could significantly increase the total nutrient contents in the soil (e.g., [93,94,95]), though beneficial effects depend on the soil type and properties [105]. For example, [82] found a 60 to 670% increase in the total contents of K, Mg and Ca after application of biochar. The higher total content of K, P and Mg in the 0–20 cm depth of the third rotation of the TACP system in the present study could be attributed to the release of nutrients to the soil by the decomposition of leaf litter of A. decurrens. The findings on K, P, Mg and Ca were also similar to those reported by [106] but for trees other than A. decurrens.

4.2. Comparison of Soil Properties between Areas inside and outside the Charcoal Production Spots

Charcoal production under the TACP system resulted in a significant increase in the total contents of P, Al, Fe, available NO3− and SO42− inside the CPS compared with outside them, but no increases in SOC, TN, Bd, Pav and Kav (Table 4 and Table 5).
The effect of fire on soil SOC is highly dependent on the type and intensity of the fire, among other factors, such as soil moisture, the soil type and the nature of the burned materials. Therefore, the effects on soil processes and their intensity by fire are highly variable [107]. At the site studied here, charcoal production did not bring about the expected change in SOC. This result contradicts the findings of [46,108], who reported a significant change in soil SOC in their studies of on the effect of charcoal production on soil properties. This result is also not in line with [109], who found higher SOC in charcoal production areas compared with non-charcoal sites in southwest Ethiopia.
The nonsignificant difference in soil Bd between areas inside and outside charcoal production spots in the TACP system indicates that the charcoal production spots in the TACP system were not sufficiently exposed to fire. The bulk density did not change inside the CPS, which may be because the soil’s physical properties do not change after fire unless a very severe fire occurs [110]. These results are not in agreement with the findings of [109], who found significantly higher SOC and a 13% reduction in Bd at kiln sites compared with the adjacent field.
Charcoal production under the TACP system also brought about a change in soil TN, demonstrating inadequate volatilization of nitrogen during charcoal production, which is the dominant mechanism of N loss from soil systems, usually in the form of ammonia and other related N gases [111]. This result agreed with [46] but was inconsistent with [109], who found a significant change in soil TN in their studies on the effect of charcoal production on soil properties in southwestern Ethiopia.
Though the soil pH decreased significantly from the initial value of 5.18 under TM to 4.49, 4.63 and 5.00 in the first, second and third rotations of the TACP system, respectively, no significant difference was observed in soil pH between soils inside and outside the CPS, which may be due to insufficient accumulation of base-forming cations or the production of alkaline primary oxides, carbonates and the loss of organic acids in the CPS [112]. In contrast to this result, [113] found increases of up to 1.2 pH units due to an accumulation of ashes from charcoal production.
In this study, no significant difference was observed in Pav and Kav between areas inside and outside CPS. The nonsignificant difference in Pav suggests that it might have not volatilized enough at the temperature generated during the charcoal production in the TACP system to make a significant variation. This result is inconsistent with [34,100,114], who found an increase in Pav in a slash-and-burn experiment. The nonsignificant difference in Kav could be attributed the direct release of fine charcoal residues from charcoal production under the TACP system. In disagreement with our result, [100] reported a significant increase in Kav in soil exposed to fire.
The results of this study indicated that Nav inside the charcoal production spots was higher compared with that outside them under the TACP system. This could be due to the accumulation of charred biomass. Orguntunde et al. [34,39,109] also reported a significant increase in the availability of Na at kiln sites compared with the adjacent agricultural fields.
Two different mechanisms responsible for the increase in the availability of NO3− inside the charcoal production spots are the direct addition of NO3− from charcoal residues or enhanced nitrification following charcoal production [96]. The rise in the available SO42− in this study inside the charcoal production spots was presumably due to the degradation of SOM by the heat of charcoal production, which increased the concentration of SO42− in the soil solution [115]. This result is consistent with other studies (e.g., [28,37,39,107]) that compared the soil nutrient status of kiln sites with adjacent land use systems.
In the present study, charcoal production increased the Al and Fe content in the charcoal production spots. This is presumably due to the release of large quantities of ashes, which are rich in nutrients, during biomass burning [116,117]. Similar results were obtained in studies related to charcoal production in Ghana [46], slash-and-burn management and soil amended with charcoal [34]. Oguntunde et al. [46] and [118] attributed the increase in these elements in charcoal production spots to decrease of nutrient leaching, especially Al and Fe which are mediated by the high adsorption capacity of charcoal [119]. According to [118], addition of charcoal in a soil system inhibits leaching of nutrients by up to 68% after depending on soil types.

5. Conclusions

Taken together, the studied soil of the TACP system in northern Ethiopia showed marked variations in SOC, TN, the C/N ratio, Bd, and the contents of Al, K, Mg, Ca, Fe, Pav, Pav, Naav, available NO3− and NH4+ with land use type, and variations in SOC, TN, C/N ratio, Pav and Kav with respect to soil depth. The TACP system resulted in improvements in SOC, TN and soil nutrients compared with the TM system. The marked improvement could be associated with the effect of litter accumulation, belowground root degradation of the acacia trees and the addition of charcoal residues to the soil. Under the TACP system, charcoal production increased the total contents of P, Al and Fe, as well as the available NO3− and available SO42− in the CPS. The increases could be related to impact of fine charcoal residues and ashes from charcoal production. Therefore, it is concluded that in general, the TACP system improves some soil properties and nutrients generally and in the charcoal production spots specifically. In the future, the joint effect of soil-improving trees and charcoal production on soil proprieties still need to be studied further to ascertain our research.

Author Contributions

Conceptualization, M.B., F.Y. and N.B.; methodology, M.B., F.Y. and N.B.; software, M.B.; formal analysis, M.B.; investigation, M.B.; resources, N.B.; data curation, M.B.; writing—original draft preparation, M.B.; writing—review and editing, M.B., F.Y., N.B. and M.T.; supervision, F.Y., N.B. and M.T. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by Forschungszentrum Jülich.

Informed Consent Statement

Not applicable.

Data Availability Statement

The datasets analyzed in this study are available from the corresponding author on reasonable request.

Acknowledgments

M.B. acknowledges funding by the German Academic Exchange Service (DAAD) through the funding program “Research Grants—Bi-nationally Supervised Doctoral Degrees, 2019/20” (57440919). M.B is also grateful to all field workers and lab technicians for their field and lab assistance.

Conflicts of Interest

The authors declare no conflict of interest.

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Soilsystems 06 00044 g001 550
Figure 1. Map of the study area.
Figure 1. Map of the study area.
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Soilsystems 06 00044 g002 550
Figure 2. Maximum, minimum and average temperatures, and mean monthly rainfall of Fagita Lekoma district from 2007 to 2017.The data used in this figure were extracted with permission from [65].
Figure 2. Maximum, minimum and average temperatures, and mean monthly rainfall of Fagita Lekoma district from 2007 to 2017.The data used in this figure were extracted with permission from [65].
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Figure 3. Photographs of (a) the TM system; (b) the TACP system: [(c) Acacia decurrens seedlings planted with tef, showing Acacia decurrens at the tree stage; (d) piles of Acacia decurrens wood; (e) a charcoal production kiln and (f) harvesting of the charcoal, in the TACP system].
Figure 3. Photographs of (a) the TM system; (b) the TACP system: [(c) Acacia decurrens seedlings planted with tef, showing Acacia decurrens at the tree stage; (d) piles of Acacia decurrens wood; (e) a charcoal production kiln and (f) harvesting of the charcoal, in the TACP system].
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Figure 4. Relationship between total nitrogen and the soil organic carbon content of the two land-use systems.
Figure 4. Relationship between total nitrogen and the soil organic carbon content of the two land-use systems.
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Figure 5. (a) Available phosphorus (Pav, mg kg−1), (b) available potassium (Kav, mg kg−1), (c) available magnesium (Mgav, mg kg−1), (d) available sodium (Naav, mg kg−1), from soil inside and outside charcoal production spots (CPS) of the three rotations of the TACP system. Different letters indicate significant differences between soils inside and outside charcoal production spots (CPS) within each rotation.
Figure 5. (a) Available phosphorus (Pav, mg kg−1), (b) available potassium (Kav, mg kg−1), (c) available magnesium (Mgav, mg kg−1), (d) available sodium (Naav, mg kg−1), from soil inside and outside charcoal production spots (CPS) of the three rotations of the TACP system. Different letters indicate significant differences between soils inside and outside charcoal production spots (CPS) within each rotation.
Soilsystems 06 00044 g005
Table
Table 1. Soil textural fractions (%) of soil samples studied in relation to land use types (TM and TACP system) and soil depths (mean ± standard error of the mean).
Table 1. Soil textural fractions (%) of soil samples studied in relation to land use types (TM and TACP system) and soil depths (mean ± standard error of the mean).
VariablesDepth (m)Land Use Types
TM SystemTACP System
Rotation 1Rotation 2Rotation 3
Sand0–0.229.75 ± 0.5028.63 ± 0.3729.25 ± 0.7526.75 ± 0.40
0.2–0.430.50 ± 0.5026.22 ± 0.3330.00 ± 0.0030.75 ± 0.36
0.4–0.619.50 ± 0.3019.50 ± 0.3319.87 ± 0.4019.25 ± 0.41
0.6–1.015.25 ± 0.2515.36 ± 0.2615.75 ± 0.5915.50 ± 0.42
Mean23.75 ± 1.7023.25 ± 1.0923.71 ± 1.1223.15 ± 1.14
Silt0–0.229.50 ± 0.2928.62 ± 0.4829.25 ± 0.7530.37 ± 0.10
0.2–0.417.50 ± 0.2929.50 ± 0.1930.00 ± 0.1817.12 ± 0.12
0.4–0.617.75 ± 0.2519.50 ± 0.3719.87 ± 0.4619.43 ± 0.58
0.6–1.019.87 ± 0.2515.37 ± 0.2315.75 ± 0.3216.62 ± 0.23
Mean20.37 ± 1.3720.53 ± 0.9920.53 ± 1.0420.81 ± 0.53
Clay0–0.241.00 ± 0.4141.00 ± 0.3341.20 ± 0.1242.87 ± 0.83
0.2–0.452.00 ± 0.4152.60 ± 0.2752.50 ± 0.1852.12 ± 0.35
0.4–0.662.75 ± 0.2562.00 ± 0.3561.83 ± 0.3561.62 ± 0.26
0.6–1.068.00 ± 0.4168.40 ± 0.2767.60 ± 0.4268.50 ± 0.71
Mean55.94 ± 2.6856.22 ± 1.8255.81 ± 1.8156.28 ± 1.76
Table
Table 2. pH, soil organic carbon (SOC) (%), total nitrogen (TN) (%) content, C/N ratio and bulk density (Bd) (g cm−3) of soil under the TM and TACP systems (mean ± standard error of the mean).
Table 2. pH, soil organic carbon (SOC) (%), total nitrogen (TN) (%) content, C/N ratio and bulk density (Bd) (g cm−3) of soil under the TM and TACP systems (mean ± standard error of the mean).
VariablesDepth (m)Land Use Types
TM SystemTACP System
Rotation 1Rotation 2Rotation 3
Bd0–0.20.76 ± 0.06 Aa0.90 ± 0.04 Aa0.87 ± 0.04 Aa0.81 ± 0.05 Aa
0.2–0.40.84 ± 0.08 Aa0.99 ± 0.04 BAa0.98 ± 0.04 BCa0.89 ± 0.03 Aa
0.4–0.60.94 ± 0.08 Aa1.05 ± 0.03 BCa1.06 ±0.03 Ca0.98 ± 0.03 BAa
0.6–1.01.03 ± 0.04 Aa1.13 ± 0.02 Ca1.00 ± 0.03 Ca1.07 ± 0.04 CBa
Mean0.89 ± 0.04 a1.02 ± 0.02 b1.01 ± 0.02 b0.94 ± 0.03 a
SOC0–0.22.34 ± 0.36 Aa4.19 ± 0.26 Ab4.10 ± 0.26 Ab1.87 ± 0.26 Aa
0.2–0.40.77 ± 0.36 Ba2.00 ± 0.27 Ba0.59 ± 0.28 Ba0.48 ± 0.27 Ba
0.4–0.60.63 ± 0.36 Ba2.72 ± 0.30 BAb0.50 ± 0.28 Ba0.36 ± 0.28 Ba
0.6–1.00.37 ± 0.36 Ba2.09 ± 0.30 Bb0.57 ± 0.26 Ba0.41 ± 0.27 Ba
Mean1.03 ± 0.32 a2.83 ± 0.25 b1.50 ± 0.24 a0.82 ± 0.24 a
TN0–0.20.20 ± 0.03 Aa0.35 ± 0.02 Ab0.32 ± 0.02 Ab0.19 ± 0.02 Aa
0.2–0.40.10 ± 0.03 Ba0.16 ± 0.02 Ba0.09 ± 0.02 Ba0.10 ± 0.02 Ba
0.4–0.60.09 ± 0.03 Ba0.22 ± 0.03 BAb0.09 ± 0.02 Bb0.08 ± 0.02 Bb
0.6–1.00.08 ± 0.03 Ba0.16 ± 0.03 Bb0.10 ± 0.02 Ba0.09 ± 0.02 Ba
Mean0.12 ± 0.02 a0.23 ± 0.02 b0.156 ± 0.02 a0.12 ± 0.02 a
C/N ratio0–0.211.49 ± 0.97 Aab12.08 ± 0.69 Ab12.72 ± 0.69 Ab9.86 ± 0.69 Aa
0.2–0.47.82 ± 0.97 Ca8.09 ± 0.79 Aa6.25 ± 0.79 Ba5.00 ± 0.79 Ba
0.4–0.66.94 ± 0.97 Ca12.39 ± 0.87 Ab5.45 ± 0.79 Bb4.40 ± 0.79 Bc
0.6–1.04.86 ± 0.97 Ba12.81 ± 0.79 Ab5.67 ± 0.69 Ba4.65 ± 0.73 Ba
Mean7.78 ± 0.79 a11.36 ± 0.63 b7.76 ± 0.59 a6.22 ± 0.60 a
pH0–0.25.06 ± 0.09 Aa4.48 ± 0.06 Ab4.65 ± 0.06 Ab5.02 ± 0.06 Aa
0.2–0.44.93 ± -0.09 Ba4.47 ± 0.06 Ab4.49 ± 0.06 Ab5.03 ± 0.06 Aa
0.4–0.65.26 ± -0.09 Aa4.49 ± 0.06 Ab4.62 ± 0.06 Ab5.07 ± 0.06 Aa
0.6–1.05.45 ± 0.09 Ca4.52 ± 0.06 Abc4.74 ± 0.06 Abc4.90 ± 0.06 Aac
Mean5.18 ± 0.05 a4.49 ± 0.03 b4.63 ± 0.03 c5.00 ± 0.03 d
Values followed by the same uppercase letter(s) within a column and/or lowercase letters across a row are not significantly different.
Table
Table 3. Available phosphorus (Pav), available potassium (Kav), available sodium (Naav), available (Mgav), available ammonium (NH4+), nitrate (NO3−) and sulfate (SO42−) content in soils in the TM and TACP systems (mean ± standard error of the mean., all contents in mg kg−1).
Table 3. Available phosphorus (Pav), available potassium (Kav), available sodium (Naav), available (Mgav), available ammonium (NH4+), nitrate (NO3−) and sulfate (SO42−) content in soils in the TM and TACP systems (mean ± standard error of the mean., all contents in mg kg−1).
VariablesDepth (m)Land Use Types
TM SystemTACP System
Rotation 1Rotation 2Rotation 3
Pav0–0.27.33 ± 1.87 Aa22.63 ± 1.42 Ab21.56 ± 1.33 Ab3.75 ± 1.33 Aa
0.2–0.46.42 ± 1.88 Aa10.22 ± 1.53 Ba5.21 ± 1.32 Ba3.00 ± 1.53 Aa
0.4–0.64.47 ± 1.88 Aab13.52 ± 1.53 Bb5.7 ± 1.53 Ba3.65 ± 1.53 Aa
0.6–1.03.30 ± 1.88 Aac9.53 ± 1.53 Bb5.55 ± 1.33 Bbc3.70 ± 0.19 Ac
Mean5.38 ± 0.94 a13.94 ± 0.75 b9.51 ± 0.70 c3.52 ± 0.73 a
Kav0–0.2321.00 ± 17.30 Aa65.63 ± 13.08 Ab32.49 ± 12.23 Ab151.27 ± 12.23 Ab
0.2–0.4145.00 ± 17.30 Ba8.23 ± 17.30 Ab10.53 ± 14.12 Bb29.93 ± 14.12 Bb
0.4–0.6117.50 ± 17.31 Ba42.80 ± 15.48 Aba8.78 ± 14.12 Bab58.67 ± 14.12 Bb
0.6–1.02.25 ± 17.30 Ba6.00 ± 14.12 Ab9.27 ± 12.23 Bb40.45 ± 13.08 Ba
Mean161.44 ± 8.30 a30.67 ± 7.54 b15.27 ± 6.61 b70.08 ± 6.71 c
Naav0–0.24.37 ± 3.35 Aa13.44 ± 2.37 Aab8.81 ± 2.37 Aab18.38 ± 1.32 Ab
0.2–0.45.00 ± 3.35 Aa14.14 ± 2.37 Aa8.66 ± 2.37 Aa15.11 ± 1.32 Aa
0.4–0.64.68 ± 3.35 Aa13.56 ± 2.37 Aab9.95 ± 2.37 Aaa14.93 ± 1.32 Ab
0.6–1.07.88 ± 3.35 Ba13.82 ± 2.37 Aa9.46 ± 2.37 Aa13.62 ± 1.32 Aa
Mean5.45 ± 1.67 a13.74 ± 1.18 b9.22 ± 1.18 a15.51 ± 1.18 c
Mgav0–0.2246.25 ± 29.53 Aa91.70 ± 28.89 Aab149.97 ± 20.89 Aab245.75 ± 20.89 Ab
0.2–0.4206.25 ± 29.53 Aa94.01 ± 28.89 Aa141.27 ± 20.89 Aa269.50 ± 20.89 Aa
0.4–0.6242.75 ± 29.53 Aa88.58 ± 20.89 Ab148.19 ± 20.89 Ab297.32 ± 20.89 Aa
0.6–1.0405.75 ± 29.53 Ba99.72 ± 20.89 A176.29 ± 20.89 Aa252.62 ± 20.89 Aa
Mean275.25 ± 14.76 a93.50 ± 10.4 b153.93 ± 10.44 c266.30 ± 10.44 a
Ammonium0–0.20.001 ± 0.000 Aa0.001 ± 0.000 Aba0.001 ± 0.000 Abc0.001 ± 0.000 Ac
0.2–0.40.001 ± 0.000 Ba0.001 ± 0.000 Aa0.001 ± 0.000 Aa0.001 ± 0.000 Aa
0.4–0.60.001 ± 0.000 Ba0.001 ± 0.000 Aab0.001 ± 0.000 Aab0.001 ± 0.000 Ab
0.6–1.00.001 ± 0.000 Ca0.001 ± 0.000 Ab0.001 ± 0.000 Aa0.001 ± 0.000 Aa
Mean0.001 ± 0.000 a0.001 ± 0.000 b0.001 ± 0.000 c0.0010 ± 0.000 a
Nitrate0–0.20.0010 ± 0.001 Aa0.004 ± 0.002 Aa0.001 ± 0.001 Aa0.005 ± 0.001 Aa
0.2–0.40.001 ± 0.001 Aa0.005 ± 0.002 Aa0. 002 ± 0.001 Aa0.003 ± 0.001 Aa
0.4–0.60.001 ± 0.001 Aa0.005 ± 0.002 Aa0.001 ± 0.001 Aa0.004 ± 0.001 Aa
0.6–1.00.001 ± 0.001 Aa0.003 ± 0.002 Aa0.001 ± 0.001 Aa0.003 ± 0.001 Aa
Mean0.001 ± 0.001 a0.004 ± 0.001 b0.001 ± 0.001 a0.004 ± 0.001 b
Sulfate0–0.20.001 ± 0.000 Aa0.001 ± 0.000 Aa0.000 ± 0.000 Aa0.000 ± 0.000 Aa
0.2–0.40.001 ± 0.000 Aa0.001 ± 0.000 Aa0.001 ± 0.000 Ba0.001 ± 0.000 Aa
0.4–0.60.002 ± 0.000 Aa0.001 ± 0.000 Aa0.000 ± 0.000 Ca0.001 ± 0.000 Aa
0.6–1.00.001 ± 0.000 Aa0.001 ± 0.000 Aa0.000 ± 0.000 Ca0.000 ± 0.000 Aa
Mean0.001 ± 0.001 a0.001 ± 0.001 a0.000 ± 0.001 b0.000 ± 0.001 b
Values followed by the same uppercase letter(s) within a column and/or lowercase letters across a row are not significantly different.
Table
Table 4. Total element content of Na, K, P, Mg, Ca, Al, Fe and Mn (in %) of soil under the TM and TACP systems at different depths (mean ± standard error of the mean), (* Total nutrient contents below the detection limit have not been presented in the table).
Table 4. Total element content of Na, K, P, Mg, Ca, Al, Fe and Mn (in %) of soil under the TM and TACP systems at different depths (mean ± standard error of the mean), (* Total nutrient contents below the detection limit have not been presented in the table).
Variables *Depth (m)Land Use Types
TM SystemTACP System
Rotation 1Rotation 2Rotation 3
Na0–0.20.005 ± 0.92 Aa0.009 ± 0.69 Aab1.135 ± 0.65 Ab0.011 ± 0.65 Ab
0.2–0.40.006 ± 0.92 Aa0.007 ± 0.92 Aa0.017 ± 0.75 Aa0.012 ± 0.75 Aa
0.4–0.60.006 ± 0.92 Aa0.008 ± 0.82 Aa1.508 ± 0.75 Aa0.010 ± 0.75 Aa
0.6–1.00.008 ± 0.92 Aa0.009 ± 0.74 Aa2.259 ± 0.65 Aa0.009 ± 0.70 Aa
Mean0.006 ± 0.46 a0.008 ± 0.40 a1.229 ± 0.35 a0.011 ± 0.36 a
K0–0.20.512 ± 0.04 Aa0.453 ± 0.03 Aa0.440 ± 0.03 Aa0.466 ± 0.03 Aa
0.2–0.40.547 ± 0.04 Aa0.529 ± 0.04 Aba0.396 ± 0.03 Aba0.389 ± 0.03 Ac
0.4–0.60.571 ± 0.04 Aa0.422 ± 0.03 Ab0.378 ± 0.03 Ab0.280 ± 0.03 Bc
0.6–1.00.595 ± 0.04 Aa0.418 ± 0.03 Ab0.452 ± 0.03 Ab0.265 ± 0.03 Bc
Mean0.556 ± 0.02 a0.455 ± 0.02 b0.417 ± 0.01 b0.350 ± 0.01 c
P0–0.20.182 ± 0.01 Aa0.190 ± 0.01 Aa0.166 ± 0.01 Ab0.183 ± 0.01 ABa
0.2–0.40.166 ± 0.01 Aa0.210 ± 0.01 Ab0.160 ± 0.01 Aa0.158 ± 0.01 Ba
0.4–0.60.178 ± 0.01 Aa0.190 ± 0.01 Aa0.182 ± 0.01 Aa0.196 ± 0.01 Ba
0.6–1.00.179 ± 0.01 Aa0.207 ± 0.01 Aa0.177 ± 0.01 Aa0.207 ± 0.01 Ba
Mean0.176 ± 0.01 a0.199 ± 0.01 b0.171 ± 0.01 a0.186 ± 0.01 a
Mg0–0.20.743 ± 0.05 Aa0.682 ± 0.03 Aa0.790 ± 0.03 Aa0.479 ± 0.03 Ab
0.2–0.40.726 ± 0.05 Aa0.843 ± 0.05 Aa0.806 ± 0.04 Aa0.455 ± 0.04 Ab
0.4–0.60.655 ± 0.05 Ca0.709 ± 0.04 Aa0.668 ± 0.04 Aa0.368 ± 0.04 Ab
0.6–1.00.548 ± 0.05 Ca0.680 ± 0.04 Aa0.661 ± 0.03 Aa0.452 ± 0.04 Aab
Mean0.668 ± 0.02 a0.728 ± 0.02 a0.731 ± 0.02 a0.438 ± 0.02 b
Ca0–0.20.216 ± 0.01 Aa0.151 ± 0.01 Ab0.169 ± 0.01 Ab0.174 ± 0.01 Ab
0.2–0.40.149 ± 0.01 Ba0.176 ± 0.01 Aa0.157 ± 0.01 Aa0.191 ± 0.01 Aa
0.4–0.60.158 ± 0.01 Bab0.154 ± 0.01 Aab0.139 ± 0.01 Aa0.191 ± 0.01 Ab
0.6–1.00.188 ± 0.01 Aa0.145 ± 0.01 Ab0.147 ± 0.01 Ab0.165 ± 0.01 Aba
Mean0.178 ± 0.006 b0.156 ± 0.006 a0.153 ± 0.005 a0.180 ± 0.005 b
Al0–0.27.578 ± 0.62 ABa7.401 ± 0.468 Aa6.326 ± 0.44 Ab9.402 ± 0.44 Ac
0.2–0.46.998 ± 0.62 Aa9.405 ± 0.619 Bab5.377 ± 0.51 Aa9.533 ± 0.51 Aab
0.4–0.67.445 ± 0.62 Aa8.022 ± 0.554 ABa5.545 ± 0.51 Ab11.387 ± 0.51 Ac
0.6–1.08.873 ± 0.62 Ba8.952 ± 0.506 ABa6.349 ± 0.44 Ab10.934 ± 0.47 Aa
Mean7.723 ± 0.31 a8.445 ± 0.27 a5.899 ± 0.24 b10.314 ± 0.24 c
Fe0–0.29.639 ± 0.46 Aa7.744 ± 0.35 Ab7.426 ± 0.32 Ab9.813 ± 0.32 Aa
0.2–0.49.273 ± 0.46 Aa9.613 ± 0.46 Ba7.857 ± 0.37 Aa9.060 ± 0.37 Aa
0.4–0.69.418 ± 0.46 Aa8.376 ± 0.41 CAa8.540 ± 0.37 Aba10.335 ± 0.37 Ac
0.6–1.09.748 ± 0.46 Aab8.872 ± 0.37 CBb8.686 ± 0.32 Ab10.413 ± 0.35 Aa
Mean9.519 ± 0.23 a8.651 ± 0.20 a8.127 ± 0.17 a9.905 ± 0.18 b
Mn0–0.20.247 ± 0.02 Aa0.245 ± 0.02 Aa0.204 ± 0.02 Aa0.318 ± 0.02 Ab
0.2–0.40.240 ± 0.02 Aab0.300 ± 0.02 Ab0.225 ± 0.02 Aa0.220 ± 0.02 Ba
0.4–0.60.269 ± 0.02 ABab0.2130 ± 0.02 Aa0.292 ± 0.012 Bb0.210 ± 0.02 Ba
0.6–1.00.313 ± 0.02 Bab0.225 ± 0.02 Ab0.277 ± 0.02 CAb0.205 ± 0.02 Bab
Mean0.27 ± 0.011 a0.246 ± 0.01 a0.249 ± 0.01 a0.238 ± 0.01 a
Values followed by the same uppercase letter(s) within a column and/or lowercase letters across a row are not significantly different.
Table
Table 5. Bulk density (Bd) (g cm−3), soil organic carbon (SOC) (%), total nitrogen (TN) (%), carbon to nitrogen (C/N) ratio, available nitrate (NO3−), available phosphate (PO43−), sulfate (SO42−), available ammonium (NH4+) and nutrient content (%) (all available nutrient contents in mg kg−1 ) and total element contents (%) in soils from inside and outside charcoal production spots (CPS) in the three rotations of the TACP system. (* Total element contents below the detection limit have not been presented in the table).
Table 5. Bulk density (Bd) (g cm−3), soil organic carbon (SOC) (%), total nitrogen (TN) (%), carbon to nitrogen (C/N) ratio, available nitrate (NO3−), available phosphate (PO43−), sulfate (SO42−), available ammonium (NH4+) and nutrient content (%) (all available nutrient contents in mg kg−1 ) and total element contents (%) in soils from inside and outside charcoal production spots (CPS) in the three rotations of the TACP system. (* Total element contents below the detection limit have not been presented in the table).
TACP System
Variables *Rotation 1Rotation 2Rotation 3
Inside CPSOutside CPSInside CPSOutside CPSInside CPSOutside CPS
Bd1.06 a0.97 a1.03 b0.99 b0.96 c0.92 c
SOC, %2.88 a2.78 a1.41 b1.59 b0.82 c0.81 c
TN, %0.23 a0.23 a0.16 b0.15 b0.11 c0.12 c
CN ratio11.74 a11.01 ab7.29 b8.39 bc6.36 c6.04 c
pH4.51 a4.47 a4.66 b4.60 b4.99 c5.02 c
Available nutrient contents:
NO3−0.01 a0.00 b0.00 a0.00 a0.00 a0.00 b
SO42−0.00 a0.00 b0.00 a0.00 a0.00 a0.00 a
NH4+0.00 a0.00 a0.00 a0.00 a0.00 a0.00 a
Total element contents:
Na0.00 a0.01 a0.01 b0.01 b0.01 c0.01 c
K0.48 a0.41 a0.45 b0.38 b0.31 c0.41 c
P0.19 a0.20 a0.17 b0.17 b0.20 c0.17 d
Mg0.73 a0.70 a0.75 b0.70 b0.41 c0.48 c
Ca0.17 a0.14 a0.17 b0.14 b0.18 c0.17 c
Al8.11 a8.55 a6.14 b5.73 c11.27 c9.01 d
Fe8.35 a8.72 a8.47 b7.64 c10.49 d9.20 e
Mn0.24 a0.25 a0.25 b0.25 b0.22 c0.27 c
Values followed by the same lowercase letters across rows (in same rotation) with respect to the charcoal production spots (CPS) are not significantly different.
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Beshir, M.; Yimer, F.; Brüggemann, N.; Tadesse, M. Soil Properties of a Tef-Acacia decurrens-Charcoal Production Rotation System in Northwestern Ethiopia. Soil Syst. 2022, 6, 44. https://doi.org/10.3390/soilsystems6020044

AMA Style

Beshir M, Yimer F, Brüggemann N, Tadesse M. Soil Properties of a Tef-Acacia decurrens-Charcoal Production Rotation System in Northwestern Ethiopia. Soil Systems. 2022; 6(2):44. https://doi.org/10.3390/soilsystems6020044

Chicago/Turabian Style

Beshir, Miftha, Fantaw Yimer, Nicolas Brüggemann, and Menfese Tadesse. 2022. "Soil Properties of a Tef-Acacia decurrens-Charcoal Production Rotation System in Northwestern Ethiopia" Soil Systems 6, no. 2: 44. https://doi.org/10.3390/soilsystems6020044

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