EA
Review #1, NDA 20-358 |
Page 11 |
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Half-lives were presented at 54, 11, and 30
hours at pH 5, 7, and 9, respectively. |
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The half-life presented are experimental
values in the presence of a xenon arc lamp.
Considerably longer half-lives were obtained from calculations which
normalized these results to flat bodies of water at various seasons and
latitudes (see page 177). Since many
of these half-lives exceed the threshold of 5 days, the statement that the
drug substance is subject to rapid photodegradation in aqueous media (page
14) is misleading. Photodegradation
cannot be considered a primary depletion mechanism unless the longer half
lives can be shown to be irrelevant to the locations or seasons where the
substance may be released. |
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DEFICIENT. |
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8. |
Environmental Effects of Released Substances |
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Microbial inhibition was conducted by (whited
out) according to EATAD 4.02 in compliance with FDA Good Laboratory
Practice regulations (see Attachment 4).
No inhibition of soil bacteria or nitrogen-fixing bacteria was
observed. An MIC of 1000 mg/L was
determined for fungi, ascomycetes, and blue-green algae. |
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Adequate. |
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Search literature and
report available test data in format items 7 and 8 and also report any
mammalian toxicity information. A
computerized structure/activity relationship modeling program could be used
to supplement the literature information. |
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9. |
Use of Resources and Energy: |
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a. Use
of Water and Energy: |
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The
Wellcome Foundation Limited (UK) |
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It
is estimated that less than 10% of the facilities energy use and less than
0.1% of the water will be
associated with drug substance production. |
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Adequate. |
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Burroughs
Wellcome Co. (USA) |
|
Drug
Substance |
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