Skip to main content
. Author manuscript; available in PMC: 2017 Sep 15.
Published in final edited form as: Sci Total Environ. 2016 May 9;565:211–221. doi: 10.1016/j.scitotenv.2016.04.162

Table 1.

Mercury concentrations in benthic invertebrates and zooplankton from 5 NH and VT lakes (means based on dry weights ± SD). N = 3 for each taxon and lake, except N = 2 amphipods in both Horseshoe and Post Pond. Means across lakes are presented in bold for each taxon.

Taxon Site Mean Hg (ng g−1) ± SD
Amphipoda Canobie Lake 131 ± 3
Gregg Lake 155 ± 40
Horseshoe Pond   32 ± 41
Post Pond 106 ± 27
Weatherhead Hollow Pond     1 ± 0
MEAN   88 ± 67
Chironomidae Canobie Lake 151 ± 25
Gregg Lake   75 ± 68
Horseshoe Pond   54 ± 13
Post Pond 147 ± 34
Weatherhead Hollow Pond 148 ± 18
MEAN 115 ± 53
Crayfish Post Pond   74 ± 12
Weatherhead Hollow Pond 129 ± 23
MEAN 102 ± 34
Odonata (Gomphidae) Post Pond   70 ± 31
Odonata (Libellulidae) Canobie Lake 264 ± 222
Gregg Lake 101 ± 14
Horseshoe Pond   34 ± 38
Post Pond 176 ± 22
Weatherhead Hollow Pond   94 ± 26
MEAN 134 ± 119
Snail Gregg Lake 137 ± 10
Horseshoe Pond 127 ± 55
Post Pond 515 ± 240
Weatherhead Hollow Pond   17 ± 28
MEAN 205 ± 234
Unionidae Post Pond 144 ± 44
Zooplankton (>202 μm) Gregg Lake 351 ± 75
Horseshoe Pond 199 ± 37
Post Pond 249 ± 204
MEAN 266 ± 129
Odonata (Coenagrionidae) Canobie Lake 212 ± 103
Gregg Lake 288 ± 27
Horseshoe Pond   52 ± 3
Post Pond 378 ± 158
Weatherhead Hollow Pond   13 ± 19
MEAN 188 ± 160