A two-stage minibioreactor system for continuous toxicity monitoring.

A two-stage minibioreactor system was successfully developed for continuous toxicity monitoring. This system consists of two minibioreactors in series. Recombinant Escherichia coli DPD2794 containing a RecA::luxCDABE fusion as a model strain was utilized to monitor environmental insults to DNA, with mitomycin C as a model toxicant. Pulse type exposures were used to evaluate the system's reproducibility and reliability. Step inputs of mitomycin C have been adopted to show the system's stability. The system's ability to monitor the possible upsets or accidental discharges of toxic chemicals was also evaluated with these step insults. All the data demonstrated that this two-stage minibioreactor system using recombinant bacteria containing stress promoters fused with lux genes is quite appropriate for continuous toxicity monitoring. Long-term operation and minimized media-usage have been investigated. Thus application to many different areas, including an early warning system of wastewater biotreatment plant upsets and the monitoring and tracking of accidental spills, discharges or failures in plant operation are plausible.     

A whole cell bioluminescent biosensor for the detection of membrane-damaging toxicity

The recombinant bacteria strain DPD2540, containing afabA::luxCDABE fusion, was used to detect the toxicity of various chemicals in this study. Membrane damaging agents such as phenol, ethanol, and cerulenin induced a rapid bioluminescent response from this strain. Other toxic agents, such as DNA-damaging or oxidative-damaging chemicals, showed a delayed bioluminescent response in which the maximum peak appeared over 150min after induction. This strain was also tested for measurement of toxicity in field samples such as wastewater and river water effluents.     

Enhancing the sensitivity of a two-stage continuous toxicity monitoring system through the manipulation of the dilution rate.

Optimization of the dilution rates has been studied to provide an enhanced sensitivity to toxicity by several recombinant bioluminescent Escherichia coli strains, TV1061 (grpE::luxCDABE), DPD2794 (recA::luxCDABE) and DPD2540 (fabA::luxCDABE), in the two-stage continuous toxicity monitoring system. It was found that the sensitivity of both TV1061 and DPD2794 to a pulse injection of phenol and mitomycin C increased with a decrease in the dilution rate. The sensitivity, however, for all the strains to step injections of the toxic chemicals was found to increase with an increase in the dilution rate up to a certain dilution rate and then decreased, mainly due to the rapid washing out of the injected chemicals. The response kinetics of the strains were explained by evaluating the mode of action of the recombinant bioluminescent bacteria to toxicity with the dilution rate, the operating parameter of minibioreactors under consideration in this study.     

Evaluation of a high throughput toxicity biosensor and comparison with a Daphnia magna bioassay

A high throughput toxicity biosensor has been designed and constructed using recombinant Escherichia coli cells, containing stress specific promoters (recA, fabA, or katG) or constitutive promoters (lac) fused to luciferase genes originating from Vibrio fisheri. These genetically engineered cells were immobilized in 96 well plates. By optimizing cell immobilization conditions and the strains' response specificity to toxic chemicals, bioluminescent outputs decreased or increased dose-dependently upon adding test chemicals. However, to date the toxicity data obtained using this biosensor have not been compared with the results of other toxicity tests. Phenolics were chosen to evaluate the correlation between the LD50 and the EC50 (GC2) or EC120 (DPD2540) of Daphnia magna and E. coli, respectively. Toxicity data obtained from constitutive strains by bioluminescent level decrements were compared with the results from D. magna as a standard. LD50 values were used as parameters of D. magna toxicity and EC50 of EC120 values were used for the immobilized biosensor. In the DPD2540 test, phenolics, membrane damaging toxic chemicals, for testing immobilized stress specific bacterial strains trigger dose-dependant bioluminescence increase within specific concentration. Although the stress specific responsiveness from the strains could not be compared with D. magna's LD50 values, these responses offer additional information, such as upon the mode of toxic action in the sample, in addition to the cellular toxicity results as indicated by the EC50. This novel high throughput toxicity biosensor can be implemented to investigate the toxicity of any other soluble materials, and can be used as a standardization tool for the evaluation of toxicity.     

A bioluminescent sensor for high throughput toxicity classification

A high throughput toxicity monitoring and classification biosensor system has been successfully developed using four immobilized bioluminescent Escherichia coli strains, DPD2511, DPD2540, DPD2794 and TV1061, which have plasmids bearing a fusion of a specific promoter to the luxCDABE operon. The bioluminescence of DPD2511 increases in the presence of oxidative damage, DPD2540 by membrane damage, DPD2794 by DNA damage and TV1061 by protein damage. In the developed biosensor these strains are immobilized in a single 96 well plate using an LB-agar matrix, and are able to detect the toxicities of hydrogen peroxide, phenol and mitomycin C in water samples. As the concentration of each chemical was increased, the bioluminescence levels from the corresponding wells, containing either DPD2511, DPD2540, DPD2794 or TV1061, increased. This increase in bioluminescence followed a dose dependent response to the toxic chemicals within a specific concentration range. In particular, each test requires only 4 h to give clear bioluminescent response signature. Storage of the biosensor at 4 degrees C for 2 weeks caused no change in its dose-dependent response. The fast and easy detection of oxidative, membrane, protein and DNA damaging agents in aqueous environments is possible due to the high throughput capability of this biosensor.     

Soil biosensor for the detection of PAH toxicity using an immobilized recombinant bacterium and a biosurfactant

A biosensor for detecting the toxicity of polycylic aromatic hydrocarbons (PAHs) contaminated soil has been successfully constructed using an immobilized recombinant bioluminescent bacterium, GC2 (lac::luxCDABE), which constitutively produces bioluminescence. The biosurfactant, rhamnolipids, was used to extract a model PAH, phenanthrene, and was found to enhance the bioavailability of phenanthrene via an increase in its rate of mass transfer from sorbed soil to the aqueous phase. The monitoring of phenanthrene toxicity was achieved through the measurement of the decrease in bioluminescence when a sample extracted with the biosurfactant was injected into the minibioreactor. The concentrations of phenanthrene in the aqueous phase were found to correlate well with the corresponding toxicity data obtained by using this toxicity biosensor. In addition, it was also found that the addition of glass beads to the agar media enhanced the stability of the immobilized cells. This biosensor system using a biosurfactant may be applied as an in-situ biosensor to detect the toxicity of hydrophobic contaminants in soils and for performance evaluation of PAH degradation in soils.     

Toxicity monitoring of endocrine disrupting chemicals (EDCs) using freeze-dried recombinant bioluminescent bacteria

Five different freeze-dried recombinant bioluminescent bacteria were used for the detection of cellular stresses caused by endocrine disrupting chemicals. These strains were DPD2794 (recA::luxCDABE), which is sensitive to DNA damage, DPD2540 (fabA::luxCDABE), sensitive to cellular membrane damage, DPD2511 (katG::luxCDABE), sensitive to oxidative damage, and TV1061 (grpE::luxCDABE), sensitive to protein damage. GC2, which emits bioluminescence constitutively, was also used in this study. The toxicity of several chemicals was determined on the first four freeze-dried bacteria, while nonspecific cellular stresses were measured using GC2. Damage caused by known endocrine disrupting chemicals, such as nonyl phenol, bisphenol A, and styrene, was detected and classified according to toxicity mode, while others, such as phathalate and DDT, were not detected with the bacteria. These results suggest that endocrine disrupting chemicals are toxic in bacteria, and do not act via an estrogenic effect, and that toxicity monitoring and classification of some endocrine disrupting chemicals may be possible in the field using these freeze-dried recombinant bioluminescent bacteria.     

A portable toxicity biosensor using freeze-dried recombinant bioluminescent bacteria

A portable biosensor has been developed to meet the demands of field toxicity analysis. This biosensor consists of three parts, a freeze-dried biosensing strain within a vial, a small light-proof test chamber, and an optic-fiber connected between the sample chamber and a luminometer. Various genetically engineered bioluminescent bacteria were freeze-dried to measure different types of toxicity based upon their modes of action. GC2 (lac::luxCDABE), a constitutively bioluminescent strain, was used to monitor the general toxicity of samples through a decrease in its bioluminescence, while specific toxicity was detected through the use of strains such as DPD2540 (fabA::luxCDABE), TV1061 (grpE::luxCDABE), DPD2794 (recA::luxCDABE), and DPD2511 (katG::luxCDABE). These inducible strains show an increase in bioluminescence under specific stressful conditions, i.e. membrane-, protein-, DNA-, and oxidative-stress, respectively. The toxicity of a sample could be detected by measuring the bioluminescence 30 min after addition to the freeze-dried strains. In an attempt to enhance the sensitivity of the freeze-dried cells, glucose and Tween 80 were tested as additives. It was found that the addition of glucose had a negative effect on the viability of the freeze-dried cells, while samples having Tween 80 showed an increase in their viability. On the other hand, the addition of either Tween 80 or glucose decreased the final bioluminescent response of DPD2540 in response to 4-chlorophenol. Using these strains, many different chemicals were tested and characterized. This portable biosensor, with a very simple protocol, can be used for field sample analysis and the monitoring of various water systems on-site.     

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.     

Response of bioluminescent bacteria to sixteen azo dyes

Recombinant bioluminescent bacteria were used to monitor and classify the toxicity of azo dyes. Two constitutive bioluminescent bacteria,Photobacterium phosphoreum andEscherichia coli, E. coli GC2 (lac::luxCDABE), were used to detect the cellular toxicity of the azo dyes. In addition, four stress-inducible bioluminescentE. coli, DPD2794 (recA::luxCDABE), a DNA damage sensitive strain; DPD2540 (fabA::luxCDABE), a membrane damage sensitive strain; DPD2511 (katG::luxCDABE), an oxidative damage sensitive strain; and TV1061 (grpE::luxCDABE), a protein damage sensitive strain, were used to provide information about the type of toxicity caused by crystal violet, the most toxic dye of the 16 azo dyes tested. These results suggest that azo dyes result in serious cellular toxicity in bacteria, and that toxicity monitoring and classification of some azo dyes, in the field, may be possible using these recombinant bioluminescent bacteria.     

An integrated mini biosensor system for continuous water toxicity monitoring

An integrated water toxicity monitoring system that uses recombinant bioluminescent bacteria was successfully developed for the continuous monitoring and classification of toxicities present in water. This system consists of four channels arranged horizontally inside of a cylinder, with each channel having two small bioreactors that are vertically connected to each other to maintain a separation of the culture reactor from test reactor. This system is easily handled and installed, making its application in the field a potential reality. As well, it performed stably and continuously due to the vertical separation of the culture reactor from the test reactor and a long term operation was also performed because of its small working volume, i.e., only 1 ml for the 1st bioreactor and 2 ml for the 2nd. During an operation with four strains, i.e., EBHJ2, DP1, DK1 and DPD2794, which are responsive to superoxide damage (EBHJ2 and DP1), hydrogen peroxide (DK1), and DNA damage (DPD2794), the O.D. and bioluminescence of the bacterial cultures inside the system were constant when no chemical was injected. However, with the addition of paraquat, hydrogen peroxide or mitomycin C, the bioluminescent responses of the strains were found to be dose-dependent to different concentrations of these chemicals.     

Pharmacogenetic studies on the prediction of efficacy and toxicity of fluoropyrimidine-based adjuvant therapy in colorectal cancer

The cytotoxic effect of 5-fluorouracil (5-FU) is mediated by the inhibition of thymidylate synthase (TS), however, at the same time 5-FU is catabolized by dihydropyrimidine dehydrogenase (DPD). Efficacy of 5-FU may therefore depend on the TS and DPD activity and on pharmacogenetic factors influencing these enzymes. Our aims were (1) to determine the distribution of DPD activity, the frequency of DPD deficiency and the DPD (IVS14+1G>A) mutation in the peripheral blood mononuclear cells of colorectal cancer (CRC) patients, and study the relationship between DPD deficiency and toxicity of 5-FU; (2) to investigate the influence of TS polymorphisms and DPD activity on the survival of CRC patients receiving 5-FU-based adjuvant therapy. The frequency of DPD deficiency was determined by radiochemical methods in the peripheral blood mononuclear cells (PBMCs) of 764 CRC patients treated with 5-FU. The relationship between the TS polymorphisms, DPD activity and the disease-free and overall survival was studied in 166 CRC patients receiving 5-FU-based adjuvant therapy. TS polymorphisms were determined in the DNA samples separated from the PBMCs, by PCR-PAGE and PCR-RFLP-PAGE (restriction fragment length polymorphism) methods. Low DPD values (<10 pmol/min/106 PBMCs) were demonstrated in 160/764 patients (20.9%), and of those DPD deficiency (<5 pmol/min/106 PBMCs) was verified in 38 patients (4.9%). In the latter group severe (>Gr 3) toxicity was found in 87%. The prevalence of the DPD IVS14+1G>A mutation among the 38 DPD-deficient patients was 7.8% (3/38) and was accompanied by severe Gr 4 toxic symptoms (neutropenia, mucositis, diarrhea). TS polymorphisms showed a relationship with the survival of CRC patients. It is important to mention that by combining the 3-3 genotypes of 5'-TSER and 3'-TSUTR polymorphisms the obtained 8 genotype combinations showed significantly different Kaplan-Meier survival curves. The evaluation of these curves with Cox regression analysis resulted in two prognostically different groups: "A" good prognosis (RR<1) and "B" bad prognosis (RR>1). The disease-free- and overall survival of these two groups were significantly different. DPD activity also showed correlation with the survival; patients with DPD activity <10 pmol/min/106 PBMCs showed significantly longer disease-free and overall survival. The determination of DPD activity proved to be a more valuable parameter in the evaluation of serious 5-FU-related toxicity compared to the IVS14+1G>A mutation analysis. According to the Cox multivariate analysis the combination of germline TS polymorphisms and DPD activity is/an independent prognostic marker of survival in CRC patients treated with adjuvant 5-FU therapy.     

An oxidative stress-specific bacterial cell array chip for toxicity analysis

An oxidative stress-specific bacterial cell array chip was fabricated and implemented in the analysis of various different chemicals. The chip consisted of twelve toxicity responsive strains that respond specifically to different oxidative toxicities such as the generation of the superoxide radical, except for strain EBMalK, which was included as a negative control. Each bioluminescent strain carried a fusion of a stress gene promoter (sodA, pqi-5, soxR, fumC, soxS, inaA, hmp, malK, katG, zwf, fpr or pgi) to the bacterial lux reporter genes. A total of nine chemicals were selected to exhibit the capabilities of this array when analyzing different oxidative toxicities. Each of the chemicals were categorized according to their structure and their ability to form radicals in vivo: (I) paraquat, an active radical producer, (II) structural analogs of paraquat that produce radicals, (III) chemicals that are distinct from paraquat but still produce radicals and (IV) chemicals having similar structures as paraquat but do not produce radicals. The results found that each strain was responsive to one or more of the compounds tested but, as a definitive factor, the responses from the chip were dependent upon the production of radicals, i.e., the strains were unresponsive to compounds that were similar in structure to paraquat but lacked the ability to generate radicals. The specificity of the strains used in the chip was also demonstrated by their ability to discriminate between the superoxide radical and hydrogen peroxide. Therefore, this cell array chip could be implemented in characterizing and understanding the toxic impacts of newly synthesized chemicals and drugs in terms of toxicity classification and the nature of oxidative damage experienced by cells.     

Widespread presence of hydrophobic paralytic shellfish toxins in Gymnodinium catenatum

The toxic dinoflagellate Gymnodinium catenatum Graham produces a newly discovered sub-class of paralytic shellfish toxins (PSTs, saxitoxins) that contain a hydroxybenzoate moiety in place of the carbamoyl group (GC toxins: GC1–GC3). GC toxins bind strongly to sodium channels and their lipophilic nature may increase their potential to bioaccumulate in marine organisms. Cultures Australian G. catenatum strains were found to contain 12–63 mol% GC toxins. The GC toxins were also detected in strains from China (38 mol%), Japan (1–2 mol%), Portugal (58 mol%), Spain (36–54 mol%), and Uruguay (10–16 mol%). A cluster analysis of molar proportions of saxitoxin derivatives produced by strains showed clear clustering by country/region of origin, indicating that GC toxins may be very useful markers to identify the source of G. catenatum in the case of new outbreaks. The GC toxins dominate the toxin profiles of many G. catenatum strains, and can contribute significantly to sample toxicity, yet these toxins may easily escape detection using conventional chromatography, resulting in significant underestimates of sample toxicity. This has significant implications for shellfish monitoring and safety.     

Role of EDTA in a simple method for determining toxicity using a bacterial indicator organism

A method to determine toxicity using a bacterium as the indicator organism previously developed (Botsford 1998) perceives most divalent cations as being toxic. Mercury is perceived as the most toxic, followed by cadmium, zinc and copper. It was found that adding 2.5 m EDTA to the reaction would relieve the toxicity of the 15 divalent cations tested. This effect does not appear to be simple chelation. One micromolar EDTA eliminated the toxicity of 1.6 m calcium or 0.006 m mercury. Thirty-six chemicals were tested for their toxicity in the presence and absence of 2.5 m EDTA and 25 ppm calcium. Twenty-one were less toxic and two of these, p-aminobenzoic acid and tetrachloroethylene would no longer appear to be toxic according to the assay when these additions were present. Six chemicals had the same toxicity with and without the additions. Nine chemicals were more toxic when the EDTA and calcium were present. This experiment was repeated with six chemicals and ten times the EDTA concentration and ten times the calcium concentration. The toxicity with 10× was compared with the toxicity with 1× the additions. The toxicity of 4 of the six chemicals changed with the higher concentration of EDTA and calcium when the absorbancy values observed in samples with the lower levels were compared with samples with the higher levels. Obviously before EDTA can be added to mitigate the toxicity of divalent cations, it must be determined how much EDTA is required to eliminate the toxicity by the ions present in the sample. Alternatively, if the nature of the contaminating organic chemical is known, it can be determined what the effect of EDTA and the divalent cation present is on the apparent toxicity of the compound.     

邻苯二甲酸二乙酯和壬基酚联合暴露对杜氏盐藻生长的影响

为了探讨环境激素类物质邻苯二甲酸二乙酯(DEP)和壬基酚(NP)对海洋微藻的联合毒性效应,选取杜氏盐藻(Dunaliella salina)为受试生物,以环境激素对杜氏盐藻单一暴露的96h EC₅₀的毒性效应作为一个毒性单位(IU),采用毒性单位法比较研究了DEP和NP单一暴露以及两者以三种不同混合比例(毒性单位比:1:1、1:4和4:1)暴露对杜氏盐藻的细胞生长、叶绿体色素含量、可溶性蛋白含量、SOD活性以及最大光能转化效率(Fv/Fm)的影响.实验结果表明:DEP和NP单一暴露对杜氏盐藻的96h EC₅₀分别为69.54 mg/L和1.47 mg/L,两种环境激素对杜氏盐藻均有抑制作用,且NP较DEP对杜氏盐藻的毒性更强.DEP和NP联合暴露较单一暴露对杜氏盐藻的细胞生长、叶绿体色素和可溶性蛋白的合成有较强的抑制作用,两种环境激素在毒性单位比为1:1、1:4、4:1三个比例水平上的联合毒性效应均表现为协同效应,其中比例为1:1的协同效应最强.     

A novel continuous toxicity test system using a luminously modified freshwater bacterium

An automated continuous toxicity test system was developed using a recombinant bioluminescent freshwater bacterium. The groundwater-borne bacterium, Janthinobacterium lividum YH9-RC, was modified with luxAB and optimized for toxicity tests using different kinds of organic carbon compounds and heavy metals. luxAB-marked YH9-RC cells were much more sensitive (average 7.3-8.6 times) to chemicals used for toxicity detection than marine Vibrio fischeri cells used in the Microtox assay. Toxicity tests for wastewater samples using the YH9-RC-based toxicity assay showed that EC50-5 min values in an untreated raw wastewater sample (23.9 +/- 12.8%) were the lowest, while those in an effluent sample (76.7 +/- 14.9%) were the highest. Lyophilization conditions were optimized in 384-multiwell plates containing bioluminescent bacteria that were pre-incubated for 15 min in 0.16 M of trehalose prior to freeze-drying, increasing the recovery of bioluminescence and viability by 50%. Luminously modified cells exposed to continuous phenol or wastewater stream showed a rapid decrease in bioluminescence, which fell below detectable range within 1 min. An advanced toxicity test system, featuring automated real-time toxicity monitoring and alerting functions, was designed and finely tuned. This novel continuous toxicity test system can be used for real-time biomonitoring of water toxicity, and can potentially be used as a biological early warning system.     

Gamma-radiation dose-rate effects on DNA damage and toxicity in bacterial cells

In order to investigate the relationship between radiation dose-rate and bacterial DNA damage as well as general cellular toxicity, two recombinant Escherichia coli strains, DPD2794 and GC2 were used. Following gamma-ray irradiation, these bioluminescent bacteria showed quantitative stress responses in terms of DNA damage and general toxicity depending on the dose rates of energy deposition, i.e. dose-rate of radiation. In addition, an inverse relationship was found, at lower dose rates between 0.5 and 1 Gy/h and a parabolic relationship at dose rates between 0.5 and 2.6 Gy/h.     

The genetic toxicity of the peroxisome proliferator class of rodent hepatocarcinogen

Peroxisome proliferators comprise a structurally diverse class of chemicals. Some of the members of this class show evidence of genetic toxicity (most evidently the in vitro clastogen Wyeth 14,643, WY), while others do not (most evidently methyl clofenapate, MCP). When attempting to understand the mechanism of rodent hepatocarcinogenesis of this class of chemicals the possible role of genetic toxicity should be assessed on a class-wide basis, i.e., if just one peroxisome proliferator is shown to be unequivocally inactive as a genetic toxin, genetic toxicity cannot be implicated in the carcinogenic activity of peroxisome proliferators as a class. In an earlier paper, we established MCP as inactive in a range of in vitro and in vivo genetic toxicity assays. However, the top dose level of MCP that could be tested for induction of chromosome aberrations (clastogenicity) in human lymphocytes and CHO cells was limited by the relative insolubility of the test agent in the assay medium. Methyl clofenapate was not toxic up to a dose that produced precipitate, so cannot be directly compared with WY, which induced aberrations only at toxic dose levels. In the present paper, we have evaluated the clastogenicity of the carcinogenic peroxisome proliferator nafenopin (NAF) at dose levels up to those that are toxic to CHO cells, and found no evidence of chromosome aberration induction. These data isolate further the genetic toxicity of WY from other peroxisome proliferators, and increase confidence in the proposal that genetic toxicity does not play a critical role in the hepatocarcinogenicity of peroxisome proliferators.     

Influence of the activated sludge system configuration on heavy metal toxicity reduction

The effect of configuration of activated sludge systems on heavy metal toxicity was investigated. Two bench-scale completely mixed activated sludge systems were operated identically in order to determine the toxic effects of Cr(VI), Zn(II) and industrial wastewater on the activated sludge biomass. One system was operated with an aerobic selector and the other without. Batch experiments based on OECD 209 (Organisation for Economic Cooperation and Development) were performed using a respirometer to find out potential toxicity reduction effect of an aerobic selector. The IC₅₀ (concentration of a chemical that exhibits 50% respiration inhibition) values of Cr(VI), Zn(II) and industrial wastewater in the activated sludge were determined. Results indicated that the heavy metals and industrial wastewater caused less inhibitory effect on the selector activated sludge system in comparison to the conventional activated sludge system. Cr(VI) was found to exert higher inhibition on both systems.