33 results on '"Perkol-Finkel S"'
Search Results
2. Floating and fixed artificial habitats : effects of substratum motion on benthic communities in a coral reef environment
- Author
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Perkol-Finkel, S., Zilman, G., Sella, I., Miloh, T., and Benayahu, Y.
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- 2006
3. Spatially Variable Effects of Artificially-Created Physical Complexity on Subtidal Benthos
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O’Shaughnessy, KA, Perkol-Finkel, S, Strain, EMA, Bishop, MJ, Hawkins, SJ, Hanley, ME, Lunt, P, Thompson, RC, Hadary, T, Shirazi, R, Yunnie, ALE, Amstutz, A, Milliet, L, Yong, CLX, Firth, LB, O’Shaughnessy, KA, Perkol-Finkel, S, Strain, EMA, Bishop, MJ, Hawkins, SJ, Hanley, ME, Lunt, P, Thompson, RC, Hadary, T, Shirazi, R, Yunnie, ALE, Amstutz, A, Milliet, L, Yong, CLX, and Firth, LB
- Abstract
In response to the environmental damage caused by urbanization, Nature-based Solutions (NbS) are being implemented to enhance biodiversity and ecosystem processes with mutual benefits for society and nature. Although the field of NbS is flourishing, experiments in different geographic locations and environmental contexts have produced variable results, with knowledge particularly lacking for the subtidal zone. This study tested the effects of physical complexity on colonizing communities in subtidal habitats in two urban locations: (1) Plymouth, United Kingdom (northeast Atlantic) and (2) Tel Aviv, Israel (eastern Mediterranean) for 15- and 12-months, respectively. At each location, physical complexity was manipulated using experimental tiles that were either flat or had 2.5 or 5.0 cm ridges. In Plymouth, biological complexity was also manipulated through seeding tiles with habitat-forming mussels. The effects of the manipulations on taxon and functional richness, and community composition were assessed at both locations, and in Plymouth the survival and size of seeded mussels and abundance and size of recruited mussels were also assessed. Effects of physical complexity differed between locations. Physical complexity did not influence richness or community composition in Plymouth, while in Tel Aviv, there were effects of complexity on community composition. In Plymouth, effects of biological complexity were found with mussel seeding reducing taxon richness, supporting larger recruited mussels, and influencing community composition. Our results suggest that outcomes of NbS experiments are context-dependent and highlight the risk of extrapolating the findings outside of the context in which they were tested.
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- 2021
4. A global analysis of complexity-biodiversity relationships on marine artificial structures
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Webb, T, Strain, EMA, Steinberg, PD, Vozzo, M, Johnston, EL, Abbiati, M, Aguilera, MA, Airoldi, L, Aguirre, JD, Ashton, G, Bernardi, M, Brooks, P, Chan, BKK, Cheah, CB, Chee, SY, Coutinho, R, Crowe, T, Davey, A, Firth, LB, Fraser, C, Hanley, ME, Hawkins, SJ, Knick, KE, Lau, ETC, Leung, KMY, McKenzie, C, Macleod, C, Mafanya, S, Mancuso, FP, Messano, LVR, Naval-Xavier, LPD, Ng, TPT, O'Shaughnessy, KA, Pattrick, P, Perkins, MJ, Perkol-Finkel, S, Porri, F, Ross, DJ, Ruiz, G, Sella, I, Seitz, R, Shirazi, R, Thiel, M, Thompson, RC, Yee, JC, Zabin, C, Bishop, MJ, Webb, T, Strain, EMA, Steinberg, PD, Vozzo, M, Johnston, EL, Abbiati, M, Aguilera, MA, Airoldi, L, Aguirre, JD, Ashton, G, Bernardi, M, Brooks, P, Chan, BKK, Cheah, CB, Chee, SY, Coutinho, R, Crowe, T, Davey, A, Firth, LB, Fraser, C, Hanley, ME, Hawkins, SJ, Knick, KE, Lau, ETC, Leung, KMY, McKenzie, C, Macleod, C, Mafanya, S, Mancuso, FP, Messano, LVR, Naval-Xavier, LPD, Ng, TPT, O'Shaughnessy, KA, Pattrick, P, Perkins, MJ, Perkol-Finkel, S, Porri, F, Ross, DJ, Ruiz, G, Sella, I, Seitz, R, Shirazi, R, Thiel, M, Thompson, RC, Yee, JC, Zabin, C, and Bishop, MJ
- Abstract
Aim Topographic complexity is widely accepted as a key driver of biodiversity, but at the patch‐scale, complexity–biodiversity relationships may vary spatially and temporally according to the environmental stressors complexity mitigates, and the species richness and identity of potential colonists. Using a manipulative experiment, we assessed spatial variation in patch‐scale effects of complexity on intertidal biodiversity. Location 27 sites within 14 estuaries/bays distributed globally. Time period 2015–2017. Major taxa studied Functional groups of algae, sessile and mobile invertebrates. Methods Concrete tiles of differing complexity (flat; 2.5‐cm or 5‐cm complex) were affixed at low–high intertidal elevation on coastal defence structures, and the richness and abundance of the colonizing taxa were quantified after 12 months. Results The patch‐scale effects of complexity varied spatially and among functional groups. Complexity had neutral to positive effects on total, invertebrate and algal taxa richness, and invertebrate abundances. However, effects on the abundance of algae ranged from positive to negative, depending on location and functional group. The tidal elevation at which tiles were placed accounted for some variation. The total and invertebrate richness were greater at low or mid than at high intertidal elevations. Latitude was also an important source of spatial variation, with the effects of complexity on total richness and mobile mollusc abundance greatest at lower latitudes, whilst the cover of sessile invertebrates and sessile molluscs responded most strongly to complexity at higher latitudes. Conclusions After 12 months, patch‐scale relationships between biodiversity and habitat complexity were not universally positive. Instead, the relationship varied among functional groups and according to local abiotic and biotic conditions. This result challenges the assumption that effects of complexity on biodiversity are universally positive. The va
- Published
- 2021
5. Floating and fixed artificial habitats: Spatial and temporal patterns of benthic communities in a coral reef environment
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Perkol-Finkel, S., Zilman, G., Sella, I., Miloh, T., and Benayahu, Y.
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- 2008
- Full Text
- View/download PDF
6. Can artificial reefs mimic natural reef communities? The roles of structural features and age
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Perkol-Finkel, S., Shashar, N., and Benayahu, Y.
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- 2006
- Full Text
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7. Recruitment of benthic organisms onto a planned artificial reef: shifts in community structure one decade post-deployment
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Perkol-Finkel, S. and Benayahu, Y.
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- 2005
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8. Design options, implementation issues and evaluating success of ecologically engineered shorelines
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Rl, Morris, Ec, Heery, Lhl, Loke, Lau E, Ema, Strain, Airoldi L, Ka, Alexander, BishopMJ, Ra, Coleman, Jr, Cordell, Dong Y, Lb, Firth, Sj, Hawkins, Heath T, Kokora M, Shing Yip Lee, Jk, Miller, Perkol-Finkel S, Rella A, Pd, Steinberg, Takeuchi I, Rc, Thompson, Todd P, Jd, Toft, and Km, Leung
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- 2019
9. Marine forests at risk: solutions to halt the loss and promote the recovery of Mediterranean canopy-forming seaweeds
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Airoldi, L, Ballesteros, E, Buonuomo, R, van Belzen, J, Bouma, TJ, Cebrian, E, De Clerk, O, Engelen, AH, Ferrario, F, Fraschetti, S, Gianni, F, Guidetti, P, Ivesa, Ljiljana, Mancuso, FP, Micheli, F, Perkol-Finkel, S, Serrao, EA, Strain, EM, Mangialajo, L, Airoldi, L, Ballesteros, E, Buonuomo, R, van Belzen, J, Bouma, Tj, Cebrian, E, De Clerk, O, Engelen, Ah, Ferrario, F, Fraschetti, S, Gianni, F, Guidetti, P, Ivesa, L, Mancuso, Fp, Micheli, F, Perkol-Finkel, S, Serrao, Ea, Strain, Em, Mangialajo, L, and Langar H., Bouafif, C., Ouerghi A.
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multiple threats ,habitat loss ,Mediterranean Sea ,conservation ,Canopy algae ,Canopy algae, habitat loss, Mediterranean Sea, multiple threats, conservation - Abstract
Along Mediterranean coasts, canopy-forming seaweeds used to form diverse, productive and valuable “forest” habitats, but in the past decades conspicuous declines, sometimes to local extinction, have been reported in many regions. Canopies are retracting particularly close to urban areas, and are replaced by turf-forming and ephemeral algae or barrens. The persisting forests are under continued threat, and current protection measures are insufficient. We provide evidence that declines of canopy algae are dramatically extensive, and are driven by multiple local (nutrient enrichment and high sediment loads, fishing, heavy metal pollution) and global stressors (increasing temperature, high wave exposure). We also show that the combined management of local stressors (such as nutrients and sediments) would increase significantly the resilience of canopy algae to future climatic stressors, preventing their further deterioration. Finally, we discuss restoration prospects in areas where these systems have been lost. We conclude identifying the main needs to understand, guide and motivate effective conservation actions in these valuable ecosystems.
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- 2014
10. European Red List of habitats Part 1. Marine habitats
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Gubbay, S, Sanders, N, Haynes, T, Janssen, JAM, Rodwell, JR, Nieto, A, García Criado, M, Beal, S, Borg, J, Kennedy, M, Micu, D, Otero, M, Saunders, G, Calix, M, Airoldi, L, Alexandrov, VV, Alcázar, E, de Andalucia, J, Babbini, L, Bakran-Petricioli, T, Ballesteros, E, Bañares España, E, Bariche, M, Bastos, E, Basso, D, Bat, L, Battelli, C, Bazairi, H, Bianchi, CN, Bitar, G, Bo, M, Brazier, P, Bush, L, Canese, S, Catrense, SP, Cefalì, ME, Cerrano, C, Chemello, R, Chernysheva, EB, Connor, D, Cook, R, Dankers, N, Darr, A, Davis, AR, Dolenc-Orbanić, N, Dubois, S, Espino, F, Flores Moya, A, Ford, J, Foulquie, M, Fowler, S, Fourt, M, Fraschetti, S, Fuller, I, Fürhaupter, K, Galil, B, Gerovasileiou, V, Giangrande, A, Giuseppe, C, Goriup, P, Grall, J, Gravina, MF, Guelmami, A, Güreşen, A, Hadjioannou, L, Haldin, JM, Hall-Spencer, J, Harmelin, JG, Haroun-Tabrae, R, Harries, D, Herkül, K, Hetman, T, Hiscock, K, Hiscock, S, Holt, R, Yssaris, Y, Jackson, E, Jeudy, A, Jimenez, C, Karamita, C, Karlsson, A, Kersting, D, Keskinen, E, Klinge, F, Klissurov, L, Knittweis-Mifsud, L, Kopiy, V, Korolesova, D, Kružić, P, Komakhidze, G, La Porta, B, Leinikki, J, Lehtonen, P, Linares, C, Lipej, L, Mačić, V, Mangialajo, L, Mariani, S, Melih, C, Metalpa, R, Mielke, E, Mihneva, V, Milchakova, N, Milonakis, K, Minguell, C, Mironova, NV, Näslund, J, Numa, C, Nyström, J, Ocaña, O, Otero, NF, Peña Freire, V, Pergent, C, Perkol-Finkel, S, Pibot, A, Pinedo, S, Poursanidis, D, Ramos, A, Revkov, NK, Roininen, J-T, Rosso, A, Ruiz, J, Salomidi, M, Schembri, P, Shiganov, T, Simboura, N, Sini, M, Smith, C, Soldo, A, Somerfield, P, Templado, J, Terentyev, A, Thibaut, T, Topçu, NE, Trigg, C, Turk, R, Tyler-Walters, H, Tunesi, L, Vera, K, Viera , M, Warzocha, J, Wells, S, Westerbom, M, Wikström, S, Wood, C, Yokes B, Zibrowius, H, BASSO, DANIELA MARIA, Gubbay, S, Sanders, N, Haynes, T, Janssen, JAM, Rodwell, JR, Nieto, A, García Criado, M, Beal, S, Borg, J, Kennedy, M, Micu, D, Otero, M, Saunders, G, Calix, M, Airoldi, L, Alexandrov, VV, Alcázar, E, de Andalucia, J, Babbini, L, Bakran-Petricioli, T, Ballesteros, E, Bañares España, E, Bariche, M, Bastos, E, Basso, D, Bat, L, Battelli, C, Bazairi, H, Bianchi, CN, Bitar, G, Bo, M, Brazier, P, Bush, L, Canese, S, Catrense, SP, Cefalì, ME, Cerrano, C, Chemello, R, Chernysheva, EB, Connor, D, Cook, R, Dankers, N, Darr, A, Davis, AR, Dolenc-Orbanić, N, Dubois, S, Espino, F, Flores Moya, A, Ford, J, Foulquie, M, Fowler, S, Fourt, M, Fraschetti, S, Fuller, I, Fürhaupter, K, Galil, B, Gerovasileiou, V, Giangrande, A, Giuseppe, C, Goriup, P, Grall, J, Gravina, MF, Guelmami, A, Güreşen, A, Hadjioannou, L, Haldin, JM, Hall-Spencer, J, Harmelin, JG, Haroun-Tabrae, R, Harries, D, Herkül, K, Hetman, T, Hiscock, K, Hiscock, S, Holt, R, Yssaris, Y, Jackson, E, Jeudy, A, Jimenez, C, Karamita, C, Karlsson, A, Kersting, D, Keskinen, E, Klinge, F, Klissurov, L, Knittweis-Mifsud, L, Kopiy, V, Korolesova, D, Kružić, P, Komakhidze, G, La Porta, B, Leinikki, J, Lehtonen, P, Linares, C, Lipej, L, Mačić, V, Mangialajo, L, Mariani, S, Melih, C, Metalpa, R, Mielke, E, Mihneva, V, Milchakova, N, Milonakis, K, Minguell, C, Mironova, NV, Näslund, J, Numa, C, Nyström, J, Ocaña, O, Otero, NF, Peña Freire, V, Pergent, C, Perkol-Finkel, S, Pibot, A, Pinedo, S, Poursanidis, D, Ramos, A, Revkov, NK, Roininen, J-T, Rosso, A, Ruiz, J, Salomidi, M, Schembri, P, Shiganov, T, Simboura, N, Sini, M, Smith, C, Soldo, A, Somerfield, P, Templado, J, Terentyev, A, Thibaut, T, Topçu, NE, Trigg, C, Turk, R, Tyler-Walters, H, Tunesi, L, Vera, K, Viera , M, Warzocha, J, Wells, S, Westerbom, M, Wikström, S, Wood, C, Yokes B, Zibrowius, H, and BASSO, DANIELA MARIA
- Abstract
The European Red List of Habitats provides an overview of the risk of collapse (degree of endangerment) of marine, terrestrial and freshwater habitats in the European Union (EU28) and adjacent regions (EU28+), based on a consistent set of categories and criteria, and detailed data and expert knowledge from involved countries. A total of 257 benthic marine habitat types were assessed. In total, 19% (EU28) and 18% (EU28+) of the evaluated habitats were assessed as threatened in categories Critically Endangered, Endangered and Vulnerable. An additional 12% were Near Threatened in the EU28 and 11% in the EU28+. These figures are approximately doubled if Data Deficient habitats are excluded. The percentage of threatened habitat types differs across the regional seas. The highest proportion of threatened habitats in the EU28 was found in the Mediterranean Sea (32%), followed by the North-East Atlantic (23%), the Black Sea (13%) and then the Baltic Sea (8%). There was a similar pattern in the EU28+. The most frequently cited pressures and threats were similar across the four regional seas: pollution (eutrophication), biological resource use other than agriculture or forestry (mainly fishing but also aquaculture), natural system modifications (e.g. dredging and sea defence works), urbanisation and climate change. Even for habitats where the assessment outcome was Data Deficient, the Red List assessment process has resulted in the compilation of a substantial body of useful information to support the conservation of marine habitats.
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- 2016
11. Mitigating the impacts of coastal defence measures
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Airoldi, L., PERKOL-FINKEL, S., Airoldi L., and Perkol-Finkel S.
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parasitic diseases ,fungi - Abstract
Defense measures have a strong impact on species composition, abundance and diversity of coastal marine environments. Understanding the factors controlling these impacts is crucial for proper management of coastal areas. We show results of field studies aiming at developing means for promoting the growth of desirable species and for controlling the spread of invasive species on coastal man-made structures.
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- 2010
12. Detrital enrichment from marine urban structures and its far-field effects on soft-bottom assemblages
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Laura Airoldi, Fontana, Giovanni, Ferrario, Filippo, Franzitta, Giulio, Perkol Finkel, S., Magnani, A., Bianchelli, S., Pusceddu, A., Marina A. Colangelo, Thrush, S. F., Airoldi L., Fontana G., Ferrario F., Franzitta G., Perkol-Finkel S., Magnani A., Bianchelli S., Pusceddu A., Colangelo M.A., and Thrush S.F.
- Abstract
We report the results of a field experiment aimed at identifying and quantifying possible changes in sedimentary environments and associated assemblages related to the unnatural addition of detritus produced by hard bottom species associated to man-made, urban structures along the coasts of the north Adriatic sea
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- 2010
13. The loss and recovery prospects of forests of canopy-forming macroalgae
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Airoldi, L., PERKOL-FINKEL, S., Airoldi L., and Perkol-Finkel S.
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- 2009
14. Blue is the New Green – Harnessing Urban Coastal Infrastructure for Ecological Enhancement
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Perkol-Finkel, S., primary and Sella, I., additional
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- 2016
- Full Text
- View/download PDF
15. Managing coastal defence structures to mitigate their impacts and elevate their ecological value
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Airoldi, L, Ferrario, F, Iveša, L, Bulleri, F, Strain, E, and PERKOL-FINKEL, S.
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- 2012
16. Studio sperimentale dei fattori che influenzano il successo di trapianto di alghe habitat forming su strutture artificiali marine
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Ferrario, F., PERKOL-FINKEL, S., Nicotera, V., and Airoldi, L.
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- 2011
17. ESDNT - Europaean scientific diving training networks (FP7-Pople-2012-ITN) call
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Ponti, Massimo, Cerrano, C., Hill, S., Shashar, N., Bruemmer, F., Sayer, M., Dickel, L., Gonella, M., Lott, C., Palma, M., Perkol-Finkel, S., Bosco, A., Longobardi, P., Norro, A., Jaklin, Andrej, and Ponti, Massimo
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EU ,scientific diving ,training network ,FP7-MC call - Abstract
Since 50's the scientific diving community has endeavoured to promote safe, effective diving through self-imposed training and education programs. In the last few decades in some countries the Government recognised peculiarity and requirements of scientific diving. In the year 20008, the Europaean Science Foundation adopted the Marine Board Europaean Scientific Diving Panel (ESDP). The main objectives of the ESDP are: i) to encourage international mobility in the Europaean scientific diving community through the implementation of a support framework ; ii) to promote safety in scientific divings across Europe ; iii) to advance underwater scientific excellence in Europe. Within the ESDP framework, the proposed ESDTN project will focus on the training of early-stage researches (ESRs) in the development and application of innovative underwater scientific methods and approaches in the fields of biology, experimental ecology, cartogaphy and human impact assessment. A limited number of experienced researchers (ERs) will be recruited to collaborate in research activities and complete their formation. ESRs and ERs will be trained to apply a range of underwater scientific methods, from measurements to manipulative field experiments, sharing competences from different fields and improving their skills. Each ESR should develop a 3-years research program in a specific scientific field increasing knowledge in natural and/or anthropogenic marine processes or developing new underwater methodologies or instruments. The trans-nationaljoint research training network will be based on Europaean universities with well established research and training experience in these fields, which can provide high-quality education and a mutually recognised PhD certificate. Associated partners will include national and international organizations and a number of small-medium enterprises (SMEs), which can provide research and complementary training and secondment opportunities.
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- 2011
18. Conservation challenges in marine urban environments
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Airoldi, L, Beck, Mw, Bulleri, F, Ferrario, F, Micheli, F, Nicotera, V, Perkol-Finkel, S, Airoldi L, MW Beck, F Bulleri, F Ferrario, F Micheli, V Nicotera, and S Perkol-Finkel
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- 2011
19. Klyxum adii spec. nov. (Octocorallia: Alcyonacea) from Kenya
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Benayahu, Y., Perkol-Finkel, S., and Naturalis journals & series
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new species ,Cnidaria ,Alcyoniidae ,parasitic diseases ,Indian Ocean - Abstract
A new species of Klyxum from Kenya, K. adii, is described and depicted. Its unique features include an encrusting growth form, short lobes, which are knob-shaped or flattened-laterally low crests and large branched spindles, thus making it different from the previously described Klyxum species.
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- 2010
20. Differential recruitment of benthic communities on neighboring artificial and natural reefs
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Perkol-Finkel, S., primary and Benayahu, Y., additional
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- 2007
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21. Fouling reefal communities on artificial reefs: Does age matter?
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Perkol-Finkel, S, primary, Shashar, N, additional, Barneah, O, additional, Ben-David-Zaslow, R, additional, Oren, U, additional, Reichart, T, additional, Yacobovich, T, additional, Yahel, G, additional, Yahel, R, additional, and Benayahu, Y, additional
- Published
- 2005
- Full Text
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22. Klyxum adii spec. nov. (Octocorallia: Alcyonacea) from Kenya.
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Benayahu, Y. and Perkol-Finkel, S.
- Subjects
- *
OCTOCORALLIA , *ALCYONACEA , *CNIDARIA , *ZOOLOGICAL research - Abstract
A new species of Klyxum from Kenya, K. adii, is described and depicted. its unique features include an encrusting growth form, short lobes, which are knob-shaped or flattened-laterally low crests and large branched spindles, thus making it different from the previously described Klyxum species. [ABSTRACT FROM AUTHOR]
- Published
- 2009
23. Design options, implementation issues and evaluating success of ecologically engineered shorelines
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Morris, R. L., Heery, E. C., Loke, L. H. L., Lau, E., Strain, E. M. A., Airoldi, L., Karen Alexander, Bishop, M. J., Coleman, R. A., Cordell, J. R., Dong, Y. -W, Firth, L. B., Hawkins, S. J., Heath, T., Kokora, M., Lee, S. Y., Miller, J. K., Perkol-Finkel, S., Rella, A., Steinberg, P. D., Takeuchi, I., Thompson, R. C., Todd, P. A., Toft, J. D., and Leung, K. M. Y.
24. Design options, implementation issues and evaluating success of ecologically engineered shorelines
- Author
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Morris, R. L., Heery, E. C., Loke, L. H. L., Lau, E., Strain, E. M. A., Airoldi, L., Alexander, K. A., Bishop, M. J., Coleman, R. A., Cordell, J. R., Dong, Y. -W, Firth, L. B., Hawkins, S. J., Heath, T., Kokora, M., Lee, S. Y., Jon Miller, Perkol-Finkel, S., Rella, A., Steinberg, P. D., Takeuchi, I., Thompson, R. C., Todd, P. A., Toft, J. D., and Leung, K. M. Y.
25. A global analysis of complexity–biodiversity relationships on marine artificial structures
- Author
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Richard C. Thompson, Catriona Macleod, Kenneth M.Y. Leung, Luciana V. R. Messano, Kathleen E. Knick, Moisés A. Aguilera, Terrence P. T. Ng, Adam Davey, Rochelle D. Seitz, Connor McKenzie, Stephen J. Hawkins, Tasman P. Crowe, Jean C. Yee, Mick E. Hanley, Edward Tak Chuen Lau, Paul R. Brooks, Ricardo Coutinho, Martin Thiel, Shimrit Perkol-Finkel, Louise B. Firth, Gregory M. Ruiz, Clarissa M. L. Fraser, Melanie J. Bishop, DJ Ross, Peter D. Steinberg, Mathew J. Perkins, Chela J. Zabin, Chee B. Cheah, Ido Sella, J. David Aguirre, Francesco Paolo Mancuso, Emma L. Johnston, Sandisiwe Mafanya, Gail V. Ashton, Maria L. Vozzo, Benny K. K. Chan, Francesca Porri, Kathryn A. O'Shaughnessy, Maritina Bernardi, Lais P. D. Naval-Xavier, Su Yin Chee, Raviv Shirazi, Marco Abbiati, Laura Airoldi, Paula Pattrick, Elisabeth M. A. Strain, Strain E.M.A., Steinberg P.D., Vozzo M., Johnston E.L., Abbiati M., Aguilera M.A., Airoldi L., Aguirre J.D., Ashton G., Bernardi M., Brooks P., Chan B.K.K., Cheah C.B., Chee S.Y., Coutinho R., Crowe T., Davey A., Firth L.B., Fraser C., Hanley M.E., Hawkins S.J., Knick K.E., Lau E.T.C., Leung K.M.Y., McKenzie C., Macleod C., Mafanya S., Mancuso F.P., Messano L.V.R., Naval-Xavier L.P.D., Ng T.P.T., O'Shaughnessy K.A., Pattrick P., Perkins M.J., Perkol-Finkel S., Porri F., Ross D.J., Ruiz G., Sella I., Seitz R., Shirazi R., Thiel M., Thompson R.C., Yee J.C., Zabin C., Bishop M.J., and Elisabeth M. A. Strain, Peter D. Steinberg, Maria Vozzo, Emma L. Johnston, Marco Abbiati, Moises A. Aguilera, Laura Airoldi, J. David Aguirre, Gail Ashton, Maritina Bernardi, Paul Brooks,Benny K. K. Chan, Chee B. Cheah, Su Yin Chee, Ricardo Coutinho, Tasman Crowe, Adam Davey, Louise B. Firth, Clarissa Fraser, Mick E. Hanley, Stephen J. Hawkins, Kathleen E. Knick, Edward T. C. Lau, Kenneth M. Y. Leung, Connor McKenzie, Catriona Macleod, Sandisiwe Mafanya, Francesco P. Mancuso, Luciana V. R. Messano, Lais P. D. Naval-Xavier, Terrence P. T. Ng, Kathryn A. O'Shaughnessy, Paula Pattrick, Mathew J. Perkins, Shimrit Perkol-Finkel, Francesca Porri, Donald J. Ross, Gregory Ruiz, Ido Sella, Rochelle Seitz, Raviv Shirazi, Martin Thiel, Richard C. Thompson, Jean C. Yee, Chela Zabin, Melanie J. Bishop
- Subjects
0106 biological sciences ,estuarie ,bays, benthic, biodiversity, breakwaters, eco-engineering, estuaries, intertidal, sea- walls, tile, urban ,Biodiversity ,Intertidal zone ,010603 evolutionary biology ,01 natural sciences ,Abundance (ecology) ,bay ,seawall ,intertidal ,Ecology, Evolution, Behavior and Systematics ,Invertebrate ,biodiversity ,Abiotic component ,Global and Planetary Change ,bays ,benthic ,Ecology ,010604 marine biology & hydrobiology ,eco-engineering ,seawalls ,estuaries ,Geography ,Habitat ,breakwaters ,breakwater ,tile ,urban ,Spatial variability ,Species richness - Abstract
Aim Topographic complexity is widely accepted as a key driver of biodiversity, but at the patch‐scale, complexity–biodiversity relationships may vary spatially and temporally according to the environmental stressors complexity mitigates, and the species richness and identity of potential colonists. Using a manipulative experiment, we assessed spatial variation in patch‐scale effects of complexity on intertidal biodiversity. Location 27 sites within 14 estuaries/bays distributed globally. Time period 2015–2017. Major taxa studied Functional groups of algae, sessile and mobile invertebrates. Methods Concrete tiles of differing complexity (flat; 2.5‐cm or 5‐cm complex) were affixed at low–high intertidal elevation on coastal defence structures, and the richness and abundance of the colonizing taxa were quantified after 12 months. Results The patch‐scale effects of complexity varied spatially and among functional groups. Complexity had neutral to positive effects on total, invertebrate and algal taxa richness, and invertebrate abundances. However, effects on the abundance of algae ranged from positive to negative, depending on location and functional group. The tidal elevation at which tiles were placed accounted for some variation. The total and invertebrate richness were greater at low or mid than at high intertidal elevations. Latitude was also an important source of spatial variation, with the effects of complexity on total richness and mobile mollusc abundance greatest at lower latitudes, whilst the cover of sessile invertebrates and sessile molluscs responded most strongly to complexity at higher latitudes. Conclusions After 12 months, patch‐scale relationships between biodiversity and habitat complexity were not universally positive. Instead, the relationship varied among functional groups and according to local abiotic and biotic conditions. This result challenges the assumption that effects of complexity on biodiversity are universally positive. The variable effect of complexity has ramifications for community and applied ecology, including eco‐engineering and restoration that seek to bolster biodiversity through the addition of complexity.
- Published
- 2021
26. European Red List of Habitats: Part 1. Marine habitats
- Author
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S. Gubbay, N. Sanders, T. Haynes, J. A. M. Janssen, J. R. Rodwell, A. Nieto, M. García Criado, S. Beal, J. Borg, M. Kennedy, D. Micu, M. Otero, G. Saunders and M. Calix, L. Airoldi, V. V. Alexandrov, E. Alcázar, J. de Andalucia, L. Babbini, T. Bakran-Petricioli, E. Ballesteros, E. Bañares España, M. Bariche, E. Bastos, D. Basso, L. Bat, C. Battelli, H. Bazairi, C. N. Bianchi, G. Bitar, M. Bo, P. Brazier, L. Bush, S. Canese, S. P. Catrense, M. E. Cefalì, C. Cerrano, R. Chemello, E. B. Chernysheva, D. Connor, R. Cook, N. Dankers, A. Darr, A. R. Davis, N. Dolenc-Orbanić, S. Dubois, F. Espino, A. Flores Moya, J. Ford, M. Foulquie, S. Fowler, M. Fourt, S. Fraschetti, I. Fuller, K. Fürhaupter, B. Galil, V. Gerovasileiou, A. Giangrande, C. Giuseppe, P. Goriup, J. Grall, M. F. Gravina, A. Guelmami, A. Güreşen, L. Hadjioannou, J. M. Haldin, J. Hall-Spencer, J. G. Harmelin, R. Haroun-Tabrae, D. Harries, K. Herkül, T. Hetman, K. Hiscock, S. Hiscock, R. Holt, Y. Issaris, E. Jackson, A. Jeudy, C. Jimenez, C. Karamita, A. Karlsson, D. Kersting, E. Keskinen, F. Klinge, L. Klissurov, L. Knittweis-Mifsud, V. Kopiy, D. Korolesova, P. Kružić, G. Komakhidze, B. La Porta, J. Leinikki, P. Lehtonen, C. Linares, L. Lipej, V. Mačić, L. Mangialajo, S. Mariani, C. Melih, R. Metalpa, E. Mielke, V. Mihneva, N. Milchakova, K. Milonakis, C. Minguell, N. V. Mironova, J. Näslund, C. Numa, J. Nyström, O. Ocaña, N. F. Otero, V. Peña Freire, C. Pergent, S. Perkol-Finkel, A. Pibot, S. Pinedo, D. Poursanidis, A. Ramos, N. K. Revkov, J-T. Roininen, A. Rosso, J. Ruiz, M. Salomidi, P. Schembri, T. Shiganov, N. Simboura, M. Sini, C. Smith, A. Soldo, P. Somerfield, J. Templado, A. Terentyev, T. Thibaut, N. E. Topçu, C. Trigg, R. Turk, H. Tyler-Walters, L. Tunesi, K. Vera, M. Viera, J. Warzocha, S. Wells, M. Westerbom, S. Wikström, C. Wood, B. Yokes and H. Zibrowius. John Rodwell Susan Gubbay, Gubbay, S., Sanders, N., Haynes, T., Janssen, J. A. M., Rodwell, J. R., Nieto, A., García Criado, M., Beal, S., Borg, J., Kennedy, M., Micu, D., Otero, M., Calix, G. Saunders and M., Airoldi, L., Alexandrov, V. V., Alcázar, E., de Andalucia, J., Babbini, L., Bakran-Petricioli, T., Ballesteros, E., Bañares España, E., Bariche, M., Bastos, E., Basso, D., Bat, L., Battelli, C., Bazairi, H., Bianchi, C. N., Bitar, G., Bo, M., Brazier, P., Bush, L., Canese, S., Catrense, S. P., Cefalì, M. E., Cerrano, C., Chemello, R., Chernysheva, E. B., Connor, D., Cook, R., Dankers, N., Darr, A., Davis, A. R., Dolenc-Orbanić, N., Dubois, S., Espino, F., Flores Moya, A., Ford, J., Foulquie, M., Fowler, S., Fourt, M., Fraschetti, S., Fuller, I., Fürhaupter, K., Galil, B., Gerovasileiou, V., Giangrande, A., Giuseppe, C., Goriup, P., Grall, J., Gravina, M. F., Guelmami, A., Güreşen, A., Hadjioannou, L., Haldin, J. M., Hall-Spencer, J., Harmelin, J. G., Haroun-Tabrae, R., Harries, D., Herkül, K., Hetman, T., Hiscock, K., Hiscock, S., Holt, R., Issaris, Y., Jackson, E., Jeudy, A., Jimenez, C., Karamita, C., Karlsson, A., Kersting, D., Keskinen, E., Klinge, F., Klissurov, L., Knittweis-Mifsud, L., Kopiy, V., Korolesova, D., Kružić, P., Komakhidze, G., La Porta, B., Leinikki, J., Lehtonen, P., Linares, C., Lipej, L., Mačić, V., Mangialajo, L., Mariani, S., Melih, C., Metalpa, R., Mielke, E., Mihneva, V., Milchakova, N., Milonakis, K., Minguell, C., Mironova, N. V., Näslund, J., Numa, C., Nyström, J., Ocaña, O., Otero, N. F., Peña Freire, V., Pergent, C., Perkol-Finkel, S., Pibot, A., Pinedo, S., Poursanidis, D., Ramos, A., Revkov, N. K., Roininen, J-T., Rosso, A., Ruiz, J., Salomidi, M., Schembri, P., Shiganov, T., Simboura, N., Sini, M., Smith, C., Soldo, A., Somerfield, P., Templado, J., Terentyev, A., Thibaut, T., Topçu, N. E., Trigg, C., Turk, R., Tyler-Walters, H., Tunesi, L., Vera, K., Viera, M., Warzocha, J., Wells, S., Westerbom, M., Wikström, S., Wood, C., and John Rodwell Susan Gubbay, B. Yokes and H. Zibrowius.
- Published
- 2016
27. European Red List of habitats Part 1. Marine habitats
- Author
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BASSO, DANIELA MARIA, Gubbay, S, Sanders, N, Haynes, T, Janssen, JAM, Rodwell, JR, Nieto, A, García Criado, M, Beal, S, Borg, J, Kennedy, M, Micu, D, Otero, M, Saunders, G, Calix, M, Airoldi, L, Alexandrov, VV, Alcázar, E, de Andalucia, J, Babbini, L, Bakran-Petricioli, T, Ballesteros, E, Bañares España, E, Bariche, M, Bastos, E, Basso, D, Bat, L, Battelli, C, Bazairi, H, Bianchi, CN, Bitar, G, Bo, M, Brazier, P, Bush, L, Canese, S, Catrense, SP, Cefalì, ME, Cerrano, C, Chemello, R, Chernysheva, EB, Connor, D, Cook, R, Dankers, N, Darr, A, Davis, AR, Dolenc-Orbanić, N, Dubois, S, Espino, F, Flores Moya, A, Ford, J, Foulquie, M, Fowler, S, Fourt, M, Fraschetti, S, Fuller, I, Fürhaupter, K, Galil, B, Gerovasileiou, V, Giangrande, A, Giuseppe, C, Goriup, P, Grall, J, Gravina, MF, Guelmami, A, Güreşen, A, Hadjioannou, L, Haldin, JM, Hall-Spencer, J, Harmelin, JG, Haroun-Tabrae, R, Harries, D, Herkül, K, Hetman, T, Hiscock, K, Hiscock, S, Holt, R, Yssaris, Y, Jackson, E, Jeudy, A, Jimenez, C, Karamita, C, Karlsson, A, Kersting, D, Keskinen, E, Klinge, F, Klissurov, L, Knittweis-Mifsud, L, Kopiy, V, Korolesova, D, Kružić, P, Komakhidze, G, La Porta, B, Leinikki, J, Lehtonen, P, Linares, C, Lipej, L, Mačić, V, Mangialajo, L, Mariani, S, Melih, C, Metalpa, R, Mielke, E, Mihneva, V, Milchakova, N, Milonakis, K, Minguell, C, Mironova, NV, Näslund, J, Numa, C, Nyström, J, Ocaña, O, Otero, NF, Peña Freire, V, Pergent, C, Perkol-Finkel, S, Pibot, A, Pinedo, S, Poursanidis, D, Ramos, A, Revkov, NK, Roininen, J-T, Rosso, A, Ruiz, J, Salomidi, M, Schembri, P, Shiganov, T, Simboura, N, Sini, M, Smith, C, Soldo, A, Somerfield, P, Templado, J, Terentyev, A, Thibaut, T, Topçu, NE, Trigg, C, Turk, R, Tyler-Walters, H, Tunesi, L, Vera, K, Viera , M, Warzocha, J, Wells, S, Westerbom, M, Wikström, S, Wood, C, Yokes B, and Zibrowius, H
- Subjects
Marine habitats, conservation, red list, European environments ,BIO/07 - ECOLOGIA - Abstract
The European Red List of Habitats provides an overview of the risk of collapse (degree of endangerment) of marine, terrestrial and freshwater habitats in the European Union (EU28) and adjacent regions (EU28+), based on a consistent set of categories and criteria, and detailed data and expert knowledge from involved countries. A total of 257 benthic marine habitat types were assessed. In total, 19% (EU28) and 18% (EU28+) of the evaluated habitats were assessed as threatened in categories Critically Endangered, Endangered and Vulnerable. An additional 12% were Near Threatened in the EU28 and 11% in the EU28+. These figures are approximately doubled if Data Deficient habitats are excluded. The percentage of threatened habitat types differs across the regional seas. The highest proportion of threatened habitats in the EU28 was found in the Mediterranean Sea (32%), followed by the North-East Atlantic (23%), the Black Sea (13%) and then the Baltic Sea (8%). There was a similar pattern in the EU28+. The most frequently cited pressures and threats were similar across the four regional seas: pollution (eutrophication), biological resource use other than agriculture or forestry (mainly fishing but also aquaculture), natural system modifications (e.g. dredging and sea defence works), urbanisation and climate change. Even for habitats where the assessment outcome was Data Deficient, the Red List assessment process has resulted in the compilation of a substantial body of useful information to support the conservation of marine habitats.
- Published
- 2016
28. Between a rock and a hard place: Environmental and engineering considerations when designing coastal defence structures
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Pippa J. Moore, Juliette Jackson, Stephen J. Hawkins, Fabio Bozzeda, Katrin Bohn, Shimrit Perkol-Finkel, Tjeerd J. Bouma, Hilmar Hinz, Louise B. Firth, Laura Airoldi, E. H. Morgan, Mick E. Hanley, Richard C. Thompson, Victor Ugo Ceccherelli, Simon P. G. Hoggart, Marco Abbiati, Marina Antonia Colangelo, Martin W. Skov, Ally J. Evans, J. van Belzen, Filippo Ferrario, Elisabeth M. A. Strain, Firth L.B., Thompson R.C., Bohn K., Abbiati M., Airoldi L., Bouma T.J., Bozzeda F., Ceccherelli V.U., Colangelo M.A., Evans A., Ferrario F., Hanley M.E., Hinz H., Hoggart S.P.G., Jackson J.E., Moore P., Morgan E.H., Perkol-Finkel S., Skov M.W., Strain E.M, van Belzen. J., and Hawkins S.J
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0106 biological sciences ,Engineering ,Environmental Engineering ,010504 meteorology & atmospheric sciences ,Biodiversity ,Ocean Engineering ,Conservation ,01 natural sciences ,Novel ecosystem ,Ecosystem services ,14. Life underwater ,Coastal protection ,Habitat enhancement ,0105 earth and related environmental sciences ,Requirements engineering ,business.industry ,010604 marine biology & hydrobiology ,Environmental resource management ,15. Life on land ,Ecological engineering ,Oceanography ,Habitat ,13. Climate action ,Breakwater ,Threatened species ,business - Abstract
Coastal defence structures are proliferating as a result of rising sea levels and stormier seas. With the realisation that most coastal infrastructure cannot be lost or removed, research is required into ways that coastal defence structures can be built to meet engineering requirements, whilst also providing relevant ecosystem services—so-called ecological engineering. This approach requires an understanding of the types of assemblages and their functional roles that are desirable and feasible in these novel ecosystems. We review the major impacts coastal defence structures have on surrounding environments and recent experiments informing building coastal defences in a more ecologically sustainable manner. We summarise research carried out during the THESEUS project (2009–2014) which optimised the design of coastal defence structures with the aim to conserve or restore native species diversity. Native biodiversity could be manipulated on defence structures through various interventions: we created artificial rock pools, pits and crevices on breakwaters; we deployed a precast habitat enhancement unit in a coastal defence scheme; we tested the use of a mixture of stone sizes in gabion baskets; and we gardened native habitat-forming species, such as threatened canopy-forming algae on coastal defence structures. Finally, we outline guidelines and recommendations to provide multiple ecosystem services while maintaining engineering efficacy. This work demonstrated that simple enhancement methods can be cost-effective measures to manage local biodiversity. Care is required, however, in the wholesale implementation of these recommendations without full consideration of the desired effects and overall management goals.
- Published
- 2014
29. Loss and recovery potential of marine habitats: an experimental study of factors maintaining resilience in subtidal algal forests at the Adriatic sea
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Shimrit Perkol-Finkel, Laura Airoldi, Perkol-Finkel S., and Airoldi L.
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Ecology/Global Change Ecology ,0106 biological sciences ,Ecology/Community Ecology and Biodiversity ,Oceans and Seas ,Marine and Aquatic Sciences ,lcsh:Medicine ,Marine and Aquatic Sciences/Historical Biology ,Ecology/Marine and Freshwater Ecology ,Marine and Aquatic Sciences/Technology and Engineering ,010603 evolutionary biology ,01 natural sciences ,Ecology/Conservation and Restoration Ecology ,Water Movements ,Seawater ,Marine ecosystem ,Ecosystem ,14. Life underwater ,lcsh:Science ,Restoration ecology ,Marine and Aquatic Sciences/Ecology ,Abiotic component ,Multidisciplinary ,Ecology ,Geography ,Reproduction ,010604 marine biology & hydrobiology ,Marine and Aquatic Sciences/Climate Change ,lcsh:R ,Marine habitats ,Eukaryota ,15. Life on land ,Transplantation ,Marine and Aquatic Sciences/Conservation Science ,Habitat destruction ,Habitat ,13. Climate action ,lcsh:Q ,Seasons ,Ecology/Ecosystem Ecology ,Research Article - Abstract
Background Predicting and abating the loss of natural habitats present a huge challenge in science, conservation and management. Algal forests are globally threatened by loss and severe recruitment failure, but our understanding of resilience in these systems and its potential disruption by anthropogenic factors lags well behind other habitats. We tested hypotheses regarding triggers for decline and recovery potential in subtidal forests of canopy-forming algae of the genus Cystoseira. Methodology/Principal Findings By using a combination of historical data, and quantitative in situ observations of natural recruitment patterns we suggest that recent declines of forests along the coasts of the north Adriatic Sea were triggered by increasing cumulative impacts of natural- and human-induced habitat instability along with several extreme storm events. Clearing and transplantation experiments subsequently demonstrated that at such advanced stages of ecosystem degradation, increased substratum stability would be essential but not sufficient to reverse the loss, and that for recovery to occur removal of the new dominant space occupiers (i.e., opportunistic species including turf algae and mussels) would be required. Lack of surrounding adult canopies did not seem to impair the potential for assisted recovery, suggesting that in these systems recovery could be actively enhanced even following severe depletions. Conclusions/Significance We demonstrate that sudden habitat loss can be facilitated by long term changes in the biotic and abiotic conditions in the system, that erode the ability of natural ecosystems to absorb and recover from multiple stressors of natural and human origin. Moreover, we demonstrate that the mere restoration of environmental conditions preceding a loss, if possible, may be insufficient for ecosystem restoration, and is scarcely cost-effective. We conclude that the loss of complex marine habitats in human-dominated landscapes could be mitigated with appropriate consideration and management of incremental habitat changes and of attributes facilitating system recovery.
- Published
- 2010
30. Design, production, and validation of the biological and structural performance of an ecologically engineered concrete block mattress: A Nature-Inclusive Design for shoreline and offshore construction.
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Sella I, Hadary T, Rella AJ, Riegl B, Swack D, and Perkol-Finkel S
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- Florida, Pilot Projects, Beds, Ecosystem
- Abstract
Over the past decade, the scientific community has studied, experimented, and published a notable body of literature on the ecological enhancement of coastal and marine infrastructure (CMI). The Nature-Inclusive Design (NID) approach refers to methods and technologies that can be integrated into the design and construction of CMI to create a suitable habitat for native species (or communities) whose natural habitat has been degraded or reduced. To examine the compliance of new environmentally sensitive technologies with structural requirements and fiscal restraints, while providing ecosystem and habitat value, this paper presents the findings of a structural-economical-biological analysis of ecologically engineered Articulated Concrete Block Mattresses (ACBMs). To evaluate the structural and biological performance of the Ecological Articulated Concrete Block Mattresses, a pilot project was deployed in April 2017 at Port Everglades, Florida, USA, and evaluated against controls of adjacent artificial structures and smooth-surface concrete blocks and monitored over a period of two years. The elements of ecological enhancement implemented in the fabrication and design of the ecologically enhanced ACBMs were comprised of bio-enhancing concrete additives and science-based designs. Based on the results of this study, these design alterations have increased the richness and diversity of sessile assemblages compared to control blocks and adjacent artificial structures and supported a higher abundance of mobile species. This ecological improvement was achieved within the operational limitations of conventional manufacturing and installation technologies, while complying with strict structural requirements for standard concrete marine construction. The results supported the working hypothesis and demonstrated that modifications of concrete composition, surface texture, and macro-design have the potential to increase the ecological value of concrete-based CMI and promote a more sustainable and adaptive approach to coastal and marine development in an era of climate resilience-building. Integr Environ Assess Manag 2022;18:148-162. © 2021 SETAC., (© 2021 SETAC.)
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- 2022
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- View/download PDF
31. Mexican blind cavefish use mouth suction to detect obstacles.
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Holzman R, Perkol-Finkel S, and Zilman G
- Subjects
- Animals, Biomechanical Phenomena, Hydrodynamics, Mouth physiology, Swimming, Behavior, Animal physiology, Characidae physiology, Lateral Line System physiology, Mechanoreceptors physiology, Spatial Navigation
- Abstract
Fish commonly use their lateral line system to detect moving bodies such as prey and predators. A remarkable case is the Mexican blind cavefish Astyanax fasciatus, which evolved the ability to detect non-moving obstacles. The swimming body of A. fasciatus generates fluid disturbances, the alteration of which by an obstacle can be sensed by the fish's lateral line system. It is generally accepted that these alterations can provide information on the distance to the obstacle. We observed that A. fasciatus swimming in an unfamiliar environment open and close their mouths at high frequency (0.7-4.5 Hz) in order to generate suction flows. We hypothesized that repeated mouth suction generates a hydrodynamic velocity field, which is altered by an obstacle, inducing pressure gradients in the neuromasts of the lateral line and corresponding strong lateral line stimuli. We observed that the frequency and rate of mouth-opening events varied with the fish's distance to obstacles, a hallmark of pulse-based navigation mechanisms such as echolocation. We formulated a mathematical model of this hitherto unrecognized mechanism of obstacle detection and parameterized it experimentally. This model suggests that suction flows induce lateral line stimuli that are weakly dependent on the fish's speed, and may be an order of magnitude stronger than the correspondent stimuli induced by the fish's gliding body. We illustrate that A. fasciatus can navigate non-visually using a combination of two deeply ancestral and highly conserved mechanisms of ray-finned fishes: the mechanism of sensing water motion by the lateral line system and the mechanism of generating water motion by mouth suction., (© 2014. Published by The Company of Biologists Ltd.)
- Published
- 2014
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- View/download PDF
32. The hydrodynamics of contact of a marine larva, Bugula neritina, with a cylinder.
- Author
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Zilman G, Novak J, Liberzon A, Perkol-Finkel S, and Benayahu Y
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- Animals, Computer Simulation, Larva physiology, Microspheres, Models, Biological, Movement, Polystyrenes chemistry, Probability, Surface Properties, Swimming physiology, Aquatic Organisms physiology, Bryozoa physiology, Hydrodynamics
- Abstract
Marine larvae are often considered as drifters that collide with larval collectors as passive particles. The trajectories of Bugula neritina larvae and of polystyrene beads were recorded in the velocity field of a vertical cylinder. The experiments illustrated that the trajectories of larvae and of beads may differ markedly. By considering a larva as a self-propelled mechanical microswimmer, a mathematical model of its motion in the two-dimensional velocity field of a long cylinder was formulated. Simulated larval trajectories were compared with experimental observations. We calculated the ratio η of the probability of contact of a microswimmer with a cylinder to the probability of contact of a passive particle with the cylinder. We found that depending on the ratio S of the swimming velocity of the microswimmer to the velocity of the ambient current, the probability of contact of a microswimmer with a collector may be orders of magnitude larger than the probability of contact of a passive particle with the cylinder: for S≈0.01, η≈1; for S≈0.1, η≈10; and for S≈1, η≈100.
- Published
- 2013
- Full Text
- View/download PDF
33. Loss and recovery potential of marine habitats: an experimental study of factors maintaining resilience in subtidal algal forests at the Adriatic sea.
- Author
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Perkol-Finkel S and Airoldi L
- Subjects
- Geography, Oceans and Seas, Reproduction, Seasons, Ecosystem, Eukaryota physiology, Seawater, Water Movements
- Abstract
Background: Predicting and abating the loss of natural habitats present a huge challenge in science, conservation and management. Algal forests are globally threatened by loss and severe recruitment failure, but our understanding of resilience in these systems and its potential disruption by anthropogenic factors lags well behind other habitats. We tested hypotheses regarding triggers for decline and recovery potential in subtidal forests of canopy-forming algae of the genus Cystoseira., Methodology/principal Findings: By using a combination of historical data, and quantitative in situ observations of natural recruitment patterns we suggest that recent declines of forests along the coasts of the north Adriatic Sea were triggered by increasing cumulative impacts of natural- and human-induced habitat instability along with several extreme storm events. Clearing and transplantation experiments subsequently demonstrated that at such advanced stages of ecosystem degradation, increased substratum stability would be essential but not sufficient to reverse the loss, and that for recovery to occur removal of the new dominant space occupiers (i.e., opportunistic species including turf algae and mussels) would be required. Lack of surrounding adult canopies did not seem to impair the potential for assisted recovery, suggesting that in these systems recovery could be actively enhanced even following severe depletions., Conclusions/significance: We demonstrate that sudden habitat loss can be facilitated by long term changes in the biotic and abiotic conditions in the system, that erode the ability of natural ecosystems to absorb and recover from multiple stressors of natural and human origin. Moreover, we demonstrate that the mere restoration of environmental conditions preceding a loss, if possible, may be insufficient for ecosystem restoration, and is scarcely cost-effective. We conclude that the loss of complex marine habitats in human-dominated landscapes could be mitigated with appropriate consideration and management of incremental habitat changes and of attributes facilitating system recovery.
- Published
- 2010
- Full Text
- View/download PDF
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