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. 2024 Feb 29;19(2):e0296836. doi: 10.1371/journal.pone.0296836

Table 2. Invertebrate and fish stable isotope signatures.

Consumer Dates Collected N δ13C (‰) δ15N (‰) δ34S (‰)
Terr 1: Riverine Insects 8 -26.25 ± 2.08 1.77 ± 2.23 6.58 ± 1.44
Coleoptera–Coccinellidae June 8–June 12, 2015 1 -25.29 ± N/A 2.58 ± N/A 7.57 ± N/A
Coleoptera–Coleoptera (other) June 8–June 12, 2015 1 -23.47 ± N/A 2.63 ± N/A 7.58 ± N/A
Hemiptera–Aphidae June 8–June 12, 2015 2 -25.93 ± 2.85 0.59 ± 2.87 5.89 ± 2.07
Hemiptera–Cicadellidae June 8–June 12, 2015 1 -25.31 ± N/A 4.53 ± N/A 6.31 ± N/A
Hymenoptera June 8–June 12, 2015 2 -27.38 ± 0.83 2.29 ± 2.09 6.52 ± 2.68
Lepidoptera June 8–June 12, 2015 1 -29.28 ± N/A -1.37 ± N/A 6.38 ± N/A
Terr 2: Marsh Insects 5 -24.01 ± 2.14 5.77 ± 1.31 8.76 ± 5.65
Hemiptera–Cicadellidae June 8–June 12, 2015 3 -23.12 ± 2.33 4.90 ± 0.74 6.80 ± 6.36
Hemiptera–Lygaeidae June 8–July 3, 2015 1 -24.48 ± N/A 7.07 ± N/A 14.69 ± N/A
Lepidoptera June 8–June 12, 2015 1 -26.22 ± N/A 7.09 ± N/A 8.72 ± N/A
Terr 3: Saldidae 3 -19.40 ± 0.69 7.87 ± 0.73 9.16 ± 4.92
Hemiptera–Saldidae June 8–July 3, 2015 3 -19.40 ± 0.69 7.87 ± 0.73 9.16 ± 4.92
Terr 4: Dolichopodidae 12 -21.41 ± 1.21 8.98 ± 1.07 9.81 ± 2.92
Diptera–Dolichopodidae June 8–July 3, 2015 12 -21.41 ± 1.21 8.98 ± 1.07 9.81 ± 2.92
Terr 5: Ephydridae 11 -23.77 ± 2.38 8.95 ± 1.07 10.16 ± 2.01
Diptera–Ephydridae June 8–July 3, 2015 11 -23.77 ± 2.38 8.95 ± 1.07 10.16 ± 2.01
Terr 6: Riverine Dipterans 7 -30.10 ± 4.37 6.30 ± 1.47 9.23 ± 1.36
Diptera–Brachycera June 8–July 3, 2015 2 -25.70 ± 1.17 6.35 ± 0.26 8.41 ± 0.93
Diptera–Chironomidae June 8–June 12, 2015 4 -33.26 ± 2.59 7.01 ± 0.88 10.27 ± 0.88
Diptera–Sciomyzidae June 8–June 12, 2015 1 -26.29 ± N/A 3.38 ± N/A 7.75 ± N/A
Terr 7: Marsh Dipterans 4 -22.31 ± 3.24 7.28 ± 0.20 10.92 ± 2.77
Diptera–Chironomidae June 8–June 12, 2015 1 -25.74 ± N/A 7.57 ± N/A 7.92 ± N/A
Diptera–Muscidae June 8–June 12, 2015 1 -24.31 ± N/A 7.14 ± N/A 9.21 ± N/A
Diptera–Tipulidae June 8–June 12, 2015 2 -19.60 ± 1.04 7.21 ± 0.06 13.27 ± 0.37
Aq 1: Riverine Isopods 3 -19.59 ± 2.35 7.60 ± 0.45 19.47 ± 0.09
Gnorimosphaeroma oregonensis May 28–June 3, 2015 3 -19.59 ± 2.35 7.60 ± 0.45 19.47 ± 0.09
Aq 2: Marsh Isopods 3 -17.24 ± 0.77 8.07 ± 0.36 20.08 ± 1.05
Gnorimosphaeroma oregonensis June 2–June 3, 2015 3 -17.24 ± 0.77 8.07 ± 0.36 20.08 ± 1.05
Aq 3: Riverine Mysids 11 -17.33 ± 4.94 10.57 ± 3.26 16.21 ± 0.51
Neomysis mercedis June 2–June 3, 2015 11 -17.33 ± 4.94 10.57 ± 3.26 16.21 ± 0.51
Aq 4: Marsh Mysids 3 -14.59 ± 0.16 11.29 ± 0.44 17.72 ± 0.17
Neomysis mercedis June 2–June 3, 2015 3 -14.59 ± 0.16 11.29 ± 0.44 17.72 ± 0.17
Aq 5: Delta Mysids 8 -13.99 ± 1.72 10.98 ± 0.81 17.05 ± 0.59
Neomysis mercedis June 2–June 3, 2015 8 -13.99 ± 1.72 10.98 ± 0.81 17.05 ± 0.59
Aq 6: Delta Shrimp 3 -13.23 ± 0.26 12 ± 0.16 18.02 ± 0.55
Crangon sp. June 2–June 3, 2015 3 -13.23 ± 0.26 12 ± 0.16 18.02 ± 0.55
Ben 1: Riverine Crustaceans 11 -20.79 ± 2.83 8.75 ± 2.28 15.03 ± 3.04
Amphipoda–Ampithoe sp. June 2–June 5, 2015 4 -21.88 ± 3.33 7.61 ± 1.63 16.17 ± 3.96
Amphipoda–Corophiidae June 2–June 8, 2015 6 -20.37 ± 2.74 9.80 ± 2.40 14.07 ± 2.57
Cumacea June 2–June 5, 2015 1 -18.96 ± N/A 6.96 ± N/A 16.25 ± N/A
Ben 2: Marsh Crustaceans 12 -17.20 ± 1.28 10.28 ± 1.44 15.80 ± 2.43
Amphipoda–Ampithoe sp. June 2–June 5, 2015 5 -17.87 ± 1.78 9.78 ± 1.17 15.99 ± 3.04
Amphipoda–Corophiidae June 2–June 8, 2015 6 -16.54 ± 0.19 10.88 ± 1.60 15.68 ± 2.26
Copepoda–Harpacticoida June 2–June 5, 2015 1 -17.74 ± N/A 9.25 ± N/A N/A
Ben 3: Delta Crustaceans 16 -13.53 ± 1.74 9.73 ± 1.01 16.11 ± 1.61
Amphipoda–Ampithoe sp. June 2–June 5, 2015 5 -14.50 ± 1.55 9.39 ± 0.39 16.99 ± 1.29
Amphipoda–Corophiidae May 28–June 8, 2015 6 -14.24 ± 1.14 9.82 ± 0.13 16.07 ± 1.50
Amphipoda–Eogammarus sp. June 2–June 5, 2015 1 -11.63 ± N/A 12.90 ± N/A 16.54 ± N/A
Copepoda–Harpacticoida June 2–June 5, 2015 1 -11.74 ± N/A 9.63 ± N/A N/A
Cumacea June 2–June 5, 2015 2 -10.87 ± 0.76 8.46 ± 0.59 13.11 ± N/A
Tanaidacea June 2–June 5, 2015 1 -13.44 ± N/A 10.35 ± N/A 14.50 ± N/A
Ben 4: Riverine Larvae 12 -21.10 ± 3.96 7.05 ± 1.16 12.18 ± 1.33
Diptera–Ceraptogonidae June 2–June 5, 2015 2 -18.14 ± 3.55 6.55 ± 0.95 N/A
Diptera–Chironomidae June 2–July 3, 2015 5 -21.33 ± 1.36 7.69 ± 1.48 11.49 ± 1.49
Diptera–Dolichopodidae June 2–June 5, 2015 1 -16.89 ± N/A 7.71 ± N/A 14.07 ± N/A
Diptera–Trichoptera June 2–June 5, 2015 4 -23.34 ± 5.69 6.35 ± 0.19 12.57 ± 0.43
Ben 5: Riverine Polychaetes 8 -23.43 ± 3.80 9.12 ± 1.74 12.13 ± 4.29
Neanthes sp. May 28–June 8, 2015 8 -23.43 ± 3.80 9.12 ± 1.74 12.13 ± 4.29
Ben 6: Delta Polychaetes 20 -14.01 ± 1.77 13.32 ± 2.92 15.73 ± 30
Eteone sp. June 2–June 8, 2015 6 -12.86 ± 0.56 15.26 ± 0.91 15.64 ± 0.14
Glycera nana June 2–June 8, 2015 2 -13.89 ± 0.02 14.98 ± 0.46 15.39 ± 0.67
Goniada brunea June 2–June 8, 2015 2 -15.22 ± 0.17 13.04 ± 0.61 10.96 ± 2.35
Neanthes sp. May 28–June 8, 2015 3 -13.14 ± 0.12 12.95 ± 1.46 14.85 ± 3.44
Phyllodocidae June 2–June 8, 2015 1 -12.78 ± N/A 14.52 ± N/A 15.32 ± N/A
Sabellidae June 2–June 8, 2015 1 -13.62 ± N/A 14.92 ± N/A 17.39 ± N/A
Spionidae June 2–June 8, 2015 5 -15.79 ± 2.59 10.11 ± 4.17 19.37 ± 0.34
Fish 1: Riverine Salmon (2015) May 27, 2015 4 -20.49 ± 1.25 11.10 ± 1.11 11.39 ± 5.22
Fish 2: Marsh Salmon (2015) May 22July 7, 2015 19 -19.26 ± 2.19 11.56 ± 1.30 12.61 ± 3.84
Fish 3: Delta Salmon (2015) May 22July 7, 2015 8 -18.27 ± 2.57 11.15 ± 1.34 11.97 ± 3.11
Fish 4: Riverine Salmon (2011) May 11May 25, 2011 10 -24.84 ± 1.74 10.68 ± 0.67 7.29 ± 1.65
Fish 5: Marsh Salmon (2011) June 6June 23, 2011 10 -21.03 ± 3.97 11.59 ± 1.10 11.04 ± 3.29
Fish 6: Delta Salmon (2011) June 8June 24, 2011 14 -18.93 ± 2.42 11.35 ± 1.54 12.65 ± 2.98
Fish 7: Marsh Sculpin (2011) June 6June 23, 2011 15 -15.98 ± 1.50 12.44 ± 0.43 15.46 ± 1.29

Stable isotope signatures (mean ± SD), collection dates, and number of composite samples collected (N) for terrestrial (Terr), aquatic (Aq), and benthic (Ben) invertebrates and fish in the Nisqually River Delta [84]. Isotopic signatures for broader consumer groups are shown in italics. The “riverine” groups include invertebrates and fish from the freshwater and tidal-forested habitats, the “marsh” groups from the transitional and emergent salt marsh habitats, and the “delta” groups from the mudflat and eelgrass habitats unless otherwise specified. Consumer groups were used in a Bayesian stable isotope mixing model to evaluate relative contributions of primary producers to invertebrate consumer diets and relative contributions of invertebrates to fish consumer diets.