Legume Research

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Evaluating Species Diversity and Distribution using Ecological Niche Modeling and Diva-GIS in Red Clover (Trifolium pratense L.)- A Temperate Forage Legume

Suheel Ahmad1,*, Sheeraz Saleem Bhat1, Sheikh M. Sultan2, Susheel K. Raina2, Natarajan Sivaraj3, Nilamani Dikshit4, Shahid Ahmed4, Tejveer Singh4, Nazim Hamid Mir1, Regu Atufa1
  • https://orcid.org/0000-0002-9369-6902, https://orcid.org/0000-0003-3836-8479, https://orcid.org/0000-0002-7299-4687, https://orcid.org/0000-0002-1421-7687, https://orcid.org/0000-0003-2899-5970, https://orcid.org/0000-0002-2437-5960, https://orcid.org/0000-0003-4209-6090, https://orcid.org/0000-0002-1748-8300, https://orcid.org/0000-0003-4209-6090, https://orcid.org/0000-0002-1748-8300
1ICAR-Indian Grassland and Fodder Research Institute, Regional Research Station, Srinagar-191 132, Jammu and Kashmir, India.
2ICAR-National Bureau of Plant Genetic Resources, Regional Station, Srinagar-191 132, Jammu and Kashmir, India.
3ICAR-National Bureau of Plant Genetic Resources, Regional Station, Hyderabad-500 030, Telangana, India.
4ICAR-Indian Grassland and Fodder Research Institute, Jhansi-284 003, Uttar Pradesh, India.
  • Submitted13-01-2025|

  • Accepted14-05-2025|

  • First Online 17-06-2025|

  • doi 10.18805/LR-5471

Background: Trifolium pratense L. (red clover) is a temperate, leguminous pasture crop cultivated in the Himalayan region, primarily as a fodder source for livestock. Its ability to fix atmospheric nitrogen and function effectively as a cover crop enables it to thrive as a companion legume in grass-legume mixtures. Beyond its local utility, red clover holds global significance for fodder security and the conservation of agro-biodiversity in the present climatic regime.

Methods: The present study employed novel ecological niche modelling (ENM) to identify ecologically suitable regions for the cultivation of red clover in India for the first time. Additionally, DIVA-GIS software was used to analyse the diversity and distribution patterns of Trifolium pratense L. within a defined ecological framework.

Result: The study identified 26 districts across three Indian states/Union Territories as suitable for red clover cultivation and on-farm conservation: 16 districts in Jammu and Kashmir (J and K), 6 in Himachal Pradesh and 4 in Uttarakhand. Agronomic characterization of 26 red clover accessions collected from various locations in Jammu  and Kashmir revealed notable variability in several traits, including plant height (34.8-64.6 cm), leaf length (22.8-65.4 mm), leaf width (13.7-45.5 mm), floret number per flower head (30.2-74.3) and dry matter yield per plant (18.0-49.4 g). Nutritional analysis also demonstrated variation in crude protein content (20.2-23.6%), neutral detergent fibre (48.3-54.2%) and acid detergent fibre (37.2-42.8%). DIVA-GIS analysis highlighted the existence of diversity-rich pockets in the southwestern region of Jammu and Kashmir. These areas represent valuable reservoirs of genetic diversity and could play a crucial role in conservation strategies while offering insights into the taxonomy, origin and evolution of the species in the Himalayan region.

Forage crops are vital for livestock nutrition, offering a balanced diet that promotes animal health, growth and productivity (Karthikeyan et al., 2024; Ravi et al., 2023). Grasses and cereal forages serve as key energy sources, supplying the carbohydrates required for maintenance and productive functions. In contrast, leguminous fodders such as alfalfa and clover are rich in protein, playing a critical role in muscle development, milk yield and overall growth (Kumar et al., 2016; Shri Rangasami et al., 2024). Perennial temperate forage crops are a vital component of livestock feeding systems, supplied in fresh (cut-and-carry), dried (hay), or conserved (silage) forms due to their rich nutritional content, including proteins, carbohydrates, vitamins and minerals (Singh et al., 2023). These crops are extensively grazed and can also be stored for feeding during lean periods. Legume crops, encompassing key grain, pasture and agroforestry species, play a vital role in ensuring agricultural, food, nutritional and livelihood security for hill farmers (Pandey and Kumar, 2014; Takawale et al., 2016).  The significance of legume crops lies in their rich nutritional profile (Jat et al., 2024), characterized by high protein content (17-50%), slow-digesting carbohydrates (0.4-55%), substantial dietary fiber (3-15%) and low fat levels (0.8-6.6%). Legumes rank third in global crop production, following cereals and oilseeds and serve as a crucial source of food, feed and fodder across both temperate and tropical climates (Kumar, 2021). Forage legumes, in particular, play a critical role not only in meeting the mineral and vitamin needs of livestock but also in enhancing soil fertility through nitrogen fixation, thereby reducing the need for synthetic fertilizers (Frame​ et al., 1998; Rasmussen et al., 2012; Carranca et al., 2015; Kamboj and Nanda, 2018). In addition, their brightly coloured flowers attract pollinators, supporting biodiversity and honey production (Nicholls and Altieri, 2013).
       
Trifolium
is a significant genus within the legume family, comprising over 200 species, though only a few are widely cultivated (Abberton and Thomas, 2011). Among these, red clover (Trifolium pratense) and white clover (T. repens) have been extensively used to improve temperate pastures and boost soil nitrogen levels. Red clover is a key forage species found in diverse habitats such as forests, meadows, orchards, cultivated lands and wastelands. Native to Eurasia and first domesticated in Europe, it is known for moderate persistence, providing good forage yields for about 3 to 6 years in pure stands. Cytogenetically, red clover is a diploid species (2n = 2x = 14) with a heterozygous nature due to gametophytic self-incompatibility (Taylor, 1982).
       
Ecological niche modelling (ENM) has become an effective tool for understanding species-climate relationships and predicting potential shifts in species distribution. The MaxEnt (maximum entropy) algorithm is widely used for this purpose, offering valuable insights for cultivation planning under current and future climate scenarios (Phillips, 2006). DIVA-GIS, an open-source software, is also frequently applied in biodiversity and spatial analysis. Given the increasing global focus on food and fodder security and the conservation of genetic resources, species like Trifolium offer promising opportunities for sustainable agriculture in temperate and sub-temperate regions.
               
The present study aims to assess the ecological resilience and diversity of red clover (Trifolium pratense L.) in the northwestern Himalayan region of India. Using Ecological Niche Modelling and DIVA-GIS, this research evaluates 26 districts across three states/Union Territories to identify suitable areas for cultivation and promote on-farm conservation of this valuable forage legume.
Data recording
 
A total of 26 accessions of Red clover collected from diverse ecological niches of Jammu and Kashmir were evaluated at ICAR- IGFRI Regional Station, Srinagar, Jammu and Kashmir (33o59' N latitude, 74o47' E longitude, 1640 m above mean sea level) consecutively for two years (Table 1). The recommended packages of practices were followed to raise a good crop. Sowing was done with (30 cm x 20 cm) crop geometry. Each genotype was sown in 3 rows of 3m length.The observations on six quantitative traits viz., plant height (cm), leaf length (mm), leaf width (mm), floret number per flower head, 100 seed weight (mg), dry matter per plant (g) were recorded on five random plants. Nutritional parameters like Crude protein % (CP), Neutral detergent fibre % (NDF), Acid detergent fibre % (ADF) were also analysed following standard procedures (Van soest, 1991; AOAC, 2000). Statistical analysis was done using MS Excel to work out descriptive statistics and variability patterns and Statistical Package for the Social Sciences (SPSS, version 19) for carrying out multivariate analysis of quantitative traits.

Table 1: Variability observed for different traits in red clover germplasm.


 
MaxEnt and DIVA-GIS analysis
 
MaxEnt software version 3.3.3k downloaded from www. cs.princeton.edu/~schapire/maxent was used for ecological niche modelling of red clover. Using 11 selected red clover evidence points which were surveyed during exploration missions organised by the Regional Research Station, Srinagar (J and K), ICAR- Indian grassland and fodder research institute (IGFRI), MaxEnt runs were performed.  The red clover evidence points were recorded using global positioning system (Garmin GPS-12). World clim (WC) database (http://www.worldclim.org), provides interpolated global climate surfaces using latitude, longitude and altitude as independent variables and represents long-term (1950-2000) monthly means of maximum, minimum, mean temperatures and total rainfall. For future climates, we used global circulation model outputs from the Intergovernmental panel on climate change, Fourth assessment report (Solomon et al., 2007). Default settings were used in MaxEnt so that the complexity of the models varied depending upon the number of data points used for model fitting. The ASCI-file generated by the MaxEnt run for current and future climatic situations of red clover were imported to grid file using DIVA-GIS software version 7.5 (Hijmans et al., 2012). The grid layer generated for each current and future climate was overlaid on India shapefile using DIVA-GIS and analysed. Diversity analysis of red clover plant traits was analysed using data and analysis menu bars on the DIVA-GIS window.
Agronomic characterization
 
Mean values of various agronomic and nutritional data recorded during the present study have shown significant differences among various accessions. Significant variability was observed for various quantitative traits within the accessions studied (Table 1).

Plant height  varied from 34.8 cm (IC-0622345) to 64.6 cm (IC­0615770), floret number per flower head  from 30.2 (IC-0622340) to 74.3 (IC-0622358), 100 seed weight from 0.132 (IC-0622345) to 0.178 mg (IC-0622358), dry matter per plant from 18.0 g (IC-0622345) to 49.4 g (IC-0622358), leaf length from 22.82 mm (IC-0622340) - 65.42 mm (IC-0622358), leaf width varied from 13.7 mm (IC-0622340) to 45.5 mm (IC-0622358). A high coefficient of variation was observed in leaf width (33.35), dry matter (26), leaf length (19.89), floret number per flower head (19.92), plant height (16.64) and less coefficient of variation was observed in forage quality parameters. Crude protein (%) showed a range of (20.21-23.64%), NDF (48.35-54.23) and ADF (37.17-42.78). Significant variation was also observed in ‘V’ marking, in some accessions, conspicuous in some whereas less prominent in others as well as absent in some (Plate 1). 

Plate 1: Variability of leaf size and ‘V’mark in red clover.


       
Probably, the present study would be the first of its kind analysing the morphological variability of red clover in India. However, its genetic diversity has been reported by few researchers around the world (De vega et al., 2015; Jones et al., 1997).  Although, a similar study was carried out with comprehensive characterization as well as comparative evaluation of white clover germplasm based on a number of agromorphological traits in mid-hills of Himachal Pradesh, India (Singh et al., 2021). Climate variables play a pivotal role in determining the genetic structure of plant populations (Greene et al., 2004).  Dendrogram based on the average linking methods grouped 26 accessions into three clusters (Fig 1). Cluster I consist of two accessions (IC-622345 and IC 622340), cluster- II consists of 04 accessions (IC- 622377, IC-622381, IC-622373 and IC-615770), cluster-III can be grouped into sub-cluster –IIIA with 06 accessions ( IC-622408, IC-622378, IC-615793, IC-622384, IC-622354 and IC-622394), cluster- III B with 14 accessions comprises of IC-622375, IC-622374, IC-622400, IC-615794, IC-622358, IC-622417, IC-622364, IC-622335, IC-622402, IC-615787, IC-622423, IC-615772, IC-615792 and IC-615781. The results are in conformity with the studies conducted in other legume crops by Goudar et al., (2017) and Wankhade et al., (2017) and Makwana et al., (2024).

Fig 1: Dendrogram using average linkage method between groups performed on plant traits.



MaxEnt analysis
 
We have used MaxEnt for generating Ecological Niche Models based on current and future climatic grids. Maximum entropy (Maxent) as a niche modelling approach has been used for making predictions or inferences from incomplete information. The species distribution models generated for red clover based on current and future climate grids have been presented (Fig 2 and 3) respectively. The probability distribution has been calculated as the sum of each weighted variable divided by a scaling constant to ensure that the probability value ranges from 0 to 1. The program starts with a uniform probability distribution and works in cycles adjusting the probabilities to maximum entropy. It iteratively alters one weight at a time to maximize the likelihood of reaching the optimum probability distribution. The information available about the target distribution of red clover often presents itself as a set of real-valued variables, called ‘features’ and the constraints are that the expected value of each feature should match its empirical average (Phillips et al., 2006).

Fig 2: Ecological niche model generated for red clover (current climate).



Fig 3: Ecological niche model generated for red clover (future climate).


       
The potential regions identified for red clover genetic resource management in Kashmir valley, Himachal Pradesh and Uttarakhand have been provided (Table 2).

Table 2: Potential regions identified for red clover (Trifolium pratense L.) genetic resources management.


       
A total of 21 districts were identified in three states/UTsof India covering 11 districts inthe UT of J  and K, 06 in Himachal Pradesh and 04 in Uttarakhand, respectively, for cultivation and on-farm conservation of red clover. Table 3 gives an estimation of relative contributions of the environmental variables to the MaxEnt models of current and future climatic conditions. Bioclimatic variables viz., temperature annual range (bio 7), precipitation of coldest quarter (bio 19), precipitation of driest month (bio14), minimum temperature of the coldest month (bio6), precipitation of wettest quarter (bio 16) contributed maximum to the current climate model with percentage values of 46.6, 9.9, 9.3, 5.1, 5.1 respectively (Table 2). Interestingly, the niche model for future climate governed by the bioclimatic variables, Mean temperature of warmest quarter (bio 10), temperature annual range (bio 7), precipitation of wettest month (bio 13), precipitation of driest month (bio 14), precipitation of coldest quarter (bio 19) with percentage values of 33.2, 18.5, 14.2, 8.9 and 12.6 respectively.

Table 3: Estimates of relative contributions of the environmental variables to the MaxEnt models (Current and future) for red clover (Trifolium pratense L.).


       
MaxEnt is considered as the most accurate model performing extremely well in predicting occurrences with other common approaches (Hijmans and Graham, 2006), especially with incomplete information. Such modelling of red clover geographic distributions based on locality factors provides an important information on the ecology, conservation biology and invasive-species management (Welk et al., 2002; Peterson and Shaw, 2003). The MaxEnt modelling approach can be used in its present form for many applications with presence-only datasets and merits further research and development (Sivaraj et al., 2016). MaxEnt as a successful prediction distribution has been used by many researchers earlier, coral reefs (Tittensor et al., 2009); forests (Carnaval and Moritz, 2008), rare plants (Williams et al., 2009) and many other species (Elith et al., 2006). The availability of detailed environmental databases, comprising ofcheap and efficient computer technology, has driven a rapid increase in predictive modelling of species environmental requirements and geographic distributions. The potential impact of climate changes on terrestrial production (especially agricultural crop) varies spatially and depends on crop-specific biophysical constraints (Kumar et al., 2021). Due to increase in animal population worldwide, the demand for fodder sources would increase in the changed climate regime. As the extensive adaptation of red clover would prove vital in meeting food security, use of MaxEnt method is highly warranted in preserving the important forage species. The potential regions identified using MaxEnt analysis would be providing new insights in red clover genetic resources in Kashmir valley and in the states of Himachal Pradesh and Uttarakhand.

DIVA-GIS diversity-analysis
 
DIVA-GIS diversity analysis was performed for the selected plant traits viz., plant height, floret, dry matter, crude protein, neutral detergent fiber and acid detergent fiber (Fig 4).  Diversity rich pockets exist in Anantnag, Kupwara, Badgam districts of J and K as derived from the DIVA-analysis diversity maps. High diversity values ranging from 2.1-3.0 were recorded for the phenotypic traits of red clover germplasm collected from J and K. A better perception of the red clover genetic diversity distribution is essential for its conservation and use. Hence, diversity-rich pockets are to be identified for covering maximum diversity that will help us in determining the conservation strategy and will improve our understanding of the taxonomy and the origin and evolution. The study showed a greater diversity in South-Western parts of J  and K, indicating that this region is an important habitat for planning on-farm conservation. GIS mapping has been successfully used in assessing biodiversity and in identifying areas of high diversity in several crops, like Phaseolus bean (Jones et al., 1997), wild potatoes (Hijmans and David, 2001), horsegram (Sunil et al., 2008), linseed (Sivaraj et al., 2009), blackgram (Babu Abraham  et al., 2010), medicinal plants (Varaprasad et al., 2007) and agrobiodiversity (Varaprasad et al., 2008).

Fig 4: DIVA-GIS diversity analysis for red clover.

Among the 26 accessions collected and evaluated, IC-0615770 and IC-0622358 showed superior performance across multiple agronomic and quality parameters, making them highly promising candidates for forage improvement programs. Ecological niche modelling identified 26 districts across Jammu and Kashmir (16), Himachal Pradesh (6) and Uttarakhand (4) as suitable zones for red clover cultivation under current and future climate scenarios. Notably, bioclimatic variables such as temperature annual range, precipitation of the driest month and minimum temperature of the coldest month were found to be the most influential environmental factors determining the species’ distribution. DIVA-GIS-based diversity analysis revealed diversity-rich pockets in the southwestern parts of Jammu  and Kashmir, particularly Anantnag, Kupwara and Budgam districts. Further molecular marker-based diversity studies (e.g. SSRs, SNPs) are recommended to validate and deepen our understanding of genetic diversity and population structure. Identified high-performing accessions should be evaluated under multi-location trials across varying altitudes and stress conditions (drought, cold, pests) to develop climate-resilient cultivars.
Authors are thankful to Indian Council of Agricultural Research and Director, ICAR-IGFRI, Jhansi for providing facilities and essential help.
 
Disclaimers
 
The views and conclusions expressed in this article are solely those of the authors and do not necessarily represent the views of their affiliated institutions. The authors are responsible for the accuracy and completeness of the information provided, but do not accept any liability for any direct or indirect losses resulting from the use of this content.
 
Informed consent
 
All animal procedures for experiments were approved by the Committee of Experimental Animal care and handling techniques were approved by the University of Animal Care Committee.
The authors declare that there are no conflicts of interest regarding the publication of this article. No funding or sponsorship influenced the design of the study, data collection, analysis, decision to publish or preparation of the manuscript.
 

  1. Abberton, M.T., Thomas, I. (2011). Genetic resources in Trifolium and their utilization in plant breeding. Plant Genetic Resources. 9: 38-44. 

  2. AOAC. (2000). Official Methods of Analysis Association of Official Analytical Chemists, Arlington, VA, USA.

  3. Babu Abraham, V., Kamala, N., Sivaraj, N., Sunil, N., Pandravada, S.R., Vanaja, M. and Varaprasad, K.S. (2010). DIVA-GIS approaches for diversity assessment of pod characteristics in black gram [Vigna mungo (L.) Hepper]. Current Science. 98: 616-619.

  4. Carnaval, A.C., Moritz, C. (2008). Historical climate modelling predicts patterns of current biodiversity in the Brazilian Atlantic forest. Journal of Biogeography. 35: 1187-1201.

  5. Carranca, C., Torres, M.O., Madeira, M. (2015). Underestimated role of legume roots for soil N fertility. Agronomy for Sustainable Develpment. 35: 1095-1102. https://doi.org/10.1007/ s13593-015-0297-y.

  6. De Vega, J.J., Ayling, S., Hegarty, M., Kudrna, D., Goicoechea, J.L., Ergon, A., Rognli, O.A. et al. (2015). Red clover (Trifolium pratense L.) draft genome provides a platform for trait improvement. Scientific Reports. 5: 17394. doi: 10.1038/ srep17394.

  7. Elith, J., Graham, C.H. Anderson, R.P., Dudý´k, M., Ferrier, S., Guisan, A., Hijmans, R.J. et al. (2006). Novel methods improve prediction of species’ distributions from occurrence data. Ecography. 29: 129-151.

  8. Frame, J., Charlton, J.F.L. Laidlaw, A.S. (1998). Temperate Forage Legumes. Wallingford, UK: CAB International. 327.

  9. Goudar, R., Srinivasa, V. and Lakshmana, D. (2017). Genetic variability and divergence studies in cluster bean (Cyamopsis tetragonoloba L.) under hill zone of Karnataka, India. Legume Research. 40: 237-240. doi: 10.18805/lr.v0iOF. 11313.

  10. Greene, S.L., Gritsenko, M., Vandemark, G. (2004). Relating morphologic and RAPD marker variation to collection site and environ- ment in wild populations of red clover (Trifoliump ratense L.). Genetic Resources and Crop Evolution. 51: 643-653.

  11. Hijmans, R.J. and David, M. (2001). Geographic distribution of wild potato species. American Journal of Botany. 88: 2101- 2112.

  12. Hijmans, R.J., Graham, C. (2006). The ability of climate envelope models to predict the effect of climate change on species distributions. Global Change Biology. 12: 2272-2281.

  13. Hijmans, R.J., Guarino, L., Mathur, P. (2012). DIVA-GIS Version 7.5, Manual. www.diva-gis.org.

  14. Jat, B.L., Sharma, H.C., Pagaria, P., Meena, A.K., Mali, G.R. and Khan, T. (2024). Legumes: Source of bioactive compounds and their potential use in legume crops improvement: A review. Legume Research. 47(11): 1827-1834. doi: 10. 18805/LR-4945.

  15. Jones, P.G., Beebe, S.E., Tohme, J. and Galway, N.W. (1997). The use of geographical information systems in biodiversity exploration and conservation. Biodiversity and Conservation. 6: 947-958.

  16. Kamboj, R. and Nanda, V. (2018). Proximate composition, nutritional profile and health benefits of legumes -A review. Legume Research. 41(3): 325-332, DOI: 10.18805/LR-3748.

  17. Karthikeyan, C., Rangasami, S.S. and Kumar, S.A. (2024). Digital revolution in livestock rarming: Empowering indian farmers with TNAU Cattle expert system and userfeedback insights. Indian Journal of Animal Research. 1: 8. doi: 10.18805/ IJAR.B-5383.

  18. Kumar, A., Pinto, M.C., Candeias, C., Dinis, P.A. (2021). Baseline maps of potentially toxic elements on soils of Garhwal Himalaya, India: assessment of their eco-environmental and human health risks. Land Degradation and Development. 32(8). https://doi.org/10.1002/ldr.3984.

  19. Kumar, B. (2021). Plant bio-regulators for enhancing grain yield and quality of legumes: A review. Agricultural Reviews. 42(2): 175-182. DOI: 10.18805/ag.R-2068.

  20. Kumar, R., Singh, M., Tomar, S.K., Meena, B.S. and Rathore, D.K. (2016). Productivity and nutritive parameters of fodder maize under varying plant density and fertility levels for improved animal productivity. Indian Journal of Animal Research. 50(2): 199-202. doi: 10.18805/ijar.9423.

  21. Makwana, H.M., Patel, P.R. and Patel, D.G. (2024). Genetic diversity for seed yield and its components in clusterbean [Cymopsis tetragonaloba (L.) Taub]. Indian Journal of Agricultural Research. 58(4): 576-580. doi: 10.18805/IJARe.A-5791. 

  22. Nicholls, C., Altieri, M. (2013). Plant biodiversity enhances bees and other insect pollinators agroecosystems. Agronomy for Sustainable Development. 33: 257-274.

  23. Pandey, M. and Kumar, N. (2024). Diversity of traditional grain legumes of Himalayan region of Uttarakhand: A review. Agricultural Reviews. 45(1): 96-102. doi:10.18805/ag.R- 2362. 

  24. Peterson, A.T., Shaw, J. (2003). Lutzomyia vectors for cutaneous leishmaniasis in southern Brazil: ecological niche models, predicted geographic distribution and climate change effects. Int. J. Parasitol. 33: 919-931.

  25. Phillips, S.J. anderson, R.P., Schapire. R.E. (2006). Maximum entropy modelling of species geographic distributions. Ecological Modelling. 190: 231-259.

  26. Rasmussen, J., Yalcinb, F.N., Nemutlu, E., Akkol, E.K., Suntar, I., Keles, H., Ina, H., Calis, I., Ersoz, T. (2012). N2-fixation and residual N effect of four legume species and four companion grass species. European Journal of Agronomy. 36: 66-74.

  27. Ravi, S., Rangasami, S.R., Vadivel, N., Ajaykumar, R. and Harishankar, K. (2023). Growth and yield attributes of groundnut (Arachis hypogaea L.) as influenced by tank-mix application of early post emergence herbicides. Legume Research. 46(8): 1080-1086. doi: 10.18805/LR-5147.

  28. Shri Rangasami, S.R., Purnima, M., Pushpam, R., Ajaykumar, R., Thirunavukkarasu, M., Sathiya, K., Rajanbabu, V. and Yazhini, G. (2024). Enhancing animal nutritional security through biofortification in forage crops: A comprehensive review. Indian Journal of Animal Research. 58(11): 1838- 1845. doi:10.18805/IJAR.B-5466.  

  29. Singh , T., Radotra, S. and Deb, D. (2021). Evaluation of white clover (Trifolium repens L.) germplasm for different agro- morphological traits diversity in mid-himalayan region. Legume Research. 44(7): 766-772. doi: 10.18805/LR- 4160.

  30. Singh, S., Ahmad, S. Bhat, S.S. Singh, T. and Mir, N.H. (2023). Yield and nutritive value of local races of grasses and legumes to rejuvenate pastures for sustaining livestock productivity in sub-Himalayan region of India. Range Management and Agroforestry 44(2): 353-362.

  31. Sivaraj, N., Elangovan, M., Kamala, V., Pandravada, S.R., Pranusha, P., Chakrabarty, S.K. (2016). Maximum entropy (maxent) approach to sorghum landraces distribution modelling. Indian Journal of Plant Genetic Resources. 29(1): 16- 21.

  32. Sivaraj, N., Sunil, N., Pandravada, S.R., Kamala, V., Rao, V.K., B.V.S.K., Prasad, R.B.N. and Varaprasad, K.S. (2009). DIVA-GIS approaches for diversity assessment of fatty acid composition in linseed (Linum usitatissimum L.) germplasm collections from peninsular India. Journal of Oilseeds Research. 26: 13-15

  33. Solomon, S., Qin D., Manning, M., Chen, Z., Marquis, M., Averyt, K.B., Tignor, M., Miller, H.L. (2007): Summary for policy- makers, the physical science basis. Contribution of working group I to the fourth assessment report of the inter- governmental panel on climate change. http://goo.gl/N4RMw.

  34. Sunil, N., Sivaraj, N., Pandravada, S.R., Kamala, V., Raghuram Reddy, P. and Varaprasad, K.S. (2008). Genetic and geographical divergence in horsegram germplasm from Andhra Pradesh, India. Plant Genetic Resources: Characterization and Utilization. 7: 84-87.

  35. Takawale, P.S., Jade, S.S. and Ghorpade, S.D. (2016). Leguminous blocks: Nutritional values and economics. Agriculture Science Digest.  36(2): 149-151, DOI:10.18805/asd.v0iof. 9623.

  36. Taylor, N.L. (1982). Stability of S alleles in a double cross hybrid of  red clover1. Crop Sci. 22: 1222-1225.

  37. Tittensor, D.P., Baco-Taylor, A.R., Brewin, P., Clark, M.R., Consalvey, M., Hal-Spencer, J., Rowden, A.A., Schlacher, T., Stocks, K., Rogers, A.D. (2009). Predicting global habitat suitability for stony corals on seamounts. Journal of Biogeography 36: 1111-1128.

  38. Van Soest, P.J., Robertson, J.B. and Lewis, B.A. (1991). Methods for dietary fibre, neutral detergent fibre and non-starch polysaccharides in relation to animal nutrition. Journal of Dairy Science. 74: 3583-3597.

  39. Varaprasad, K.S., Sivaraj, N., Ismail, M. and Pareek, S.K.(2007). GIS mapping of selected medicinal plants diversity in the Southeast coastal zone for effective collection and conservation. In: Advances in Medicinal Plants. [Reddy, K.J., Bahadur, B.B., Bhadraiah and Rao, M.L.N. (eds)] Universities  Press (India) Private Ltd. pp 69-78. 

  40. Varaprasad, K.S., Sivaraj, N., Pandravada, S.R., Kamala, V. and Sunil, N. (2008). GIS mapping of agrobio-diversity in Andhra Pradesh. Proceedings of Andhra Pradesh Akademi of Sciences. Special Issue on Plant wealth of Andhra Pradesh. pp: 24-33.

  41. Wankhade, R.S., Kale, V.S., Nagre, P.K. and Patil, R.K. (2017). Genetic divergence studies in cluster bean genotypes. Legume Research. 40(5): 811-817. doi: 10.18805/lr.v0i0.7292.

  42. Welket, E., Schubert, K. and Hoffmann, M.H. (2002). Present and potential distribution of invasive mustard (Alliara petiolata) in North America. Diversity and Distributions. 8: 219-233.

  43. Williams, J.N., Seo, C.W., Thorne, J., Nelson, J.K., Erwin, S., O’brien, J.M., Schwartz, M.W. (2009). Using species distribution models to predict new occurrences for rare plants. Diversity and Distributions. 15: 565-576.

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