Review of the Ecotoxicological Properties of the Methylenedianiline Substances.

Concerning chronic toxicity, D. magna is the most sensitive species tested against MDA aquatic exposures, with a 21 days-NOEC of 0.00525 mg/L. Exposure of daphnids takes place via the aquatic phase. Other species of the same phylum (Arthropoda) appear to be less sensitive albeit with exposures via soil or sediment, with a 28 days-NOEC of 562 mg/kg d. w. soil (F. candida) and 41.3 mg/kg d. w. sediment (Hyalella azteca), for reproductive and survival endpoints, respectively. Also for acute toxicity, D. magna is more sensitive than the other species, with an 48 h-EC50 that spreads over two orders of magnitude, ranging from 0.019 to 2.7 mg/L. Fish show a more uniform reaction to MDA, with 96 h-LC50 ranging from about 20 to 60 mg/L; chronic data for fish are not available. Acute toxicity data for algae and cyanobacteria are in the range of 1-10 mg/L; based on growth rate, the 72 h-NOECr or ErC10 of MDA to algae is 0.3-9.3 mg/L.For sediment organisms, the black worm L. variegatus shows the highest sensitivity against MDA with a NOEC between ≤3.75 mg/kg and 30 mg/kg d. w., followed by the amphipod H. azteca. The lower sensitivity of L. variegatus in the second study compared to the first study is obviously attributable to the different feeding regimes (semi-continuous feeding against pre-spiked sediment). One argument might be that semi-continuous feeding allows the organisms to avoid the contaminated food. However, a change from semi-continuous feeding to sediment pre-spiked with nettle powder (Urtica sp.) results in an earlier and much stronger increase in ammonia concentration in the system. This became apparent after both studies on the blackworm were finalized. The ammonia 96 h-EC50 for the blackworm is 0.69 mg/L at pH = 8.2, and the 96 h-EC10 at pH = 8.2 is 0.33 mg/L (Hickey and Vickers, Arch Environ Contam Toxicol 26:292-298, 1994). As a result, the lower NOEC and LOEC in the second study with L. variegatus are probably attributable to interference by ammonia.MDA binds irreversibly to soil and sediment which may explain the general, but not uniform lower sensitivity of soil and sediment organisms against aquatic organisms. However, species with intense soil or sediment contact (L. variegatus and E. fetida) show in general lower NOEC values than those organisms with less direct contact (3.75 and 11.2 mg/kg d. w., respectively). On the one hand it may be hypothesized that this intense contact to soil bound MDA is one reason for the higher sensitivity; on the other hand, metabolic capacity against MDA of the organisms tested is unknown at this point in time and might as well explain differences in species sensitivity. For plants there are only acute data available, and in respect to acute toxicity L. sativa is more sensitive to MDA than E. fetida.Limited aquatic data available so far do not indicate that the toxicity of pMDA is different to MDA. In addition, the limited set of data generated with the marine M. macrocopa (crustacean), N. fustulum (diatom) and V. fisheri (bacteria) do not indicate that sea water organisms are more sensitive to MDA than fresh water organisms.In mammals, MDA is unlikely to interact with the endocrine sexual system; interaction with the adrenergic system cannot be ruled out, and effects of MDA on the thyroid hormone system have been demonstrated. MDA inhibits the thyroid peroxidase which might contribute to the thyroid gland tumors observed in chronic studies with rats and mice. Some anti-androgenic activity in in vitro studies with yeast cell did not prevail in in vivo studies with rats and mice.