1998
DOI: 10.1016/s0038-0717(97)00147-8
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Insecticidal activity and biodegradation of the toxin from bacillus thuringiensis subsp. kurstaki bound to humic acids from soil

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Cited by 198 publications
(139 citation statements)
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“…Soils containing M have a better buffering capacity against changes in pH than soils without M [58,69]. These and previous studies confirmed that Bt toxins bound on clays or other surface-active particles [61,63,64,70] could accumulate in soil and retain insecticidal activity. These results have importance when evaluating the potential risks associated with the release to the environment of transgenic plants and bacteria containing genes from subspecies of Bt that encode for active toxins.…”
Section: Adsorption and Binding Of Purified Bt Toxins On Clay Mineralsupporting
confidence: 66%
“…Soils containing M have a better buffering capacity against changes in pH than soils without M [58,69]. These and previous studies confirmed that Bt toxins bound on clays or other surface-active particles [61,63,64,70] could accumulate in soil and retain insecticidal activity. These results have importance when evaluating the potential risks associated with the release to the environment of transgenic plants and bacteria containing genes from subspecies of Bt that encode for active toxins.…”
Section: Adsorption and Binding Of Purified Bt Toxins On Clay Mineralsupporting
confidence: 66%
“…First, physicochemical conditions and sediment composition must be favourable to avoid the complete degradation of DNA. In Lake Anterne, sediment compounds, such as clays, sands, humic substances and organomineral complexes, that allow DNA adsorbance, together with cold temperature and periodic anoxic conditions on the lake bottom (see Methods), are likely to have favoured DNA preservation [28][29][30] . Moreover, DNA was present in all samples, even the oldest, suggesting that the DNA was sufficiently preserved to successfully reconstruct the presence of the taxa of interest.…”
Section: Discussionmentioning
confidence: 99%
“…Cry1Ab can be introduced into agricultural soils through root exudates (32,33) and from maize biomass (34), with the exuded and leached protein persisting for up to 180 d and 3 y, respectively (34,35). Cry1Ab protein binds strongly to surface soils containing clay minerals, humic acids, and organomineral complexes (36)(37)(38)(39)(40)(41)(42), and it has the potential to enter adjacent streams through surface runoff and erosion. Our results from tile drains indicate that tiles may be a mechanism by which Cry1Ab leached from detritus on fields or from soils can be transported to streams.…”
Section: Discussionmentioning
confidence: 99%