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Wetland sediment inhabited by a midge larva (Diptera: Chironomidae) in its U-shaped burrow, and oligochaete worms (Oligochaeta: Tubificinae) feeding head-down in sediments. Oligochaete consumption of organic particles from deeper sediment layers and subsequent translocation and accumulation of particles at the sediment–water interface causes a downward movement of sediment, the rate of which is determined by oligochaete size and density. Particles move downward until they reach the zone of oligochaete feeding, where they are ingested and transported rapidly above the sediment–water interface. This process, which may be repeated several times until particles pass below the zone of oligochaete feeding, results in enhanced transport and “conveyor belt” cycling of organic particles between oxic and anoxic layers of sediments. Meanwhile, midge larvae ventilate their U-shaped burrows in shallower layers of sediment, alternately drawing nitrate and oxygen as well as organic particles into burrows, thereby enhancing oxygenation of sediments, nitrification, and denitrification, and the production of N2 and N2O in shallow sediments.

Wetland sediment inhabited by a midge larva (Diptera: Chironomidae) in its U-shaped burrow, and oligochaete worms (Oligochaeta: Tubificinae) feeding head-down in sediments. Oligochaete consumption of organic particles from deeper sediment layers and subsequent translocation and accumulation of particles at the sediment–water interface causes a downward movement of sediment, the rate of which is determined by oligochaete size and density. Particles move downward until they reach the zone of oligochaete feeding, where they are ingested and transported rapidly above the sediment–water interface. This process, which may be repeated several times until particles pass below the zone of oligochaete feeding, results in enhanced transport and “conveyor belt” cycling of organic particles between oxic and anoxic layers of sediments. Meanwhile, midge larvae ventilate their U-shaped burrows in shallower layers of sediment, alternately drawing nitrate and oxygen as well as organic particles into burrows, thereby enhancing oxygenation of sediments, nitrification, and denitrification, and the production of N2 and N2O in shallow sediments.

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One of the goals of urban ecology is to link community structure to ecosystem function in urban habitats. Pollution-tolerant wetland invertebrates have been shown to enhance greenhouse gas (GHG) flux in controlled laboratory experiments, suggesting that they may influence urban wetland roles as sources or sinks of GHG. However, it is unclear if the...

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... synergistic or antagonistic effects when present in combination, due to their different modes of bioturbation. For example, midge larvae bioirrigate sediments through construction and ventilation of U-shaped tubes, but oligochaetes redistribute sediments to a greater degree and at greater depths than midge larvae, via "conveyor-belt feeding" ( Fig. 1; Lagauz ere et al. 2009). Furthermore, given the variable environmental conditions present in field settings, the degree to which invertebrate effects can be detected relative to other drivers of GHG flux amidst the "noise" in urban environments requires further ...
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... d 13 N (&). A few specimens were removed from each core, allowed to clear their guts for 24 h, and dried at 60°C for 48 h. These were weighed to the nearest lg, and then analyzed for C org and N org content and stable isotope ratios (d 13 C, d 13 N) using the methods already described. Data are provided in the supporting information (Appendix S1: Fig. ...
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... communities in all sites were dominated by oligochaetes and midge larvae. Oligochaetes accounted for ~82% AE 10% and 60% AE 20% (mean AE 95% CI) of average total invertebrate density in treatment wetlands and gc ponds, respectively (Fig. 3, Appendix S1: Table S3). Tubificinae (family Naididae) was the most abundant subfamily of oligochaetes, accounting for 78% AE 9% and 85% AE 14% of all oligochaetes encountered in treatment wetlands and gc ponds (Appendix S1: Table S4). Oligochaete density did not differ significantly between treatment wetlands and gc ponds (F 1,22 = 2.15, P = ...
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... that of the top-performing CO 2 flux model, which included temperature, density of all large oligochaetes and chironomids, and sediment C org content (Table 1, Fig. 4). The improvement of CH 4 flux prediction with the inclusion of benthic invertebrate density in models was even greater, with the RMSE of the best model excluding invertebrates being 29% higher (poorer predictive ability) than that of the top-performing CH 4 flux model, which included temperature, density of large oligochaetes, and sediment C org content (Table 1, Fig. 5). ...
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... the case of N 2 O flux, inclusion of invertebrate density did not substantially improve the predictive ability of models. All of the highest-ranked models (Δi < 2) models included temperature, nitrate + nitrite (NO X ), oxygen % saturation (DO) and an interaction term (NO X 9 DO), but the RMSE of models excluding or including invertebrates were similar (within 4.5%) in predictive ability (Table 1, Fig. 6). ...
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... of dissolved O 2 in water column; NO X 9 DO%, interaction between NO X and DO%. (Figs. 4, 5) is likely due to several factors, including (1) enhanced upward gas transport and diffusion through invertebrate burrows, (2) rapid cycling of organic matter between oxic and anoxic layers of sediment, due to conveyor-belt feeding by oligochaetes (Fig. 1), and (3) simultaneous enhancement of oxygenation and aerobic microbial respiration in upper sediment layers due to increased porosity, and enhanced anoxia (and therefore methane production) in lower layers of sediment due to microbial and oligochaete respiration. While it has been suggested that invertebrates grazing on methanotrophic ...
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... that invertebrates grazing on methanotrophic bacteria have the potential to enhance CH 4 fluxes in aquatic ecosystems ( Kankaala et al. 2007), this seems unlikely in the current study. The d 13 C values as low as À38.4 & suggest the possibility that midge larvae may have consumed methanotrophic bacteria at a few of our study sites (Appendix S1: Fig. S1; Jones et al. 2008), but this was rare and not observed for oligochaetes, which were the only taxa with densities significantly correlated to CH 4 ...
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... laboratory analyses at Monash University, Benedikt Fest and Steve Livesley assisted with greenhouse gas analysis at the University of Melbourne, and Jennifer Gonzalez and Guillermo Mendoza assisted with sorting and identification of preserved invertebrates at Scripps Institution of Oceanography. Meredith K. Meyers assisted with the creation of Fig. 1. We also thank Teresa Mackintosh, and William Steele from Melbourne Water, who fostered discussion and facilitated access to constructed wetland sites in Australia; and Dave Mason, Michael Freeman, Robert Sim, Chris Allen, and Stuart Cooper who generously provided access and resources to facilitate sampling ponds at their golf clubs ...
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... Chironominae Orthocladiinae Figure S1. To estimate invertebrate trophic position, midge larvae and oligochaetes were analyzed for δ13C (‰) and δ13N (‰). ...

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