The natural Cu, Cr, Zn and Mn phytoaccumulation potential was screened for three widespread species, in the Constanta coastal area, Romania: Brassica rapa, Crambe maritima and Lepidium draba. Samples of aboveground organs and soil were...
moreThe natural Cu, Cr, Zn and Mn phytoaccumulation potential was screened for three widespread species, in the Constanta coastal area, Romania: Brassica rapa, Crambe maritima and Lepidium draba. Samples of aboveground organs and soil were taken for each species and analyzed for heavy metal concentration values. The Biological Accumulation Coefficients (BAC) was determined, in order to evaluate the phytoaccumulation potential. None of the three species surpassed the widely-accepted minimal thresholds for Cu, Cr, Zn and Mn hyperaccumulators. The highest average values, such as 42.7 ppm, for Cu (L. draba), 40 ppm, for Cr (Brassica rapa) 147.9 ppm, for Zn (C. maritima) and 26.9 ppm, for Mn (C. maritima) were registered. However, C. maritima and L. draba had BAC above 1 for Cu and Zn (L. draba, also for Cr), while B. rapa had a BAC of 2.75 for Cu and 2.73 for Cr showing a significant potential for metal accumulation. Heavy metals are not only important for Global industry, but they cause significant environmental and agricultural concern. Polluted soils make crops less productive or, even, unsafe for human consumption. These are the reasons why, during the past decades, much attention was given to phytoaccumulation and potential heavy metal hyperaccumulators. Heavy metals are toxic to plants. If excessive concentrations are present, metals accumulate in root cells, causing serious damage. However, many species have strategies to limit toxicity. One of them is exclusion of metal ions, meaning either a limitation of root uptake or a sequestration in root tissue, to prevent metal translocation to sensitive photosynthetic tissues. The other strategy is accumulation, with its extreme version, hyperaccumulation: metals are translocated and distributed across both underground and aboveground organs [1, 2]. Only around 0.2% of known plant species can be defined as hyperaccumulators (with metal concentrations 100-1,000 times higher than the average). However, their potential applications make them of great interest. Phytoextraction (metal extraction using plants) may have two main purposes: phytoremediation-removing heavy metals from polluted soils, through cropping and harvesting accumulator plants-and phytomining-generating revenue from exploiting otherwise sub-economic metal deposits [1, 2]. This is why finding potential hyperaccumulators in the native vegetation of each region is of great importance. The Brassicaceae family is very important from this point of view, many of the species with remarkable metal accumulating abilities belonging to this group: Thalaspi sp., Alyssum sp., Arabidopsis halleri, Streptanthus polygaloides, Brassica juncaea etc. [1]. The purpose of the current research was to determine the metals accumulation abilities of three Brassicaceae species, commonly growing in Romanian Black Sea coastal areas, as a part of a wider screening research for potential metal hyperaccumulators in this region. Brassica rapa L. subsp. oleifera (field mustard) is a well-known oleaginous plant (a source of canola oil) that is relatively often found growing spontaneously on the slopes bordering sandy beaches on the Romanian seaside. Crambe maritima L. (sea kale) is a halophile plant which grows on sandy beaches throughout temperate areas of Europe. Perennial, deciduous, it has a fleshy, massive, root system, thick stems and large glaucous leaves with crisped edges. White flowers are grouped in large inflorescences. The globulous seeds are easily dispersed by wind or water and vegetative reproduction can occur throught stem or root fragments. It is edible, cultivated as a garden vegetable in certain parts of the world [3]. Lepidium draba L. (syn. Cardaria draba; whitetop, or hoary cress), is a medium-sized perennial herb (10-80 cm tall), with an extensive horizontal root system, allowing vegetative reproduction. It has simple, toothed and alternating leaves. Small white flowers are grouped in compound corymb clusters, while silicles are small and heart-or egg-shaped. It is used for medicinal purposes in some regions, seed and leaf infusions having expectorant and purgative properties [4]. Experimental part Vegetal raw material (aboveground organs: shoots and leaves) was collected in June 2014 from the Trei Papuci and Modern beaches and surrounding areas, in Constanta county, Romania. The three plant species samples were taken from three different locations along this area. Also, from the same locations, a soil sample for each plant, was taken. Small pieces of vegetal organs and soil samples, were mineralized according to Shanker et al. and Burada et al. [5, 6]. Samples were oven dried at 80 o C for 3 days. 0.25 g of each sample were taken for analysis, digested overnight in 5 mL of HNO 3 67% concentration and boiled one hour at 150 o C. After cooling, 2 mL H 2 O 2 p.a. were added, followed by boiling at 150 o C for 2 h. Resulting solutions were diluted at 50 mL and NH 4 Cl 2% respective CaCl 2 0.5% were added, in order to reduce interference. Digested samples were analyzed using a HR-CS Atomic Absorption Spectrometer ContrAA700, Analytik Jena AG, Germany, with acetylene flame (acetylene-nitrous oxide flame, for Cr) at specific wavelengths for copper (324 nm),