2018
DOI: 10.1016/j.marenvres.2018.09.013
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Community bioirrigation potential (BIPc), an index to quantify the potential for solute exchange at the sediment-water interface

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Cited by 36 publications
(33 citation statements)
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“…Sediment porosity was determined from water content and solid-phase density measurements, accounting for the salt content of the pore water. Chl a was extracted from the freeze-dried sediment sample using acetone and quantified through UV spectrophotometry (Ritchie, 2006). The C / N ratio was calculated from total C and N concentrations, determined using an Interscience Flash 2000 organic element analyzer.…”
Section: Samplingmentioning
confidence: 99%
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“…Sediment porosity was determined from water content and solid-phase density measurements, accounting for the salt content of the pore water. Chl a was extracted from the freeze-dried sediment sample using acetone and quantified through UV spectrophotometry (Ritchie, 2006). The C / N ratio was calculated from total C and N concentrations, determined using an Interscience Flash 2000 organic element analyzer.…”
Section: Samplingmentioning
confidence: 99%
“…4) contains burrow type, feeding mode, burrow depth and an exponent to scale the metabolic rate, but from our analysis it appears that introducing more context dependency could improve results. In Renz et al (2018) for example, a distinction was made between an organism's activity based on the sediment type in which it occurred (cohesive or permeable sediment) in the calculation of their index, the community bioirrigation potential (BIP c ), although no comparison with measured irrigation rates has taken place. Furthermore, Wrede et al (2018) suggested including a temperature correction factor (Q 10 ) in the calculations to account for the expected metabolic response of macrofauna to increasing water temperatures (Brey, 2010).…”
Section: The Bioirrigation Potentialmentioning
confidence: 99%
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“…Transport processes in the solute phase (bioirrigation) primarily determine the oxidation status of the sediment by a downward transport of dissolved oxygen from the water column into the sediment and a release of reduced/adsorbed compounds like ammonia, phosphate, hydrogen sulfide, or methane (e.g., Aller, 1982). Particle reworking by fauna (particulate phase transport) often causes a rapid downward transport of labile fresh organic material derived from the water column (e.g., Graf, 1992), a slower transport of inorganic particles in the same direction, and may be responsible for the release of particle-associated contaminants due to changing redox conditions (e.g., Emerson et al, 1984;Kersten, 1988). Bioturbation is considered sensitive to anthropogenic drivers (Griffiths et al, 2017), but its effects on ecosystem functioning remain unclear.…”
Section: Introductionmentioning
confidence: 99%