Influence of cobalt uptake by Vicia faba seeds on chlorophyll morphosis induction, SOD polymorphism, and DNA methylation.

Vicia faba plants show polymorphism to cobalt (Co) excess, expressed by a different degree of chlorophyll morphosis (CM)-from normally green (N) to yellow (Y) seedlings. For superoxide dismutase (SOD), the high V. faba polymorphism was revealed and increased by Co stress. Epigenetic mechanisms may be involved in both phenomena. For such reasons, we investigated the effect of 5-azacytosine (AzaC) and Na butyrate (NaBut) on CM induction, SOD polymorphism, and DNA methylation-demethylation events in Co(NO(3) )(2) affected plants, without or with AzaC or NaBut. CMs were induced after treatment of seeds for 8 h with 7.5 mM Co(NO(3) )(2) plus 12 h with H(2) O or 8 h with H(2) O plus 12 h with Co(NO(3) )(2) . In the same order AzaC and NaBut were applied in concentrations equimolar to Co(NO(3) )(2) . SOD isoforms were investigated electrophoretically, and for DNA methylation-demethylation events the Aina [Aina et al. (2004) Physiol Plant 121:472-480] system was applied upon using the random amplified polymorphic DNA (RAPD) method employing restrictases MspI and HpaII. The effect of AzaC and NaBut on CM induction in combination with Co was unclear. Posttreatment with Co was more effective than Co-pretreatment. SOD polymorphism was significantly strengthened by NaBut. Detection of DNA methylation-demethylation events depended on the primers used for RAPD analysis. With AP5 and MP4 primers, DNA demethylation was observed in N-seedlings after exposure to Co, AzaC or NaBut applied separately. With primer A6, only DNA methylation events were determined in N-seedlings from seeds exposed to Co or Co-AzaC, and in Y-seedlings after Co-AzaC or Co-NaBut treatment. UPGMA grouping of the results showed that all N-seedlings comprised one common cluster after Co exposure, independently of treatment combinations (Co alone, Co with AzaC, Co with NaBut). On the contrary, no significant differences were determined in SOD polymorphism among the most resistant N-seedlings and the most severely affected Y-seedlings.

The Butterfly Effect: Mild Soil Pollution with Heavy Metals Elicits Major Biological Consequences in Cobalt-Sensitized Broad Bean Model Plants.

Among the heavy metals (HMs), only cobalt induces a polymorphic response in Vicia faba plants, manifesting as chlorophyll morphoses and a 'break-through' effect resulting in the elevated accumulation of other HMs, which makes Co-pretreated broad bean plants an attractive model for investigating soil pollution by HMs. In this study, Co-sensitized V. faba plants were used to evaluate the long-term effect of residual industrial pollution by examining biochemical (H2O2, ascorbic acid, malondialdehyde, free proline, flavonoid, polyphenols, chlorophylls, carotenoids, superoxide dismutase) and molecular (conserved DNA-derived polymorphism and transcript-derived polymorphic fragments) markers after long-term exposure. HM-polluted soil induced a significantly higher frequency of chlorophyll morphoses and lower levels of nonenzymatic antioxidants in Co-pretreated V. faba plants. Both molecular markers effectively differentiated plants from polluted and control soils into distinct clusters, showing that HMs in mildly polluted soil are capable of inducing changes in DNA coding regions. These findings illustrate that strong background abiotic stressors (pretreatment with Co) can aid investigations of mild stressors (slight levels of soil pollution) by complementing each other in antioxidant content reduction and induction of DNA changes.

Soil-surface genotoxicity of military and urban territories in Lithuania, as revealed by Tradescantia bioassays.

The soil surface is a major natural system that accumulates pollutants and allows researchers to disclose the history and the present state of contamination of an area with toxic pollutants. This conclusion is based on the comparison of genotoxicity of aqueous extracts and DMSO extracts of topsoil from military territories in various locations left behind after the retreat of the Soviet Army from Lithuania, and several sites in the city of Vilnius, characterized by different history and current traffic intensity. The specific character of the soil-surface contamination was shown in a series of Tradescantia micronucleus (Trad-MN) and stamen-hair mutation (Trad-SHM) bioassays and tests. The most effective ones were the Trad-MN and, unexpectedly, the branched-hair tests. A preliminary result of the study is the somaclonal variation of individual Tradescantia plants revealed by the RAPD method of DNA analysis. A comparison of aqueous extracts and DMSO extracts of the soil showed the permanent character of the mobile forms of genotoxic pollutants in the soil surface, despite the fact that several military territories were already closed 20 years ago.

Cyto/genotoxicological evaluation of hot spots of soil pollution using Allium bioassays in relation to geochemistry.

Soil from industrial and landfill sites affected by anthropogenic activity was screened for implicit negative effects in an Allium test-system in relation to geochemistry. The concentrations of 15 elements were compared to the ecotoxicologically-based soil guideline values. Admitted geoindices were used to classify test-soils according to risk/hazard categories. Test-soils were screened for the possible deleterious effects in common onion (Allium cepa L.) by employing a test battery of cytogenetic bioassays (root growth inhibition, mitotic activity, frequency of chromosome aberrations and micronuclei, and cell death rate) complemented with two assays of molecular DNA markers, random amplified polymorphic DNA (RAPD) and inter-simple sequence repeat (ISSR). Soil from industrial sites was more severely polluted and more cytotoxic for onions compared to soil from landfill sites. However, the cyto/genotoxic outcome of soil exposure in A. cepa was the same for all test-soils; the detrimental effects were observed in onions treated with every test-soil. Thus, test-soils could not be classified as non- and genotoxic, although certain of them had permissible contamination levels. The chromosome aberration frequency and cell death rates were consistent with the intensity of soil contamination, contrary to the micronuclei rate, which was independent of the soil risk/hazard level. Despite a relationship between risk (RI) and total soil contamination (Z) geoindices, both indices correlated with a different Allium cyto/genotoxicity endpoint, although the Z index was preferred over the RI index as being more informative in correlation analysis. Allium bioassays complemented each other by depicting different aspects of exposure to toxic substances, and determination of cyto/genotoxicity in a battery of different bioassays is important in the risk assessment of ecologically dangerous soils, and an application of a test battery is strongly advised.

Response of Tradescantia plants to oxidative stress induced by heavy metal pollution of soils from industrial areas.

Numerous investigations have demonstrated that even soil in which concentrations of individual elements do not exceed permissible limits can cause harmful effects in living organisms. In the present study, polluted-soil-induced oxidative stress was evaluated using Tradescantia clone 4430, which is widely used for genotoxicity evaluations, employing biochemical (superoxide dismutase (SOD), contents of ascorbic acid (AA), carotenoids (Car), hydrogen peroxide (H2O2), chlorophyll (Chl) a/b ratio), and molecular (RAPD and differential display (DD-PCR)) markers after long-term exposure. The activity (staining intensity) of SOD isoforms in Tradescantia leaves was higher in plants grown in all heavy-metal-polluted test soils compared to the control. No direct link between the soil pollution category and the contents of AA, Car, Chl a/b in Tradescantia leaves was revealed, but the concentration of H2O2 was shown to be a sensitive biochemical indicator that may appropriately reflect the soil contamination level. Both short-term (treatment of cuttings with H2O extracts of soil) and long-term (0.5 and 1.0 year) exposure increased MN frequencies, but the coincidence of the MN induction and the soil pollution level was observed only in some cases of long-term exposure. Soil (geno)toxin-induced polymorphism in the RAPD profile was determined with two primers in plants after long-term exposure to soils of an extremely hazard category. Transcript profiling of plants after long-term cultivation in test soils using DD-PCR showed that the majority of differentially expressed transcript-derived fragments (TDFs) were homologous to genes directly or indirectly participating in photosynthesis, the abiotic stress response, and signal transduction cascades.

Metal bioaccumulation and mutagenesis in a Tradescantia clone following long-term exposure to soils from urban industrial areas and closed landfills.

Soil mutagens, particularly metals, may persist long after the source of pollution has been removed, representing a hazard to plants, animals, and humans in or near contaminated areas. Often, due to urban growth, previous land uses may be forgotten and hazards overlooked. We exposed Tradescantia clone #4430 plants to soil from two industrial areas (with different former uses) and two urban waste landfills in the city of Vilnius, all of which were long disused. Two modes of exposure were used: long-term exposure of growing plants in test soils for 0.5 or 1.0y, and short-term exposure of cuttings to water and dimethyl sulfoxide (DMSO) soil extracts. An increased frequency of micronuclei (MN) was observed with both modes of exposure. The concentrations of 24 metals and other elements were analyzed in the test soils and in above-ground plant parts, under both exposure modes, and the concentration coefficients (Cc) for various elements, the total contamination index (Zs) for soils and plants, and the bioaccumulation factor (BAF) for plants were calculated. These measurements allow a comparison of the contamination levels of soils and plants with equalized values. Metal accumulation levels in plants and soils showed significant differences, providing a better understanding of the genotoxicity of soils from closed landfills and highlighting the need to determine the concentrations of metals and other genotoxicants in plants in relation to genotoxicity.

Use of Tradescantia clone 4430 for direct long-term soil mutagenicity studies.

Soil mutagens permanently and directly affect terrestrial plants, soil microorganisms and invertebrates and indirectly impact vertebrate and human populations. However, the dynamic response to soil mutagens under conditions of long-term exposure has been studied insufficiently. The clonal nature of Tradescantia #4430 and the well-developed associated test systems for evaluation of genotoxicity allow investigation of the permanent effects of direct exposure to the soil not only on plants of the same genotype, but even with the same individual plants, as was done in the present study. Twenty soil samples of different origin were studied in Tradescantia after 0.5, 1 and 2 years of direct exposure to the soil, in order to examine the induction of pink cells (PC), colorless cells (CC) and branched hairs (BH). Additionally, after 0.5 years, micronucleus (MN) formation was assessed, and after 1 year, the variation of random amplified polymorphic DNA (RAPD) markers was evaluated. Nine soil samples were of urban origin, and the others came from different soils from former military grounds. The results of the 0.5-year exposure were compared with the effects of aqueous/DMSO extracts tested in previous work. The long-term exposure period allowed not only a better differentiation of the soils within territories, but also permitted detection of differences between soils of urban and military origin. The results also depended on the test used to evaluate genotoxicity. The 'burst' phenomenon, consisting of a sudden increase of BH variation and, especially, of CC, was observed only in tests of samples from several military sites, mainly after a 2-year exposure. MN formation was less frequent after 0.5 years of exposure compared with the results from aqueous extracts, and this difference was highly significant. The variation of the RAPD markers in a significant portion of the soil samples coincided with a higher level of variation according to other tests (PC, CC, BH), but predicting the genotoxicity of the soils based on their elemental soil composition at the end of the experiment was impossible. At several points where a 'burst' was observed, the concentration of a number of elements was lower. A cumulative effect is hypothesized to explain these observations. Tradescantia clone #4430 is the most suitable system for such studies.