2020
DOI: 10.1016/j.ecss.2020.106790
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Using species distribution models to guide seagrass management

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Cited by 25 publications
(23 citation statements)
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“…Our study provides the first spatially explicit assessment of the biodiversity enhancement value of seagrass beds. We use our modelling & Costello, 2018), restoration potential (Adams et al, 2016;Bittner et al, 2020) and climate vulnerability of seagrass beds (Valle et al, 2014) without considering the implications for associated fauna because of uncertainty about the interacting drivers and spatial patterns of seagrass-associated biodiversity. We find that current seagrass supports 43%-64% more species than comparable unvegetated areas because of positive effects of seagrass bed presence and total cover on faunal richness.…”
Section: Discussionmentioning
confidence: 99%
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“…Our study provides the first spatially explicit assessment of the biodiversity enhancement value of seagrass beds. We use our modelling & Costello, 2018), restoration potential (Adams et al, 2016;Bittner et al, 2020) and climate vulnerability of seagrass beds (Valle et al, 2014) without considering the implications for associated fauna because of uncertainty about the interacting drivers and spatial patterns of seagrass-associated biodiversity. We find that current seagrass supports 43%-64% more species than comparable unvegetated areas because of positive effects of seagrass bed presence and total cover on faunal richness.…”
Section: Discussionmentioning
confidence: 99%
“…The spatial distribution and abundance of seagrass-associated fauna may also vary in response to environmental conditions (e.g., ocean temperature, phytoplankton production, pH and dissolved oxygen) that can fluctuate across space and over diel, seasonal, annual and inter-annual time-scales, especially for more mobile fauna like marine fishes (Faletti et al, 2019;Garwood et al, 2013;Unsworth et al, 2007). Additionally, seascape features like habitat connectivity and proximity to anthropogenic stressors can affect seagrass patterns and associated fauna at landscape scales (Bittner et al, 2020;Gilby et al, 2018). However, the relative influence of these potentially interacting factors on faunal biodiversity patterns has not been previously explored.…”
Section: Introductionmentioning
confidence: 99%
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“…The current study only developed seagrass HSMs by using a maximum entropy modeling technique. Although this technique showed promising results [ 93 , 94 , 146 ], there are modeling techniques such as ecological-niche factor analysis [ 27 ], random forest, boosted regression tree, and generalized additive model [ 31 ] which are reported to perform well. Thus, future study is required to develop seagrass HSM by using several modeling techniques.…”
Section: Discussionmentioning
confidence: 99%
“…Οι μεγάλες εστίες απώλειας των θαλάσσιων αγγειόσπερμων γειτονεύουν με πυκνοκατοικημένες περιοχές, συμπεριλαμβανομένης της Ευρώπης, της Αυστραλίας και της Βόρειας Αμερικής (Kemp 2000). Παρόλο που σημαντικές χρονικές μεταβολές στην ανάπτυξη των θαλάσσιων αγγειόσπερμων μπορεί να σχετίζονται με υδρολογικές αλλαγές που συνδέονται με φυσικούς κλιματολογικούς κύκλους, μεταβολές του περιφερειακού υδρολογικού καθεστώτος λόγω δραστηριοτήτων του ανθρώπου μπορεί επίσης να είναι υπεύθυνες για μαζικές μειώσεις της αφθονίας των θαλάσσιων αγγειόσπερμων (Kemp 2000, Spalding et al 2003, Boudouresque et al 2009, Bittner et al 2020. Σε τοπική κλίμακα, οι απώλειες των θαλάσσιων αγγειόσπερμων έχουν αποδοθεί μεταξύ άλλων στη βυθοκόρηση για τη συντήρηση διαύλων πλοήγησης, την αλίευση με τράτα βυθού, τις δραστηριότητες σκαφών και τις απορρίψεις ιλύος (Kemp 2000, Spalding et al 2003, Boudouresque et al 2009.…”
Section: συρρίκνωση των λειμώνων των θαλάσσιων αγγειόσπερμωνunclassified