2012
DOI: 10.1007/s12237-012-9502-2
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Increased Variability of Microbial Communities in Restored Salt Marshes nearly 30 Years After Tidal Flow Restoration

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Cited by 18 publications
(25 citation statements)
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References 57 publications
(5 reference statements)
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“…In the histogram for each box, the number of significantly positive (green), negative (red), and not significant (NS) (gray) observations is plotted shorelines (Gittman et al 2016a). However, the majority of observations in Box 1a were negative and included decreased species diversity and/or abundance for a wide range of assemblages including microbial communities (Bernhard et al 2012), primary producers (e.g., Sturdevant et al 2002;O'Connor et al 2011), infaunal invertebrates (e.g., Peterson et al 2000;Seitz et al 2006;Bilkovic and Mitchell 2013), nekton and fish (Bilkovic 2011;Boys et al 2012;Peterson 2014, 2015) and waterbirds (Bolduc and Afton 2003). In Box 1b, negative responses to armoring dominated the results with decreases in diversity and abundance reported for mangroves (Anthony and Gratiot 2012; Heatherington and Bishop 2012), salt marsh vegetation (Bozek and Burdick 2005), invertebrates (Seitz et al 2006;Lawless and Seitz 2014;Swamy et al 2002), and nekton and fish (e.g., Balouskus and Targett 2016;Peterson 2014, 2015).…”
Section: E2: Species Assemblagesmentioning
confidence: 99%
“…In the histogram for each box, the number of significantly positive (green), negative (red), and not significant (NS) (gray) observations is plotted shorelines (Gittman et al 2016a). However, the majority of observations in Box 1a were negative and included decreased species diversity and/or abundance for a wide range of assemblages including microbial communities (Bernhard et al 2012), primary producers (e.g., Sturdevant et al 2002;O'Connor et al 2011), infaunal invertebrates (e.g., Peterson et al 2000;Seitz et al 2006;Bilkovic and Mitchell 2013), nekton and fish (Bilkovic 2011;Boys et al 2012;Peterson 2014, 2015) and waterbirds (Bolduc and Afton 2003). In Box 1b, negative responses to armoring dominated the results with decreases in diversity and abundance reported for mangroves (Anthony and Gratiot 2012; Heatherington and Bishop 2012), salt marsh vegetation (Bozek and Burdick 2005), invertebrates (Seitz et al 2006;Lawless and Seitz 2014;Swamy et al 2002), and nekton and fish (e.g., Balouskus and Targett 2016;Peterson 2014, 2015).…”
Section: E2: Species Assemblagesmentioning
confidence: 99%
“…Archaeal amo A genes were quantified as described in Moin et al (2009). Bacterial 16S rRNA genes were quantified as described in Bernhard et al (2012). Average amplification efficiencies from at least three separate runs were 101.3 ± 13.3% (betaproteobacterial amo A genes), 107.4 ± 5.2% (archaeal amo A genes), and 91.7 ± 4.5% (bacterial 16S rRNA genes).…”
Section: Methodsmentioning
confidence: 99%
“…Recently, molecular method-based studies have indicated that bacterial diversity in sediment has been linked with impacts of anthropogenic activities, such as increase of eutrophication and chemical pollution [9][10][11][12][13], changes in species of phytoplankton or zooplankton [14][15][16], and operating a dredging, reclamation, or remediation project [17][18][19][20]. Furthermore, some efforts have been made to study the bacterial community structure dynamics related to mariculture processes.…”
Section: Introductionmentioning
confidence: 99%