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. 2021 Jul 3;9(1):coab049. doi: 10.1093/conphys/coab049

Table 1.

Locations and attributes of wetlands, ordered from highest to lowest salinity (mg/l Cl), where we collected waterborne CORT, larvae to extract interrenal CORT, water samples to extract ambient CORT or a combination of the aforementioned

Larvae
2017 2018 Salinity (mg/l Cl)
Site State Location T L C T L C Water 2017 2018 2019
LOS1 ND Lostwood NWR 11 9 1.46
SWA2 ND Swanson WPA 9 9 5.06
BGWLB MT Private 3 9 y 6.81 18.94 <32
AND10 MT Anderson WPA 9 9.72
PAR1 MT Pary WPA 7 6 10 y 30 101 41
NOR7 ND Norman WPA 8 1 16 44.33 41
NOR5 ND Norman WPA 9 101
BGWLC MT Private 8 445
264M MT Rabenberg WPA y 445
264Z MT Rabenberg WPA 8 552
NOR10 ND Norman WPA 5 9 727
264K MT Rabenberg WPA 10 y 1001.50 813
264J MT Rabenberg WPA 3 y 2494.50 2225.00
NOR9 ND Norman WPA 9 4 4103.00
124F MT Rabenberg WPA y 11 754.00

For ‘State’: ND indicates North Dakota; MT, Montana.

For ‘Location’: WPA indicates US Fish and Wildlife Service Waterfowl Production Area; NWR, National Wildlife Refuge.

For ‘Larvae’: T = barred tiger salamanders, L = northern leopard frogs, C = boreal chorus frogs; paired baseline and interrenal CORT samples were collected in 2017 and paired baseline and stress-induced CORT samples were collected in 2018.

For ‘Water’: y = replicate water samples collected on the same day in 2019 from several wetlands to assess variation in ambient CORT within wetlands.

Blank cells indicate that no samples were taken at that site in that year.