SlideShare ist ein Scribd-Unternehmen logo
1 von 72
Downloaden Sie, um offline zu lesen
Vol. 41, No. 3, July-September 2018 / NRS 0099
ISSN 0864-0394 (printed version) / ISSN 2078-8452 (online version)
Quarterly journal. Official organ of the Ministry of Higher Education for pastures and forages | 1978
MISSION: to disseminate research results,
development of technologies and innovation,
related to the farming sector.
EDITORIAL POLICY: publication designed
for national and foreign researchers, professors
of universities and institutes of technical educa-
tion, farming entrepreneurs, organizations that
promote rural development, decision-makers
linked to the farming sector, livestock farmers
and producers.
Thejournalpublishesscientificpapers(research
papers, review papers, short communications,
technical notes, case studies, opinions and re-
flections) which contribute to the knowledge of
agricultural sciences and territorial rural deve-
lopment.
The publication of the contributions will depend
on the approval of the Editorial Board, which
will be supported on the opinion of the Scienti-
fic Committee. The revision of the papers inclu-
des a previous editorial evaluation, in which the
following aspects are reviewed: 1) fulfillment of
thejournalguidelines;2)novelty;3)qualityofthe
title, abstract, keywords and references; as well
as an academic evaluation made according to the
double-blind peer-review system, to guarantee
theimpartialityoftheprocess.
Asgeneralrule,nomorethansixauthorsshould
appear.Onlythosewhoparticipatedinsufficient
degreetoassumethepublicresponsibilityofthe
contentofthepaper,whocededthecontribution
for its editorial reproduction, will be considered
as authors. They are responsible for the results,
criteria and opinions that appear in the papers.
All contributions can be copied, used, disse-
minated and publicly exposed, as long as the
authorship and original source of their publi-
cation (journal, editorial) are cited and they
are not used for commercial purposes.
TOPICS
•	Introduction, evaluation and dissemination of
plant genetic resources related to the farming
sector.
•	Agroecological management of production
systems.
•	Sustainable livestock production.
•	Conservation of forages and agroindustrial
byproducts for animal feeding.
•	Agroforestry for animal and agricultural
production.
•	Integrated food and energy production
systems in rural areas.
•	Utilization of alternative medicine in tropical
farming systems.
•	Adaptation to and mitigation of the climate
change in farming ecosystems.
•	Economic, managerial and social aspects of
farming production.
•	Extension, agricultural innovation and
technology transference.
•	Rural and local development.
ESTACIÓN EXPERIMENTAL DE PASTOS Y FORRAJES INDIO HATUEY
EDITORIAL COUNCIL
Editor-in-Chief | Dra. Tania Sánchez Santana
Assistant Editor | M.Sc. Nayda Armengol López
Editor-Agricultural Sciences | Dra. Marta Hernández Chávez
Editor-Veterinary Sciences | Dr. Javier Arece García
EDITORIAL COMMITTEE
Dr.C. Jesús Suárez Hernández	 | Dra.C. Maybe Campos Gómez
Dra.C. Marlen Navarro Boulandier 	 | Dra.C. Maykelis Díaz Solares	
Dr.C. Jesús M. Iglesias Gómez	 | Dr.C. Hilda B. Wencomo Cárdenas
Dr.C. Anesio R. Mesa Sardiñas	 | Dr.C. Luis A. Hernández Olivera
Dra.C. Hilda C. Machado Martínez | Dr.C. Osmel Alonso Amaro
Dr.C. Giraldo J. Martín Martín	 | Dra.C. Odalys C. Toral Pérez
Dr.C. Luis Lamela López 	 | M.Sc. Onel López Vigoa
Dra.C. Mildrey Soca Pérez	 | M.Sc. Milagros de la C. Milera Rodríguez
Dr.C. Félix Ojeda García	 | M.Sc. Yolai Noda Leyva
Dr.C. Gertrudis Pentón Fernández	 | M.Sc. Juan C. Lezcano Fleires
SCIENTIFIC COMMITTEE
Dra. Sonia Jardines González | Universidad de Matanzas, Cuba
Dra. Angela Borroto Pérez | UNIVERSIDAD DE CIEGO DE ÁVILA, Cuba
Dr. Aníbal E. Fernández Mayer | Instituto Nacional de Tecnología
Agropecuaria, Argentina
Dr. Argemiro Sanavria | Universidad Federal Rural de Rio de Janeiro, Brasil
Dr. Tyrone J. Clavero Cepeda | Universidad de Zulia, Venezuela
Dr. José M. Palma García | Universidad de Colima, México
Dr. Oscar Romero Cruz | Universidad de Granma, Cuba
Dr. Carlos J. Bécquer Granados | Estación Experimental de Pastos y Forrajes
de Sancti SpÍritus, Cuba
Dr. Rodobaldo Ortíz Pérez | Instituto NACIONAL de Ciencias agrícolas, CUBA
Dr. Pedro C. Martín Méndez | Instituto de Ciencia Animal, Cuba
Dr. Pedro P. del Pozo Rodríguez | Universidad Agraria de La Habana, Cuba
Dr. Redimio Pedraza Olivera | Universidad de Camagüey, Cuba
Dr. Rafael S. Herrera García | Instituto de Ciencia Animal, Cuba
Dr. Pedro José González Cañizares | Instituto Nacional de ciencias agrícolas, CUBA
Dr. Ángel Arturo Santana Pérez | Universidad de Granma, Cuba
SUPPORT COMMITTEE
Editing and correction
M.Sc. Alicia Ojeda González
Design and editing
Dailys Rubido González
Miresleidys Rodríguez Rizo
Translation	
B.A. Nidia Amador Domínguez
Cover design
B.A. Israel de Jesús Zaldívar Pedroso
Vol. 41, No. 3, July-September / 2018
Revista Trimestral. Órgano oficial del Ministerio de Educación Superior para el área de los pastos y forrajes
Quarterly journal. Official organ of the Ministry of Higher Education for pastures and forages
PASTURE AND FORAGE
RESEARCH STATION
INDIO HATUEY
INDEX
SciELO
SciELO Citation Index Web of Science
Electronic Journals Index (SJSU)
REDALYC
CAB Abstracts
AGRIS (FAO)
PERIODICA (México)
BIBLAT (México)
Open Science Directory
REGISTER
DOAJ
Fuente académica de EBSCO
LATINDEX
Cubaciencia
Actualidad Iberoamericana (Chile)
PERI (Brasil)
TROPAG (Holanda)
ORTON (Costa Rica)
BAC (Colombia)
AGROSI (México)
EMBRAPA (Brasil)
Forrajes Tropicales (CIAT)
Ulrich’s International
Periodicals Directory
Catálogo de Publicaciones
Seriadas Cubanas
Catálogo colectivo COPAC(ReinoUnido)
Catálogo colectivo SUDOC (Francia)
Catálogo colectivo ZDB (Alemania)
Papers to be considered by the
editorial committee, please contact:
Dra.C. Tania Sánchez Santana /
tania@ihatuey.cu
© 2018. Estación Experimental
de Pastos y Forrajes Indio Hatuey
Central España Republicana,
CP 44280, Matanzas, Cuba
 (53) (45) 571225 / 571235
http://www.ihatuey.cu
Online
http: //payfo.ihatuey.cu
http: //scielo.sld.cu
CONTENT
| REVIEW paper |
Economic appraisal of the environment and its application in the Cuban
animal husbandry sector
NadiaBáez-Quiñones...................................................................................................149
| scientific paper |
Selection of accessions of Urochloa brizantha (Hochst. ex A. Rich.) R. D.
Webster for acid soils
Yuseika Olivera-Castro, Onel López-Vigoa, Pedro Pablo del Pozo-Rodríguez,
Lisset Castañeda-Pimienta, Agustín Olmedo-Juárez, Javier Arece-García
and Rolando Rojo-Rubio..................................................................................158
| scientific paper |
Selection of local resources for sheep feeding in the Las Tunas municipality,
Cuba
Javier Antonio Herrera-Toscano and Oscar Carmenate-Figueredo.......................164
| scientific paper |
Influence of EcoMic®
and Pectimorf®
on the establishment of Leucaena
leucocephala (Lam.) de Wit. cv. Cunningham
Maritza Rizo-Alvarez, Dariel Morales-Querol, Tania Sánchez-Santana, Onel
López-Vigoa, Yuseika Olivera-Castro, Miguel A. Benítez-Alvarez and
Fernando Ruz-Suárez.......................................................................................170
| scientific paper |
Inoculation of Canavalia ensiformis with arbuscular mycorrhizal fungi
in the establishment stage
Lázaro J. Ojeda-Quintana, Pedro J. González-Cañizares, Ramón Rivera-Espinosa,
Eduardo Furrazola-Gómez, Juan J de la Rosa-Capote, Martha E. Hernández-
Vilches, Yudeimy I. Rodríguez-González and Consuelo Hernández-
Rodríguez...........................................................................................................175
| scientific paper |
Productivity of Tifton 85 bermudagrass, inoculated with Bradyrhizobium sp.
and Trichoderma harzianum, subject to agricultural drought stress
Carlos José Bécquer-Granados, Urbano Ávila-Cordoví, José Ángel Nápoles-Gómez,
Yaldreisy Galdo-Rodríguez, María Hernández-Obregón, Ivón Muir-Rodríguez,
Orquidia Álvarez-Figueroa and Fernando Medinilla-Nápoles.........................182
| scientific paper |
Resistance to penetration in a Chromic Vertisol with natural pasture
Juan Alejandro Villazón-Gómez, George Martín-Gutiérrez, Yakelín Cobo-Vidal
and Daniel Hernández-Rojas...........................................................................188
| scientific paper |
Evaluation of the structure, functioning and performance of mixed
agriculture-animal farming agrosystems
Katia Bover-Felices, Eliel González-García, Fabien Stark, Charles-Henri Moulin
and Jesús Suárez Hernández..........................................................................193
| scientific paper |
Animal husbandry-forestry integration as alternative for family agriculture
in a region of Uruguay
Liber Manuel Acosta-Casella, Virginia Courdin-Máximo and Pedro Raúl
Arbeletche-Favat...............................................................................................203
| scientific paper |
Effect of different proportions of Moringa oleifera:Cenchrus purpureus
on voluntary intake and nitrogen balance
Delfín Gutiérrez-González, Nelson N. González-González, Arabel Elías-Iglesias,
Roberto García-López and Osvaldo R. Tuero-Martínez.............................211
Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Economic appraisal of the environment	149
Economic appraisal of the environment and its application in the Cuban
animal husbandry sector
Nadia Báez-Quiñones
Instituto de Ciencia Animal, Apartado postal 24, San José de las Lajas, Mayabeque, Cuba
E-mail: nadia@ica.co.cu
Abstract
The objective of this paper is to present the environmental economic appraisal methods and their application
in the Cuban animal husbandry sector. For such purpose the Total Economic Value theory is taken as reference, and
the most widely used methods and techniques are identified according to the adopted concept of value. A group of
studies about the application of the environmental economic in Cuba is reviewed, and four cases of interest in the
animal husbandry sector are analyzed. The topic of the application of the environmental economic appraisal in the
animal husbandry sector is not very frequent in scientific literature. This is only limited to determining the main
environmental functions and the magnitude of their impact, but their economic value is not taken into consideration.
It is concluded that the Total Economic Value theory is one of the most widely used for the economic appraisal of the
environment. In addition, there are diverse highly useful techniques for economically appraising the environmental
impact of animal husbandry in Cuba.
Keywords: animal husbandry, environmental impact, economic viability
Review paper
Introduction
Some of the main environmental problems that
exist in Cuba are: soil degradation and deforesta-
tion; loss of biodiversity; contamination; as well
as the deficiencies and difficulties regarding manage-
ment, water availability and quality, and their im-
pacts on climate change (CITMA, 2016). These
problems have incidence on the agricultural sector
and are often caused by it; in which the excessive
exploitation of animal husbandry systems plays an
important role.
Animal production significantly contributes
to the emissions of greenhouse gases (GHG). The
main emission sources in the sector are enteric
fermentation, manure management and deposit of
feces and urine in the pasturelands (Wilkes et al.,
2017).
In most cases, the environmental problems, or
the benefits generated by ecosystems, are not con-
sidered in economic accountancy systems (Biondi,
2016). This constitutes one of the main causes of
the increasing overexploitation and deterioration of
natural resources (Miranda et al., 2007).
For such reason, Miranda (2002) stated that,
when a new technology is going to be incorporated,
the costs that, at long term, can be generated by
the environmental deterioration caused by the
assimilation of a new technology, should be taken
into consideration, and not only the investment
costs and their recovery period.
In recent years, in Cuba there has been pro-
gressive advance in the economic appraisal of
the environment, mainly in protected areas and
in the tourism and forestry sectors (Machín and
Hernández, 2009; Hernández, 2011; Rodríguez et
al., 2011; Domínguez-Junco et al., 2012; Labrada,
2013; Poey and García 2013; Zequeira et al., 2013;
Rodríguez-Córdova et al., 2017). This proves the
need and importance of the use of economic ap-
praisal, so that it allows the practice of effective and
economically efficient policies for the sustainable
management of species and ecosystems (Machín
and Casas, 2006).
The objective of this paper is to present the en-
vironmental economic appraisal methods and their
application in the Cuban animal husbandry sector.
Economic appraisal of the environment and
Total Economic Value (TEV)
The relation between growth and environment
has gained great strength for economics researchers
in recent years, mainly because of the increasing
degradation of natural resources –which accompa-
nies the increase of production at world scale– and
to the need of quantifying the elements that com-
pose ecosystems (Figueroa, 2013).
150 	 Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Nadia Báez-Quiñones
Although some natural resources have a price
in the market, it does not contemplate, in most cases,
the wide variety of functions that add a higher
economic value, generally disesteemed when
making decisions related to their management.
This value lies on the fact that natural resources
and the environment fulfill at least four functions,
positively perceived by society (Rangel et al., 2013).
They are:
•	 they are part of the function of production of a
large quantity of economic goods and services;
•	 they perform environmental functions, whose
services are demanded by society;
•	 they act as receptors of diverse types of residues
and wastes;
•	 they constitute an integrated system that provi-
des the elemental means to sustain all kinds of
life.
The environmental economic appraisal consti-
tutes an important tool for the adequate definition
of the instruments of environmental policy. It can
be defined as a set of techniques and methods which
allow to measure the expectations of benefits and
costs derived from actions, such as the use of an
environmental asset, the performance of an envi-
ronmental improvement or the generation of envi-
ronmental damage (Azqueta, 1994).
In the last decades, the environmental appraisal
methodologies have had a broad development in the
measurement of those aspects that were previous-
ly classified as intangible and which at present can
be measured in monetary terms (Hernández et al.,
2013).
The economic value of environmental goods
and services is a very controversial topic in
literature. Cerda (2003) states that it is important to
emphasize that neither «the environment» nor «the
life» are being appraised, as many people assume,
but that the preference of people in the face of
changes in the conditions of the environment and
with regards to changes in the risks they face are
appraised. In this sense, Hernández et al. (2010)
suggested that economists should appreciate the
value of ecosystems far beyond their contribution
in raw materials and tangible products. From these
ideas, the Total Economic Value (TEV) theory is
proposed, which has been used by such authors
as Ferro et al. (2016) and Almeida et al. (2018),
as the approach to be taken into consideration for
determining the economic value of an ecosystem.
The TEV approach states that any good or
service is composed by several attributes, some of
which are tangible and easily measurable, while
others can be more difficult to quantify. However,
the total value is the sum of all these components
and not only of those that can be easily measured.
The limits and terminology for the TEV components
slightly vary between one specialist and the other,
but it generally includes value of use and value of
non-use (Dixon and Pagiola, 1998). Besides, each
one can be subdivided into additional categories
(table 1).
The value of use is formed by the value of direct
use, which refers to the resource that is obtained
by the development of certain activity; the value
of indirect use, including those benefits that are
derived from the functioning of ecosystems; and
the value of choice, which refers to the possibility
of using, or not, the environmental resource in the
future. On the other hand, the value of non-use is
subdivided into legacy value and existence value.
The former refers to the possibility that the resource
be consumed by future generations, and the latter,
to the knowledge of the existence of a certain
environmental asset; which, although due to moral
conviction, seems valuable (Ferro et al., 2016).
Table 1. Categories of the economic value ascribable to natural resources.
Value of use Value of non-use
Direct use Indirect use Choice value Legacy value Existence value
Directly consumable
values
Benefits derived
from ecosystem
functions
Future direct
and indirect
values
Value of the resources
for future generations
Value of knowing
that there still is an
environment component
Milk, meat, biomass,
recreation, health
Control of: climate,
soils, nutrient
recycling
Bioprospection,
conservation of
habitats
Conservation of
habitats in the face of
irreversible changes
Habitat, species, genes,
ecosystems
Source: modified from Pearce and Morán (1994).
Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / economic appraisal of the environment 151
Summarizing, the TeV theory is one of the
most used in scientific literature, because it allows
to appraise the environmental goods and services
taking into consideration the highest possible quan-
tity of the values they have. Thus, a monetary value
is assigned to such resources, which, in spite of not
being their real value, offers the possibility of in-
cluding them in the accountancy systems at the dif-
ferent levels. Nevertheless, it is criticized by some
experts due to its subjective character, because the
assignation of values depends, to a large extent, on
the specialist’s point of view.
Most utilized methods and techniques for the
economic appraisal of the environment
environmental appraisal techniques intend to
obtain the willingness to pay for a positive change
in an environmental good or the willingness to
accept a compensation for a negative change. The
environmental economy is focused on two basic
areas: the field of appraisal (impact and environ-
mental cost studies), for which it uses a series of
instruments and methodologies such as benefit/
cost studies, contingent appraisal and disposition to
pay, among others; and the field of environmental
policy and management, in which it proposes di-
verse instruments of environmental fiscal policy,
constitution of secondary markets, environmental
policies and management (Raffo, 2015). It should
be clarified that this review adopts the position of
environmental economy, emphasis is not made on
the precepts of ecological economy1
.
The different values that are assigned to en-
vironmental goods and services can be excluding,
alternate or competitive, for which it is not always
possible to consider that the total economic value
associated with an environmental good or service
is the simple sum of the different values of use and
non-use (Leal, 2005). In this regard, there are di-
verse appraisal methods and techniques, which are
classified according to the concept of value that is
adopted or the level of availability of the required
information. The most common classifications
in literature are: methods of declared preferences
or revealed preferences (Maldonado and Cuervo,
2016); and direct or indirect methods (Pardo and
Sanjinés, 2014). The most utilized techniques ac-
cording to the concept of value are shown in figure 1,
and are explained below.
1
It considers economy as a subsystem of the ecosphere, and assumes that mankind and its economy must be subject to the limits
imposed by the biophysical restrictions set by ecosystems, source of the goods and services that feed them (Goodland and Daly, 1996).
152 	 Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Nadia Báez-Quiñones
•	 Direct market values or available market prices.
This technique is used in economies where there
are well defined markets, in which the practice
is followed of assigning a monetary value to
the biological resource in question, under the
assumption that such price reasonably describes
the value it has, being understood that such
concept goes beyond being only value of use
(Guillén et al., 2007).
•	 Method of opportunity costs. It is used when
there are two or more choices of use of the
environmental area. The opportunity cost of
utilizing resources, in a certain way, is the most
highly valued alternative in which these resources
could have been invested and to which the society
would have to renounce when the resources
are used in another specific way (Zequeira et
al., 2016). For example, the decision of using a
vegetative area to start agricultural production
against the alternative of opening a national
park; if opening the park is chosen, the economic
appraisal is given by the market prices when
weighing the agricultural losses by their price.
•	 Method of the changes in productivity. This me-
thod attempts to estimate economically the envi-
ronmental impact on a natural resource, through
the appraisal of the effect this impact generates
on production, the cost or the profits genera-
ted by the other good which does have market.
Such effect on the production of another good
or service implies a change in people’s welfare.
Through the appraisal of such change in welfare
an approximation of the value of that environ-
mental impact is obtained. An example of the
application of the method can be the case of
water quality and agricultural production. If the
water quality decreases due to contamination,
there will be a decrease in yields, which would
be translated into higher production costs and,
thus, a higher price of the product. This ultima-
tely affects people, who will have to pay a higher
price for the product, and thus its usefulness de-
creases (MINAM, 2015).
•	 Method of replacement costs. The replacement cost
technique is based on the measurement of the costs
that are incurred by replacing productive assets
damaged by the disturbance of natural resources
and ecosystem processes. For example, the cost
of acid deposition related to air contamination
in urban areas could be approached through the
cost of replacement or restoration of the damaged
infrastructure (Murillo and González, 2017).
•	 Method of hedonic prices. The environmental
quality affects the price people are willing to
pay for certain goods or services. The method
is based on the fact that many of the prices ob-
served for the goods are prices for a set of at-
tributes. This approach estimates the welfare
derived from the environmental characteristics
that influence directly the market prices of a spe-
cific good. The most used variants are based on
the price of properties and on the salaries (Díaz,
2017).
•	 Travel cost method (TCM). It is based on the
costs that are incurred by the visitor to a place
to enjoy the recreation ecosystemic services pro-
vided by a certain site. For example, in the case
of natural parks, people enjoy the natural areas,
but, to do that, they need to consume some pri-
vate goods to travel to the site, and it is on those
private expenses this method is based in order to
determine an approximation to the value of the
natural resource (Tomio and Ullrich, 2015).
•	 Method of avoided costs (MAC). It estimates
the costs which are incurred to prevent the
damage caused by environmental degradation.
This technique examines the expenses in order
to determine the importance people assign to
the impacts on the environment and health.
The fundamental premise is that an individual
perception of the cost imposed by damage is
related to what the person pays to prevent it from
occurring (Ripka de Almeida et al., 2018).
•	 Method of contingent appraisal or of construc-
ted markets. The method consists in the design
of a hypothetic market, presented to the indivi-
dual through a questionnaire, which is later used
to simulate several markets in which values are
assigned to the resources. The intention is to
know the preferences of society on environmen-
tal quality, and how much it will be willing to
pay for not being deprived of the benefits of ha-
ving such resources (Pérez-Torres, 2016).
•	 Model of economic evaluation of the eco-friend-
ly productive activity. This model uses three
fundamental criteria to define a practice or pro-
duct as eco-friendly (Barzev et al., 2013). They
are: 1) competitiveness: it is the technology used
in each economic alternative; 2) environmen-
tal measures: it is the quantification of negative
impacts (translated into costs) and the measu-
res proposed to mitigate them, thus generating
social benefits; and 3) economic viability: it is
the application of the costs-benefits technique to
Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Economic appraisal of the environment	153
compare costs versus benefits of the economic
activity (including environmental costs and be-
nefits).
The environmental measures in the model
represent the different costs that are incurred to
prevent negative impacts on the environment.
In addition, the additional incomes or profits
generated by adopting those mitigation measures
of the negative impacts, are quantified.
The methods and techniques that are used
in literature vary from one author to the other,
and their election depends fundamentally on the
pursued objective. It is very common to find several
techniquesappliedinthesameresearch,whichallows
to appraise each of the environmental functions of
the goods and services of the area under study.
Application in the Cuban animal husbandry
sector
In the Cuban animal husbandry activity, the
field of the instruments of environmental policy
and management is very limited because there is
not a clearly defined economic-environmental
policy in which compensation systems are used for
good practices, such as payments for environmental
services, and there is not a market of carbon
certificates either. These compensation systems
have been applied in several countries of America
by such authors as Murgueitio et al. (2013), Zapata
et al. (2015), Artunduaga and Escobar (2016),
with very good results in the achievement of the
sustainable management of the activity.
There are several studies in the field of environ-
mental economic appraisal which have been con-
ducted in Cuba in recent years (table 2). Among the
reviewed papers the ones that have as study object
the territories and protected areas stand out. In the
first case are the reports and doctoral and master
of science theses which were elaborated within the
framework of the UNDP/GEF Sabana-Camagüey
Project. They were focused on several ecosystems
of the zone, where the studies were aimed at ap-
praising in economic terms the natural resources
of national parks, mangroves and basins, which in
most cases are dedicated to tourism development.
In the case of the animal husbandry sector,
four cases of interest were found in the last years
in which the economic appraisal of the environ-
mental impact was applied. This does not mean
that they are the only ones, because in several of
the cited works (Rangel et al., 2013; Ferro et al.,
2016; Zequeira et al., 2016) the function of animal
husbandry as one of the values of direct use in the
studied systems was evaluated, although this sector
was not the protagonist (table 2).
The study conducted by Miranda et al. (2007)
was focused on the economic appraisal of the car-
bon sequestered in a farm with natural pasture and
another one converted in a silvopastoral system
(SPS), with 11 years of exploitation. The estimated
amount of stored carbon per hectare in the systems
was approximately valued in 1 590 dollars (USD).
From this amount, 80 % was contributed by the
SPS, which surpassed the natural pasture, and the
Table 2. Studies of environmental economic appraisal conducted in Cuba, by sector.
Sector Studies Authors
Animal husbandry 4
Miranda et al. (2007, 2008); De la Cruz et al. (2013); Manzano et al. (2013);
Valdés et al. (2013)
Mining 1 Reynaldo and Guardado (2017)
Tourism 4
Figueredo et al. (2013); Gutiérrez and Soulary (2013); Labrada (2013); Zequeira et
al. (2013)
Protected areas 5
Machín and Hernández (2009); Hernández (2011); Villarreal and Unger (2012);
Delgado (2013); Rodríguez et al. (2017)
Forestry 3 Rodríguez et al. (2011); Domínguez-Junco et al. (2012); Poey and García (2013)
Basins 3 Rangel et al. (2013); Ferro et al. (2016); Zequeira et al. (2016)
Fishery 2 Bucarano et al. (2013); Betanzos-Vega et al. (2014)
Entrepreneurial 1 Cañizares-Roig and Martín-García (2016)
Territorial 8 PNUD (2007) UNDP/GEF Sabana-Camagüey Project
Source: elaborated by the author.
154 	 Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Nadia Báez-Quiñones
high economic contribution of the system with trees
was proven. For its estimation the direct method of
market prices was used, and the carbon mass held
was multiplied by its price in the market of carbon
certificates.
Miranda et al. (2008) completed the study with
the economic appraisal of how much the biodiversity
function represented in animal husbandry
ecosystems. For such purpose the technique of
avoided costs due to weed control, assigned to
that environmental service, was used. In both
study cases it was concluded that the estimation of
environmental benefits, along with the economic
incomes by way of milk production, constitutes a
valorization of animal husbandry ecosystems.
De la Cruz et al. (2013) evaluated the imple-
mentation of the management plan of the buffalo
stock with biodiversity conservation techniques.
For such purpose two dairy farms with sustainable
management and two with traditional management
were compared. In spite of the costs of the dairy
farms with sustainable management being higher,
because they internalized the environmental costs
(reforestation of the area for the utilization of liv-
ing fences, protection against fires, maintenance of
channels and dams, among others), in them high
positive impacts were generated (decrease of soil
erosion, utilization of trees for animal feeding and
shade, production of fruit and firewood for sale,
among others). From the economic point of view,
this area showed higher incomes in all the periods.
In the study all the additional incomes which would
be obtained from sustainable management were not
taken into consideration; thus, the positive economic
impacts (externalities) were not really quantified,
although it constitutes an approximation to what
should be done regarding the economic appraisal of
environmental services.
Valdés et al. (2013) studied the economic fea-
sibility of constructing a plant of pig waste treat-
ment with anaerobic digestion technology. For such
purpose, the benefit-cost ratio and the investment
recovery period were determined. In the determi-
nation of the incomes and costs the environmental
aspects were taken into consideration. The savings
by way of diesel substitution and contribution of nu-
trients from the substitution of chemical fertilization
by fertilization with biosolid, were included.
During the bibliographic review, it could be ob-
served that the environmental economic appraisal
in the animal husbandry sector is not very frequent
in Cuba. This is only limited to determining the
main environmental functions and the magnitude
of their impact, but their economic value is not con-
sidered. However, work has been started to be done
in order to determine the economic impact of the
animal husbandry activity on the environment, not
only from the negative point of view, but also from
the large variety of environmental services and
goods that are derived from it.
Conclusions
The Total Economic Value theory is one of
the most used for the economic appraisal of the
environment. In addition, there are diverse highly
useful techniques to appraise economically the
environmental impact of animal husbandry in
Cuba, and their election depends on the objective
pursued by the research. In the same study several
techniques can be used in order to determine the
economic values of each of the environmental
functions identified in the ecosystem.
In recent years, the studies of environmental
economic appraisal have been increased in the
Cuban animal husbandry sector; nevertheless,
they are not sufficient, if the role played by animal
husbandry in the intensification of environmental
problems and the potentialities it has for mitigating
them is taken into consideration.
Bibliographic references
Almeida, A. R. de; Silva, C. L. da & Hernández-San-
toyo, A. Métodos de valoración económica
ambiental: instrumentos para el desarrollo de
políticas ambientales. Universidad y Sociedad.
10 (3):134-141, 2018.
Artunduaga, L. & Escobar, Y. Identificación del pago
por servicios ambientales captura de carbono en
sistemas ganaderos de la microcuenca La Mono
en el municipio de Belén de los Andaquíes. Tesis
en opción al grado de Maestría en Tributación.
Florencia, Colombia: Universidad de la Amazo-
nia, 2016.
Azqueta, D. Valoración económica de la calidad am-
biental. Madrid: McGraw-Hill, 1994.
Barzev, R.; Cruz, D. M. de la; Báez, C. M.; Méndez,
L.; León, O. & Manzano, A., et al. Potenciando
la conservación de la biodiversidad mediante la
evaluación económica y ambientalmente sosteni-
ble de actividades productivas en el ecosistema
Sabana-Camagüey, Cuba. La Habana: Agencia
Medio Ambiente, 2013.
Betanzos-Vega, A.; Rivero-Suárez, Sarah & Ma-
zón-Suástegui, J. M. Factibilidad económi-
co-ambiental para el cultivo sostenible de ostión
Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Economic appraisal of the environment	155
de mangle Crassostrea rhizophorae (Güilding,
1828), en Cuba. Lat. Am. J. Aquat. Res. 42 (5):1148-
1158, 2014.
Biondi, M. En busca de aportes teóricos para lograr la
identidad de la contabilidad ambiental. Contabi-
lidad y Auditoría. 32 (16):12-29, 2016.
Bucarano, L.; Rodríguez, E.; González, O. & Castillo,
E. Práctica de producción sostenible en la activi-
dad pesquera. Experiencia piloto de la creación
de una granja demostrativa y experimental para
el cultivo de esponjas comerciales: Manejo sos-
tenible de recursos pesqueros al centro del ar-
chipiélago Sabana-Camagüey. En: Potenciando
la conservación de la biodiversidad mediante la
evaluación económica y ambientalmente sosteni-
ble de actividades productivas en el ecosistema
Sabana Camagüey, Cuba. Sancti Spíritus, Cuba:
Agencia de Medio Ambiente. p. 49-56, 2013.
Cañizares-Roig, Marlene & Martín-García, Marili.
Procedimiento para cuantificar los costos de las
actividades ambientales en la gestión de sosteni-
bilidad del recurso agua potable. Cofín Habana.
11 (2):160-183, 2016.
Cerda, A. Valoración económica del medio ambiente.
II Curso Instrumentos de Mercado y Fuentes de
Financiamiento para el Desarrollo Sostenible.
Cartagena de Indias, Colombia, 2003.
CITMA. Estrategia Ambiental Nacional 2016/2020.
Informe del Ministerio de Ciencia, Tecnología y
Medio Ambiente. La Habana: CITMA, 2016.
De la Cruz, D. M.; Báez, C. M.; Méndez, L. & León,
O. Manejo sostenible de la masa bufalina en
la Reserva de la Biosfera Buenavista. En: Po-
tenciando la conservación de la biodiversidad
mediante la evaluación económica y ambiental-
mente sostenible de actividades productivas en
el ecosistema Sabana Camagüey, Cuba. Sancti
Spíritus, Cuba: Agencia de Medio Ambiente.
p. 19-28, 2013.
Delgado, L. Enfoques económicos-financieros del Sis-
tema Nacional de Áreas Protegidas de Cuba. En:
Potenciando la conservación de la biodiversidad
mediante la evaluación económica y ambiental-
mente sostenible de actividades productivas en
el ecosistema Sabana Camagüey, Cuba. Sancti
Spíritus, Cuba: Agencia de Medio Ambiente.
p. 68-78, 2013.
Díaz, C. Aspectos conceptuales y metodológicos de
la Guía para la aplicación de la valoración eco-
nómica ambiental. Bogotá: Oficina de Negocios
Verdes y Sostenibles, MINIAMBIENTE, 2017.
Dixon, J. & Pagiola, S. Análisis económico y evalua-
ción ambiental. In: Environmental Assessment
Sourcebook. p. 1-17, 1998.
Domínguez-Junco, O.; Betancourt-Figueras, Y.; Ro-
dríguez-Crespo, G.; González-Montpellier, L. E.
& Benítez-Menéndez, O. Fundamentación polí-
tica socioeconómica del cobro de los servicios
ecosistémicos forestales en Cuba. AIA 14 (1):49-
60, 2012.
Ferro, H.; Gómez, G. & Herrera, P. Valoración eco-
nómica de los impactos ambientales seleccio-
nados del cuabal en la Reserva Ecológica La
Coca, La Habana, Cuba. Acta Botánica Cubana
215 (1):24-37, 2016.
Figueredo, T.; Pina, F. & Angulo, J. Aportes de bie-
nes y servicios ambientales del Parque Nacional
Jardines de la Reina (PNJR) a la economía del
sector. En: Potenciando la conservación de la
biodiversidad mediante la evaluación económi-
ca y ambientalmente sostenible de actividades
productivas en el ecosistema Sabana Camagüey,
Cuba. Sancti Spíritus, Cuba: Agencia de Medio
Ambiente. p. 85-105, 2013.
Figueroa, A. Crecimiento económico y medio am-
biente. Revista CEPAL. 109:20-42, 2013.
Goodland, R. & Daly, H. Environmental sustainabi-
lity: universal and non-negotiable. Ecol. appl.
6 (4):1002-1017, 1996.
Guillén, W. E.; Guzmán, C. J. & Plasencia, M. G. Eva-
luación de la implementación de pago por servi-
cios ambientales en El Salvador. Tesis en opción
al grado de Licenciatura en Economía. Antiguo
Cuscatlán, El Salvador: Universidad Centroame-
ricana José Simeón Cañas, 2007.
Gutiérrez, G. & Soulary, D. Valoración de los servi-
cios ambientales de los ecosistemas: Ecosistema
Sabana-Camagüey. Caso: Laguna La Redonda.
En: Potenciando la conservación de la biodi-
versidad mediante la evaluación económica y
ambientalmente sostenible de actividades pro-
ductivas en el ecosistema Sabana Camagüey,
Cuba. Sancti Spíritus, Cuba: Agencia de Medio
Ambiente. p. 106-118, 2013.
Hernández, A. Bases teórico metodológicas para la
valoración económica de bienes y servicios am-
bientales a partir de técnicas de decisión mul-
ticriterio. Estudio de caso: Parque Nacional
Viñales, Pinar del Río, República de Cuba. Tesis
en opción al grado científico de Doctor. Alicante,
España: Universidad de Alicante, 2011.
Hernández, A.; Casas, M.; Leon, M. A.; Caballero,
R. & Pérez, V. E. La Ciencia Económica y el
Medio Ambiente: un aporte desde la valoración
económica ambiental. Rev. Paran. Desenvolv.
34 (125):25-38, 2013.
Hernández, A.; Casas, M.; Leon, M. A. & Pérez, V.
E. Valoración económica de bienes y servicios
ambientales en áreas protegidas: contribución al
proceso de toma de decisiones. Retos de la Di-
rección 4 (2):3-12, 2010.
Labrada, G. Viabilidad económica de la actividad
turística en el Área Protegida de recursos ma-
156 	 Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Nadia Báez-Quiñones
nejados Jobo Rosado. En: Potenciando la con-
servación de la biodiversidad mediante la
evaluación económica y ambientalmente soste-
nible de actividades productivas en el ecosiste-
ma Sabana Camagüey, Cuba. Sancti Spíritus,
Cuba: Agencia Medio Ambiente. p. 71-84, 2013.
Leal, C. L. Valoración económica del medio ambien-
te. Caso de la Reserva de la Biosfera de los Tuxtlas.
Tesis Licenciatura en Economía. Puebla, Cuba:
Escuela de Ciencias Sociales, Universidad de las
Américas, 2005.
Machín, M. M. & Casas, M. Valoración económica
de los recursos naturales. Pinar del Río, Cuba:
Universidad de Pinar del Río, 2006.
Machín, M. M. & Hernández, A. Hacia una aproxima-
ción de la valoración económica en áreas prote-
gidas. Estudio de caso: Parque Nacional Viñales,
Cuba. Revista UDO Agrícola. 9 (4):873-884,
2009.
Maldonado, J. & Cuervo, R. Valoración económica
del Parque Nacional Natural Corales de Profun-
didad. Bol. Invest. Mar. Cost. 45 (1):99-121, 2016.
Manzano, A.; Caraballoso, A. & Castro, M. Compa-
ración de las emisiones de GEI de la producción
bufalina con las actividades de remoción de
dióxido de carbono en áreas reforestadas de la
UBPC No. 5. Agropecuaria Bolivia, Ciego de
Ávila. En: Potenciando la conservación de la
biodiversidad mediante la evaluación económi-
ca y ambientalmente sostenible de actividades
productivas en el ecosistema Sabana Camagüey,
Cuba. Sancti Spíritus, Cuba: Agencia de Medio
Ambiente. p. 29-36, 2013.
MINAM. Manual de valoración económica del patri-
monio natural. Lima: Ministerio del Ambiente,
2015.
Miranda, Taymer. Algunas consideraciones sobre la
valoración económica del impacto ambiental
en el sector agropecuario. Pastos y Forrajes.
25 (3):147-153, 2002.
Miranda, Taymer; Machado, R.; Machado, Hilda &
Duquesne, P. Carbono secuestrado en ecosis-
temas agropecuarios cubanos y su valoración
económica. Estudio de caso. Pastos y Forrajes.
30 (4):483-491, 2007.
Miranda, Taymer; Machado, R.; Machado, Hilda &
Duquesne, P. Valoración económica de bienes y
servicios ambientales en dos ecosistemas de uso
ganadero. Zootecnia Trop. 26 (3):187-189, 2008.
Murillo, L. G. & González, C. V. Criterios técnicos
para el uso de herramientas económicas en
los proyectos, obras o actividades objeto de li-
cenciamiento ambiental. Bogotá: Ministerio de
Ambiente y Desarrollo Sostenible y Autoridad
Nacional de Licencias Ambientales, 2017.
Pardo, Y. Y. & Sanjinés, G. N. Valoración económi-
ca de servicios ambientales en sistemas agrofo-
restales en América Latina. Revista FACCEA.
4 (2):141-150, 2014.
Pearce, D. W. & Morán, D. The economic value of di-
versity. Londres: UICN, 1994.
Pérez-Torres, F. J. Medio ambiente, bienes ambienta-
les y métodos de valoración. Equidad & Desa-
rrollo. 25:119-158, 2016.
PNUD. Ecosistema Sabana-Camagüey. Informe téc-
nico del proyecto PNUD/GEF Sabana-Cama-
güey. Cuba, 2007.
Poey, J. I. & García, Y. Y. Evaluación económica de
un proyecto forestal en la UBPS Guamuta, y sus
potencialidades de comercialización de dióxido
de carbono. En: Potenciando la conservación de
la biodiversidad mediante la evaluación econó-
mica y ambientalmente sostenible de actividades
productivas en el ecosistema Sabana Camagüey,
Cuba. Matanzas, Cuba: Agencia de Medio Am-
biente. p. 37-48, 2013.
Raffo, E. Valoración económica ambiental: el proble-
ma del costo social. Industrial Data. 18 (1):108-
118, 2015.
Rangel, R. A.; Durán, O.; Gómez, G.; Ferro, H.; Ba-
rranco, G. & Sánchez, M. Valoración económi-
co-ambiental de recursos naturales seleccionados
en la cuenca del río Guanabo, La Habana, Cuba.
REVIBEC. 20:45-55, 2013.
Reynaldo, C. L. & Guardado, R. M. Procedimiento
para la valoración económica y ambiental en la
actividad minera de níquel. An. de la Acad. 6 (3),
2017.
Rodríguez, Y.; Renda, A.; Gutiérrez, J. E. & Plasen-
cia, T. Bienes y servicios ambientales obtenidos
del raleo I y II en pinares en la cuenca hidrográ-
fica del Río San Diego, Pinar del Río. Revista
Forestal Baracoa. 30 (2):25-32, 2011.
Rodríguez-Córdova, R.; Mir-Frutos, Z. & Guz-
mán-Alberteris, L. Incidencia de la valoración
económica de bienes y servicios ecosistémicos
en la gestión ambiental. Universidad y Sociedad.
9 (5):262-267, 2017.
Tomio, M. & Ullrich, D. R. Valoración económica
ambiental en el turismo. Estudios y perspectivas
del turismo. 24:172-187, 2015.
Valdés, L. A.; Ulloa, D. R.; Gómez, C.; Jiménez, Y.;
Castro, M. & Vidal, V. Factibilidad económica
del uso de la tecnología de digestión anaerobia en
el tratamiento de residuales porcinos a pequeña
y mediana escala. RCCP. 20 (4):238-241, 2013.
Villarreal, Y. & Unger, P. V. Valoración económica
de los ecosistemas del área protegida Reserva
Ecológica Punta del Este. ConFin Habana. 4:1-7,
2012.
Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Economic appraisal of the environment	157
Wilkes, A.; Reisinger, A.; Wollenberg, E. & van Dijk,
S. Medición, reporte y verificación de las emi-
siones de GEI de la ganadería de países en de-
sarrollo de la UNFCCC: prácticas actuales y
oportunidades de mejora. Informe 17. Programa
de Investigación de CGIAR en Cambio Climáti-
co, Agricultura y Seguridad Alimentaria (CCA-
FS) y Alianza Mundial de Investigación sobre los
Gases de Efecto Invernadero de Origen Agrope-
cuario (GRA). Wageningen, Holanda, 2017.
Zapata, C.; Robalino, J. & Solarte, A. Influencia del
Pago por Servicios Ambientales y otras variables
biofísicas y socioeconómicas en la adopción de
sistemas silvopastoriles a nivel de finca. LRRD.
27 (4). http://www.lrrd.org/lrrd27/4/zapa/27063.
html. [07/07/2018], 2015.
Zequeira, M. E.; Figueredo, E. & Echemendía, A. Me-
canismo financiero turístico por concepto de servi-
cios ecosistémicos para sostener la oferta de agua:
Cayo Sabinal, Camagüey, Cuba. En: Potenciando
la conservación de la biodiversidad mediante la
evaluación económica y ambientalmente sosteni-
ble de actividades productivas en el Ecosistema
Sabana Camagüey, Cuba. Sancti Spíritus, Cuba:
Agencia de Medio Ambiente. p. 119-131, 2013.
Zequeira, M. E.; Figueredo, E.; León, M. M. & Mon-
tero, R. Costo de oportunidad para bienes am-
bientales en la zona costera norte de la provincia
de Camagüey, Cuba. Ecociencia. 3 (2), 2016.
Received: May 16, 2018
Accepted: September 5, 2018
158 	 Pastos y Forrajes, Vol. 41, No. 3, July-September, 158-163, 2018 / Yuseika Olivera-Castro
Scientific Paper
Selection of accessions of Urochloa brizantha (Hochst. ex A. Rich.) R. D.
Webster for acid soils
Yuseika Olivera-Castro1
, Onel López-Vigoa1
, Pedro Pablo del Pozo-Rodríguez2
, Lisset
Castañeda-Pimienta1
, Agustín Olmedo-Juárez3
, Javier Arece-García1
and Rolando Rojo-Rubio4
1
Estación Experimental de Pastos y Forrajes Indio Hatuey, Universidad de Matanzas, Ministerio de Educación Superior
Central España Republicana, CP 44280, Matanzas, Cuba
2
Universidad Agraria de La Habana Fructuoso Rodríguez, Mayabeque, Cuba
3
Centro Nacional de Investigación Disciplinaria en Parasitología Veterinaria (CENID-PAVET) Jiutepec, Morelos, México
4
Centro Universitario UAEM-Temascaltepec, Universidad Autónoma del Estado de México
E-mail: yuseika@ihatuey.cu
Abstract
A collection of 19 Urochloa brizantha accessions was studied, in association with Stylosanthes guianensis
on a soil characterized by acidity, in order to select the best ones for this soil type. The measured and estimated
variables were: vegetative height, availability and non-consumed pasture residue. In addition, leafiness, cover, vigor,
CP content, fiber (NDF and ADF) degradation and IVDMD, were determined. The interpretation of the results was
done through principal component analysis; and for grouping the associations and selecting those that had similar
characteristics, cluster analysis was used. The existence of a high accumulated variability (75,9 %) was detected in
the first four components. When analyzing the agronomic and nutritional value performance, after three years of
exploitation, the formation of six groups was identified; the associations in which the accessions that form group II
were present (CIAT-16335 and CIAT-26646) stood out, reaching the highest values in height, availability and utilization,
as well as high vigor and high CP contents and IVDMD. These associations that included the accessions that belonged to
group II (CIAT-16335 and CIAT-26646) were present showed the best performance, when making an overall analysis of
agronomic and nutritional value variables. It is recommended to study structural and floristic composition variables, as
well as the seed production potential, in order to propose a pre-commercial variety for the agroecosystems with acid soil.
Keywords: height, evaluation, nutritional value
Introduction
In the 1980’s, the species of cultivated pastures
represented approximately 60 % of pasturelands
in the country. Nevertheless, after more than
three decades under exploitation, they barely reach
19 %, and some show a high degree of degradation
(CITMA, 2012).
In addition to this problem, there is a marked
fertility loss in soils dedicated to animal husbandry
(Hernández, 2016), element that constitutes one of
the main causes of the degradation of cultivated
pastures, whose consequence results in a reduction
of plant biomass yield and quality and its direct im-
plication in the decrease of milk and meat produc-
tion (Padilla et al., 2013).
Such aspects force the adoption of strategies
aimed at the application of technologies that in-
clude the introduction and evaluation of species
and/or accessions, which can contribute to the im-
provement of the feeding basis of animal husbandry
zones and which, in turn, allow to reach adequate
production, quality and persistence of pasturelands;
because animal feeding is supported mainly on the
utilization of pastures and forages, as it is one of
the cheapest sources (Verdecia-Acosta et al., 2014).
In many studies it has been proven that the spe-
cies of the Urochloa genus grow on a broad range
of soils, and some of them are recommended spe-
cifically for acid soils, in Cuba as well as in other
tropical zones of America (Silva et al., 2016); in
this type of soil, Urochloa decumbens (Stapf) R. D.
Webster, Urochloa humidicola (Rendle) Morrone
& Zuloaga, Urochloa dictyoneura (Fig. & De Not.)
Veldkamp, and Urochloa brizantha (Hochst. ex A.
Rich.) R. D. Webster, stand out.
Based on the above-described facts, it is essen-
tial to identify the U. brizantha materials that adapt
better to these soils, from their morphophysiologi-
cal and productive characteristics; such accessions
could make a better utilization of nutrients and pro-
vide sufficient biomass, with the required quality,
for the maintenance, production and reproduction
of grazing animals.
Hence the objective of this study was to select
the best accessions of a U. brizantha collection in as-
sociation with Stylosanthes guianensis for acid soils.
Pastos y Forrajes, Vol. 41, No. 3, July-September,158-163, 2018 / Selection of accessions of Urochloa brizantha	 159
Materials and Methods
Location of the experimental area. The study
was conducted in areas of the Pastures and Forages
Research Station of Cascajal, Santo Domingo mu-
nicipality –Villa Clara province, Cuba–, located at
22º 36’ North latitude and 80º 04’ West longitude,
at 60 m.a.s.l.
Characteristics of the climate. The climate of the
zone is classified as tropical, characteristic of Cuba.
The performance of the climate variables is shown in
table 1; the rainfall volume varied among the years
the study lasted, and only in the first year the rainfall
was higher compared with the other two years.
The maximum, minimum and mean tempera-
ture, relative humidity and light hours showed simi-
lar values among the years.
Soil of the experimental area. The study was
conducted on a distic, petroferric, Ferruginous,
Nodular Gley soil, characterized by acid pH (4,2),
as well as low organic matter content (1,91 %), total
N (0,40 %) and assimilable P (1,90 mg/100 g). re-
garding these characteristics, it can be considered
an acid soil and with low fertility, according to
Hernández-Jiménez et al. (2015).
Experimental procedure
Soil preparation. For the soil preparation the
conventional method was used, consisting in plow-
ing, harrowing, crossing, harrowing and furrowing.
Design and treatments. A randomized block
design was used with three replicas. The plots
measured 23,52 m2
, and were separated by 1,50 m
spaces on both sides.
The treatments were represented by 19 previously
selected U. brizantha accessions: CIAT-16300, CIAT-
16317, CIAT-16809, CIAT-16469, CIAT-16322, CIAT-
16132, CIAT-16128, CIAT-16335, CIAT-1539, CIAT-26290,
CIAT-16332, CIAT-16819, CIAT-16303, CIAT-16334,
CIAT-16448, CIAT-26646, CIAT-16485, CIAT-16197 and
CIAT-26032,inassociationwithS.guianensis.
Planting, sowing and establishment. The grass
was planted by vegetative seed, consisting in por-
tions of tillers formed by five to eight 20-cm long
shoots, approximately. A distance between plants
and between rows of 0,70 m was used, which is
equivalent to a density of 20 000 plants/ha. The
rows as well as the external tillers were separated
from the plot edges by 0,35 m; the depth was 10 cm.
As legume, S. guianensis (Aubl.) Sw. CIAT-184
was used, accession selected in Cuba as commer-
cial variety (MINAG, 2016), which has shown adap-
tation to this soil type (Castañeda-Alvarez et al.,
2016). It was planted by drilling, at a depth of 2 cm
and space between rows of 0,70 m, with density of
1,5 kg of PGS/ha. Its seeds were previously scari-
fied in water at 80 ºC during two minutes.
The planting as well as the seeding were simul-
taneously performed in April, related to the rainfall
occurred in that month. During 45 days after these
activities the space between the plots was manually
weeded twice, and some weak or dead grass plants
were replaced, so that all the treatments were repre-
sented by a similar number of tillers. Throughout
the experimental period neither irrigation nor ferti-
lization was used.
Animals. Homogeneous groups of 29 crossbred
(Creole x Zebu) fattening animals (20,3 LAU) were
used,withanaverageweightof350kgandgoodhealth
status, which had water and mineral salts available 24
h per day in a paddock designed for this purpose. No
energy or protein supplementation was offered.
Management. A simulated grazing system was
used, in which the animals were led to the area
when the treatments reached resting times between
85 and 95 days in the dry season (DS) and between
50 and 60 days in the rainy season (RS). The average
permanence days were 2 and 1 day and the grazing
intensity was 94,4 and 47,2 LAU days/ha for both
seasons, respectively. During the three years of the
study a total of 15 rotations were made, five in each
year, from which two corresponded to the DS and
three to the RS.
Measurements. The “Methodology for the
evaluation of herbaceous species”, proposed by the
Table 1. Climate performance during the research.
Year
Variables
Rainfall (mm)
Temperature (°C)
Relative humidity (%) Light hours
maximum minimum mean
1 1 697,7 31,5 19,5 24,4 78 7,9
2 1 153,5 31,3 19,2 24,3 76 8,0
3 1 262,3 30,2 18,5 23,6 77 7,8
160 	 Pastos y Forrajes, Vol. 41, No. 3, July-September, 158-163, 2018 / Yuseika Olivera-Castro
Pastures and Forages Research Station Indio Hatuey
(Machado et al., 1997) and approved by the National
Sub-Commission of Pasture and Forage varieties,
was taken as basis.
Agronomic variables. The plant height was
represented by the mean value of this variable in the
four tillers used for the determination of availability
(this was equivalent to a sample size of 8,3 %). For
the leafiness, cover and vigor a walk was made
that included the entire plot; and the value of each
variable was visually calculated, according to the
gradological scale used. The biomass availability
was estimated one day before the animals entered
the area, and the residue of non-consumed pasture,
when the animals left.
The measurements and estimations were made
in all the rotations.
Variables of the nutritional value. The broma-
tological composition was determined through the
proximal chemical analysis. Of each sample the N
content was analyzed by the Kjeldahl method, and the
CP content was estimated (N x 6,25). The fiber (NDF
and ADF) degradation was determined through the
Van Soest method.
The in vitro gas production technique was used
for obtaining the IVDMD and the parameters of the
different phases of this process: fraction b, fraction c
and Lag phase.
The analyses were conducted in the Nutrition
laboratory of the School of Veterinary Medicine of
the Autonomous University of Mexico State, Toluca,
Mexico State.
Statistical analysis. The principal component
analysis (PCA) was used. To identify the compo-
nents that explained the highest variations, those
that had a proper value higher than one were se-
lected; while in order to identify the variables that
influenced the most the variability extracted for
each component it was taken into consideration that
the sum or preponderance factors reached a value
higher than 0,60.
To group the accessions and select those that
had most prominent similar characteristics the
cluster analysis was used; from the results obtained
in the PCA. As grouping criterion the Euclidean
distance was used, and Ward method as form of
ascending hierarchical aggregation (Torres et al.,
2006). The cutting line for forming the groups was
based on the criterion expressed by Núñez-Colín
and Escobedo-López (2011). The statistical package
SPSS version 15®
was used.
Results and Discussion
When performing the PCA (table 2) the exis-
tence of high accumulated variability in the first
Table 2. Results of the PCA and relation among the variables.
Analyzed variables
Principal components
CP1 CP2 CP3 CP4
Vegetative height (cm) -0,46 0,70 0,01 0,40
Vigor (Ve) 0,89 0,05 -0,10 -0,01
Leafiness (Ve) 0,36 0,14 -0,38 0,26
Availability (t DM/ha/rotation) -0,58 0,69 -0,14 0,27
Utilization (%) 0,80 -0,16 0,32 0,13
CP (%) 0,22 -0,01 0,78 0,41
NDF (%) 0,19 0,29 0,02 -0,84
ADF (%) 0,33 0,37 -0,60 -0,10
IVDMD 0,58 0,56 0,23 0,31
Fraction b -0,53 -0,41 0,55 -0,17
Fraction c 0,20 0,65 0,54 -0,34
Lag phase 0,14 -0,70 -0,24 0,32
Proper value 3,0 2,6 1,9 1,5
Variance (%) 25,0 21,9 16,0 12,9
Accumulated (%) 25,0 46,9 63,0 75,9
Underlined values indicate higher contribution.
Pastos y Forrajes, Vol. 41, No. 3, July-September,158-163, 2018 / Selection of accessions of Urochloa brizantha	 161
four components was noted, based on the variables
included in the study. The variance in CP1 reached
avalueof25,0%,andinCP2,21,9%.InCP1,thevariables
with higher influence on the extracted variance were
vigor and utilization percentage; while in CP2, vege-
tative height, Lag phase, availability and fraction c, all
positively related; Lag phase did it inversely.
Although two elements of the degradability
equation did not show a strong incidence on the prin-
cipal components: IVDMD and fraction b, it is con-
sidered that they should be taken into consideration
due to their importance in the interpretation of
results.
The IVDMD was explained in the CP1-CP2
plane and, thus, linked to agronomic and nutritional
factors: vigor, utilization percentage, vegetative
height, availability, fraction c and Lag phase, all
positively related to that variable except the last one.
These variables, excluding the last, showed a stressed
trend to reaching higher percentages of IVDMD,
aspect that coincides with the expected result when
agronomic and nutritional value variables like these
are jointly analyzed (Tsuzukibashi et al., 2016).
On the other hand, fraction b, with sum or pre-
ponderance values close to 0,60, in CP3, was linked
to factors of the nutritional value, such as CP and
ADF, positively with the former and inversely with
the latter, which is in correspondence with the sig-
nificance of that variable.
The previously described results allow to con-
sider that there was a higher differentiation degree
among the associations with regards to the variables
present in CP1-CP2, and much less for variables
such as CP, ADF and NDF, which only extracted
16,0 and 12,9 % in CP3 and CP4, respectively.
When forming the groups through the cluster
analysis, based on the results of the PCA, the presence
of six different groups was detected. Table 3 shows
the typification of the accessions by groups and
their identification.
Similarity was found among the associations in
groups V and VI for the mean value of the variable
vegetative height, although its values were low-
er than that of groups I, III and IV. However, the
ones that formed group II (CIAT-26646 and CIAT-
16335) exceeded that of the last ones.
Table 3. Typification of the accessions by group and their identification.
Variables
Group I Group II Group III Group IV Group V Group VI
X SD X SD X SD X SD X SD X SD
Height 64,2 7,2 70,1 4,9 67,8 2,3 58,3 3,1 40,2 3,2 46,9 6,1
Vigor 3,0 0,0 4,0 0,0 4,0 0,0 4,0 0,0 4,0 0,0 4,0 0,0
Leafiness 3,4 0,5 4,0 0,0 4,0 0,0 3,7 0,5 3,7 0,5 4,0 0,0
Availability 3,6 0,5 3,8 0,8 3,4 0,2 2,8 0,3 2,3 0,1 2,7 0,0
Utilization 25,3 5,3 64,0 8,1 21,4 13,4 48,4 27,9 57,1 2,3 57,8 8,8
CP 9,9 1,3 11,2 1,7 9,4 1,6 10,4 1,6 10,4 1,8 9,3 1,1
NDF 76,1 1,2 75,3 1,2 75,0 0,9 78,4 2,1 75,8 1,1 77,6 0,7
ADF 41,0 1,2 42,8 0,9 41,1 1,6 40,8 1,4 40,7 0,6 43,7 0,0
IVDMD 50,2 5,0 65,1 2,5 50,4 1,9 54,8 1,1 51,9 0,8 57,2 1,6
Fraction b 163,8 3,6 143,6 5,2 140,7 3,3 153,1 1,7 158,8 8,5 142,7 7,0
Fraction c 0,02 0,0 0,02 0,0 0,02 0,0 0,02 0,0 0,02 0,0 0,02 0,0
Lag phase 1,49 0,5 1,39 1,2 1,1 0,4 0,5 0,1 2,1 0,2 1,8 0,2
Group Quantity of accessions Name of the accessions♦
I 5 CIAT-16300,CIAT-16322,CIAT-16819,CIAT-16332,CIAT-16132
II 2 CIAT-26646, CIAT-16335
III 2 CIAT-16197, CIAT-16809
IV 4 CIAT-16317, CIAT-16334, 1539, CIAT-26290
V 3 CIAT-26032, CIAT-16448, CIAT-16485
VI 3 CIAT-16128, CIAT-16303, CIAT-16469
♦
Associated with S. guianensis
162 	 Pastos y Forrajes, Vol. 41, No. 3, July-September, 158-163, 2018 / Yuseika Olivera-Castro
Regarding vigor, the accessions that formed
group I (CIAT-16300, CIAT-16322, CIAT-16819,
CIAT-16332, CIAT-16132) showed the worst perfor-
mance with regards to those in the other groups,
which, as average, reached value 4 according to the
scale used.
In the associations that were part of groups IV,
V and VI a relatively similar value was detected for
the variable availability, but lower than that of the
other groups. Among the latter (I, II and III), the
associations integrated by CIAT-26646 and CIAT-
16335 (group II) stood out with the highest value,
aspect that is considered of relevant interest, be-
cause it defines the biomass volume that is available
for animal feeding.
The percentage of utilization by the animals in
the above-mentioned associations was also higher
when compared with the mean of the other groups;
this has marked importance, due to the role this
variable plays in the consumption made by the ani-
mals. This same pattern was found for CP.
The parameters that are obtained when the cal-
culations are made to define the IVDMD values
through the gas production technique constitute an
extremely important tool to estimate the capacity of
degradation of the forages that compose the diet of
ruminants and, also, the factors with higher influence
on it (Vargas-Bayona et al., 2013).
Hence, when analyzing in these associations
the performance of fraction c and the Lag phase,
variables that characterize the forage degradation
rate, it was observed that the values of the former
were similar for all the groups; while the associa-
tions that formed group IV showed the best result
(0,5) for the latter, which means that they showed
the lesser time for the rumen microorganisms to
start the feed degradation.
Ortega-Aguirre et al. (2015) stated that there are
differencesamongtheparametersofthedegradability
equation for fractions b and c among forages of
different species, but not among accessions of the
same species. In this research such performance was
rather shown in fraction b, which showed variability
for the studied associations, according to the PCA.
An outstanding place corresponds to group
II (CIAT-16335 and CIAT-26646), regarding the
performance of the evaluated materials. These
accessions reached the greatest height, high vigor,
the highest values of availability and also in terms of
utilization, as well as high CP contents and IVDMD.
In this last variable similar results have been reported
in the grass Megathyrsus maximus cv. Mombaza
(60,9 %) and a little bit higher in Brachiaria hibrido
cv. Mulato (67,5 %), according to the report by Silva
et al. (2016).
The accession CIAT-26646, in particular, has
stood out in diverse animal husbandry systems.
In that sense, Njarui et al. (2016) referred the
potentialities of this material, which stood out for
its good acceptability, high resistance to pest attack,
good growth, high degree of associability with
legumes of twining or creeping growth habit, as well
as a CP content of 11 %. These and other outstanding
characteristics have allowed such accession to
become one of the most widely used in tropical
regions for cattle production (Caballero, 2014).
In the species U. brizantha there are satisfacto-
ry results regarding their agronomic performance
and nutritional value, such as the ones reported by
Tsuzukibashi et al. (2016), who found, depending
on the cutting age, different values of the nutrition-
al variables (up to 68 and 30 % for NDF and ADF,
respectively; and between 8,8 and 18,6 % of CP)
when studying cvs. Marandú. Piatã and Xaraés;
this confirms that this species has cultivars with ac-
ceptable quality for livestock feeding.
It is concluded that the associations in which
the accessions that formed group II (CIAT-16335
and CIAT-26646) were present showed the best
performance, when making an overall analysis of
agronomic and nutritional value variables Likewise, to
study structural and floristic composition variables, as
wellastheseedproductionpotential,isrecommended,
in order to propose a pre-commercial variety for the
agroecosystems with acid soil without using inputs.
Bibliographic references
Caballero, P. J. Brachiaria brizantha cv. La Liber-
tad (MG4). Paraguay: Semillas sudamericanas.
http://semillassudamerica.com/spa/productos/
producto-brachiaria-brizantha-cv-la-liber-
tad-mg4. [07/12/2017], 2014.
Castañeda-Álvarez, N. P.; Álvarez, F.; Arango, J.;
Chanchy, L.; García, G. F.; Sánchez, V. et al.
Especies vegetales útiles para sistemas silvopas-
toriles del Caquetá, Colombia. Cali, Colombia:
Deutsche Gesellschaft für Internationale Zusam-
mena, Centro Internacional de Agricultura Tro-
pical, 2016.
CITMA. Informe de Cuba a la Conferencia de las
Naciones Unidas sobre Desarrollo Sostenible
Río+20. La Habana: Ministerio de Ciencia, Tec-
nología y Medio Ambiente, 2012.
Hernández, Marta. Los suelos dedicados a la ganade-
ría en Cuba. Conferencia. Maestría en Pastos y
Forrajes; 3.5; Matanzas, Cuba: EEPF Indio Ha-
tuey. p. 20, 2016.
Pastos y Forrajes, Vol. 41, No. 3, July-September,158-163, 2018 / Selection of accessions of Urochloa brizantha	 163
Hernández-Jiménez, A.; Pérez-Jiménez, J. M.;
Bosch-Infante, D. & Castro-Speck, N. Clasifica-
ción de los suelos de Cuba. Mayabeque, Cuba:
Instituto Nacional de Ciencias Agrícolas, Insti-
tuto de Suelos, Ediciones INCA, 2015.
Machado, R.; Seguí, Esperanza & Alonso, O. Con-
ferencia Metodología para la evaluación de es-
pecies herbáceas. Matanzas, Cuba: EEPF Indio
Hatuey, 1997.
MINAG. Lista oficial de variedades comerciales. Re-
gistro de variedades comerciales. La Habana:
Ministerio de la Agriculturas, 2016.
Njarui, D. M. G.; Gatheru, M.; Ghimire, S. R. & Mure-
ithi, J. G. Effects of seasons and cutting intervals
on productivity and nutritive value of Brachiaria
grass cultivars in semi-arid eastern Kenya. D. M.
G.Njarui, E. M. Gichangi, S. R. Ghimire, R. W.
Muinga. Climate smart Brachiaria grasses for
improving livestock production in East Africa:
Kenya Experience. Proceedings of a workshop.
Naivasha, Kenya: Kenya Agricultural and Lives-
tock Research Organization. p. 46-61, 2016.
Núñez-Colín, C. A. & Escobedo-López, Diana. Uso
correcto del análisis clúster en la caracteriza-
ción de germoplasma vegetal. Agron. Mesoam.
22 (2):415-427, 2011.
Ortega-Aguirre, C. A.; Lemus-Flores, C.; Bugarín-Pra-
do, J. O.; Alejo-Santiago, G.; Ramos-Quirarte, A.;
Grageola-Núñez, O. et al. Agronomic characteris-
tics, bromatological composition, digestibility and
consumption animal in four species of grasses of
the genera Brachiaria and Panicum. Trop. Sub-
trop. Agroecosyst. 18:291-301, 2015.
Padilla, C.; Sardiñas, Y.; Febles, G. & Fraga, Nidia.
Estrategias para el control de la degradación en
pastizales invadidos por Sporobolus indicus (L)
R. Br. Rev. cubana Cienc. agríc. 47 (2):113-117,
2013.
Silva, Janaina de L.; Ribeiro, Karina G.; Herculano,
Bruna N.; Pereira, O. G.; Pereira, Rosana C. &
Soares, Luciana F. P. Massa de forragem e ca-
racterísticas estruturais e bromatológicas de cul-
tivares de Brachiaria e Panicum. Ciênc. anim.
bras. 17 (3):342-348, 2016.
Torres, Verena; Figueredo, J.; Lizazo, D. & Álvarez,
A. Modelo estadístico para la medición del im-
pacto de la innovación o transferencia tecnoló-
gica en la rama agropecuaria. Informe técnico.
San José de las Lajas, Cuba: Instituto de Ciencia
Animal, 2006.
Tsuzukibashi, Denise; Costa, J. P. R.; Moro, Fabiola V.;
Ruggieri, Ana C. & Malheiros, E. B. Anatomia
quantitativa, digestibilidade in vitro e composição
química de cultivares de Brachiaria brizantha.
Rev. Ciências Agrárias. 39 (1):46-53, 2016.
Vargas-Bayona, J. E.; Mejía-Porras, G.; Bedoya-Mas-
huth, Julia & Gómez-Patiño, J. F. Estimación de
la técnica in vitro de gases frente a otras técni-
cas de digestibilidad. Spei Domus. 9 (18):59-70,
2013.
Verdecia-Acosta, D. M.; Herrera-García, R. S.; Ra-
mírez-de-la Ribera, J. L.; Acosta, I. L.; Bo-
das-Rodríguez, R.; Andrés-Lorente, Sonia et
al. Caracterización bromatológica de seis espe-
cies forrajeras en el Valle del Cauto, Cuba. AIA.
18 (3):75-90, 2014.
Received: April 23, 2018
Accepted: June 21, 2018
164 	 Pastos y Forrajes, Vol. 41, No. 3, July-September, 164-169, 2018 / Javier Antonio Herrera-Toscano
Scientific Paper
Selection of local resources for sheep feeding in the Las Tunas municipality,
Cuba
Javier Antonio Herrera-Toscano1
and Oscar Carmenate-Figueredo2
1
Instituto de Ciencia Animal, San José de las Lajas, gaveta postal No. 1, CP 32700, Mayabeque, Cuba.
2
Facultad de Agronomía, Universidad de Las Tunas, Municipio Las Tunas, Provincia Las Tunas, Cuba
E-mail: jherrera@ica.co.cu
Abstract
The objective of this study was to select the main available local resources, with potentialities for sheep feeding,
in the Las Tunas municipality –Las Tunas province, Cuba–. The method of expert consultation was applied, to a panel
of 26 members. The local resources were classified into non-forage and forage ones. Their evaluation was based on
different criteria: annual availability, total supply cost, nutritional value, conservation time and cost, adaptability
to local edaphoclimatic conditions, production in the dry season, resistance to pests and diseases, and production
without irrigation and fertilization. Nine locally available resources were selected for sheep feeding, 66 % of which
were forage ones. The highest value in forage resources corresponded to Leucaena leucocephala (Lam) de Wit (4,68
± 0,02) and the lowest, to Moringa oleifera Lam (3,18 ± 0,87). In non-forage resources, calcium carbonate had the
highest value (4,75 ± 0,75) and distillery vinasse, the lowest value (3,0 ± 0,10). Regarding the integral evaluation of the
forage resources, the highest values corresponded to Saccharum officinarum L., L. leucocephala and the Pennisetum
varieties: 4,54; 4,51 and 4,43, respectively; and the lowest ones to Tithonia diversifolia (Hemsl.) A. Gray, M. oleifera
and Morus alba L.: 2,99; 2,66 and 2,64, respectively. It is concluded that in the Las Tunas municipality there are
between five and six resources with potentialities for sheep production, among which calcium carbonate as non-forage
resource and L. leucocephala as forage resource stood out.
Keywords: evaluation, animal production, food security
Introduction
The adverse economic situation faced by Cuba
originates the need to increase food production radi-
cally; this objective is an issue of maximum con-
cern and occupation by the Cuban Government and
State. For such reason, a diversification of agricul-
tural production is mandatory in order to offer meat
products from different animal species.
In this sense, sheep are an important source
for meat production under tropical conditions.
Arece et al. (2013) stated that Pelibuey is the breed
with more potential for the production of small
ruminants in Cuba and plays a significant role, in
small-scale family economy as well as in the state
entrepreneurial sector.
Nevertheless, sheep production shows a set of
limitations that causes scarce and unstable yields,
which leads to low levels of sale and consumption
of this product throughout the country; in this re-
gard, the National Office of Statistics and Informa-
tion (ONEI, 2017) indicated that 14 291 t of sheep
meat were sold in agricultural markets, by the end
of 2016, scenario that constitutes a limiting factor
in the commercialization of this product.
On the other hand, the Pelibuey breed shows
good adaptation to the tropical environment, which
allows its exploitation in diverse types of produc-
tive systems, from the low-input to intensive pro-
duction systems, although the former are the most
widely used ones(Partida-de-la-Peña et al., 2013).
Factors of diverse nature have restricted the
development of sheep rearing in the tropical zone;
for example, the adverse climate conditions, relat-
ed to scarce and irregular rainfall volumes, high
temperatures and high relative humidity. This is
manifested in the insufficient productive yield of
the exploited breeds, as well as in the farmers’ so-
cioeconomic situation. On the other hand, the im-
plementation of crossing programs of tropical sheep
with improved breeds is insufficient, and besides an
inadequate sanitary management of the animals is
made; however, the quantitative as well as qualita-
tive limitations in the feeding basis are considered by
many researchers the fundamental and most difficult
problem to solve (Ruiz, 2011; Velasco et al., 2015).
The above-stated facts show the importance
of using feasible methodologies to identify the avail-
able resources at local level, with potentialities for
Pastos y Forrajes, Vol. 41, No. 3, July-September, 164-169, 2018 / Local resources for sheep feeding	165
animal feeding and management. In this sense, the
concept of local resource emerges as a philoso-
phy, which could be defined as any resource that is
obtained in a certain zone and is used for its benefit.
This perspective, which has often been the object
of research (Rendón et al., 2014; Meza-Carranco et
al., 2016), should be assimilated and enhanced with
higher intensity to aspire to improve sustainably the
productivity and efficiency indexes, in production
systems with sheep and other species.
Based on the above-explained facts, the objec-
tive of this work was to select the main available lo-
cal resources, with potentialities for feeding sheep
in the Las Tunas municipality, Cuba.
Materials and Methods
Characteristics of the study zone. The study
was conducted in the Las Tunas municipality, Las
Tunas province, Cuba, located at 20º 57’ 25” N latitude,
76º 57’ 13” W longitude, with an altitude above sea
level of 90 m. the main climate variables in the
last ten years averaged rainfall values of 1 038 mm,
temperature of 28 ºC and 76 % of relative humidity,
which corresponds to a dry tropical climate.
Concerning the methodology used, there are
several procedures aimed at investigating and com-
piling the perceptive information about a certain
issue in particular; the Delphi method is one of
them. It is the most widely used expert consultation
research technique. It consists in the systematic uti-
lization of an intuitive judgment by a group of indi-
viduals who have knowledge about a specific topic
(Rowe and Wright, 2011).
Delphi procedure for this study. A panel of 26
experts was created, integrated by professionals with
work experience in the studied zone. Two rounds of
interviews took place: in the first one the quantity
and types of resources that could be used in the farm
were selected, and in the second one the resources
were evaluated, with the experts’ participation. The
questionnaire was applied in all the cases through
interview to the experts; they showed differences
regarding their professions and belonged to four
entities: four from the Institute of Animal Science;
seven from the University of Las Tunas; six from
the Provincial Agriculture Delegation; five from the
provincial Cuban Association of Animal Production
(NGO) and four from the Las Tunas Pastures and
Forages Research Station. The average of years of
professional experience in the group was 26,6.
The resources were classified into forage and
non-forage ones, and their evaluation was based on
different criteria (table 1).
A questionnaire was elaborated that contained
two questions directly related to the utilization of
the potential local resources in sheep feeding in the
Las Tunas municipality and its vicinity.
Question 1. Evaluate the pertinence of how
many feeding resources you consider necessary in
a farm for feeding sheep in Las Tunas municipality.
Question 2. Select the local resources you con-
sider viable for sheep feeding in Las Tunas munici-
pality, and evaluate each resource in correspondence
with the proposed scale.
In the measurement of the experts’ opinions,
Likert’s (1932) scale was used; for the evaluation of
the resources an index resulting from the sum of the
values of each item, from which the defining deci-
sion was made, was taken into consideration. The
variable total supply cost was considered negative,
as it is a detrimental element in productive systems.
Question 1: 1. Totally disagree, 2. Almost dis-
agree, 3. Moderately agree, 4. Almost agree, 5. To-
tally agree.
Question 2: 1. Completely inadequate, 2. Al-
most inadequate, 3. Moderately adequate, 4. Al-
most adequate, 5. Completely adequate.
With the information obtained from each ex-
pert, according to their answers the descriptive
Table 1. Criteria used in the selection of local resources.
Non-forage resources Forage resources
Annual availability Annual availability
Total supply cost Adaptability to the local edaphoclimatic conditions
Nutritional value (protein and/or energy) Production in the dry season
Conservation time and cost Resistance to pests and diseases
Production without irrigation or fertilization
Nutritional value (protein and/or energy)
166 	 Pastos y Forrajes, Vol. 41, No. 3, July-September, 164-169, 2018 / Javier Antonio Herrera-Toscano
statistics average and typical deviation were calcu-
lated, through the Microsoft Excel worksheet.
Results and Discussion
The panel members’ opinion about the quan-
tity of necessary resources to guarantee sheep
rearing under the conditions of the municipalities
indicated that they should be five or more than
this value. This result is due, to a large extent, to
two main factors: first, rainfall seasonality, which
originates instability in the availability and quality of
feedstuffs, which in turn entails that it is necessary
to have a high degree of diversification in the feeding
front; and, second, the imperative of balancing the
diet to cover the basic nutritional requirements of
the animals (NRC, 2016; Perdomo et al., 2017).
The values close to zero of the typical deviation
(table 2) indicated that there was homogeneity in
the responses and, thus, little dispersion around
them (Solanas et al., 2005).
Table 3 shows the results of the selection of the
resources that were mostly considered by the experts
and their corresponding degree of importance. In to-
tal the resources mentioned were nine; it should be
emphasized that 66 % of these resources are forage
ones, which has direct relation with the principles of
ruminant animal production under tropical condi-
tions and the production costs (Alonso, 2016).
The highest values in the forage resources were
obtained in white leadtree (Leucaena leucocepha-
la) and the Pennisetum varieties; in the non-forage
resources, the calcium carbonate source turned
out to be the preferred one. With this selection it is
guaranteed that the energy requirements are cov-
ered with sugarcane (S. officinarum) and the Pennise-
tum varieties.
Table 2. Stadigraphs of the application of the Likert scale for the
selection of the necessary feeding resources in a sheep
production farm.
Item Average Standard deviation
One resource 1,00 -
Two resources 1,00 -
Three resources 2,30 0,56
Four resources 3,72 0,97
Five resources 4,40 0,61
More than five resources 4,45 0,78
Likert scale: 1. Completely disagree, 2. Almost disagree, 3. Moderately
agree, 4. Almost agree, 5. Completely agree.
Table 3. Stadigraphs of the application of the Likert scale in the
determination of the importance of the feeding resources.
Item Average Typical deviation
L. leucocephala 4,68 0,02
Saccharum officinarum 3,65 0,24
Pennisetum varieties 4,30 0,06
Tithonia diversifolia 3,28 0,40
Moringa oleifera 3,18 0,87
Morus alba 4,02 0,63
Calcium carbonate 4,75 0,35
Common salt (NaCl) 3,80 0,24
Distillery vinasse 3,00 0,10
Likert scale. 1. Completely inadequate, 2. Almost inadequate, 3. Modera-
tely adequate, 4. Almost adequate, 5. Completely adequate
Pastos y Forrajes, Vol. 41, No. 3, July-September, 164-169, 2018 / Local resources for sheep feeding	167
Protein could be covered mainly with white
leadtree, Mexican sunflower (T. diversifolia) and
mulberry (M. alba). The minerals would be covered
with the calcium carbonate sources, salt and dis-
tillery vinasse. The proposed list served as starting
point in the selection of the resources with higher
potential, in order to guarantee the stable growth
and development of the different sheep catego-
ries under the conditions of the locality. Similarly
to the above-explained case, the values of typical
deviation indicated that the dispersion around the
responses was low, which showed a high level of
consensus.
Regarding the selection of forage resources, the
first three species turned out to be the ones with the
best integral scoring (table 4). In the case of white
leadtree, most of the surveyed persons stated that it
adapts well to the soil and climate conditions of the
territory, coinciding with the results obtained by
Pérez-Corría et al. (2014) and Román-Miranda et
al. (2016), and Miranda et al. (2016), who concluded
that it is a species with excellent performance in
many parts of the world and shows good chemical
composition and nutritional value. The variable
yield in the dry season, one of those with higher
discriminating capacity in this research, was
qualified as sufficient, which coincides with the
reports by Bacab et al. (2013) and Reyes et al.
(2015) under tropical conditions, where the yields
were 2,47 and 2,04 t DM ha-1
per month in the dry
season, respectively.
Based on the resistance to the attack by pests
and diseases, the experts’ judgment was equally
positive; because, although this species is prefe-
rably attacked by phytophagous insects, such as
Heteropsylla cubana and Mormidea pictiventris,
there are enough organisms that act as biological
controls, for which they do not represent an important
threat for the sustainability of the systems in which
the tree is used (Alonso et al., 2005).
Another aspect considered as positive was its
yield without irrigation and fertilization, conditions
under which animal husbandry is developed in the
Las Tunas municipality. Thus, the weighting of the
criteria that were analyzed indicated that white
leadtree shows a remarkable integral value for its
utilization in local productive systems.
Sugarcane turned out to be the species of
higher integral value, due to its excellent dry
matter yield in low-input systems under tropical
conditions, in dry seasons; and due to its rusticity,
in spite of its nutritional deficiencies, which can be
solved in the proposed technological scheme. This
species, because of the above-mentioned attributes,
is considered by many researchers as strategic
par excellence (Martín, 2004). Similar results to
those of sugarcane were obtained in the evaluation
of the Pennisetum varieties, among which are:
Cenchrus purpureus x Pennisetum glaucum cv.
OM-22, Cenchrus purpureus vc. CT-169, elephant
grass and others. It should be emphasized that the
nutritional value of this species is higher than that
of sugarcane, and their yields in tons of dry matter
per hectare are very similar, factors that show their
real possibilities (Nava-Cabello et al., 2013).
In the other species (Mexican sunflower,
drumstick tree and mulberry) the results were low-
er, because they showed lower dry matter yield in
the dry season without irrigation and fertilization,
Table 4. Results of the evaluation of the forage resources.
Item L. leucocephala S. officinarum
Pennisetum
varieties
T. diversifolia M. oleifera M. alba
Adaptability to the
local edaphoclimatic
conditions
4,65 4,78 3,6 4,03 3,22 2,06
Production in the dry
season
4,31 5,00 5,00 2,30 2,43 2,08
Resistance to pests and
diseases
4,66 4,75 4,70 4,07 1,87 2,21
Production without irri-
gation and fertilization
4,20 4,90 4,85 1,86 2,04 2,21
Nutritional value 4,75 3,31 4,00 2,46 3,75 4,67
Integral value 4,51 4,54 4,43 2,94 2,66 2,64
168 	 Pastos y Forrajes, Vol. 41, No. 3, July-September, 164-169, 2018 / Javier Antonio Herrera-Toscano
compared with the previous ones. The reports by
Ruiz et al. (2012), Meza et al. (2016) and Pentón
et al. (2016) support this statement. The low nutri-
tional value of T. diversifolia was interesting, which
could have been related to its low dry matter con-
tent, of 10 and 12 % for the rainy and dry seasons,
respectively, according to Lezcano et al. (2012). In
M. oleifera the main deficiency was the suscepti-
bility to pests and diseases and to the invasion by
weeds in the establishment stage (Meza et al., 2016;
Padilla et al., 2017). Based on the criteria expressed
by the panel members, the integral evaluation of
these last three species was lower than three units,
for which they were placed (according to the scale)
in the categories «Completely inadequate» or «Al-
most inadequate»; this implied that they were not
chosen as potentially usable resources for sheep
production under the specific conditions of the Las
Tunas municipality.
In general, in all the non-forage resources an
adequate level of consensus was reached regarding
their favorable nutritional and economic feasibility
for feeding sheep. The qualitative evaluation of the
three non-forage resources that were selected by the
experts is shown in table 5.
The chosen calcium source was considered
as highly available, because it can be acquired by
farmers throughout the year, aspect that, combined
with the little quantity that is necessary in order to
cover the requirements of the animals, confers a
low cost to it. With regards to the other attributes,
it was considered that it shows sufficient nutritional
value with regards to the nutrient it contributes;
and its physical and chemical properties allow that,
under adequate conditions, the product could be
preserved for a long time period. The sum of the
above-mentioned criteria indicated, integrally, that
the calcium-carrying source is considered adequate.
Regarding the distillery vinasse, resource that
according to Vargas et al. (2014) is appropriate for
feeding different animal species, especially rumi-
nants, was equally evaluated as available in high
degree and low cost, because it is a residue from the
process of obtaining alcohol. Its nutritional value was
qualified as sufficient. On the other hand, its con-
servation is feasible and lasting as long as it is done
in airtight containers. Another important aspect,
but not studied in this research, is that the utiliza-
tion of distillery vinasse constitutes an alternative
to decrease environmental contamination (Rendón
et al., 2014). The above-stated fact allowed to con-
clude that such resource is appropriate for feeding
sheep in the territory.
The criteria that were expressed in the case of
common salt (NaCl) were also favorable; the least
positive aspect was cost, which could be lower
depending on the places where the product is pur-
chased. Although it is an available resource, it is
not ideal to supply the mineral deficiencies that
could appear in the animals, for which it would be
necessary to implement the use of multiple mineral
supplements that make a contribution of other im-
portant elements for the functioning of the animal
organism (Stewart, 2013).
It is concluded that there are between five and
six resources with potentialities for sheep produc-
tion in the Las Tunas municipality, among which
calcium carbonate as non-forage resource and L.
leucocephala as forage stand out.
Acknowledgements
The authors thank the workers of the provin-
cial delegation of the Ministry of Agriculture in Las
Tunas province, Republic of Cuba, for the logistic
support provided.
Bibliographic references
Alonso, J. Agro-ecological principles in Cuban tech-
nologies with legumes for animal production.
Cuban J. Agric. Sci. 50 (2):171-183, 2016.
Alonso, J.; Valenciaga, Nurys; Achang, G. & Mora, C.
Study of the arthropods associated with a silvopas-
toral system leucaena-guinea grass in different ex-
ploitation. Cuban J. Agric. Sci. 39 (2):217-221, 2005.
Table 5. Average and integral values of the application of the Likert scale in the evaluation of
the non-forage resources.
Item
Annual
availability
Total supply
cost
Nutritional
value
Conservation
time
Integral
value
Calcium carbonate 5,00 -1,40 4,35 5,00 3,23
Distillery vinasse 5,00 -2,20 4,36 4,86 3,00
Common salt (NaCl) 5,00 -2,10 4,55 5,00 3,11
Likert scale. 1. Completely inadequate, 2. Almost inadequate, 3. Moderately adequate, 4. Almost ade-
quate, 5. Completely adequate.
Pastos y Forrajes, Vol. 41, No. 3, July-September, 164-169, 2018 / Local resources for sheep feeding	169
Arece, J.; López, Y.; Molina, M. & Alpízar, A. Cam-
bios fisiopatológicos en ovinos Pelibuey en es-
tabulación, después de infestación experimental
con estrongílidos gastrointestinales. Pastos y Fo-
rrajes. 36 (3):354-359, 2013.
Bacab, P.; Madera, H.; Solorio, N.; Vera, F. & Marru-
fo, D. Los sistemas silvopastoriles intensivos con
Leucaena leucocephala: una opción para la ga-
nadería tropical. AIA. 17 (3):67-81, 2013.
Lezcano, Yohanka; Soca, Mildrey; Ojeda, F.; Roque,
E.; Fontes, Dayamí; Montejo, I. L. et al. Carac-
terización bromatológica de Tithonia diversifolia
(Hemsl.) A. Gray en dos etapas de su ciclo fisio-
lógico. Pastos y Forrajes. 35 (3):275-282, 2012.
Likert, R. A technique for the measurement of attitu-
des. Archives of Psychology. 22 (140):5-55, 1932.
Martín, P. La alimentación del ganado con caña de
azúcar y sus subproductos. San José de las Lajas,
Cuba: EDICA, 2004.
Meza-Carranco, Z.; Olivares-Sáenz, E.; Gutié-
rrez-Ornelas, E.; Bernal-Barragán, H.; Aran-
da-Ruiz, Juana; Vázquez-Alvarado, R. E. et al.
Crecimiento y producción de biomasa de morin-
ga (Moringa oleifera Lam.) bajo las condiciones
climáticas del Noreste de México. Tecnociencia
Chiguagua. 5 (3):143-153, 2016.
Nava-Cabello, J. J.; Gutiérrez-Ornelas, E.; Zava-
la-García, F.; Olivares-Sáenz, E.; Treviño, J. E.;
Bernal-Barragán, H. et al. Establecimiento del
pasto ‘CT-115’ (Pennisetum purpureum) en una
zona semiárida del noreste de México. Rev. Fito-
tec. Mex. 36 (3):239-244, 2013.
NRC. Nutrient requirements of beef cattle. Washing-
ton, D.C.: National Academy of Sciences, 2016.
ONEI. Sector agropecuario indicadores selecciona-
dos. La Habana: Oficina Nacional de Estadística
e Información. http://www.one.cu/publicacio-
nes/05agropecuario/ppalesindsector agrop/ppa-
les_inddic17.pdf. [18/03/2018], 2017.
Padilla, C.; Valenciaga, Nurys; Crespo, G.; González,
Daimarys & Rodríguez, Idalmis. Requerimien-
tos agronómicos de Moringa oleifera (Lam.) en sis-
temas ganaderos. LRRD. 29 (11). http://www.lrrd.
org/lrrd29/11/idal29218.html. [18/03/2018], 2017.
Partida-de-la-Peña, J. A.; Braña-Varela, D.; Jiménez-Se-
veriano, H.; Ríos-Rincón, F. G. & Buendía-Rodrí-
guez, G. Producción de carne ovina. Ajuchitlán,
México: Centro Nacional de Investigación Discipli-
naria en Fisiología y Mejoramiento Animal, 2013.
Pentón, Gertrudis; Rivera, R.; Martín, G. J.; Oropesa,
Katerine; Soto, F. & Cabrera, J. Intercalamiento
de Canavalia ensiformis (L.) inoculada con hon-
gos micorrízicos arbusculares para la producción
de forraje de Morus alba (L.). Pastos y Forrajes.
39 (1):33-40, 2016.
Perdomo, Ismary & Izquierdo, H. Visión prospectiva
de la sustentabilidad agroindustrial. Ninth LAC-
CEI Latin American and Caribbean Conference
(LACCEI’2011), Engineering for a Smart Planet,
Innovation, Information Technology and Com-
putational Tools for Sustainable Development.
Medellín, Colombia. http://www.laccei.org/
LACCEI2011-Medellin/published/IE050 _Per-
domo.pdf. [18/03/2018], 2011.
Pérez-Corría, Kirenia; Fonseca-Fuente, N.; Váz-
quez-Aldana, J.; Aldana-Gámez, Niurky &
Botello-León, A. Utilización de la Leucaena
leucocephala como alimento local para la oveja
Pelibuey durante la gestación. Revista Granma
Ciencia. 18 (1). http://www.grciencia.granma.
inf.cu/ 2014_18_n1_a5.html. [18/03/2018], 2014.
Rendón, M. E.; Noguera, R. R. & Posada, S. L. Vi-
naza de caña como aditivo acidificante en la ela-
boración de ensilaje de maíz (Zea mays). LRRD.
26 (1). http://www.lrrd.org/lrrd26/1/rend26007.
html. [18/03/2018], 2014.
Reyes, J. J.; Padilla, C.; Martín, P. C.; Gálvez, M.; Rey,
Sara; Noda, Aida et al. Consumo de forrajes tropica-
les por vacas lecheras, mestizas Siboney, manejadas
en sistemas de estabulación. AIA. 19 (1):31-40, 2015.
Román-Miranda, María L.; Palma-García, J. M.; Zo-
rrilla-Rios, J. M. & Mora-Santacruz, A. Produc-
ción de materia seca de Leucaena leucocephala
y vegetación herbácea en un banco de proteína
pastoreada por ovinos. Revista de Sistemas Ex-
perimentales. 3 (6):42-50, 2016.
Rowe, G. & Wright, G. The Delphi technique: past,
present, and future prospects: Introduction to the
special issue. Technol. Forecast. Soc. Change.
78 (9):1487-1490, 2011.
Ruiz, R. Producción de leche basada en pastos y forra-
jes tropicales. Rev. Ciencia y Tecnología Gana-
dera. 5 (1):1- 21, 2011.
Ruiz, T. E.; Febles, G. & Díaz, H. Distancia de plantación,
frecuencia y altura de corte en la producción de bio-
masa de Tithonia diversifolia colecta 10 durante el
año. Rev. cubana Cienc. agríc. 46 (4):423-426, 2012.
Solanas, A.; Salafranca, L.; Fauquet, J. & Núñez, M.
Estadística descriptiva en Ciencias del Compor-
tamiento. Madrid: Thompson, 2005.
Stewart, L. Mineral supplements for beef cattle:
University of Georgia. http://extension.uga.
edu/publications/files/pdf/B%20895_3.PDF.
[08/06/2018], 2013.
Vargas, S. A.; Noguera, R. R. & Posada, S. L. Inclu-
sión de vinaza de caña y su efecto sobre el perfil
de fermentación y calidad nutricional del ensila-
je de pasto maralfalfa (Pennissetum sp.). LRRD.
26(12).http://www.lrrd.org/lrrd26/12/varg26216.
html. [18/03/2018], 2014.
Velasco, J.; Pedraza, R.; Rivera, Verónica; Jara, R. &
Guapi, R. Análisis de unidades vacunas lecheras
ecuatorianas. Rev. Prod. Anim. 27 (3):1-7, 2015.
Received: January 15, 2018
Accepted: April 12, 2018
170 Pastos y Forrajes, Vol. 41, No. 3, July-September, 170-174, 2018 / Maritza Rizo-Alvarez
Scientific Paper
Influence of EcoMic®
and Pectimorf®
on the establishment
of Leucaena leucocephala (Lam.) de Wit. cv. Cunningham
Maritza Rizo-Alvarez, Dariel Morales-Querol, Tania Sánchez-Santana, Onel López-Vigoa,
Yuseika Olivera-Castro, Miguel A. Benítez-Alvarez and Fernando Ruz-Suárez
Estación Experimental de Pastos y Forrajes Indio Hatuey, Universidad de Matanzas, Ministerio de Educación Superior
Central España Republicana, CP 44280, Matanzas, Cuba
E-mail: maritza.rizo@ihatuey.cu
Abstract
TheobjectiveofthestudywastoevaluatetheinfluenceofthebiofertilizerEcoMic®
,thebioactiveproductPectimorf®
and their combination, on some morphobotanical variables during the establishment of Leucaena leucocephala(Lam.) cv.
Cunningham. For such purpose a randomized block design was used with three replicas, and the following treatments: T1:
thermal scarification (control), T2: inoculation with EcoMic®
, T3: imbibition in Pectimorf®
, T4: imbibition in Pectimorf®
+ inoculation with EcoMic®
. The variables height, number of branches and stem diameter were measured until the plants
were 12 months old. The best values of each variable were obtained when, after thermal scarification (T1), the seeds were
inoculated with EcoMic®
(T2) or imbibed in Pectimorf®
(T3), without significant differences between them; while the
control showed the lowest values. The height increased in T2 and T3 by 12 %, with regards to T1. It is concluded that
the imbibition in Pectimorf®
or the inoculation with EcoMic®
of the seeds from L. leucocephala cv. Cunningham, after
thermal scarification, improved the biological response of the plants during the establishment regarding their height,
number of branches and stem diameter. Hence they can be used indistinctly, in order to reduce such period in the animal
husbandry systems where it is used.
Keywords: height, scarification, inoculation, seeds
Introduction
Legumes perform functions of high agroeco-
logical relevance in silvopastoral systems (SPS),
because they improve the quality of the animal diet
and contribute nitrogen to the system, which im-
plies an advantage from the biological and economic
point of view; hence the interest in ensuring the es-
tablishment of these species in the systems.
Among the most widely used legumes in SPS is
Leucaena leucocephala (Lam.) de Wit., due to the
crude protein content of its foliage (Petit-Aldana
et al., 2010), to its capacity to regrow after pruning
or browsing and to be rapidly re-established after
biotic or abiotic stress, among other aspects;
nevertheless, this species shows difficulties for its
establishment due to the dormancy of its seeds.
In this sense, the establishment constitutes one
of the most vulnerable stages in the life cycle of
plants. In the case of the species with exclusively
sexual reproduction, persistence depends on the
establishment of new seedlings and on the longevity
of adult plants (Ramos-Font et al., 2015).
At present, the use of biofertilizers and
bioactive products constitutes a common practice
in agriculture to reduce the establishment period
of crops and, in turn, improve productivity; among
the most widely used for this purpose are Azofert®
,
EcoMic®
and Pectimorf®
(João et al., 2016).
The application of Glomus mosseae
significantly increased growth indicators (fresh
leaf biomass, fresh root biomass and height) in
L. leucocephala, with regards to the addition of
native mycorrhiza; and, also, mycorrhizal infection
exceeded 90 % of the roots (Cuesta et al., 2006). The
bioactive product Pectimorf®
has been validated in
sugarcane, rice, tomato and citrus fruits (Terrero,
2010) and also in sorghum (Pentón et al., 2011), but
in L. leucocephala it has been tested only under
nursery conditions (Bover-Felices et al., 2017).
That is why the objective of this research was to
evaluate the influence of the bioproducts EcoMic®
and Pectimorf®
on some morphobotanical variables,
during the establishment of L. leucocephala cv.
Cunningham.
Materials and Methods
Locality and geographical location. The trial
was conducted in 1,6 ha belonging to the ani-
mal production areas of the Pastures and Forages
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018
Revista pastos y forrajes vol41n3 2018

Weitere ähnliche Inhalte

Ähnlich wie Revista pastos y forrajes vol41n3 2018

Biotechnological strategies for the conservation of medicinal and ornamental ...
Biotechnological strategies for the conservation of medicinal and ornamental ...Biotechnological strategies for the conservation of medicinal and ornamental ...
Biotechnological strategies for the conservation of medicinal and ornamental ...
Marco Vinicio Robles Aguilar
 
03 agricultural information to the farmers in tamil nadu 2
03 agricultural information to the farmers in tamil nadu 203 agricultural information to the farmers in tamil nadu 2
03 agricultural information to the farmers in tamil nadu 2
prjpublications
 
03 agricultural information to the farmers in tamil nadu 2
03 agricultural information to the farmers in tamil nadu 203 agricultural information to the farmers in tamil nadu 2
03 agricultural information to the farmers in tamil nadu 2
IAEME Publication
 
Agricultural information to the farmers in
Agricultural information to the farmers inAgricultural information to the farmers in
Agricultural information to the farmers in
prjpublications
 
Nanotechnology An Innovative Approach for Smart Agriculture
Nanotechnology An Innovative Approach for Smart AgricultureNanotechnology An Innovative Approach for Smart Agriculture
Nanotechnology An Innovative Approach for Smart Agriculture
ijtsrd
 
Antibacterial Activity of Citrus Sinensis X against Pathogenic Bacterias
Antibacterial Activity of Citrus Sinensis X against Pathogenic BacteriasAntibacterial Activity of Citrus Sinensis X against Pathogenic Bacterias
Antibacterial Activity of Citrus Sinensis X against Pathogenic Bacterias
ijtsrd
 

Ähnlich wie Revista pastos y forrajes vol41n3 2018 (20)

Biotechnological strategies for the conservation of medicinal and ornamental ...
Biotechnological strategies for the conservation of medicinal and ornamental ...Biotechnological strategies for the conservation of medicinal and ornamental ...
Biotechnological strategies for the conservation of medicinal and ornamental ...
 
Stimulation of physiological parameters of Rosmarinus officinalis L. with the...
Stimulation of physiological parameters of Rosmarinus officinalis L. with the...Stimulation of physiological parameters of Rosmarinus officinalis L. with the...
Stimulation of physiological parameters of Rosmarinus officinalis L. with the...
 
Tuesday kn speech 0830 0855 room 2 haverkort
Tuesday kn speech 0830 0855 room 2 haverkortTuesday kn speech 0830 0855 room 2 haverkort
Tuesday kn speech 0830 0855 room 2 haverkort
 
Granada 2004
Granada 2004Granada 2004
Granada 2004
 
Granada 2004
Granada 2004Granada 2004
Granada 2004
 
03 agricultural information to the farmers in tamil nadu 2
03 agricultural information to the farmers in tamil nadu 203 agricultural information to the farmers in tamil nadu 2
03 agricultural information to the farmers in tamil nadu 2
 
03 agricultural information to the farmers in tamil nadu 2
03 agricultural information to the farmers in tamil nadu 203 agricultural information to the farmers in tamil nadu 2
03 agricultural information to the farmers in tamil nadu 2
 
Maps in pakistan
Maps in pakistanMaps in pakistan
Maps in pakistan
 
Agricultural information to the farmers in
Agricultural information to the farmers inAgricultural information to the farmers in
Agricultural information to the farmers in
 
Use of GREMAG® technology to improve seed germination and seedling survival
Use of GREMAG® technology to improve seed germination and seedling survivalUse of GREMAG® technology to improve seed germination and seedling survival
Use of GREMAG® technology to improve seed germination and seedling survival
 
Ecological engineering and biocontrol
Ecological engineering and biocontrolEcological engineering and biocontrol
Ecological engineering and biocontrol
 
Contribution of standards for developing networks, crop ontologies and a glob...
Contribution of standards for developing networks, crop ontologies and a glob...Contribution of standards for developing networks, crop ontologies and a glob...
Contribution of standards for developing networks, crop ontologies and a glob...
 
crop breeding.pdf
crop breeding.pdfcrop breeding.pdf
crop breeding.pdf
 
Biodivercities by 2030 : transforming cities with biodiversity
Biodivercities by 2030 : transforming cities with biodiversityBiodivercities by 2030 : transforming cities with biodiversity
Biodivercities by 2030 : transforming cities with biodiversity
 
Knowledge Level of Recommended Brinjal Production Technologies among the Trib...
Knowledge Level of Recommended Brinjal Production Technologies among the Trib...Knowledge Level of Recommended Brinjal Production Technologies among the Trib...
Knowledge Level of Recommended Brinjal Production Technologies among the Trib...
 
Economic Botany Ethnomedicine and Phytochemistry | NEP 2020 Book
Economic Botany Ethnomedicine and Phytochemistry | NEP 2020 BookEconomic Botany Ethnomedicine and Phytochemistry | NEP 2020 Book
Economic Botany Ethnomedicine and Phytochemistry | NEP 2020 Book
 
Nanotechnology An Innovative Approach for Smart Agriculture
Nanotechnology An Innovative Approach for Smart AgricultureNanotechnology An Innovative Approach for Smart Agriculture
Nanotechnology An Innovative Approach for Smart Agriculture
 
PlantBreedingandGenetics.ppt
PlantBreedingandGenetics.pptPlantBreedingandGenetics.ppt
PlantBreedingandGenetics.ppt
 
Antibacterial Activity of Citrus Sinensis X against Pathogenic Bacterias
Antibacterial Activity of Citrus Sinensis X against Pathogenic BacteriasAntibacterial Activity of Citrus Sinensis X against Pathogenic Bacterias
Antibacterial Activity of Citrus Sinensis X against Pathogenic Bacterias
 
1 brochure (agrotech 2017)
1 brochure (agrotech 2017)1 brochure (agrotech 2017)
1 brochure (agrotech 2017)
 

Kürzlich hochgeladen

Formation of low mass protostars and their circumstellar disks
Formation of low mass protostars and their circumstellar disksFormation of low mass protostars and their circumstellar disks
Formation of low mass protostars and their circumstellar disks
Sérgio Sacani
 
Presentation Vikram Lander by Vedansh Gupta.pptx
Presentation Vikram Lander by Vedansh Gupta.pptxPresentation Vikram Lander by Vedansh Gupta.pptx
Presentation Vikram Lander by Vedansh Gupta.pptx
gindu3009
 
Biopesticide (2).pptx .This slides helps to know the different types of biop...
Biopesticide (2).pptx  .This slides helps to know the different types of biop...Biopesticide (2).pptx  .This slides helps to know the different types of biop...
Biopesticide (2).pptx .This slides helps to know the different types of biop...
RohitNehra6
 
Discovery of an Accretion Streamer and a Slow Wide-angle Outflow around FUOri...
Discovery of an Accretion Streamer and a Slow Wide-angle Outflow around FUOri...Discovery of an Accretion Streamer and a Slow Wide-angle Outflow around FUOri...
Discovery of an Accretion Streamer and a Slow Wide-angle Outflow around FUOri...
Sérgio Sacani
 
The Philosophy of Science
The Philosophy of ScienceThe Philosophy of Science
The Philosophy of Science
University of Hertfordshire
 
Pests of cotton_Borer_Pests_Binomics_Dr.UPR.pdf
Pests of cotton_Borer_Pests_Binomics_Dr.UPR.pdfPests of cotton_Borer_Pests_Binomics_Dr.UPR.pdf
Pests of cotton_Borer_Pests_Binomics_Dr.UPR.pdf
PirithiRaju
 
DIFFERENCE IN BACK CROSS AND TEST CROSS
DIFFERENCE IN  BACK CROSS AND TEST CROSSDIFFERENCE IN  BACK CROSS AND TEST CROSS
DIFFERENCE IN BACK CROSS AND TEST CROSS
LeenakshiTyagi
 
CALL ON ➥8923113531 🔝Call Girls Kesar Bagh Lucknow best Night Fun service 🪡
CALL ON ➥8923113531 🔝Call Girls Kesar Bagh Lucknow best Night Fun service  🪡CALL ON ➥8923113531 🔝Call Girls Kesar Bagh Lucknow best Night Fun service  🪡
CALL ON ➥8923113531 🔝Call Girls Kesar Bagh Lucknow best Night Fun service 🪡
anilsa9823
 
Pests of mustard_Identification_Management_Dr.UPR.pdf
Pests of mustard_Identification_Management_Dr.UPR.pdfPests of mustard_Identification_Management_Dr.UPR.pdf
Pests of mustard_Identification_Management_Dr.UPR.pdf
PirithiRaju
 

Kürzlich hochgeladen (20)

Formation of low mass protostars and their circumstellar disks
Formation of low mass protostars and their circumstellar disksFormation of low mass protostars and their circumstellar disks
Formation of low mass protostars and their circumstellar disks
 
Lucknow 💋 Russian Call Girls Lucknow Finest Escorts Service 8923113531 Availa...
Lucknow 💋 Russian Call Girls Lucknow Finest Escorts Service 8923113531 Availa...Lucknow 💋 Russian Call Girls Lucknow Finest Escorts Service 8923113531 Availa...
Lucknow 💋 Russian Call Girls Lucknow Finest Escorts Service 8923113531 Availa...
 
GBSN - Microbiology (Unit 1)
GBSN - Microbiology (Unit 1)GBSN - Microbiology (Unit 1)
GBSN - Microbiology (Unit 1)
 
All-domain Anomaly Resolution Office U.S. Department of Defense (U) Case: “Eg...
All-domain Anomaly Resolution Office U.S. Department of Defense (U) Case: “Eg...All-domain Anomaly Resolution Office U.S. Department of Defense (U) Case: “Eg...
All-domain Anomaly Resolution Office U.S. Department of Defense (U) Case: “Eg...
 
Presentation Vikram Lander by Vedansh Gupta.pptx
Presentation Vikram Lander by Vedansh Gupta.pptxPresentation Vikram Lander by Vedansh Gupta.pptx
Presentation Vikram Lander by Vedansh Gupta.pptx
 
Biopesticide (2).pptx .This slides helps to know the different types of biop...
Biopesticide (2).pptx  .This slides helps to know the different types of biop...Biopesticide (2).pptx  .This slides helps to know the different types of biop...
Biopesticide (2).pptx .This slides helps to know the different types of biop...
 
VIRUSES structure and classification ppt by Dr.Prince C P
VIRUSES structure and classification ppt by Dr.Prince C PVIRUSES structure and classification ppt by Dr.Prince C P
VIRUSES structure and classification ppt by Dr.Prince C P
 
Discovery of an Accretion Streamer and a Slow Wide-angle Outflow around FUOri...
Discovery of an Accretion Streamer and a Slow Wide-angle Outflow around FUOri...Discovery of an Accretion Streamer and a Slow Wide-angle Outflow around FUOri...
Discovery of an Accretion Streamer and a Slow Wide-angle Outflow around FUOri...
 
Unlocking the Potential: Deep dive into ocean of Ceramic Magnets.pptx
Unlocking  the Potential: Deep dive into ocean of Ceramic Magnets.pptxUnlocking  the Potential: Deep dive into ocean of Ceramic Magnets.pptx
Unlocking the Potential: Deep dive into ocean of Ceramic Magnets.pptx
 
The Philosophy of Science
The Philosophy of ScienceThe Philosophy of Science
The Philosophy of Science
 
Pests of cotton_Borer_Pests_Binomics_Dr.UPR.pdf
Pests of cotton_Borer_Pests_Binomics_Dr.UPR.pdfPests of cotton_Borer_Pests_Binomics_Dr.UPR.pdf
Pests of cotton_Borer_Pests_Binomics_Dr.UPR.pdf
 
DIFFERENCE IN BACK CROSS AND TEST CROSS
DIFFERENCE IN  BACK CROSS AND TEST CROSSDIFFERENCE IN  BACK CROSS AND TEST CROSS
DIFFERENCE IN BACK CROSS AND TEST CROSS
 
Recombination DNA Technology (Nucleic Acid Hybridization )
Recombination DNA Technology (Nucleic Acid Hybridization )Recombination DNA Technology (Nucleic Acid Hybridization )
Recombination DNA Technology (Nucleic Acid Hybridization )
 
CALL ON ➥8923113531 🔝Call Girls Kesar Bagh Lucknow best Night Fun service 🪡
CALL ON ➥8923113531 🔝Call Girls Kesar Bagh Lucknow best Night Fun service  🪡CALL ON ➥8923113531 🔝Call Girls Kesar Bagh Lucknow best Night Fun service  🪡
CALL ON ➥8923113531 🔝Call Girls Kesar Bagh Lucknow best Night Fun service 🪡
 
GBSN - Biochemistry (Unit 1)
GBSN - Biochemistry (Unit 1)GBSN - Biochemistry (Unit 1)
GBSN - Biochemistry (Unit 1)
 
Chromatin Structure | EUCHROMATIN | HETEROCHROMATIN
Chromatin Structure | EUCHROMATIN | HETEROCHROMATINChromatin Structure | EUCHROMATIN | HETEROCHROMATIN
Chromatin Structure | EUCHROMATIN | HETEROCHROMATIN
 
Pests of mustard_Identification_Management_Dr.UPR.pdf
Pests of mustard_Identification_Management_Dr.UPR.pdfPests of mustard_Identification_Management_Dr.UPR.pdf
Pests of mustard_Identification_Management_Dr.UPR.pdf
 
Hire 💕 9907093804 Hooghly Call Girls Service Call Girls Agency
Hire 💕 9907093804 Hooghly Call Girls Service Call Girls AgencyHire 💕 9907093804 Hooghly Call Girls Service Call Girls Agency
Hire 💕 9907093804 Hooghly Call Girls Service Call Girls Agency
 
Raman spectroscopy.pptx M Pharm, M Sc, Advanced Spectral Analysis
Raman spectroscopy.pptx M Pharm, M Sc, Advanced Spectral AnalysisRaman spectroscopy.pptx M Pharm, M Sc, Advanced Spectral Analysis
Raman spectroscopy.pptx M Pharm, M Sc, Advanced Spectral Analysis
 
Botany krishna series 2nd semester Only Mcq type questions
Botany krishna series 2nd semester Only Mcq type questionsBotany krishna series 2nd semester Only Mcq type questions
Botany krishna series 2nd semester Only Mcq type questions
 

Revista pastos y forrajes vol41n3 2018

  • 1. Vol. 41, No. 3, July-September 2018 / NRS 0099 ISSN 0864-0394 (printed version) / ISSN 2078-8452 (online version) Quarterly journal. Official organ of the Ministry of Higher Education for pastures and forages | 1978 MISSION: to disseminate research results, development of technologies and innovation, related to the farming sector. EDITORIAL POLICY: publication designed for national and foreign researchers, professors of universities and institutes of technical educa- tion, farming entrepreneurs, organizations that promote rural development, decision-makers linked to the farming sector, livestock farmers and producers. Thejournalpublishesscientificpapers(research papers, review papers, short communications, technical notes, case studies, opinions and re- flections) which contribute to the knowledge of agricultural sciences and territorial rural deve- lopment. The publication of the contributions will depend on the approval of the Editorial Board, which will be supported on the opinion of the Scienti- fic Committee. The revision of the papers inclu- des a previous editorial evaluation, in which the following aspects are reviewed: 1) fulfillment of thejournalguidelines;2)novelty;3)qualityofthe title, abstract, keywords and references; as well as an academic evaluation made according to the double-blind peer-review system, to guarantee theimpartialityoftheprocess. Asgeneralrule,nomorethansixauthorsshould appear.Onlythosewhoparticipatedinsufficient degreetoassumethepublicresponsibilityofthe contentofthepaper,whocededthecontribution for its editorial reproduction, will be considered as authors. They are responsible for the results, criteria and opinions that appear in the papers. All contributions can be copied, used, disse- minated and publicly exposed, as long as the authorship and original source of their publi- cation (journal, editorial) are cited and they are not used for commercial purposes. TOPICS • Introduction, evaluation and dissemination of plant genetic resources related to the farming sector. • Agroecological management of production systems. • Sustainable livestock production. • Conservation of forages and agroindustrial byproducts for animal feeding. • Agroforestry for animal and agricultural production. • Integrated food and energy production systems in rural areas. • Utilization of alternative medicine in tropical farming systems. • Adaptation to and mitigation of the climate change in farming ecosystems. • Economic, managerial and social aspects of farming production. • Extension, agricultural innovation and technology transference. • Rural and local development. ESTACIÓN EXPERIMENTAL DE PASTOS Y FORRAJES INDIO HATUEY EDITORIAL COUNCIL Editor-in-Chief | Dra. Tania Sánchez Santana Assistant Editor | M.Sc. Nayda Armengol López Editor-Agricultural Sciences | Dra. Marta Hernández Chávez Editor-Veterinary Sciences | Dr. Javier Arece García EDITORIAL COMMITTEE Dr.C. Jesús Suárez Hernández | Dra.C. Maybe Campos Gómez Dra.C. Marlen Navarro Boulandier | Dra.C. Maykelis Díaz Solares Dr.C. Jesús M. Iglesias Gómez | Dr.C. Hilda B. Wencomo Cárdenas Dr.C. Anesio R. Mesa Sardiñas | Dr.C. Luis A. Hernández Olivera Dra.C. Hilda C. Machado Martínez | Dr.C. Osmel Alonso Amaro Dr.C. Giraldo J. Martín Martín | Dra.C. Odalys C. Toral Pérez Dr.C. Luis Lamela López | M.Sc. Onel López Vigoa Dra.C. Mildrey Soca Pérez | M.Sc. Milagros de la C. Milera Rodríguez Dr.C. Félix Ojeda García | M.Sc. Yolai Noda Leyva Dr.C. Gertrudis Pentón Fernández | M.Sc. Juan C. Lezcano Fleires SCIENTIFIC COMMITTEE Dra. Sonia Jardines González | Universidad de Matanzas, Cuba Dra. Angela Borroto Pérez | UNIVERSIDAD DE CIEGO DE ÁVILA, Cuba Dr. Aníbal E. Fernández Mayer | Instituto Nacional de Tecnología Agropecuaria, Argentina Dr. Argemiro Sanavria | Universidad Federal Rural de Rio de Janeiro, Brasil Dr. Tyrone J. Clavero Cepeda | Universidad de Zulia, Venezuela Dr. José M. Palma García | Universidad de Colima, México Dr. Oscar Romero Cruz | Universidad de Granma, Cuba Dr. Carlos J. Bécquer Granados | Estación Experimental de Pastos y Forrajes de Sancti SpÍritus, Cuba Dr. Rodobaldo Ortíz Pérez | Instituto NACIONAL de Ciencias agrícolas, CUBA Dr. Pedro C. Martín Méndez | Instituto de Ciencia Animal, Cuba Dr. Pedro P. del Pozo Rodríguez | Universidad Agraria de La Habana, Cuba Dr. Redimio Pedraza Olivera | Universidad de Camagüey, Cuba Dr. Rafael S. Herrera García | Instituto de Ciencia Animal, Cuba Dr. Pedro José González Cañizares | Instituto Nacional de ciencias agrícolas, CUBA Dr. Ángel Arturo Santana Pérez | Universidad de Granma, Cuba SUPPORT COMMITTEE Editing and correction M.Sc. Alicia Ojeda González Design and editing Dailys Rubido González Miresleidys Rodríguez Rizo Translation B.A. Nidia Amador Domínguez Cover design B.A. Israel de Jesús Zaldívar Pedroso
  • 2. Vol. 41, No. 3, July-September / 2018 Revista Trimestral. Órgano oficial del Ministerio de Educación Superior para el área de los pastos y forrajes Quarterly journal. Official organ of the Ministry of Higher Education for pastures and forages PASTURE AND FORAGE RESEARCH STATION INDIO HATUEY INDEX SciELO SciELO Citation Index Web of Science Electronic Journals Index (SJSU) REDALYC CAB Abstracts AGRIS (FAO) PERIODICA (México) BIBLAT (México) Open Science Directory REGISTER DOAJ Fuente académica de EBSCO LATINDEX Cubaciencia Actualidad Iberoamericana (Chile) PERI (Brasil) TROPAG (Holanda) ORTON (Costa Rica) BAC (Colombia) AGROSI (México) EMBRAPA (Brasil) Forrajes Tropicales (CIAT) Ulrich’s International Periodicals Directory Catálogo de Publicaciones Seriadas Cubanas Catálogo colectivo COPAC(ReinoUnido) Catálogo colectivo SUDOC (Francia) Catálogo colectivo ZDB (Alemania) Papers to be considered by the editorial committee, please contact: Dra.C. Tania Sánchez Santana / tania@ihatuey.cu © 2018. Estación Experimental de Pastos y Forrajes Indio Hatuey Central España Republicana, CP 44280, Matanzas, Cuba  (53) (45) 571225 / 571235 http://www.ihatuey.cu Online http: //payfo.ihatuey.cu http: //scielo.sld.cu CONTENT | REVIEW paper | Economic appraisal of the environment and its application in the Cuban animal husbandry sector NadiaBáez-Quiñones...................................................................................................149 | scientific paper | Selection of accessions of Urochloa brizantha (Hochst. ex A. Rich.) R. D. Webster for acid soils Yuseika Olivera-Castro, Onel López-Vigoa, Pedro Pablo del Pozo-Rodríguez, Lisset Castañeda-Pimienta, Agustín Olmedo-Juárez, Javier Arece-García and Rolando Rojo-Rubio..................................................................................158 | scientific paper | Selection of local resources for sheep feeding in the Las Tunas municipality, Cuba Javier Antonio Herrera-Toscano and Oscar Carmenate-Figueredo.......................164 | scientific paper | Influence of EcoMic® and Pectimorf® on the establishment of Leucaena leucocephala (Lam.) de Wit. cv. Cunningham Maritza Rizo-Alvarez, Dariel Morales-Querol, Tania Sánchez-Santana, Onel López-Vigoa, Yuseika Olivera-Castro, Miguel A. Benítez-Alvarez and Fernando Ruz-Suárez.......................................................................................170 | scientific paper | Inoculation of Canavalia ensiformis with arbuscular mycorrhizal fungi in the establishment stage Lázaro J. Ojeda-Quintana, Pedro J. González-Cañizares, Ramón Rivera-Espinosa, Eduardo Furrazola-Gómez, Juan J de la Rosa-Capote, Martha E. Hernández- Vilches, Yudeimy I. Rodríguez-González and Consuelo Hernández- Rodríguez...........................................................................................................175 | scientific paper | Productivity of Tifton 85 bermudagrass, inoculated with Bradyrhizobium sp. and Trichoderma harzianum, subject to agricultural drought stress Carlos José Bécquer-Granados, Urbano Ávila-Cordoví, José Ángel Nápoles-Gómez, Yaldreisy Galdo-Rodríguez, María Hernández-Obregón, Ivón Muir-Rodríguez, Orquidia Álvarez-Figueroa and Fernando Medinilla-Nápoles.........................182 | scientific paper | Resistance to penetration in a Chromic Vertisol with natural pasture Juan Alejandro Villazón-Gómez, George Martín-Gutiérrez, Yakelín Cobo-Vidal and Daniel Hernández-Rojas...........................................................................188 | scientific paper | Evaluation of the structure, functioning and performance of mixed agriculture-animal farming agrosystems Katia Bover-Felices, Eliel González-García, Fabien Stark, Charles-Henri Moulin and Jesús Suárez Hernández..........................................................................193 | scientific paper | Animal husbandry-forestry integration as alternative for family agriculture in a region of Uruguay Liber Manuel Acosta-Casella, Virginia Courdin-Máximo and Pedro Raúl Arbeletche-Favat...............................................................................................203 | scientific paper | Effect of different proportions of Moringa oleifera:Cenchrus purpureus on voluntary intake and nitrogen balance Delfín Gutiérrez-González, Nelson N. González-González, Arabel Elías-Iglesias, Roberto García-López and Osvaldo R. Tuero-Martínez.............................211
  • 3. Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Economic appraisal of the environment 149 Economic appraisal of the environment and its application in the Cuban animal husbandry sector Nadia Báez-Quiñones Instituto de Ciencia Animal, Apartado postal 24, San José de las Lajas, Mayabeque, Cuba E-mail: nadia@ica.co.cu Abstract The objective of this paper is to present the environmental economic appraisal methods and their application in the Cuban animal husbandry sector. For such purpose the Total Economic Value theory is taken as reference, and the most widely used methods and techniques are identified according to the adopted concept of value. A group of studies about the application of the environmental economic in Cuba is reviewed, and four cases of interest in the animal husbandry sector are analyzed. The topic of the application of the environmental economic appraisal in the animal husbandry sector is not very frequent in scientific literature. This is only limited to determining the main environmental functions and the magnitude of their impact, but their economic value is not taken into consideration. It is concluded that the Total Economic Value theory is one of the most widely used for the economic appraisal of the environment. In addition, there are diverse highly useful techniques for economically appraising the environmental impact of animal husbandry in Cuba. Keywords: animal husbandry, environmental impact, economic viability Review paper Introduction Some of the main environmental problems that exist in Cuba are: soil degradation and deforesta- tion; loss of biodiversity; contamination; as well as the deficiencies and difficulties regarding manage- ment, water availability and quality, and their im- pacts on climate change (CITMA, 2016). These problems have incidence on the agricultural sector and are often caused by it; in which the excessive exploitation of animal husbandry systems plays an important role. Animal production significantly contributes to the emissions of greenhouse gases (GHG). The main emission sources in the sector are enteric fermentation, manure management and deposit of feces and urine in the pasturelands (Wilkes et al., 2017). In most cases, the environmental problems, or the benefits generated by ecosystems, are not con- sidered in economic accountancy systems (Biondi, 2016). This constitutes one of the main causes of the increasing overexploitation and deterioration of natural resources (Miranda et al., 2007). For such reason, Miranda (2002) stated that, when a new technology is going to be incorporated, the costs that, at long term, can be generated by the environmental deterioration caused by the assimilation of a new technology, should be taken into consideration, and not only the investment costs and their recovery period. In recent years, in Cuba there has been pro- gressive advance in the economic appraisal of the environment, mainly in protected areas and in the tourism and forestry sectors (Machín and Hernández, 2009; Hernández, 2011; Rodríguez et al., 2011; Domínguez-Junco et al., 2012; Labrada, 2013; Poey and García 2013; Zequeira et al., 2013; Rodríguez-Córdova et al., 2017). This proves the need and importance of the use of economic ap- praisal, so that it allows the practice of effective and economically efficient policies for the sustainable management of species and ecosystems (Machín and Casas, 2006). The objective of this paper is to present the en- vironmental economic appraisal methods and their application in the Cuban animal husbandry sector. Economic appraisal of the environment and Total Economic Value (TEV) The relation between growth and environment has gained great strength for economics researchers in recent years, mainly because of the increasing degradation of natural resources –which accompa- nies the increase of production at world scale– and to the need of quantifying the elements that com- pose ecosystems (Figueroa, 2013).
  • 4. 150 Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Nadia Báez-Quiñones Although some natural resources have a price in the market, it does not contemplate, in most cases, the wide variety of functions that add a higher economic value, generally disesteemed when making decisions related to their management. This value lies on the fact that natural resources and the environment fulfill at least four functions, positively perceived by society (Rangel et al., 2013). They are: • they are part of the function of production of a large quantity of economic goods and services; • they perform environmental functions, whose services are demanded by society; • they act as receptors of diverse types of residues and wastes; • they constitute an integrated system that provi- des the elemental means to sustain all kinds of life. The environmental economic appraisal consti- tutes an important tool for the adequate definition of the instruments of environmental policy. It can be defined as a set of techniques and methods which allow to measure the expectations of benefits and costs derived from actions, such as the use of an environmental asset, the performance of an envi- ronmental improvement or the generation of envi- ronmental damage (Azqueta, 1994). In the last decades, the environmental appraisal methodologies have had a broad development in the measurement of those aspects that were previous- ly classified as intangible and which at present can be measured in monetary terms (Hernández et al., 2013). The economic value of environmental goods and services is a very controversial topic in literature. Cerda (2003) states that it is important to emphasize that neither «the environment» nor «the life» are being appraised, as many people assume, but that the preference of people in the face of changes in the conditions of the environment and with regards to changes in the risks they face are appraised. In this sense, Hernández et al. (2010) suggested that economists should appreciate the value of ecosystems far beyond their contribution in raw materials and tangible products. From these ideas, the Total Economic Value (TEV) theory is proposed, which has been used by such authors as Ferro et al. (2016) and Almeida et al. (2018), as the approach to be taken into consideration for determining the economic value of an ecosystem. The TEV approach states that any good or service is composed by several attributes, some of which are tangible and easily measurable, while others can be more difficult to quantify. However, the total value is the sum of all these components and not only of those that can be easily measured. The limits and terminology for the TEV components slightly vary between one specialist and the other, but it generally includes value of use and value of non-use (Dixon and Pagiola, 1998). Besides, each one can be subdivided into additional categories (table 1). The value of use is formed by the value of direct use, which refers to the resource that is obtained by the development of certain activity; the value of indirect use, including those benefits that are derived from the functioning of ecosystems; and the value of choice, which refers to the possibility of using, or not, the environmental resource in the future. On the other hand, the value of non-use is subdivided into legacy value and existence value. The former refers to the possibility that the resource be consumed by future generations, and the latter, to the knowledge of the existence of a certain environmental asset; which, although due to moral conviction, seems valuable (Ferro et al., 2016). Table 1. Categories of the economic value ascribable to natural resources. Value of use Value of non-use Direct use Indirect use Choice value Legacy value Existence value Directly consumable values Benefits derived from ecosystem functions Future direct and indirect values Value of the resources for future generations Value of knowing that there still is an environment component Milk, meat, biomass, recreation, health Control of: climate, soils, nutrient recycling Bioprospection, conservation of habitats Conservation of habitats in the face of irreversible changes Habitat, species, genes, ecosystems Source: modified from Pearce and Morán (1994).
  • 5. Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / economic appraisal of the environment 151 Summarizing, the TeV theory is one of the most used in scientific literature, because it allows to appraise the environmental goods and services taking into consideration the highest possible quan- tity of the values they have. Thus, a monetary value is assigned to such resources, which, in spite of not being their real value, offers the possibility of in- cluding them in the accountancy systems at the dif- ferent levels. Nevertheless, it is criticized by some experts due to its subjective character, because the assignation of values depends, to a large extent, on the specialist’s point of view. Most utilized methods and techniques for the economic appraisal of the environment environmental appraisal techniques intend to obtain the willingness to pay for a positive change in an environmental good or the willingness to accept a compensation for a negative change. The environmental economy is focused on two basic areas: the field of appraisal (impact and environ- mental cost studies), for which it uses a series of instruments and methodologies such as benefit/ cost studies, contingent appraisal and disposition to pay, among others; and the field of environmental policy and management, in which it proposes di- verse instruments of environmental fiscal policy, constitution of secondary markets, environmental policies and management (Raffo, 2015). It should be clarified that this review adopts the position of environmental economy, emphasis is not made on the precepts of ecological economy1 . The different values that are assigned to en- vironmental goods and services can be excluding, alternate or competitive, for which it is not always possible to consider that the total economic value associated with an environmental good or service is the simple sum of the different values of use and non-use (Leal, 2005). In this regard, there are di- verse appraisal methods and techniques, which are classified according to the concept of value that is adopted or the level of availability of the required information. The most common classifications in literature are: methods of declared preferences or revealed preferences (Maldonado and Cuervo, 2016); and direct or indirect methods (Pardo and Sanjinés, 2014). The most utilized techniques ac- cording to the concept of value are shown in figure 1, and are explained below. 1 It considers economy as a subsystem of the ecosphere, and assumes that mankind and its economy must be subject to the limits imposed by the biophysical restrictions set by ecosystems, source of the goods and services that feed them (Goodland and Daly, 1996).
  • 6. 152 Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Nadia Báez-Quiñones • Direct market values or available market prices. This technique is used in economies where there are well defined markets, in which the practice is followed of assigning a monetary value to the biological resource in question, under the assumption that such price reasonably describes the value it has, being understood that such concept goes beyond being only value of use (Guillén et al., 2007). • Method of opportunity costs. It is used when there are two or more choices of use of the environmental area. The opportunity cost of utilizing resources, in a certain way, is the most highly valued alternative in which these resources could have been invested and to which the society would have to renounce when the resources are used in another specific way (Zequeira et al., 2016). For example, the decision of using a vegetative area to start agricultural production against the alternative of opening a national park; if opening the park is chosen, the economic appraisal is given by the market prices when weighing the agricultural losses by their price. • Method of the changes in productivity. This me- thod attempts to estimate economically the envi- ronmental impact on a natural resource, through the appraisal of the effect this impact generates on production, the cost or the profits genera- ted by the other good which does have market. Such effect on the production of another good or service implies a change in people’s welfare. Through the appraisal of such change in welfare an approximation of the value of that environ- mental impact is obtained. An example of the application of the method can be the case of water quality and agricultural production. If the water quality decreases due to contamination, there will be a decrease in yields, which would be translated into higher production costs and, thus, a higher price of the product. This ultima- tely affects people, who will have to pay a higher price for the product, and thus its usefulness de- creases (MINAM, 2015). • Method of replacement costs. The replacement cost technique is based on the measurement of the costs that are incurred by replacing productive assets damaged by the disturbance of natural resources and ecosystem processes. For example, the cost of acid deposition related to air contamination in urban areas could be approached through the cost of replacement or restoration of the damaged infrastructure (Murillo and González, 2017). • Method of hedonic prices. The environmental quality affects the price people are willing to pay for certain goods or services. The method is based on the fact that many of the prices ob- served for the goods are prices for a set of at- tributes. This approach estimates the welfare derived from the environmental characteristics that influence directly the market prices of a spe- cific good. The most used variants are based on the price of properties and on the salaries (Díaz, 2017). • Travel cost method (TCM). It is based on the costs that are incurred by the visitor to a place to enjoy the recreation ecosystemic services pro- vided by a certain site. For example, in the case of natural parks, people enjoy the natural areas, but, to do that, they need to consume some pri- vate goods to travel to the site, and it is on those private expenses this method is based in order to determine an approximation to the value of the natural resource (Tomio and Ullrich, 2015). • Method of avoided costs (MAC). It estimates the costs which are incurred to prevent the damage caused by environmental degradation. This technique examines the expenses in order to determine the importance people assign to the impacts on the environment and health. The fundamental premise is that an individual perception of the cost imposed by damage is related to what the person pays to prevent it from occurring (Ripka de Almeida et al., 2018). • Method of contingent appraisal or of construc- ted markets. The method consists in the design of a hypothetic market, presented to the indivi- dual through a questionnaire, which is later used to simulate several markets in which values are assigned to the resources. The intention is to know the preferences of society on environmen- tal quality, and how much it will be willing to pay for not being deprived of the benefits of ha- ving such resources (Pérez-Torres, 2016). • Model of economic evaluation of the eco-friend- ly productive activity. This model uses three fundamental criteria to define a practice or pro- duct as eco-friendly (Barzev et al., 2013). They are: 1) competitiveness: it is the technology used in each economic alternative; 2) environmen- tal measures: it is the quantification of negative impacts (translated into costs) and the measu- res proposed to mitigate them, thus generating social benefits; and 3) economic viability: it is the application of the costs-benefits technique to
  • 7. Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Economic appraisal of the environment 153 compare costs versus benefits of the economic activity (including environmental costs and be- nefits). The environmental measures in the model represent the different costs that are incurred to prevent negative impacts on the environment. In addition, the additional incomes or profits generated by adopting those mitigation measures of the negative impacts, are quantified. The methods and techniques that are used in literature vary from one author to the other, and their election depends fundamentally on the pursued objective. It is very common to find several techniquesappliedinthesameresearch,whichallows to appraise each of the environmental functions of the goods and services of the area under study. Application in the Cuban animal husbandry sector In the Cuban animal husbandry activity, the field of the instruments of environmental policy and management is very limited because there is not a clearly defined economic-environmental policy in which compensation systems are used for good practices, such as payments for environmental services, and there is not a market of carbon certificates either. These compensation systems have been applied in several countries of America by such authors as Murgueitio et al. (2013), Zapata et al. (2015), Artunduaga and Escobar (2016), with very good results in the achievement of the sustainable management of the activity. There are several studies in the field of environ- mental economic appraisal which have been con- ducted in Cuba in recent years (table 2). Among the reviewed papers the ones that have as study object the territories and protected areas stand out. In the first case are the reports and doctoral and master of science theses which were elaborated within the framework of the UNDP/GEF Sabana-Camagüey Project. They were focused on several ecosystems of the zone, where the studies were aimed at ap- praising in economic terms the natural resources of national parks, mangroves and basins, which in most cases are dedicated to tourism development. In the case of the animal husbandry sector, four cases of interest were found in the last years in which the economic appraisal of the environ- mental impact was applied. This does not mean that they are the only ones, because in several of the cited works (Rangel et al., 2013; Ferro et al., 2016; Zequeira et al., 2016) the function of animal husbandry as one of the values of direct use in the studied systems was evaluated, although this sector was not the protagonist (table 2). The study conducted by Miranda et al. (2007) was focused on the economic appraisal of the car- bon sequestered in a farm with natural pasture and another one converted in a silvopastoral system (SPS), with 11 years of exploitation. The estimated amount of stored carbon per hectare in the systems was approximately valued in 1 590 dollars (USD). From this amount, 80 % was contributed by the SPS, which surpassed the natural pasture, and the Table 2. Studies of environmental economic appraisal conducted in Cuba, by sector. Sector Studies Authors Animal husbandry 4 Miranda et al. (2007, 2008); De la Cruz et al. (2013); Manzano et al. (2013); Valdés et al. (2013) Mining 1 Reynaldo and Guardado (2017) Tourism 4 Figueredo et al. (2013); Gutiérrez and Soulary (2013); Labrada (2013); Zequeira et al. (2013) Protected areas 5 Machín and Hernández (2009); Hernández (2011); Villarreal and Unger (2012); Delgado (2013); Rodríguez et al. (2017) Forestry 3 Rodríguez et al. (2011); Domínguez-Junco et al. (2012); Poey and García (2013) Basins 3 Rangel et al. (2013); Ferro et al. (2016); Zequeira et al. (2016) Fishery 2 Bucarano et al. (2013); Betanzos-Vega et al. (2014) Entrepreneurial 1 Cañizares-Roig and Martín-García (2016) Territorial 8 PNUD (2007) UNDP/GEF Sabana-Camagüey Project Source: elaborated by the author.
  • 8. 154 Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Nadia Báez-Quiñones high economic contribution of the system with trees was proven. For its estimation the direct method of market prices was used, and the carbon mass held was multiplied by its price in the market of carbon certificates. Miranda et al. (2008) completed the study with the economic appraisal of how much the biodiversity function represented in animal husbandry ecosystems. For such purpose the technique of avoided costs due to weed control, assigned to that environmental service, was used. In both study cases it was concluded that the estimation of environmental benefits, along with the economic incomes by way of milk production, constitutes a valorization of animal husbandry ecosystems. De la Cruz et al. (2013) evaluated the imple- mentation of the management plan of the buffalo stock with biodiversity conservation techniques. For such purpose two dairy farms with sustainable management and two with traditional management were compared. In spite of the costs of the dairy farms with sustainable management being higher, because they internalized the environmental costs (reforestation of the area for the utilization of liv- ing fences, protection against fires, maintenance of channels and dams, among others), in them high positive impacts were generated (decrease of soil erosion, utilization of trees for animal feeding and shade, production of fruit and firewood for sale, among others). From the economic point of view, this area showed higher incomes in all the periods. In the study all the additional incomes which would be obtained from sustainable management were not taken into consideration; thus, the positive economic impacts (externalities) were not really quantified, although it constitutes an approximation to what should be done regarding the economic appraisal of environmental services. Valdés et al. (2013) studied the economic fea- sibility of constructing a plant of pig waste treat- ment with anaerobic digestion technology. For such purpose, the benefit-cost ratio and the investment recovery period were determined. In the determi- nation of the incomes and costs the environmental aspects were taken into consideration. The savings by way of diesel substitution and contribution of nu- trients from the substitution of chemical fertilization by fertilization with biosolid, were included. During the bibliographic review, it could be ob- served that the environmental economic appraisal in the animal husbandry sector is not very frequent in Cuba. This is only limited to determining the main environmental functions and the magnitude of their impact, but their economic value is not con- sidered. However, work has been started to be done in order to determine the economic impact of the animal husbandry activity on the environment, not only from the negative point of view, but also from the large variety of environmental services and goods that are derived from it. Conclusions The Total Economic Value theory is one of the most used for the economic appraisal of the environment. In addition, there are diverse highly useful techniques to appraise economically the environmental impact of animal husbandry in Cuba, and their election depends on the objective pursued by the research. In the same study several techniques can be used in order to determine the economic values of each of the environmental functions identified in the ecosystem. In recent years, the studies of environmental economic appraisal have been increased in the Cuban animal husbandry sector; nevertheless, they are not sufficient, if the role played by animal husbandry in the intensification of environmental problems and the potentialities it has for mitigating them is taken into consideration. Bibliographic references Almeida, A. R. de; Silva, C. L. da & Hernández-San- toyo, A. Métodos de valoración económica ambiental: instrumentos para el desarrollo de políticas ambientales. Universidad y Sociedad. 10 (3):134-141, 2018. Artunduaga, L. & Escobar, Y. Identificación del pago por servicios ambientales captura de carbono en sistemas ganaderos de la microcuenca La Mono en el municipio de Belén de los Andaquíes. Tesis en opción al grado de Maestría en Tributación. Florencia, Colombia: Universidad de la Amazo- nia, 2016. Azqueta, D. Valoración económica de la calidad am- biental. Madrid: McGraw-Hill, 1994. Barzev, R.; Cruz, D. M. de la; Báez, C. M.; Méndez, L.; León, O. & Manzano, A., et al. Potenciando la conservación de la biodiversidad mediante la evaluación económica y ambientalmente sosteni- ble de actividades productivas en el ecosistema Sabana-Camagüey, Cuba. La Habana: Agencia Medio Ambiente, 2013. Betanzos-Vega, A.; Rivero-Suárez, Sarah & Ma- zón-Suástegui, J. M. Factibilidad económi- co-ambiental para el cultivo sostenible de ostión
  • 9. Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Economic appraisal of the environment 155 de mangle Crassostrea rhizophorae (Güilding, 1828), en Cuba. Lat. Am. J. Aquat. Res. 42 (5):1148- 1158, 2014. Biondi, M. En busca de aportes teóricos para lograr la identidad de la contabilidad ambiental. Contabi- lidad y Auditoría. 32 (16):12-29, 2016. Bucarano, L.; Rodríguez, E.; González, O. & Castillo, E. Práctica de producción sostenible en la activi- dad pesquera. Experiencia piloto de la creación de una granja demostrativa y experimental para el cultivo de esponjas comerciales: Manejo sos- tenible de recursos pesqueros al centro del ar- chipiélago Sabana-Camagüey. En: Potenciando la conservación de la biodiversidad mediante la evaluación económica y ambientalmente sosteni- ble de actividades productivas en el ecosistema Sabana Camagüey, Cuba. Sancti Spíritus, Cuba: Agencia de Medio Ambiente. p. 49-56, 2013. Cañizares-Roig, Marlene & Martín-García, Marili. Procedimiento para cuantificar los costos de las actividades ambientales en la gestión de sosteni- bilidad del recurso agua potable. Cofín Habana. 11 (2):160-183, 2016. Cerda, A. Valoración económica del medio ambiente. II Curso Instrumentos de Mercado y Fuentes de Financiamiento para el Desarrollo Sostenible. Cartagena de Indias, Colombia, 2003. CITMA. Estrategia Ambiental Nacional 2016/2020. Informe del Ministerio de Ciencia, Tecnología y Medio Ambiente. La Habana: CITMA, 2016. De la Cruz, D. M.; Báez, C. M.; Méndez, L. & León, O. Manejo sostenible de la masa bufalina en la Reserva de la Biosfera Buenavista. En: Po- tenciando la conservación de la biodiversidad mediante la evaluación económica y ambiental- mente sostenible de actividades productivas en el ecosistema Sabana Camagüey, Cuba. Sancti Spíritus, Cuba: Agencia de Medio Ambiente. p. 19-28, 2013. Delgado, L. Enfoques económicos-financieros del Sis- tema Nacional de Áreas Protegidas de Cuba. En: Potenciando la conservación de la biodiversidad mediante la evaluación económica y ambiental- mente sostenible de actividades productivas en el ecosistema Sabana Camagüey, Cuba. Sancti Spíritus, Cuba: Agencia de Medio Ambiente. p. 68-78, 2013. Díaz, C. Aspectos conceptuales y metodológicos de la Guía para la aplicación de la valoración eco- nómica ambiental. Bogotá: Oficina de Negocios Verdes y Sostenibles, MINIAMBIENTE, 2017. Dixon, J. & Pagiola, S. Análisis económico y evalua- ción ambiental. In: Environmental Assessment Sourcebook. p. 1-17, 1998. Domínguez-Junco, O.; Betancourt-Figueras, Y.; Ro- dríguez-Crespo, G.; González-Montpellier, L. E. & Benítez-Menéndez, O. Fundamentación polí- tica socioeconómica del cobro de los servicios ecosistémicos forestales en Cuba. AIA 14 (1):49- 60, 2012. Ferro, H.; Gómez, G. & Herrera, P. Valoración eco- nómica de los impactos ambientales seleccio- nados del cuabal en la Reserva Ecológica La Coca, La Habana, Cuba. Acta Botánica Cubana 215 (1):24-37, 2016. Figueredo, T.; Pina, F. & Angulo, J. Aportes de bie- nes y servicios ambientales del Parque Nacional Jardines de la Reina (PNJR) a la economía del sector. En: Potenciando la conservación de la biodiversidad mediante la evaluación económi- ca y ambientalmente sostenible de actividades productivas en el ecosistema Sabana Camagüey, Cuba. Sancti Spíritus, Cuba: Agencia de Medio Ambiente. p. 85-105, 2013. Figueroa, A. Crecimiento económico y medio am- biente. Revista CEPAL. 109:20-42, 2013. Goodland, R. & Daly, H. Environmental sustainabi- lity: universal and non-negotiable. Ecol. appl. 6 (4):1002-1017, 1996. Guillén, W. E.; Guzmán, C. J. & Plasencia, M. G. Eva- luación de la implementación de pago por servi- cios ambientales en El Salvador. Tesis en opción al grado de Licenciatura en Economía. Antiguo Cuscatlán, El Salvador: Universidad Centroame- ricana José Simeón Cañas, 2007. Gutiérrez, G. & Soulary, D. Valoración de los servi- cios ambientales de los ecosistemas: Ecosistema Sabana-Camagüey. Caso: Laguna La Redonda. En: Potenciando la conservación de la biodi- versidad mediante la evaluación económica y ambientalmente sostenible de actividades pro- ductivas en el ecosistema Sabana Camagüey, Cuba. Sancti Spíritus, Cuba: Agencia de Medio Ambiente. p. 106-118, 2013. Hernández, A. Bases teórico metodológicas para la valoración económica de bienes y servicios am- bientales a partir de técnicas de decisión mul- ticriterio. Estudio de caso: Parque Nacional Viñales, Pinar del Río, República de Cuba. Tesis en opción al grado científico de Doctor. Alicante, España: Universidad de Alicante, 2011. Hernández, A.; Casas, M.; Leon, M. A.; Caballero, R. & Pérez, V. E. La Ciencia Económica y el Medio Ambiente: un aporte desde la valoración económica ambiental. Rev. Paran. Desenvolv. 34 (125):25-38, 2013. Hernández, A.; Casas, M.; Leon, M. A. & Pérez, V. E. Valoración económica de bienes y servicios ambientales en áreas protegidas: contribución al proceso de toma de decisiones. Retos de la Di- rección 4 (2):3-12, 2010. Labrada, G. Viabilidad económica de la actividad turística en el Área Protegida de recursos ma-
  • 10. 156 Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Nadia Báez-Quiñones nejados Jobo Rosado. En: Potenciando la con- servación de la biodiversidad mediante la evaluación económica y ambientalmente soste- nible de actividades productivas en el ecosiste- ma Sabana Camagüey, Cuba. Sancti Spíritus, Cuba: Agencia Medio Ambiente. p. 71-84, 2013. Leal, C. L. Valoración económica del medio ambien- te. Caso de la Reserva de la Biosfera de los Tuxtlas. Tesis Licenciatura en Economía. Puebla, Cuba: Escuela de Ciencias Sociales, Universidad de las Américas, 2005. Machín, M. M. & Casas, M. Valoración económica de los recursos naturales. Pinar del Río, Cuba: Universidad de Pinar del Río, 2006. Machín, M. M. & Hernández, A. Hacia una aproxima- ción de la valoración económica en áreas prote- gidas. Estudio de caso: Parque Nacional Viñales, Cuba. Revista UDO Agrícola. 9 (4):873-884, 2009. Maldonado, J. & Cuervo, R. Valoración económica del Parque Nacional Natural Corales de Profun- didad. Bol. Invest. Mar. Cost. 45 (1):99-121, 2016. Manzano, A.; Caraballoso, A. & Castro, M. Compa- ración de las emisiones de GEI de la producción bufalina con las actividades de remoción de dióxido de carbono en áreas reforestadas de la UBPC No. 5. Agropecuaria Bolivia, Ciego de Ávila. En: Potenciando la conservación de la biodiversidad mediante la evaluación económi- ca y ambientalmente sostenible de actividades productivas en el ecosistema Sabana Camagüey, Cuba. Sancti Spíritus, Cuba: Agencia de Medio Ambiente. p. 29-36, 2013. MINAM. Manual de valoración económica del patri- monio natural. Lima: Ministerio del Ambiente, 2015. Miranda, Taymer. Algunas consideraciones sobre la valoración económica del impacto ambiental en el sector agropecuario. Pastos y Forrajes. 25 (3):147-153, 2002. Miranda, Taymer; Machado, R.; Machado, Hilda & Duquesne, P. Carbono secuestrado en ecosis- temas agropecuarios cubanos y su valoración económica. Estudio de caso. Pastos y Forrajes. 30 (4):483-491, 2007. Miranda, Taymer; Machado, R.; Machado, Hilda & Duquesne, P. Valoración económica de bienes y servicios ambientales en dos ecosistemas de uso ganadero. Zootecnia Trop. 26 (3):187-189, 2008. Murillo, L. G. & González, C. V. Criterios técnicos para el uso de herramientas económicas en los proyectos, obras o actividades objeto de li- cenciamiento ambiental. Bogotá: Ministerio de Ambiente y Desarrollo Sostenible y Autoridad Nacional de Licencias Ambientales, 2017. Pardo, Y. Y. & Sanjinés, G. N. Valoración económi- ca de servicios ambientales en sistemas agrofo- restales en América Latina. Revista FACCEA. 4 (2):141-150, 2014. Pearce, D. W. & Morán, D. The economic value of di- versity. Londres: UICN, 1994. Pérez-Torres, F. J. Medio ambiente, bienes ambienta- les y métodos de valoración. Equidad & Desa- rrollo. 25:119-158, 2016. PNUD. Ecosistema Sabana-Camagüey. Informe téc- nico del proyecto PNUD/GEF Sabana-Cama- güey. Cuba, 2007. Poey, J. I. & García, Y. Y. Evaluación económica de un proyecto forestal en la UBPS Guamuta, y sus potencialidades de comercialización de dióxido de carbono. En: Potenciando la conservación de la biodiversidad mediante la evaluación econó- mica y ambientalmente sostenible de actividades productivas en el ecosistema Sabana Camagüey, Cuba. Matanzas, Cuba: Agencia de Medio Am- biente. p. 37-48, 2013. Raffo, E. Valoración económica ambiental: el proble- ma del costo social. Industrial Data. 18 (1):108- 118, 2015. Rangel, R. A.; Durán, O.; Gómez, G.; Ferro, H.; Ba- rranco, G. & Sánchez, M. Valoración económi- co-ambiental de recursos naturales seleccionados en la cuenca del río Guanabo, La Habana, Cuba. REVIBEC. 20:45-55, 2013. Reynaldo, C. L. & Guardado, R. M. Procedimiento para la valoración económica y ambiental en la actividad minera de níquel. An. de la Acad. 6 (3), 2017. Rodríguez, Y.; Renda, A.; Gutiérrez, J. E. & Plasen- cia, T. Bienes y servicios ambientales obtenidos del raleo I y II en pinares en la cuenca hidrográ- fica del Río San Diego, Pinar del Río. Revista Forestal Baracoa. 30 (2):25-32, 2011. Rodríguez-Córdova, R.; Mir-Frutos, Z. & Guz- mán-Alberteris, L. Incidencia de la valoración económica de bienes y servicios ecosistémicos en la gestión ambiental. Universidad y Sociedad. 9 (5):262-267, 2017. Tomio, M. & Ullrich, D. R. Valoración económica ambiental en el turismo. Estudios y perspectivas del turismo. 24:172-187, 2015. Valdés, L. A.; Ulloa, D. R.; Gómez, C.; Jiménez, Y.; Castro, M. & Vidal, V. Factibilidad económica del uso de la tecnología de digestión anaerobia en el tratamiento de residuales porcinos a pequeña y mediana escala. RCCP. 20 (4):238-241, 2013. Villarreal, Y. & Unger, P. V. Valoración económica de los ecosistemas del área protegida Reserva Ecológica Punta del Este. ConFin Habana. 4:1-7, 2012.
  • 11. Pastos y Forrajes, Vol. 41, No. 3, July-September, 149-157, 2018 / Economic appraisal of the environment 157 Wilkes, A.; Reisinger, A.; Wollenberg, E. & van Dijk, S. Medición, reporte y verificación de las emi- siones de GEI de la ganadería de países en de- sarrollo de la UNFCCC: prácticas actuales y oportunidades de mejora. Informe 17. Programa de Investigación de CGIAR en Cambio Climáti- co, Agricultura y Seguridad Alimentaria (CCA- FS) y Alianza Mundial de Investigación sobre los Gases de Efecto Invernadero de Origen Agrope- cuario (GRA). Wageningen, Holanda, 2017. Zapata, C.; Robalino, J. & Solarte, A. Influencia del Pago por Servicios Ambientales y otras variables biofísicas y socioeconómicas en la adopción de sistemas silvopastoriles a nivel de finca. LRRD. 27 (4). http://www.lrrd.org/lrrd27/4/zapa/27063. html. [07/07/2018], 2015. Zequeira, M. E.; Figueredo, E. & Echemendía, A. Me- canismo financiero turístico por concepto de servi- cios ecosistémicos para sostener la oferta de agua: Cayo Sabinal, Camagüey, Cuba. En: Potenciando la conservación de la biodiversidad mediante la evaluación económica y ambientalmente sosteni- ble de actividades productivas en el Ecosistema Sabana Camagüey, Cuba. Sancti Spíritus, Cuba: Agencia de Medio Ambiente. p. 119-131, 2013. Zequeira, M. E.; Figueredo, E.; León, M. M. & Mon- tero, R. Costo de oportunidad para bienes am- bientales en la zona costera norte de la provincia de Camagüey, Cuba. Ecociencia. 3 (2), 2016. Received: May 16, 2018 Accepted: September 5, 2018
  • 12. 158 Pastos y Forrajes, Vol. 41, No. 3, July-September, 158-163, 2018 / Yuseika Olivera-Castro Scientific Paper Selection of accessions of Urochloa brizantha (Hochst. ex A. Rich.) R. D. Webster for acid soils Yuseika Olivera-Castro1 , Onel López-Vigoa1 , Pedro Pablo del Pozo-Rodríguez2 , Lisset Castañeda-Pimienta1 , Agustín Olmedo-Juárez3 , Javier Arece-García1 and Rolando Rojo-Rubio4 1 Estación Experimental de Pastos y Forrajes Indio Hatuey, Universidad de Matanzas, Ministerio de Educación Superior Central España Republicana, CP 44280, Matanzas, Cuba 2 Universidad Agraria de La Habana Fructuoso Rodríguez, Mayabeque, Cuba 3 Centro Nacional de Investigación Disciplinaria en Parasitología Veterinaria (CENID-PAVET) Jiutepec, Morelos, México 4 Centro Universitario UAEM-Temascaltepec, Universidad Autónoma del Estado de México E-mail: yuseika@ihatuey.cu Abstract A collection of 19 Urochloa brizantha accessions was studied, in association with Stylosanthes guianensis on a soil characterized by acidity, in order to select the best ones for this soil type. The measured and estimated variables were: vegetative height, availability and non-consumed pasture residue. In addition, leafiness, cover, vigor, CP content, fiber (NDF and ADF) degradation and IVDMD, were determined. The interpretation of the results was done through principal component analysis; and for grouping the associations and selecting those that had similar characteristics, cluster analysis was used. The existence of a high accumulated variability (75,9 %) was detected in the first four components. When analyzing the agronomic and nutritional value performance, after three years of exploitation, the formation of six groups was identified; the associations in which the accessions that form group II were present (CIAT-16335 and CIAT-26646) stood out, reaching the highest values in height, availability and utilization, as well as high vigor and high CP contents and IVDMD. These associations that included the accessions that belonged to group II (CIAT-16335 and CIAT-26646) were present showed the best performance, when making an overall analysis of agronomic and nutritional value variables. It is recommended to study structural and floristic composition variables, as well as the seed production potential, in order to propose a pre-commercial variety for the agroecosystems with acid soil. Keywords: height, evaluation, nutritional value Introduction In the 1980’s, the species of cultivated pastures represented approximately 60 % of pasturelands in the country. Nevertheless, after more than three decades under exploitation, they barely reach 19 %, and some show a high degree of degradation (CITMA, 2012). In addition to this problem, there is a marked fertility loss in soils dedicated to animal husbandry (Hernández, 2016), element that constitutes one of the main causes of the degradation of cultivated pastures, whose consequence results in a reduction of plant biomass yield and quality and its direct im- plication in the decrease of milk and meat produc- tion (Padilla et al., 2013). Such aspects force the adoption of strategies aimed at the application of technologies that in- clude the introduction and evaluation of species and/or accessions, which can contribute to the im- provement of the feeding basis of animal husbandry zones and which, in turn, allow to reach adequate production, quality and persistence of pasturelands; because animal feeding is supported mainly on the utilization of pastures and forages, as it is one of the cheapest sources (Verdecia-Acosta et al., 2014). In many studies it has been proven that the spe- cies of the Urochloa genus grow on a broad range of soils, and some of them are recommended spe- cifically for acid soils, in Cuba as well as in other tropical zones of America (Silva et al., 2016); in this type of soil, Urochloa decumbens (Stapf) R. D. Webster, Urochloa humidicola (Rendle) Morrone & Zuloaga, Urochloa dictyoneura (Fig. & De Not.) Veldkamp, and Urochloa brizantha (Hochst. ex A. Rich.) R. D. Webster, stand out. Based on the above-described facts, it is essen- tial to identify the U. brizantha materials that adapt better to these soils, from their morphophysiologi- cal and productive characteristics; such accessions could make a better utilization of nutrients and pro- vide sufficient biomass, with the required quality, for the maintenance, production and reproduction of grazing animals. Hence the objective of this study was to select the best accessions of a U. brizantha collection in as- sociation with Stylosanthes guianensis for acid soils.
  • 13. Pastos y Forrajes, Vol. 41, No. 3, July-September,158-163, 2018 / Selection of accessions of Urochloa brizantha 159 Materials and Methods Location of the experimental area. The study was conducted in areas of the Pastures and Forages Research Station of Cascajal, Santo Domingo mu- nicipality –Villa Clara province, Cuba–, located at 22º 36’ North latitude and 80º 04’ West longitude, at 60 m.a.s.l. Characteristics of the climate. The climate of the zone is classified as tropical, characteristic of Cuba. The performance of the climate variables is shown in table 1; the rainfall volume varied among the years the study lasted, and only in the first year the rainfall was higher compared with the other two years. The maximum, minimum and mean tempera- ture, relative humidity and light hours showed simi- lar values among the years. Soil of the experimental area. The study was conducted on a distic, petroferric, Ferruginous, Nodular Gley soil, characterized by acid pH (4,2), as well as low organic matter content (1,91 %), total N (0,40 %) and assimilable P (1,90 mg/100 g). re- garding these characteristics, it can be considered an acid soil and with low fertility, according to Hernández-Jiménez et al. (2015). Experimental procedure Soil preparation. For the soil preparation the conventional method was used, consisting in plow- ing, harrowing, crossing, harrowing and furrowing. Design and treatments. A randomized block design was used with three replicas. The plots measured 23,52 m2 , and were separated by 1,50 m spaces on both sides. The treatments were represented by 19 previously selected U. brizantha accessions: CIAT-16300, CIAT- 16317, CIAT-16809, CIAT-16469, CIAT-16322, CIAT- 16132, CIAT-16128, CIAT-16335, CIAT-1539, CIAT-26290, CIAT-16332, CIAT-16819, CIAT-16303, CIAT-16334, CIAT-16448, CIAT-26646, CIAT-16485, CIAT-16197 and CIAT-26032,inassociationwithS.guianensis. Planting, sowing and establishment. The grass was planted by vegetative seed, consisting in por- tions of tillers formed by five to eight 20-cm long shoots, approximately. A distance between plants and between rows of 0,70 m was used, which is equivalent to a density of 20 000 plants/ha. The rows as well as the external tillers were separated from the plot edges by 0,35 m; the depth was 10 cm. As legume, S. guianensis (Aubl.) Sw. CIAT-184 was used, accession selected in Cuba as commer- cial variety (MINAG, 2016), which has shown adap- tation to this soil type (Castañeda-Alvarez et al., 2016). It was planted by drilling, at a depth of 2 cm and space between rows of 0,70 m, with density of 1,5 kg of PGS/ha. Its seeds were previously scari- fied in water at 80 ºC during two minutes. The planting as well as the seeding were simul- taneously performed in April, related to the rainfall occurred in that month. During 45 days after these activities the space between the plots was manually weeded twice, and some weak or dead grass plants were replaced, so that all the treatments were repre- sented by a similar number of tillers. Throughout the experimental period neither irrigation nor ferti- lization was used. Animals. Homogeneous groups of 29 crossbred (Creole x Zebu) fattening animals (20,3 LAU) were used,withanaverageweightof350kgandgoodhealth status, which had water and mineral salts available 24 h per day in a paddock designed for this purpose. No energy or protein supplementation was offered. Management. A simulated grazing system was used, in which the animals were led to the area when the treatments reached resting times between 85 and 95 days in the dry season (DS) and between 50 and 60 days in the rainy season (RS). The average permanence days were 2 and 1 day and the grazing intensity was 94,4 and 47,2 LAU days/ha for both seasons, respectively. During the three years of the study a total of 15 rotations were made, five in each year, from which two corresponded to the DS and three to the RS. Measurements. The “Methodology for the evaluation of herbaceous species”, proposed by the Table 1. Climate performance during the research. Year Variables Rainfall (mm) Temperature (°C) Relative humidity (%) Light hours maximum minimum mean 1 1 697,7 31,5 19,5 24,4 78 7,9 2 1 153,5 31,3 19,2 24,3 76 8,0 3 1 262,3 30,2 18,5 23,6 77 7,8
  • 14. 160 Pastos y Forrajes, Vol. 41, No. 3, July-September, 158-163, 2018 / Yuseika Olivera-Castro Pastures and Forages Research Station Indio Hatuey (Machado et al., 1997) and approved by the National Sub-Commission of Pasture and Forage varieties, was taken as basis. Agronomic variables. The plant height was represented by the mean value of this variable in the four tillers used for the determination of availability (this was equivalent to a sample size of 8,3 %). For the leafiness, cover and vigor a walk was made that included the entire plot; and the value of each variable was visually calculated, according to the gradological scale used. The biomass availability was estimated one day before the animals entered the area, and the residue of non-consumed pasture, when the animals left. The measurements and estimations were made in all the rotations. Variables of the nutritional value. The broma- tological composition was determined through the proximal chemical analysis. Of each sample the N content was analyzed by the Kjeldahl method, and the CP content was estimated (N x 6,25). The fiber (NDF and ADF) degradation was determined through the Van Soest method. The in vitro gas production technique was used for obtaining the IVDMD and the parameters of the different phases of this process: fraction b, fraction c and Lag phase. The analyses were conducted in the Nutrition laboratory of the School of Veterinary Medicine of the Autonomous University of Mexico State, Toluca, Mexico State. Statistical analysis. The principal component analysis (PCA) was used. To identify the compo- nents that explained the highest variations, those that had a proper value higher than one were se- lected; while in order to identify the variables that influenced the most the variability extracted for each component it was taken into consideration that the sum or preponderance factors reached a value higher than 0,60. To group the accessions and select those that had most prominent similar characteristics the cluster analysis was used; from the results obtained in the PCA. As grouping criterion the Euclidean distance was used, and Ward method as form of ascending hierarchical aggregation (Torres et al., 2006). The cutting line for forming the groups was based on the criterion expressed by Núñez-Colín and Escobedo-López (2011). The statistical package SPSS version 15® was used. Results and Discussion When performing the PCA (table 2) the exis- tence of high accumulated variability in the first Table 2. Results of the PCA and relation among the variables. Analyzed variables Principal components CP1 CP2 CP3 CP4 Vegetative height (cm) -0,46 0,70 0,01 0,40 Vigor (Ve) 0,89 0,05 -0,10 -0,01 Leafiness (Ve) 0,36 0,14 -0,38 0,26 Availability (t DM/ha/rotation) -0,58 0,69 -0,14 0,27 Utilization (%) 0,80 -0,16 0,32 0,13 CP (%) 0,22 -0,01 0,78 0,41 NDF (%) 0,19 0,29 0,02 -0,84 ADF (%) 0,33 0,37 -0,60 -0,10 IVDMD 0,58 0,56 0,23 0,31 Fraction b -0,53 -0,41 0,55 -0,17 Fraction c 0,20 0,65 0,54 -0,34 Lag phase 0,14 -0,70 -0,24 0,32 Proper value 3,0 2,6 1,9 1,5 Variance (%) 25,0 21,9 16,0 12,9 Accumulated (%) 25,0 46,9 63,0 75,9 Underlined values indicate higher contribution.
  • 15. Pastos y Forrajes, Vol. 41, No. 3, July-September,158-163, 2018 / Selection of accessions of Urochloa brizantha 161 four components was noted, based on the variables included in the study. The variance in CP1 reached avalueof25,0%,andinCP2,21,9%.InCP1,thevariables with higher influence on the extracted variance were vigor and utilization percentage; while in CP2, vege- tative height, Lag phase, availability and fraction c, all positively related; Lag phase did it inversely. Although two elements of the degradability equation did not show a strong incidence on the prin- cipal components: IVDMD and fraction b, it is con- sidered that they should be taken into consideration due to their importance in the interpretation of results. The IVDMD was explained in the CP1-CP2 plane and, thus, linked to agronomic and nutritional factors: vigor, utilization percentage, vegetative height, availability, fraction c and Lag phase, all positively related to that variable except the last one. These variables, excluding the last, showed a stressed trend to reaching higher percentages of IVDMD, aspect that coincides with the expected result when agronomic and nutritional value variables like these are jointly analyzed (Tsuzukibashi et al., 2016). On the other hand, fraction b, with sum or pre- ponderance values close to 0,60, in CP3, was linked to factors of the nutritional value, such as CP and ADF, positively with the former and inversely with the latter, which is in correspondence with the sig- nificance of that variable. The previously described results allow to con- sider that there was a higher differentiation degree among the associations with regards to the variables present in CP1-CP2, and much less for variables such as CP, ADF and NDF, which only extracted 16,0 and 12,9 % in CP3 and CP4, respectively. When forming the groups through the cluster analysis, based on the results of the PCA, the presence of six different groups was detected. Table 3 shows the typification of the accessions by groups and their identification. Similarity was found among the associations in groups V and VI for the mean value of the variable vegetative height, although its values were low- er than that of groups I, III and IV. However, the ones that formed group II (CIAT-26646 and CIAT- 16335) exceeded that of the last ones. Table 3. Typification of the accessions by group and their identification. Variables Group I Group II Group III Group IV Group V Group VI X SD X SD X SD X SD X SD X SD Height 64,2 7,2 70,1 4,9 67,8 2,3 58,3 3,1 40,2 3,2 46,9 6,1 Vigor 3,0 0,0 4,0 0,0 4,0 0,0 4,0 0,0 4,0 0,0 4,0 0,0 Leafiness 3,4 0,5 4,0 0,0 4,0 0,0 3,7 0,5 3,7 0,5 4,0 0,0 Availability 3,6 0,5 3,8 0,8 3,4 0,2 2,8 0,3 2,3 0,1 2,7 0,0 Utilization 25,3 5,3 64,0 8,1 21,4 13,4 48,4 27,9 57,1 2,3 57,8 8,8 CP 9,9 1,3 11,2 1,7 9,4 1,6 10,4 1,6 10,4 1,8 9,3 1,1 NDF 76,1 1,2 75,3 1,2 75,0 0,9 78,4 2,1 75,8 1,1 77,6 0,7 ADF 41,0 1,2 42,8 0,9 41,1 1,6 40,8 1,4 40,7 0,6 43,7 0,0 IVDMD 50,2 5,0 65,1 2,5 50,4 1,9 54,8 1,1 51,9 0,8 57,2 1,6 Fraction b 163,8 3,6 143,6 5,2 140,7 3,3 153,1 1,7 158,8 8,5 142,7 7,0 Fraction c 0,02 0,0 0,02 0,0 0,02 0,0 0,02 0,0 0,02 0,0 0,02 0,0 Lag phase 1,49 0,5 1,39 1,2 1,1 0,4 0,5 0,1 2,1 0,2 1,8 0,2 Group Quantity of accessions Name of the accessions♦ I 5 CIAT-16300,CIAT-16322,CIAT-16819,CIAT-16332,CIAT-16132 II 2 CIAT-26646, CIAT-16335 III 2 CIAT-16197, CIAT-16809 IV 4 CIAT-16317, CIAT-16334, 1539, CIAT-26290 V 3 CIAT-26032, CIAT-16448, CIAT-16485 VI 3 CIAT-16128, CIAT-16303, CIAT-16469 ♦ Associated with S. guianensis
  • 16. 162 Pastos y Forrajes, Vol. 41, No. 3, July-September, 158-163, 2018 / Yuseika Olivera-Castro Regarding vigor, the accessions that formed group I (CIAT-16300, CIAT-16322, CIAT-16819, CIAT-16332, CIAT-16132) showed the worst perfor- mance with regards to those in the other groups, which, as average, reached value 4 according to the scale used. In the associations that were part of groups IV, V and VI a relatively similar value was detected for the variable availability, but lower than that of the other groups. Among the latter (I, II and III), the associations integrated by CIAT-26646 and CIAT- 16335 (group II) stood out with the highest value, aspect that is considered of relevant interest, be- cause it defines the biomass volume that is available for animal feeding. The percentage of utilization by the animals in the above-mentioned associations was also higher when compared with the mean of the other groups; this has marked importance, due to the role this variable plays in the consumption made by the ani- mals. This same pattern was found for CP. The parameters that are obtained when the cal- culations are made to define the IVDMD values through the gas production technique constitute an extremely important tool to estimate the capacity of degradation of the forages that compose the diet of ruminants and, also, the factors with higher influence on it (Vargas-Bayona et al., 2013). Hence, when analyzing in these associations the performance of fraction c and the Lag phase, variables that characterize the forage degradation rate, it was observed that the values of the former were similar for all the groups; while the associa- tions that formed group IV showed the best result (0,5) for the latter, which means that they showed the lesser time for the rumen microorganisms to start the feed degradation. Ortega-Aguirre et al. (2015) stated that there are differencesamongtheparametersofthedegradability equation for fractions b and c among forages of different species, but not among accessions of the same species. In this research such performance was rather shown in fraction b, which showed variability for the studied associations, according to the PCA. An outstanding place corresponds to group II (CIAT-16335 and CIAT-26646), regarding the performance of the evaluated materials. These accessions reached the greatest height, high vigor, the highest values of availability and also in terms of utilization, as well as high CP contents and IVDMD. In this last variable similar results have been reported in the grass Megathyrsus maximus cv. Mombaza (60,9 %) and a little bit higher in Brachiaria hibrido cv. Mulato (67,5 %), according to the report by Silva et al. (2016). The accession CIAT-26646, in particular, has stood out in diverse animal husbandry systems. In that sense, Njarui et al. (2016) referred the potentialities of this material, which stood out for its good acceptability, high resistance to pest attack, good growth, high degree of associability with legumes of twining or creeping growth habit, as well as a CP content of 11 %. These and other outstanding characteristics have allowed such accession to become one of the most widely used in tropical regions for cattle production (Caballero, 2014). In the species U. brizantha there are satisfacto- ry results regarding their agronomic performance and nutritional value, such as the ones reported by Tsuzukibashi et al. (2016), who found, depending on the cutting age, different values of the nutrition- al variables (up to 68 and 30 % for NDF and ADF, respectively; and between 8,8 and 18,6 % of CP) when studying cvs. Marandú. Piatã and Xaraés; this confirms that this species has cultivars with ac- ceptable quality for livestock feeding. It is concluded that the associations in which the accessions that formed group II (CIAT-16335 and CIAT-26646) were present showed the best performance, when making an overall analysis of agronomic and nutritional value variables Likewise, to study structural and floristic composition variables, as wellastheseedproductionpotential,isrecommended, in order to propose a pre-commercial variety for the agroecosystems with acid soil without using inputs. Bibliographic references Caballero, P. J. Brachiaria brizantha cv. La Liber- tad (MG4). Paraguay: Semillas sudamericanas. http://semillassudamerica.com/spa/productos/ producto-brachiaria-brizantha-cv-la-liber- tad-mg4. [07/12/2017], 2014. Castañeda-Álvarez, N. P.; Álvarez, F.; Arango, J.; Chanchy, L.; García, G. F.; Sánchez, V. et al. Especies vegetales útiles para sistemas silvopas- toriles del Caquetá, Colombia. Cali, Colombia: Deutsche Gesellschaft für Internationale Zusam- mena, Centro Internacional de Agricultura Tro- pical, 2016. CITMA. Informe de Cuba a la Conferencia de las Naciones Unidas sobre Desarrollo Sostenible Río+20. La Habana: Ministerio de Ciencia, Tec- nología y Medio Ambiente, 2012. Hernández, Marta. Los suelos dedicados a la ganade- ría en Cuba. Conferencia. Maestría en Pastos y Forrajes; 3.5; Matanzas, Cuba: EEPF Indio Ha- tuey. p. 20, 2016.
  • 17. Pastos y Forrajes, Vol. 41, No. 3, July-September,158-163, 2018 / Selection of accessions of Urochloa brizantha 163 Hernández-Jiménez, A.; Pérez-Jiménez, J. M.; Bosch-Infante, D. & Castro-Speck, N. Clasifica- ción de los suelos de Cuba. Mayabeque, Cuba: Instituto Nacional de Ciencias Agrícolas, Insti- tuto de Suelos, Ediciones INCA, 2015. Machado, R.; Seguí, Esperanza & Alonso, O. Con- ferencia Metodología para la evaluación de es- pecies herbáceas. Matanzas, Cuba: EEPF Indio Hatuey, 1997. MINAG. Lista oficial de variedades comerciales. Re- gistro de variedades comerciales. La Habana: Ministerio de la Agriculturas, 2016. Njarui, D. M. G.; Gatheru, M.; Ghimire, S. R. & Mure- ithi, J. G. Effects of seasons and cutting intervals on productivity and nutritive value of Brachiaria grass cultivars in semi-arid eastern Kenya. D. M. G.Njarui, E. M. Gichangi, S. R. Ghimire, R. W. Muinga. Climate smart Brachiaria grasses for improving livestock production in East Africa: Kenya Experience. Proceedings of a workshop. Naivasha, Kenya: Kenya Agricultural and Lives- tock Research Organization. p. 46-61, 2016. Núñez-Colín, C. A. & Escobedo-López, Diana. Uso correcto del análisis clúster en la caracteriza- ción de germoplasma vegetal. Agron. Mesoam. 22 (2):415-427, 2011. Ortega-Aguirre, C. A.; Lemus-Flores, C.; Bugarín-Pra- do, J. O.; Alejo-Santiago, G.; Ramos-Quirarte, A.; Grageola-Núñez, O. et al. Agronomic characteris- tics, bromatological composition, digestibility and consumption animal in four species of grasses of the genera Brachiaria and Panicum. Trop. Sub- trop. Agroecosyst. 18:291-301, 2015. Padilla, C.; Sardiñas, Y.; Febles, G. & Fraga, Nidia. Estrategias para el control de la degradación en pastizales invadidos por Sporobolus indicus (L) R. Br. Rev. cubana Cienc. agríc. 47 (2):113-117, 2013. Silva, Janaina de L.; Ribeiro, Karina G.; Herculano, Bruna N.; Pereira, O. G.; Pereira, Rosana C. & Soares, Luciana F. P. Massa de forragem e ca- racterísticas estruturais e bromatológicas de cul- tivares de Brachiaria e Panicum. Ciênc. anim. bras. 17 (3):342-348, 2016. Torres, Verena; Figueredo, J.; Lizazo, D. & Álvarez, A. Modelo estadístico para la medición del im- pacto de la innovación o transferencia tecnoló- gica en la rama agropecuaria. Informe técnico. San José de las Lajas, Cuba: Instituto de Ciencia Animal, 2006. Tsuzukibashi, Denise; Costa, J. P. R.; Moro, Fabiola V.; Ruggieri, Ana C. & Malheiros, E. B. Anatomia quantitativa, digestibilidade in vitro e composição química de cultivares de Brachiaria brizantha. Rev. Ciências Agrárias. 39 (1):46-53, 2016. Vargas-Bayona, J. E.; Mejía-Porras, G.; Bedoya-Mas- huth, Julia & Gómez-Patiño, J. F. Estimación de la técnica in vitro de gases frente a otras técni- cas de digestibilidad. Spei Domus. 9 (18):59-70, 2013. Verdecia-Acosta, D. M.; Herrera-García, R. S.; Ra- mírez-de-la Ribera, J. L.; Acosta, I. L.; Bo- das-Rodríguez, R.; Andrés-Lorente, Sonia et al. Caracterización bromatológica de seis espe- cies forrajeras en el Valle del Cauto, Cuba. AIA. 18 (3):75-90, 2014. Received: April 23, 2018 Accepted: June 21, 2018
  • 18. 164 Pastos y Forrajes, Vol. 41, No. 3, July-September, 164-169, 2018 / Javier Antonio Herrera-Toscano Scientific Paper Selection of local resources for sheep feeding in the Las Tunas municipality, Cuba Javier Antonio Herrera-Toscano1 and Oscar Carmenate-Figueredo2 1 Instituto de Ciencia Animal, San José de las Lajas, gaveta postal No. 1, CP 32700, Mayabeque, Cuba. 2 Facultad de Agronomía, Universidad de Las Tunas, Municipio Las Tunas, Provincia Las Tunas, Cuba E-mail: jherrera@ica.co.cu Abstract The objective of this study was to select the main available local resources, with potentialities for sheep feeding, in the Las Tunas municipality –Las Tunas province, Cuba–. The method of expert consultation was applied, to a panel of 26 members. The local resources were classified into non-forage and forage ones. Their evaluation was based on different criteria: annual availability, total supply cost, nutritional value, conservation time and cost, adaptability to local edaphoclimatic conditions, production in the dry season, resistance to pests and diseases, and production without irrigation and fertilization. Nine locally available resources were selected for sheep feeding, 66 % of which were forage ones. The highest value in forage resources corresponded to Leucaena leucocephala (Lam) de Wit (4,68 ± 0,02) and the lowest, to Moringa oleifera Lam (3,18 ± 0,87). In non-forage resources, calcium carbonate had the highest value (4,75 ± 0,75) and distillery vinasse, the lowest value (3,0 ± 0,10). Regarding the integral evaluation of the forage resources, the highest values corresponded to Saccharum officinarum L., L. leucocephala and the Pennisetum varieties: 4,54; 4,51 and 4,43, respectively; and the lowest ones to Tithonia diversifolia (Hemsl.) A. Gray, M. oleifera and Morus alba L.: 2,99; 2,66 and 2,64, respectively. It is concluded that in the Las Tunas municipality there are between five and six resources with potentialities for sheep production, among which calcium carbonate as non-forage resource and L. leucocephala as forage resource stood out. Keywords: evaluation, animal production, food security Introduction The adverse economic situation faced by Cuba originates the need to increase food production radi- cally; this objective is an issue of maximum con- cern and occupation by the Cuban Government and State. For such reason, a diversification of agricul- tural production is mandatory in order to offer meat products from different animal species. In this sense, sheep are an important source for meat production under tropical conditions. Arece et al. (2013) stated that Pelibuey is the breed with more potential for the production of small ruminants in Cuba and plays a significant role, in small-scale family economy as well as in the state entrepreneurial sector. Nevertheless, sheep production shows a set of limitations that causes scarce and unstable yields, which leads to low levels of sale and consumption of this product throughout the country; in this re- gard, the National Office of Statistics and Informa- tion (ONEI, 2017) indicated that 14 291 t of sheep meat were sold in agricultural markets, by the end of 2016, scenario that constitutes a limiting factor in the commercialization of this product. On the other hand, the Pelibuey breed shows good adaptation to the tropical environment, which allows its exploitation in diverse types of produc- tive systems, from the low-input to intensive pro- duction systems, although the former are the most widely used ones(Partida-de-la-Peña et al., 2013). Factors of diverse nature have restricted the development of sheep rearing in the tropical zone; for example, the adverse climate conditions, relat- ed to scarce and irregular rainfall volumes, high temperatures and high relative humidity. This is manifested in the insufficient productive yield of the exploited breeds, as well as in the farmers’ so- cioeconomic situation. On the other hand, the im- plementation of crossing programs of tropical sheep with improved breeds is insufficient, and besides an inadequate sanitary management of the animals is made; however, the quantitative as well as qualita- tive limitations in the feeding basis are considered by many researchers the fundamental and most difficult problem to solve (Ruiz, 2011; Velasco et al., 2015). The above-stated facts show the importance of using feasible methodologies to identify the avail- able resources at local level, with potentialities for
  • 19. Pastos y Forrajes, Vol. 41, No. 3, July-September, 164-169, 2018 / Local resources for sheep feeding 165 animal feeding and management. In this sense, the concept of local resource emerges as a philoso- phy, which could be defined as any resource that is obtained in a certain zone and is used for its benefit. This perspective, which has often been the object of research (Rendón et al., 2014; Meza-Carranco et al., 2016), should be assimilated and enhanced with higher intensity to aspire to improve sustainably the productivity and efficiency indexes, in production systems with sheep and other species. Based on the above-explained facts, the objec- tive of this work was to select the main available lo- cal resources, with potentialities for feeding sheep in the Las Tunas municipality, Cuba. Materials and Methods Characteristics of the study zone. The study was conducted in the Las Tunas municipality, Las Tunas province, Cuba, located at 20º 57’ 25” N latitude, 76º 57’ 13” W longitude, with an altitude above sea level of 90 m. the main climate variables in the last ten years averaged rainfall values of 1 038 mm, temperature of 28 ºC and 76 % of relative humidity, which corresponds to a dry tropical climate. Concerning the methodology used, there are several procedures aimed at investigating and com- piling the perceptive information about a certain issue in particular; the Delphi method is one of them. It is the most widely used expert consultation research technique. It consists in the systematic uti- lization of an intuitive judgment by a group of indi- viduals who have knowledge about a specific topic (Rowe and Wright, 2011). Delphi procedure for this study. A panel of 26 experts was created, integrated by professionals with work experience in the studied zone. Two rounds of interviews took place: in the first one the quantity and types of resources that could be used in the farm were selected, and in the second one the resources were evaluated, with the experts’ participation. The questionnaire was applied in all the cases through interview to the experts; they showed differences regarding their professions and belonged to four entities: four from the Institute of Animal Science; seven from the University of Las Tunas; six from the Provincial Agriculture Delegation; five from the provincial Cuban Association of Animal Production (NGO) and four from the Las Tunas Pastures and Forages Research Station. The average of years of professional experience in the group was 26,6. The resources were classified into forage and non-forage ones, and their evaluation was based on different criteria (table 1). A questionnaire was elaborated that contained two questions directly related to the utilization of the potential local resources in sheep feeding in the Las Tunas municipality and its vicinity. Question 1. Evaluate the pertinence of how many feeding resources you consider necessary in a farm for feeding sheep in Las Tunas municipality. Question 2. Select the local resources you con- sider viable for sheep feeding in Las Tunas munici- pality, and evaluate each resource in correspondence with the proposed scale. In the measurement of the experts’ opinions, Likert’s (1932) scale was used; for the evaluation of the resources an index resulting from the sum of the values of each item, from which the defining deci- sion was made, was taken into consideration. The variable total supply cost was considered negative, as it is a detrimental element in productive systems. Question 1: 1. Totally disagree, 2. Almost dis- agree, 3. Moderately agree, 4. Almost agree, 5. To- tally agree. Question 2: 1. Completely inadequate, 2. Al- most inadequate, 3. Moderately adequate, 4. Al- most adequate, 5. Completely adequate. With the information obtained from each ex- pert, according to their answers the descriptive Table 1. Criteria used in the selection of local resources. Non-forage resources Forage resources Annual availability Annual availability Total supply cost Adaptability to the local edaphoclimatic conditions Nutritional value (protein and/or energy) Production in the dry season Conservation time and cost Resistance to pests and diseases Production without irrigation or fertilization Nutritional value (protein and/or energy)
  • 20. 166 Pastos y Forrajes, Vol. 41, No. 3, July-September, 164-169, 2018 / Javier Antonio Herrera-Toscano statistics average and typical deviation were calcu- lated, through the Microsoft Excel worksheet. Results and Discussion The panel members’ opinion about the quan- tity of necessary resources to guarantee sheep rearing under the conditions of the municipalities indicated that they should be five or more than this value. This result is due, to a large extent, to two main factors: first, rainfall seasonality, which originates instability in the availability and quality of feedstuffs, which in turn entails that it is necessary to have a high degree of diversification in the feeding front; and, second, the imperative of balancing the diet to cover the basic nutritional requirements of the animals (NRC, 2016; Perdomo et al., 2017). The values close to zero of the typical deviation (table 2) indicated that there was homogeneity in the responses and, thus, little dispersion around them (Solanas et al., 2005). Table 3 shows the results of the selection of the resources that were mostly considered by the experts and their corresponding degree of importance. In to- tal the resources mentioned were nine; it should be emphasized that 66 % of these resources are forage ones, which has direct relation with the principles of ruminant animal production under tropical condi- tions and the production costs (Alonso, 2016). The highest values in the forage resources were obtained in white leadtree (Leucaena leucocepha- la) and the Pennisetum varieties; in the non-forage resources, the calcium carbonate source turned out to be the preferred one. With this selection it is guaranteed that the energy requirements are cov- ered with sugarcane (S. officinarum) and the Pennise- tum varieties. Table 2. Stadigraphs of the application of the Likert scale for the selection of the necessary feeding resources in a sheep production farm. Item Average Standard deviation One resource 1,00 - Two resources 1,00 - Three resources 2,30 0,56 Four resources 3,72 0,97 Five resources 4,40 0,61 More than five resources 4,45 0,78 Likert scale: 1. Completely disagree, 2. Almost disagree, 3. Moderately agree, 4. Almost agree, 5. Completely agree. Table 3. Stadigraphs of the application of the Likert scale in the determination of the importance of the feeding resources. Item Average Typical deviation L. leucocephala 4,68 0,02 Saccharum officinarum 3,65 0,24 Pennisetum varieties 4,30 0,06 Tithonia diversifolia 3,28 0,40 Moringa oleifera 3,18 0,87 Morus alba 4,02 0,63 Calcium carbonate 4,75 0,35 Common salt (NaCl) 3,80 0,24 Distillery vinasse 3,00 0,10 Likert scale. 1. Completely inadequate, 2. Almost inadequate, 3. Modera- tely adequate, 4. Almost adequate, 5. Completely adequate
  • 21. Pastos y Forrajes, Vol. 41, No. 3, July-September, 164-169, 2018 / Local resources for sheep feeding 167 Protein could be covered mainly with white leadtree, Mexican sunflower (T. diversifolia) and mulberry (M. alba). The minerals would be covered with the calcium carbonate sources, salt and dis- tillery vinasse. The proposed list served as starting point in the selection of the resources with higher potential, in order to guarantee the stable growth and development of the different sheep catego- ries under the conditions of the locality. Similarly to the above-explained case, the values of typical deviation indicated that the dispersion around the responses was low, which showed a high level of consensus. Regarding the selection of forage resources, the first three species turned out to be the ones with the best integral scoring (table 4). In the case of white leadtree, most of the surveyed persons stated that it adapts well to the soil and climate conditions of the territory, coinciding with the results obtained by Pérez-Corría et al. (2014) and Román-Miranda et al. (2016), and Miranda et al. (2016), who concluded that it is a species with excellent performance in many parts of the world and shows good chemical composition and nutritional value. The variable yield in the dry season, one of those with higher discriminating capacity in this research, was qualified as sufficient, which coincides with the reports by Bacab et al. (2013) and Reyes et al. (2015) under tropical conditions, where the yields were 2,47 and 2,04 t DM ha-1 per month in the dry season, respectively. Based on the resistance to the attack by pests and diseases, the experts’ judgment was equally positive; because, although this species is prefe- rably attacked by phytophagous insects, such as Heteropsylla cubana and Mormidea pictiventris, there are enough organisms that act as biological controls, for which they do not represent an important threat for the sustainability of the systems in which the tree is used (Alonso et al., 2005). Another aspect considered as positive was its yield without irrigation and fertilization, conditions under which animal husbandry is developed in the Las Tunas municipality. Thus, the weighting of the criteria that were analyzed indicated that white leadtree shows a remarkable integral value for its utilization in local productive systems. Sugarcane turned out to be the species of higher integral value, due to its excellent dry matter yield in low-input systems under tropical conditions, in dry seasons; and due to its rusticity, in spite of its nutritional deficiencies, which can be solved in the proposed technological scheme. This species, because of the above-mentioned attributes, is considered by many researchers as strategic par excellence (Martín, 2004). Similar results to those of sugarcane were obtained in the evaluation of the Pennisetum varieties, among which are: Cenchrus purpureus x Pennisetum glaucum cv. OM-22, Cenchrus purpureus vc. CT-169, elephant grass and others. It should be emphasized that the nutritional value of this species is higher than that of sugarcane, and their yields in tons of dry matter per hectare are very similar, factors that show their real possibilities (Nava-Cabello et al., 2013). In the other species (Mexican sunflower, drumstick tree and mulberry) the results were low- er, because they showed lower dry matter yield in the dry season without irrigation and fertilization, Table 4. Results of the evaluation of the forage resources. Item L. leucocephala S. officinarum Pennisetum varieties T. diversifolia M. oleifera M. alba Adaptability to the local edaphoclimatic conditions 4,65 4,78 3,6 4,03 3,22 2,06 Production in the dry season 4,31 5,00 5,00 2,30 2,43 2,08 Resistance to pests and diseases 4,66 4,75 4,70 4,07 1,87 2,21 Production without irri- gation and fertilization 4,20 4,90 4,85 1,86 2,04 2,21 Nutritional value 4,75 3,31 4,00 2,46 3,75 4,67 Integral value 4,51 4,54 4,43 2,94 2,66 2,64
  • 22. 168 Pastos y Forrajes, Vol. 41, No. 3, July-September, 164-169, 2018 / Javier Antonio Herrera-Toscano compared with the previous ones. The reports by Ruiz et al. (2012), Meza et al. (2016) and Pentón et al. (2016) support this statement. The low nutri- tional value of T. diversifolia was interesting, which could have been related to its low dry matter con- tent, of 10 and 12 % for the rainy and dry seasons, respectively, according to Lezcano et al. (2012). In M. oleifera the main deficiency was the suscepti- bility to pests and diseases and to the invasion by weeds in the establishment stage (Meza et al., 2016; Padilla et al., 2017). Based on the criteria expressed by the panel members, the integral evaluation of these last three species was lower than three units, for which they were placed (according to the scale) in the categories «Completely inadequate» or «Al- most inadequate»; this implied that they were not chosen as potentially usable resources for sheep production under the specific conditions of the Las Tunas municipality. In general, in all the non-forage resources an adequate level of consensus was reached regarding their favorable nutritional and economic feasibility for feeding sheep. The qualitative evaluation of the three non-forage resources that were selected by the experts is shown in table 5. The chosen calcium source was considered as highly available, because it can be acquired by farmers throughout the year, aspect that, combined with the little quantity that is necessary in order to cover the requirements of the animals, confers a low cost to it. With regards to the other attributes, it was considered that it shows sufficient nutritional value with regards to the nutrient it contributes; and its physical and chemical properties allow that, under adequate conditions, the product could be preserved for a long time period. The sum of the above-mentioned criteria indicated, integrally, that the calcium-carrying source is considered adequate. Regarding the distillery vinasse, resource that according to Vargas et al. (2014) is appropriate for feeding different animal species, especially rumi- nants, was equally evaluated as available in high degree and low cost, because it is a residue from the process of obtaining alcohol. Its nutritional value was qualified as sufficient. On the other hand, its con- servation is feasible and lasting as long as it is done in airtight containers. Another important aspect, but not studied in this research, is that the utiliza- tion of distillery vinasse constitutes an alternative to decrease environmental contamination (Rendón et al., 2014). The above-stated fact allowed to con- clude that such resource is appropriate for feeding sheep in the territory. The criteria that were expressed in the case of common salt (NaCl) were also favorable; the least positive aspect was cost, which could be lower depending on the places where the product is pur- chased. Although it is an available resource, it is not ideal to supply the mineral deficiencies that could appear in the animals, for which it would be necessary to implement the use of multiple mineral supplements that make a contribution of other im- portant elements for the functioning of the animal organism (Stewart, 2013). It is concluded that there are between five and six resources with potentialities for sheep produc- tion in the Las Tunas municipality, among which calcium carbonate as non-forage resource and L. leucocephala as forage stand out. Acknowledgements The authors thank the workers of the provin- cial delegation of the Ministry of Agriculture in Las Tunas province, Republic of Cuba, for the logistic support provided. Bibliographic references Alonso, J. Agro-ecological principles in Cuban tech- nologies with legumes for animal production. Cuban J. Agric. Sci. 50 (2):171-183, 2016. Alonso, J.; Valenciaga, Nurys; Achang, G. & Mora, C. Study of the arthropods associated with a silvopas- toral system leucaena-guinea grass in different ex- ploitation. Cuban J. Agric. Sci. 39 (2):217-221, 2005. Table 5. Average and integral values of the application of the Likert scale in the evaluation of the non-forage resources. Item Annual availability Total supply cost Nutritional value Conservation time Integral value Calcium carbonate 5,00 -1,40 4,35 5,00 3,23 Distillery vinasse 5,00 -2,20 4,36 4,86 3,00 Common salt (NaCl) 5,00 -2,10 4,55 5,00 3,11 Likert scale. 1. Completely inadequate, 2. Almost inadequate, 3. Moderately adequate, 4. Almost ade- quate, 5. Completely adequate.
  • 23. Pastos y Forrajes, Vol. 41, No. 3, July-September, 164-169, 2018 / Local resources for sheep feeding 169 Arece, J.; López, Y.; Molina, M. & Alpízar, A. Cam- bios fisiopatológicos en ovinos Pelibuey en es- tabulación, después de infestación experimental con estrongílidos gastrointestinales. Pastos y Fo- rrajes. 36 (3):354-359, 2013. Bacab, P.; Madera, H.; Solorio, N.; Vera, F. & Marru- fo, D. Los sistemas silvopastoriles intensivos con Leucaena leucocephala: una opción para la ga- nadería tropical. AIA. 17 (3):67-81, 2013. Lezcano, Yohanka; Soca, Mildrey; Ojeda, F.; Roque, E.; Fontes, Dayamí; Montejo, I. L. et al. Carac- terización bromatológica de Tithonia diversifolia (Hemsl.) A. Gray en dos etapas de su ciclo fisio- lógico. Pastos y Forrajes. 35 (3):275-282, 2012. Likert, R. A technique for the measurement of attitu- des. Archives of Psychology. 22 (140):5-55, 1932. Martín, P. La alimentación del ganado con caña de azúcar y sus subproductos. San José de las Lajas, Cuba: EDICA, 2004. Meza-Carranco, Z.; Olivares-Sáenz, E.; Gutié- rrez-Ornelas, E.; Bernal-Barragán, H.; Aran- da-Ruiz, Juana; Vázquez-Alvarado, R. E. et al. Crecimiento y producción de biomasa de morin- ga (Moringa oleifera Lam.) bajo las condiciones climáticas del Noreste de México. Tecnociencia Chiguagua. 5 (3):143-153, 2016. Nava-Cabello, J. J.; Gutiérrez-Ornelas, E.; Zava- la-García, F.; Olivares-Sáenz, E.; Treviño, J. E.; Bernal-Barragán, H. et al. Establecimiento del pasto ‘CT-115’ (Pennisetum purpureum) en una zona semiárida del noreste de México. Rev. Fito- tec. Mex. 36 (3):239-244, 2013. NRC. Nutrient requirements of beef cattle. Washing- ton, D.C.: National Academy of Sciences, 2016. ONEI. Sector agropecuario indicadores selecciona- dos. La Habana: Oficina Nacional de Estadística e Información. http://www.one.cu/publicacio- nes/05agropecuario/ppalesindsector agrop/ppa- les_inddic17.pdf. [18/03/2018], 2017. Padilla, C.; Valenciaga, Nurys; Crespo, G.; González, Daimarys & Rodríguez, Idalmis. Requerimien- tos agronómicos de Moringa oleifera (Lam.) en sis- temas ganaderos. LRRD. 29 (11). http://www.lrrd. org/lrrd29/11/idal29218.html. [18/03/2018], 2017. Partida-de-la-Peña, J. A.; Braña-Varela, D.; Jiménez-Se- veriano, H.; Ríos-Rincón, F. G. & Buendía-Rodrí- guez, G. Producción de carne ovina. Ajuchitlán, México: Centro Nacional de Investigación Discipli- naria en Fisiología y Mejoramiento Animal, 2013. Pentón, Gertrudis; Rivera, R.; Martín, G. J.; Oropesa, Katerine; Soto, F. & Cabrera, J. Intercalamiento de Canavalia ensiformis (L.) inoculada con hon- gos micorrízicos arbusculares para la producción de forraje de Morus alba (L.). Pastos y Forrajes. 39 (1):33-40, 2016. Perdomo, Ismary & Izquierdo, H. Visión prospectiva de la sustentabilidad agroindustrial. Ninth LAC- CEI Latin American and Caribbean Conference (LACCEI’2011), Engineering for a Smart Planet, Innovation, Information Technology and Com- putational Tools for Sustainable Development. Medellín, Colombia. http://www.laccei.org/ LACCEI2011-Medellin/published/IE050 _Per- domo.pdf. [18/03/2018], 2011. Pérez-Corría, Kirenia; Fonseca-Fuente, N.; Váz- quez-Aldana, J.; Aldana-Gámez, Niurky & Botello-León, A. Utilización de la Leucaena leucocephala como alimento local para la oveja Pelibuey durante la gestación. Revista Granma Ciencia. 18 (1). http://www.grciencia.granma. inf.cu/ 2014_18_n1_a5.html. [18/03/2018], 2014. Rendón, M. E.; Noguera, R. R. & Posada, S. L. Vi- naza de caña como aditivo acidificante en la ela- boración de ensilaje de maíz (Zea mays). LRRD. 26 (1). http://www.lrrd.org/lrrd26/1/rend26007. html. [18/03/2018], 2014. Reyes, J. J.; Padilla, C.; Martín, P. C.; Gálvez, M.; Rey, Sara; Noda, Aida et al. Consumo de forrajes tropica- les por vacas lecheras, mestizas Siboney, manejadas en sistemas de estabulación. AIA. 19 (1):31-40, 2015. Román-Miranda, María L.; Palma-García, J. M.; Zo- rrilla-Rios, J. M. & Mora-Santacruz, A. Produc- ción de materia seca de Leucaena leucocephala y vegetación herbácea en un banco de proteína pastoreada por ovinos. Revista de Sistemas Ex- perimentales. 3 (6):42-50, 2016. Rowe, G. & Wright, G. The Delphi technique: past, present, and future prospects: Introduction to the special issue. Technol. Forecast. Soc. Change. 78 (9):1487-1490, 2011. Ruiz, R. Producción de leche basada en pastos y forra- jes tropicales. Rev. Ciencia y Tecnología Gana- dera. 5 (1):1- 21, 2011. Ruiz, T. E.; Febles, G. & Díaz, H. Distancia de plantación, frecuencia y altura de corte en la producción de bio- masa de Tithonia diversifolia colecta 10 durante el año. Rev. cubana Cienc. agríc. 46 (4):423-426, 2012. Solanas, A.; Salafranca, L.; Fauquet, J. & Núñez, M. Estadística descriptiva en Ciencias del Compor- tamiento. Madrid: Thompson, 2005. Stewart, L. Mineral supplements for beef cattle: University of Georgia. http://extension.uga. edu/publications/files/pdf/B%20895_3.PDF. [08/06/2018], 2013. Vargas, S. A.; Noguera, R. R. & Posada, S. L. Inclu- sión de vinaza de caña y su efecto sobre el perfil de fermentación y calidad nutricional del ensila- je de pasto maralfalfa (Pennissetum sp.). LRRD. 26(12).http://www.lrrd.org/lrrd26/12/varg26216. html. [18/03/2018], 2014. Velasco, J.; Pedraza, R.; Rivera, Verónica; Jara, R. & Guapi, R. Análisis de unidades vacunas lecheras ecuatorianas. Rev. Prod. Anim. 27 (3):1-7, 2015. Received: January 15, 2018 Accepted: April 12, 2018
  • 24. 170 Pastos y Forrajes, Vol. 41, No. 3, July-September, 170-174, 2018 / Maritza Rizo-Alvarez Scientific Paper Influence of EcoMic® and Pectimorf® on the establishment of Leucaena leucocephala (Lam.) de Wit. cv. Cunningham Maritza Rizo-Alvarez, Dariel Morales-Querol, Tania Sánchez-Santana, Onel López-Vigoa, Yuseika Olivera-Castro, Miguel A. Benítez-Alvarez and Fernando Ruz-Suárez Estación Experimental de Pastos y Forrajes Indio Hatuey, Universidad de Matanzas, Ministerio de Educación Superior Central España Republicana, CP 44280, Matanzas, Cuba E-mail: maritza.rizo@ihatuey.cu Abstract TheobjectiveofthestudywastoevaluatetheinfluenceofthebiofertilizerEcoMic® ,thebioactiveproductPectimorf® and their combination, on some morphobotanical variables during the establishment of Leucaena leucocephala(Lam.) cv. Cunningham. For such purpose a randomized block design was used with three replicas, and the following treatments: T1: thermal scarification (control), T2: inoculation with EcoMic® , T3: imbibition in Pectimorf® , T4: imbibition in Pectimorf® + inoculation with EcoMic® . The variables height, number of branches and stem diameter were measured until the plants were 12 months old. The best values of each variable were obtained when, after thermal scarification (T1), the seeds were inoculated with EcoMic® (T2) or imbibed in Pectimorf® (T3), without significant differences between them; while the control showed the lowest values. The height increased in T2 and T3 by 12 %, with regards to T1. It is concluded that the imbibition in Pectimorf® or the inoculation with EcoMic® of the seeds from L. leucocephala cv. Cunningham, after thermal scarification, improved the biological response of the plants during the establishment regarding their height, number of branches and stem diameter. Hence they can be used indistinctly, in order to reduce such period in the animal husbandry systems where it is used. Keywords: height, scarification, inoculation, seeds Introduction Legumes perform functions of high agroeco- logical relevance in silvopastoral systems (SPS), because they improve the quality of the animal diet and contribute nitrogen to the system, which im- plies an advantage from the biological and economic point of view; hence the interest in ensuring the es- tablishment of these species in the systems. Among the most widely used legumes in SPS is Leucaena leucocephala (Lam.) de Wit., due to the crude protein content of its foliage (Petit-Aldana et al., 2010), to its capacity to regrow after pruning or browsing and to be rapidly re-established after biotic or abiotic stress, among other aspects; nevertheless, this species shows difficulties for its establishment due to the dormancy of its seeds. In this sense, the establishment constitutes one of the most vulnerable stages in the life cycle of plants. In the case of the species with exclusively sexual reproduction, persistence depends on the establishment of new seedlings and on the longevity of adult plants (Ramos-Font et al., 2015). At present, the use of biofertilizers and bioactive products constitutes a common practice in agriculture to reduce the establishment period of crops and, in turn, improve productivity; among the most widely used for this purpose are Azofert® , EcoMic® and Pectimorf® (João et al., 2016). The application of Glomus mosseae significantly increased growth indicators (fresh leaf biomass, fresh root biomass and height) in L. leucocephala, with regards to the addition of native mycorrhiza; and, also, mycorrhizal infection exceeded 90 % of the roots (Cuesta et al., 2006). The bioactive product Pectimorf® has been validated in sugarcane, rice, tomato and citrus fruits (Terrero, 2010) and also in sorghum (Pentón et al., 2011), but in L. leucocephala it has been tested only under nursery conditions (Bover-Felices et al., 2017). That is why the objective of this research was to evaluate the influence of the bioproducts EcoMic® and Pectimorf® on some morphobotanical variables, during the establishment of L. leucocephala cv. Cunningham. Materials and Methods Locality and geographical location. The trial was conducted in 1,6 ha belonging to the ani- mal production areas of the Pastures and Forages