Next Article in Journal
Omics Profiles of the Null Segregants of RNA-Directed DNA Methylation-Positive Tobacco Plants
Previous Article in Journal
Addressing Black Soil Compaction: An Integrated Analysis of the Mechanisms, Efficacy, and Future Directions of Conservation Tillage
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Agronomic and Nutritional Potential of Ryegrass (Lolium multiflorum Lam.) Accessions as Raw Material for Silage in the Tropical Andes of Peru

by
Leidy G. Bobadilla
1,2,*,
Miguel A. Altamirano-Tantalean
2,
William Carrasco-Chilón
3,
Vanesa Lizbeth Silva Baca
2,
Flor L. Mejía
2,
Ysai Paucar
2,
Leandro Valqui
2,
William Bardales
4,
Jorge L. Maicelo
2 and
Héctor V. Vásquez
1,2,*
1
Escuela de Posgrado, Programa Doctoral en Ciencias para el Desarrollo Sustentable, Facultad de Ingeniería Zootecnista, Biotecnología, Agronegocios y Ciencia de Datos, Universidad Nacional Toribio Rodríguez de Mendoza de Amazonas, Chachapoyas 01001, Peru
2
Laboratorio de Agrostología, Instituto de Investigación en Ganadería y Biotecnología, Facultad de Ingeniería Zootecnista, Biotecnología, Agronegocios y Ciencia de Datos, Universidad Nacional Toribio Rodríguez de Mendoza de Amazonas, Chachapoyas 01001, Peru
3
Dirección de Desarrollo Tecnológico Agrario, Instituto Nacional de Innovación Agraria (INIA), Estación Experimental de Baños del Inca, Jr. Wiracocha s/n, Baños del Inca, Cajamarca 06004, Peru
4
Instituto de Investigación en Ganadería y Biotecnología, Facultad de Ingeniería Zootecnista, Biotecnología, Agronegocios y Ciencia de Datos, Universidad Nacional Toribio Rodríguez de Mendoza de Amazonas, Chachapoyas 01001, Peru
*
Authors to whom correspondence should be addressed.
Agronomy 2026, 16(2), 275; https://doi.org/10.3390/agronomy16020275
Submission received: 10 December 2025 / Revised: 18 January 2026 / Accepted: 19 January 2026 / Published: 22 January 2026
(This article belongs to the Section Grassland and Pasture Science)

Abstract

In the tropical Andes, rangeland degradation has become one of the main threats to the sustainability of livestock production in the face of climate change. In this context, optimizing the yield and nutritional quality of raw material for silage is essential to sustain livestock productivity. The aim of this study was to identify local accessions (LM) of Lolium multiflorum Lam. with greater forage potential through evaluations in consecutive cuts made at the anthesis phenological stage, using a randomized complete block design with four replicates and ten local accessions (LM1, LM2, LM3, LM4, LM6, LM7, LM8, LM11, LM12 and LM13). The statistical analysis, based on linear mixed models, showed that cuts at anthesis had a significant effect among accessions, revealing high variability in agronomic and nutritional performance across cuts. In LM4, plant height at the fourth cut was 2.48-fold higher than at the first cut. Likewise, LM4 and LM13 were identified as the latest accessions to reach anthesis in the first cut, with a decreasing trend across cuts and stabilization from the third cut onward. These accessions also showed the greatest basal coverage area, increasing 9.94- and 8.18-fold in the fourth cut relative to the first. Fresh forage yields in LM4 and LM13 increased 13.2- and 10.1-fold, and dry matter yields 13.98- and 9.86-fold, compared with the first cut. They also exhibited the highest average daily dry matter ac-cumulation rate. By contrast, the fresh forage and dry matter yields of the remaining accessions were significantly lower than those of LM4 and LM13. The main difference between these two accessions was observed in dry matter percentage, with higher values and a stable trend in LM4 across all cuts. In terms of nutritional quality, LM4 presented crude protein of 24.2% in the second cut and 24.0% in the fourth cut, while digestibility was 86.2% in the second cut and 85.0% in the fourth cut. In conclusion, although the ensiling process was not evaluated in this study, LM4 showed the most stable and outstanding values in both agronomic and nutritional performance, thus emerging as a promising accession for selection and use as raw material for silage production in the tropical Andes.

1. Introduction

Cattle farming plays a fundamental role in food security, providing proteins and micronutrients that are essential in the human diet [1,2]. In Peru, there are more than 881,000 cattle producers, over 40% of whom live in poverty and operate farms smaller than 5 ha [3,4]. In the Amazonas region, around 16% of the land area has been affected by anthropogenic activities, and more than 70% of this area is degraded, with low-quality native grasslands, deteriorated improved pastures, and reduced availability of fallow land due to the conversion of grasslands and scrublands into cropland [5,6,7].
Currently, climate change is one of the main challenges for cattle production, as it reduces food supply through prolonged droughts, strong seasonality, temperature fluctuations, and an increased presence of pests and diseases, thereby increasing the vulnerability of small-scale cattle producers [8,9]. In addition, extensive pastoralism practices, which require high labor demand and large areas of pasture, have driven the transition to stall systems [10,11]. As a result, livestock farmers have become increasingly dependent on imported feed supplements, which has raised production costs and undermined their financial sustainability [12,13].
Faced with this problem, many producers resort to using Pennisetum clandestinum, a species considered invasive and used mainly as a secondary forage resource [14]. This situation implies the need for forages with greater agronomic and nutritional potential, in order to help reduce risk factors in production. However, the indiscriminate introduction of exotic or highly improved fodder genotypes can reduce local biodiversity and accelerate the degradation of ecosystems [15]. The genus Lolium, although not native to the Tropical Andes of Peru, stands out for its resistance and tolerance to different altitudinal zones; its acclimatization to cold reveals a valuable genetic reservoir against frost and drought [16], demonstrating an adaptive capacity between 1800 and 3600 m above sea level, with low levels of damage and incidence of pests and diseases [17].
It should be noted that yields and nutritional composition vary among Lolium species [18]. Lolium multiflorum Lam. stands out for its usefulness in the phytoremediation of contaminated soils, accelerating the degradation of polycyclic aromatic hydrocarbons (PAHs), such as phenanthrene, and reducing their half-life [19]. It also increases nitrogen (N) adsorption in the soil and significantly reduces nitrate leaching compared to Lolium perenne [20], and has superior ensilability, with greater stability and quality than other species of the genus [21]. However, the growth cycle of ryegrass depends on both the genotype and the environment in which it develops, revealing differences between varieties in days to flowering, days to anthesis, persistence, longevity, yield, and nutritional composition [22,23,24,25]. These differences may be associated with responses to photoperiod and vernalization requirements [26,27], as well as functional traits such as root architecture and regrowth capacity, which determine tolerance to water and heat stress and production stability between harvests [28,29,30].
In this context, one alternative is to evaluate locally sourced ryegrass (Lolium multiflorum Lam.) varieties from other regions of the country, selected for their origin in environments with altitudinal zones and agroecological conditions similar to those of the study area. In the Peruvian Tropical Andes, there is still limited scientific evidence on the agronomic and nutritional performance of local ryegrass accessions, justifying the need to establish a scientific basis that can guide the future sustainability of livestock systems [31,32].
The lack of appropriate technologies for forage conservation during critical periods of scarcity restricts producers’ options for dealing with climate variability. In response, producers often increase animal stocking rates to compensate for yield losses, which reduces the forage available per head and makes system performance more dependent on herd size than on individual performance, thus reducing meat and milk yields [33,34]. In addition, as forage matures, its digestibility decreases and it becomes less viable for consumption as fresh forage, being better utilized in silage [35]. Therefore, the initial evaluation of the harvested material is key to determining its suitability during the silage process and future losses of dry matter and nutritional value at each stage, allowing for improved planning to cope with critical periods and reduce forage losses, thus contributing to the stability of the system [36,37].
There is wide range of unexplored genetic diversity regarding how its agronomic and nutritional characteristics vary when used as raw material for silage under the conditions of the tropical Andes of Peru. In this context, the objective of this study was to identify local accessions of Lolium multiflorum Lam. with greater forage potential through evaluations in consecutive cuts made at the anthesis phenological stage. The hypothesis was that, even when evaluated at anthesis and under similar agroecological conditions, the accessions differ consistently in yield and nutritional composition, and that the changes resulting from consecutive cuts do not occur to the same extent in all of them. In particular, it is expected that at least one accession will combine higher yield and nutritional value with greater stability between cuts, expressed as less variation of these attributes throughout the cuts, positioning itself as a promising candidate as raw material for forage conservation strategies. This study generated an experimental database describing the behavior of little-explored local accessions. It is important to note that this study only evaluated the harvested forage as silage raw material (agronomic and nutritional characteristics) and did not assess the ensiling process or fermentation quality. Therefore, our study was limited to the silage potential inferred from the raw material attributes and highlights the need for future research on silage quality and the management of these accessions under different conditions in the Peruvian tropical Andes. Our results can guide producers’ decision-making to reduce the impact of climate change without compromising ecosystems in the Tropical Andes, thus contributing to the sustainability of livestock systems.

2. Materials and Methods

2.1. Description of the Research Area

The study was conducted in the province of Chachapoyas, Amazonas region, Peru, at an altitude of 2446 m above sea level, with coordinates 77°51′43.82″ W longitude and 6°12′27.35″ S latitude. During the experimental period, from July 2024 to June 2025, meteorological data were collected using a Vantage Pro2-Davis station (Davis Instruments Corp., Hayward, CA, USA). As shown in Figure 1, data were recorded for the following parameters: temperature (maximum: 21.16 ± 1.94 °C; minimum: 10.37 ± 1.76 °C) (Figure 1b,c), relative humidity (78.15 ± 8.21%), and precipitation (2.26 ± 5.12 mm day−1) (Figure 1a,d). Values are reported as mean ± standard deviation (SD).
Likewise, soil sampling was carried out based on the Peruvian state’s soil study regulations DS No. 013-2010-AG [38]. In the total area of the investigation (525 m2), a zigzag route was carried out marking 10 sampling points. The surface of each point was cleaned and a shovel was inserted to a depth of 32 cm. The extracted subsamples were mixed and homogenized and, applying the quartering method, a composite sample of 1 kg was formed [39]. Next, the samples were then coded and transferred to the Laboratorio de Investigación de Suelos y Aguas (LABISAG) at the Universidad Nacional Toribio Rodríguez de Mendoza de Amazonas, accredited by the Instituto Nacional de Calidad, Ministerio de Producción, in accordance with standard NTP-ISO/IEC 17025:2017 [40]. The physicochemical parameters were analyzed according to the Bazán methodology [41], indicating a clayey-sandy texture (sand 48%, silt 10% and clay 42%). In addition, the pH (5.5), electrical conductivity (0.07 dS m−1), organic matter content (4.47%), carbon (2.59%), nitrogen (0.22%), phosphorus (10.19 ppm) and potassium (175.21 ppm) were determined.

2.2. Obtaining Plant Material

The ten ryegrass (Lolium multiflorum Lam.) accessions were acquired from an altitude of 2667 m above sea level, with geographic coordinates 78°27′07″ W longitude and 07°09′56″ S latitude. The field evaluation, however, was conducted at 2446 m above sea level; this altitudinal difference was considered moderate and not expected to markedly affect plant establishment under the study conditions. These accessions were under ex situ conservation in the Programa Nacional de Investigación en Pastos y Forrajes del Instituto Nacional de Innovación Agraria (INIA), located at the Estación Experimental Agraria Baños del Inca in the department of Cajamarca. All accessions were collected in the department of Cajamarca for conservation in the germplasm bank; the origin characteristics of each accession are described in Table 1. Among the characteristics of the conservation area was a relatively stable day length throughout the year, with a maximum photoperiod of approximately 12.1 h. The propagation method in our study was vegetative, using clumps (planting points) of eight 12 cm-long tillers taken from vigorous mother plants in optimal phytosanitary conditions to obtain identical plants. The accessions were selected for their fresh forage yields exceeding 800 kg ha−1 and for being considered local accessions. For transport, the tillers were removed with the corresponding portion of soil adhering to the roots and placed in Kraft paper bags containing moistened paper towels to prevent dehydration of the plant material during transport prior to planting.

2.3. Experimental Design

The study was conducted using a randomized complete block design (RCBD) with four replicates (blocks). The local accessions factor included 10 levels: LM1, LM2, LM3, LM4, LM6, LM7, LM8, LM11, LM12, and LM13. In each block, one plot was established per accession (10 plots per block), for a total of 40 experimental units (Figure 2). Four successive cuts were made on each experimental unit, considering four levels: first, second, third, and fourth cuts; each cut was made when each accession reached anthesis. Agronomic parameters were evaluated in the four cuts, while nutritional parameters were evaluated only in the second and fourth cuts.

2.4. Establishment of the Experimental Area

Land preparation began with primary tillage using a disc plow at a depth of 32 cm to loosen the soil. Secondary tillage was carried out with two cross-passes of an offset disc harrow to break up soil clods, followed by a final pass with a leveling harrow to even out the surface and prepare the land for planting. The layout of the experimental units and the opening of furrows were performed manually using stakes, string, and hand tools. Each experimental unit consisted of a 2 m × 3 m (6 m2) plot, with 1.5 m spacing between plots and between blocks. Planting was carried out manually on 1 July 2024, using groups of eight tillers for each ryegrass (Lolium multiflorum Lam.) accession. Planting was uniform, with 0.75 m between clumps (planting points) and 0.75 m between rows. Each experimental unit contained eight clumps, and each clump was established with eight tillers. The plant material was provided by the Germplasm Bank of the Programa Nacional de Investigación en Pastos y Forrajes del Instituto Nacional de Innovación Agraria (INIA). Fertilization consisted of applying chicken manure at a rate of 300 g m−2, containing 2.67% nitrogen, 3.74% phosphorus, and 2.19% potassium. Irrigation was applied using a sprinkler system with a flow rate of 25 L s−1. During the first two weeks after sowing, irrigation was applied twice per week, with each irrigation event lasting 20 min. This resulted in an irrigation depth of approximately 46 mm per event, equivalent to a total weekly irrigation of 92 mm (equivalent to 922 m3 ha−1). Subsequently, irrigation frequency was reduced and adjusted according to rainfall conditions. Weed control was carried out manually every 10 days based on prior monitoring. For pest and disease management, carbendazim (200 mL ha−1) was applied to control Puccinia graminis, and cypermethrin (300 mL ha−1) to control Dalbulus maidis.

2.5. Evaluation Parameters

2.5.1. Qualitative Morphological Characterization

The morphological characterization of the ten accessions was performed to identify possible variations associated with the study conditions and their agronomic usefulness. Growth habit was evaluated to describe plant architecture; leaf color was evaluated as a visual indicator of chlorophyll status and vigor; and traits such as basal node and texture were evaluated to differentiate between accessions and possible implications for palatability. The evaluation was performed following the criteria of Maity et al. [42], as shown in Table 2.

2.5.2. Plant Height

Plant height was recorded for each accession when it reached anthesis. Measurements were taken using a Bahco flexometer (SNA Europe SAS, Éragny-sur-Oise, France), selecting six groups at random and measuring from the base of the stem (ground level) to the tip of the tallest leaf [43].

2.5.3. Days to Anthesis

Days to anthesis were defined as when 70% of the clumps in each experimental unit had flowers with fully emerged anthers and stigmas [44].

2.5.4. Basal Coverage Area

Basal coverage area was assessed by selecting six groups per experimental unit. In each group, the major and minor diameters were measured at ground level, and the cover area was calculated using the formula for the area of an ellipse [45]. The formula Equation (1) is expressed as:
B a s a l   c o v e r a g e   a r e a c m 2 = π L D 2 M D 2  
where LD: largest diameter (cm) and MD: minor diameter (cm).

2.5.5. Yield Parameters

Fresh forage yield was determined by harvesting a 1 m2 quadrat located in the central area of each 2 × 3 m plot, avoiding plot borders to minimize edge effects. The harvest was carried out at a height of 5 cm from ground level and the forage obtained was weighed in situ using an electronic scale (precision ± 5 g). The data were recorded in a field book in units of kg m−2. In addition, 1000 g of fresh forage was extracted from each sample and placed in an oven for 72 h at a temperature of 60 °C until a constant weight was reached. The dry matter (%) was calculated by dividing the dry weight by the fresh weight and multiplying the result by 100. To calculate the dry forage yield (t ha−1), the fresh forage yield was first extrapolated to t ha−1 and multiplied by the dry matter percentage (%).

2.5.6. Dry Matter Accumulation Rate

The average dry matter accumulation rate was calculated by dividing the dry matter yield by the number of days elapsed until anthesis for each accession in each cut. The results were expressed in kg ha−1 day−1 [46].

2.5.7. Nutritional Composition

Nutritional analysis was performed at the Laboratorio de Nutrición Animal y Bromatología (LABNUT) de la Universidad Nacional Toribio Rodríguez de Mendoza de Amazonas, where neutral detergent fiber (NDF), acid detergent fiber (ADF), protein, and digestibility were evaluated. Samples were transported from the field to the laboratory in labeled Kraft paper bags. The samples were then divided into 5- to 10 cm segments, and 250 to 500 g of chopped sample were collected for each experimental unit. The resulting material was placed in new, pre-weighed Kraft paper bags. The initial fresh weight was recorded on a gram scale, and the sample was subsequently dried at 60 °C for 48 h in a forced-air oven until a constant weight was reached. Once the dried sample was obtained, its dry weight was recorded, and it was then ground in a hammer mill with a 2 mm screen for subsequent analysis.
Crude protein content was processed using AOAC Method No. 928.08 [47]. This procedure involved digesting the sample with sulfuric acid and converting the nitrogen to ammonia, followed by quantification by titration with hydrochloric acid. The nitrogen obtained was then multiplied by 6.25 to estimate the crude protein concentration. NDF and ADF were determined using the ANKOM A200 procedure [48]. NDF was quantified using a neutral detergent solution in the presence of alpha-amylase and sodium sulfite, followed by rinsing with acetone and oven drying. ADF was measured using an acidic detergent solution, followed by filtration and oven drying. In vitro digestibility was determined using the ANKOM DAISY II Incubator system, following the standardized protocol of ANKOM Technology for forage and fibrous materials. The dry, ground samples were weighed at 0.50 g in ANKOM F57 filter bags that had been pre-washed with acetone for 5 min and completely dried at room temperature to remove surfactants that could inhibit microbial activity. The bags were heat-sealed and placed in the digestion jars in the incubator, including one blank filter bag per jar for subsequent correction. Two buffer solutions were used: buffer solution A, composed of por KH2PO4 (10 g L−1), MgSO4. 7 H2 O (0.5 g L−1), NaCL (0.5 g L−1), CaCl2. 2H2 (0.1 g L−1), and reagent-grade urea (0.5 g L−1), and buffer solution B, composed of por Na2CO3 (15 g L−1) y Na2S. 9H2O (1 g L−1). Both solutions were preheated to 39 °C and mixed in a 1:5 ratio (B:A) until a final pH of 6.8 was reached. For each digestion beaker, 1600 mL of the buffer mixture was added, and the beaker were placed in the incubator, allowing thermal stabilization for 30 min before the addition of the ruminal inoculum.
The ruminal fluid was obtained from a single bovine. Collection was performed using thermos preheated with water at 39 °C to preserve microbial activity. At the time of collection, the hot water was removed to introduce the ruminal fluid. It was transported to the laboratory within 30 min of collection, where the ruminal fluid was extracted from the thermos and homogenized in a blender (previously heated and purged with CO2) for 30 s. This procedure allowed the microorganisms adhering to the fibrous fraction to be detached. The material was then filtered through four layers of gauze to obtain the clarified ruminal fluid in a previously heated container, purged with CO2 during the transfer of the inoculum.
Once the digestion beaker had reached thermal stability, they were individually removed from the incubator, and 400 mL of rumen fluid was added to each beaker. Subsequently, each beaker was purged with CO2 for approximately 30 s, creating a gaseous atmosphere over the contents without allowing direct bubbling in the liquid medium, and then hermetically sealed. Incubation was carried out for 48 h in an ANKOM DAISY II incubator, which provides continuous stirring and automatic temperature control, maintaining a temperature of 39.5 ± 0.5 °C. At the end of the incubation period, the beaker were drained, and the filter bags were gently rinsed twice with cold distilled water to remove excess digestion solution and soluble compounds. Subsequently, the bags were treated with a neutral detergent solution in an ANKOM fiber analyzer to remove microbial residues and remaining soluble fractions. In vitro digestibility was calculated from the final NDF residue, applying the correction for white bags, according to the standard equations of the DAISY II method [49].

2.6. Data Analysis

Data analysis was performed using Rstudio software version 4.5.0 for Windows. Statistical analysis was based on a linear mixed-effects model using the lmer function of the lme4 package [50]. The model included accessions and cuts as fixed effects, as well as their bidirectional interaction (accessions × cut). Likewise, the block and the plot nested within the block were included as random terms in order to capture possible variability between experimental units. The assumptions of normality and homogeneity of variances of the model were validated by visual inspection of diagnostic graphs. To determine statistical differences in fixed effects, a type III analysis of variance (ANOVA) was used with the Kenward-Roger method using the lmerTest package [51]. When significance was found, simple effects were analyzed by comparing estimated marginal means with the emmeans package [52] applying Sidak’s adjustment. Data not meeting model assumptions were natural log-transformed prior to analysis. For biological interpretation, table values are reported as back-transformed estimated marginal means on the original scale using the exponential function.

3. Results

3.1. Parameters’ Morphology

3.1.1. Qualitative Morphological Evaluation

The ten accessions presented different qualitative morphological characteristics, indicating diversity in physical attributes between accessions over the course of their development, as shown in Table 3.
Figure 3 shows the differences in the coloration of the basal node of three local accessions, which reveals marked variation between them.

3.1.2. Plant Height

Plant height revealed significant effects of the accessions (p < 0.001) and cuts (p < 0.001), as well as their interaction (p < 0.001). During the first cut, LM12 had the greatest regrowth height (31.5 ± 0.5 cm); however, regrowth height decreased to 20.4 ± 0.3 cm by the fourth cut. Accession LM13 had the greatest plant height in the second cut (33.7 ± 0.3 cm) and in the third cut (60.1 ± 0.7 cm), but this upward trend was not maintained in the fourth cut, where regrowth height decreased to 53.8 ± 0.4 cm. In contrast, LM4 showed a sustained increase in plant height across cuts, reaching the greatest value in the fourth cut (57.7 ± 0.6 cm), which was 2.48 times greater than in the first cut (Table 4).

3.1.3. Basal Coverage Area and Days to Anthesis

Basal coverage area and days to anthesis showed significant effects of accessions (p < 0.001) and cuts (p < 0.001), as well as their interaction (p < 0.001). Both variables showed different patterns among accessions in the different cuts (Table 5). Basal coverage area increased significantly in LM4 and LM13, which showed the largest and most consistent increases from the first to the fourth cut (LM4: 33.8 ± 0.9 to 336.0 ± 5.8 cm2; LM13: 47.2 ± 3.3 to 386.2 ± 5.9 cm2), while the lowest coverage in the fourth cut was recorded for LM1 (17.5 ± 0.9 cm2) and LM3 (17.3 ± 1.2 cm2). In terms of days to anthesis, most accessions remained below 50 days in all cuts, while LM4 and LM13 were markedly later in the first cut (120.8 ± 2.4 and 132.2 ± 2.6 days, respectively) and then showed pronounced reductions in subsequent cuts, with smaller changes between the third and fourth cuts (LM4: 65.5 ± 1.8 vs. 70.0 ± 0.0; LM13: 57.8 ± 1.7 vs. 57.2 ± 1.4 days). When summarizing the pattern as the average of the second to fourth cuts in relation to the first cut, LM4 decreased from 120.8 to 74.5 days on average, and LM13 from 132.2 to 63.3 days, while the previous accessions, such as LM1, LM3, and LM6, showed comparatively smaller differences between the first cut and the average of the second to fourth cuts. Overall, LM4 and LM13 combined the greatest basal expansion with a marked reduction in time to anthesis after the first cut, while the remaining accessions generally maintained earlier flowering and lower Basal coverage area.

3.2. Parameters’ Yield

3.2.1. Fresh Forage and Dry Matter Yields

Fresh forage and dry matter yields (Table 6) showed significant effects of accessions (p < 0.001) and cuts (p < 0.001), as well as their interaction (p < 0.001). Fresh forage yield (t ha−1) in all accessions did not exceed the threshold of 0.80 t ha−1 in any cut, with the exception of LM13 and LM4, which easily exceeded the threshold across all cuts. During the first cut, LM13 (1.75 ± 0.04 t ha−1) showed the highest average, being statistically superior to LM4 (1.01 ± 0.05 t ha−1) by 73.27% in fresh forage. However, after the second cut onwards, LM4 and LM13 consistently showed the highest averages without statistical difference and with a sustained upward trend between cuts, where LM4 and LM13 increased by 13.2 and 10.1 times more than in the first cut. For dry matter yield (t ha−1), a similar pattern was observed, with the same LM4 and LM13 accessions standing out with values exceeding 0.200 t ha−1 and a tendency to increase between cuts, showing values of 3.751 ± 0.219 and 2.888 ± 0.288 t ha−1 in the fourth cut, with an increase of 13.98 and 9.86 times compared to their initial value in the first cut. Furthermore, there was no statistically significant difference between the two accessions in the third and fourth cuttings. Overall, LM4 and LM13 are among the alternatives with the highest biomass for silage production, showing an upward trend with each cut.

3.2.2. Daily Accumulation Rate and Dry Matter Percentage

The average daily accumulation rate of dry matter and dry matter percentage showed significant effects of accessions (p < 0.001) and cuts (p < 0.001), as well as their interaction (p < 0.001), as shown in Table 7. The highest dry matter percentage values were recorded in LM4 in all cut, being statistically higher than LM13. However, it did not differ from LM2 in the first cutting, LM3 and LM8 in the second cut, and in the third and fourth cut only showed differences with LM13. Based on the average daily accumulation rate LM4, LM6, LM8, and LM13 showed the highest accumulations, but did not differ from LM12 during the first cut. Likewise, LM4 and LM13 showed the highest values from the first to the fourth cut in a stable manner between cuts with statistically higher values compared to the other accessions from the second cut onwards.

3.3. Nutritional Composition

3.3.1. Acid Detergent Fiber and Neutral Detergent Fiber

Acid detergent fiber (ADF) and neutral detergent fiber (NDF) showed significant effects of accessions (p < 0.001) and cuts (p < 0.001), as well as their interaction (p < 0.05) (Table 8). In general, LM8 (together with LM12) consistently presented the lowest ADF values, suggesting a less fibrous profile, while LM7 recorded the highest ADF values and showed no differences between cuts; in the fourth cut, LM3 did not differ from LM7. Regarding NDF, the highest values were observed in LM3 and LM13, indicating generally more fibrous accessions, with increases from the second to the fourth cut. Taken together, these patterns differentiate accessions with lower fiber (LM8 and LM12) from those with higher fiber (LM7 and LM3 for FDA; LM3 and LM13 for NDF) throughout the harvests.

3.3.2. Protein and In Vitro Digestibility

Protein content and in vitro digestibility showed significant effects of accession (p < 0.001) and cut (p < 0.001), as well as their interaction (p < 0.05), as shown in Table 9. Overall, LM4 presented the most favorable profile, registering the highest crude protein values and high in vitro digestibility in both cuts. Crude protein remained unchanged from the second to the fourth cut in LM4, LM8, LM12, and LM13, while it decreased in the remaining accessions, with LM3 showing the lowest protein content in both cuts. Regarding digestibility, most accessions showed no change between cuts; however, it decreased from the second to the fourth cut in LM2, LM7, and LM12. Although LM8 showed the highest digestibility, not differing from LM4 in both cuts, LM7 registered the lowest in both cuts.

4. Discussion

Our study revealed high variability in basal coverage area among accessions within each cut [53]. This could explain why accessions LM4 and LM13 exhibited the highest performance at the end of the fourth cut, exceeding the basal coverage area recorded in the first cut by more than eight times. This increase may also be linked to a high adaptive capacity to the thermal regime [24]. Among the advantages that accessions LM4 and LM13 could offer by presenting greater basal coverage area is weed suppression, helping to mitigate competition for resources [54,55]. They could also contribute to reducing soil erosion [56,57].
With regard to days to anthesis, accessions LM4 and LM13 exceeded 120 days in the first cut, exhibiting a decreasing trend until stabilizing in the third cut. In contrast, accessions LM1, LM3, LM6, and LM8 showed phenological stability throughout the cuts with shorter days. The record of longer and shorter days until anthesis in our study can be attributed to genetic variation in the reproductive phenology of each accession, influenced by sensitivity to photoperiod [58]. This variation in days to anthesis is relevant because it allows early and late accessions to be differentiated, which is useful for selection and improvement aimed at synchronizing flowering with cutting windows and improving production stability between harvests under tropical Andean conditions [59,60,61].
In turn, the origin of the accessions conditions the type of inductive requirement [62]. For example, Cooper [63] revealed that 50% of the population of Lolium multiflorum Lam. requires induction by cold and short days, while the remaining 50% shows a quantitative response with no induction. In this context, the behavior recorded in LM4 and LM13 could be associated with obligate or partial vernalization requirements. This could be supported by the initial delay and subsequent stabilization, indicating that the requirements were progressively met after cumulative exposure to winter conditions during successive cuts, allowing for a faster reproductive transition in subsequent cycles. This could be corroborated by the study by Adhikari et al. [25] with the selection of plants and the crossing of early and late groups in Lolium species, where they observed variations that differed by up to 28 days between populations. Our results allowed us to identify the phenological cycle of each accession under the conditions of the Tropical Andes, facilitating the planning of cuts and conservation. In this regard, LM4 and LM13 represent a late group with a subsequent sharp reduction in time to anthesis, while LM1, LM3, LM6, and LM8 maintain early and consistent behavior, information that can be used in selection schemes and management decisions.
Regarding fresh forage yields, our study showed that, in accessions that were later to anthesis, yields were significantly higher, with a fourth cut yield 13.2 and 10.1 times higher than the value recorded in the first cut in accessions LM4 and LM13. These results are consistent with the study by Choi [64], which indicates that the longer the days until anthesis, the longer the active growth period, leading to greater light interception and biomass accumulation. He also points out that the most optimal cuts for greater productivity of late-cycle Lolium multiflorum Lam. are during the heading and flowering stage, with no significant differences, at which point there is a balance between quantity and quality. Previous research has also shown that greater plant height is associated with higher fresh forage yields [65,66]. This is consistent with our results, where the greatest plant height recorded between cuts was observed in LM4 and LM13. In addition, LM4 and LM13 obtained the highest daily dry matter accumulation rates in a stable manner between cuts. This is supported by the study by Gaytán Valencia et al. [46], who obtained higher fresh forage and dry matter yields in Medicago sativa L. when cutting at four weeks, showing a higher daily accumulation of dry matter compared to cutting at three weeks. On the other hand, yield according to the planting method may vary [67]. Based on our study, it has the limitation that only the vegetative propagation method was used, which implies future studies in the same local accessions using different propagation methods. Among the qualitative traits shared by LM4 and LM13 was the dark green color of their leaves. This characteristic could be associated with genetic or environmental factors, which play an important role in leaf senescence by interfering with yellowing through alteration of the chlorophyll decomposition pathway, allowing stay-green genotypes to remain green longer and part of the photosynthetic apparatus (thylakoid membrane proteins) to remain intact for longer [68].
In general terms, dry matter yield (t ha−1) was less than 0.200 t ha−1 for most accessions and cuts, with the exception of the results presented in LM4 and LM13. According to studies in local accessions of Lolium multiflorum Lam. under chemical fertilization (160-130-66 kg of N-P2O5-K2O ha−1 year−1) dry matter yields were obtained that ranged between 3.64 and 4.49 t ha−1 with cuts made every 60 days [31]. Based on our results, yields of 3.7 and 2.8 t ha−1 were obtained at 57.2 and 70 days to anthesis in the fourth cutting, competitive ranges close to those obtained with synthetic fertilization, with stability from the third cutting onward under organic fertilization. These findings are promising, considering that chemical fertilization with nitrogen (N) could double biomass yields, as reported by Vásquez et al. [43] in the INIA 910—Kumymarca variety at a N dose of 180 kg ha−1. Consequently, LM4 and LM13 are emerging as the accessions with the greatest biomass yield potential in the Tropical Andes. Our results suggest future research evaluating the response of LM4 and LM13 to different nitrogen gradients, in order to enhance key physiological components for performance such as tiller density and leaf area index [69].
The percentage of dry matter varied between accessions and cuts. The LM4 accession presented the most stable values between cuts, with values ranging from 26.7 to 28.5%, higher than LM13. In terms of ensilability, dry matter contents below 25% (equivalent to 75% moisture) are associated with a higher risk of poor fermentation, high pH, and effluent losses during ensiling; while values between 25% and 30% dry matter (≥70% moisture) still reflect a wet raw material and correlate with greater damage due to bacterial proliferation and deterioration of nutritional quality under certain conditions [70,71]. In our study, most accessions harvested at anthesis showed dry matter values below the recommended levels, except for LM2 in the first cut and LM8 in the second, confirming a high moisture content in the raw material. Therefore, strategies such as pre-wilting and the use of inoculants (e.g., Lactobacillus plantarum) may be necessary to increase dry matter and improve silage quality, as reported by Lio et al. [72]. From a practical standpoint, accession LM4, which has higher dry matter content and lower moisture content than the other accessions, may require a shorter pre-wilting period to achieve suitable silage conditions, potentially shorter than for more moist accessions. This management can be complemented with inoculants to promote more stable fermentation and obtain better quality silage.
Nutritional analysis revealed the highest acid detergent fiber (ADF) contents in LM7 (33.3 ± 0.13% and 34.4 ± 0.33%). These results were similar to those reported by Yavuz et al. [73] in the evaluation of ryegrass lines, where they obtained values ranging from 31.41 to 34.75% ADF using the half-sib family selection breeding method. Likewise, among accessions, it was observed that certain accessions increased the percentage of ADF in the fourth cut, while others remained stable. This could be related to the genetic expression of each accession in response to seasonal changes or environmental variability [74]. It should be noted that our study was limited to nutritional composition evaluations during anthesis only. The literature mentions that during this stage, plant senescence is greater, evidencing greater lignification, which could have an impact on the increase in neutral detergent fiber (NDF) [75]. Based on our findings, NDF values exceeded 50% in all our accessions. In contrast, Alende et al. [76] reported values below 46.05% in intermediate tetraploids and short-cycle diploids of Lolium multiflorum Lam. On the other hand, there are studies that indicate that rumination time is quadratically related to the NDF concentration in the diet of cattle and to digestibility, indicating that NDF regulation affects ruminal function [77]. The results obtained in our study serve as a starting point for future evaluations, with the aim of reducing the NDF content above 50% in all accessions, to fill the knowledge gap on the performance of these accessions in evaluations with earlier cuts before anthesis.
Based on protein content, accession LM4 presented the highest stable values among cuts, with figures ranging between 24.2 and 24% protein. However, these values may vary depending on topography [78] and under different silvopastoral systems in interaction with the season [79]. In addition, it has been reported that some lines of Lolium multiflorum Lam. may show different responses (high or low) to nitrogen uptake, although these differences are not always consistent and may be reversed in subsequent cycles [80,81]. This behavior could have contributed to the variability observed in our experiment, as nitrogen is directly related to increased protein content in Lolium multiflorum Lam. Plants [82]. In this sense, N use efficiency can translate into differential responses in yield and nutritional quality depending on the availability of nitrogen in the soil, and would be conditioned by traits such as plant architecture and root biomass development [83,84].
The results shown in our study on LM4 are more remarkable than studies with phosphate fertilization applications, which showed protein values of 17.87% in Panicum maximum [85]. Similarly, it was higher than the results presented in the evaluation of six forage grasses, where the highest value reached 14.23% [86]. However, the high protein content observed in LM4 could make it susceptible to greater protein degradation during the silage process, but the higher percentage of dry matter (%) compared to the other accessions could contribute to moderating proteolysis and, consequently, reducing the formation of soluble nitrogen during silage [87]. Studies indicate that intrinsic plant proteases can initiate the early stages of forage proteolysis after cutting, even in the absence of ruminal microorganisms, contributing to the initial formation of peptides and soluble nitrogen [88]. This suggests that the outstanding protein and dry matter values in LM4 need to be further studied in evaluations at each stage of silage, and how this affects its performance in terms of its contribution to quality.
On the other hand, digestibility in LM4 and LM8 remained stable in the second and fourth cut, with statistically high values. These results are promising, suggesting a possible trend toward increased meat and milk production if these values remain stable during ensiling [89]. It should be noted that a high lignin content can affect digestibility, acting as a physical barrier to microbial degradation [90]. Furthermore, the results obtained in our study were superior to those of other local grasses [78]. This reveals the broad potential of local Lolium multiflorum Lam. accessions in the Tropical Andes, based on LM4.
One of the main limitations of this study is that it was conducted during a single annual cycle (July 2024 to June 2025) and at a single location, so the consistency of the trends observed could vary in years with different precipitation patterns or at sites with different Andean elevations. In addition, the evaluation was restricted to four cuts, so longer trials are required to corroborate the stability of each accession over time. Furthermore, the forage was evaluated only as raw material, without considering its behavior during the silage process, which highlights the need for additional studies that include the preparation and evaluation of silage to more accurately quantify its contribution to quality. Taken together, these results constitute a preliminary reference for the performance of local accessions under the agroecological conditions evaluated in the Tropical Andes and lay the foundation for future research.

5. Conclusions

Agronomic performance was significantly higher in LM4 and LM13. Accession LM4 had the highest plant height at the fourth cut (57.7 ± 0.6 cm), which was 2.48 times higher than at the first cut. In terms of days to anthesis, LM4 and LM13 were the latest accessions, with values decreasing at the third cut and remaining stable in subsequent cuts, along with greater basal coverage area than the other accessions between cuts. Compared to the first cut, fresh forage yield in LM4 and LM13 increased 13.2 and 10.1 times during the fourth cut; likewise, dry matter yield increased 13.98 and 9.86 times, with a tendency to increase between cuts. This was associated with a higher average daily accumulation of dry matter. However, LM13 had a low percentage of dry matter compared to LM4, being lower in all cuts. In addition, LM4 showed a stable trend between cuts, with no variability in the percentage of dry matter. In terms of nutritional content, LM4 showed superiority in protein content between the second and fourth cuts, with stability between the two. It also revealed the greatest stability and highest digestibility values between cuts. Overall, LM4 was identified as a promising candidate for future evaluations as a silage feedstock under field conditions, including assessments throughout the process; in addition, it requires evaluations in multiple environments and over several years to confirm the extrapolation of our data. Given the relatively high moisture content of the harvested biomass in some accessions, wilting prior to ensiling is recommended to achieve an optimal dry matter range and reduce the risk of effluent losses and suboptimal fermentation. LM4 appears to be the option closest to the optimum moisture point, thus reducing wilting time.

Author Contributions

Conceptualization, H.V.V., L.V. and Y.P.; methodology, L.V., V.L.S.B. and W.B.; software, J.L.M., L.G.B. and M.A.A.-T.; validation, M.A.A.-T., W.B. and W.C.-C.; formal analysis, J.L.M., M.A.A.-T. and W.C.-C.; investigation, L.G.B., M.A.A.-T. and V.L.S.B.; resources, W.C.-C. and Y.P.; data curation, F.L.M., W.B. and Y.P.; writing—original draft preparation, F.L.M., H.V.V. and L.G.B.; writing—review and editing, F.L.M., V.L.S.B. and W.B.; visualization, J.L.M., W.C.-C. and Y.P.; supervision, H.V.V., L.V. and L.G.B.; project administration, F.L.M., L.V. and V.L.S.B.; funding acquisition, H.V.V., J.L.M. and L.G.B. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the National Council for Science, Technology and Technological Innovation (CONCYTEC) and the National Program for Scientific Research and Advanced Studies (PROCIENCIA) under call E077-2023-01-BM “Scholarships for Doctoral Programs in Interinstitutional Alliances”, grant, PE501088652-2024 and under call E033-2023-01-BM “Interinstitutional Alliances for Doctoral Programs”, grant PE501084305-2023.

Data Availability Statement

The original contributions presented in the study are included in this article; further inquiries can be directed to the corresponding authors.

Acknowledgments

The authors would like to thank the Doctoral Program in Sciences for Sustainable Development at the Universidad Nacional Toribio Rodríguez de Mendoza de Amazonas. Special thanks are also extended to the National Council for Science, Technology and Technological Innovation (CONCYTEC) and the National Program for Scientific Research and Advanced Studies (PROCIENCIA), within the framework of Call E033-2023-01-BM “Interinstitutional Alliances for Doctoral Programs”, under grant number PE501084305-2023.

Conflicts of Interest

The authors declare that they have no conflicts of interest.

References

  1. Van Vliet, S.; Provenza, F.D.; Kronberg, S.L. Health-promoting phytonutrients are higher in grass-fed meat and milk. Front. Sustain. Food Syst. 2021, 4, 555426. [Google Scholar] [CrossRef]
  2. Pratelli, G.; Tamburini, B.; Badami, G.D.; Lo Pizzo, M.; De Blasio, A.; Carlisi, D.; Di Liberto, D. Cow’s milk: A benefit for human health? Omics tools and precision nutrition for lactose intolerance management. Nutrients 2024, 16, 320. [Google Scholar] [CrossRef] [PubMed]
  3. OECD Food and Agriculture Organization of the United Nations. OCDE-FAO Perspectivas Agrícolas 2025–2034; OECD Publishing: Paris, France, 2025. [Google Scholar] [CrossRef]
  4. Ministerio de Agricultura y Riego (MINAGRI). Plan Ganadero: Diagnóstico de Crianzas Priorizadas Para el 2017–2021; Dirección General de Políticas Agrarias, Dirección de Estudios Económicos e Información Agraria: Lima, Peru, 2017. Available online: https://faolex.fao.org/docs/pdf/per174289.pdf (accessed on 2 December 2025).
  5. Eckert, S.; Kiteme, B.; Njuguna, E.; Zaehringer, J.G. Agricultural Expansion and Intensification in the Foothills of Mount Kenya: A Landscape Perspective. Remote Sens. 2017, 9, 784. [Google Scholar] [CrossRef]
  6. Echevarría, M.; Pizarro, D.; Gómez, C. Alimentación de Ganadería en Sistemas Silvopastoriles de la Amazonia Peruana; Universidad Nacional Agraria La Molina, Programa Nacional de Innovación Agraria: Lima, Peru, 2019; Available online: https://www.researchgate.net/profile/Dante-izarro/publication/335542022_Alimentacion_de_ganaderia_en_sistemas_silvopastoriles_de_la_Amazonia_peruana/links/5d6c8adc299bf1808d5eab03/Alimentacion-de-ganaderia-en-sistemas-silvopastoriles-de-la-Amazonia-peruana.pdf (accessed on 2 December 2025).
  7. Thompson, J.B.; Zurita-Arthos, L.; Müller, F.; Chimbolema, S.; Suárez, E. Land use change in the Ecuadorian páramo: The impact of expanding agriculture on soil carbon storage. Arct. Antarct. Alp. Res. 2021, 53, 48–59. [Google Scholar] [CrossRef]
  8. Morales-Salmerón, L.; Fernández-Boy, E.; Madejón, E.; Domínguez, M.T. Soil legacy and organic amendment role in promoting the resistance of contaminated soils to drought. Appl. Soil Ecol. 2024, 195, 105226. [Google Scholar] [CrossRef]
  9. Mansfield, S.; Ferguson, C.; Gerard, P.; Hodges, D.; Kean, J.; Phillips, C.; Hardwick, S.; Zydenbos, S. Climate change impacts on pest ecology and risks to pasture resilience. NZGA: Res. Pract. Ser. 2021, 17, 123–138. [Google Scholar] [CrossRef]
  10. Hadush, M. Exploring farmers’ seasonal and full year adoption of stall feeding of livestock in Tigrai Region, Ethiopia. Ekon. Poljopr. 2017, 64, 919–944. [Google Scholar] [CrossRef]
  11. Duchicela, S.; Llambí, L.; Bonnesoeur, V.; Román-Dañobeytia, F. Pastoralism in the high tropical Andes: A review of the effect of grazing intensity on plant diversity and ecosystem services. Appl. Veg. Sci. 2024, 27, e12791. [Google Scholar] [CrossRef]
  12. Alvarez-García, W.; Muñoz-Vílchez, Y.; Figueroa, D.; Estrada, R.; Quilcate, C. A review of sustainable cattle genetic improvement in the Peruvian Highlands. Vet. Anim. Sci. 2025, 27, 100427. [Google Scholar] [CrossRef]
  13. Thomasz, E.; Pérez-Franco, I.; García-García, A. The Economic Impact of Climate Risk on Extensive Livestock: The Case of Lamb Production in Extremadura, Spain. Sustainability 2020, 12, 7254. [Google Scholar] [CrossRef]
  14. Villar Cabeza, M.Á.; Cuellar Bautista, J.E.; Valentin Castañeda, S.L. Valoración Técnica, Económica y Ambiental de Tres Sistemas de Silvopasturas en la Región Cajamarca; Instituto Nacional de Innovación Agraria (INIA): Lima, Peru, 2014; Available online: https://repositorio.inia.gob.pe/handle/20.500.12955/376 (accessed on 2 December 2025).
  15. Morales-Romero, D.; Angulo-Cota, R.M.; Ortega-Rosas, C.I.; Cota-Arriola, O.; Molina-Freaner, F. Does Buffelgrass Have a Long Permanence in an Established Pasture? An Analysis of the Population Dynamics of This Exotic Grass in Central Sonora, Mexico. Ecologies 2025, 6, 48. [Google Scholar] [CrossRef]
  16. Augustyniak, A.; Perlikowski, D.; Rapacz, M.; Kościelniak, J.; Kosmala, A. Insight into cellular proteome of Lolium multiflorum/Festuca Arundinacea introgression forms to decipher crucial mechanisms of cold acclimation in forage grasses. Plant Sci. 2018, 272, 22–31. [Google Scholar] [CrossRef] [PubMed]
  17. Villalobos, L.; Sánchez, J.M. Evaluación agronómica y nutricional del pasto ryegrass perenne tetraploide (Lolium perenne) producido en lecherías de las zonas altas de Costa Rica. I. Producción de biomasa y fenología. Agron. Costarric. 2010, 34, 31–42. [Google Scholar] [CrossRef]
  18. Zhu, J.; Giri, K.; Cogan, N.O.; Smith, K.F.; Jacobs, J.L. Genotype-by-environment interaction analysis of dry matter yield of perennial ryegrass cultivars across south-eastern Australia using factor analytic models. Field Crops Res. 2023, 303, 109143. [Google Scholar] [CrossRef]
  19. Liu, S.L.; Cao, Z.H.; Liu, H.E. Effect of ryegrass (Lolium multiflorum L.) growth on degradation of phenanthrene and enzyme activity in soil. Plant Soil Environ. 2013, 59, 247–253. [Google Scholar] [CrossRef]
  20. Maxwell, T.M.R.; McLenaghen, R.D.; Edwards, G.R.; Di, H.J.; Cameron, K.C. Italian ryegrass swards reduce N leaching via greater N uptake and lower drainage over perennial ryegrass cultivars varying in cool season growth rates. N. Z. J. Agric. Res. 2019, 62, 69–82. [Google Scholar] [CrossRef]
  21. Burns, G.A.; O’Kiely, P.; Grogan, D.; Watson, S.; Gilliland, T.J. Comparison of herbage yield, nutritive value and ensilability traits of three ryegrass species evaluated for the Irish Recommended List. Ir. J. Agric. Food Res. 2015, 54, 31–40. [Google Scholar] [CrossRef]
  22. Barre, P.; Ruttink, T.; Muylle, H.; Lootens, P.; Rohde, A.; Didier, C.; Roldán-Ruiz, I. Natural diversity in vegetative and reproductive investments of perennial ryegrass is shaped by the climate at the place of origin. Grass Forage Sci. 2018, 73, 193–205. [Google Scholar] [CrossRef]
  23. Tubbs, T.B.; Chastain, T.G. Genetic variation for seed retention in accessions and genotypic lines of perennial ryegrass (Lolium perenne L.). Crop Sci. 2023, 63, 306–319. [Google Scholar] [CrossRef]
  24. Ahmed, L.Q.; Escobar-Gutiérrez, A.J. Unexpected intraspecific variability of perennial ryegrass (Lolium perenne L.) in response to constant temperature during germination and initial heterotrophic growth. Front. Plant Sci. 2022, 13, 856099. [Google Scholar] [CrossRef]
  25. Adhikari, P.; Baldwin, B.S.; Morrison, J.I. Divergent selection for anthesis of annual ryegrass (Lolium perenne ssp. multiflorum (Lam.) Husnot). Crop Breed. Genet. Genom. 2025, 7, e250003. [Google Scholar] [CrossRef]
  26. Giunta, F.; De Vita, P.; Mastrangelo, A.; Sanna, G.; Motzo, R. Environmental and Genetic Variation for Yield-Related Traits of Durum Wheat as Affected by Development. Front. Plant Sci. 2018, 9, 8. [Google Scholar] [CrossRef] [PubMed]
  27. Innes, P.J.; Newell, M.T.; Pembleton, K.G.; Hayes, R.C.; Radanielson, A.M. A study of the vernalization requirements of mountain rye (Secale strictum syn. S. montanum) may help explain low grain yields of perennial cereals compared to wheat. AoB Plants 2025, 17, plaf015. [Google Scholar] [CrossRef] [PubMed]
  28. Maphosa, L.; Preston, A.; Richards, M.F. Effect of Sowing Date and Environment on Phenology, Growth and Yield of Lentil (Lens culinaris Medikus.) Genotypes. Plants 2023, 12, 474. [Google Scholar] [CrossRef]
  29. Galindo-Castañeda, T.; Lynch, J.P.; Six, J.; Hartmann, M. Improving Soil Resource Uptake by Plants Through Capitalizing on Synergies Between Root Architecture and Anatomy and Root-Associated Microorganisms. Front. Plant Sci. 2022, 13, 827369. [Google Scholar] [CrossRef]
  30. Choukri, H.; Hejjaoui, K.; El-Baouchi, A.; El Haddad, N.; Smouni, A.; Maalouf, F.; Thavarajah, D.; Kumar, S. Heat and Drought Stress Impact on Phenology, Grain Yield, and Nutritional Quality of Lentil (Lens culinaris Medikus). Front. Nutr. 2020, 7, 596307. [Google Scholar] [CrossRef]
  31. Carrasco-Chilón, W.; Cervantes-Peralta, M.; Mendoza, L.; Muñoz-Vílchez, Y.; Quilcate, C.; Nuñez-Melgar, D.C.; Vásquez, H.; Alvarez-García, W.Y. Morphological Differentiation, Yield, and Cutting Time of Lolium multiflorum L. under Acid Soil Conditions in Highlands. Plants 2024, 13, 2331. [Google Scholar] [CrossRef]
  32. Wiering, N.P.; Ehlke, N.J.; Catalano, D.; Martinson, K.; Sheaffer, C.C. Forage potential of winter-hardy perennial ryegrass populations in monoculture and binary alfalfa mixture. Agron. J. 2021, 113, 5183–5195. [Google Scholar] [CrossRef]
  33. Pizarro, D.M.; Erickson, M.G.; Gómez-Bravo, C.A.; Picasso, V.D.; Lucantoni, D.; Mottet, A.; Wattiaux, M.A. Agroecological performance of smallholder dairy cattle systems in the Peruvian Amazon. Agric. Syst. 2025, 223, 104199. [Google Scholar] [CrossRef]
  34. McCarthy, B.; Delaby, L.; Pierce, K.M.; Journot, F.; Horan, B. Meta-analysis of the impact of stocking rate on the productivity of pasture-based milk production systems. Animal 2011, 5, 784–794. [Google Scholar] [CrossRef]
  35. Ahmed, S.; Grecchi, I.; Ficuciello, V.; Bacciu, N.; Minuti, A.; Bani, P. Effects of hybrid and maturity stage on in vitro rumen digestibility of immature corn grain. Ital. J. Anim. Sci. 2014, 13, 455–461. [Google Scholar] [CrossRef]
  36. Vásquez, H.V.; Reyna, M.; Valqui-Valqui, L.; Bobadilla, L.G.; Maicelo, J.L.; Zagaceta Llanca, L.H.; Yalta Vela, J.; Isla Pérez, J.M.; Paucar, Y.; Altamirano-Tantalean, M.A.; et al. Impact of the Association of Maize with Native Beans on the Morphological Growth, Yield, and Nutritional Composition of Forage Intended for Silage in the Peruvian Amazon. Agronomy 2025, 15, 2445. [Google Scholar] [CrossRef]
  37. Borreani, G.; Tabacco, E.; Schmidt, R.J.; Holmes, B.J.; Muck, R.E. Silage review: Factors affecting dry matter and quality losses in silages. J. Dairy Sci. 2018, 101, 3952–3979. [Google Scholar] [CrossRef] [PubMed]
  38. Ministerio de Desarrollo Agrario y Riego (MIDAGRI). Decreto Supremo N.º 013-2010-AG. Reglamento para la Ejecución de Levantamiento de Suelos; Ministerio de Desarrollo Agrario y Riego (MIDAGRI): Lima, Peru, 2010.
  39. Oliva-Cruz, M.; Cabañas-López, J.R.; Altamirano-Tantalean, M.A.; Juarez-Contreras, L.; Vigo, C.N. Agronomic Behavior of Peanut (Arachis hypogaea L.) Cultivars under Three Planting Densities in the Northeast of Peru. Agronomy 2024, 14, 1905. [Google Scholar] [CrossRef]
  40. NTP-ISO/IEC 17025:2017; Requisitos Generales Para la Competencia de los Laboratorios de Ensayo y Calibración. 3rd ed. Instituto Nacional de Calidad (INACAL): Lima, Peru, 2017. Available online: https://transparencia.produce.gob.pe/images/stories/Repositorio/transparencia/proyectos-de-inversion/niveles-de-servicio/2021/ITP/NC/NTP_ISO_IEC_17025_2017.pdf (accessed on 23 September 2025).
  41. Bazán, R. Manual de Procedimientos de los Análisis de Suelos y Agua con Fines de Riego. Available online: https://repositorio.inia.gob.pe/server/api/core/bitstreams/55bde890-0de8-4f7b-8d15-8b39ea07cd26/content (accessed on 2 December 2025).
  42. Maity, A.; Singh, V.; Martins, M.B.; Ferreira, P.J.; Smith, G.R.; Bagavathiannan, M. Species identification and morphological trait diversity assessment in ryegrass (Lolium spp.) populations from the Texas Blackland Prairies. Weed Sci. 2021, 69, 379–392. [Google Scholar] [CrossRef]
  43. Vásquez, H.V.; Valqui, L.; Bobadilla, L.G.; Meseth, E.; Trigoso, M.J.; Zagaceta, L.H.; Valqui-Valqui, L.; Saravia-Navarro, D.; Barboza, E.; Maicelo, J.L. Agronomic and Nutritional Evaluation of INIA 910—Kumymarca Ryegrass (Lolium multiflorum Lam.): An Alternative for Sustainable Forage Production in Department of Amazonas (NW Peru). Agronomy 2025, 15, 100. [Google Scholar] [CrossRef]
  44. Canto, M.W.; Pancera, E.J.; Neto, A.B.; Bremm, C.; Vier, P.U.; Costa, A.C.S. Effects of nitrogen fertilisation and irrigation on seed yield and yield components of signal grass (Urochloa decumbens). Crop Pasture Sci. 2020, 71, 294–303. [Google Scholar] [CrossRef]
  45. Gurevitch, J. Competition and the local distribution of the grass Stipa neomexicana. Ecology 1986, 67, 46–57. [Google Scholar] [CrossRef]
  46. Gaytán Valencia, J.A.; Castro Rivera, R.; Villegas Aparicio, Y.; Aguilar Benítez, G.; Solís Oba, M.M.; Carrillo Rodríguez, J.C.; Negrete Sánchez, L.O. Rendimiento de alfalfa (Medicago sativa L.) a diferentes edades de la pradera y frecuencias de defoliación. Rev. Mex. Cienc. Pecu. 2019, 10, 353–366. [Google Scholar] [CrossRef]
  47. Horwitz, W.; Latimer, G.W. (Eds.) Official Methods of Analysis of AOAC International, 18th ed.; AOAC International: Gaithersburg, MD, USA, 2005; Available online: https://www.researchgate.net/publication/292783651_AOAC_2005 (accessed on 2 December 2025).
  48. ANKOM Technology. ANKOM A200 Fiber Analyzer. Available online: https://www.ankom.com/?srsltid=AfmBOoqOv_HvQ_qn7yYG-l3FSCd5dekfQtCPBwOkQGdwkR5LxzZZGyJK (accessed on 2 December 2025).
  49. ANKOM Technology. Method 3: In Vitro True Digestibility Using the ANKOM DAISYII Incubator; ANKOM Technology: Macedon, NY, USA, 2005; Available online: https://www.ankom.com/sites/default/files/2024-08/Method_3_InVitro_D200_D200I.pdf (accessed on 17 January 2026).
  50. Bates, D.; Mächler, M.; Bolker, B.; Walker, S. Fitting linear mixed-effects models using lme4. J. Stat. Softw. 2015, 67, 1–48. [Google Scholar] [CrossRef]
  51. Kuznetsova, A.; Brockhoff, P.B.; Christensen, R.H.B. lmerTest package: Tests in linear mixed effects models. J. Stat. Softw. 2017, 82, 1–26. [Google Scholar] [CrossRef]
  52. Searle, S.R.; Speed, F.M.; Milliken, G.A. Population marginal means in the linear model: An alternative to least squares means. Am. Stat. 1980, 34, 216–221. [Google Scholar] [CrossRef]
  53. Feng, H.; Zhou, J.; Zhou, A.; Bai, G.; Li, Z.; Chen, H.; Su, D.; Han, X. Grassland ecological restoration based on the relationship between vegetation and its below-ground habitat analysis in steppe coal mine area. Sci. Total Environ. 2021, 778, 146221. [Google Scholar] [CrossRef] [PubMed]
  54. Sanderson, M.; Johnson, H.; Hendrickson, J. Cover crop mixtures grown for annual forage in a semi-arid environment. Agron. J. 2018, 110, 525–534. [Google Scholar] [CrossRef]
  55. Malaspina, M.; Chantre, G.R.; Yanniccari, M. Effect of cover crops mixtures on weed suppression capacity in a dry sub-humid environment of Argentina. Front. Agron. 2024, 5, 1330073. [Google Scholar] [CrossRef]
  56. Donovan, M.; Monaghan, R. Impacts of grazing on ground cover, soil physical properties and soil loss via surface erosion: A novel geospatial modelling approach. J. Environ. Manag. 2021, 287, 112206. [Google Scholar] [CrossRef]
  57. Podwojewski, P.; Janeau, J.L.; Grellier, S.; Valentin, C.; Lorentz, S.; Chaplot, V. Influence of grass soil cover on water runoff and soil detachment under rainfall simulation in a sub-humid South African degraded rangeland. Earth Surf. Process. Landf. 2011, 36, 911–922. [Google Scholar] [CrossRef]
  58. Yamaguchi, H.; Suzuki, S. Variation in photoperiodical response of heading in Italian ryegrass (Lolium multiflorum Lam.). In Proceedings of the International Grassland Congress (IGC), 1985; Available online: https://uknowledge.uky.edu/igc/1985/ses2/7 (accessed on 10 December 2025).
  59. Fè, D.; Cericola, F.; Byrne, S.; Lenk, I.; Ashraf, B.H.; Pedersen, M.G.; Roulund, N.; Asp, T.; Janss, L.; Jensen, C.S.; et al. Genomic Dissection and Prediction of Heading Date in Perennial Ryegrass. BMC Genom. 2015, 16, 921. [Google Scholar] [CrossRef]
  60. Herridge, R.; Samarth; Brownfield, L.; Macknight, R. Identification and Characterization of Perennial Ryegrass (Lolium perenne) Vernalization Genes. Front. Plant Sci. 2021, 12, 640324. [Google Scholar] [CrossRef]
  61. Laidlaw, A.S. The Relationship between Tiller Appearance in Spring and Contribution to Dry-Matter Yield in Perennial Ryegrass (Lolium perenne L.) Cultivars Differing in Heading Date. Grass Forage Sci. 2005, 60, 200–209. [Google Scholar] [CrossRef]
  62. Aamlid, T.S.; Heide, O.M.; Boelt, B. Primary and secondary induction requirements for flowering of contrasting European varieties of Lolium perenne. Ann. Bot. 2000, 86, 1087–1095. [Google Scholar] [CrossRef]
  63. Cooper, J.P. Short-day and low-temperature induction in Lolium. Ann. Bot. 1960, 24, 232–246. [Google Scholar] [CrossRef]
  64. Choi, K.-J. Changes in dry matter yield and feed value of Italian ryegrass ‘Hwasan 101’ at different growth stages. J. Korean Soc. Grassl. Forage Sci. 2011, 31, 107–112. [Google Scholar] [CrossRef]
  65. Varol, I.S.; Ciftci, B.; Kaymaz, E.; Kaplan, M. Water and nitrogen impacts on water use, forage yield and quality of annual ryegrass. Sci. Rep. 2025, 15, 34143. [Google Scholar] [CrossRef]
  66. Vallejos-Cacho, R.; Vallejos-Fernández, L.A.; Alvarez-García, W.Y.; Tapia-Acosta, E.A.; Saldanha-Odriozola, S.; Quilcate-Pairazaman, C.E. Sustainability of Lolium multiflorum L. ‘Cajamarquino Ecotype’, Associated with Trifolium repens L., at Three Cutting Frequencies in the Northern Highlands of Peru. Sustainability 2024, 16, 6927. [Google Scholar] [CrossRef]
  67. Vásquez, H.V.; Valqui, L.; Valqui-Valqui, L.; Bobadilla, L.G.; Maicelo, J.L.; Altamirano-Tantalean, M.A.; Ampuero-Trigoso, G.; Yalta Vela, J. Effects of Planting Methods on the Establishment, Yield, and Nutritional Composition of Hybrid Grass Cuba OM-22 in the Dry Tropics of Peru. Agronomy 2025, 15, 2497. [Google Scholar] [CrossRef]
  68. Thomas, H.; Ougham, H.; Canter, P.; Donnison, I. What stay-green mutants tell us about nitrogen remobilization in leaf senescence. J. Exp. Bot. 2002, 53, 801–808. [Google Scholar] [CrossRef]
  69. Peters, T.; Taube, F.; Kluß, C.; Reinsch, T.; Loges, R.; Fenger, F. How Does Nitrogen Application Rate Affect Plant Functional Traits and Crop Growth Rate of Perennial Ryegrass-Dominated Permanent Pastures? Agronomy 2021, 11, 2499. [Google Scholar] [CrossRef]
  70. Webster, J. The Biochemistry of Silage (Second Edition). By P. McDonald, A.R. Henderson and S. J. E. Heron. Marlow, Bucks, UK: Chalcombe Publications, (1991), pp. 340, £49.50, ISBN 0-948617-225. Exp. Agric. 1992, 28, 125. [Google Scholar] [CrossRef]
  71. Lajús, C.R.; Sebben, C.; Pasqualotto, D.L.; Spode, M.R.; Sabadini, P.B.; Dalcanton, F.; da Luz, G.L.; Onofre, S.B.; Cericato, A.; Topolski Pavan Batiston, T.F. Production and nutritive value of silage corn in different reproductive stages. Int. J. Adv. Eng. Res. Sci. 2020, 7, 130–136. [Google Scholar] [CrossRef]
  72. Liu, C.; Zhao, G.Q.; Wei, S.N.; Kim, H.J.; Li, Y.F.; Kim, J.G. Changes in fermentation pattern and quality of Italian ryegrass (Lolium multiflorum Lam.) silage by wilting and inoculant treatments. Anim. Biosci. 2021, 34, 48–55. [Google Scholar] [CrossRef] [PubMed]
  73. Yavuz, T.; Sürmen, M.; Albayrak, S.; Çankaya, N. Determination of forage yield and quality characteristics of annual ryegrass (Lolium multiflorum Lam.) lines. J. Agric. Sci. 2017, 23, 234–241. [Google Scholar]
  74. Colas, V.; Barre, P.; van Parijs, F.; Wolters, L.; Quitté, Y.; Ruttink, T.; Roldán-Ruiz, I.; Escobar Gutiérrez, A.J.; Muylle, H. Seasonal differences in structural and genetic control of digestibility in perennial ryegrass. Front. Plant Sci. 2022, 12, 801145. [Google Scholar] [CrossRef] [PubMed]
  75. Geren, H.; Kavut, Y.T.; Unlu, H.B. Effect of different cutting intervals on the forage yield and some silage quality characteristics of giant king grass (Pennisetum hybridum) under Mediterranean climatic conditions. Turk. J. Field Crops 2020, 25, 1–8. [Google Scholar] [CrossRef]
  76. Alende, M.; Fluck, A.C.; Volpi-Lagreca, G.; Andrae, J.G. Chemical composition and in vitro digestibility of annual ryegrass varieties grown in greenhouse conditions. RIA Rev. Investig. Agropecu. 2020, 46, 50–55. [Google Scholar]
  77. Souza, J.G.; Ribeiro, C.V.D.M.; Harvatine, K.J. Meta-analysis of rumination behavior and its relationship with milk and milk fat production, rumen pH, and total-tract digestibility in lactating dairy cows. J. Dairy Sci. 2022, 105, 188–200. [Google Scholar] [CrossRef]
  78. Gobena, G.; Urge, M.; Hundie, D.; Kumsa, D. Identification and evaluation of agro-ecological variation in dry matter yield and nutritional values of local grasses used as livestock feed in Adola Reedde, Guji Zone, Ethiopia. J. Appl. Anim. Res. 2022, 50, 369–379. [Google Scholar] [CrossRef]
  79. Valqui, L.; Saucedo-Uriarte, J.A.; Altamirano-Tantalean, M.A.; Bobadilla, L.G.; Portocarrero Villegas, S.M.; Bardales, W.; Frias, H.; Zagaceta Llanca, L.H.; Valqui-Valqui, L.; Puerta-Chavez, L.J.; et al. Influence of tree species on soil physicochemical composition, macrofauna, and forage production. J. Agric. Food Res. 2025, 23, 102220. [Google Scholar] [CrossRef]
  80. Goodman, P.J. Selection for Nitrogen Responses in Lolium. Ann. Bot. 1977, 41, 243–256. [Google Scholar] [CrossRef]
  81. Quatrin, M.P.; Olivo, C.J.; Agnolin, C.A.; Machado, P.R.; Nunes, J.S.; Correa, M.R.; Rodrigues, P.F.; Bratz, V.F.; Simonetti, G.D. Efeito da adubação nitrogenada na produção de forragem, teor de proteína bruta e taxa de lotação em pastagens de azevém. Bol. Ind. Anim. 2015, 72, 21–26. [Google Scholar] [CrossRef]
  82. Vásquez, H.V.; Valqui, L.; Valqui-Valqui, L.; Bobadilla, L.G.; Reyna, M.; Maravi, C.; Pajares, N.; Altamirano-Tantalean, M.A. Influence of Nitrogen Fertilization and Cutting Dynamics on the Yield and Nutritional Composition of White Clover (Trifolium repens L.). Plants 2025, 14, 2765. [Google Scholar] [CrossRef] [PubMed]
  83. Bugge, G. Stickstoffausnutzungsvermögen von Lolium perenne und Lolium multiflorum-Sorten. J. Agron. Crop Sci. 1988, 161, 65–71. [Google Scholar] [CrossRef]
  84. Moir, J.L.; Edwards, G.R.; Berry, L.N. Nitrogen uptake and leaching loss of thirteen temperate grass species under high N loading. Grass Forage Sci. 2013, 68, 313–325. [Google Scholar] [CrossRef]
  85. Susilawati, I.; Supriyadi, K.R.; Susilawati, I.; Mustafa, H.K. Produksi dan kandungan protein kasar hijauan dengan pemberian pupuk fosfat pada pertanaman campuran rumput Benggala (Panicum maximum) dengan legum sentro (Centrosema pubescens). J. Nutr. Ternak Trop. Ilmu Pakan 2021, 3, 26–31. [Google Scholar] [CrossRef]
  86. Tenikecier, H.S.; Ates, E. Chemical composition of six grass species (Poaceae sp.) from protected forest range in northern Bulgaria. Asian J. Appl. Sci. 2018, 11, 71–75. [Google Scholar] [CrossRef]
  87. Muhandiram, N.P.K.; Humphreys, M.W.; Fychan, R.; Davies, J.W.; Sanderson, R.; Marley, C.L. Designing agricultural grasses to help mitigate proteolysis during ensiling to optimize protein feed provisions for livestock. Food Energy Secur. 2023, 12, e475. [Google Scholar] [CrossRef]
  88. Zhu, W.Y.; Kingston-Smith, A.H.; Troncoso, D.; Merry, R.J.; Davies, D.R.; Pichard, G.; Thomas, H.; Theodorou, M.K. Evidence of a role for plant proteases in the degradation of herbage proteins in the rumen of grazing cattle. J. Dairy Sci. 1999, 82, 2651–2658. [Google Scholar] [CrossRef]
  89. Keady, T.; Hanrahan, S.; Marley, C.; Scollan, N.D. Production and utilization of ensiled forages by beef cattle, dairy cows, pregnant ewes and finishing lambs—A review. Agric. Food Sci. 2013, 22, 70–92. [Google Scholar] [CrossRef]
  90. Halpin, C. Lignin engineering to improve saccharification and digestibility in grasses. Curr. Opin. Biotechnol. 2019, 56, 223–229. [Google Scholar] [CrossRef]
Figure 1. Meteorological conditions during the experimental period. (a) precipitation; (b) maximum temperature; (c) minimum temperature; and (d) relative humidity.
Figure 1. Meteorological conditions during the experimental period. (a) precipitation; (b) maximum temperature; (c) minimum temperature; and (d) relative humidity.
Agronomy 16 00275 g001
Figure 2. Experimental design and field layout. The diagram illustrates the Randomized Complete Block Design (RCBD) with four blocks. The bottom legend (Accessions evaluated) identifies the ten accessions corresponding to the color-coded plots. The circular insert details the experimental unit (plot), and the flow chart on the right depicts the repeated measures sampling strategy (four sequential cuts) performed on the same plots.
Figure 2. Experimental design and field layout. The diagram illustrates the Randomized Complete Block Design (RCBD) with four blocks. The bottom legend (Accessions evaluated) identifies the ten accessions corresponding to the color-coded plots. The circular insert details the experimental unit (plot), and the flow chart on the right depicts the repeated measures sampling strategy (four sequential cuts) performed on the same plots.
Agronomy 16 00275 g002
Figure 3. Differences in the coloration of the basal node of each accession. (a) Accession LM13 with a light green basal node, (b) accession LM6 with a green basal node, and (c) accession LM8 with a reddish basal node.
Figure 3. Differences in the coloration of the basal node of each accession. (a) Accession LM13 with a light green basal node, (b) accession LM6 with a green basal node, and (c) accession LM8 with a reddish basal node.
Agronomy 16 00275 g003
Table 1. Origin of accessions within the germplasm bank.
Table 1. Origin of accessions within the germplasm bank.
AccessionsCodeCollection SiteProvinceEAST CoordinateNORTH Coordinate
Lolium multiflorum Paccha—LM1LM1PacchaChota78°48′40.85″ W6°19′43.16″ S
Lolium multiflorum Cutervo—LM2LM2CutervoCutervo78°49′15.76″ W6°22′34.56″ S
Lolium multiflorum Tacabamba—LM3LM3TacabambaChota78°36′36.29″ W6°23′37.05″ S
Lolium multiflorum Tacabamba—LM4LM4TacabambaChota78°36′36.29″ W6°23′37.05″ S
Lolium multiflorum Calquis—LM6LM6CalquisSan Miguel78°58′26.35″ W6°55′15.54″ S
Lolium multiflorum El Agrario—LM7LM7El AgrarioSan Miguel78°50′55.37″ W7°0′2.52″ S
Lolium multiflorum Bambamarca—LM8LM8BambamarcaHualgayoc78°29′52.3″ W6°40′42.1″ S
Lolium multiflorum Sendamal—LM11LM11SendamalCelendín78°10′52.49″ W6°57′54.96″ S
Lolium multiflorum Sendamal—LM12LM12SendamalCelendín78°10′52.49″ W6°57′54.96″ S
Lolium multiflorum Micuypampa—LM13LM13CelendínCajamarca78°12′45.07″ W7°1′32.91″ S
Table 2. Evaluation criteria for qualitative characteristics.
Table 2. Evaluation criteria for qualitative characteristics.
AttributesClassification
Growth habitA scale of 1 to 5 was established to rate the angle of the stem or main tillers, taking the horizontal axis as a reference, where erect (greater than 60°) (1), semi-erect (between 30° and 60°) (3), and prostrate (less than 30°) (5)
Leaf colorLeaf color was rated on a scale of 1 to 5 as light green (1), green (3), and dark green (5)
Basal node colorThe color of the basal node was rated on a scale of 1 to 5 as light green (1), green (3), and reddish (5)
Texture of leafThe texture of leaf was evaluated on a scale of 1 to 5: very smooth (1), smooth (3), and rough (5)
Table 3. Qualitative morphological characteristics in ten ryegrass accessions.
Table 3. Qualitative morphological characteristics in ten ryegrass accessions.
AccessionGrowth HabitLeaf ColorBasal Node ColorTexture of Leaf
LM15153
LM23153
LM31153
LM43555
LM61355
LM73113
LM81133
LM113313
LM123113
LM133515
Morphological classification: growth habit: erect (1), semi-erect (3), prostrate (5); leaf color: light green (1), green (3), dark green (5); basal node color: light green (1), green (3), reddish (5); and leaf texture: very smooth (1), smooth (3), rough (5).
Table 4. Evaluation of plant height.
Table 4. Evaluation of plant height.
AccessionsPlant Height (cm2)
First CutSecond CutThird CutFourth Cut
LM125.2 ± 0.1 cB20.3 ± 0.3 eC26.7 ± 0.2 cdeA26.4 ± 0.3 dAB
LM223.1 ± 0.1 dA19.9 ± 0.5 eB18.3 ± 0.3 fC23.4 ± 0.2 eA
LM328.1 ± 0.1 bA28.0 ± 0.5 bA25.4 ± 0.2 eB25.8 ± 0.3 dB
LM423.3 ± 0.5 dD29.5 ± 0.2 bC54.0 ± 0.5 bB57.7 ± 0.6 aA
LM629.3 ± 0.2 bA25.5 ± 0.2 cC27.9 ± 0.3 cB23.4 ± 0.4 eD
LM720.8 ± 0.5 eD24.6 ± 0.3 cdC27.1 ± 0.3 cdB28.9 ± 0.4 cA
LM828.6 ± 0.3 bA28.6 ± 0.3 bA19.0 ± 0.2 fB18.6 ± 0.2 gB
LM1126.1 ± 0.4 cB25.5 ± 0.3 cB27.8 ± 0.4 cA23.1 ± 0.2 eC
LM1231.5 ± 0.5 aA23.6 ± 0.2 dC25.7 ± 0.4 deB20.4 ± 0.3 fD
LM1328.1 ± 0.4 bD33.7 ± 0.3 aC60.1 ± 0.7 aA53.8 ± 0.4 bB
Note. Means ± standard error of the sample mean is presented. Different lowercase letters in the same column indicate significant differences between accessions within each cut, while different uppercase letters in the same row indicate significant differences between cuts for the same accession.
Table 5. Morphological evaluation of basal coverage area and days to anthesis.
Table 5. Morphological evaluation of basal coverage area and days to anthesis.
AccessionsBasal Coverage Area (cm2)
First CutSecond CutThird CutFourth Cut
LM114.7 ± 0.8 eC14.2 ± 0.7 gC22.1 ± 0.8 dA17.5 ± 0.9 fB
LM223.3 ± 1.0 cdB24.1 ± 1.6 deB40.7 ± 1.5 bA42.8 ± 0.5 cA
LM36.8 ± 0.3 gC7.6 ± 0.4 hC14.0 ± 0.9 eB17.3 ± 1.2 fA
LM433.8 ± 0.9 bD151.9 ± 4.0 aC268.9 ± 10 aB336.0 ± 5.8 aA
LM628.0 ± 1.2 bcC65.2 ± 2.1 bA38.3 ± 1.4 bB69.8 ± 2.5 bA
LM710.8 ± 0.3 fD15.2 ± 0.8 fgC22.6 ± 1.3 dB40.7 ± 2.0 cdA
LM828.8 ± 1.0 bcAB31.7 ± 1.2 cA26.4 ± 0.6 cdB32.2 ± 0.4 deA
LM1115.6 ± 0.6 eC19.1 ± 0.9 efB28.6 ± 1.4 cA29.1 ± 1.1 eA
LM1222.0 ± 0.9 dC26.4 ± 1.1 cdAB24.2 ± 4.1 cdBC30.1 ± 1.1 eA
LM1347.2 ± 3.3 aD168.8 ± 6.4 aC286.6 ± 6.5 aB386.2 ± 5.9 aA
AccessionsDays to Anthesis
First CutSecond CutThird CutFourth Cut
LM140.8 ± 1.5 cdA35.0 ± 0.8 defgA39.8 ± 1.7 bA40.2 ± 1.0 cdA
LM246.2 ± 1.1 cA42.2 ± 2.7 cdAB34.5 ± 1.0 bcC37.0 ± 1.0 cdeBC
LM343.5 ± 1.5 cdA40.2 ± 1.3 cdefA37.0 ± 1.8 bcA41.5 ± 1.2 cA
LM4120.8 ± 2.4 bA88.0 ± 2.3 aB65.5 ± 1.8 aC70.0 ± 0.0 aC
LM636.0 ± 0.6 dA32.8 ± 1.7 efgA39.8 ± 7.9 bA34.5 ± 1.6 cdeA
LM749.0 ± 1.2 cA41.2 ± 1.1 cdeB38.5 ± 1.8 bB36.8 ± 1.2 cdeB
LM835.0 ± 0.0 dA28.0 ± 0.0 gA28.5 ± 0.5 cA29.2 ± 0.8 eA
LM1145.5 ± 1.4 cAB49.0 ± 1.2 cA38.5 ± 1.4 bBC31.5 ± 0.6 deC
LM1240.8 ± 3.1 cdA31.5 ± 1.3 fgB31.0 ± 1.6 bcB31.5 ± 0.6 deB
LM13132.2 ± 2.6 aA74.8 ± 2.5 bB57.8 ± 1.7 aC57.2 ± 1.4 bC
Note. Means ± standard error of the sample mean is presented. Different lowercase letters in the same column indicate significant differences between accessions within each cut, while different uppercase letters in the same row indicate significant differences between cuts for the same accession.
Table 6. Evaluation of fresh forage (t ha−1) and dry matter yield (t ha−1).
Table 6. Evaluation of fresh forage (t ha−1) and dry matter yield (t ha−1).
AccessionsFresh Forage Yield (t ha−1)
First CutSecond CutThird CutFourth Cut
LM10.30 ± 0.02 dB0.12 ± 0.01 eC0.61 ± 0.01 bA0.72 ± 0.05 cA
LM20.15 ± 0.01 eC0.13 ± 0.01 eC0.30 ± 0.02 cB0.43 ± 0.03 deA
LM30.06 ± 0.00 fC0.16 ± 0.01 deB0.29 ± 0.03 cA0.36 ± 0.02 eA
LM41.01 ± 0.05 bC4.26 ± 0.26 aB15.20 ± 0.78 aA13.41 ± 0.69 aA
LM60.38 ± 0.02 cdC0.49 ± 0.02 bB0.60 ± 0.03 bB1.00 ± 0.03 bA
LM70.15 ± 0.00 eC0.24 ± 0.02 cB0.54 ± 0.11 bA0.51 ± 0.01 dA
LM80.42 ± 0.03 cA0.23 ± 0.02 cC0.33 ± 0.01 cAB0.32 ± 0.02 eB
LM110.17 ± 0.00 eC0.19 ± 0.01 cdC0.25 ± 0.02 cB0.32 ± 0.02 eA
LM120.34 ± 0.02 cdB0.48 ± 0.02 bA0.28 ± 0.05 cB0.31 ± 0.01 eB
LM131.75 ± 0.04 aC5.46 ± 0.11 aB19.98 ± 0.43 aA17.68 ± 0.79 aA
AccessionsDry Matter Yield (t ha−1)
First CutSecond CutThird CutFourth Cut
LM10.058 ± 0.004 cdB0.023 ± 0.002 gC0.142 ± 0.01 bA0.182 ± 0.016 bA
LM20.047 ± 0.004 deC0.036 ± 0.001 fC0.072 ± 0.003 dB0.100 ± 0.008 cdA
LM30.011 ± 0.001 gC0.043 ± 0.001 efB0.073 ± 0.004 dA0.077 ± 0.005 deA
LM40.268 ± 0.015 aC1.218 ± 0.107 aB4.327 ± 0.212 aA3.751 ± 0.219 aA
LM60.087 ± 0.008 bB0.092 ± 0.006 bcB0.165 ± 0.014 bA0.215 ± 0.016 bA
LM70.031 ± 0.002 fC0.06 ± 0.002 deB0.120 ± 0.026 bcA0.112 ± 0.003 cA
LM80.098 ± 0.010 bA0.079 ± 0.007 cdA0.080 ± 0.004 cdA0.082 ± 0.003 cdeA
LM110.032 ± 0.002 efC0.044 ± 0.004 efB0.059 ± 0.004 dA0.069 ± 0.008 eA
LM120.082 ± 0.003 bcB0.122 ± 0.014 bA0.072 ± 0.01 dB0.074 ± 0.004 deB
LM130.292 ± 0.010 aC0.870 ± 0.045 aB3.107 ± 0.158 aA2.888 ± 0.288 aA
Note. Means ± standard error of the sample mean is presented. Different lowercase letters in the same column indicate significant differences between accessions within each cut, while different uppercase letters in the same row indicate significant differences between cuts for the same accession.
Table 7. Evaluation of daily accumulation rate and percentage of dry matter.
Table 7. Evaluation of daily accumulation rate and percentage of dry matter.
AccessionsDry Matter (%)
First CutSecond CutThird CutFourth Cut
LM119.6 ± 0.91 cdB19.0 ± 2.09 cdeB23.3 ± 1.44 aAB25.6 ± 1.94 aA
LM231.8 ± 1.49 aA27.3 ± 2.38 bAB24.0 ± 1.90 aB23.4 ± 1.93 aB
LM319.5 ± 0.40 cdC28.1 ± 1.94 abA25.7 ± 1.95 aAB21.7 ± 0.37 abBC
LM426.7 ± 1.01 abA28.5 ± 0.79 abA28.5 ± 0.62 aA28.0 ± 0.55 aA
LM622.5 ± 1.07 bcdAB18.8 ± 1.75 deB27.2 ± 1.44 aA21.5 ± 1.14 abB
LM721.1 ± 0.90 bcdA25.1 ± 1.97 bcdA22.2 ± 0.48 abA22.1 ± 0.38 abA
LM823.5 ± 1.84 bcdB34.7 ± 1.38 aA24.2 ± 1.32 aB26.1 ± 1.21 aB
LM1118.8 ± 0.66 cdA23.2 ± 1.42 bcdA23.9 ± 1.18 aA21.5 ± 1.16 abA
LM1224.4 ± 0.97 bcA25.6 ± 2.37 bcA26.6 ± 3.00 aA24.2 ± 1.58 aA
LM1316.8 ± 0.53 dA15.9 ± 0.60 eA15.5 ± 0.48 bA16.2 ± 0.94 bA
AccessionsDry Matter Accumulation Rate (kg ha−1 day−1)
First CutSecond CutThird CutFourth Cut
LM11.4 ± 0.1 bcB0.7 ± 0.1 eC3.6 ± 0.4 bcA4.5 ± 0.5 bcA
LM21.0 ± 0.1 cdB0.9 ± 0.0 deB2.1 ± 0.1 deA2.7 ± 0.2 deA
LM30.3 ± 0.0 fC1.1 ± 0.1 cdB2.0 ± 0.1 deA1.9 ± 0.2 eA
LM42.2 ± 0.2 aC13.9 ± 1.3 aB66.1 ± 2.9 aA53.6 ± 3.1 aA
LM62.4 ± 0.3 aC2.8 ± 0.3 bC4.5 ± 0.7 bB6.2 ± 0.4 bA
LM70.6 ± 0.1 eC1.5 ± 0.1 cB3.1 ± 0.6 bcdA3.1 ± 0.1 cdA
LM82.8 ± 0.3 aA2.8 ± 0.3 bA2.8 ± 0.2 cdA2.8 ± 0.1 deA
LM110.7 ± 0.0 deC0.9 ± 0.1 deC1.5 ± 0.2 eB2.2 ± 0.2 deA
LM122.0 ± 0.2 abB3.9 ± 0.5 bA2.4 ± 0.4 deB2.4 ± 0.1 deB
LM132.2 ± 0.0 aC11.7 ± 0.8 aB53.8 ± 2.3 aA50.7 ± 5.7 aA
Note. Means ± standard error of the sample mean is presented. Different lowercase letters in the same column indicate significant differences between accessions within each cut, while different uppercase letters in the same row indicate significant differences between cuts for the same accession.
Table 8. Evaluation of neutral detergent fiber and acid detergent fiber.
Table 8. Evaluation of neutral detergent fiber and acid detergent fiber.
AccessionsADF (%)
Second CutFourth Cut
LM128.4 ± 0.30 cdB30.3 ± 0.23 bA
LM229.3 ± 0.54 bcA30.0 ± 0.36 bcA
LM330.9 ± 0.53 bB33.4 ± 0.75 aA
LM427.0 ± 0.51 dB28.2 ± 0.64 cdA
LM629.6 ± 0.58 bcA30.5 ± 0.49 bA
LM733.3 ± 0.13 aA34.4 ± 0.33 aA
LM824.5 ± 0.23 eA24.7 ± 0.22 eA
LM1128.0 ± 0.06 cdB31.1 ± 0.64 bA
LM1226.6 ± 0.32 deA26.2 ± 0.27 deA
LM1328.3 ± 0.45 cdA29.2 ± 0.64 bcA
AccessionsNDF (%)
Second CutFourth Cut
LM153.9 ± 0.19 bcdA55.1 ± 0.36 bcdA
LM252.5 ± 0.71 cdA53.1 ± 0.21 dA
LM357.1 ± 0.14 aB58.6 ± 0.44 aA
LM452.9 ± 0.35 bcdA54.1 ± 0.75 cdA
LM654.2 ± 0.52 bcB56.4 ± 0.64 bcA
LM754.0 ± 0.58 bcdB55.4 ± 0.19 bcA
LM850.1 ± 0.11 eA50.7 ± 0.47 eA
LM1153.7 ± 0.35 bcdA54.3 ± 0.30 cdA
LM1251.8 ± 0.32 deA50.5 ± 1.09 eB
LM1354.8 ± 0.32 abB57.0 ± 0.51 abA
Note. Means ± standard error of the sample mean is presented. Different lowercase letters in the same column indicate significant differences between accessions within each cut, while different uppercase letters in the same row indicate significant differences between cuts for the same accession.
Table 9. Protein and digestibility assessment.
Table 9. Protein and digestibility assessment.
AccessionsProtein (%)
Second CutFourth Cut
LM117.4 ± 0.05 dA15.0 ± 0.25 deB
LM214.0 ± 0.47 fgA12.5 ± 0.32 fB
LM312.6 ± 0.09 gA10.5 ± 0.30 gB
LM424.2 ± 0.62 aA24.0 ± 0.38 aA
LM617.0 ± 0.48 deA15.9 ± 0.42 dB
LM713.7 ± 0.35 fgA11.4 ± 0.34 fgB
LM820.2 ± 0.51 bcA19.5 ± 0.50 bcA
LM1115.3 ± 0.48 efA13.2 ± 0.29 efB
LM1218.4 ± 0.50 cdA17.9 ± 0.59 cA
LM1321.1 ± 0.65 bA20.4 ± 0.49 bA
AccessionsIn vitro digestibility (%)
Second cutFourth cut
LM178.7 ± 0.37 cdA79.3 ± 0.47 cA
LM281.0 ± 0.36 cA79.2 ± 0.33 cB
LM378.0 ± 0.15 dA77.7 ± 0.56 cdA
LM486.2 ± 0.20 abA85.0 ± 0.94 abA
LM680.0 ± 0.56 cdA79.6 ± 0.46 cA
LM778.2 ± 0.40 dA76.8 ± 0.75 dB
LM888.0 ± 0.36 aA87.2 ± 0.51 aA
LM1178.5 ± 0.20 dA78.6 ± 0.35 cdA
LM1285.9 ± 0.38 abA83.8 ± 0.32 bB
LM1385.1 ± 0.54 bA84.0 ± 0.52 bA
Note. Means ± standard error of the sample mean is presented. Different lowercase letters in the same column indicate significant differences between accessions within each cut, while different uppercase letters in the same row indicate significant differences between cuts for the same accession.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Bobadilla, L.G.; Altamirano-Tantalean, M.A.; Carrasco-Chilón, W.; Silva Baca, V.L.; Mejía, F.L.; Paucar, Y.; Valqui, L.; Bardales, W.; Maicelo, J.L.; Vásquez, H.V. Agronomic and Nutritional Potential of Ryegrass (Lolium multiflorum Lam.) Accessions as Raw Material for Silage in the Tropical Andes of Peru. Agronomy 2026, 16, 275. https://doi.org/10.3390/agronomy16020275

AMA Style

Bobadilla LG, Altamirano-Tantalean MA, Carrasco-Chilón W, Silva Baca VL, Mejía FL, Paucar Y, Valqui L, Bardales W, Maicelo JL, Vásquez HV. Agronomic and Nutritional Potential of Ryegrass (Lolium multiflorum Lam.) Accessions as Raw Material for Silage in the Tropical Andes of Peru. Agronomy. 2026; 16(2):275. https://doi.org/10.3390/agronomy16020275

Chicago/Turabian Style

Bobadilla, Leidy G., Miguel A. Altamirano-Tantalean, William Carrasco-Chilón, Vanesa Lizbeth Silva Baca, Flor L. Mejía, Ysai Paucar, Leandro Valqui, William Bardales, Jorge L. Maicelo, and Héctor V. Vásquez. 2026. "Agronomic and Nutritional Potential of Ryegrass (Lolium multiflorum Lam.) Accessions as Raw Material for Silage in the Tropical Andes of Peru" Agronomy 16, no. 2: 275. https://doi.org/10.3390/agronomy16020275

APA Style

Bobadilla, L. G., Altamirano-Tantalean, M. A., Carrasco-Chilón, W., Silva Baca, V. L., Mejía, F. L., Paucar, Y., Valqui, L., Bardales, W., Maicelo, J. L., & Vásquez, H. V. (2026). Agronomic and Nutritional Potential of Ryegrass (Lolium multiflorum Lam.) Accessions as Raw Material for Silage in the Tropical Andes of Peru. Agronomy, 16(2), 275. https://doi.org/10.3390/agronomy16020275

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop