Comparison of biosorption and phytoremediation of cadmium and methyl parathion, a case-study with live Lemna gibba and Lemna gibba powder.

Heavy metals and pesticides can be adsorbed by several biomasses such as living or non-living aquatic plants. In this study adsorption properties of live Lemna gibba and Lemna gibba powder were investigated with regard to cadmium and methyl parathion (MP). Toxicity data (IC50) on live L. gibba indicated that the period of four days was adequate for phytoremediation. Initial adsorption studies showed that both adsorbents were capable of removing cadmium and methyl parathion. Cadmium and methyl parathion adsorption onto L. gibba powder was fast and equilibrium was attained within 120min. The adsorption data could be well interpreted by the Freundlich model. The KF were: 7.8963 (Cd(2+)/ live Lemna); 0.7300 (MP/live Lemna); 11.5813 (Cd(2+)/Lemna powder); 1.1852 (MP/Lemna powder) indicating that Cd(2+) was more efficiently removed by both biosorbents than MP. Adsorption kinetics for cadmium and methyl parathion in both systems and rate constants were determined for each contaminant. It was found that the overall adsorption process was best described by pseudo-second-order kinetics. Boyd model and external mass-transfer expression were tested. It was concluded that cadmium and methyl parathion sorption onto Lemna powder is governed by film diffusion.

Toxicity of copper/dimethomorph combination for Lemna minor and depuration of the fungicides by aquatic plant.

Runoff-water of Champagne vineyards is often collected in decantation ponds where pesticides may be eliminated before the water is transferred to rivers. In order to accelerate this process, Lemna minor was tested for its phytoremediation capacity. In the ponds several pesticides coexist. Therefore, the cross-influence of copper and dimethomorph, two pesticides frequently used on grape to control fungal diseases, was studied on toxicity and their removal by L. minor. The toxicity of copper and dimethomorph alone and in combination, was assessed by growth inhibition of L. minor cultures after 96 h and 168 h. Copper had a severe impact on growth (maximum inhibition: 90% at 1000 microg/L) while dimethomorph (as pure ingredient DMM(P) or formulated as Forum DMM(F)) did not (inhibition < 45% at 1000 microg/L) after 168 h of treatment. When both chemicals were combined, a synergistic effect was detected after 96 h of exposure to copper and DMM(F). However, this interaction tended towards additivity after 168 h. Additivity was also observed when DMM(P) replaced DMM(F) in the mixture of copper and dimethomorph at 96h00 and 168h00. The removal of copper depended on DMM(F) concentration. For example, with 250 microg/L of dimethomorph as Forum, removal of copper increased from 36 to 41%. Depuration of DMM(F) by L. minor varied between 10 and 40% after 96 h. This depuration decreased in the presence of copper possibly due to the metal toxicity.

Leaching of terbumeton and terbumeton-desethyl from mini-columns packed with soil aggregates in laboratory conditions.

Leaching of terbumeton (TER) and terbumeton-desethyl (TED) from mini-columns packed with natural soil aggregates was investigated. Five soil samples from the Champagne area (France) with different physicochemical parameters were used. The soil samples were hand-packed into a 50 mm column in laboratory conditions. An aqueous solution of TER or TED was percolated through the column and collected effluents were analyzed for TER or TED using HPLC-DAD. The leaching experiments showed that TER and TED were moderately mobile. TED was more mobile than TER, possibly because of its higher polarity. The proportion of organic matter affected the mobility of TER and TED through soil columns (r=0.971) and leaching was lowest for soil having the highest organic matter content (5.9%). TER and TED were not significantly influenced by leaching solution composition (deionized water or CaCl(2) solution), but were strongly affected by soil packing. Packing resulted in less rapid release of compounds suggesting that unpacking may have contributed to preferential pathways through the soil columns. Increasing contact time between TER and soils before leaching decreased the mobility of TER and increased its persistence in soils. Indeed, 76% of TER was released when leaching started after a 15 h contact time whereas it was down to 26% after an aging treatment of 360 h. A proportion of TER (from 8% to 32%) and TED (from 8% to 17%) remained in soil. Associated to its high stability in soils this could in part account for a very slow transfer over the years towards the groundwater.

Daily variations in the sensitivity of soybean seedlings to low temperature.

Every 4 hr during a time span of 32 hr and of 76 hr a different group of soybean seedlings [Glycine max (L.) Merr., cv. Corsoy] maintained under a regime of 16 hr of light followed by 8 hr of darkness was exposed to -10 degrees C for 4 min. Extent of sensitivity to low temperature was evaluated approximately 10 days after exposure to freezing temperature by determining the weight of the plants and chlorophyll content of the cotyledons. The amount of sensitivity to low temperature was related to the time of exposure and displayed a significant 24-hr oscillation. Plants appeared to be least sensitive to cold injury during the late portions of the light span. Plants subjected to water stress were less sensitive to cold and no significant 24-hr oscillation in response to low temperature could be detected by the cosinor method of analysis.

Glutathione-S-transferase activity of Fucus spp. as a biomarker of environmental contamination.

Coastal zones are important areas from both ecological and economical points of view. However, in the last decades, in several regions of the globe, they have been increasingly impacted by complex discharges of contaminants and by marine traffic accidents. The Portuguese Atlantic coast is particularly exposed to these contaminants due to the proximity of important navigation routes. Several rocky shore organisms have been tested and used as bioindicators of environmental contamination. However, to the best of our knowledge Fucus spp., which are key species in rocky shore communities, have not been used as bioindicators in monitoring studies based on biomarkers. The objective of this study was to investigate the potential of glutathione-S-transferase (GST) activity of several Fucus species (Fucus ceranoides, Fucus spiralis var. platycarpus, Fucus spiralis var. spiralis and Fucus vesiculosus var. vesiculosus) to discriminate sites with different contamination levels along the Portuguese Northwestern coast, between the Minho river estuary and the Aveiro's Lagoon, as an environmental biomarker. With the exception of F. spiralis var. spiralis, for which a confusing pattern of activity was found requiring further analysis, all the other species and varieties showed higher GST levels in more contaminated sites than in less contaminated ones, indicating that Fucus spp. are suitable for use as bioindicators and their GSTs as biomarkers of environmental contamination in coastal zones and estuaries.

Phytotoxicity of diuron alone and in combination with copper or folpet on duckweed (Lemna minor).

The photosystem II-herbicide diuron is widely used for weed control in Champagne's vineyards. Its important use and its relative persistence make it of particular interest for ecotoxicological studies. Toxicity of diuron was assessed on Lemna minor L., a representative aquatic macrophyte regularly used for toxicological studies. Toxicity assessments were based on inhibition of growth and total chlorophyll content of L. minor cultures after 7 days. Growth was inhibited and IC(50) and IC(90) were, respectively, 25 and 60 microg l(-1), but chlorophyll content of L. minor increased in response to the herbicide. When diuron was combined with copper, growth inhibition of L. minor depended on the concentrations of both chemicals. For some concentrations, combination of these chemicals resulted in a slight (but non-significant) antagonism. Additivity was observed for all other mixtures. When diuron was combined with folpet, growth and chlorophyll content of L. minor only depended on the concentration of the herbicide. Diuron was also found to prevent the copper-induced decrease of chlorophyll content when it was combined with this metal. A multifactorial model was found more appropriate to characterize interactions between pesticides than Abott's model.

Effects of procymidone, fludioxonil and pyrimethanil on two non-target aquatic plants.

Procymidone, fludioxonil, and pyrimethanil are widely used to control the pathogenic fungus Botrytis cinerea in Champagne's vineyards. These fungicides may end up in surface waters and present potential risks for aquatic vascular plants and algae. Therefore, their toxicity was evaluated on Lemna minor and Scenedesmus acutus in six-day or 48-h tests, respectively. Based on growth and chlorophyll (Chl) content of L. minor and S. acutus cultures, the results showed that the alga was the most sensitive to the fungicides. Among the fungicides, pyrimethanil was the most toxic for L. minor, its nominal IC50 was 46.16 mg l(-1) and that of the other two was >100 mg l(-1). In contrast, pyrimethanil appeared the least toxic for S. acutus at low concentration, nominal IC50 were 22.81, 4.85, and 4.55 mg l(-1) for pyrimethanil, fludioxonil, and procymidone, respectively. Fate of the fungicides in the media was also investigated and acute toxicity of the agrochemicals is discussed in regard to concentration in the culture media. Poor solubility of procymidone and fludioxonil appeared to be partly responsible for the low toxicity of these fungicides. Based on these toxicity data and the concentrations found in ponds collecting vineyard runoff water, these pesticides should not impair the establishment of pioneer plants.

Metallothionein induction in the aquatic oligochaete Tubifex tubifex exposed to the herbicide isoproturon.

Metallothioneins (MTs), are low molecular weight proteins, mainly involved in metal ion detoxification. Recently it has been demonstrated that MTs participate in several cellular functions such as regulation of growth, and anti-oxidative defenses. Moreover, pesticides can induce their synthesis. The aim of the current work was to determine the effects of isoproturon either pure or formulated as Matin (suspension containing 500 g x l(-1) isoproturon) on the metallothionein and total protein content of the aquatic worm Tubifex tubifex. MT levels in exposed worms increased significantly after 7 and 15 days of exposure to 50 mg x l(-1) of herbicide. Isoproturon reduced metal (Cu, Zn, and Cd) content of metallothioneins, and it also increased total protein content of the worms. The results suggest that MT induction may not be considered as a specific biomarker of metal exposure but it can be used as a non specific biomarker of isoproturon effect in the worm.

Cold sensitivity oscillations of young soybean plants.

Every 4 hr, a different group of soybean seedlings (Glycine max [L.] Merr. cv. Corsoy), maintained in a controlled environment chamber (LD 16:8), were briefly subjected to cold (-10 degrees C for 4 min). Ten days after the beginning of the cold treatment, plants were harvested, weighed, and their cotyledons assayed for chlorophyll. In other experiments, potassium levels of the foliage were monitored. Both the sensitivity of plants to cold and the potassium content of unifoliolate leaves not subjected to cold displayed a significant 24-hr oscillation. Less injury and the lowest level of potassium occurred near the end of the light span. Cotyledon chlorophyll levels again were shown to be a good indicator of injury, with the highest levels in the most severely injured plants.

Toxic responses and catalase activity of Lemna minor L. Exposed to folpet, copper, and their combination.

Toxicity of copper and folpet--two fungicides widely used on grape--was evaluated on Lemna minor L., a sensitive aquatic weed regularly used for (eco)toxicological studies. Toxicity assessments were based on inhibition of growth and chlorophyll content of L. minor cultures after 7 days. IC10, IC50, and IC90 were determined for both compounds alone and were respectively, 0.03, 0.16, and 0.95 mg liter-1 for copper and 1.20, 7.50, and > 40 mg liter-1 for folpet. When both compounds were combined, the response of L. minor depended on the initial folpet concentration. Indeed, a slight synergy was observed for 5 mg liter-1 folpet, while at folpet concentrations of 20 to 35 mg liter-1, the two fungicides were antagonists. The antagonism was positively correlated with folpet concentration. Antagonism between Cu and folpet could not be explained by a reduced bioavailability of Cu since concentration of free copper in the mixture did not depend on the presence of folpet. One physiological defense response elicited by copper in plants is an increase in catalase activity. Copper and folpet stimulated catalase activity and changes in the activity of the enzyme could not account for the synergy but possibly for the antagonism. Nevertheless, catalase activity increase significantly after a 24-h exposure to 25 micrograms liter-1 of copper. The use of this property as a rapid and sensitive biomarker to monitor the toxicity of xenobiotics alone or in combination and of environmental water is discussed.

Biological effects of two insecticides on earthworms (Lumbricus terrestris L.) under laboratory conditions.

Earthworms (Lumbricus terrestris L.) were exposed to endosulfan and aldicarb for 2, 7, and 15 days and lethal concentrations were determined. Worms were then exposed to these concentrations (LC10, LC25, and LC50) of endosulfan and (LC10 and LC25) of aldicarb. Growth rate, total protein content, and insecticide residues were determined. Aldicarb was more toxic than endosulfan and both insecticides caused a significant reduction of growth rate and total protein content of earthworms. Residues remaining in the soil after 2 to 15 days ranged between 37.75% and 68.54% of applied concentration for endosulfan and between 10.13% and 67.71% of applied concentration for aldicarb. Less than 1% of soil concentration was detected in worms and accumulation was more important in the case of endosulfan. This study proposes the use of growth rate and total protein content as biomarkers for contamination by endosulfan and aldicarb.

Fate and sublethal effects of isoproturon on mature earthworm (Lumbricus terrestris L.).

This study was conducted to investigate the effects of isoproturon in mature earthworm (Lumbricus terrestris L.) under laboratory condition. Earthworms were exposed to soils contaminated with different concentrations for various duration. Residues were monitored in soil and earthworms after 7, 15, 30, 45, and 60 days of exposure to different isoproturon concentrations. Acute toxicity of isoproturon was determined together with growth rate and total soluble protein content of worms. These parameters were related to isoproturon concentration in soil and earthworms. No lethal effect of isoproturon was observed even at the highest concentration tested (1.4 g/kg soil) after 60 days after treatment. Residues of isoproturon have caused a significant reduction of the growth rate. Additionally a reduction of total soluble protein was observed in all treated worms. Decrease of isoproturon concentration in soil was slow and depended on herbicide initial concentration. In the worms, it increased during the first 15 days and decreased thereafter. This study is suggesting the use of the growth rate of earthworms as biomarker of exposure to isoproturon.

Metallothionein induction in aquatic oligochaete tubifex tubifex exposed to herbicide isoproturon.

Metallothioneins (MTs) are low-molecular-weight proteins mainly involved in metal ion detoxification. Recently it has been demonstrated that MTs participate in several cellular functions such as regulation of growth and antioxidative defenses. Moreover, pesticides can induce their synthesis. The aim of the current work was to determine the effects of isoproturon, either pure or formulated as Matin (suspension containing an isoproturon concentration of 500 g. L(-1)), on the metallothionein and total protein contents of the aquatic worm Tubifex tubifex. MT levels in exposed worms increased significantly after 7 and 15 days of exposure to a concentration of the herbicide of 50 mg. L(-1). Isoproturon reduced the metal (Cu, Zn, and Cd) content of metallothioneins, and it also increased the total protein content of the worms. These results suggest that MT induction may not be considered a specific biomarker of metal exposure but that it can be used as a nonspecific biomarker of the effect of isoproturon effect in aquatic worms.