Table 4.
Taxon, species | End point | Effect direction | Conc where effect was observed (μg/L) | Conc tested (μg/L) | Nonmonotonic dose response | Atrazine grade | Experiment type | Exposure duration | Reference |
---|---|---|---|---|---|---|---|---|---|
Salamander | |||||||||
A. macrodactylum | Infectivity of ATV | ↓ | Not provided | 1.84, 18.4, 184 | Dose response not provided | Tech | SR | 30 days | Forson and Storfer 2006aa |
A. tigrinum | Percentage infected with ATV | ↑ at 16 but not 1.6 or 160 | 16 | 1.6, 16, 160 | Yes | Tech | SR | Until metamorphosis | Forson and Storfer 2006bb |
A. tigrinum | Viral load | ND; p = 0.14 | – | 20, 200 | No | Tech | SR | 2 weeks | Kerby and Storfer 2009 |
A. tigrinum | Mortality due to ATV | ↑ | Not provided | 20, 200 | No | Tech | SR | 2 weeks | Kerby and Storfer 2009 |
Frog | |||||||||
R. pipiens | Rhabdias ranae nematode prevalence | ND; trend toward ↑ | – | 2.1, 21, 210 | No | Tech | SR | 21 days | Christin et al. 2003c |
R. pipiens | No. of adult R. ranae nematode | ↑, clear dose response | 21 + 210 > controls, 210 > water control | 2.1, 21, 210 | No | Tech | SR | 21 days | Gendron et al. 2003c |
R. pipiens | Chryseobacterium (Flavobacterium) menigosepticum infections | ↑ | 0.1 | 0.1 | NA | Tech | SR | Until metamorphosis | Hayes et al. 2006c,d |
R. pipiens | R. ranae nematode within host migration | Faster | 21, 210 | 2.1, 21, 210 | No | Tech | SR | 21 days | Gendron et al. 2003c |
R. pipiens | R. ranae nematode maturation and reproduction | Earlier | 21, 210 | 2.1, 21, 210 | No | Tech | SR | 21 days | Gendron et al. 2003c |
R. sylvatica | No. of Ribieoria sp. and Telorchis sp. | ↑ | 3, 30 | 3, 30 | No | Tech | SR | 4 weeks | Kiesecker 2002 |
R. sylvatica | Limb deformities caused by Ribieoria sp. | ↑ in ponds with atrazine | Ponds with atrazine | Unknown | NA | Comm | FS | Unknown | Kiesecker 2002 |
R. clamitans | No. of Echinostoma trivolvis cercariae | ↑ | 201 | 201 | NA | Tech | SR | 2 weeks | Rohr et al. 2008be |
R. pipiens | No. of larval trematodes | ↑ | < 1 Do not know maximum Conc | Unknown | No | Comm | FS | Unknown | Rohr et al. 2008cf |
R. clamitans | No. of larval Plagiorchid trematodes | ↑ | 117 | 117 | NA | Tech | PE | 4 weeks | Rohr et al. 2008c |
R. clamitans | No. of Echinostoma trivolvis cercariae | ↓, but amphibians not exposed to atrazine | 20, 200 | 20, 200 | No | Comm; Aatrexg | PE | Cercariae exposed for 2 hr | Koprivnikar et al. 2006h,i,j |
Fish | |||||||||
C. auratus | Mortality due to Aeromonas hydrophila challenge | ↑ | 42 | 42 | NA | Tech | SR | 12 weeks | Fatima et al. 2007c |
Abbreviations: ↓, decreased; ↑, increased; ATV, Ambystoma tigrinum virus; Comm, commercial; Conc, concentration; FS, field survey; 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).
Effect was observed when combining of 1.84, 18.4, and 184 treatments and comparing with controls; effect might be predominantly due to 184.
160 ppb was thought to reduce ATV infectivity explaining nonmonotonicity.
Atrazine was a component of a mixture of pesticides tested, and thus the experiment did not isolate the effects of atrazine.
Saw this effect only when atrazine was mixed with eight other pesticides.
Effect was found pooling pesticides and comparing them with control treatments.
No quantified factors correlated with atrazine could parsimoniously explain patterns in infection.
Aatrex is 59.2% inactive ingredients.
Effects could be due to inactive ingredients.
Effects could be due to chemicals other than atrazine that might be in the pond water used to make the stock solutions.
All LC50s were calculated incorrectly.