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Environmental Profiles of Chemical Flame-Retardant Alternatives for

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Algal Toxicity (OPPTS Harmonized Guideline 850.5400; OECD Guideline 201)<br />

Conclusion:<br />

The available algal toxicity data were judged tentatively adequate to meet the endpoint, pending<br />

the availability <strong>of</strong> additional in<strong>for</strong>mation from the studies that were not included in the published<br />

articles.<br />

Basis <strong>for</strong> Conclusion:<br />

Seventy-two-hour static studies in Selenastrum capricornutum, Scenedesmus subspicatus,<br />

Chlorella vulgaris (Millington et al., 1988), a 96-hour static study in Selenastrum capricornutum<br />

(Mayer et al., 1981), and a 22-day study in Ankistrodesmus falcatus were located. These data are<br />

summarized in Table 1-3. Taken together, these data may be adequate; however, additional<br />

in<strong>for</strong>mation is needed from the studies be<strong>for</strong>e they can be used as the basis <strong>for</strong> satisfying the<br />

algal toxicity endpoint.<br />

Millington et al. (1988) conducted a series <strong>of</strong> 72-hour static studies that were designed to<br />

evaluate the influence <strong>of</strong> various standard test media (OECD, U.S. EPA, and Bold’s basal) on the<br />

toxicity <strong>of</strong> triphenyl phosphate to three algal species, Selenastrum capricornutum, Scenedesmus<br />

subspicatus, and Chlorella vulgaris. These static studies followed OECD Guideline 201. Five<br />

concentrations ranging from 0.05 to 5 mg/L were tested in triplicate cultures. The test<br />

concentrations were not analytically confirmed. The resulting 72-hour NOAEC values ranged<br />

from 0.1 to 1 mg/L depending on the algal species tested and the test media used. EC50 values<br />

were not derived, and raw data were not available to allow <strong>for</strong> an independent calculation <strong>of</strong><br />

EC50 values. Overall, the studies appear to have been adequately conducted. Deficiencies in<br />

the data included reporting deficiencies (e.g., raw data, water quality values determined during<br />

the study, and growth <strong>of</strong> control replicates), lack <strong>of</strong> analytical confirmation <strong>of</strong> the test<br />

concentrations, and lack <strong>of</strong> EC50 determinations. Provided that the missing study details can be<br />

obtained and that an EC50 value can be determined, these data appear adequate to satisfy the<br />

algal toxicity endpoint.<br />

Mayer et al. (1981) conducted a 96-hour static test in Selenastrum capricornutum. Many details<br />

from this study were obtained from the unpublished report submitted to EPA (EG&G<br />

Bionomics, 1978d). Five concentrations that ranged from 0.6 to 10 mg/L were tested. Test<br />

concentrations were not analytically confirmed. An EC50 <strong>of</strong> 2 mg/L (95% confidence interval<br />

<strong>of</strong> 0.6-4 mg/L) was derived from this study. A clear NOAEC was not established because a 4%<br />

decrease in cell number and a 15% decrease in chlorophyll-" concentration was observed at the<br />

lowest concentration <strong>of</strong> 0.6 mg/L. Although the study appears to have been adequately<br />

conducted, initial and final cell concentrations <strong>of</strong> controls or treated cultures were not reported.<br />

Provided that these study details can be obtained, the 96-hour EC50 reported in this study<br />

appears to be adequate to satisfy the short-term algal toxicity endpoint. It should be noted that<br />

the EC50 determined from this study is at the approximate water solubility limit <strong>of</strong> TPP (2<br />

mg/L). The lack <strong>of</strong> a clear NOAEC precludes the use <strong>of</strong> this study as the sole basis to satisfy the<br />

1-39

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