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For this reason, to expand our knowledge of the role of DMA in the soil, the influence of this As form on plant survivability as well as on the phytoextraction of other As forms or other elements, it is necessary to examine the unique toxic properties Acer AIM 3.0 CH-7007 DMA. Information about inorganic compounds has dominated in investigations of As in soils, whereas organic As compounds, which are sometimes found as minor components of soil, can also reach high concentrations Singh et al. Methylated As forms have been detected, e.

DMA was the second most common organic As species after arsenobetaine, AsB in the forest floor, up to 0. Abedin et al. A similar concentration-dependent influx of DMA and well-described uptake by the model Acer AIM 3.0 CH-7007 above was shown for rice Oryza sativa L.

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There is evidence that DMA is a highly mobile form within the plant, more effectively translocated from root to the shoots than other As forms Faroog et al. Raab et al. High rates of DMA readily translocated from roots to shoots were also described, e.

Higher translocation of DMA can be explained by the lack of a complex with thiols such as phytochelatin PC formation Raab et al. Plants were characterized by their biomass and concentration of particular As forms and calcium Capotassium Kmagnesium MgAcer AIM 3.0 CH-7007 sodium Na in roots, stems, and leaves of seedlings. Additionally, analyses of boron B and silicon Si content, elements important in As III transport and also phosphorus P and sulfur Sand elements crucial in As V transport were performed.

Presence of DMA in the environment can be an important factor limited to survivability of studied young tree species and finally their use in phytoremediation practice. Two-year-old leafless seedlings of A. Norway maple and T.

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All seedlings were planted in the experiment in such a way that the mean biomass of plants growing in a particular experimental system was almost the same. Experiment design Seedlings of A.

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During this time, each plant was watered with the same amount of deionized water. Afterwards, the plants were washed with distilled water to remove soil particles from the root systems.

The plants were then dried with paper towels and weighed to estimate their biomass before the experiment. One plant was placed in one pot. Seven experimental systems control; DMA0.

The mean values of temperature, moisture, and concentration of CO2 were Acer AIM 3.0 CH-7007 The plants were automatically watered with deionized water during the experiment to provide seedlings with the support of a similar mean level of the solution. Addition of water in this way allowed us to limit evapotranspiration and an extreme increase of DMA presence in the space of roots. Sample preparation and biomass analysis At the end of the experiment, seedlings of Acer AIM 3.0 CH-7007 tree species were carefully washed with deionized water, dried with paper towels, and divided into parts roots, stems, and leaves to estimate their final biomass and calculate the percentage biomass increase during the experiment. Plant parts from particular experimental systems were then ground for 0.


Accurately weighed 0. The arsenic species and total As concentration were determined immediately after the extraction procedure.


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