Intermittent, temporary or seasonal rivers or streams cease to flow every year or at least twice every five years.[1] Such rivers drain large arid and semi-arid areas, covering approximately a third of the Earth's surface.[2] The extent of temporary rivers is increasing, as many formerly perennial rivers are becoming temporary because of increasing water demand, particularly for irrigation.[3] Despite inconsistent water flow, intermittent rivers are considered land-forming agents in arid regions, as they are agents of significant deposition and erosion during flood events.[4] The combination of dry crusted soils and the highly erosive energy of the rain cause sediment resuspension and transport to the coastal areas.[5] They are among the aquatic habitats most altered by human activities.[6] During the summer even under no flow conditions the point sources are still active such as the wastewater effluents,[7][8] resulting in nutrients and organic pollutants accumulating in the sediment. Sediment operates as a pollution inventory and pollutants are moved to the next basin with the first flush.[9] Their vulnerability is intensified by the conflict between water use demand and aquatic ecosystem conservation.[10] Advanced modelling tools have been developed to better describe intermittent flow dynamic changes such as the tempQsim model.[5]
^Tzoraki, Ourania; Nikolaidis, Nikolaos P. (November 2007). "A generalized framework for modeling the hydrologic and biogeochemical response of a Mediterranean temporary river basin". Journal of Hydrology. 346 (3–4): 112–121. Bibcode:2007JHyd..346..112T. doi:10.1016/j.jhydrol.2007.08.025.
^Thornes, J.B. (1977). "Channel Changes in Ephemeral Streams: Observations, Problems, and Models". In Gregory, Kenneth John (ed.). River Channel Changes. Wiley. pp. 317–335. ISBN978-0-471-99524-1. OCLC646996248.
^de Girolamo, A. M.; Calabrese, A.; Pappagallo, G.; Santese, G.; lo Porto, A. (2012). "Impact of anthropogenic activities on a Temporary River". Fresenius Environmental Bulletin. 21 (11): 3278–3286.
^ abTzoraki, Ourania; Nikolaidis, Nikolaos P.; Trancoso, Anna Rosa; Braunschweig, Frank; Neves, Ramiro (15 January 2009). "A reach-scale biogeochemical model for temporary rivers". Hydrological Processes. 23 (2): 272–283. Bibcode:2009HyPr...23..272T. doi:10.1002/hyp.7138.
^Moyle, P. B. (December 2014). "Novel Aquatic Ecosystems: The New Reality for Streams in California and Other Mediterranean Climate Regions". River Research and Applications. 30 (10): 1335–1344. Bibcode:2014RivRA..30.1335M. doi:10.1002/rra.2709.
^Perrin, Jean-Louis; Tournoud, Marie-George (December 2009). "Hydrological processes controlling flow generation in a small Mediterranean catchment under karstic influence". Hydrological Sciences Journal. 54 (6): 1125–1140. Bibcode:2009HydSJ..54.1125P. doi:10.1623/hysj.54.6.1125.
^Chahinian, N.; Bancon-Montigny, C.; Brunel, V.; Aubert, G.; Salles, C.; Marchand, P.; Rodier, C.; Seidel, J.L.; Gayrard, E.; Hernandez, F.; Perrin, J.L.; Tournoud, M.G. (October 2013). "Temporal and spatial variability of organotins in an intermittent Mediterranean river". Journal of Environmental Management. 128: 173–181. Bibcode:2013JEnvM.128..173C. doi:10.1016/j.jenvman.2013.05.004. PMID23747368.
^Bernal, Susana; von Schiller, Daniel; Sabater, Francesc; Martí, Eugènia (November 2013). "Hydrological extremes modulate nutrient dynamics in mediterranean climate streams across different spatial scales". Hydrobiologia. 719 (1): 31–42. Bibcode:2013HyBio.719...31B. doi:10.1007/s10750-012-1246-2.
^Webb, J. Angus; Nichols, Susan J.; Norris, Richard H.; Stewardson, Michael J.; Wealands, Stephen R.; Lea, Patrick (April 2012). "Ecological Responses to Flow Alteration: Assessing Causal Relationships with Eco Evidence". Wetlands. 32 (2): 203–213. Bibcode:2012Wetl...32..203W. doi:10.1007/s13157-011-0249-5.