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Fig 1.

Hypothetical sediment Corg spatial distributions (black lines) relative to a seagrass meadow edge.

These hypotheses assume (A) increasing current attenuation with distance into the meadow, (B) attenuation over a short distance and high suspended sediment availability, and (C) attenuation with low suspended sediment availability.

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Fig 1 Expand

Fig 2.

The restored South Bay eelgrass meadow showing its expansion history and sampling transects.

Sites B1-4 provided bare control sites (background photo printed under a CC BY license, with permission from R. Orth [51]).

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Fig 2 Expand

Fig 3.

Sediment Corg concentrations along transects by bed depth interval.

Error bars = SE.

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Fig 3 Expand

Table 1.

Sediment Corg concentrations and blue carbon stocks within the seagrass meadow by bed depth interval (CO2 estimated using molecular weight ratio).

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Table 1 Expand

Table 2.

Linear relationships between sediment Corg and independent variables measured at sites by bed depth interval.

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Table 2 Expand

Fig 4.

Organic matter, Corg, and bulk C:N distributions by bed depth interval within the meadow.

Transect sites are shown in the first Fig; the maps were generated by kriging.

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Fig 4 Expand

Fig 5.

Meadow grain size (mean and sand fraction) and peak seagrass shoot density distributions.

Sample sites are shown in each Fig; the maps were generated by kriging. Note that the inverse of sand fraction represents < sand-size particles.

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Fig 5 Expand

Table 3.

Kendall correlation (Tau B) for sediment bulk Corg and possible explanatory variables (n = 66 sites; top number = τ, bottom number = p-value; significant correlations at Bonferroni adjusted α’<0.0018 highlighted in bold).

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Table 3 Expand

Fig 6.

Sediment Corg concentration relationships with measured independent variables.

Comparisons are by bed depth interval as noted; see Table 2 for individual regression statistics.

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Fig 6 Expand

Table 4.

Spatial autoregressive model results for 0–3 cm data.

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Table 4 Expand