Open Access Open Access  Restricted Access Subscription Access

Focal Plant and Neighbourhood Fruit Crop Size Effects on Fruit Removal by Frugivores in a Semi-Arid Landscape Invaded by Lantana camara L.


Affiliations
1 Nature Conservation Foundation, Mysuru - 570 002, India
2 Wildlife Institute of India, Dehradun - 248 002, India

Mutualistic associations between frugivorous vertebrates and fleshy-fruited plants result in seed dispersal, a vital ecological process affecting plant populations and communities. Invasive fleshy-fruited plants can easily integrate into existing mutualistic networks if generalist frugivorous species start consuming invasive fruit. Additionally, the presence of a copiously fruiting invasive plant in the neighbourhood of fruiting native plants could affect the fruit removal from such plants by either reducing (competitive interaction), increasing (facilitative interaction) or not affecting (no interaction) visits by frugivorous vertebrates. In this study, we explore the effects of the presence of a fruiting invasive shrub Lantana camara L. in the neighbourhood of fruiting native species Erythroxylum monogynum Roxb. and Flueggea leucopyrus Willd. on the visit and fruit removal rate by avian frugivores in a semi-arid bird preserve in southern India. We conducted plant watches within fruiting patches of 30 m radius and observed the identity, numbers and fruit-handling behaviour by avian frugivores on focal native plants. We found that, on average, for the same fruit crop size, E. monogynum received more visits and more fruit removal than F. leucopyrus irrespective of the presence of fruiting neighbours. Focal tree fruit crop size was a better predictor of frugivore behaviour than the fruit crop size of neighbouring plants (both native and invasive) and was positively associated with frugivore visit rate and fruit removal from focal plants. We infer that there is little evidence for facilitation or competition by invasive neighbours for the dispersal services of vertebrate mutualists at the spatial and temporal scale examined in this study. Longer-term, larger-scale data are required to assess the changing impacts of invasive plants on native plant–frugivore interactions.

Keywords

Fruiting Neighbourhood, Invasive Plant, Lantana camara, Plant-Frugivore Association, Semi-Arid Landscape.
User
Notifications
Font Size

  • Nathan, R. and Muller-Landau, H. C., Spatial patterns of seed dispersal, their determinants and consequences for recruitment. Trends Ecol. Evol., 2000, 15, 278-285.
  • Levine, J. M. and Murrell, D. J., The community-level consequences of seed dispersal patterns. Annu. Rev. Ecol., Evol. Syst., 2003, 34, 549-574.
  • Bascompte, J., Jordano, P. and Olesen, J. M., Asymmetric coevolutionary networks facilitate biodiversity maintenance. Science, 2006, 312, 431-433.
  • Pearson, R. G. and Dawson, T. P., Long-distance plant dispersal and habitat fragmentation: identifying conservation targets for spatial landscape planning under climate change. Biol. Conserv., 2005, 123, 389-401.
  • Levey, D. J., Bolker, B. M., Tewksbury, J. J., Sargent, S. and Haddad, N. M., Effects of landscape corridors on seed dispersal by birds. Science, 2005, 309, 146-148.
  • Wenny, D. G., Sekercioglu, Ç. H., Cordeiro, N. J., Rogers, H. S. and Kelly, D., Seed dispersal by fruit-eating birds. In Why Birds Matter: Avian Ecological Function and Ecosystem Services, University of Chicago Press, Chicago, 2016.
  • Burns, K. C., What causes size coupling in fruit-frugivore interaction webs? Ecology, 2013, 94, 295-300.
  • Bello, C. et al., Atlantic frugivory: a plant-frugivore interaction data set for the Atlantic Forest. Ecology, 2017, 98, 1729-1729.
  • Schaefer, H. M., Schmidt, V. and Winkler, H., Testing the defence trade-off hypothesis: how contents of nutrients and secondary compounds affect fruit removal. Oikos, 2003, 102, 318-328.
  • Blendinger, P. G., Loiselle, B. A. and Blake, J. G., Crop size, plant aggregation, and microhabitat type affect fruit removal by birds from individual melastome plants in the Upper Amazon. Oecologia, 2008, 158, 273-283.
  • Smith, A. D. and McWilliams, S. R., Fruit removal rate depends on neighborhood fruit density, frugivore abundance, and spatial context. Oecologia, 2014, 174, 931-942.
  • Morales, J. M. and Carlo, T. A., The effects of plant distribution and frugivore density on the scale and shape of dispersal kernels. Ecology, 2006, 87, 1489-1496.
  • Morales, J. M., Rivarola, M. D., Amico, G. and Carlo, T. A., Neighborhood effects on seed dispersal by frugivores: testing theory with a mistletoe-marsupial system in Patagonia. Ecology, 2012, 93, 741-748.
  • Richardson, D. M., Allsopp, N., D'Antonio, C. M., Milton, S. J. and Rejmánek, M., Plant invasions - the role of mutualisms. Biol. Rev. Camb. Philos. Soc., 2000, 75, 65-93.
  • Traveset, A. and Richardson, D. M., Biological invasions as disruptors of plant reproductive mutualisms. Trends Ecol. Evol., 2006, 21, 208-216.
  • Bascompte, J. and Jordano, P., Plant-animal mutualistic networks: the architecture of biodiversity. Ann. Rev. Ecol., Evol. Syst., 2007, 38, 567-593.
  • Buckley, Y. M. et al., Management of plant invasions mediated by frugivore interactions. J. Appl. Ecol., 2006, 43, 848-857.
  • Davis, M., Do native birds care whether their berries are native or exotic? No. BioScience, 2011, 61, 501-502.
  • Kueffer, C., Kronauer, L. and Edwards, P. J., Wider spectrum of fruit traits in invasive than native floras may increase the vulnerability of oceanic islands to plant invasions. Oikos, 2009, 118, 1327-1334.
  • Mokotjomela, T. M., Musil, C. F. and Esler, K. J., Frugivorous birds visit fruits of emerging alien shrub species more frequently than those of native shrub species in the South African Mediterranean climate region. S. Afr. J. Bot., 2013, 86, 73-78.
  • Traveset, A. and Richardson, D. M., Mutualistic interactions and biological invasions. Ann. Rev. Ecol., Evol. Syst., 2014, 45, 89- 113.
  • Richardson, D. M. and Rejmánek, M., Trees and shrubs as invasive alien species - a global review. Div. Distrib., 2011, 17, 788- 809.
  • Bhagwat, S. A., Breman, E., Thekaekara, T., Thornton, T. F. and Willis, K. J., A battle lost? Report on two centuries of invasion and management of Lantana camara L. in Australia, India and South Africa. PLoS ONE, 2012, 7, e32407.
  • Kannan, R., Shackleton, C. M. and Shaanker, R. U., Reconstructing the history of introduction and spread of the invasive species, Lantana, at three spatial scales in India. Biol. Invasions, 2013, 15, 1287-1302.
  • Aravind, N. A., Rao, D., Ganeshaiah, K. N., Uma Shaanker, R. and Poulsen, J. G., Impact of the invasive plant, Lantana camara, on bird assemblages at Male Mahadeshwara Reserve Forest, South India. Trop. Ecol., 2010, 51, 325-338.
  • Ramaswami, G., Kaushik, M., Prasad, S., Sukumar, R. and Westcott, D., Dispersal by generalist frugivores affects management of an invasive plant. Biotropica, 2016, 48, 638-644.
  • Chimera, C. G. and Drake, D. R., Patterns of seed dispersal and dispersal failure in a Hawaiian dry forest having only introduced birds. Biotropica, 2010, 42, 493-502.
  • Heleno, R. H., Ramos, J. A. and Memmott, J., Integration of exotic seeds into an Azorean seed dispersal network. Biol. Invasions, 2013, 15, 1143-1154.
  • Ramaswami, G., Somnath, P. and Quader, S., Plant-disperser mutualisms in a semi-arid habitat invaded by Lantana camara L. Plant Ecol., 2017, 218, 935-946.
  • Davidar, P. and Morton, E. S., The relationship between fruit crop sizes and fruit removal rates by birds. Ecology, 1986, 67, 262- 265.
  • Murray, K. G., Selection for optimal fruit-crop size in birddispersed plants. Am. Nat., 1987, 129, 18-31.
  • Willson, M. F. and Whelan, C. J., Variation of dispersal phenology in a bird-dispersed shrub, Cornus drummondii. Ecol. Monographs, 1993, 63, 151-172.
  • Ortiz-Pulido, R. and Rico-Gray, V., The effect of spatio-temporal variation in understanding the fruit crop size hypothesis. Oikos, 2000, 91, 523-527.
  • Camargo, P. H., Martins, M. M., Feitosa, R. M. and Christianini, A. V., Bird and ant synergy increases the seed dispersal effectiveness of an ornithochoric shrub. Oecologia, 2016, 181, 507-518.
  • Prasad, S. and Sukumar, R., Context-dependency of a complex fruit-frugivore mutualism: temporal variation in crop size and neighborhood effects. Oikos, 2010, 119, 514-523.
  • Aslan, C. E. and Rejmánek, M., Avian use of introduced plants: ornithologist records illuminate interspecific associations and research needs. Ecol. Appl, 2010, 20, 1005-1020.
  • Jordaan, L. A. and Downs, C. T., Nutritional and morphological traits of invasive and exotic fleshy-fruits in South Africa. Biotropica, 2012, 44, 738-743.
  • Gosper, C. R. and Vivian-Smith, G., Selecting replacements for invasive plants to support frugivores in highly modified sites: a case study focusing on Lantana camara. Ecol. Manage. Restor., 2006, 7, 197-203.
  • Carlo, T. A. and Morales, J. M., Inequalities in fruit-removal and seed dispersal: consequences of bird behaviour, neighbourhood density and landscape aggregation. J. Ecol., 2008, 96, 609-618.

Abstract Views: 236




  • Focal Plant and Neighbourhood Fruit Crop Size Effects on Fruit Removal by Frugivores in a Semi-Arid Landscape Invaded by Lantana camara L.

Abstract Views: 236  | 

Authors

Geetha Ramaswami
Nature Conservation Foundation, Mysuru - 570 002, India
Brihadeesh Santharam
Wildlife Institute of India, Dehradun - 248 002, India
Suhel Quader
Nature Conservation Foundation, Mysuru - 570 002, India

Abstract


Mutualistic associations between frugivorous vertebrates and fleshy-fruited plants result in seed dispersal, a vital ecological process affecting plant populations and communities. Invasive fleshy-fruited plants can easily integrate into existing mutualistic networks if generalist frugivorous species start consuming invasive fruit. Additionally, the presence of a copiously fruiting invasive plant in the neighbourhood of fruiting native plants could affect the fruit removal from such plants by either reducing (competitive interaction), increasing (facilitative interaction) or not affecting (no interaction) visits by frugivorous vertebrates. In this study, we explore the effects of the presence of a fruiting invasive shrub Lantana camara L. in the neighbourhood of fruiting native species Erythroxylum monogynum Roxb. and Flueggea leucopyrus Willd. on the visit and fruit removal rate by avian frugivores in a semi-arid bird preserve in southern India. We conducted plant watches within fruiting patches of 30 m radius and observed the identity, numbers and fruit-handling behaviour by avian frugivores on focal native plants. We found that, on average, for the same fruit crop size, E. monogynum received more visits and more fruit removal than F. leucopyrus irrespective of the presence of fruiting neighbours. Focal tree fruit crop size was a better predictor of frugivore behaviour than the fruit crop size of neighbouring plants (both native and invasive) and was positively associated with frugivore visit rate and fruit removal from focal plants. We infer that there is little evidence for facilitation or competition by invasive neighbours for the dispersal services of vertebrate mutualists at the spatial and temporal scale examined in this study. Longer-term, larger-scale data are required to assess the changing impacts of invasive plants on native plant–frugivore interactions.

Keywords


Fruiting Neighbourhood, Invasive Plant, Lantana camara, Plant-Frugivore Association, Semi-Arid Landscape.

References





DOI: https://doi.org/10.18520/cs%2Fv116%2Fi3%2F405-411