Ecological Archives A025-040-A1
Josephine C. Iacarella, Jaimie T. A. Dick, Mhairi E. Alexander, and Anthony Ricciardi. 2015. Ecological impacts of invasive alien species along temperature gradients: testing the role of environmental matching. Ecological Applications 25:706–716. http://dx.doi.org/10.1890/14-0545.1
Appendix A. Details of the studies and data included in the meta-analysis.
Table A1. Impact and thermal optima data for 16 invasive alien species (IAS) that directly impact native populations through predation or herbivory in inland water systems. In cases where all native species were consumed, a detection limit specific to the study was added to the numerator of the log response ratios (LR) within the study (denoted by [+ amount added]).
IAS group |
Species |
Thermal optimum measure, value |
Field method, study temp. |
Location |
Native population impacted |
Effect size: LR |
Effect size source; ref. |
Study temp. ref. |
Thermal optimum ref. |
Crustacean |
Bythotrephes longimanus |
Juvenile growth rate, 20°C |
Enclosure, 23.5°C |
Saginaw Bay, Lake Huron |
Ceriodaphnia spp. |
3.50 |
Table 1; 1 |
1 |
2 |
Cycops bicuspidatus |
0.12 |
||||||||
Bosmina spp. |
2.72 |
||||||||
Copepod nauplii |
0.39 |
||||||||
Chydorus sphaericus |
1.74 |
||||||||
Daphnia retrocurva |
2.79 |
||||||||
Crustacean |
Bythotrephes longimanus |
Juvenile growth rate, 20°C |
Enclosure, 23.5°C |
Saginaw Bay, Lake Huron |
Eubosmina coregoni |
3.44 |
Table 1; 1 |
1 |
2 |
Asplanchna spp. |
1.67 |
||||||||
Enclosure, 21.9°C |
Lake Huron |
Copepod nauplii |
1.23 |
||||||
Bythotrephes longimanus |
Juvenile growth rate, 20°C |
Mesocosm, 21.2°C |
Kakakise Lake, Ontario |
Zooplankton |
0.73 |
Week 4 in Fig. 3a; 3 |
3 |
2 |
|
Survey, 24°C |
Harp Lake, Ontario |
Zooplankton |
0.13 |
1992 & 1995 in Fig. 3a; 4 |
4 |
||||
Eriocheir sinensis |
Larval development, 1518°C |
Mesocosm, 17.7°C |
San Francisco Bay, CA |
Cladophora spp. |
1.84 |
Fig. 1; 5 |
5 |
6 |
|
Ludwigia spp. |
0.98 |
||||||||
Gumaga spp. |
0.75 |
||||||||
Corbicula spp. |
0.34 |
||||||||
Cercopagis pengoi |
Egg development, 13°C |
Survey, 8.9°C |
Lake Ontario |
Cyclopoid nauplii |
2.45 |
August 1999 in Fig. 6; 7 |
7 |
8 |
|
Calanoid nauplii |
1.78 |
||||||||
Crustacean |
Cercopagis pengoi |
Egg development, 13°C |
Survey, 16.8°C |
Gulf of Riga, Baltic Sea |
Bosmina coregoni |
6.05 |
Month 9 in Fig. 2b & d; 9 |
9 |
8 |
Acartia spp. |
0.09 |
||||||||
Carcinus maenas |
Larval development, 2025°C |
Enclosure, 11.9°C |
Bodega Bay, CA |
Cumella vulgaris |
2.53 |
Table 2; 10 |
11 |
12 |
|
Transennella tantilla |
0.81 |
||||||||
Leptochelia dubia |
0.94 |
||||||||
Transennella confusa |
1.52 |
||||||||
Corophium spp. |
1.45 |
||||||||
Exogene spp. |
0.48 |
||||||||
Pseudopolydora spp. |
0.76 |
||||||||
Phoronopsis viridis |
0.05 |
||||||||
Crustacean |
Mysis diluviana |
Juvenile maturation & molting rate, 88.5°C |
Enclosure, 9°C |
Lake Michigan |
Cladocera |
20.88 |
August in Table 1; 13 |
13 |
14, 15 |
Diaptomid adults |
0.96 |
||||||||
Cyclopoid adults |
0.00 |
||||||||
Copepod nauplii |
7.06 |
||||||||
Diaptomid copepodites |
2.72 |
||||||||
Cyclopoid copepodites |
8.14 |
||||||||
Survey, 20.3°C |
Flathead Lake, MT |
Cladocera |
0.32 |
August in Fig. 3a & b; 16 |
17 |
||||
Copepod |
0.59 |
||||||||
Limnomysis benedeni |
Egg & larval development, 15.9°C |
Mesocosm, 15°C |
University of Cologne, Germany |
Bosmina spp. |
1.36 |
Day 3 in Fig. 4; 18 |
18 |
19 |
|
Daphnia spp. |
1.18 |
||||||||
Copepod nauplii |
0.18 |
||||||||
Rotifera |
0.48 |
||||||||
Crustacean |
Procambarus clarkii |
Juvenile growth & molting rate, 16°C |
Enclosure, 21.5°C |
Lago della Doccia, Italy |
Potamogeton filiformis |
2.91 |
Fig. 1; 20 |
20 |
21 |
Nymphoides peltata |
0.67 |
||||||||
Haitia acuta |
1.22 |
||||||||
Mesocosm, 17.7°C |
San Francisco Bay, CA |
Cladophora spp. |
1.69 |
Fig. 1; 22 |
22 |
||||
Ludwigia spp. |
0.17 |
||||||||
Gumaga spp. |
0.41 |
||||||||
Corbicula spp. |
0.02 |
||||||||
Enclosure, 21.2°C |
Santa Ynez River, CA |
Benthic invertebrates |
0.86 |
Fig. 4; 23 |
23 |
||||
Enclosure, 21.7°C |
Ventura River, CA |
Benthic invertebrates |
0.46 |
||||||
Exclosure, 18°C |
Coyote Hills Marsh, CA |
Potamogeton pectinatus |
7.72 |
End of July in Fig. 5; 24 |
24 |
||||
Mesocosm, 20.5°C |
SW Iberia, Portugal |
Bufo calamita |
4.58 (+1) |
5 day exposure in Fig. 2, 25 |
25 |
||||
Crustacean |
Procambarus clarkii |
Juvenile growth & molting rate, 16°C |
Mesocosm, 20.5°C |
SW Iberia, Portugal |
Discoglossus galganoi |
1.55 (+1) |
5 day exposure in Fig. 2, 25 |
25 |
21 |
Pelobates cultripes |
1.74 (+1) |
||||||||
Peodytes ibericus |
0.84 (+1) |
||||||||
Bufo bufo |
2.77 (+1) |
||||||||
Alytes cisternasii |
0.80 (+1) |
||||||||
Hyla arborea |
0.77 (+1) |
||||||||
Hyla meridionalis |
0.52 (+1) |
||||||||
Rana perezi |
0.94 (+1) |
||||||||
Orconectes rusticus |
Juvenile growth rate, 2628°C |
Enclosure, 23.5°C |
Sugarbush Lake, WI |
Vallisneria americana |
0.53 |
Exp. 1, 3, & 5 in Fig. 1; 26 |
26 |
27 |
|
V. americana dominated macrophyte assemblage |
0.03 |
||||||||
Crustacean |
Orconectes rusticus |
Juvenile growth rate, 2628°C |
Enclosure, 23.5°C |
Sparkling Lake, WI |
Juncus pelocarpus dominated macrophyte assemblage |
0.26 |
Exp. 1, 3, & 5 in Fig. 1; 26 |
26 |
27 |
Enclosure, 23.3°C |
Plum Lake, WI |
Macrophytes (12 spp.), excluding Elodea canadensis |
2.30 |
Beginning of September in Fig. 2a & b, Fig. 5a; 28 |
29 |
||||
E. canadensis |
2.58 |
||||||||
Gastropoda (11 spp.) |
4.12 |
||||||||
Pacifastacus leniusculus |
Juvenile growth rate, 2326°C |
Survey, 18.9°C |
River Great Ouse, UK |
Cottus gobio |
0.12 |
Text on pg. 645; 30 |
30 |
31, 32 |
|
Noemacheilus barbatulus |
0.18 |
||||||||
Fish |
Cyprinus carpio |
Juvenile maximum scope for growth, 27°C |
Exclosure, 25.3°C |
Provo, Utah Lake |
Potamogeton pectinatus |
4.25 (+0.01) |
Fig. 3; 33 |
33 |
34 |
Exclosure, 26.4°C |
Saratoga, Utah Lake |
P. pectinatus |
0.84 (+0.01) |
||||||
Fish |
Cyprinus carpio |
Juvenile maximum scope for growth, 27°C |
Survey, 16°C |
Acambay, Mexico |
Macrophytes |
1.05 |
Table 1; 35 |
35 |
34 |
Exclosure, 20°C |
Lake Manitoba, Manitoba |
Chara spp. |
1.10 |
Fig. 2; 36 |
36 |
||||
Exclosure, 20.7°C |
Sulfur Springs, Lake Erie |
P. pectinatus dominated macrophyte assemblage |
1.71 |
August 28th in Table 2; 37 |
38 |
||||
Salvelinus fontinalis |
Juvenile growth rate, 1316.1°C |
Enclosure, 13.5°C |
Cascades Stream, Quebec |
Drifting invertebrates |
0.33 |
Table 1; 39 |
39 |
40, 41 |
|
Salmo trutta |
Juvenile growth rate, 1015.6°C |
Enclosure, 16.5°C |
Shag River, New Zealand |
Invertebrate predators |
0.64 |
Table 1; 42 |
43 |
44 |
|
Invertebrate grazers |
0.55 |
||||||||
Fish |
Salmo gairdneri |
Juvenile growth rate, 17.2°C |
Survey, 14.1°C |
Lake Eucumbene creeks, New South Wales |
Galaxiidae |
6.66 (+0.01) |
Table 3; 45 |
46 |
47 |
Carassius auratus |
Growth rate, 25°C |
Mesocosm, 27.1°C |
Ste. Anne de Bellevue, Quebec |
Potamogeton spp. |
1.49 |
Text on pg. 579; 48 |
48 |
49 |
|
Neogobius melanostomus |
Egg development, 1921°C |
Survey, 18.9°C |
Door Peninsula, Lake Michigan |
Dreissena polymorpha |
1.03 (+1) |
Table 2; 50 |
51 |
52, 53 |
|
Dreissena bugensis |
3.42 (+1) |
||||||||
Isopoda |
3.09 (+1) |
||||||||
Amphipoda |
1.91 (+1) |
||||||||
Trichoptera |
0.87 (+1) |
||||||||
Diptera |
0.51 (+1) |
||||||||
Gastropoda |
1.31 (+1) |
||||||||
Fish |
Neogobius melanostomus |
Egg development, 1921°C |
Survey, 24.3°C |
St. Lawrence River, Quebec |
Gastropoda (<14 mm) |
3.84 |
2009 in Fig. 2a; 54 |
55 |
52, 53 |
D. polymorpha & D. bugensis (<14 mm) |
1.96 |
||||||||
Gambusia affinis |
Growth rate, 28.630.9°C |
Enclosure, 18°C |
Walter Spring, UT |
Iotichthys phlegethontis (913 mm) |
0.25 |
Fig. 1; 56 |
56 |
57 |
|
I. phlegethontis (2328 mm) |
0.49 |
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