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Introducción: La minería de oro a cielo abierto ocasiona impactos drásticos sobre los bosques naturales en regiones tropicales de alta biodiversidad, y la eficiencia de "revegetación", un proceso de resembrar y reconstruir el suelo, continúa siendo poco estudiado. Objetivo: Evaluar el efecto del tiempo sucesional y la distancia al bosque de referencia sobre la estructura biológica y composición de especies en minas de oro revegetadas. Métodos: Realizamos inventarios de vegetación en minas abandonadas en el bosque tropical lluvioso de Chocó, Colombia. Las minas contaban con 6, 10, 15, 19 y 24 años de sucesión natural. En cada escenario, establecimos cuatro parcelas de 2×50 m: a 50 m y 100 m de distancia desde el borde bosque-mina (ecotono). Resultados: Se identificaron 300 especies (193 géneros y 75 familias). La riqueza, diversidad y equitatividad cambian poco con el tiempo sucesional en las minas, pero alcanzan valores superiores en el bosque de referencia. La composición de especies es similar entre las minas con distinto tiempo sucesional, pero difiere ampliamente del bosque de referencia (solo 7 % de semejanza). La calidad del sustrato y las estrategias reproductivas de plantas herbáceas (principalmente Cyperaceae y Melastomataceae) y arbóreas (Cespedesia spathulata y Miconia reducens) que crecen espontáneamente en las minas, juegan un papel importante en la revegetación natural temprana. Conclusiones: 24 años de sucesión natural es poco tiempo para apreciar una recuperación sustancial de la vegetación en las minas si se compara con el bosque, y la distancia desde el ecotono parece no tener efecto significativo; sin embargo, la calidad de sustrato y estrategias reproductivas de plantas herbáceas son importantes en la etapa temprana de recuperación de las áreas impactadas por la minería de oro en Chocó.

Introduction: Open pit gold mining causes drastic impacts on natural forests in tropical regions of high biodiversity, and the efficacy of "revegetation", a process of replanting and rebuilding the soil, is still poorly studied. Objective: To evaluate the effect of successional time, and distance to the reference forest, on the biological structure and species composition of revegetated gold mines. Methods: We inventoried the adjacent forest and abandoned gold mines in the tropical rain forest of Chocó, Colombia. The mines had 6, 10, 15, 19 and 24 years of natural succession. In each scenario, we set four 2 × 50 m plots: two 50 m and two 100 m from the forest-mine edge (ecotone). Results: We identified 300 plant species (193 genera, 75 families). The richness, diversity and evenness changed little with successional time in the mines but reached higher values in the forest. The species composition was similar between the mines with different successional times but differed widely from the forest (only 7 % similarity). The substrate quality and reproductive strategies of herbaceous plants (mainly Cyperaceae and Melastomataceae) and trees (Cespedesia spathulata and Miconia reducens) that grow spontaneously in the mines, play an important role on the early natural revegetation. Conclusions: The 24 years of natural succession have been insufficient to reach a community of a complexity similar to that of the forest, and distance from the ecotone has no significant effect; however, the substrate quality and reproductive strategies of herbaceous plants are important in the early stages of mine recovery in the Chocó.

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Between 1984 and 1998, people living in Arica were involuntarily exposed to metal-containing waste stored in the urban area. The study aims to determine whether children who lived near the waste disposal site during early childhood experienced negative effects on their cognitive development. The cognitive performance was assessed using the Wechsler Intelligence Scale for Children. The exposure variable was defined by the year of birth in three categories: (1) Pre-remediation (born before 1999); (2) During-remediation (born between 1999 and 2003); and (3) Post-remediation (born after 2003). In the crude analysis, a difference of 10 points in the IQ average was observed between the group born in the pre- (81.9 points) and post-remediation period (91.1 points). The difference between both groups was five times higher as compared to children of similar age and socioeconomic status in other cities of Chile. This result could be related with a period of high potential for exposure to this contaminated site.

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Past studies have shown that tropical forest regeneration on degraded farmlands is initially limited by lack of seed dispersal, but few studies have tracked changes in abundance and composition of seed rain past the first few years after land abandonment. We measured seed rain for 12 months in 10 6-9-year-old restoration sites and five mature, reference forests in southern Costa Rica in order to learn (1) if seed rain limitation persists past the first few years of regeneration; (2) how restoration treatments influence seed community structure and composition; and (3) whether seed rain limitation is contingent on landscape context. Each restoration site contained three 0.25-ha treatment plots: (1) a naturally regenerating control, (2) tree islands, and (3) a mixed-species tree plantation. Sites spanned a deforestation gradient with 9-89% forest area within 500 m around the treatment plots. Contrary to previous studies, we found that tree seeds were abundant and ubiquitous across all treatment plots (585.1 ± 142.0 seeds · m(-2) · yr(-1) [mean ± SE]), indicating that lack of seed rain ceased to limit forest regeneration within the first decade of recovery. Pioneer trees and shrubs comprised the vast majority of seeds, but compositional differences between restoration sites and reference forests were driven by rarer, large-seeded species. Large, animal-dispersed tree seeds were more abundant in tree islands (4.6 ± 2.9 seeds · m(-2) · yr(-1)) and plantations (5.8 ± 3.0 seeds · m(-2) · yr(-1)) than control plots (0.2 ± 0.1 seeds · m(-2) · yr(-1)), contributing to greater tree species richness in actively restored plots. Planted tree species accounted for < 1% of seeds. We found little evidence for landscape forest cover effects on seed rain, consistent with previous studies. We conclude that seed rain limitation shifted from an initial, complete lack of tree seeds to a specific limitation on large-seeded, mature forest species over the first decade. Although total seed abundance was equal among restoration treatments, tree plantations and tree islands continued to diversify seed rain communities compared to naturally regenerating controls. Compositional differences between regenerating plots and mature forests suggest that large-seeded tree species are appropriate candidates for enrichment planting.

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This paper describes dose reconstruction for a joint Ukrainian-American case-control study of leukemia that was conducted in a cohort of 110,645 male Ukrainian cleanup workers of the Chornobyl (Chernobyl) accident who were exposed to various radiation doses over the 1986-1990 time period. Individual bone-marrow doses due to external irradiation along with respective uncertainty distributions were calculated for 1,000 study subjects using the RADRUE method, which employed personal cleanup history data collected in the course of an interview with the subject himself if he was alive or with two proxies if he was deceased. The central estimates of the bone-marrow dose distributions range from 3.7 × 10(-5) to 3,260 mGy, with an arithmetic mean of 92 mGy. The uncertainties in the individual stochastic dose estimates can be approximated by lognormal distributions; the average geometric standard deviation is 2.0.

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The oil from the 2010 Deepwater Horizon spill in the Gulf of Mexico was documented by shoreline assessment teams as stranding on 1,773 km of shoreline. Beaches comprised 50.8%, marshes 44.9%, and other shoreline types 4.3% of the oiled shoreline. Shoreline cleanup activities were authorized on 660 km, or 73.3% of oiled beaches and up to 71 km, or 8.9% of oiled marshes and associated habitats. One year after the spill began, oil remained on 847 km; two years later, oil remained on 687 km, though at much lesser degrees of oiling. For example, shorelines characterized as heavily oiled went from a maximum of 360 km, to 22.4 km one year later, and to 6.4 km two years later. Shoreline cleanup has been conducted to meet habitat-specific cleanup endpoints and will continue until all oiled shoreline segments meet endpoints. The entire shoreline cleanup program has been managed under the Shoreline Cleanup Assessment Technique (SCAT) Program, which is a systematic, objective, and inclusive process to collect data on shoreline oiling conditions and support decision making on appropriate cleanup methods and endpoints. It was a particularly valuable and effective process during such a complex spill.

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Recalcitrance and contamination in Mahogany (Swietenia macrophylla King) and Spanish cedar (Cedrela odorata L.) stem tissues are the main causes of its ineffective in vitro propagation. The objectives of this research were: a) to evaluate sodium hypochlorite (NaOCl) and plant preservative mixture (PPM®) as surface disinfectants and/or added to the culture medium for the in vitro establishment of nodal explants taken from 10-year-old Mahogany and Spanish cedar plants, and b) to evaluate the in vitro response of such explants treated with N6-benzylaminopurine (BAP) (0, 2.2, 4.4, 8.8, 17.7 μM), silver nitrate (AgNO3) (0, 3 mg l-1), activated charcoal (0, 1 g l-1) and vented caps. All the experiments were arranged in a completely randomized design. The NaOCl at 15%, for 20 min, as a surface sterilization or PPM® at 2 ml l-1 into the culture medium, were the best treatments to reduce contamination for both species. For Mahogany explants, BAP at 17.7 μM resulted in higher percentages of bud breaks than Spanish cedar (64% and 25%, respectively). Leaves on elongated shoots dropped off by 20 days after starting the explants in culture and neither the activated charcoal nor the AgNO3 alone or combined prevented leaf abscission. The AgNO3 decreased contamination, but also increased leaf abscission. Bud breaks was two-fold higher for nodal explants established in vessels with vented caps than with normal caps. Mahogany nodal explants were easier to surface sterilize and more buds broke from BAP treated explants than Spanish cedar treated explants in the in vitro establishment.

La contaminación y la recalcitrancia de tejidos de tallo de Caoba (Swietenia macrophylla King) y Cedro español (Cedrela odorata L.) son las causas principales de su inefectiva micro-propagación. Los objetivos de la investigación fueron: a) evaluar el hipoclorito de sodio (NaClO) y una mezcal preservadora de plantas (PPM®) como desinfectantes superficiales y/o agregados al medio de cultivo para el establecimiento in vitro de explantes nodales de Caoba y Cedro español de 10 años de edad; b) evaluar la respuesta in vitro de tales explantes tratados con N6-benzylaminopurine (BAP) (0, 2.2, 4.4, 8.8, 17.7 μM), nitrato de plata (AgNO3) (0, 3 mg l-1), carbón activado (0, 1 g l-1) y tapas porosas. Los experimentos fueron establecidos bajo un diseño completamente al azar. La contaminación se redujo en ambas especies con NaOCl al 15% durante 20 min como desinfección superficial o con PPM® (2 ml l-1) agregado al medio de cultivo. El mayor porcentaje de brotación de explantes se obtuvo con BAP a 17.7 μM en caoba (64%) comparado con cedro (25%). Los brotes se defoliaron a los 20 días de cultivo y ni el carbón activado ni el AgNO3, solos o combinados evitaron la defoliación. El AgNO3 disminuyó la contaminación, pero incrementó la defoliación. La brotación fue dos veces mayor en los explantes nodales establecidos en recipientes con tapas porosas que cuando se utilizaron tapas normales. Los explantes nodales de Caoba respondieron mejor a la desinfección superficial y a los tratamientos de BAP comparados con los de Cedro español en el establecimiento in vitro.

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