Effect of condensed tannins from Leucaena leucocephala on rumen fermentation, methane production and population of rumen protozoa in heifers fed low-quality forage.
Methane (C[H.sub.4]) gas is a byproduct of anaerobic fermentation of carbohydrates in the rumen. It is considered a greenhouse gas with a global warming potential twenty-three times greater than that of C[O.sub.2]  and every year 80 million tons are generated from anthropogenic activities. It has been estimated that enteric methane contributes 39.1% of greenhouse gas emissions generated by the livestock sector . Additionally, C[H.sub.4] emissions represent an energy loss which ranges from 2% to 12% of the gross energy consumed by ruminants .
In tropical regions, ruminants are usually fed low-quality forages which are characterized by their low concentration of crude protein (CP) and digestible energy, and their high content of neutral detergent fiber (NDF) and lignin, which induces a higher methane convention rate value  decreasing the efficiency of energy utilization . Nonetheless, feeding ruminants with legumes favors a lower C[H.sub.4] production .
In the tropical regions, there is a large diversity of legume species which contain secondary metabolites such as condensed tannins (CT), which decreases the protozoa population, methanogenic archaea , and the synthesis of enteric C[H.sub.4] [8,9]. Leucaena leucocephala (L. leucocephala) is one of the main tropical shrub species which contains CT with potential to reduce C[H.sub.4] emissions , improve CP digestibility , N retention [8,9] and improve the efficiency of energy intake by ruminants . Harrison et al  have recently reported higher levels of productivity with cattle fed leucaena in Australia as well as lower enteric C[H.sub.4] emissions to the atmosphere.
The aim of the work hereby described was to assess the effect of supplying increasing concentrations of CT from L. leucocephala in the ration on feed intake, molar proportions of volatile fatty acids (VFAs), changes in rumen protozoa population and enteric C[H.sub.4] emissions by heifers fed a basal ration of tropical grass.
MATERIALS AND METHODS
The animals were treated in accordance with guidelines and regulations for animal experimentation of the Faculty of Veterinary Medicine and Animal Science (FMVZ), University of Yucatan, Merida, Mexico.
The experiment was carried out at the FMVZ, University of Yucatan in Merida, Mexico. Climate in the region is warm with an average temperature of 26.8[degrees]C and average rainfall of 984.4 mm per year .
Five crossbred (Bos taurusxBos indicus) heifers with an average body weight (BW) of 295[+ or -]6.8 kg were housed in metabolic crates in a roofed building with concrete floor without walls. Before the experiment heifers were internally dewormed with Ivermectin (AGROVET, S.A de C.V. Mexico, Federal District, Mexico) (1%; 1 mL/50 kg BW) and injected intramuscularly with ADE vitamins (1 mL/10 kg BW).
Experimental design and treatments
A 5x5 Latin square design  was used; each period lasted 19 days (13 days for adaptation to management and rations, and six days for measurements of response variables). During the adaptation period (13 days), the animals remained outside the chambers and only during the measurement period (6 days) the intake, digestibility and enteric methane production were measured. Prior to the experiment, animals were adapted to enter the respiration chambers for a period of ~3 weeks to reduce the effect of stress on voluntary intake of dry matter (DM) and behavior in and out of the chambers. Basal ration consisted of fresh forage of Taiwan (Pennisetum purpureum [Ppurpureum]) grass and increasing levels of chopped forage of L. leucocephala as a replacement for the P. purpureum forage which was homogeneously mixed (Forage-legume) to avoid selection. The chemical composition of the forages is shown in Table 1. Experimental treatments were increasing levels of L. leucocephala (0%, 20%, 40%, 60%, and 80% of DM) in the ration. Additionally, heifers were supplemented with a commercial mineral mixture Fogysal Cattle (FOGYSA S.A de C.V Merida, Yucatan, Mexico) (250 g/heifers/d).
Determination of rumen pH and molar proportions of volatile fatty acid: Samples of rumen liquor were taken by an esophageal tube according to Ramos-Morales et al . Rumen liquor was obtained during six days before measurements in each period, six hours postprandial according to recommendations by Hales et al  and Bathha et al  in order to analyze rumen pH and pattern of VFA's in the rumen. Samples of rumen liquor were filtered through double layers of cheesecloth to retain large particles. Rumen pH was determined immediately after taking the sample with a portable potentiometer (HANNA Instruments, Woonsocket, RI, USA), previously calibrated with buffers at pH's 4, 7 and 10. For the determination of molar proportions of VFA's in rumen liquor, 4 mL samples were taken and added 1 mL of a deproteinizing solution consisting of metaphosphoric and 3-methilvaleric acids. For VFA analysis, the technique proposed by Ryan  was employed using a gas chromatograph (Hewlett-Packard, 5890 series III), equipped with a flame ionization detector and a column HP-FFAP measuring 30 mx0.53 mm, temperature of the injector and the detector was in both cases 200[degrees]C.
Measurement of enteric C[H.sub.4]
Measurement of C[H.sub.4] was carried out while heifers were housed in respiration chambers , with dimensions 2.10 mx1.60 mx3.10 m (height, width and length, respectively) and a total internal volume of 9.38 m3. Mass flow generators (Sable Systems International, Las Vegas, NV, USA) pulled out the air from the chamber at a rate of 500 L/min creating a negative pressure of 475 Pa inside the chamber relative to the outside environment.
Measurement of C[H.sub.4] in air samples was carried out with an infrared analyzer (MA-10, Sable Systems International, USA). High purity C[H.sub.4] gas (99.9999% C[H.sub.4]; Praxair, Mexico) was released from a small cylinder into the chambers and the recovery rate was assessed to be 100.2% which is comparable to recovery rates obtained in other laboratories . The methane analyzer was zeroed by infusing pure [N.sub.2] and the linearity ([r.sup.2] = 0.9999) of the analyzer response was assessed by infusing increasing concentrations of methane (1,000; 2,500; 5,000; 7,500 ppm) diluted in [N.sub.2] before each run. Heifers were kept inside the respiration chambers at a temperature of 23[degrees]C and relative humidity of 55%. Fresh water was available at all times from an automatic drinking bowl and a small fan mixed the air inside the chambers. Methane measurements were carried out during three consecutive days for 23 h continuously during the measurement period of the response variables, inside the respiration chambers intake and digestibility were also measured [20,4]. Data obtained were adjusted to 24 h runs with ExpeData software (Sable Systems International, USA) and converted to liters of methane produced per day.
Heifers were fed ad libitum allowing a refusal of at least 15% of the dry matter offered the previous day. Feed refusals were weighed at 0900 h the following day. Voluntary intake was determined by the difference between the amount offered and refused. Feed offered covered an estimated intake of 7.0 kg DM/d.
Rumen protozoa population
Protozoa in samples of rumen liquor were counted according to the procedures described by Rosales . One mL of rumen liquor was mixed with 1 mL of methylgreen formalin saline solution (35 mL/L formaldehyde, 0.14 mM NaCl, 0.92 mM methylgreen) and centrifuged at 2,000 rpm for 20 min. Then, an aliquot was taken and introduced to a modified Fusch-Rosenthal chamber (Electron Microscopy Science, Hatfield, PA, USA) (IVD 98/79 CE) and observed under the microscope (Mikon-YS100) (Nikon Instruments Inc, Melville, NY, USA) at 40x. Number of ciliate protozoa was reported as log 10 from total number+1 per mL of rumen liquor. Number of protozoa was estimated with the following formulae : Number of cells per [mL.sup.-1] = [(n1+n2+n3+n4+n5)/5]/0.022 [mm.sup.3]x[10.sup.3]xd. where: n1...n5: number of protozoa per large square and d = dilution factor. Classification of protozoa was carried out according to Ogimoto and Imai .
Dry matter was determined in a forced air oven at 55[degrees]C for 48 h (constant weight) (#7.007) . Nitrogen (CP = Nx6.25) determinations were carried out with a LECCO CN-2000 series 3740 instrument (LECCO, Corporation, Saint Joseph, MI, USA) (#2.057) . Organic matter was assessed by in cineration in muffle furnace at 550[degrees]C for 6 h (AOAC Method #923.03) and the content of NDF and acid detergent fiber (ADF) were determined using the methods described by Van Soest et al . Concentration of CT in forage samples was performed by the HCL-butanol method described by Makkar .
Data on voluntary intake, apparent digestibility, nitrogen balance, protozoa population and C[H.sub.4] production were subjected to analysis of variance for a 5x5 Latin square design  using the procedure PROC ANOVA from SAS (SAS Inst. Inc., Cary, NC, USA) with the model [Y.sub.ijk] = [mu]+[P.sub.i]+[A.sub.j]+[T.sub.k]+[e.sub.ijk], where [Y.sub.ijk] is the dependent variable, [mu] is the general mean, [P.sub.i] is the effect of period, [A.sub.j] is the effect of animal, [T.sub.k] is the effect of treatment, and [e.sub.ijk] is the residual error. Statistical differences were declared significant at p[less than or equal to]0.05. Additionally, surface response analysis was carried out to assess the linear, quadratic or cubic effects  of the response to treatments (0%, 20%, 40%, 60%, and 80% of L. leucocephala in the ration).
Dry matter intake (DMI, kg/d and g/[kg.sup.0.75]) was similar among treatments with different levels of L. leucocephala forage, reporting an average of 7.0 (kg/d) and 98.7 (g/[kg.sup.0.75]), respectively (p>0.05). Organic matter intake (OMI) followed the same trend as DMI (Table 2). However, crude protein intake (CPI) increased linearly as the level of incorporation of L. leucocephala in the ration was augmented (p<0.0001).
Enteric methane production
The average of methane production in this study was 20.1 L/kg of DMI with the control treatment and as L. leucocephala increased in the diet there was a reduced C[H.sub.4] production; with incorporation of 80% of L. leucocephala in the ration methane production reduced by 61.6% respect to 0% of legume (linear reduction p = 0.0005). Also, methane emissions expressed as L C[H.sub.4]/d, kg of DM, OM, NDF, ADF intake, kg of digestibility dry matter, and organic matter digestibility (OMD), neutral detergent fiber digestibility (NDFD), an acid detergent fiber digestibility (ADFD) was linearly reduced (p<0.01) as the percentage incorporation of L. leucocephala in the ration was increased (Table 3).
pH, N[H.sub.3]-N, and molar proportions of volatile fatty acid in the rumen
No differences were observed in rumen pH as the inclusion of L. leucocephala in the ration of cattle was increased (p>0.05). Although rumen N[H.sub.3]-N was different between treatments and linearly increased as the level of the foliage of the legume was increased (p<0.01). As from 80% of L. leucocephala (36 mg/dL) in the ration, rumen N[H.sub.3]-N was significantly increased (138%) with respect to the treatment without incorporation of L. leucocephala (15.3 mg/dL) (p<0.05) (Table 4).
Molar proportions of acetic, propionic and butyric acids in rumen liquor were not affected (p>0.05) by the incorporation of L. leucocephala in the ration, registering averages of 53.8, 12.9, and 5.7 mmol/L, respectively. When the molar proportion of acetic acid was expressed as percentage, a linear increase (p = 0.037) was detected as the level of incorporation of L. leucocephala was increased. Conversely, the molar proportion of propionic acid maintained a linear reduction (p = 0.032) as L. leucocephala was increased in the ratio (p<0.0002) (Table 4).
Rumen protozoa population
Total protozoa numbers, holotrichs, and entodiniomorph in the rumen of cattle were not affected at 6 h after intake of L. leucocephala forage (p>0.05) (Table 5).
Intake of tropical foliage that contains CT at moderate concentrations (3% to 6% of DM) improves the nutrient intake of ruminant rations, particularly DM, OM, and CP . In the present work, the incorporation of up to 80% of L. leucocephala equivalent to a supply of 16.4 g/kg DMI of CT only had an influence on the greater CP intake (kg/d, CPI/kg digestibility organic matter intake [DOMI]) without affecting DMI, OMI, and acid detergent fiber intake (Table 2). Additionally, reduction in NDF intake might have been influenced by the small amount of NDF contained in the foliage of L. leucocephala (580.8 g/kg DM) and as the level of incorporation of tree foliage was increased, the amount of NDF was reduced . These results differ from those of Delgado et al  when they included 27% of L. leucocephala in sheep rations and observed an increase in the DMI and OMI, similar to results reported by Wahyuni et al  who observed an increase in DMI when they included increasing levels of L. leucocephala, registering an increase of 30%, when 60% leucaena was incorporated in the ration compared to a control treatment.
It has been pointed out that doses below 2% CT do not affect DMI [31,32]. Grainger et al  found that 1.46% CT in the ration of dairy cows did not affect DMI and Beauchemin et al  using 2% CT in cattle rations did not find an effect on nutrient intake. In this study, levels of up to 80% L. leucocephala only produces 1.64% of CT per kg DMI in the cattle ration, thus it is unlikely that this level influenced DM and OM intakes.
Enteric methane production
In this experiment, with heifers fed foliage of L. leucocephala, the methane production was lower (11.5 L/kg of DM) [6,34,8] in respect to the heifers without inclusion of L. leucocephala (20.1 L/kg of DM) in the ration. In this context, 80% of L. leucocephala foliage in the ration, decreased by ~61% the rumen methane production with respect to the control treatment, these results were similar to those obtained [35,8,34].
In the present work, a linear reduction in ruminal methane production was observed as the level of foliage of L. leucocephala in the ration was increased (Table 3) and could be associated with CT content. Several studies have demonstrated that inclusion of CT using L. leucocephala, reduces ruminal methane production. Tan et al  under in vitro conditions found a linear reduction in C[H.sub.4] production when they included 20%, 30%, 40%, 50%, and 60% of L. leucocephala, reporting a reduction of 63% in C[H.sub.4] production when the level of incorporation of the legume was 60% compared to the control treatment (0% L. leucocephala). Rira et al  included 75% and 100% of L. leucocephala in an in vitro system and found reductions of 27.0% and 31.5% in C[H.sub.4] emissions, while Molina-Botero et al  incubated 100% of L. leucocephala and found a reduction of 31% in C[H.sub.4] emissions when expressed as g/kg DM. Delgado et al  included 27% of L. leucocephala in sheep rations and observed a reduction of 15.6% in C[H.sub.4] emissions (L/kg DMI).
In the experiment hereby described, a reduction of 39.4% was recorded in C[H.sub.4] production with 40% of DM ration of L. leucocephala fed to growing heifers housed in open-circuit respiration chambers. Recent work by Soltan et al  included 35% of L. leucocephala in sheep rations and found a reduction in C[H.sub.4] production of 14.3% when expressed as L/kg of digestible organic matter, this result is lower than that found in the present experiment with 40% of inclusion of L. leucocephala (32.1% less C[H.sub.4]). Also, these results differ from results reported by Kennedy and Chamrley  who registered a reduction (L C[H.sub.4]/kg DMI) in emissions of 13.4% and 20.5% when they included 22% and 44% of L. leucocephala in cattle rations.
A higher reduction in methane production per kg of DMI was found in the experiment hereby described with 20% and 40% incorporation of L. leucocephala (26.7% and 39.4% less C[H.sub.4]/kg DMI, respectively) and when results were expressed as L C[H.sub.4]/kg DOMI, our results were similar to the values reported by Kennedy and Chamrley  with 22% and 44% of L. leucocephala in the ration (19.2% and 28.2% less C[H.sub.4]/kg DOMI). However, our results with 80% of inclusion of L. leucocepha in the diet differed from that reported by Dias-Moreira et al  whoadded 82% of L. leucocephala (40 g CT/kg DM) to sheep rations and found a reduction of 26% in rumen methane production. This could be associated with the CT concentrations on the diet. Grainger et al  included 1.46% CTs per kg dry matter and found a reduction of 22.3%, and in our present work the inclusion of 1.64% CT per kg of ration DM (80% of L. leucocephala), induced a reduction in methane production of 61.3%.
Min et al  found that the inclusion of 2% of CT as DM exerted a reduction of 31% in ruminal C[H.sub.4] production. In several experiments using plants containing CTs, similar reductions in C[H.sub.4] emissions to those found in the experiment hereby described have been registered. Puchala et al  found that goats fed Lespedeza cuneata containing 153 g CT/kg DM reduced enteric C[H.sub.4] emissions by 57.1%. Similar data were reported by Animut et al  in goats eating 200, 447, and 613 g DM of Lespedeza striata and found a reduction in C[H.sub.4] emissions of 32.8%, 47.3%, and 58.4%, respectively.
This lower digestibility [4,8] could reduce C[H.sub.4] synthesis because the fibrous component on the diet with legume was lower due to their lower amounts of lignified components compared with tropical grasses, so the time of residence in the rumen is shorter [39,40,7]. In this experiment, a reduction in rumen protozoa population was not observed, probably due to the low concentration of CT (<20 g/kg DM; ), however, several workers have mentioned that CT can reduce protozoa population but furthermore, they can also reduce the enzymatic activity of protozoa and bacteria .
Rumen pH and molar proportions of volatile fatty acid
Rumen pH was unaffected by the level of inclusion of L. leucocephala due to the fact that the forages had a high content of cellulose. The increase in the concentration of rumen N[H.sub.3]-N is related to the increase in CP digestibility and it was observed that rumen ammonia concentration in the treatments with inclusion of L. leucocephala was above values considered as normal (15 to 20 mg/dL). This is contrary to that reported by Traiyakun et al , who included 0%, 25%, 50%, and 75% of L. leucocephala in goat rations and found no effect on rumen N[H.sub.3]-N concentrations. Osakwe and Steingass  observed a reduction in rumen N[H.sub.3]-N concentrations as the level of L. leucocephala was increased from 0%, 25%, and 50% of ration dry matter, claiming this was due to the reduction in rumen degradation of CP . In the present study, rumen concentrations of acetic, propionic and butyric acids (mmol/L) were unaffected; however, when acetic acid is expressed as a percentage relative to the other VFA, its contribution increased as the level of L. leucocephala in the ration was increased. On the contrary, percentage of propionic acid was linearly reduced as L. leucocephala in the ration was increased, and the same trend was observed for the proportion of butyric acid. It was observed that the ratio acetic:propionic acid was increased as the level of L. leucocephala in the ration was augmented. These results agree with those reported by Tan et al  who under in vitro conditions incorporated 0%, 20%, 30%, 40%, 50%, and 60% L. leucocephala, and observed a linear increase in the concentration of acetic acid, but a reduction in the proportion of propionic acid and an increase in the acetic:propionic ratio in the rumen. Our results are also supported by Tiemann et al , who evaluated the molar proportions of VFA under in vitro conditions when they mixed L. leucocephala with P purpureum and found that L. leucocephala resulted in a higher amount of acetic acid but reduced the concentration of propionic acid. Rira et al  evaluated in vitro inclusions of 25%, 50%, 75%, and 100% L. leucocephala and they did not find any effect on the molar proportions (mol/100 mol) of acetic and propionic acids. However, when they included 44% of L. leucocephala in Texel sheep rations, a reduction of 5.6% in acetic acid and an increase of 22.8% in the concentration of propionic acid were found. The results of other studies also differ; Soltan et al  found that at levels of 50% of L. leucocephala, total concentration of VFA was increased by 17.3%, contrary to that found in the present experiment where no effect was observed on any of the main VFA in the rumen. Authors such as Tiemann et al  pointed out that the source of CT is an important factor which determines the effect on ruminal fermentation, however, the concentrations, molecular weight and the chemical structure of CTs are all important factors which determine their effect on the molar proportions of VFA [45,46]. It is still possible that the low concentrations of CT (1.64% CT/kg DMI) at the maximum level (80% of ration DM as L. leucocephala) of incorporation of the legume, had no effect in the concentrations of VFA when expressed as mmol/L.
Rumen protozoa population
The precise mechanism whereby CTs reduce C[H.sub.4] production is still uncertain, however CTs have the capacity to reduce protozoa  and methanogenic archaea populations . CT could also reduce C[H.sub.4] production by means of indirect mechanisms as the reduction in digestibility of dietary components  by forming chemical complexes with carbohydrates and proteins as it was found in this experiment in which a reduction in OMD was recorded as the level of incorporation of L. leucocephala was increased as well as by linearly reduced NDFD and ADFD (Table 2).
Several studies indicate that CTs of tropical trees or legumes have the capacity of reducing rumen protozoa [46,47,36,35], and bacteria  populations. It is known that protozoa populations are responsible for 37% of C[H.sub.4] emissions  and they can degrade up to 50% of the fibrous fraction of feedstuffs [49,50]. Working with protozoa-free animals, Yanez-Ruiz et al  found a reduction in C[H.sub.4] emissions. In the experiment hereby described, no effect was detected of CT contained in L. leucocephala on rumen populations of holotrich and entodiniomorph, similar data was reported by Sliwinski et al  who fed 0.5% and 1.0% CT/kg DM and did not find any effect on these populations in the rumen. These findings are similar to those reported by Rira et al  who incorporated 44% of L. leucocephala as a source of CT and did not find any effect on rumen protozoa population. However, under in vitro conditions, Tan et al  included 20%, 30%, 40%, 50%, and 60% of L. leucocephala and found a linear reduction in total and ciliate protozoa. Also, Galindo et al  found that at inclusions of 30% of L. leucocephala, rumen protozoa population was reduced by 39.4%. Puchala et al  supplemented goats with Lespedeza cuneata (20% CT/kg DM) and observed a reduction of 65% in ciliate protozoa compared to the treatment when only grass was fed. These findings suggest that small doses of CT in L. leucocephala (1.64% CT/kg DMI; 80% of L. leucocephala in ration DM) have no effect on rumen protozoa population.
As a source of CT, the tropical legume tree L. leucocephala has the capacity to reduce enteric methane emissions in cattle without affecting DM and OM intake, while providing a considerably improved intake of rumen fermentable N for the growth of the microbial population. Inclusion of 80% of L. leucocephala in the diet of heifers fed low-quality tropical forages has the capacity to reduce up to 61.3% the methane emission without affecting DMI and OMI, protozoa population and the molar concentration of VFA's.
CONFLICT OF INTEREST
We certify that there is no conflict of interest with any financial organization regarding the material discussed in the manuscript.
The senior author is grateful to CONACYT-Mexico for granting a PhD scholarship at the Faculty of Veterinary Medicine and Animal Science, University of Yucatan, Merida, Mexico.
[1.] Moss AR, Jouany JP, Newbold J. Methane production by ruminants: its contribution to global warming. INR EDP Sciences Ann Zootech 2000;49:231-53.
[2.] Gerber PJ, Steinfeld H, Herderson B, et al. Tackling climate change through livestock- a global assessment of emission and mitigation opportunities. Rome, Italy: Food and Agriculture Organization (FAO); 2013. 206 p.
[3.] Johnson KA, Johnson DE. Methane emissions from cattle. J Anim Sci 1995;73:2483-92.
[4.] Kennedy PM, Charmley E. Methane yields from Brahman cattle fed tropical grasses and legumes. Anim Prod Sci 2012; 52:225-39.
[5.] Chaokaur A, Nishida T, Phaowphaisal I, Sommart K. Effects of feeding level on methane emissions and energy utilization of Brahman cattle in the tropics. Agric Ecosyst Environ 2014; 199:225-30.
[6.] Archimede H, Eugene M, Marie-Magdeleine C, et al. Comparison of methane production between C3 and C4 grasses and Legumes. Anim Feed Sci Technol 2011;166-167:59-64.
[7.] Min BR, Solaiman S, Shange R, Eun JS. Gastrointestinal bacterial and methanogenic archaea diversity dynamics associated with condensed tannin-containing pine bark diet in goats using 16S rDNA amplicon pyrosequencing. Int J Microbiol 2014;2014:141909.
[8.] Soltan YA, Morsy AS, Sallam SMA, et al. Contribution of condensed tannins and mimosine to the methane mitigation caused by feeding Leucaena leucocephala. Arch Anim Nutr 2013;67:169-84.
[9.] Gunun P, Wanapat M, Gunun N, et al. Effects of condensed tannins in mao (Antidesma thwaitesianum Muell. Arg.) seed meal on rumen fermentation chracteristics and nitrogen utilization in goats. Asian-Australas J Anim Sci 2016;29:1111-9.
[10.] Rira M, Morgavi DP, Archimede H, et al. Potential of tannin-rich plants for modulating ruminal microbes and ruminal fermentation in sheep. J Anim Sci 2015;93:334-47.
[11.] Wahyuni S, Yulianti ES, Komara W, et al. The performance of Ongole cattle offered either grass, sundried Leucaena leucocephala or varying proportions of each. Trop Anim Prod 1982; 7:275-83.
[12.] Bruinenberg MH, van der Honing Y, Agnew RE, et al. Energy metabolism of dairy cows fed on grass. Livest Prod Sci 2002; 75:117-28.
[13.] Harrison MT, McSweeney C, Tomkins N, Eckard RJ. Improving greenhouse gas emissions intensities of subtropical and tropical beef farming systems using Leucaena leucocephala. Agric Syst 2015;136:138-46.
[14.] Garcia E. Modifications to the climate classification system of Copen to adapt it to the conditions of the Mexican Republic. Mexico, Mexico: Institute of Geography, National Autonomous University of Mexico; 1981.
[15.] Cochran WG, Cox GM. Experimental designs. 2nd edition. New York, USA: John Wiley and Sons Inc.; 1968. 661 p.
[16.] Ramos-Morales E, Arco-Perez A, Martin-Garcia AI, et al. Use of stomach tubing as an alternative to rumen cannulation to study ruminal fermentation and microbiota in sheep and goats. Anim Feed Sci Technol 2014;198:57-66.
[17.] Hales KE, Brown-Brandl TM, Freetly HC. Effects of decreased dietary roughage concentration on energy metabolism and nutrient balance in finishing beef cattle. J Anim Sci 2014;92: 264-71.
[18.] Bhatta R, Enishi O, Yabumoto Y, et al. Methane reduction and energy partitioning in goats fed two concentrations of tannin from Mimosa Spp. J Agric Sci (Camb) 2013;151:119-28.
[19.] Ryan JP. Determination of volatile fatty acids and some related compounds in ovine rumen fluid, urine and blood plasma by gas-liquid chromatography. Anal Biochem 1980;108:374-84.
[20.] Pinares-Patino CS, Waghorn G. Technical manual on respiration chamber designs. Wellington, New Zealand: Ministry of Agriculture and Forestry; 2012.
[21.] Gardiner TD, Coleman MD, Innocenti F, et al. Determination of the absolute accuracy of UK chamber facilities used in measuring methane emissions from livestock. Measurement 2015; 66:272-9.
[22.] Rosales M. Use of fodder trees for the control of ruminal protozoa. Livest Res Rural Dev 1989;1:79-85.
[23.] FAO. Determination of cell concentrations using haemocytometer according to Fuchs Rosenthal and Burker [Internet]. Gent, Belgium: FAO, 2003 [April 16, 2016]. Available from: http://www.fao.org/DOCREP/003/W3732E/w3732e0b.htm
[24.] Ogimoto K, Imai S. Atlas of rumen microbiology. Tokyo, Japan: Japan Scientific Societies Press; 1981. 223 p.
[25.] AOAC. Official methods of analysis. Association of Official Analytical Chemists. 15th Edition. Washington DC, USA: AOAC International; 1980. 70 p.
[26.] Van Soest PJ, Robertson JB, Lewis BA. Methods for dietary fiber, neutral detergent fiber and non-starch polysaccharides in relation to animal nutrition. J Dairy Sci 1991;74:3583-97.
[27.] Makkar HPS. Quantification of tannins in tree and shrub foliage: a laboratory analysis. Dordrecht, The Netherlands: Kluwer Amademic Publisher; 2003.
[28.] SAS. Institute Inc., SAS/STAT. Software, Ver. 9.00. Cary, NC, USA: SAS Inc.; 2006.
[29.] Kumar R, Singh M. Tannins: their adverse role in ruminant nutrition. J Agric Food Chem 1984;32:447-53.
[30.] Delgado DC, Galindo J, Ibett JCO, Dominguez M, Dorta N. Supplementation with foliage of L. leucocephala. Its effect on the apparent digestibility of nutrients and production of methane in sheep. Rev Cub Cienc Agric 2013;47:267-71.
[31.] Min BR, Pinchak WE, Anderson RC, Fulford JD, Puchala R. Effects of condensed tannins supplementation level on weight gain and in vitro and in vivo bloat precursors in steers grazing winter wheat. J Anim Sci 2006;84:2546-54.
[32.] Beauchemin KA, McGinn SM, Martinez TF, McAllister TA. Use of condensed tannin extract from quebracho trees to reduce methane emissions from cattle. J Anim Sci 2007;85: 1990-6.
[33.] Grainger C, Clarke T, Auldist MJ, et al. Potential use of Acacia mearnsii condensed tannins to reduce methane emissions and nitrogen excretion from grazing dairy cows. Canadian J Anim Sci 2009;89:241-51.
[34.] Dias-Moreira G, Tavares-Lima P de M, Oliveira-Borge B, et al. Tropical tanniniferous legumes used as an option to mitigate sheep enteric methane emission. Trop Anim Health Prod 2013; 45:879-82.
[35.] Puchala R, Animut G, Patra AK, et al. Methane emissions by goats consuming Sericea lespedeza at different feeding frequencies. Anim Feed Sci Technol 2012;175:76-84.
[36.] Tan HY, Sieo CC, Abdullah N, et al. Effects of condensed tannins from Leucaena on methane production, rumen fermentation and populations of methanogens and protozoa in vitro. Anim Feed Sci Technol 2011;169:185-93.
[37.] Molina-Botero IC, Cantet JM, Montoya S, Correa-Londono GA, Barahona-Rosales R. In vitro methane production from two tropical grasses alone or in combination with Leucaena leucocephala or Gliricidia sepium. Ces Med Vet Zootec 2013; 8:31.
[38.] Animut G, Puchala R, Goetsch AL, et al. Methane emission by goats consuming diets with different levels of condensed tannins from lespedeza. Anim Feed Sci Technol 2008;144:212
[39.] Pinares-Patino CS, Ulyatt MJ, Lassey KR, Barry TN, Holmes CW. Rumen function and digestion parameters associated with differences between sheep in methane emissions when fed chaffed lucerne hay. J Agric Sci 2003;140:205-14.
[40.] Assoumaya C, Sauvant D, Archimede H. Comparative study of ingestion and digestion of tropical and temperate forage. INRA Prod Anim 2007;20:383-92.
[41.] Jayanegara A, Leiber F, Kreuzer M. Meta-analysis of the relationship between dietary tannin level and methane formation in ruminants from in vivo and in vitro experiments. J Anim Physiol Anim Nutr 2012;96:365-75.
[42.] Traiyakun S, Harakord W, Yuangklang C, Paengkoum P. Leucaena leucocephala meal as replacement to soybean meal in growing goat diets. J Agric Sci Technol 2011;1:1150-4.
[43.] Osakwe II, Steingass H. Ruminal fermentation and nutrient digestion in West African Dwarf (WAD) sheep fed Leucaena leucocephala supplemental diets. Agroforest Syst 2006;67:12933.
[44.] Soltan YA, Morsy AS, Sallam SMA, Louvandini H, Abdalla AL. Comparative in vitro evaluation of forage legumes (prosopis, acacia, atriplex, and leucaena) on ruminal fermentation and methanogenesis. J Anim Feed Sci 2012;21:759-72.
[45.] Tiemann TT, Lascano CE, Wettstein HR, et al. Effect of the tropical tannin-rich shrub legumes Calliandra calothyrsus and Flemingia macrophylla on methane emission and nitrogen and energy balance in growing lambs. Animal 2008;2:790-9.
[46.] Finlay BJ, Esteban G, Clarke KJ, et al. Some rumen ciliates have endosymbiotic methanogens. FEMS Microbiol Lett 1994;117: 157-61.
[47.] Galindo J, Gonzalez N, Delgado D, et al. Modulating effect of Leucaena leucocephala on the ruminal microbiota. Zootec Trop 2008;26:249-52.
[48.] Yanez-Ruiz DR, Hart KJ, Martin-Garcia IA, Ramos S, Newbold CJ. Diet composition at weaning affects the rumen microbial population and methane emissions by lambs. Aust J Exp Agric 2008;48:186-8.
[49.] Coleman GS. The distribution of carboxymethylcellulase between fractions taken from the rumen of sheep containing no protozoa or one of five different protozoal populations. J Agric Sci 1986;106:121-7.
[50.] Demeyer DL. Rumen microbes and digestion of plant cell walls. Agric Environ 1981;6:295-337.
[51.] Sliwinski BJ, Carla RS, Machmuller A, Kreuze M. Efficacy of plant extracts rich in secondary constituents to modify rumen fermentation. Anim Feed Sci Technol 2002;101:101-14.
Angel T. Pineiro-Vazquez (1,2)*, Jorge R. Canul-Solis (1), Guillermo O. Jimenez-Ferrer (3), Jose A. Alayon-Gamboa (4), Alfonso J. Chay-Canul (5), Armin J. Ayala-Burgos (1), Carlos F. Aguilar-Perez (1), and Juan C. Ku-Vera (1)
* Corresponding Author: Angel T. Pineiro-Vazquez Tel: +52-9991013338, Fax: +52-9991013338, E-mail: email@example.com
(1) Facultad de Medicina Veterinaria y Zootecnia, Universidad Autonoma de Yucatan. C.P. 97300 Merida, Yucatan, Mexico
(2) Instituto Tecnologico de Conkal, Avenida Tecnologico s/n C.P. 97345 Conkal, Yucatan, Mexico
(3) El Colegio de la Frontera Sur (ECOSUR), Ganaderia y Ambiente, Carretera Panamericana y Periferico Sur s/n, Barrio Maria Auxiliadora, San Cristobal de Las Casas, Chiapas 29290, Mexico
(4) El Colegio de la Frontera Sur, Unidad Campeche, Mexico. Av. Rancho Poligono 2-A, Ciudad Industrial Lerma, C.P.24500, Campeche, Mexico
(5) Division Academica de Ciencias Agropecuarias, Universidad Juarez Autonoma de Tabasco, Carretera Villahermosa-Teapa, km 25, R/a. La Huasteca 2a. Seccion, C.P. 86280 Villahermosa, Tabasco, Mexico
Angel T. Pineiro-Vazquez
Submitted Mar 15, 2017; Revised May 31, 2017; Accepted Oct 22, 2017
Table 1. Chemical composition of the forages (g/kg DM) Pennisetum Leucaena Item purpureum leucocephala Organic matter 930.32 940.5 Crude protein 60.64 160.29 NDF 670.62 580.85 ADF 410.99 420.01 Lignin 70.24 160.0 Secondary metabolites (g/kg DM) Total phenols (1) 0 7.7 Condensed tannins (2) 0 21.0 DM, dry matter; NDF, neutral detergent fiber; ADF, acid detergent fiber. (1) Expressed as g tannic acid eq/kg DM. (2) Expressed as g leucocyanidin eq/kg DM. Table 2. Intake and apparent digestibility in crossbred heifers fed Pennisetum purpureum grass and increasing levels of Leucaena leucocephala Percentage of L. leucocephala supplemented (% of DM) Items 0 20 40 60 BW (kg) 293.80 298.80 289.20 298.20 Intake DM (kg/d) 7.03 7.15 7.07 7.00 OM (kg/d) 6.54 6.70 6.62 6.53 CP (kg/d) 0.50 0.70 0.82 0.93 NDF (kg/d) 4.63 4.50 4.30 4.10 ADF (kg/d) 2.85 2.81 2.77 2.67 Digestible intake (kg/d) DDM 3.90 3.71 3.46 3.46 OMD 3.72 3.54 3.32 3.29 NDFD 2.60 2.15 1.91 1.77 ADFD 1.55 1.30 1.12 1.05 Percentage of Contrast L. leucocephala supplemented (% of DM) Items 80 SE L BW (kg) 295.40 6.81 Intake DM (kg/d) 7.00 0.60 ns OM (kg/d) 6.50 0.55 ns CP (kg/d) 1.22 0.10 ** NDF (kg/d) 3.83 0.40 ns ADF (kg/d) 2.50 0.25 ns Digestible intake (kg/d) DDM 3.40 0.54 ns OMD 3.21 0.52 ns NDFD 1.51 0.33 * ADFD 0.81 0.22 * DM, dry matter; SE, standard error; L, linear contrast; BW, body weight; OM, organic matter; CP, crude protein; NDF, neutral detergent fiber; ADF, acid detergent fiber; DDM: digestible dry matter; OMD: digestible organic matter; NDFD: digestible neutral detergent fiber; ADFD: digestible acid detergent fibre. * p<0.05; ** p<0.01; ns: non-significant (p>0.05). No significant effects were found for the quadratic and cubic contrasts. Table 3. Methane (C[H.sub.4]) production in crossbred heifers fed Pennisetum purpureum grass and increasing levels of Leucaena leucocephala Percent of L. leucocephala supplemented (% of DM) Items 0 20 40 60 80 BW(kg) 293.8 298.8 289.2 298.2 295.4 Enteric methane L C[H.sub.4]/d 137.3 101.2 87.4 74.9 53.5 L C[H.sub.4]/kg of DMI 20.1 14.7 12.1 10.5 7.7 L C[H.sub.4]/kg of OMI 21.6 15.7 13.0 11.2 8.3 L C[H.sub.4]/kg of NDFI 30.4 23.3 20.0 17.9 14.3 L C[H.sub.4]/kg of ADFI 49.1 37.2 31.0 27.7 21.9 L of methane/kg of digestible fractions intake L C[H.sub.4]/kg of DDM 37.7 30.3 25.8 22.7 17.3 L C[H.sub.4]/kg of OMD 39.6 31.6 26.9 23.9 18.5 L C[H.sub.4]/kg of NDFD 56.5 52.4 47.6 48.7 49.2 L C[H.sub.4]/kg of ADFD 92.0 86.1 84.5 88.8 131.5 Contrast Items SE L Q C BW(kg) 6.8 Enteric methane L C[H.sub.4]/d 14.8 ** ns ns L C[H.sub.4]/kg of DMI 2.1 ** ns ns L C[H.sub.4]/kg of OMI 2.3 ** ns ns L C[H.sub.4]/kg of NDFI 3.4 ** ns ns L C[H.sub.4]/kg of ADFI 5.3 ** ** ns L of methane/kg of digestible fractions intake L C[H.sub.4]/kg of DDM 5.1 ** ns ns L C[H.sub.4]/kg of OMD 5.4 ** ns ns L C[H.sub.4]/kg of NDFD 11.5 ns ns ns L C[H.sub.4]/kg of ADFD 33.2 ns ns ns DM, dry matter; SE, standard error; L, linear contrast; Q, quadratic contrast; C, cubic contrast; BW, body weight; DMI, dry matter intake; OMI, organic matter intake; NDFI, neutral detergent fiber intake; ADFI, acid detergent fiber intake; DDM, digestible dry matter; OMD, digestible organic matter; NDFD, digestible neutral detergent fiber; ADFD, digestible acid detergent fiber. * p<0.05; ** p<0.01; ns, non-significant (p>0.05). Table 4. Effects of CT on ruminal pH, N-N[H.sub.3], and volatile fatty acids (VFA's) in crossbred heifers fed Pennisetum purpureum grass and increasing levels of Leucaena leucocephala Percent of L. leucocephala supplemented (% of DM) Items 0 20 40 60 80 Rumen pH 6.8 6.9 6.7 6.8 6.8 Rumen N-N[H.sub.3] (mg/dL) 15.3 22.0 27.3 34.0 36.5 Volatile fatty acids concentration (mmol/L) Acetate 52.6 54.8 53.4 52.1 54.4 Propionate 13.6 13.1 12.8 12.2 12.8 Butyrate 6.1 6.1 5.6 5.3 5.4 Isobutyric 0.4 0.36 0.4 0.37 0.3 Valeric 0.3 0.34 0.4 0.4 0.4 Isovaleric 0.2 0.2 0.2 0.2 0.2 TotalVFA 73.5 75.0 72.9 70.7 73.8 A:P 3.8 4.1 4.1 4.2 4.2 Molar proportions of VFA (%) Acetate 71.4 72.9 73.1 73.5 73.5 Propionate 18.6 17.6 17.7 17.4 17.5 Butyrate 8.5 8.3 7.7 7.6 7.5 Isobutyric 0.5 0.5 0.5 0.5 0.5 Valeric 0.4 0.4 0.5 0.6 0.6 Isovaleric 0.3 0.3 0.3 0.3 0.3 Contrast Items SE L Q C Rumen pH 0.10 ns ns ns Rumen N-N[H.sub.3] (mg/dL) 0.07 ** ns ns Volatile fatty acids concentration (mmol/L) Acetate 5.31 ns ns ns Propionate 1.14 ns ns ns Butyrate 0.47 ns ns ns Isobutyric 0.04 ns ns ns Valeric 0.04 * ns ns Isovaleric 0.04 ns ns ns TotalVFA 6.90 ns ns ns A:P 0.10 * ns ns Molar proportions of VFA (%) Acetate 0.67 * ns ns Propionate 0.33 * ns ns Butyrate 0.41 ns ns ns Isobutyric 0.05 ns ns ns Valeric 0.04 ** ns ns Isovaleric 0.06 * ns ns CT, condensed tannins; NH3, ammonia; DM, dry matter; SE, standard error; L, linear contrast; Q, quadratic contrast; C, cubic contrast; A:P, acetic:propionic relationship. * p<0.05; ** p<0.01; ns, non-significant (p>0.05). Table 5. Population of rumen protozoa ([log.sub.10] cells /mL) in crossbred heifers fed Pennisetum purpureum grass and increasing levels of Leucaena leucocephala Percent of L. leucocephala supplemented (% of DM) Items 0 20 40 60 80 SE Population of rumen protozoa Holotrich ([log.sub.10]) 4.0 4.1 4.1 3.9 4.1 0.18 Entodiniomorph ([log.sub.10]) 5.5 5.3 5.5 5.5 5.5 0.07 Total protozoa ([log.sub.10]) 9.5 9.4 9.6 9.3 9.6 0.19 Contrast Items L Q C Population of rumen protozoa Holotrich ([log.sub.10]) ns ns ns Entodiniomorph ([log.sub.10]) ns ns ns Total protozoa ([log.sub.10]) ns ns ns DM, dry matter; SE, standard error; L, linear contrast; Q, quadratic contrast; C, cubic contrast. * p<0.05; ** p<0.01; ns, non-significant (p>0.05).
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|Author:||Pineiro-Vazquez, Angel T.; Canul-Solis, Jorge R.; Jimenez-Ferrer, Guillermo O.; Alayon-Gamboa, Jose|
|Publication:||Asian - Australasian Journal of Animal Sciences|
|Date:||Nov 1, 2018|
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