Faculty Bibliography

Bacillus thuringiensis subsp. israelensis produces parasporal insecticidal crystal proteins (ICPs) that have larvicidal activity against some members of the order Diptera, such as blackflies and mosquitoes. Hydrolysis of the ICPs in the larval gut results in four major proteins with a molecular mass of 27, 65, 128, and 135 kDa. Toxicity is caused by synergistic interaction between the 25-kDa protein (proteolytic product of the 27-kDa protein) and one or more of the higher-molecular-mass proteins. Equilibrium adsorption of the proteins on the clay minerals montmorillonite and kaolinite, which are homoionic to various cations, was rapid (<30 min for maximal adsorption), increased with protein concentration and then reached a plateau (68 to 96% of the proteins was adsorbed), was significantly lower on kaolinite than on montmorillonite, and was not significantly affected by the valence of the cation to which the clays were homoionic. Binding of the toxins decreased as the pH was increased from 6 to 11, and there was 35 to 66% more binding in phosphate buffer at pH 6 than in distilled water at pH 6 or 7.2. Only 2 to 12% of the adsorbed proteins was desorbed by two washes with water; additional washings desorbed no more toxins, indicating that they were tightly bound. Formation of clay-toxin complexes did not alter the structure of the proteins, as indicated by sodium dodecyl sulfate-polyacrylamide gel electrophoresis of the equilibrium supernatants and desorption washes and by dot blot enzyme-linked immunosorbent assay of the complexes, which was confirmed by enhanced chemiluminescence Western blot analysis. Free and clay-bound toxins resulted in 85 to 100% mortality of the mosquito Culex pipiens. Persistence of the bound toxins in nonsterile water after 45 days was significantly greater (mortality of 63% +/- 12.7%) than that of the free toxins (mortality of 25% +/- 12.5%)

The culture of transgenic Bt corn (Zea mays L.) has resulted in concern about the uptake of the Cry1Ab protein toxin by crops subsequently grown in soils in which Bt corn has been grown. The toxin released to soil in root exudates of Bt corn, from the degradation of the biomass of Bt corn, or as purified toxin, was not taken up from soil, where the toxin is bound on surface-active particles (e.g. clays and humic substances), or from hydroponic culture, where the toxin is not bound on particles, by non-Bt corn, carrot (Daucus carota L.), radish (Raphanus sativus L.), and turnip (Brassica rapa L.). The persistence of the toxin in soil for 90 days after its addition in purified form or for 120-180 days after its release in exudates or from biomass, the longest times evaluated, confirmed that the toxin was bound on surface-active particles in soil, which protected the toxin from biodegradation. The greater toxicity of the toxin in soil amended with 9% montmorillonite or kaolinite than in soil amended with 3% of these clay minerals indicated that the binding and persistence of the toxin increased as the clay concentration was increased.

The anti-lepidopteran toxin (Cry1Ab protein) encoded by truncated genes from Bacillus thuringiensis was released in the root exudates from all hybrids of Bt corn studied and which represented three transformation events (Bt11, MON810, and 176). In vitro and in situ studies indicated that the toxin released in root exudates accumulates in soil, as it adsorbs and binds rapidly on surface-active particles (e.g. clays and humic substances), and retains insecticidal activity for at least 180 d, the longest time studied. The results indicated that the release of the Cry1Ab protein by roots is a common phenomenon with transgenic Bt corn and is not restricted to only the one Bt corn hybrid (NK4640Bt) and tranformation event (Bt11) studied initially. © 2002 Elsevier Science Ltd. All rights reserved.

The effects of montmorillonite (M) or kaolinite (K) on the vertical movement of the insecticidal Cry1Ab protein of Bacillus thuringiensis subsp. kurstaki (Bt) were studied in repacked soil columns. The protein was added to the columns either in a purified form, as root exudates from growing plants of Bt corn, or within the biomass of residues of Bt corn. The soil was amended to 0, 3, 6, 9, or 12% (vol vol^-1) with the clays. Vertical movement of the protein generally decreased as the content of either clay was increased, and the amount of protein recovered in leachates increased as the concentration of purified protein added was increased. The largest amount of purified protein (ca. 75%) was leached from soil not amended with clay, whereas the lowest amount (ca. 16%) was recovered from columns containing soil amended to 12% with M or K. The Cry1Ab protein was also present in leachates from soil columns in which various hybrids of Bt corn were grown or to which biomass of Bt corn had been added, whereas it was absent in leachates from columns in which the respective isolines of non-Bt corn were grown or to which biomass of non-Bt corn had been added. The Cry1Ab protein exhibited stronger binding and higher persistence, as well as remaining nearer the soil surface, in soil that contained the higher clay concentrations (i.e. had a higher cation-exchange capacity and specific surface area), indicating that it could be transported to surface waters via runoff and erosion. In contrast, the protein was more readily leached through soil with lower clay concentrations, indicating that it could contaminate groundwater. © 2002 Elsevier Science Ltd. All rights reserved.

Multisystem pseudohypoaldosteronism (PHA), is a syndrome of unresponsiveness to aldosterone with autosomal recessive inheritance. Previously we showed that mutations in the epithelial sodium channel (ENaC) alpha-, beta-, and gamma-subunits are responsible for PHA. In this study we examined four independent probands with multisystem PHA, three of whom were born to consanguineous parents. In our search for mutations we also determined the complete coding sequences of each of the three genes encoding alpha-, beta-, and gamma-subunits in individuals representing different ethnic groups. Our analyses revealed the following homozygous mutations in three probands: 1) insertion of a T in exon 8 of the alpha ENaC gene that causes a frameshift error at Tyr(447) and leads to a premature stop codon at K459 in a Pakistani patient; 2) R508stop mutation in exon 11 of the alpha ENaC gene in an Indian patient; and 3) a splice site mutation in intron 12 of the beta ENaC gene (1669 + 1 g-->a) in a Scottish patient. The parents were heterozygous for the latter two mutations. The second mutation was previously observed in an Iranian Jewish patient. Our sequencing of the alpha-, beta-, and gamma-coding sequences revealed some sequence variants, some of which may represent single nucleotide polymorphisms. The gamma-subunit protein sequence was completely conserved in the six subjects examined. The homozygous mutations identified in the alpha and beta ENaC genes should result in reduced or abolished ENaC activity in PHA patients, explaining the disease symptoms.

A UV-resistant mutant (Bt-m) of Bacillus thuringiensis subsp. kurstaki, producing a dark brown pigment, identified as melanin, was studied. Bt-m had higher larvicidity against Heliothis armigera than its parent. Survival of Bt-m spores and their insecticidal activity to irradiation at 254 nm and 366 nm were higher than those of the parent. The only toxic polypeptide produced by Bt-m was Cry1Ac (130 kDa); it lost cry1Aa, cry2Aa, and cry2Ab

There were no significant differences in the percent mortality and weight of earthworms (Lumbricus terrestris) after 40 days in soil planted with Bt (NK4640Bt) or non-Bt corn or after 45 days in soil amended with biomass of Bt or non-Bt corn. The toxin was present in the guts and casts of earthworms in soil planted with Bt corn or amended with biomass of Bt corn, but it was cleared within 2-3 days from the guts after placing in fresh soil. There were no significant differences in the colony-forming units of culturable bacteria (including actinomycetes) and fungi and in the numbers of protozoa and nematodes between rhizosphere soil of Bt and non-Bt corn or between soil amended with biomass of Bt and non-Bt corn. The Cry1Ab protein in root exudates and biomass of Bt corn appears not to be toxic to earthworms, nematodes, protozoa, bacteria, and fungi. The presence of the toxin in the guts and casts of earthworms confirmed that the toxin released in root exudates and from transgenic biomass was bound on surface-active particles in soil, which protected the toxin from biodegradation, as has been observed in this laboratory with purified toxin. © 2001 Elsevier Science Ltd. All rights reserved.

Bt corn has been genetically modified to express the Cry1Ab protein of Bacillus thuringiensis to kill lepidopteran pests. Fluorescence microscopy and staining with toluidine blue indicated a higher content of lignin in the vascular bundle sheaths and in the sclerenchyma cells surrounding the vascular bundle in all ten Bt corn hybrids, representing three different transformation events, studied than of their respective non-Bt isolines. Chemical analysis confirmed that the lignin content of all hybrids of Bt corn, whether grown in a plant growth room or in the field, was significantly higher (33-97% higher) than that of their respective non-Bt isolines. As lignin is a major structural component of plant cells, modifications in lignin content may have ecological implications.

The insecticidal toxin encoded by the cry1Ab gene from Bacillus thuringiensis was released in root exudates from transgenic Bt corn during 40 days of growth in soil amended to 0, 3, 6, 9, or 12% (v/v) with montmorillonite or kaolinite in a plant growth room and from plants grown to maturity in the field. The presence of the toxin in rhizosphere soil was determined by immunological and larvicidal assays. No toxin was detected in any soils from isogenic non-Bt corn or without plants. Persistence of the toxin was apparently the result of its binding on surface-active particles in the soils, which reduced the biodegradation of the toxin. The release of the toxin could enhance the control of insect pests or constitute a hazard to nontarget organisms, including the microbiota of soil, and increase the selection of toxin-resistant target insects.