Toxicity Of Soil Samples Research Articles

Enzymatic Activity and Its Relationship with Organic Matter Characterization and Ecotoxicity to Aliivibrio fischeri of Soil Samples Exposed to Tetrabutylphosphonium Bromide.

This study aimed to determine the impact of tetrabutylphosphonium bromide [TBP][Br] on the soil environment through an experiment on loamy sand samples. The tested salt was added to soil samples at doses of 0 (control), 1, 10, 100, and 1000 mg kg−1 dry matter (DM). During the experiment, the activity of selected enzymes involved in carbon, phosphorus, and nitrogen cycles, characteristics of organic matter with Fourier-transform infrared (FT-IR) spectroscopy, and toxicity of soil samples in relation to Aliivibrio fischeri were determined at weekly intervals. The results showed that low doses of [TBP][Br] (1 and 10 mg kg−1 DM) did not have much influence on the analyzed parameters. However, the addition of higher doses of the salt into the soil samples (100 and 1000 mg kg−1 DM) resulted in a decrease in the activity of enzymes participating in the carbon and phosphorus cycle and affected the activation of those enzymes involved in the nitrogen cycle. This may be due to changes in aerobic conditions and in the qualitative and quantitative composition of soil microorganisms. It was also observed that the hydrophobicity of soil organic matter was increased. Moreover, the findings suggested that the soil samples containing the highest dose of [TBP][Br] (1000 mg kg−1 DM) can be characterized as acute environmental hazard based on their toxicity to Aliivibrio fischeri bacteria. The increased hydrophobicity and ecotoxicity of the soil samples exposed to the tested salt were also positively correlated with the activity of dehydrogenases, proteases, and nitrate reductase. Observed changes may indicate a disturbance of the soil ecochemical state caused by the presence of [TBP][Br].

Autotoxicity of the soil of consecutively cultured tea plantations on tea (Camellia sinensis) seedlings

The production and quality of Tie-Guan-Yin tea (Camellia sinensis) decrease with time after continuous picking over multiple years. However, it is unclear how the soils of consecutively cultured tea plantations affect the growth of tree seedlings. In this study, soil samples were collected from 4-, 9-, and 30-age Tie-Guan-Yin plantations within the original production area, Longjuan town, Anxi County, China. The toxicity of soil samples were tested by laboratory bioassay. Then, new tea seedlings were transplanted in situ into the land of three age tea plantations. One year after transplantation, the growth indexes, physiological parameters (protective enzymes and primary metabolites), photosynthesis parameters, and main tea quality indicators were measured. The results showed that the 4-, 9-, and 30-age soils inhibited lettuce root growth by 10.32, 24.19, and 48.04 %, respectively. The consecutively cultured soil negatively impacted on the growth, physiology, photosynthesis, and overall quality of transplanted tea seedlings. For example, seedlings grown in the 30-age soil had 20 % lower growth rates, 17 % less soluble sugar, 28 % less soluble protein, 37 % less polyphenol, 34 % less theanine, 25 % less amino acid, 37 % less caffeine, and 40 % less of eight catechols than tea seedlings grown in new soil with no history of tea production. These results indicated that the soils of consecutively cultured tea plantations resulted in significant autotoxicity which negatively affected tea seedling growth, metabolism, tea yield, and tea quality. Greater understanding of the causes and mechanisms of autotoxicity is critical to the reclamation of longstanding tea plantation and improvement of the yield and quality of the tea they produce.

Bioassays for evaluating the water‐extractable genotoxic and toxic potential of soils polluted by metal smelters

Physicochemical analyses of polluted soils are limited in their ability to determine all hazardous compounds, their bioavailability, and their combined effects on living organisms. Bioassays, on the other hand, can evaluate environmental quality more accurately. This study assesses the genotoxic potential of water extracts from soil polluted with metals (Pb, Cd, and Zn) by the former lead smelter in zerjav, Slovenia using comet assay with Tetrahymena thermophila and human hepatoma cells (HepG2). In addition, the toxicity of soil samples and their extracts was evaluated using Vibrio fischeri and delayed fluorescence of Lemna minor. Chemical analyses of metals using atomic absorption spectrophotometry (AAS) was performed for comparison. Measurements of the total metal concentrations showed that four of five plots near the former lead smelter were highly contaminated with Pb, Cd, and Zn, but the amount of metals in water/soil extracts was low at all the sampling plots. Genotoxicity was demonstrated using T. thermophila for the majority of the extracts, and HepG2 cells for only some of the extracts. Whereas V. fischeri indicated a gradual decrease in soil toxicity with greater distance from the smelter, the toxicity of extracts did not correlate with proximity. Low concentrations of metals in water extracts stimulated L. minor growth. The results indicate that comet assay with T. thermophila and HepG2 cells and the BSPT with V. fischeri are suitable protocols for screening the genotoxic and toxic potential of water/soil extracts by comet assay, whereas chemical analyses of total metal concentrations in soil do not solely suffice for evaluating metal pollution in the environment. Biological assays are thus crucial for risk assessment.

Microbial Toxicity Tests and Chemical Analysis as Monitoring Parameters at Composting of Creosote-Contaminated Soil

Traditionally, chemical analyses are used in the assessment of contaminated soil and in monitoring the efficiency of soil remediation processes. We investigated if chemical analysis could be supported and even partly replaced by biological toxicity tests. In two case studies creosote-contaminated soil was composted outdoors in 5- and 100-m 3 windrows. Degradation of polyaromatic hydrocarbons (PAHs) was followed by chemical analysis and toxicity tests. Polyaromatic hydrocarbons were quantified and idenfitifed by HPLC. Because the soil was also contaminated by copper-, chromium-, and arsenic-containing fungicides, these elements were analyzed by atomic absorption spectrometry. The toxicity of soil samples was assessed by a soil-contact modification of the luminescent bacteria ( Vibrio fischeri) test and in the other case also by enzyme synthesis inhibition (Toxi-ChromoPad test, Escherichia coli). The toxicity of soil water extracts was measured by the standard luminescent bacteria ( V. fischeri) test and bacterial ( Pseudomonas putida) growth inhibition test. After the first 4 months of the composting period the total amount of PAHs was reduced in all windrows, and in particular, the loss of two- and some three-ring compounds was high, almost 90%. Toxicity decreased concurrently with the decrease in PAH concentration during composting, but after 4 months, one of the piles inoculated with mycobacteria and containing more three- and four-ring compounds was found to be more toxic than at the beginning. After the next summer, total PAH content was further reduced but some four-ring or heavier compounds were demonstrated to be poorly degraded. The toxicity was also reduced to the same level as in the control pile. The total PAH content and the toxicity were both reduced significantly during 5 months of composting

The toxicity of soil samples containing TNT and other ammunition derived compounds in the enchytraeid and collembola-biotest

The effect of ammunition-like compounds and armament waste on the mortality and reproduction of terrestrial invertebrates was assayed by using two biotests: the enchytraeid-biotest with Enchytraeus crypticus and the collembola-biotest with Folsomia Candida. Toxicity was investigated by using standard soil (Lufa 2.2) spiked with 2,4,6-trinitrotoluene (TNT), hexahydro-l,3,5-trinitro-l,3,5-triazine (hexogen, RDX), octahydro-l,3,5,7-tetranitro-l,3,5,7-tetrazocine (octogen, HMX) and 2,4,6-triaminotoluene (TAT). Ecotoxicity was investigated with ammunition-contaminated soil material from the former ammunition plant "Tanne" at Clausthal-Zellerfeld (CTNTla) and the Brandplatz (incineration site) in Torgau-Elsnig (TETNT1a), Germany. TNT increased mortality and reduced reproduction of both test organisms corresponding to the concentrations used, whereas hexogen, octogen and TAT had no effect in the tested concentrations (1000-2000 mg/kg). From the two soil materials, TETNT1a was much more toxic than CTNT1a. The LC50(7d) in the enchytraeid-biotest was 570 mg TNT/kg and the EC50(28d) 369 mg TNT/kg soil material (dw). In the collembola-biotest the LC50(7d) was 185 mg TNT/kg and the EC50(28d) 110 mg TNT/kg soil matter (dw).

Evaluation and application of aquatic toxicity tests: use of the Microtox test for the prediction of toxicity based upon concentrations of contaminants in soil

The quality control for the reuse of cleaned soil from a contaminated site consisted in the determination of the main contaminants by analytical chemical methods such as GC and HPLC. Since it is not possible to analyze for all contaminants a toxicity test should be used to detect large concentrations of not routinely analyzed chemicals. The aim of the study was to develop a system for toxicity testing, which should be able to predict the toxicity of soil samples based on the concentration of chemicals in the soil and to detect toxic chemicals not analyzed by the routinely conducted soil analysis. Based upon the relative sensitivity to various contaminants as well as practical aspects such as test duration and costs the Microtox® test was favoured over the bioassays with Daphnia magna and Scenedesmus subspicatus. The Microtox® test was used to measure the toxicity of various pesticides and their major metabolites. The toxicity data of the pure compounds were used to predict the toxicity (EC50 and % inhibition of the bioluminescence reaction) of defined mixtures of chemicals in water by applying two different mathematical appriaches which are based on the additivity of the effects of the single chemicals. The predicted values were compared with the experimental data and showed good agreement. In order to be able to predict the toxicity of soil samples using the Microtox® test the soil/water partition coefficient (K d) was measured for the main contaminants. The toxicity of soil samples was predicted by calculating the concentration of the contaminants in the leachate by using the corresponding concentration in the soil and applying the K d values determined. From the calculated composition of the leachate the expected toxicity was estimated. This value was compared with the toxicity experimentally determined in the Microtox® test.