Non-observed Effect Level Research Articles

Gene expression and morphological responses of Lolium perenne L. exposed to cadmium (Cd2+) and mercury (Hg2+)

Soil contamination with heavy metals is a major problem worldwide, due to the increasing impact mainly caused by anthropogenic activities. This research evaluated the phytoremediation capacity of, Lolium perenne for heavy metals such as cadmium (Cd2+) and mercury (Hg2+), and the effects of these metals on morphology, biomass production, and the changes on gene expression. Seeds of L. perenne were exposed to six concentrations of Cd2+ and Hg2+ in the range of 0 to 25 mg L−1, and two mixtures of Cd2+–Hg2. The Non-Observed Effect Level (NOEL) was established with dose response curves and the expression of specific genes was evaluated applying a commercially available quantitative reverse transcription (RT-qPCR) assay. There was no significant effect when exposing the seeds to Hg2+, for Cd2+ the maximum concentration was established in 0.1 mg L−1, and for the two concentrations of mixtures, there was a negative effect. An increase of expression of genes that regulate antioxidant activity and stress was found when the plant was exposed to heavy metals. Given the high tolerance to metals analyzed that was reflected both, the development of the plant and in its molecular response, these results highlight that L. perenne is a plant with phytoremediator potential.

Detection and Prioritization of Developmentally Neurotoxic and/or Neurotoxic Compounds Using Zebrafish.

The standard methods for toxicity testing using rodent models cannot keep pace with the increasing number of chemicals in our environment due to time and resource limitations. Hence, there is an unmet need for fast, sensitive, and cost-effective alternate models to reliably predict toxicity. As part of Tox21 Phase III's effort, a 90-compound library was created and made available to researchers to screen for neurotoxicants using novel technology and models. The chemical library was evaluated in zebrafish in a dose-range finding test for embryo-toxicity (ie, mortality or morphological alterations induced by each chemical). In addition, embryos exposed to the lowest effect level and nonobservable effect level were used to measure the internal concentration of the chemicals within the embryos by bioanalysis. Finally, considering the lowest effect level as the highest testing concentration, a functional assay was performed based on locomotor activity alteration in response to light-dark changes. The quality control chemicals included in the library, ie, negative controls and replicated chemicals, indicate that the assays performed were reliable. The use of analytical chemistry pointed out the importance of measuring chemical concentration inside embryos, and in particular, in the case of negative chemicals to avoid false negative classification. Overall, the proposed approach presented a good sensitivity and supports the inclusion of zebrafish assays as a reliable, relevant, and efficient screening tool to identify, prioritize, and evaluate chemical toxicity.

USING OF THYMUS VULGARIS EXTRACTS TO CONTROL THE SNAIL VECTOR IN SCHISTOSOMIASIS (Part II)

The aim of this study is to determine the toxicity of Thymus Vulgaris aquatic plant extracts comparing with copper sulfates against Bulinus truncatus the vector of urinary Bilharziasis. Samples of the snails were collected from a site in Al-Rasheed district (30 km) southern of Baghdad. The isolation, identification, and acclimatization made in the laboratory. Many toxic parameters as NOEL (Non-Observed Effect Level), Threshold, EC (Effective Concentration) and LC (Lethal Concentration) levels were determined in this study. The EC50 of T. vulgaris and Copper sulfates to B. truncatus were (8.4, and 0.9g/L) respectively. The LC50 of T. vulgaris and Copper sulfates to B. truncatus were (18.7, and 2.2 g/L) respectively. The study showed that the T. vulgaris extracts were less effective than CuSO4. The results improved that the toxicity of extracts was concentration and time dependent. This work concluded the ability to use the target extracts in control of snails the middle host of the cause of urinary Schistosomiasis.

Chemical carcinogenesis - mode of action to inform quantitative human risk.

Chemical carcinogenesis - mode of action to inform quantitative human risk.

Time-Dependent Toxicity of Neonicotinoids and Other Toxicants:Implications for a New Approach to Risk Assessment

A fundamental goal of toxicology is to determine safe levels of exposure to potentially poisonous substances for humans and the environment. Traditionally, safe levels have been estimated in laboratory toxicity bioassays by calculating the non-observable effect level (NOEL) of a chemical to a variety of organisms which are representative of certain taxa, i.e. mammals, birds, fish, crustaceans, algae, etc. There are, however, fundamental problems with the validity of this approach, both conceptual and statistical in nature, as indicated by Landis and Chapman and other authors. Thus, the outdated NOEL concept is being replaced by the no-effect concentration (NEC) level, which assumes that toxic chemicals do not have any effect on a population of organisms at very low concentrations.

Boron removal by membrane processes

Boron has been widely distributed in the environment, in most cases at low concentrations. Due to its detrimental effect on the reproducibility of living organisms, the European Union stipulates the maximum admissible value for the concentration of boron at 1 ppm and the World Health Organisation at 0.3 ppm as the non-observed effect level (NOEL) for drinking water. The aim of this work is the boron removal by membrane processes, in particularly the evaluation of the effect of nanofiltration and reverse osmosis membranes, as their coupling was also studied on the elimination of boron. The RO and NF tests were carried out with the use of an Osmonics spiral module equipped with AG 2514 TF and HL 2514T membranes respectively. Using conventional membranes, significant removal of boron has been observed only in its ionic form. Our experimental results indicated that boron rejection mostly depends upon membrane type, pH level, and to a lesser extent on the recovery. More detailed analysis of the above-mentioned...

Value of GST-P Positive Preneoplastic Hepatic Foci in Dose-Response Studies of Hepatocarcinogenesis: Evidence for Practical Thresholds with Both Genotoxic and Nongenotoxic Carcinogens. A Review of Recent Work

Recent low-dose carcinogenesis studies, including major group projects are reviewed. The prevailing paradigm is that carcinogens, particularly genotoxic compounds, have no threshold in exerting their potential for cancer induction. However, the nonthreshold hypothesis can be challenged for cancer risk assessment in humans. A recent very large-scale cooperative effort in Japan furthermore showed that the genotoxic hepatocarcinogen, 2-amino-3,8-dimethylimidazo[4,5-f]quinoxaline, forms DNA adducts and 8-hydroxy-2'-deoxyguanosine at low doses, but does not induce glutathione S-transferase placental form (GST-P) positive foci as preneoplastic lesions in rat liver (< or = 10 ppm in diet). Moreover, very low doses of a N-nitroso compound. diethylnitrosamine (DEN), were also found not to significantly induce GST-P positive foci in rat liver (< or = 0.01 ppm in drinking water). Given the direct correlation between induction of the preneoplastic lesions in the short-term and carcinomas in the longer term with different carcinogens, the results imply a practical nonobserved effect level for hepatocarcinogenicity. Similar results were also observed with so-called nongenotoxic carcinogens such as phenobarbital (PB) and p,p-dichlorodiphenyltrichloroethane (DDT), which do not exert positive effects on lesion development at very low doses. Furthermore, experiments with application of PB and DDT after treatment with DEN indicate that at very low doses (< or = 2 ppm in diet), they may even inhibit the development of GST-P positive foci. The data reviewed provide evidence that preneoplastic foci in the liver can be employed as end-point lesions in place of tumors and that exposure to very low levels of carcinogens, typical of those found in the human environment, does not necessarily present as a risk factor.

Immunotoxicological investigation in rats dosed repeatedly with combinations of cypermethrin, As(III), and Hg(II)

The effects of the combined exposure of cypermethrin (CY), NaAsO 2 (As), and HgCl 2 (Hg) were investigated in male Wistar rats following 4 weeks of oral exposure. Standard toxicological (body weight gain, organ weights of brain, thymus, heart, lung, liver, kidneys, adrenals, testes, and popliteal lymph node), haematological (white blood cell, red blood cell, haematocrit, MCV-mean volume of red blood cells, and cell content of the femoral bone marrow), and immune function (IgM-PFC response, delayed type hypersensitivity (DTH) reaction) parameters were measured. The two doses selected for the combination were: a high (H) dose equal to lowest observed effect level determined in preliminary experiments (CY(H)=55.4 mg/kg, As(H)=13.3 mg/kg, Hg(H)=3.20 mg/kg), and a low (L) dose which was ineffective (non-observed effect level); CY(L)=11.1 mg/kg, As(L)=3.33 mg/kg, Hg(L)=0.40 mg/kg). CY(H) was combined with As(L) or Hg(L), and the H doses of the heavy metals were combined with CY(L). Beside vehicle control, the H dose components of the combinations were also used as internal controls. The main finding of this study was that certain combinations, when compared to H dose internal control, significantly altered the body weight gain (As(H)+CY(L)), the relative weight of adrenals and popliteal lymph node (CY(H)+As(L) and CY(H)+Hg(L)), the cell content of the femoral bone marrow (CY(H)+Hg(L)), and the time course of DTH reaction (CY(H)+As(L)). According to the present results, combined exposure with CY and the heavy metals investigated can modify the toxicity and/or the functional detection limit of the single substances.

Influence of pH in the elimination of boron by means of reverse osmosis

The European Union (EU) stipulates the maximum admissible value for the concentration of boron at 1 ppm and the World Health Organization (WHO) at 0.3 ppm as the non-observed effect level (NOEL) for drinking water. The content of boron in water can be reduced by means of various processes. Treatment by means of conventional reverse osmosis only reduces the boron content by 60%. This paper analyzes the possibility of treating the permeate water in a way that increases the pH.

Immunotoxicological investigations on rats treated subacutely with dimethoate, As3+ and Hg2+ in combination.

Effects of combined exposure with dimethoate (DM), HgCl2 (Hg), and NaAsO2 (As) were investigated following a 28 - day oral exposure in male Wistar rats. In preliminary experiments, the LOEL (Lowest Observed Effect Level) and NOEL (Non Observed Effect Level) doses of the substances were determined using the same experimental system [determination of body weight gain, organ weights of brain, thymus, heart, lung, kidneys, adrenals, spleen, testicles, popliteal lymph node, white blood cell (WBC) and red blood cell (RBC) count, haematocrit (Ht), mean cell volume (MCV) of RBCs, cell content of the femoral bone marrow, IgM-plaque forming cell (PFC) content of the spleen, delayed type hypersensitivity (DTH) reaction] and animal strain. In the combination studies, LOEL dose of DM (28.2 mg/kg) was combined with NOEL doses of the heavy metals ( HgCl2 = 0.40 mg/kg, NaAsO2 = 3.33 mg/kg), and vice versa (DM = 7.04 mg/kg, HgCl2 = 3.20 mg/kg, NaAsO2 = 13.3 mg/kg). In the DM-Hg combinations, significant alterations were found versus the corresponding high- dose internal control in the body weight gain, relative liver and kidney weights, and in the PFC response. When DM was combined with As, interactions were indicated by changes of relative liver weight, MCV value, and the PFC content of the spleen. These results support the theory that the interactions between pesticides and heavy metals may modify the toxic effects of the single substances, and may also change the functional detection limits of the exposure. The changes in the functional detection limits, if they occur, can lead to false-positive and false-negative results in human epidemiological studies.

Dose-dependent induction of carcinomas and glutathione S-transferase placental form negative eosinophilic foci in the rat liver by di(2-ethylhexyl)phthalate after diethylnitrosamine initiation.

The dose-dependence of di(2-ethylhexyl)phthalate (DEHP) hepatocarcinogenicity was investigated in male F344 rats which were initially injected with diethylnitrosamine (200 mg/kg, i.p.) and subjected to partial hepatectomy at week 3. The animals were administered DEHP in the diet at concentrations of 30, 300, 3,000, or 12,000 ppm starting 2 weeks after the DEN injection for up to 46 weeks and killed at weeks 8, 24, 48 and 52. Additional groups were given clofibrate (3,000 ppm in diet) or basal diet instead of the DEHP diet. Incidences of hepatocellular carcinomas were 75% (9/12, P < 0.01) for 12,000 ppm, 10% (1/10) for 3,000 ppm, 7% (1/14) for 300 ppm, 0% (0/13) for 30 ppm, 15% (2/13) for clofibrate, and 8% (1/13) for the basal diet group at week 52, 4 weeks after cessation of chemical feeding. Development of glutathione S-transferase placental form (GST-P) positive foci was only slightly increased by clofibrate-administration at week 52 and consistently lower than the control level in the DEHP-treated groups after 24 weeks. In contrast, GST-P negative eosinophilic foci were dose-dependently increased in the more than 300 ppm DEHP and clofibrate treated groups. At the 30 ppm dose level, however, no morphological changes were apparent in the liver. Thus, the non-observed effect level regarding the promotional activity of hepatocarcinogenesis was demonstrated at 30 ppm, the effects being predictable on the basis of development of GST-P negative eosinophilic foci.

Toxicity study of a rubber antioxidant, 2-mercaptobenzimidazole, by repeated oral administration to rats.

The chemical structure of 2-mercaptobenzimidazole (2-MBI), which is widely used as a rubber antioxidant, is partially similar to those of thiourea (TU) and ethylenethiourea (ETU), both potent thyrotoxic compounds. In order to determine the oral toxicity of 2-MBI, a 28-day repeated dose toxicity study in Wistar rats followed by observation over a 14-day recovery period was conducted at dose levels of 2, 10 and 50 mg/kg 2-MBI administered by gavage. No toxic deaths occurred due to 2-MBI treatment. Decreases of body weight gain and food consumption in the 50 mg/kg dose group were observed during the second half of the treatment period. In addition, hematological examination and serum biochemical tests revealed decreased white blood cells and hemoglobin and increased serum urea nitrogen, cholesterol, phospholipid, gamma-glutamyl transpeptidase and the Na+/K+ ratio in the 50 mg/kg dose group. Marked thyroid enlargement (to 10 fold the control weight), histopathologically associated with diffuse hyperplasia of follicles with decreased colloid and thickening of the fibrous capsule, was found. Reduction in thymus weight was also observed in a dose-dependent manner, without significant histopathological alteration. The non-observed effect level (NOEL) of 2-MBI in this gavage study was found to be less than 2 mg/kg/day based on the significant decrease in thymus weight in the 2 mg/kg 2-MBI treatment group. In an ancillary study, measurement of serum levels of T3, T4 and TSH, and thyroid weight after gavage treatment with 0.15 and 0.3 mmol/kg of three antithyroid compounds for 14 days revealed a more potent antithyroid effect for 2-MBI than for TU or ETU.

Role of fibre characteristics on cytotoxicity and induction of anaphase/telophase aberrations in rat pleural mesothelial cells in vitro: correlations with in vivo animal findings.

Thirteen samples of natural fibres and five samples of man-made fibres (MMF) were tested to determine their cytotoxicity and ability to produce chromosome missegregation in cultures in rat pleural mesothelial cells (RPMC). The natural samples included attapulgite, two amphiboles (amosite and crocidolite); seven consisted of chrysotile from various origins and three were obtained after chemical treatment of chrysotile. MMF included three refractory ceramic fibres (RCF) and two vitreous fibres (MMVF). All fibre samples were characterized by electron microscopic measurement of the fibre dimensions. Cytotoxicity was assayed on the basis of determination of mitochondrial integrity and chromosome missegregation by light microscopy examination of anaphases/telophases. The carcinogenic potency of 10 natural samples has been previously investigated using intrapleural inoculation in rats. It was therefore possible to establish correlations between in vitro and in vivo data obtained with the same set of samples. The various samples of chrysotile produced different in vitro effects, in agreement with the dispersion of response also observed in vivo. Cytotoxicity appears to be dependent on both fibre length and fibre diameter, as the longest or thickest fibres were the most toxic. The production of abnormal anaphases/telophases appears to depend on the presence of fibres of selected size, such as those previously defined by Stanton et al. (L > 8 micrograms; D < or = 0.25 microns); a threshold values was determined below which no abnormal anaphases/telophases were detected. This non-observable effect level was estimated to be 2.5 x 10(5) 'Stanton' fibres per cm2. There was no correlation between cytotoxicity and mesothelioma induction; in contrast, a correlation was found between the ability of a sample to produce chromosome missegregation in vitro and mesothelioma in vivo.