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Hexagonal mesoporous silica modified with carboxylic acid (SiAc) has been obtained by reaction between chloroacetic acid and 3-aminopropyltrimethoxysilane, which was immobilized on porous material by a sol-gel process in the presence of an n-dodecylamine template. SiAc was characterized by TG, FT-IR, (29)Si NMR, (13)C NMR, SEM, surface charge density, surface area and porous diameter, which proved that the carboxylic group was chemically bonded to an inorganic structure, and the material presented a nanometric structure with spheres <50 nm and porous diameter of 10 nm. Herbicides 2,4-D and picloram were anchored on SiAc porous gel to produce the materials named SiD and SiPi, respectively. The controlled release of picloram from the SiAc was less than that of 2,4-D. After 26 days of releasing, 4.43 × 10(-5) mol L(-1) of picloram was delivered by SiPi, and 5.0 × 10(-5) L(-1) was released from the SiD in 30 days.

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BACKGROUND AND AIMS: The thin cell layer (TCL) technique is based on the use of very small explants and has allowed enhanced in vitro morphogenesis in several plant species. The present study evaluated the TCL technique as a procedure for somatic embryo production and plantlet regeneration of peach palm. METHODS: TCL explants from different positions in the shoot apex and leaf sheath of peach palm were cultivated in MS culture medium supplemented with 0-600 microM Picloram in the presence of activated charcoal. The production of primary calli and embryogenic calli was evaluated in these different conditions. Histological and amplified fragment length polymorphism (AFLP) analyses were conducted to study in vitro morphogenetic responses and genetic stability, respectively, of the regenerated plantlets. KEY RESULTS: Abundant primary callus induction was observed from TCLs of the shoot meristem in culture media supplemented with 150-600 microM Picloram (83-97%, respectively). The production of embryogenic calli depends on Picloram concentration and explant position. The best response observed was 43% embryogenic callus production from shoot meristem TCL on 300 microM Picloram. In maturation conditions, 34+/-4 somatic embryos per embryogenic callus were obtained, and 45.0+/-3.4% of these fully developed somatic embryos were converted, resulting in plantlets ready for acclimatization, of which 80% survived. Histological studies revealed that the first cellular division events occurred in cells adjacent to vascular tissue, resulting in primary calli, whose growth was ensured by a meristematic zone. A multicellular origin of the resulting somatic embryos arising from the meristematic zone is suggested. During maturation, histological analyses revealed bipolarization of the somatic embryos, as well as the development of new somatic embryos. AFLP analyses revealed that 92% of the regenerated plantlets were true to type. The use of TCL explants considerably improves the number of calli and somatic embryos produced in comparison with previously described protocols for in vitro regeneration of peach palm. CONCLUSIONS: The present study suggests that the TCL somatic embryogenesis protocol developed is feasible, although it still requires further optimization for in vitro multiplication of peach palm, especially the use of similar explants obtained from adult palm trees.

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A Mg/Al layered double hydroxide (LDH) was intercalated with the anionic herbicides 2,4-D, MCPA, and picloram by using three different methodologies: (i) direct synthesis (DS), (ii) regeneration (RE), and (iii) ion exchange (IE). The resulting complexes were characterized and assayed by batch release and column leaching tests, aiming at the controlled release of these herbicides. All the tested LDH-herbicide complexes displayed similar slow herbicide release properties in water, although the IE method seemed to result in complexes with a greater fraction of herbicide in a readily available form. Apparently, the LDH-herbicide complexes released most of the active ingredient present in the complexes at the end of the batch release experiment. This was attributed to the replacement of the intercalated herbicide by carbonate and hydroxyl anions from the aqueous solution. Compared to the free herbicides, the application of the three LDH-herbicide complexes (RE) to soil columns resulted in reduction in the maximum herbicide concentration in leachates and led to the retardation of herbicide leaching through the soil. All LDH-herbicide complexes presented an herbicidal efficacy similar to that of the free (technical) herbicides. Our results indicated the potential applicability of LDHs as supports for the preparation of slow release formulations of acid herbicides such as 2,4-D, MCPA, or picloram.

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The second most used herbicide in the Vietnam war was Agent White, which contained the active components 2,4-dichlorophenoxyacetic acid (2,4-D) and 4-amino-3,5,6-trichloropicolinic acid (picloram). The herbicide formulation Tordon 75D is similar in terms of its active components to Agent White and is currently used by the agricultural industry in Australia. As part of an investigation into the possible adverse effects of this herbicide on male reproductive performance, groups of five male rats were gavaged 5 days a week for 9 weeks with either 0.125 ml/kg (low dose), 0.25 ml/kg (middle dose), or 0.5 ml/kg (high dose) Tordon 75D or water (controls). The high dose corresponded to 150 mg/kg body weight 2,4-D and 37.5 mg/kg picloram acid equivalents. At the end of the treatment period, the testes were collected, weighed, and examined histologically and blood samples were taken to determine serum testosterone. Groups of high dose animals were also examined after 1, 2, and 4 weeks treatment. The 9 weeks treatment with Tordon 75D caused severe reduction in testicular weight in some high dose animals. Histologically, the small testes showed shrunken tubules with germ cell depletion. This damage was still evident in some rats following a 21 weeks recovery period suggesting that the testicular damage was permanent. Testicular damage was not due to endocrine disruption as there were no significant differences in the serum concentration of testosterone in control animals compared to Tordon 75D-treated animals. Blood levels associated with the high dose were determined in a separate study and were much higher than those likely to be obtained by occupational exposure to this herbicide.

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Male Vietnam veterans have repeatedly expressed concern that exposure to herbicides in Vietnam may have caused birth defects in their offspring. The second most used herbicide was a mixture of 2,4-D and picloram called Agent White. This study is an investigation into the possible male-mediated reproductive toxicology of this herbicide. Male rats were gavaged for 5 days per week for 9 weeks with a mixture of 2,4-D and picloram called Tordon 75D(R) (the Australian derivative of Agent White). Three doses were tested; the high dose was considered the maximum tolerated dose. Each male was mated with two untreated females during weeks 2 and 3, 4 and 5, and 8 and 9 of treatment, and with four untreated females after an 11-week recovery period. Negative controls were males dosed with distilled water, and positive controls were males dosed with cyclophosphamide at 5.1 mg/kg/day. All mated females were killed on day 20 of gestation, and the fetuses were weighed and examined for either structural malformations or skeletal development. Litter size, fetal weight, and malformation rate were all unaffected by treatment. The cyclophosphamide positive controls showed the expected large increase in postimplantation loss. In general, within the limitations of the power of the study, the results did not show any evidence that exposure to a herbicide formulation containing 2,4-D and picloram is likely to cause male-mediated birth defects or other adverse reproductive outcomes.

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Female CD-1 mice were exposed to Tordon 202c, a herbicide containing 2,4-dichlorophenoxyacetic acid and picloram, in the drinking water for 15 w at concentrations ranging from 0 to 0.3% of the product formulation. After 3 w of the 15-w treatment period, the mice received 1.5 mg/g urethan ip. Pulmonary adenoma production was evaluated 12 w later. Tordon 202c exposure produced a dose-dependent increase in tumor number, but had no effect on tumor size. Urethan-induced sleeping times which reflected the rate of urethan metabolism or excretion were altered, but a specific dose-related effect which could be correlated with tumor production was not observed. This suggests that Tordon 202c exposure influences adenoma formation by immunological mechanisms rather than by causing indirect effects on urethan metabolism or excretion.

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The chronic toxicity and oncogenicity of the herbicide picloram was studied in male and female Fischer 344 rats administered 0, 20, 60, or 200 mg/kg.d technical-grade picloram via their feed for 2 yr. A comprehensive set of in-life and clinical pathology parameters was measured and an extensive list of tissues was examined grossly and by light microscopy from control and treatment groups of animals. The primary treatment-related effect observed in the study was hepatocellular swelling and altered tinctorial properties in the central regions of the liver lobules of both sexes of rats ingesting 60 or 200 mg/kg.d picloram. Males were more affected than females. Increases in liver weights accompanied these changes in both sexes of rats ingesting the high dose level of picloram. All other histopathologic lesions observed were typical of those that normally occur in aged Fischer 344 rats. There were no treatment-related increases in the incidence of any particular tumor type or in total tumors. No treatment-related effects were observed in rats ingesting 20 mg/kg.d of the test material.

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The fate of picloram (4-amino-3,5,6-trichloropicolinic acid), an active ingredient in TORDON brand herbicides, was defined in 6 healthy male volunteers following single po doses of 5.0 and 0.5 mg/kg, and a dermal dose of 2.0 mg/kg. Picloram was administered orally as the sodium salt in grape juice. The dermal dose was applied to the volunteers' backs as the free acid dissolved in ethanol. The data indicate picloram was rapidly absorbed from the gastrointestinal tract (t1/2 = 20 min) and rapidly excreted unchanged in the urine. Over 90% of the po dose was recovered as unchanged picloram in the urine excreted through 72 hr; most of the dose (greater than 75%) was excreted within 6 hr and the remainder was excreted with an average half-life of 27 hr. By comparison picloram was slowly absorbed through the skin (t1/2 = 12 hr) and, based on the quantity of picloram excreted in the urine, only a small fraction (0.2%) of the picloram applied to the skin was absorbed. These data indicate that picloram because of its rapid excretion has a low potential to accumulate in man during repeated or prolonged exposures. In addition, picloram was poorly absorbed through human skin and it is unlikely that acutely toxic quantities will be absorbed by this route.

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