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Bromeliad living in canopy of tropical and cloudy forest has little or none dependency for 
acquire nutrients from soil. Some elements are essential for survival, so an efficient adaptive strategies 
for trapping and accumulate elements directly from air moisture and particles are developed to 
assurance the availability of nutrients, even is periods of scarcity. Some nutrients naturally abundant on 
environment, derived from rainfall, deposition of particulates and falling debris on dossel, are required 
to growth and physiological requirements. Bromeliads tank body-types is a structural adaptation for 
capturing and assimilation of elements dissolved in rainwater and uptake falling organic debris (Oliveira, 
2004), and others specialized structure that facility the absorbing of water and nutrients load, as 
specialized scales around surface leaf to increasing area to bulk ratio to humidity and suspended particle 
matter ( ). Essential and available nutrients as phosphorus are needed to consumption to current 
metabolism, taken up by developing bromeliads leaves or reallocate to reserve (Winkler & Zotz, 2009). 
On this way, chemical composition in bromeliads reflects the atmospheric conditions in tropical forest, 
as seen in conservation units (Elias et al. 2008). Besides, bromeliads without or less interation with soil 
developed the CAM Metabolic Pathway, an adaptive response to allow economic nutrients and water 
application to generate ATP and biomass, to ensure the survival on tropical forest dossel ( ). 
In spite of different preference to acquisition of nutrients and pollutants from air because of 
nutritional requirements, others vegetal than bromeliads have been employee to monitoring 
environment quality in vicinity of industrial sources and well-know polluted megacities around world, 
transport of toxic elements by wind currents (Saiki 2001) or chlorosis and necrosis indicators to ozone 
and fluorine emission in lichens (Klumpp et al., 2001), and also through Tobacco leaves (Domingos et 
al, ), as well as micromorphological signal in pollen of Tradescantia genus exposed these same pollutants 
() and Lolium genus (). Biomonitoring range of wind-transport to contaminants includes pristine areas, 
priorities do conservation efforts (). In studies of monitoring air polluting Tillandsia genus are most used 
worldwide, whereas transplant of Tillandsia usneoides have been employee in urban localities (Viana et 
al., 2001; Figueiredo et al, 2007) and in mining tailing exposed to wind (Pitassi et al., 2009), and inside 
chloro-alcali plants (Olaf & Malm, 1997). Collecting of others native bromeliads species showed be 
useful to generate available data reflecting field exposure to contamination from atmospheric route, 
through the accumulation of trace elements (Cortés, 2004; Graciano et al., 2003; Elias et al., 2008) and 
physiological responses to injuries (Gonzalo & Pignata, 2011; Pignata et al. 2010). 
The advantage of introducing bromeliads to monitoring purpose is estimating the degree of 
deposition of chemical contamination and so on quantitative estimates of chemical concentration, 
though the results obtained not measure total exposure along the period, only a relative concentration 
(Steinnes, 1995). Some limitations the complexity of types of chemical linkages of trace and major 
elements inner of tissues of bromeliads leaves featuring the difference of the capacity of retention and 
accumulation along the time. As well as chemical affinity, the reallocation of elements through vegetal
body varies for each bromeliad species, accumulation in mature leaves. For example, both 
macronutrients Ca and K, show different mobility and preferences between young-mature leaves. In the 
other hand, Zn and Fe are less abundant on medium, but required to regulatory functions in vegetal and 
enriched in older parts of vegetal. The Br is not-essential, so show small concentration in leaves tissues, 
such as not well-defined distribution pattern between the tissues (Elias et al., 2009). 
Researching about useful species of tropical epiphyte as standard tolls for monitoring impacts 
from natural and anthropogenic atmospheric input of trace-metal in Mata Atlântica region was 
demonstrated with the bromeliad Canistropsis billbergioides (L.). C. billbergioides was collected to 
monitoring pollutants derived-wind transport, through chemical contents accumulates in tissues (Elias 
et al. 2005). A diversity of bromeliads can be found in Mata Atlântica biome in Ilha Grande, Southern 
coast of Rio de Janeiro State, in according to Nunes-Freitas et al. (2009). Chemical determination of 
leaves of bromeliads collected in Ilha Grande therefore can be interesting to understanding the actual 
degree of wind-transport impact from continent sources of trace and major elements in some places 
along Ilha Grande coast. The actual results of deposition in bromeliads leaves from previous surveys in 
Ilha Grande can be compared to detecting temporal variation and, if possible, these causes related to 
some anthropogenic or natural, punctual or diffuse local or continental sources. Furthermore, was 
sampled some genus of tropical bromeliads tissues to know better about differentiation on efficiency of 
assimilation of metals, for environmental air route from distant or local source, and can be identified 
better tool for air pollution monitoring survey. In according to Zamboni-Mello et al (2008), south-coast 
of Ilha Grande is impacted by transport of air pollution because high levels recorded for some trace 
elements comparing to baseline concentration of others localities. On this way, content of airborne 
matter in vegetal tissues features variance on anthropogenic metal in relation to distance for known 
fixed and mobile source on continent that can employee to characterization of impact degree and also 
tested to be used in future air monitoring programs. 
Elias, C.; De Nadai Fernandes, E. A.; França, E. J.; Bacchi, M. A. 2005. Bromélia epífita 
Canistropsis billbergioides acumuladora de elementos químicos para biomonitoração na Mata Atlântica 
Elias C., Fernandes E. A. N., França E. J., Bacchi M. A. 2009. Chemical Changes in Bromeliads 
Leaves at Different Vegetative Stages. Journal of Radioanalytical and Nuclear Chemistry, v. 282, (1), p. 
111-115
Elias C., E. A. N. Fernandes, França E. J., Bacchi M. A., Tagliaferro F. S. 2008. Native Bromeliads as 
Biomonitors of Airborne Chemical Elements in a Brazilian Resting Forest. Journal of Radioanalytical and 
Nuclear Chemistry, v. 278, (2), 423-427 
Bermudez G. M. A. and Pignata M. L. 2011. Antioxidant Response of Three Tillandsia Species 
Transplanted to Urban, Agricultural, and Industrial Areas. Archives of Environmental Contamination and 
Toxicology, v. 61, (3), 401-413.

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Bromelias especializacoes

  • 1. Bromeliad living in canopy of tropical and cloudy forest has little or none dependency for acquire nutrients from soil. Some elements are essential for survival, so an efficient adaptive strategies for trapping and accumulate elements directly from air moisture and particles are developed to assurance the availability of nutrients, even is periods of scarcity. Some nutrients naturally abundant on environment, derived from rainfall, deposition of particulates and falling debris on dossel, are required to growth and physiological requirements. Bromeliads tank body-types is a structural adaptation for capturing and assimilation of elements dissolved in rainwater and uptake falling organic debris (Oliveira, 2004), and others specialized structure that facility the absorbing of water and nutrients load, as specialized scales around surface leaf to increasing area to bulk ratio to humidity and suspended particle matter ( ). Essential and available nutrients as phosphorus are needed to consumption to current metabolism, taken up by developing bromeliads leaves or reallocate to reserve (Winkler & Zotz, 2009). On this way, chemical composition in bromeliads reflects the atmospheric conditions in tropical forest, as seen in conservation units (Elias et al. 2008). Besides, bromeliads without or less interation with soil developed the CAM Metabolic Pathway, an adaptive response to allow economic nutrients and water application to generate ATP and biomass, to ensure the survival on tropical forest dossel ( ). In spite of different preference to acquisition of nutrients and pollutants from air because of nutritional requirements, others vegetal than bromeliads have been employee to monitoring environment quality in vicinity of industrial sources and well-know polluted megacities around world, transport of toxic elements by wind currents (Saiki 2001) or chlorosis and necrosis indicators to ozone and fluorine emission in lichens (Klumpp et al., 2001), and also through Tobacco leaves (Domingos et al, ), as well as micromorphological signal in pollen of Tradescantia genus exposed these same pollutants () and Lolium genus (). Biomonitoring range of wind-transport to contaminants includes pristine areas, priorities do conservation efforts (). In studies of monitoring air polluting Tillandsia genus are most used worldwide, whereas transplant of Tillandsia usneoides have been employee in urban localities (Viana et al., 2001; Figueiredo et al, 2007) and in mining tailing exposed to wind (Pitassi et al., 2009), and inside chloro-alcali plants (Olaf & Malm, 1997). Collecting of others native bromeliads species showed be useful to generate available data reflecting field exposure to contamination from atmospheric route, through the accumulation of trace elements (Cortés, 2004; Graciano et al., 2003; Elias et al., 2008) and physiological responses to injuries (Gonzalo & Pignata, 2011; Pignata et al. 2010). The advantage of introducing bromeliads to monitoring purpose is estimating the degree of deposition of chemical contamination and so on quantitative estimates of chemical concentration, though the results obtained not measure total exposure along the period, only a relative concentration (Steinnes, 1995). Some limitations the complexity of types of chemical linkages of trace and major elements inner of tissues of bromeliads leaves featuring the difference of the capacity of retention and accumulation along the time. As well as chemical affinity, the reallocation of elements through vegetal
  • 2. body varies for each bromeliad species, accumulation in mature leaves. For example, both macronutrients Ca and K, show different mobility and preferences between young-mature leaves. In the other hand, Zn and Fe are less abundant on medium, but required to regulatory functions in vegetal and enriched in older parts of vegetal. The Br is not-essential, so show small concentration in leaves tissues, such as not well-defined distribution pattern between the tissues (Elias et al., 2009). Researching about useful species of tropical epiphyte as standard tolls for monitoring impacts from natural and anthropogenic atmospheric input of trace-metal in Mata Atlântica region was demonstrated with the bromeliad Canistropsis billbergioides (L.). C. billbergioides was collected to monitoring pollutants derived-wind transport, through chemical contents accumulates in tissues (Elias et al. 2005). A diversity of bromeliads can be found in Mata Atlântica biome in Ilha Grande, Southern coast of Rio de Janeiro State, in according to Nunes-Freitas et al. (2009). Chemical determination of leaves of bromeliads collected in Ilha Grande therefore can be interesting to understanding the actual degree of wind-transport impact from continent sources of trace and major elements in some places along Ilha Grande coast. The actual results of deposition in bromeliads leaves from previous surveys in Ilha Grande can be compared to detecting temporal variation and, if possible, these causes related to some anthropogenic or natural, punctual or diffuse local or continental sources. Furthermore, was sampled some genus of tropical bromeliads tissues to know better about differentiation on efficiency of assimilation of metals, for environmental air route from distant or local source, and can be identified better tool for air pollution monitoring survey. In according to Zamboni-Mello et al (2008), south-coast of Ilha Grande is impacted by transport of air pollution because high levels recorded for some trace elements comparing to baseline concentration of others localities. On this way, content of airborne matter in vegetal tissues features variance on anthropogenic metal in relation to distance for known fixed and mobile source on continent that can employee to characterization of impact degree and also tested to be used in future air monitoring programs. Elias, C.; De Nadai Fernandes, E. A.; França, E. J.; Bacchi, M. A. 2005. Bromélia epífita Canistropsis billbergioides acumuladora de elementos químicos para biomonitoração na Mata Atlântica Elias C., Fernandes E. A. N., França E. J., Bacchi M. A. 2009. Chemical Changes in Bromeliads Leaves at Different Vegetative Stages. Journal of Radioanalytical and Nuclear Chemistry, v. 282, (1), p. 111-115
  • 3. Elias C., E. A. N. Fernandes, França E. J., Bacchi M. A., Tagliaferro F. S. 2008. Native Bromeliads as Biomonitors of Airborne Chemical Elements in a Brazilian Resting Forest. Journal of Radioanalytical and Nuclear Chemistry, v. 278, (2), 423-427 Bermudez G. M. A. and Pignata M. L. 2011. Antioxidant Response of Three Tillandsia Species Transplanted to Urban, Agricultural, and Industrial Areas. Archives of Environmental Contamination and Toxicology, v. 61, (3), 401-413.