Spatial distribution of the litter carbon stock in the Cerrado biome in Minas Gerais state, Brazil

Distribuição espacial do estoque de carbono na serrapilheira de fragmentos do bioma Cerrado em Minas Gerais, Brasil

ABSTRACT

Litter corresponds to the layer of decomposing dead organic matter present on the soil surface. This layer is very important for nutrient cycling and contributes with organic matter accumulation in the soil, besides the carbon stock. The objective herein was to quantify the carbon biomass, both content and stock, and map the litter C-stock in the Cerrado biome, which is formed by Savanna Grassland (SG), Cerrado Stricto Sensu (CE) and Forest Savanna (FS), in Minas Gerais state, southeastern Brazil. The data were collected in 26 fragments in Minas Gerais state, totaling 210 sampling locations. A variographic study was conducted and, for mapping, the ordinary kriging method was used for delimitation of homogeneous zones. It was possible to detect high variability in the carbon biomass, carbon content and C-stock in the Cerrado biome litter in Minas Gerais state. The carbon content presented lower variability, ranging from 40 to 44%, so that it is not responsible for explaining the variability of the litter C-stock. Savanna Grassland and Savanna Forest present, respectively, the lowest and highest C-stocks. C-stock presented a considerable spatial structure dependence, allowing to use the geostatistical procedures for mapping it in the Cerrado biome of the Minas Gerais state. The C-stock kriging map showed good accuracy, allowing to verify that the lowest C-stocks in the litter are found from the center to the northern of the Minas Gerais since the highest air temperatures are also verified in this direction.

Index terms:
Climate change; Kriging; mapping procedures; accumulated biomass.

RESUMO

A serrapilheira corresponde à camada de matéria morta em decomposição presente sobre o solo. Esta camada é de grande importância na ciclagem de nutrientes e aporte de matéria orgânica sobre o solo, além de estocar carbono. Objetivou-se quantificar a biomassa, teor e estoque de carbono e espacializar o estoque de C da serrapilheira do Cerrado de Minas Gerais. Os dados foram coletados em 26 fragmentos de Cerrado no Estado de MG, totalizando 335 pontos amostrados em todo estado. Foi realizado o estudo variográfico e, para o mapeamento, utilizou-se a Krigagem, para delimitação de zonas homogêneas. Foi possível detectar alta variabilidade nas características avaliadas, biomassa, teor e estoque de carbono na serrapilheira do Cerrado em Minas Gerais, Brasil. O teor de C foi a característica que apresentou menor variabilidade, com intervalo de 40-44%, de modo que não é um atributo crítico para explicar o estoque de C na serrapilheira. O Campo Cerrado tem o mais baixo estoque de C, e o Cerradão o mais alto. O estoque de C apresenta considerável dependência da estrutura espacial, permitindo o uso de procedimentos geoestatísticos para mapeá-lo no bioma Cerrado do estado de Minas Gerais. O mapa de krigagem de estoque de C mostrou boa precisão e com base nele, foi possível verificar que os estoques de menor teor de carbono na serrapulheira são encontrados do centro para o norte do estado de Minas Gerais, onde tem-se as maiores temperaturas médias anuais.

Termos para indexação:
Mudanças climáticas; Krigagem; procedimentos de mapeamento; biomassa acumulada.

INTRODUCTION

In recent decades, the increase in carbon dioxide (CO₂) concentrations in the atmosphere has contributed significantly to the threat of climate change caused by global warming. Deforestation is responsible for about 25% of annual atmospheric CO₂ emissions across the globe (Paiva; Faria, 2007). On the other hand, in Brazil, land use changes and deforestation are the main practices that contribute to soil carbon flow into the atmosphere, placing the country in fourth position, along with the United States, China and Russia, in the ranking of countries that emit the most CO₂ into the atmosphere (Matthews et al., 2014). In Minas Gerais state, which is located in southeastern Brazil, deforestation and land use changes have accounted for 54% of all greenhouse gas emissions in Brazil (Brazil, 2011).

Minas Gerais still retains about 35% of its area covered by native vegetation, from which, 62% is formed by Cerrado (Brazilian Savanna) and the other 38%, Atlantic Forest (Scolforo et al., 2016). The Cerrado occupies an area of 122147 km², considering the different physiognomic variations, and has undergone extensive anthropic pressure (Rezende et al., 2006; Rufini et al., 2010). However, in order to preserve the Cerrado, development projects have been necessary aiming making the vegetation maintenance more favorable than deforestation, which can be achieved with carbon credit trading policies. Therefore, it is essential technologies to estimate as accurate as possible the carbon stocks in forests environment and thus to develop maps for spatially estimations of it in the various existing compartments of a forest.

In this context, the geostatistical theory and its spatial interpolation capabilities (Mello et al., 2015; Scolforo et al., 2015) are the tools that allow to quantify precisely and accurately this kind variable. Such methods are widely employed in meteorological, soil attributes and hydrological studies, among others (Ahmed; Marsily 1987; Angulo-Martinez et al., 2009; Hengl; Heuvelink; Rossiter, 2007; Mello et al., 2013), with great results. Thus, it is possible to generate spatial distribution maps of the variable of interest, covering parts not sampled with interpolated information from the sampled locations taking into account the main properties of these techniques, which are minimum variance and summing of the weights equal to 1 (Isaaks; Srivastava, 1989).

One of the compartments present in plant ecosystems is the litter, which can be defined as the layer of organic matter deposited over the soil surface that remains until it is fragmented and broken down by physical-chemical and biotic processes (Aduan; Vilela; Klink, 2003). This matter comes from leaves, flowers, fruits, stems, scraps and animal fecal material (Aduan; Vilela; Klink, 2003; Bellote; Dedecek; Silva, 2008; Silva et al., 2007; Silva et al., 2009). In tropical forests, in general, litter production and its accumulation are continuous over the time (Carreira; Rondon; Zaidan, 2006), in different amounts, depending on the vegetation type which directly influence the amount of litter deposited on the ground (Silva et al., 2007; Silva et al., 2009).

The litter is a terrestrial ecosystem that is fundamental for nutrients cycling and supply carbon to the soils (Gregorich et al., 2016). Studies have demonstrated that its removal, which mostly occurs by land-use changes and burning, causes negative impacts on the soil quality properties, like soil bulk density, soil organic matter and microbiological diversity (Tanner; Sheldrake; Turner, 2016). However, an excessive accumulation of organic matter in soil surface can also promote effects in soil’s function which are not yet entirely understood by the science as reported by Leff et al. (2012); Lajtha et al. (2014a); Lajtha et al. (2014b) and Bowden et al. (2014). Both decomposition rate and burning of the litter affect the CO₂ emissions to the atmosphere, which has been increased due to the increase in observed air temperatures in Minas Gerais state in the last 50 years (Ávila et al., 2014) and, indeed, contributing directly with the global warming (Conant et al., 2011).

Carbon stocks in litter can vary greatly. Paiva et al. (2011) determined a range from 2.32 - 4.83 Mg ha^-1 for Cerrado biome in the Federal District region (Mid-West Brazil), while Morais et al. (2013a) found values ranging from 2.28 to 8.88 Mg ha^-1 for a Savanna Forest of Minas Gerais. However, the few studies available and the different methodologies used (Watzlawick et al., 2010; Froufe et al., 2011; Paiva et al., 2011; Torres et al., 2013) hinder the understanding of these stocks.

Taking in mind the importance and the natural variability of the litter in the tropical region, this study aimed to quantify and map the biomass, carbon content and C-stocks of litter on the Cerrado biome in Minas Gerais state, southeastern Brazil.

MATERIAL AND METHODS

Physiographic characterization of Minas Gerais state, Brazil

The area of Minas Gerais is 586,528 km², the altitude ranges from 50 to 2500 m, the average annual temperature varies from 14 °C in the south to 27 °C in the north, and the average annual rainfall varies from 700 mm in the north to 2000 mm in the far southern (Carvalho et al., 2008).

Minas Gerais still accounts for approximately 35% of its total area covered by native vegetation (Scolforo et al., 2016), which is split into two major biomes: the Cerrado (Brazilian Savanna) that covers 62% of this area (121821 km²) and Atlantic Forest, covering 38% (83464 km²) (Scolforo et al., 2016; Carvalho et al., 2008).

With a regularly seasonal climate, generally well-drained acid soils, mainly Oxisols, Cambisols and Quartzarenic Neosol (Curi et al., 2008), the Cerrado vegetation is described by Oliveira Filho, et al. (2006) and Scolforo et al. (2008a) as Savanna Grassland (SG) which is formed by bushes, with ground-cover around 10% of the surface; Cerrado Stricto Sensu (CE), with greater density trees and shrubs and a higher occurrence in Minas Gerais, with ground-cover ranging from 10 to 60%; and Forest Savanna (FS), with ground-cover of 80%, and with a continuous canopy formation. The woody stratum, composed of twisted trees and shrubs, varies between 1.5 m to 15 m in height. Average dry matter, volume and basal area values for each of these Phyto-physiognomies can be observed in Table 1.

Table 1:
Average values for the main biometric variables of the physiognomic types under study for the Minas Gerais state, Brazil.

Physiognomic types	N	G	Dg	H	Vol	DW	C
Savanna Grassland (SG)	370.4	3.5	11.2	4.3	17.7	10.9	5.0
Cerrado Stricto Sensu (CE)	1168.9	9.4	10.2	5.1	48.5	29.3	14.3
Forest Savanna (FS)	1626.8	18.3	12.0	7.4	128.9	64.6	35.1

• N: number of plants per hectare; G: average basal area (m²ha^-1); Dg: quadratic mean diameter (cm); H: average height of the plants (m); Vol: average volume (m³ ha^-1); DW: dry weight (Mg ha^-1); C: shoot carbon stock (Mg ha^-1). Source: Scolforo et al. (2008b).

Sampling strategy

The data sets were collected in 26 Cerrado fragments (Figure 1) that are part of the permanent plot network of the Forest Inventory of Minas Gerais state (Scolforo et al., 2008b). These fragments were selected seeking to cover ranges of temperature, altitude, rainfall pattern and physiognomic differences found in the Cerrado biome in Minas Gerais.

Figure 1:
Study area with the Cerrado fragments analyzed. (Minas Gerais state basins: DO: Doce; GD: Grande; JQ: Jequitinhonha; MU: Mucuri; PA: Pardo; PI: Piracicaba; PN: Paranaiba; PS: Paraíba do Sul; SF: San Francisco; SM: São Mateus).

In each selected fragment, sampled points were randomly selected in 30% of the plots, totaling 214 samples. However, the number of samples varied between the fragments as each one of these fragments has a different number of samples. In each sampled fragment, it was randomly selected a sample point, within a plot with wide varying from 0 to 10 m and length varying from 10 to 100 m. For the latter, the first 10 m was neglected since in this strip studies related to natural regeneration have been conducted.

At each sampled point, we collected litter samples using a 0.5 m x 1 m (0.5 m²) steel template as a reference area. The collected material was taken to laboratory and dried in an oven at 70 ^oC up to obtain a constant weight. Dry biomass (g) of each sample was quantified using a weight-machine with an accuracy of 0.01 g. Afterwards, the samples were crushed, grinded and sieved through a mesh of 0.250 mm. After that, the samples were dried again in an oven with forced air circulation at 70 ºC during 48 hours, and then, the carbon content was determined.

For carbon content determination, a “Elementar” carbon analyzer, type TOC, model Vario TOC Cube, was used, considering samples from 2 to 4 mg from the litter. The samples were packed in tin capsules and taken to an oven at 950 ºC for dry combustion. The CO₂ generated by each sample was quantified using an infrared detector, type NDIR, which relates the carbon generated with respective weight of the samples. Litter C-stocks were obtained weighting the dry biomass value by the respective content and the calculated value was extrapolated to 1 hectare, allowing to obtain the C-stock in Mg ha^-1.

Statistical analysis

Biomass, carbon content and C-stock data undergone descriptive statistical analysis, generating information on average, minimum and maximum values for each fragment, and also for all the fragments. For mapping the C stored in the litter we used geostatistical techniques such as variography study and ordinary kriging. In this methodology, the Exponential, Gaussian and Spherical models were tested by means fitting them using the geoR package of the R Core Team software (2013). After fittings, the best model was selected through cross validation, adopting the reduced average error statistics, being the closer to 0 the better the model, and the standard deviation of the reduced errors, which the closer 1 the better the model. Subsequently, the kriging map was generated in ArcGIS software (ESRI, 2004), using the previous selected spatial model.

Interpolation maps were generated in a raster format with 100 m x 100 m grid, or 10000 m² area for each pixel within the Cerrado biome. Thus, it was possible to generate of litter C-stock maps for the entire Cerrado biome in Minas Gerais state.

RESULTS AND DISCUSSION

Basic statistical analysis

The average carbon content in the Cerrado litter was 43.27% (± 2.85%), with SG and CE physiognomies presenting lower and higher C content, respectively. The coefficient of variation for carbon content was 6.6%. This low carbon variability allowed to ensure that the average carbon content of the Cerrado litter is approximately 44%.

Considering the areas covered by each one of the physiognomies presented by Carvalho et al. (2008), the FS physiognomy area in Minas Gerais state accounts for only 355.01 km² but present the greatest average C-stock (4.68 Mg C ha^-1). CE physiognomy presents an average C-stock of 3.74 Mg C ha^-1, although to occupy an area much greater than FS (5560.62 km²). SG physiognomy has an area similar CE (5374.31 km²), however, an average C-stock of 2.47 Mg C ha^-1. The average C-stock in the litter of Brazilian Cerrado biome accounts for 3.79 Mg C ha^-1, representing 48% of the variability. It is important highlight that FS physiognomy occupies only small areas in Triangulo Mineiro region (west of Minas Gerais) while CE and SG are the physiognomy predominant in the Cerrado biome within Minas Gerais state (Figure 1).

FS physiognomy presents both a greater number and large size trees which indeed has greater contribution with litter formation when compared to CE and SG physiognomies. Besides that, FS is formed by species with strong decidual characteristic during the dry season in the state (winter period), increasing the deposition of organic matter in the surface.

Table 2 contains the basic statistics of carbon biomass, carbon content and C-stock observed in the Cerrado biome litter obtained from the 26 fragments evaluated in Minas Gerais state. The average biomass value was 8.73 Mg ha^-1 (± 4.11 Mg ha^-1), and the lower and the higher average values were, respectively, found to CE (1.8 Mg ha^-1) and FS (20.04 Mg ha^-1). These finds mean that the litter biomass variability in the Cerrado biome is approximately 47.1%, which is characterized as a high variability. However, the wider of the biomass values is common observed in Brazilian Cerrado as it is formed by very different physiognomies and biometric characteristics (Table 1). This wide variation in Cerrado vegetation is a feature that implies in difficulty to understand their cycles. This characteristic is noticed when viewing the data presented in Table 2, which presents a wide range of biomass stock values and also those for the carbon content, which therefore also affects the C stock values.

Table 2:
Descriptive statistics for carbon biomass, content and stock in litter for different fragments of Cerrado in Minas Gerais state.

Fragment	Phyto- physiognomy	Number of samples	Biomass (Mg ha-1)			C Content (%)			C Stock (Mg ha-1)
			Minimum	Average	Maximum	Minimum	Average	Maximum	Minimum	Average	Maximum
13	CE	10	4.38	12.88	23.67	41.12	44.11	46.70	2.05	5.65	10.43
21	CE	10	5.06	8.34	15.79	40.68	46.46	49.59	2.22	3.90	7.68
34	CE	9	6.62	12.79	22.43	40.59	45.50	48.47	2.96	5.81	10.30
46	CE	6	2.49	7.61	17.57	38.58	42.96	46.44	1.03	3.27	8.02
47	CE	6	0.04	1.80	6.43	36.83	41.97	47.94	0.02	0.69	2.37
53	CE	6	2.47	3.62	6.35	37.01	42.51	49.13	1.04	1.51	2.35
56	SG	6	2.46	4.39	7.85	28.99	35.10	40.78	0.93	1.54	2.78
67	CE	6	2.49	6.32	10.18	41.93	44.98	48.29	1.06	2.84	4.27
70	CE	11	2.18	5.35	10.63	40.14	44.19	47.87	0.97	2.40	4.99
73	CE	5	1.46	3.77	7.39	33.66	43.89	49.67	0.49	1.69	3.38
74	CE	11	1.50	6.58	15.00	38.53	43.73	48.13	0.64	2.84	6.29
75	CE	18	4.09	9.42	20.00	33.31	41.44	49.05	1.43	3.96	9.51
84	CE	4	2.19	5.45	9.22	41.50	46.16	49.60	1.09	2.45	3.83
86	SG	17	2.35	7.60	20.24	40.42	44.79	50.40	0.99	3.39	8.18
89	CE	14	4.02	8.15	21.75	42.08	47.13	51.22	2.06	3.80	9.55
94	CE	8	3.64	15.21	26.27	47.56	49.14	51.99	1.83	7.51	13.43
96	CE	7	6.00	14.35	22.64	38.42	43.24	49.44	2.39	6.27	10.06
98	CE	5	5.63	8.07	11.97	42.85	46.70	50.05	2.47	3.77	5.39
102	FS	18	6.22	10.86	18.91	32.20	40.16	46.37	2.50	4.35	8.01
103	FS	5	2.92	5.62	12.73	37.33	40.73	42.96	1.09	2.34	5.47
104	CE	6	3.43	6.74	10.12	39.16	42.45	46.43	1.44	2.86	4.22
106	FS	5	6.15	9.29	14.05	36.43	40.91	43.91	2.61	3.79	5.68
107	FS	5	5.23	20.04	32.45	39.01	41.34	42.95	2.21	8.24	13.94
121	CE	6	5.73	10.19	16.69	36.22	41.23	46.43	2.08	4.15	6.04
122	CE	7	4.29	11.08	23.48	38.50	43.94	48.01	1.91	4.97	11.27
126	CE	4	5.72	11.37	21.39	38.85	40.34	41.72	2.31	4.54	8.31
Average			3.80	8.73	16.35	38.53	43.27	47.44	1.61	3.79	7.14
Maximum			6.62	20.04	32.45	47.56	49.14	51.99	2.96	8.24	13.94
Minimum			0.04	1.80	6.35	28.99	35.10	40.78	0.02	0.69	2.35
Standard deviation			1.78	4.11	6.87	3.76	2.85	2.91	0.76	1.82	3.28

However, it should be noted that the wide range of values, which demonstrate high variability, a characteristic also mentioned by Aduan and Vilela, Klink, (2003) and Watzlawick et al. (2012), even taken just a single fragment (Morais et al., 2013), hinders comparison with other studies. It occurs due to the both scarce and available data, even in those studies already cited, in which almost was employed different procedures for collection as well as data analysis methods (Caldeira et al., 2008; Watzlawick et al., 2012).

To decrease the amplitude, average values per vegetation type were generated (Table 3), and the values are similar to those shown in other studies (IPCC 2006; Caldeira et al., 2008; Vieira et al., 2010; Froufe et al., 2011; Paiva et al., 2011; Ribeiro et al., 2011; Watzlawick et al., 2012; Morais et al., 2013; Torres et al., 2013) for various vegetation types. The differences among the averages for physiognomies correlated with the number of trees and biomass stock, which means the higher the values of these characteristics, the higher the stocks of biomass and C in the litter. In Table 4, values of biomass, C-stock and carbon content for the litter from different physiognomies in Brazil are also presented.

Table 3:
Average values and standard deviation of carbon biomass content and C-stock in the litter of the Cerrado biome and its different physiognomies studied in Minas Gerais state.

Physiognomy	Litter
	Biomass (Mg ha-1)	C (%)	C Stock (Mg ha-1)
SG	6.00 (± 2.27)	39.95 (± 6.85)	2.47 (± 1.31)
CE	8.45 (± 3.69)	44.10 (± 2.24)	3.74 (± 1.71)
FS	11.45 (± 6.13)	40.79 (± 0.49)	4.68 (± 2.52)

Table 4:
Biomass, C-stock and C content for litter from different physiognomies in Brazil.

State	Physiognomies	Litter			Reference
		Biomass (Mg ha-1)	C-content (%)	C-stock (Mg ha-1)
DF	Cerrado	4.54 - 9.47	52.02-52.79	2.32 - 4.83	Paiva et al. (2011)
MG	Semidecidual Forest	11.57 (± 4.14)	-	5.82 (±2.10)	Torres et al. (2013)
MG	Forest Savanna	4.86 - 19.31	43.80 - 47.80	2.28 - 8.88	Morais et al. (2013)
SP	Cerrado	-	-	5.27 - 7.25	Froufe et al. (2011)
MG	Cerrado	6.32	-	-	Ribeiro et al. (2011)
SC	Ombrophilous Forest	4.47-5.28	-	-	Caldeira et al. (2008)
PR	Ombrophilous Forest	8.01 (± 1.75)	-	3.06 (± 0.69)	Watzlawick et al. (2012)
RS	Decidual Forest	19.93	-	-	Vieira et al. (2010)
Brazil	Entire Brazil	-	37	-	IPCC (2006)

• DF: “Brazilian Federal District”; MG: Minas Gerais State; SP: São Paulo State; SC: Santa Catarina State; PR: Paraná State; RS: Rio Grande do Sul State.

The range of values is given by the litter formation process, which is a complex interaction among edafo-climatic factors, source material, trees density and species composition, among others (Yang et al., 2005; Cunha; Gama Rodrigues, 2014; White et al., 2013). Wtzlawick et al. (2012) and O’Connell and Sakan (1997) related that the low level of nutrients accumulated in the litter and the soil water deficit are the factors more unfavorable to decomposition, both intrinsic characteristics of the Brazilian Cerrado biome.

Litter carbon stock mapping

After variogram analysis, it was found that was possible to fit spatial models to describe the semivariance in function of distance, meaning the existence of spatial dependence. Thus, Exponential, Gaussian and Spherical models were adjusted (Figure 2). All three models showed good fit, proving that there is a structural function, which was possible to be modeled. The parameters of the fitted models are shown in Table 5 as well as the statistical precision based on the cross-validation outputs from the three semivariogram models tested.

Figure 2:
Experimental semivariogram and the three models fitted for the Cerrado litter C stock in Minas Gerais state, Brazil.

Based on these statistics obtained from cross validation (Table 5), it was possible to choose the model with the best performance that will be used in the kriging process. We found that the Spherical model showed less reduced mean deviation and reduced standard deviation of the mean close to 1, thus, this model was used to perform the kriging map for the litter C-stock in Minas Gerais state.

Table 5:
Parameters of the geostatistical models fitted for the Cerrado litter C stock in Minas Gerais state, Brazil.

Model	τ2	σ2	τ2+σ2	Range (Km)	RMD	SD
Exponential	1.57	4.65	6.22	240	-0.0004430	1.7067
Spherical	2.54	3.81	6.35	120	0.0001743	1.3574
Gaussian	2.55	4.27	6.82	171	0.0015833	1.3738

• Nugget effect (τ2), structured variation (σ2), landing (τ2 + σ2), reduced mean deviation (RMD) and reduced standard deviation of the mean (SD).

The kriging map for litter C-stock was generated using the Spherical model parameters (Table 5) and is shown in Figure 3. The northeast and west regions of Minas Gerais showed higher values. The first presents remnants of deciduous forests and transitions for another biome, however, this region has more species that tend to lose greater amounts of leaves during the dry season, a typical characteristic situation for these vegetation types and the weather hot and dry, which require biological strategies for survival. This vegetation is highly susceptible to burning (forest fire), which is responsible for emission of approximately 4 Pg C year^-1 in the tropical and subtropical regions (27% of all over South America) (Maraseni et al., 2016). Thus, the litter has a high contribution to biomass and, consequently, to C-stock, thus, its burning represents a very high percentage of contribution for CO₂ emissions, being one of the most important environmental concern of the Minas Gerais state. The west region has Forest Savanna remnants, which correspond vegetation types with the greatest number of trees and larger trees, therefore also responsible for a high amount of biomass and number of leaves falling to the ground in the winter. In addition, there are also humid conditions more favorable for decomposition of the raw material that forms the litter (Valentine et al., 2008), which reduces the carbon concentration.

Figure 3:
Litter C-stock map for the Cerrado biome, in Minas Gerais state, Brazil.

Regions with lower C-stock (green area on the map) correspond to Savanna Grassland and Cerrado Strictu Sensu vegetation type. These are described as areas with few small trees, both in height and in crown size. Therefore, with lower leaf volume and less contribution to biomass deposited in the ground and consequently lower litter C-stock (Figure 3). However, these Cerrado species present a lower decomposition rate (Valentine et al., 2008), which favors the maintenance of C in the litter accumulated on the ground and onto the soils.

Considering the data published on the SEEG Brazil (2017), the total C stocked in the litter of Cerrado biome has been equivalent to 4.5% of the CO₂ emitted by Minas Gerais state between 1990 and 2015, thus, its adequate management is fundamental to keep this biome as a very important carbon sunk not only for the studied state but also for Brazil.

CONCLUSIONS

It was possible to detect a high variability in the characteristics evaluated, carbon biomass, content and stock in the Cerrado biome litter in Minas Gerais, state, Brazil. The carbon content was the characteristic that had the lowest variability, with a range of 40-44%, so that it is not a critical attribute to account for the litter C-stock. The Savanna Grassland has the lowest C-stock, and the Savanna Forest, the highest. C-stock presents a considerable spatial structure dependence, allowing to make use of geostatistical procedures to map it in the Cerrado biome of the Minas Gerais state. In addition, kriging C-stock map showed good accuracy, being possible to verify that the lowest litter C-stocks are found from the center to the north of Minas Gerais state since the climate is hotter in this direction.

ACKNOWLEDGEMENTS

The authors thank the coordinators of the Inventário florestal de Minas Gerais, for the availability of data used in this study. Also, to Fundação de Amparo à Pesquisa do Estado de Minas Gerais - FAPEMIG (Processo CAG - APQ-00291-11) and the Coordenação do Aperfeiçoamento de Pessoal de Nível Superior - CAPES, for granting the Doctoral scholarship to the 1st author. Special thanks to the entire team of students and trainees of UFLA/DCF/LEMAF and other professionals in the field and in the lab, who contributed to sample collection and generation of data used in this study.

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Publication Dates

• Publication in this collection
  Sep-Oct 2017

History

• Received
  14 Mar 2017
• Accepted
  19 June 2017