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Revista Cubana de Ciencias Forestales

versión On-line ISSN 2310-3469

Rev cubana ciencias forestales vol.8 no.3 Pinar del Río sept.-dic. 2020  Epub 05-Sep-2020

 

Original article

Arboreal biomass and economic carbon valuation of the Cerro Tres Puntas of Pilasca (Salas-Motupe, Lambayeque, Peru)

Guillermo Eduardo Delgado Paredes1  * 
http://orcid.org/0000-0001-5769-8209

Felipe Zuñe Da Silva1 
http://orcid.org/0000-0001-5810-9031

Cecilia del Carmen Vásquez Diaz1 
http://orcid.org/0000-0002-3229-5048

Boris Esquerre Ibañez1 
http://orcid.org/0000-0003-2283-8106

Jorge Antonio Fuluy Chung1 
http://orcid.org/0000-0003-2007-1490

Consuelo Rojas Idrogo1 
http://orcid.org/0000-0003-3525-6711

1Universidad Nacional Pedro Ruiz Gallo. Perú.

Abstract

The work was developed in the Cerro Tres Puntas de Pilasca, in the district of Salas-Motupe, Lambayeque region, Perú. The objective of the study was to determine its tree biomass, accumulated carbon and economic valuation. For this purpose, four linear transects were established covering 11.4 ha of the total 2,975 ha of the study area. In each transect were evaluated the height and diameter (1.30 cm above the ground) ≥ 5.0 cm of all tree individuals. Also, botanical collections were made for their identification. 410 individuals were registered, comprised of 17 species, 17 genera and 10 families. The estimated biomass in the four transects gave an average of 796.62 t ha-1, which transformed into tons of carbon gave 1 460.6 t CO2 ha-1, meaning an economic valuation of 28 963.70 USD per ha. The families that contribute more biomass to the Cerro Tres Puntas de Pilasca were Moraceae and Lauraceae, with 8 457.95 t ha-1 and 5 738.79 t ha-1 respectively, while in the rest of the families the biomass was less than 1 000 t ha-1. Cerro Tres Puntas de Pilasca proved to be an important forest with high biomass values for the region of Lambayeque.

Keywords: Aerial biomass; Tropical dry forest; Carbon sequestration; Native tree species; Perú.

Introduction

The greatest threat of our times that confronts humanity and that involves and compromises all its actors is global warming, verified by the increase of the atmospheric temperature due to the great emissions of Greenhouse Gases (GHG) such as carbon dioxide (CO2) - the most important due to the amounts that are emitted -, methane (NH4), nitrogen oxides (NOx) and chlorofluorocarbons (CFC). In this sense, tropical forests play an indispensable role in the global terrestrial carbon cycle (Houghton, 2005), having quantitatively significant carbon reservoirs, stored in the form of biomass (Pan et al., 2011; Feldpausch et al., 2012; Poorter et al., 2016). However, such extensions threaten a steady reduction in areas due to intense deforestation, habitat fragmentation and land use changes (Song et al., 2018).

Among terrestrial ecosystems, forest systems are particularly remarkable, since their arboreal articulation retains large amounts of atmospheric carbon, compared to other types of vegetation (Albritton and Dokken, 2001). Therefore, one of the most important processes in the forest balance stands out, the carbon cycle (C), a chemical element and the main formator of biological matter. The carbon cycle consists of several stages, ranging from its absorption by plants to its transformation into biomass (Brown, 1997). It is estimated that tropical trees absorb ~72 Pg C from the atmosphere per year (Beer et al., 2010). In addition, it is estimated that the carbon stock of tropical forests exceeds 370 Pg C (Pan et al., 2011). These carbon sinks represent an intense flow of continuous mitigation of one of the most important greenhouse gases. It should be noted that tropical forests are subject to global appreciation for the services they provide to mitigate GHG concentrations. In this sense, the reduction of GHG emissions and the reduction of global temperature are patterns of global interest. However, estimating the size of carbon resources over time is an arduous and almost impossible task, even when considering a set of complex variables and interactions of different elements of an ecosystem (Mitchard, 2018). Other studies on carbon capture and storage have been conducted in various ecological environments in Latin America, although not precisely in seasonally dry tropical forests. Such is the case of a destructive sampling carried out in Granma, in the Sierra Maestra of Cuba (Toirac et al., 2018).

Among Peruvian's impressive biomes is one of the world's most fragile and threatened ecosystems, the Tropical Seasonal Dry Forest (TDS) (Apgaua et al., 2014). In the ecological context of biomass and carbon studies, the seasonally dry tropical forests of the Lambayeque region have little information available, because the vast majority of studies are in the private sector. However, a relevant study reported that in the various types of dry forests located in the hamlet of El Choloque (Tongorrape, Motupe, Lambayeque), in nine circular plots of 30 m radius, within an area of 159.3 ha, the capture and storage of C, as a mitigation against climate change, was analyzed in the species Bursera graveolens, Loxopterygium huasango, Prosopis limensis and Parkinsonia praecox, obtaining a potential of capture of C by primary biomass (foliage and leaf litter) of 0.52 t C ha-1, a potential of storage of C at the level of the aerial biomass (major branches and shaft) of 4.23 t C ha-1 in a forest with an average age of 25 years and in the soil of 42.19 t C ha-1(Chávez, 2018).

Considering that there are still gaps in the estimation of biomass and carbon accumulation, as well as their valuation in the dry forests of the Lambayeque region, the objective of this research was to determine these elements in the Cerro Tres Puntas de Pilasca, Salas, Lambayeque region (Perú), as a real contribution of the seasonally dry tropical forests of the Lambayeque region.

Materials and methods

Study area

The study area was located in the Pilasca farmhouse, 5 km from the district of Salas, in the province and region of Lambayeque, Peru (Figure 1), at the coordinates 6°14'16,23"; S 79°35'34,81" W and 6°12'46,46" S; 79°33'59,58" W, comprising In addition, the Cerros Tierra Blanca and Gato, which belong to the Salas district and the Cerro Tres Puntas , which belongs to the Motupe district, covering an extension of approximately 2,975 hectares, with an elevation between 1,545 and 1,986 meters above sea level. The area corresponds to a very rough and dangerous topography, with enormous rocks and deep, dry ravines and scarce rocky clearings where primitive and subsistence agriculture thrives, predominating medium and large sized trees and shrubs no higher than 5 m high, as well as a very varied herbaceous vegetation.

Fig. 1. - Map of the Lambayeque region (Perú) 

Sample collection and processing

The field work was carried out between the months of March and June 2018. Due to the difficult accessibility and dangerousness of the terrain, the Gentry woody plant sampling method (1995) was used, with adaptations for the study area. Four sampling units (line transects) were established in the field, covering 11.4 ha, as indicated in the work of Delgado-Paredes et al., (2020). In each transect, the height and diameter (1.30 cm from the ground) ≥ 5,0 cm of all tree individuals were recorded. Likewise, botanical collections were made for their subsequent identification. botanical samples were identified from physical-virtual literature, consultations to specialists and visits to herbaria. All families were classified according to APG IV (APG, 2016). Finally, they were deposited in the Pedro Ruiz Gallo Herbarium (HPRG).

Data analysis

To facilitate the logical-structural interpretation of the study, the arboreal individuals were classified according to their dendrometry and botanical identification. The biomass calculation was estimated from the allometric ratio for tropical trees, as a function of diameter, height and wood density. For the calculation, it was used the formula of Chave et al. (2014): B = 0.0673*(De*((Di)^2)*A)^0.976; Where,B = Biomass (t ha-1), De = Density (g cm3), Diameter (cm), A = Height (m). For the density of each tree the database present in The World Agroforestry Centre (ICRAF) was used. When no data were obtained at the species level, results were used at the genus or family level. When no data were obtained, a global average of 0.62 g cm3 was used. Finally, average estimates of biomass by family were compared and correlated with altitude, the latter from linear regression, choosing as confidence parameters the r-square (R2) and significance less than 5%. All the calculations, analysis and graphs were made through the statistical environment R 3.6.3 (R Core Team, 2020).

For the valuation calculation, the carbon conversion from the total biomass obtained was used, using Brown and Lugo's (1992) formula: C=B*0.5, where C = Carbon (t C ha-1) and B = Biomass (t ha-1). Subsequently, to define the value of carbon, the formula described by the IPCC (2003) and Mogas and Riera (2005) was used, where one ton of C is equal to 3,667 tons of CO2 and was adjusted to the value proposed by the Electronic System for Negotiating Carbon Dioxide Emission Rights (SENDECO2, 2017) and the Banco de la Nación del Perú (BN) as of December 2018, where one ton of CO2 is equivalent to US$19.83 per hectare.

Results and discussion

There were 410 individuals recorded, comprised of 17 species, 17 genera and 10 families. Table 1 shows the relationship of arboreal species registered in the four transects evaluated in the seasonally dry forest of Cerro Tres Puntas (Salas-Motupe, Lambayeque, Peru), highlighting the Fabaceae family with the highest number of species (Table 1).

Table 1 - Arboreal species present in the evaluated area of the Cerro Tres Puntas seasonally dry tropical forest species present in the evaluated area of the Cerro Tres Puntas seasonally dry tropical forest (Salas-Motupe, Lambayeque, Perú) 

No Family Species Common name No indiv.
1 Anacardiaceae Loxopterygium huasango Spruce ex Endl. hualtaco 20
2 Boraginaceae Cordia lutea Lam. overo 29
3 Burseraceae Bursera graveolens (Kunth) Tr. & Pl. palo santo 4
4 Fabaceae Albizia multiflora (Kunth) Barneby & J.W. Grimes angolo 8
5 - Caesalpinia glabrata Kunth charán 5
6 - Erythrina smithiana Krukoff frejolillo 32
7 - Pithecellobium excelsum (Kunth) Mart. chaquiro 21
8 - Prosopis limensis Benth. algarrobo 9
9 - Senna atomaria (L.) Irwing & Barneby chapa 15
10 - Vachellia macracantha (Willd.) Seigler & Ebinger faique 154
11 Lauraceae Beilschmiedia sulcata (Ruiz & Pav.) Kostern palta de zorro 1
12 Malvaceae Eriotheca ruizii (K. Schum.) A. Robins pasayo 6
13 Guazuma ulmifolia Lam. guazumo 11
14 Moraceae Ficus obtusifolia Kunth higuerón 17
15 Olacaceae Ximenia americana L. ciruelillo 17
16 Sapindaceae Sapindus saponaria L. choloque 6
17 Ulmaceae Celtis iguanaea (Jacq.) Sarg. palo blanco 55

In the diameter classification, individuals with minimum diameters of 5.0 and maximum of 219.9 cm were recorded, resulting in the diameter class of 10 to 19.9 cm with the largest number of individuals (128) (Figure 2), while in the analysis of the altimetric class, up to 39.9 m in height were recorded, resulting in the altimetric class of 5 to 9.9 m with the largest number of individuals (205) (Figure 3).

Fig. 2. - Diameter structure of arboreal vegetation in the evaluated area of the Cerro Tres Puntas seasonally dry tropical forest (Salas-Motupe, Lambayeque, Perú) 

Fig. 3. - Altimetric structure of arboreal vegetation in the evaluated area of the Cerro Tres Puntas seasonally dry tropical forest (Salas-Motupe, Lambayeque, Perú) 

The estimated biomass for the four transects evaluated in the Cerro Tres Puntas seasonally dry tropical forest yielded an average of 796.62 t ha-1, where the lowest values corresponded to transects one and two with S 288 t ha-1, increasing in transect three up to 428 t ha-1, while in transect four the increase was up to more than five times with 2 182.11 t ha-1(Figure 4). It was also observed a trend in the increase of biomass at the same time that the altitude increased. However, no significance was found for the relationship (R2= 0.48; P=0.29) (Figure 4). Likewise, it could be seen that the families that contribute the most biomass to the Cerro Tres Puntas de Pilasca were Moraceae and Lauraceae, with 8,457.95 t ha-1 and 5,738.79 t ha-1, respectively, while in the rest of the families the biomass was less than 1,000 t ha-1(Table 2), even though these values usually vary with the number of species and individuals sampled.

Fig. 4 - Biomass (t ha-1) of arboreal vegetation and its relationship to altitudinal levels in the evaluated area of the Cerro Tres Puntas seasonally dry tropical forest (Salas-Motupe, Lambayeque, Perú). T= transect 

Table 2 - Biomass (t ha-1) of arboreal vegetation and its relationship with altitudinal levels in the evaluated area of Cerro Tres Puntas seasonally dry tropical forest (Salas-Motupe, Lambayeque, Perú) 

Families N° Individuals Biomass (t ha-1)
Anacardiaceae 20 502,82
Boraginaceae 29 23,13
Burseraceae 4 103,8
Fabaceae 244 177,42
Malvaceae 17 338,88
Moraceae 17 8 457,95
Olacaceae 17 58,23
Lauraceae 1 5 738,79
Sapindaceae 6 150,94
Ulmaceae 55 997,84

Undoubtedly, these individuals, still preserved at all costs by the Pilasca community, are the most important chronological reference in the forest. In the estimation of total accumulated biomass in community forests in the Frailesca region of Chiapas, Mexico, it was demonstrated that this was in relation to the age of the tree, since older individuals such as the Pinus maximinoii, from 40 to 100 years and Quercus rugosa, from 20 to 70 years, stored 158 and 117 Mg ha-1, respectively, while younger individuals such as Quercus robur, from 20 to 40 years, stored only 5.9 Mg h-1 of carbon, (Rodríguez-Larramendi et al., 2016). This close relationship between normalized diameter (m), tree age and photosynthetic processes that lead to biomass accumulation and carbon sequestration in different forest species has been observed in other species such as Gliricidia sepium and Leucaena leucocephala, in silvopastoral systems (Gómez-Castro et al., 2010), where atmospheric carbon sequestration increased with age.

These kinds of studies, in the seasonally dry tropical forests of Perú and especially in the seasonally dry tropical forests of northern Perú and even more so in the Lambayeque region, are almost non-existent. In a forest of Tongorrape, Motupe (Lambayeque), with an average age of 25 years, where the species Bursera graveolens, Loxopterygium huasango, Prosopis limensis and Parkinsonia praecox were evaluated, with diameter > 5.0 cm, the potential of carbon capture by primary biomass (foliage and leaf litter) was 0.52 t C ha-1, to which was added the aerial biomass (major branches and shaft) of 4.23 t C ha-1, in the lapse of five months (Chávez, 2018); Figures that only allow a slight comparison with the results obtained in the study presented, carried out in the Cerro Tres Puntas.

Regarding the economic valuation of the Cerro Tres Puntas seasonally dry tropical forest, determined from the transformation of tons of biomass into tons of carbon, from 796.62 t ha-1 of biomass was obtained 398.31 t C ha-1. Likewise, it was found that there are 1 460.6 t CO2 ha-1, which when multiplied by the value of CO2 in December 2018, according to SENDECO2 and the Banco de la Nación del Perú was 28 963.70 USD per hectare.

Conclusions

The study of the arboreal biomass, accumulated carbon and economic valuation of the BTES, Cerro Tres Puntas de Pilasca (Salas-Motupe), of the Lambayeque region, determined an average of 796.62 t ha-1, identifying the species Ficus obtusifolia (Moraceae) and Beilschmiedia sulcata (Lauraceae) as the ones with the highest biomass with 8 457.95 t ha-1 and 5 738.79 t ha-1, respectively, as well as the transformation of tons of carbon that reached 1 460.6 t CO2 ha-1, meaning an economic valuation of 28 963.70 USD ha.

Acknowledgements

The authors would like to thank Dr. Ernesto Hashimoto Moncayo, Vice-Rector of Research at the Universidad Nacional Pedro Ruiz Gallo (Lambayeque) and the administrative officers Héctor Valdiviezo Castillo and Melissa Saldarriaga Heros, for the facilities that made the execution of the study possible. Also, to the community members of Pilasca, Froilán Sánchez and Isabel Valencia, for their guide services in the numerous ascents to the Cerro Tres Puntas.

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Received: June 07, 2020; Accepted: September 30, 2020

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