Table 1.
Summary of the results for the effects of atrazine on the developmental rate and size at or near metamorphosis for amphibians.
Net effect on developmental rate |
Size at or near metamorphosis |
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Taxon, species | Effect direction | Conc where effect was observed (μg/L) | Nonmono-tonic dose response | Excluded from meta-analysis? | Effect direction | Conc where effect was observed (μg/L) | Nonmono-tonic dose response | Excluded from meta-analysis? | Conc tested (μg/L) | Atrazine grade | Experiment type | Exposure duration | Reference |
Frog | |||||||||||||
Bufo americanus | ND | – | NA | No | ↓ | 200 | NA | No | 200 | Comm; Aatrexa | PE | ≤ 88 days | Boone and James 2003b |
B. americanus | ↓c | 250, 500, 1,000 | Yes | No | ↓d | No Conc differed from controls | No | No | 250, 500, 1,000, 5,000, 10,000 | Tech | SR | 3 weeks | Freeman et al. 2005 |
B. americanus | ND | – | No | No | No data | – | No data | Yes | 1, 3, 30 | Tech | SR | LTM | Storrs and Semlitsch 2008 |
Rhinella arenarum | ↑ at 100 and 1,000, ↓ at 5,000 | 100, 1,000, 5,000 | Yes | No | No data | – | No data | Yes | 100, 1,000, 5,000 | Tech | SR | LTM | Brodeur et al. 2009 |
Hyla chrysoscelis | ↑ | 192 | No | No | No data | – | No data | Yes | 96, 192 | Tech | PE, two pulses | ≤ 129 days | Briston and Threlkeld 1998b |
Hyla versicolor | NDe | – | Possibly | No | ↓ | 200, 2,000 | No | No | 20, 200, 2,000 | Tech | PE | Mean of 13 days | Diana et al. 2000f |
H. versicolor | ND | – | NA | No | No data | – | No data | Yes | 1, 3, 30 | Tech | SR | LTM | Storrs and Semlitsch 2008 |
Rana clamitans | ↓ | 10 | Yes | No | ↓ | 10 | Yes | No | 10, 25 | Tech | SR | ≤ 273 days | Coady et al. 2004f |
Rana pipiens | Unknowng | – | No | Yes | ↓h | Not tested | No | No | 20, 200 | Tech | SR | LTM | Allran and Karasov 2000 |
R. pipiens | ND | – | NA | No | ↓ | 0.1 | NA | No | 0.1 | Tech | SR | LTM | Hayes et al. 2006 |
R. pipiens | ND | – | NA | No | ND | – | NA | No | 5 | Not provided | SR | ETM, ≤ 45 days | Bridges et al. 2004i |
Rana sphenocephala | ND | – | NA | No | ↓ | 200 | NA | No | 200 | Comm; Aatrexa | PE | ≤ 57 days | Boone and James 2003b |
R. sphenocephala | ND | – | NA | No | No data | – | No data | Yes | 1, 3, 30 | Tech | SR | LTM | Storrs and Semlitsch 2008 |
Rana sylvatica | No data | – | No data | Yes | ↓ | Unknown; conc in ponds not provided | NA | No | 3, 30 | Comm | FS | Unknown | Kiesecker 2002j |
Xenopus laevis | No data | – | No data | Yes | ND | – | No | No | 1, 10, 25 | Tech | SR | Mean of 56 days | Carr et al. 2003 |
X. laevis | ND | – | NA | No | No data | – | No data | Yes | 1, 10, 25 | Tech | SR | ETM | Du Preez et al. 2008 |
X. laevis | ↑ | 100, 450, 800 | No | No | Unknownk | – | Unknown | Yes | 100, 450, 800 | Tech | SR | 4 weeks | Freeman and Rayburn 2005 |
X. laevis | Unknown l,m,n | – | Unkown | Yes | ↓o | 0.01, 1, 100 | Possibly | No | 0.01, 0.1, 1.0, 25, and 100 | Tech | SR | ≤ 75 days | Kloas et al. 2009 |
X. laevis | ↓ detected by regression | No Conc differed from controls | No | No | ↓ | 20, 40, 80, 160, 320 | No | No | 20, 40, 80, 160, 320 | Tech | SR | LTM | Sullivan and Spence 2003 |
X. laevis | No data | – | NA | Yes | ↓ | 400 | NA | No | 400 | Tech | SR | LTM | Langerveld et al. 2009 |
Salamander | |||||||||||||
Ambystoma barbouri | ↑ | 40, 400 | No | No | ↓ | 400 | No | No | 4, 40, 400 | Tech | SR | Mean of 52 days exposure | Rohr et al. 2004 |
Ambystoma macrodactylum | ↑ | 184 | No | No | ↓ | 184 | No | No | 1.84, 18.4, 184 | Tech | SR | 30 days | Forson and Storfer 2006a |
Ambystoma tigrinum | ↑ | 16 vs. 1.6, but not vs. 0 | Possibly; no data | No | ND; trend toward ↓p | – | No data | No | 1.6, 16, 160 | Tech | SR | LTM | Forson and Storfer 2006b |
Ambystoma maculatum | ↑ and ↓q | 250 | Yes | No | ↓ | 250 | No | No | 75, 250 | Tech | SR | 86 days | Larson et al. 1998 |
A. maculatum | ↓ | 200 | NA | No | ↓ | 200 | NA | No | 200 | Comm; Aatrexa | PE | ≤ 57 days | Boone and James 2003e |
Ambystoma texanum | ↓ | 200 | NA | No | ↓ | 200 | NA | No | 200 | Comm; Aatrexa | PE | ≤ 88 days | Boone and James 2003b,r |
Abbreviations: ↓, decreased; ↑, increased; Comm, commercial; Conc, concentration; ETM, embryo to metamorphosis, or earlier (cases where amphibians metamorphosed before atrazine exposure ceased); FS, field survey; LTM, early larvae to metamorphosis; NA, not applicable (used when there were too few concentrations to evaluate nonmonotonicity); ND, not detected; PE, pulse experiment; SR, static renewal experiment; Tech, technical. Excluded studies are listed in Supplemental Material, Table S1 (doi:10.1289/ehp.0901164.S1).
Aatrex is 59.2% inactive ingredients.
Community-level study.
Authors show that atrazine modifies the thyroid axis for both X. laevis and B. americanus.
All five atrazine concentrations tested reduced frog size relative to controls, but no within-group variance estimates were provided.
200 ppb developed faster than 2,000 ppb.
Only a single egg mass; might not reflect general response.
Use only 50% of the metamorphs in the time to metamorphosis analysis without describing how they selected this subset of metamorphs or why they used only 50% for time to metamorphosis but 100% of the metamorphs for size at metamorphosis.
Authors report an interaction between atrazine and time for frog length, indicating that control animals were larger than those exposed to atrazine by the end of the experiment.
Tested as a mixture of 5 μ/L atrazine and 5 μ/L carbaryl.
Compared ponds with and without atrazine; effects might be due to other factors.
Frogs lose weight at metamorphosis, thus mass measurements were confounded by grouping tadpole and metamorph weights.
Provide no within-group variance estimate.
No statistics provided but conclude that there was no effect of atrazine.
Graphs for developmental rate through time are indiscernible.
Detected effects in only one of two experiments and for females only.
p = 0.080 for regression analysis, one-tailed test.
Results depended on developmental stage; authors showed that atrazine modifies thyroxine and corticosterone hormones.
Results depended on drying conditions.