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<br />pottaat m rare that the amine, ester, aDd <br />sodium formulations of 2,4D are all also <br />rapidly cleared because of their rapid con- <br />version to 2,4D acid oo absorption into <br />the body. The rapid clearance of un- <br />changed 2,4D from the body, coupled <br />with itt lack of genotoxiciry, further sup- <br />pmu the coochtsion that there is no plau- <br />sible toxicological evidence whereby <br />2,4D can be expected m be a carcinogen <br />(27). <br />Netuvtoricity <br />High and repeated dose resting in numer- <br />ous sallies with multiple species have not <br />deretted oeraological impacts from expo- <br />sure tu 2,4D (22w7). Subehronic oral <br />studies in rats with 2,4D acid, estea, and <br />amine salt derivatives found oo evidence <br />of hismlogical lesions or clinical signs of <br />mxiciry to the nervous system (13,16). In <br />additiog oeurolo®cal effects have not <br />been reported in a 13-week oral sub- <br />chronic study of 2,4D acid in mice, not <br />in dogs treated with single oral doses up <br />to 125 mg/kg (3 p, nor in a 1-year chronic <br />feeding study in dogs, nor in several 2- <br />year chronic studies in rodents (16,17). <br />Na neurological effects were indi- <br />cated in a recent 1-year chronic neraomx- <br />icological study in tats (16). The tats were <br />evaluated by functional observational baz- <br />tery, momr activity assay, and netnopath- <br />ology assessment The only effect noted <br />in tats exposed to 75 mg/kg/day was a <br />slight declirte (496) in average body <br />weight <br />Reproduction/Ti~ratolagy <br />No birth defear have been observed re- <br />lated m 2,4D or is derivatives in several <br />reproductive and developmental studies <br />conducted in laboratory animals (16). <br />Available studies suggest that exposures <br />high enough m be toxic to the moths may <br />also be toxic tu the Beats, with tesulliog <br />effect ao rtproduction and tlevehtpment <br />however, tro effects wain seen at borer <br />doses. These effects omtr only when the <br />dose is so Ltrge as ro overwhehn the pro- <br />cessing capaciry of the motber's kidneys. <br />The substantially lower exposttms sus- <br />tained by humans could not plausbly te- <br />SUI[ In these CffeCLS. <br />Environmental Tot~cology <br />Exposures of wildlife to 2,4D, whether <br />from dirut spraying or consumption of <br />treated vegetating is so low as m have m <br />toxicological significance (26). Indeed, <br />the greatest effect of 2,4D oo wildlife is <br />likely to be the presentation of an en- <br />hanced habitat foQowmg spraying, which <br />allows the infilnatioo of lower-growing, <br />Emit-bearing plmts. As docr>menred in <br />one long-trim study (3), many common <br />game species oaarpied the habitat created <br />by a sprayed ntiliry rightof-way oat of <br />an apparent preference and prospered <br />them over a period of mom than two de- <br />cades. <br />Ctinrent studies show rbaz 2,4D is <br />practically nontoxic to fish and only <br />slightly toxic to aquatic invertebrates <br />(Table 2). The compound is considered <br />practically nontoxic to the mallard duck <br />and bobwhite quail in 8-day dietary stud- <br />ies, only slightly toxic [o buds in acute <br />oral resting, ptacdcally nontoxic to hon- <br />eybees, and slightly mxic m earthworms <br />at high doses (lti). <br />EXPOSURE RIDUCTION <br />U addition m generating new studies, the <br />Task Fartx has coached an agreement with <br />the EPA to initiate a 2,4D exposure re- <br />duction program (11). The program re- <br />quires safety procedures in the mixing, <br />handling, and application of 2,4-D; the <br />use of protective clothing; improved per- <br /> <br />sonal hygiene practices; and an extensive <br />user education program. All 2,4-D prod- <br />ucts shipped by registrants in 1995 are <br />being packaged under the new label speci- <br />fied by this progi-dID. <br />BENEFITS <br />in response to concern by the EPA about <br />the health effects of farm worker expo- <br />sum to 2,4D and the phenoxy class of <br />herbicides, the USDA initiarod a benefits <br />assessment in 1993 to detertnine the etro- <br />nomie implications of a complete ban of <br />TABLE 2 Envlratntarttal to:kilt' suntrrrrry for 2,4D (axld). <br />eoo.mta w~ anus oral tny,• son mono tz~o pra9 ~~` nine <br />Yauard dark ear der ~` ~582o t~ P~keaY ~~ <br />9ee.dits goal se+ratsry tea a6a2o ppm Pr+~rs~osr~ <br />RenUw rtov 96tnur tCa 96a rngiL paeirallr rgnbrda <br />eweo® o~nom t.ca zta mW- ~+~ <br />Fatherd rrQVn~ 86-true ~s 3aa mg0. Pry mmodc <br />OgrMa 4a-huu I.G,a a mplL tEph[M/ tmrk <br />Aaeudran rani ABhov ~i sn ~r1 prarslullr ridtadc <br />FMOYBae tapicW L6a to yyDee R°°i'~' nwoda <br />e.ra.ams r+darutoECe taomyhoo ~iyrytmie <br />e17re LDS vafue ind4ates the 4rhat dose ofan active ingrcdent which it e>pected ro muse death fa 5096 <br />ofthr tart animals txated The higher dte LDy de tower dre acute taanry of the compound <br />°Dimethylamine soh of 2.4-D. <br />`The LCy ua7ue nsdicaves the 4rhel ca.centrmbn ofan actise ingredient which is espNesf to carat deaM <br />ro 50% of the test anurmis treated <br />eNDEC is the rm ahsmed effect concemration. <br />Studies rhrsw that 2,4-D is practically nontoxic <br />to mallard ducks. <br />