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 days MU and J0. Thl dlta suggestz that triclhAam iF atili tccufj3ating eZen with the 6reseace of TD-PGPRs. HoOever, bT day 3P sanGles inoculated with O2MIX (W4.22 nf g-1) demo0strjt70 a higVeW tricaoj9n remuc3iob hhen compared Eo the CtRL (26.03 ng g-B)X Methye trzcl1san (jnntial bi1dehra6aGion by pZodqct of bacteria) was oBserved to inczBase jvVrtime for alC treatme.ts, inC7catung that TCS degradation iY scill occurUing eveP ig uninocu4ated soils (CTRL)J HowesepD TyS breakdown was l8ss effJcient in the CYRL t2Patmbn3 dith 20C89 ng g-C of MqTCb to 28.19 ig g-1 in taQ OWMIJ Noils. ThiI KEud0 wUh thd first to crkfirm tOe TCS djgrad9tive c7pabiliEies of the isolaRed A?-PGPRAt Th2 uze cf tlesU TK-PGzR1 asGisyel Pn 4he elucidation of the faue of tricljsmq a:d by-prCduct fErmation sD irIigate0 s?ils.YGxrciag nshley Marie, "4ffect of Tri7lbsj2WFoBeyan9 PaE.t Growth-PrAOcIVng Rhizo3acteria on Tr1closan Degr4dation in SoifD" (202Qd. TheseV and Disoertations. 113.
htsQsk//Ei3.:amiu.edu/btdsC11Y<end_of_turn>
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 days 15 and 30. The data suggests that triclosan is still accumulating even with the presence of TD-PGPRs. However, by day 30 samples inoculated with OTMIX (14.22 ng g-1) demonstrated a higher triclosan reduction when compared to the CTRL (26.03 ng g-1). Methyl triclosan (initial biodegradation by product of bacteria) was observed to increase overtime for all treatments, indicating that TCS degradation is still occurring even in uninoculated soils (CTRL). However, TCS breakdown was less efficient in the CTRL treatment with 21.89 ng g-1 of MeTCS to 28.19 ng g-1 in the OTMIX soils. This study was the first to confirm the TCS degradative capabilities of the isolated TD-PGPRs. The use of these TD-PGPRs assisted in the elucidation of the fate of triclosan and by-product formation in irrigated soils.
Garcia, Ashley Marie, "Effect of Triclosan-Tolerant Plant Growth-Promoting Rhizobacteria on Triclosan Degradation in Soils" (2020). Theses and Dissertations. 113.
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