Abstract
Our objectives were to examine the species composition and diversity of soil seed bank (SSB) and standing vegetation (SV), explore association between compositional diversity of SV, SSB and selected environmental factors and assess the implications of SSB on regeneration of flooded riparian vegetation in Hamedan province, Iran. We estimated the ground cover of SV and SSB composition in 90 plots (1 m × 1 m) distributed across 15 sites in the river riparian zone. We evaluated the SSB by seedling emergence method. Canonical correspondence analysis (CCA) was used in a direct gradient analysis of the SV/SSB with the environmental factors. In total, 136 species were identified from germinated seed bank in the greenhouse and there were 131 plant species recorded in the aboveground vegetation. 31 species were observed in the SSB while they were absent in the SV, while there were also 26 species that were only present in the SV. Dominant species in the SSB were floatable seed species, i.e. Cyperus difformis and Dactylis glomerata. In addition, the results indicated a more pronounced effect of environmental factors on SV than on SSB distributions in which a higher number of environmental factors associated significantly with SV than with SSB (6 vs. 4). However, elevation, soil moisture content and total organic matter had significant effects on community distribution of both SSB and SV. The species diversity and composition evenness were significantly higher in the SSB than SV. Although, 105 species were common to SSB and SV, the mean Czekanowski similarity between SV and SSB was very low (15.5%). However, we argue that the recovery of vegetation in degraded sites can still rely on SSB. We concluded that the seed movement among plant communities through hydrochory led to a spatial homogenization of SSB, resulting in a decrease in SSB-SV similarity and an increase in SSB species diversity and compositional evenness. Differences in plant diversity and richness between the SSB and the SV are supposed to be a complementation of diversity between below- and above-ground and therefore, greater community resilience is predicted under stochastic disturbance events such as flooding in the riparian area.
Similar content being viewed by others
References
Alvarado, J., Marquez, M., & Leon, L. E. (1988). Determination of organic nitrogen by the kjeldahl method using microwave acid digestion. Analytical Letters, 21, 357–365.
Asadian, G. H., Akbarzadeh, M. R., & Sadeghimanesh, M. (2019). The effects of the exclosure on the improvement of the range lands in Hamedan province. Iranian Journal of Range and Desert Research, 16, 343–352.
Asaeda, T., Rashid, M., & Sanjaya, H. (2015). Flushing sediment from reservoirs triggers forestation in the downstream reaches. Ecohydrology, 8(3), 426–437.
Burrows, C. J. (1990). Processes of vegetation change. Unwin Hyman Ltd.
Cambardella, C. A., & Elliott, E. T. (1992). Particulate soil organic matter changes across a grassland cultivation sequence. Soil Science Society of America Journal, 56, 777–783.
Cambardella, C. A., Gajda, A. M., Doran, J. W., Wienhold, B. J., & Kettler, T. A. (2001). Estimation of particulate and total organic matter by weight loss-on-ignition. In R. Lal, J. M. Kimble, R. F. Follett, & B. A. Stewart (Eds.), Assessment methods for soil carbon (pp. 349–359). Advances in Soil Science, CRC Press.
Capon, S. J., & Brock, M. A. (2006). Flooding, soil seed bank dynamics and vegetation resilience of a hydrologically variable desert floodplain. Freshwater Biology, 51(2), 206–223.
Casler, M. D., & Undersander, D. J. (2018). Identification of temperate pasture grasses and legumes. Horse Pasture Management, 2, 11–35.
Cho, H. J., **, S. N., Lee, H., Marrs, R. H., & Cho, K. H. (2018). The relationship between the soil seed bank and above-ground vegetation in a sandy floodplain South Korea. Ecology and Resilient Infrastructure, 5(3), 145–155.
Dalton, R. L., Carpenter, D. J., Boutin, C., & Allison, J. E. (2017). Factors affecting soil seed banks of riparian communities in an agricultural ecosystem: Potential for conservation of native plant diversity. Applied Vegetation Science, 20, 446–458.
de Jager, M., Kaphingst, B., Janse, E. L., Buisman, R., Rinzema, S. G. T., & Soons, M. B. (2018). Seed size regulates plant dispersal distances in flowing water. Journal of Ecology, 107, 307–317.
De Leon, I. A., Mariano, N. A., Sorani, V., Flores-Franco, G., Rendon Alquicira, E., & Wehncke, E. V. (2019). Physical environmental conditions determine ubiquitous spatial differentiation of standing plants and seedbanks in neotropical riparian dry forests. PLoS ONE, 14(3), e0212185.
de Souza, E. B., Bao, F., Damasceno Junior, G. A., & Pott, A. (2021). Differences between species in seed bank and vegetation helps to hold functional diversity in a floodable neotropical savanna. Journal of Plant Ecology, 14, 605–615.
Erfanzadeh, R., Abbasi Kesbi, M., Fattahi, B., & Sher, A. A. (2023). Is the soil seed bank a reliable source for passive restoration of intensive grazed habitats in river riparian areas of western Iran? Ecological Engineering, 192, 106965.
Erfanzadeh, R., Shayesteh Palaye, A. A., & Ghelichnia, H. (2020). Shrub effects on germinable soil seed bank in overgrazed grasslands. Plant Ecology and Diversity, 13, 199–208.
Garssen, A., Baattrup-Pedersen, A., Voesenek, L., Verhoeven, J., & Soons, M. (2015). Riparian plant community responses to increased flooding: A meta-analysis. Global Change Biology, 21, 2881–2890.
Georgiou, S., & Turner, R. K. (2012). Valuing ecosystem services: The case of multi-functional Wetlands’. Oxfordshire: Routledge.
Ghorbani, J., Nazari, N., Zali, S. H., & Tamartash, R. (2011). Species composition and seed density of soil seed bank in mountain grassland of north Alborz. Journal of Plant Research, 27, 310–319.
González, E., Sher, A. A., Anderson, R. M., Bay, R. F., Bean, D. W., Bissonnete, G. J., Bourgeois, B., Cooper, D. J., Dohrenwend, K., Eichhorst, K. D., & El Waer, H. (2017). Vegetation response to invasive Tamarix control in southwestern US rivers: a collaborative study including 416 sites. Ecological Applications, 27(6), 1789–1804.
Goodson, J. M., Gurnell, P. A. M., Angold, G., & Morrissey, I. P. (2003). Evidence for hydrochory and the deposition of viable seeds within winter flow-deposited sediments: The river dove, Derbyshire, UK. River Research and Applications, 19, 317–334.
Gothe, E., Wiberg-Larsen, P., Kristensen, E. A., Baattrup-Pedersen, A., Sandin, L., & Friberg, N. (2015). Impacts of habitat degradation and stream spatial location on biodiversity in a disturbed riverine landscape. Biodiversity Conservation, 24, 1423–1441.
Gray, A. J., & Bunce, R. G. H. (1972). The ecology of Morecambe Bay. VI. Soils and vegetation of the salt marshes: A multivariate approach. Journal of Applied Ecology, 9, 221–234.
Hampe, A. (2004). Extensive hydrochory uncouples spatiotemporal patterns of seed fall and seedling recruitment in a ‘bird-dispersed’ riparian tree. Journal of Ecology, 92, 797–807.
Hanlon, T. J., Williams, C. E., & Moriarity, W. J. (1998). Species composition of soil seed banks of Allegheny Plateau riparian forests. Journal of the Torrey Botanical Society, 125, 199–215.
Jabbari, I., Ghobadian, R., & Jadid, A. (2023). The effect of April 2019 flash flood on the morphology of the meandering confluence of the Dinver river to Gamasiab using SRH-2D numeric model. Geography and Development, 21(70), 1–26.
Kent, M., & Coker, P. (1994). Vegetation description and analysis. A practical approach. Chichester: Wiley.
Latombe, G., Hui, C., & McGeoch, M. A. (2015). Beyond the continuum: A multi-dimensional phase space for neutral–niche community assembly. Proceedings of the Royal Society B: Biological Sciences, 282, 20152417.
Latombe, G., Richardson, D. M., McGeoch, M. A., Altwegg, R., Catford, J. A., Chase, J. M., Courchamp, F., Esler, K. J., Jeschke, J. M., Landi, P., Measey, J., Midgley, G. F., Minoarivelo, H. O., Rodger, J. G., & Hui, C. (2021). Mechanistic reconciliation of community and invasion ecology. Ecosphere, 12(2), e03359. https://doi.org/10.1002/ecs2.3359
Lee, H., Alday, J. G., Cho, K. H., Lee, E. J., & Marrs, R. H. (2014). Effects of flooding on the seed bank and soil properties in a conservation area on the Han River, South Korea. Ecological Engineering, 70, 102–113.
Leps, J., & Smilauer, P. (2003). Multivariate analysis of ecological data using CANOCO. Cambridge University Press.
Mmusi, M., Tsheboeng, G., Teketay, T., Murray-Hudson, M., Kashe, K., & Madome, J. (2021). Species richness, diversity, density and spatial distribution of soil seed banks in the riparian woodland along the Thamalakane River of the Okavango Delta, northern Botswana. Trees, Forests and People, 6, 100160.
Moody, K., Munroe, C.E., Lubigan, R.T., Paller, Jr. EC. (1984). Major weeds of the Philippines. Weed science society of the Philippines. College Laguna (Philippines): University of the Philippines at Los Baños 328 p.
Nilsson, C., Brown, R. L., & Jansson, R. (2010). The role of hydrochory in structuring riparian and wetland vegetation. Biological Review of the Cambridge Philosophical Society, 85, 837–858.
Odum, E. P. (1971). Fundamentals of ecology (3rd ed.). Saunders.
Osca, J. M., Galán, F., & Moreno-Ramón, H. (2021). Rice paddy soil seedbanks composition in a Mediterranean wetland and the influence of winter flooding. Agronomy, 11, 1199.
Peterson, E. E., Sheldon, F., Darnell, R., Bunn, S. E., & Harch, B. D. (2011). A comparison of spatially explicit landscape representation methods and their relationship to stream condition. Freshwater Biology, 56(3), 590–610.
Pétillon, J., Erfanzadeh, R., Garbutt, A., Maelfait, J. P., & Hoffmann, M. (2010). Inundation frequency determines the post-pioneer successional pathway in a newly created salt marsh. Wetlands, 30, 1097–1105.
Prihar, S. S., & Hundal, S. S. (1971). Determination of bulk density of soil clod by saturation. Geoderma, 5, 283–286.
Rasran, L., Vogt, K., & Jensen, K. (2021). Hydrochorous seed transport in a small river in Northern Germany as trait-dependent filter of plant dispersal and recruitment. Hydrobiology, 106, 277–286.
Rechinger, K. H. (1964). Flora Iranica: Akademische Druck-und Verlagsanstalt Graz (p. 549). University of Tehran.
Rezaei Moghaddam, M. H., Jabbari, I., & Pirozynezhad, N. (2016). A Study of Meandering, Braided and Ana Branching channel plan forms, using sinuosity and braided indexes in Gamasiab River. Journal of Watershed Management Research, 7, 272–283.
Sahrawat, K. L. (1982). Simple modification of the Walkley-Black method for simultaneous determination of organic carbon and potentially mineralizable nitrogen in tropical rice soils. Plant and Soil, 69, 73–77.
Silvestri, S., & Marani, M. (2004). Salt-marsh vegetation and morphology: Basic physiology, modelling and remote sensing observations. The Ecogeomorphology of Tidal Marshes, Coastal Estuarine Studies, 59, 5–25.
Smart, S. M., Thompson, K., Marrs, R. H., Le Duc, M. G., Maskell, L. C., & Firbank, L. G. (2006). Biodiversity loss and biotic homogenization across human-modified ecosystems. Proceeding of the Royal Society B, 273, 2659–2665.
Soleimaninejad, Z., Ghavam, M., Tavili, A., & Toluei, Z. (2021). Investigating the soil seed bank and its relation with the aboveground vegetation along an elevation gradient in Kashan Iran. Journal of Rangeland Sciences, 11(3), 336–356.
Thompson, K. (2000). Seeds: The ecology of regeneration in plant communities (2nd ed.). Wallingford: CABI Publishing.
Thompson, K., Bakker, J. P., & Bekker, R. M. (1997). The soil seed banks of North West Europe: Methodology, density and longevity. Cambridge University Press.
Tilman, D. (2004). Niche tradeoffs, neutrality, and community structure: A stochastic theory of resource competition, invasion, and community assembly. Proceedings of the National Academy of Sciences of the United States of America, 101, 10854–10861.
Ullah, H., Mulk Khan, S., Jaremko, M., Jahangir, S., Ullah, Z., Ali, L., Ahmad, Z., & Badshah, H. (2022). Vegetation assessments under the influence of environmental variables from the Yakhtangay hill of the Hindu-Himalayan range North Western Pakistan. Scientific Reports, 12, 20973.
Vince, S. W., & Snow, A. A. (1984). Plant zonation in an Alaskan salt marsh. I. Distribution, abundance and environmental factors. Journal of Ecology, 72, 651–667.
Vogt, K., Rasran, L., & Jensen, K. (2004). Water-borne seed transport and seed deposition during flooding in a small river-valley in Northern Germany. Flora, 199, 377–388.
Willems, J. H., & Bik, L. P. M. (1998). Restoration of high species density in calcareous grassland: The role of seed rain and soil seed bank. Applied Vegetation Sciences, 1, 91–100.
Wisheu, I. C., & Keddy, P. A. (1992). Competition and centrifugal organization of plant communities: Theory and tests. Journal of Vegetation Science, 3, 147–156.
Zarezadeh Mehrizi, Sh., Bazrafshan, J., & Bazrafshan, O. (2019). Flow regime changes of Gamasiab river under climate change scenarios. Journal of Environmental Studies, 44, 587–602.
Zou, C., Martini, F., **a, S. W., Castillo-Diaz, D., & Goodale, U. M. (2021). Elevation and micro environmental conditions directly and indirectly influence forests’ soil seed bank communities. Global Ecology and Conservation, 26, e01443.
Author information
Authors and Affiliations
Corresponding author
Appendix 1
Appendix 1
Average percentage cover of species in the standing vegetation and soil seed bank density per m2 together with family names, life spans and life forms information. P: perennial, A: annual, B: biennial, T: tree, F: forb, G: grass, S: shrub
Species names | Family | Life span | Life form | Soil seed bank | Standing vegetation |
---|---|---|---|---|---|
Acer negundo | Sapindaceae | P | T | 2.83 | 0.02 |
Achillea aleppica | Asteraceae | P | F | 0.00 | 0.04 |
Adiantum capillus | Adiantaceae | P | F | 1.70 | 0.09 |
Aegilops tauschii | Gramineae | A | G | 14.72 | 0.20 |
Aegilops trioncialis | Gramineae | A | G | 8.49 | 0.51 |
Agropyron trichophorum | Gramineae | P | G | 9.63 | 2.88 |
Alhagi camelorum | Fabaceae | P | S | 0.00 | 1.34 |
Allium ampeloprasum | Amaryllidaceae | A | F | 11.32 | 0.04 |
Alopecurus mucronatus | Gramineae | P | S | 2.26 | 0.07 |
Alopecurus myosuroides | Gramineae | A | S | 52.66 | 1.28 |
Alysum desertorum | Crucifereae | A | F | 2.83 | 0.13 |
Amaranthus blitoides | Amaranthaceae | A | F | 9.06 | 0.05 |
Amaranthus viridis | Amaranthaceae | A | F | 24.91 | 0.00 |
Anchusa italica | Boraginaceae | A | F | 2.26 | 0.07 |
Anthemis repens | Asteraceae | P | F | 0.00 | 0.01 |
Asperula arvensis | Rubiaceae | A | F | 1.70 | 0.00 |
Astragalus trachyacanthus | Fabaceae | P | S | 0.00 | 0.13 |
Astragalus gossypinus | Fabaceae | P | S | 2.26 | 1.50 |
Avena fatua | Gramineae | A | G | 5.66 | 0.58 |
Boissiera squarrosa | Gramineae | A | G | 23.78 | 0.22 |
Bothriochloa ischaemum | Gramineae | P | G | 0.00 | 0.08 |
Brachypodium sylvaticum | Gramineae | P | G | 5.66 | 0.00 |
Brassica napus | Cruciferae | A | F | 10.19 | 0.01 |
Bromus danthonia | Gramineae | A | G | 27.74 | 0.65 |
Bromus sterilis | Gramineae | B | F | 14.16 | 0.02 |
Bromus tectorum | Gramineae | A | G | 54.36 | 2.79 |
Bromus tomentosus | Gramineae | P | G | 27.18 | 1.04 |
Bunium persicum | Umbellifereae | P | F | 6.23 | 0.31 |
Capsella bursa-pastoris | Cruciferae | A | F | 2.83 | 0.04 |
Cardaria draba | Cruciferae- | P | F | 0.00 | 0.05 |
Carthamus oxyacantha | Asteraceae | P | F | 7.93 | 0.06 |
Catabrosa aquatica | Gramineae | P | F | 1.70 | 0.00 |
Centaurea behen | Asteraceae | A | F | 0.00 | 0.04 |
Centaurea persica | Asteraceae | P | F | 4.53 | 1.57 |
Centaurea solstitialis | Asteraceae | A | F | 0.57 | 0.02 |
Cerastium dichotomum | Caryophylaceae | P | F | 0.00 | 0.02 |
Chaerophyllum macropodum | Apiaceae | P | F | 9.06 | 0.47 |
Chenopodium album | Chenopodiaceae | A | F | 7.36 | 0.05 |
Chenopodium murale | Chenopodiaceae | A | F | 6.79 | 0.09 |
Cichorium intybus | Asteraceae | A | F | 22.08 | 1.61 |
Cirsium arvense | Asteraceae | P | F | 7.93 | 0.61 |
Convolus arvensis | Convolvulaceae | P | F | 2.26 | 0.46 |
Coronilla varia | Fabaceae | P | F | 0.00 | 0.01 |
Cousinia cylindracea | Asteraceae | A | F | 0.57 | 0.15 |
Crataegus pointica | Rosaceae | P | S | 0.57 | 0.02 |
Crataegus pseudoheterophylla | Rosaceae | P | S | 1.70 | 0.15 |
Crozophora tinctoria | Euphorbiaceae | A | F | 1.70 | 0.01 |
Cynodon dactylon | Gramineae | P | G | 53.79 | 8.42 |
Cyperus difformis | Cyperaceae | A | F | 167.36 | 2.06 |
Cyperus fuscus | Cyperaceae | A | F | 58.89 | 0.01 |
Dactylis glomerata | Gramineae | P | G | 65.12 | 3.73 |
Daphne macrantha | Thymelaeaceae | P | S | 1.70 | 0.01 |
Datura stramonium | Solanaceae | A | F | 1.70 | 0.00 |
Digitaria ciliaris | Gramineae | A | G | 8.49 | 0.02 |
Diplotaxis muralis | Cruciferae | P or A | F | 3.40 | 0.00 |
Ducrosia anethifolia | Apiaceae | P | F | 0.00 | 0.12 |
Echinops ecbatanus | Asteraceae | P | F | 2.26 | 0.84 |
Echinops orientalis | Asteraceae | P | F | 1.70 | 0.33 |
Equisetum ramosissimum | Equisetaceae | A | F | 0.57 | 0.30 |
Equisetum arvense | Equisetaceae | P | F | 13.59 | 0.16 |
Eryngium billardieri | Apiaceae | P | F | 0.57 | 0.04 |
Eryngium canadensis | Apiaceae | P | F | 2.83 | 0.00 |
Eryngium thyrsoideum | Apiaceae | P | F | 0.57 | 0.01 |
Eryngium variifolium | Apiaceae | A | F | 0.00 | 0.09 |
Euphorbia aucheri | Euphorbiaceae | A | F | 1.13 | 0.01 |
Euphorbia boissieriana | Euphorbiaceae | P | F | 2.83 | 0.11 |
Euphorbia cheiradenia | Euphorbiaceae | P | F | 7.93 | 0.17 |
Falcaria vulgaris | Apiaceae | B | F | 0.57 | 0.69 |
Ferula microcolea | Apiaceae | P | F | 0.57 | 0.44 |
Festuca arundinaceae | Gramineae | P | G | 8.49 | 0.88 |
Festuca ovina | Gramineae | P | G | 10.76 | 0.73 |
Galium aparine | Rubiaceae | P | F | 37.94 | 1.09 |
Galium verum | Rubiaceae | P | F | 1.70 | 2.28 |
Glycyrrhiza glabra | Fabaceae | P | F | 0.00 | 0.26 |
Gundelia tornifortii | Asteraceae | P | F | 0.00 | 0.47 |
Gypsophila elegans | Caryophylaceae | P | S | 0.00 | 0.67 |
Helianthemum salicifolium | Cistaceae | B | F | 9.06 | 0.47 |
Henrardia persica | Gramineae | A | G | 1.13 | 0.33 |
Heptaptera anisoptera | Apiaceae | P | F | 0.57 | 0.18 |
Hordeum bulbosum | Gramineae | P | G | 18.69 | 2.11 |
Hordeum marinum | Gramineae | A | G | 0.57 | 1.52 |
Hypericum perforatum | Hypericaceae | P | F | 0.57 | 0.01 |
Inula britannica | Asteraceae | B | F | 7.36 | 0.00 |
Isatis cappadocica | Cruciferae | A | F | 10.76 | 0.17 |
Ixiolirion tataricum | Amaryllidaceae | P | F | 21.52 | 0.00 |
Juncus inflexus | Juncaceae | P | G | 54.92 | 1.73 |
Lactuca hirsuta | Asteraceae | B | F | 33.97 | 0.00 |
Lactuca orientalis | Asteraceae | P | F | 1.13 | 0.21 |
Lactuca serriola | Asteraceae | B | F | 6.79 | 0.28 |
Lamium amplexicaule | Labiatae | P | F | 2.83 | 0.00 |
Leontodon taraxacoides | Asteraceae | P | F | 3.96 | 0.00 |
Lepidium draba | Cruciferae | P | F | 0.57 | 0.00 |
Leucopoa sclerophylla | Gramineae | P | G | 6.23 | 0.00 |
Libanotis transcaucasica | Umbelliferae | P | F | 3.96 | 0.00 |
Lolium rigidum | Gramineae | A | G | 33.97 | 1.61 |
Lotus gebelia | Fabaceae | P | F | 44.17 | 1.14 |
Malva sylvestris | Malvaceae | A | F | 0.00 | 0.06 |
Marrubium astracanicum | Labiatae | P | F | 0.00 | 0.08 |
Medicago orbicularis | Fabaceae | P | F | 13.02 | 0.03 |
Medicago sativa | Fabaceae | P | F | 10.19 | 0.12 |
Melilotus officinalis | Fabaceae | P | F | 3.40 | 0.19 |
Mentha aquatica | Labiatae | P | F | 66.25 | 0.02 |
Mentha longifolia | Labiatae | P | F | 29.44 | 0.06 |
Mentha pulegium | Labiatae | P | F | 17.55 | 0.19 |
Morus alba | Moraceae | P | T | 1.70 | 0.00 |
Nasturtium officinale | Cruciferae | P | F | 13.59 | 0.00 |
Noaea mucronata | Chenopodiaceae | P | S | 2.26 | 0.08 |
Ocimum basilicum | Labiatae | A | F | 1.70 | 0.59 |
Phalaris paradoxa | Gramineae | A | G | 11.32 | 0.16 |
Phleum exaratum | Gramineae | A | G | 12.46 | 0.34 |
Phlomis Kurdica | Labiatae | P | S | 3.96 | 0.18 |
Phlomis olivieri | Labiatae | P | F | 0.00 | 0.34 |
Phragmetis australis | Gramineae | P | G | 20.38 | 1.56 |
Plantago lanceolata | Plantaginaceae | P | S | 7.36 | 0.00 |
Plantago major | Plantaginaceae | P | S | 23.22 | 0.12 |
Poa bulbosa | Gramineae | P | G | 7.44 | 3.99 |
Poa pratensis | Gramineae | P | G | 8.49 | 0.94 |
Poa trivialis | Gramineae | P | G | 2.83 | 0.37 |
Polygonum alpestre | Polygonaceae | P | F | 1.70 | 0.00 |
Polygonum patulum | Polygonaceae | A | F | 0.00 | 0.06 |
Polygonum thymifolium | Polygonaceae | A | F | 1.70 | 0.02 |
Populus nigra | Salicaceae | P | T | 2.26 | 0.00 |
Portulaca oleracea | Caryophylaceae | A | F | 10.19 | 0.00 |
Potentilla reptans | Rosaceae | P | F | 14.16 | 1.26 |
Prunus armeniaca | Rosaceae | P | T | 3.96 | 0.00 |
Prunus avium | Rosaceae | P | T | 1.70 | 0.00 |
Prunus divaricacta | Rosaceae | P | T | 0.57 | 0.08 |
Quercus brantii | Fagaceae | P | T | 0.57 | 0.51 |
Rheum ribes | Polygonaceae | P | F | 0.00 | 0.02 |
Rubus sanctus | Rosaceae | P | S | 1.70 | 0.84 |
Salix alba | Salicaceae | P | T | 0.00 | 0.06 |
Salvia acetabolosa | Labiatae | P | S | 1.13 | 0.11 |
Salvia syriaca | Labiatae | A | F | 0.00 | 0.20 |
Sanguisorba minor | Rosaceae | A | F | 16.99 | 0.79 |
Scabiosa rotate | Dipsacoideae | A | F | 0.00 | 0.02 |
Scariola orientalis | Asteraceae | P | F | 3.96 | 0.01 |
Scorzonera pseudolanata | Asteraceae | A | F | 9.63 | 0.01 |
Scrophularia variegata | Scrophulariaceae | P | F | 0.00 | 0.01 |
Senecio vernalis | Asteraceae | A | F | 0.00 | 0.03 |
Silene swertifolia | Caryophylaceae | A | F | 1.70 | 0.01 |
Solanum nigrum | Solanaceae | A | F | 1.70 | 0.00 |
Sonchus oleraceus | Asteraceae | A | F | 1.70 | 0.00 |
Stachys inflata | Labiatae | P | F | 0.00 | 0.07 |
Stipa barbata | Gramineae | P | G | 0.00 | 0.43 |
Symphytum tuberosum | Boraginaceae | P | F | 1.13 | 0.00 |
Taeniatherum crinitum | Gramineae | A | G | 13.02 | 2.26 |
Tamarix sp. | Tamaricaceae | P | S | 5.66 | 0.00 |
Taraxicum officinale | Asteraceae | P | F | 2.83 | 0.18 |
Tragopogon longirostris | Asteraceae | P | F | 0.57 | 0.06 |
Trifolium campestre | Fabaceae | A | F | 5.66 | 0.00 |
Trifolium repens | Fabaceae | P | F | 8.49 | 0.32 |
Tulipa montana | Liliaceae | A | F | 9.63 | 0.00 |
Typha persica | Gramineae | P | G | 1.13 | 0.12 |
Ulmus minor | Ulmaceae | P | T | 2.26 | 0.10 |
Valiantia hispida | Rubiaceae | A | F | 15.29 | 0.01 |
Verbena officinalis | Verbenaceaea | P | F | 1.13 | 0.00 |
Veronica persica | Scrophulariaceae | A | F | 8.49 | 0.00 |
Vicia variabilis | Fabaceae | A | F | 13.02 | 0.05 |
Viola canina | Violaceae | A | F | 4.53 | 0.04 |
Vitis sp. | Vitaceae | P | S | 1.13 | 0.10 |
Xanthium strumarium | Asteraceae | A | F | 1.13 | 0.00 |
Zizphora tenuior | Labiatae | A | F | 0.57 | 0.01 |
Zoegea leptaurea | Asteraceae | P | F | 3.96 | 0.81 |
Rights and permissions
Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law.
About this article
Cite this article
Kesbi, M.A., Erfanzadeh, R. & Fattahi, B. Similarity between soil seed bank and standing vegetation and their relationship with soil and topographical characteristics in a riparian zone. COMMUNITY ECOLOGY 25, 89–101 (2024). https://doi.org/10.1007/s42974-023-00180-4
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s42974-023-00180-4