Abstract:
The invention is concerned with a biologically based test system for the detection of inorganic and organic pollutants in water samples. In particular, the present invention is concerned with the development of a strategy for the control of background expression of biosensors in the biologically based test system. Furthermore, the present invention provides a test kit for determining concentrations of inorganic and organic pollutants in water samples, the test kits are suitable for field tests.

Description:
BACKGROUND OF THE INVENTION 
     The present invention relates to a biologically based test system for the detection of inorganic and organic pollutants in water samples. In particular, the present invention is concerned with the development of a strategy for the control of background expression of biosensors in said biologically based test system. More particularly, the present invention comprises a biologically based test system for the detection of arsenite and arsenate in potable water with a controlled background expression of the biosensor. Furthermore, the present invention provides a test kit for determining arsenite and arsenate concentrations in water samples, said test kits are suitable for field tests. 
     Arsenite and arsenate are found in toxic concentrations in groundwaters in many countries all over the world and seriously threaten the life of millions of people, especially in Southeast Asian countries, like Bangladesh. In the early 1990s, high levels of arsenic in potable water of Bangladesh were first detected. Presently, about 20 million people of the total population of Bangladesh (125 million) are suspected to be drinking contaminated water. Up to a certain degree, arsenic toxicity is reversible by drinking arsenic-free water. In Bangladesh, however, arsenic-free water is not available in many places and chronic poisoning develops. The effects of arsenic poisoning can vary from skin pigmentation, development of warts, diarrhea and ulcers during the initial stages. In the most severe cases, arsenic poisoning causes liver and renal deficiencies or cancer that can lead to death (6). It is assumed that the structural similarity with phosphate causes the toxicity of arsenate. Since arsenate mimics phosphate, it can be taken up through phosphate channels and can interfere in different metabolic processes (5), (9). Arsenic poisoning is undetectable in its early stages, and takes between 8 and 14 years to have a clear impact on human health. The final impact is depending on the amount of arsenic ingested, the nutritional status and the immune response of the individual. 
     More than ten years ago, most of Bangladesh&#39;s population obtained its potable water from surface ponds, but this was bacteriologically unsafe and, therefore, an undesired situation. Because of these reasons, the use of groundwater as source for potable water was promoted. It is estimated that 95% or more of Bangladeshis now use groundwater for drinking water. Unfortunately, the use of groundwater for drinking water has caused unsuspected dreadful effects, due to very high concentrations of arsenic. The content of arsenic in Bangladesh&#39; groundwater is naturally determined. 
     The drinking water limit for As-contamination in Bangladesh is 50 μg/l. The World Health Organization, however, recommends an index of 10 μg/l. The highest concentrations of arsenic found in Bangladesh are around 2.4 mg/l. Arsenic in potable water is not only a problem in Bangladesh, but also in other countries like India, Mexico, Vietnam or the Republic of Yugoslavia. Measuring the concentrations of arsenite and arsenate in water used as drinking water is therefore an absolute necessity. Accurate determination of arsenic compounds is usually done by Atomic Fluorescence Spectroscopy or Atomic Adsorption Spectroscopy, but both techniques require substantial investments and are not available in rural and poorer areas. Chemical field tests exist as well, but these are not accurate in the range of the present drinking water standards (10 to 50 microgram per liter) and themselves give rise to pollution with heavy metals like mercury and zinc. Moreover, the measurement of arsenite by traditional analytical chemical methods is difficult and costly (23). Thus, there is a strong interest to produce chemical field test kits, which are sensitive enough to detect arsenite around the drinking water limit of 50 μg/l. Most available tests use hydrochloric acid and zinc to produce arsine-gas (AsH 3 ), which is then reacting with mercuric bromide on a paper, producing a brown color. However, this test is still unreliable at concentrations below 150 μg/l. 
     Alternative measuring strategies could involve an assay with whole cell living biosensors. Such assays have already been described in the art. In this type of biosensor assay microorganisms are used as specific and sensitive devices for sensing the bioavailability of a particular pollutant or pollutant class (21). The idea of sensing is based on the ability of pollutants to invoke a specific and inducible response in microorganisms. The signaling pathway thus activated will regulate the expression of one or more genes. The extent of this gene expression serves as a measure of the available (“sensed”) concentration of the compound. A rapid and sensitive way to measure such gene expression is to fuse relevant promoter sequences to reporter genes, like those coding for bacterial luciferase, beta-galactosidase or green flurorescent protein (GFP). 
     A bacterial bioassay has been described (16, 17, 19, 22 and 23), which is based on the natural resistance mechanisms of bacteria against arsenic. This assay makes use of biosensors, which are able to detect arsenite and arsenate in water samples. Said biosensors are usually genetically modified bacteria, comprising a gene coding for a regulatory protein inducing the production of a specific marker protein in the presence of arsenic. The biosensors are remarkable sensitive and detect arsenite at concentrations of 5 microgram per liter. The activity of the marker protein is usually measured by a luminometer. 
     However, bioassays developed so far are afflicted with high background expressions of the marker proteins, which lead to false positive results at arsenite concentrations in the microgram per liter range and this has limited until now the development of a simple field colorimetric test. Background expression occurs in all arsenic-based biosensors due to the nature of the DNA-binding of the regulatory protein. 
     Therefore, an urgent need exists for the development and availability of a simple, cheap, reliable, and accurate test system with a controlled background expression of the biosensor, which is suitable as a field test for the measurement of heavy metals, such as arsenic in water samples. 
     SUMMARY OF THE INVENTION 
     The present invention solves the above-mentioned problem by providing an improved biologically based test system for the detection of pollutants in water samples comprising a genetically modified bacterium producing a marker protein upon induction of a regulatory protein, wherein the activity of said regulatory protein is induced by the presence of said pollutant, characterized in that said genetically modified bacterium comprises at least one additional DNA binding site for the regulatory protein directly in front of the gene for the marker protein. 
     More particularly, the present invention provides an improved test system for the detection of heavy metals such as arsenite and arsenate in water samples. 
     DETAILED DESCRIPTION OF THE INVENTION 
     Many bacterial strains, like  Ralstonia metallidurens, Pseudomonas aeruginosa  or  Staphylococcus aureus  contain genetic determinants for resistance to heavy metals such as Hg 2+ , Ag 2+ , AsO 2   − , AsO 4   3− , Bi 3+ , BO 3   3− , Cd 2+ , Co 2+ , CrO 4   2− , Cu 2+ , Ni 2+ , Pb 3+ , Sb 2+ , TeO 3   2− , Tl + , or Zn 2+  (20). These resistance determinants are often found on plasmids and/or transposons. Resistance to arsenic and antimony are also associated with plasmid-encoded resistance operons, which are widespread among bacterial species, although many bacteria carry arsenite resistance genes on the chromosome. Bacterial resistance to arsenite (As(III)), arsenate (AS(V)) and antimonite (Sb(III)) is found both in gram-negative and gram-positive bacteria (3). 
     Thus, in a preferred embodiment of the present invention the genetically modified bacteria is an  Escherichia coli  strain bearing a genetically modified plasmid; said plasmid carrying an arsenite resistance regulatory gene, a gene coding for a marker protein and at least one additional DNA binding site for an arsenite resistance regulatory protein in front of the gene for the marker protein in order to reduce background expression. 
     In yet another preferred embodiment the  Escherichia coli  strain is the strain  E. coli  K12, the arsenite resistance regulatory gene is derived from the naturally occurring  E. coli  plasmid R773, cloned into any suitable  E. coli  K12 plasmids like pBR322, pUC18, pACYC184 and RSF1010. 
     As already mentioned the present invention uses the naturally occurring plasmid R773 of  Escherichia coli  as source for the arsenite resistance gene. The specific DNA region of this plasmid conferring arsenic and antimony resistance is known as the ars operon. The system demonstrates a high selectivity for arsenite and antimonite, and, to a lesser extent to bismuth oxide. Other anions like phosphate, carbonate, nitrate and sulfate do not induce the system (19). 
     The ars operon of  E. coli  plasmid R773 contains five genes, encoding the proteins ArsR, ArsD, ArsA, ArsB and ArsC. ArsR and ArsD are so-called regulatory proteins. ArsR controls the basal level of protein expression, whereas ArsD controls the maximal level of protein expression. ArsA and ArsB form a pump to remove antimonite and arsenite from the cytosol to the periplasm of the bacteria. ArsA is an ATPase that provides the energy necessary for this process and ArsB is the transmembrane protein. ArsC reduces arsenate to arsenite, which can then subsequently be effluxed by the pump (17). 
     The signaling pathway for arsenic sensing functions as follows: In the absence of antimonite or arsenite the ArsR protein binds to the DNA near the promoter region of the ars operon, repressing transcription of the ars genes. When arsenite or antimonite enter the cell, they bind to ArsR and cause a conformational change in the protein, which results in the release of ArsR from the promoter DNA. Transcription of the ars operon then starts. Arsenate (AsV) itself does not directly induce ars transcription. When the intracellular concentration of ArsD becomes sufficient to saturate the operator, transcription is again repressed. At higher As(III) or Sb(III) concentrations, ArsD dissociates from the operator, producing again an increase in ars expression (4), (2), (see  FIG. 1 ). Regulation of the ars operon is mediated from a site on the DNA in front of the arsR gene, to which the ArsR protein binds. The natural system is expressed constitutively to a low level, without which ArsR itself would not be synthesized and the cycle of repression and repression-release would not function. 
     For purposes of the present invention only the gene coding for the ArsR protein was isolated from the plasmid R733 and transcriptionally fused to a gene coding for a marker protein downstream of arsR. Upon activation of the ars operon the marker gene fusion is transcribed. However, due to the said nature of the ArsR activation cycle, a low transcription of the gene for the marker protein will occur in absence of arsenite. In the present invention the low constitutive transcription of the marker gene is effectively reduced by placing another binding site for ArsR downstream of the gene for arsR and in front of the marker gene. 
     In a further embodiment of the present invention the gene coding for a marker protein is selected from the group comprising alkaline phosphatase (phoA), chloramphenicol acetyl transferase (CAT-gene), catechol dioxygenase (xylE), bacterial luciferase, eukaryotic luciferase, beta-galactosidase, and green fluorescent protein (GFP), most preferably bacterial luciferase, green fluorescent protein and beta-galactosidase. 
     Genes coding for such marker proteins are widely used as so called reporter genes. They are linked to other genes or regulatory sequences, in the present invention to the arsR gene of the ars operon of plasmid R773 or any other arsR gene, in order to indicate their activity. 
     Another very important embodiment of the present invention comprises a biologically based test kit for the determination of heavy metal in water samples, said test kit is suitable for field tests in that it can be stored at room temperature and is easily decontaminated. 
     In a preferred embodiment the biologically based test kit of the present invention comprises a colorimetric paper strip comprising genetically modified bacteria, said bacteria containing a plasmid conferring resistance to a heavy metal and being immobilized and dried in a matrix on the calorimetric paper strip. 
     In yet another preferred embodiment of the present invention the test kit is suitable for the detection of arsenite and arsenate in water samples. 
     In a more preferred embodiment the genetically modified bacteria immobilized on the paper strip are derived from the  E. coli  strain K12, the arsR gene is derived form the naturally occurring plasmid R773 and introduced into a suitable  E. coli  plasmid vector, said plasmid vector being genetically modified by carrying at least one additional DNA binding site for the ArS protein. 
     Another embodiment of the present invention is a method for preparing a calorimetric paper strip test kit, comprising the steps of:
         a) Cultivating bacterial cells;   b) Transferring 5 to 20 microliter, preferably 10 microliter of the bacterial suspension of step a) on small paper strips;   c) Placing the paper strips in sterile tubes; and   d) Drying of the paper strips under constant temperatur and gradually lowered vacuum.       

     A further embodiment of the present invention comprises a biologically based test kit for the determination of heavy metal concentrations, such as arsenite and arsenate concentrations in water samples, said test kit comprising a multi-well plate coated with genetically modified bacteria derived from the  E. coli  strain K12, said bacteria comprising an  E. coli  plasmid vector carrying the gene coding for the arsenite resistance protein ArsR from the naturally occurring plasmid R773, said plasmid vector carrying at least one additional DNA binding site for the ArsR protein. 
     A further embodiment of the invention is a method for producing a multi-well test kit, comprising the steps of:
     a) cultivating bacterial cells;   b) transferring 30 to 70 microliter, preferably 50 microliter of the bacterial suspension of step a) into a glass vial or multi-well plate; and   c) drying of the bacterial suspension under constant temperature and gradually lowered vacuum.   

     Another preferred embodiment of the present invention is the use of the described test kits in field tests for the detection of arsenite and arsenate in water samples. 
    
    
     
       BRIEF DESCRIPTION OF THE DRAWINGS 
       The invention is further illustrated by Figures wherein 
         FIG. 1  is a scheme of the regulation and organization of the ars genes. 
         FIG. 2  shows a schematic drawing of plasmid pJAMA8-arsR. In front of the arsR-gene is a terminator structure (‘Term’), followed by the arsR-promoter and binding site for ArsR (‘ABS’). Located behind the arsR-gene are the genes for bacterial luciferase (‘luxA’ and ‘luxB’). Positions of relevant restriction sites are indicated. 
         FIG. 3  is a schematic drawing of the plasmid used for colorimetric detection of arsenite contamination. Abbreviations and symbols as in  FIG. 2 . 
         FIG. 4  demonstrates light emission from the biosensor cells ( E. coli  DH5α pJAMA8-arsR) in response to different arsenite concentrations after 30 minutes exposure time. Shown are the averages of three independent incubations mixed from three frozen batches of biosensor cells. Vertical bars indicate the calculated deviation from the average (assuming normal distribution). Multiwell assay with a total volume of 0.2 ml and 0.05 ml cell culture. 
         FIG. 5  shows the reproducibility of biosensor calibration in response to different arsenite concentrations. Calibration curves were produced by three different individuals from different frozen cell batches on the same day. Induction time: 30 minutes. Data points in each curve indicate the averages from two independent incubations from the same batch. 
         FIG. 6  demonstrates standard calibration of  E. coli  DH5α (pJAMA-arsR) with arsenate. Data points are the averages of three independent incubations mixed from four frozen cell batches. Incubation time: 30 minutes. Incubation temperature: 37° C. Multiwell assay with 1 ml total volume and 0.15 ml cell culture. 
         FIG. 7  shows the effect of 0.2 μM FeSO4 on the light emission of the biosensor exposed to a range of arsenite concentrations. Incubation time: 30 minutes at 37° C. Data points indicate the average from two independent assays. 
         FIG. 8  shows the effect of 2 mM Fe 3 EDTA on the light emission of the biosensor exposed to a range of arsenite concentrations. Incubation time: 30 minutes at 37° C. Data points indicate the average from three independent assays. Vertical bars point to the average deviation. 
         FIG. 9  shows the effect of including 0.2 μM FeSO4 on the light emission of the biosensor exposed to a range of arsenate concentrations. Incubation: 30 minutes at 37° C. Data points indicate the average from three independent assays. Vertical bars point to the average deviation. 
     
    
    
     The following examples are intended to further illustrate the present invention. They are meant to be exemplary to the invention and do not to limit its scope. 
     EXAMPLES 
     Two types of whole cell living biosensors are described. Both consist of the bacterium  Escherichia coli  K12, a non-pathogenic laboratory strain, into which different plasmids—with the sensing elements—are introduced. One of these produces the luciferase enzyme upon contact of the bacteria with arsenite. The activity of the luciferase enzyme results in light production and can be measured very sensitively and quantitatively. The second biosensor produces the enzyme beta-galactosidase upon contact of the bacteria with arsenite. The activity of beta-galactosidase can be assayed by the formation of a colored compound. This second biosensor formed the basis for a quick semi-quantitative field color test. 
     Example 1 
     Construction of a Biosensor for Arsenic Detection Based on Luciferase 
     For reasons of detection accuracy and ease of the measurement, a biosensor in  E. coli  was produced, which would produce light (=bioluminescence) in response to the presence of arsenite. By genetic engineering techniques known in the art, a DNA fragment containing the promoter for arsR (ParsR) and the gene for arsR was isolated, which was in vitro combined with a DNA fragment containing the genes for bacterial luciferase (luxAB). This plasmid, pJAMA8-arsR, was then reintroduced into  E. coli  strain DH5α ( FIG. 4 ).  E. coli  DH5α is a laboratory strain and derivative of  E. coli  K12, classified to the lowest biosafety level and without any known pathogenicity determinants. The response of this  E. coli  (pJAMA8-arsR) was carefully calibrated and found to be sufficient to detect arsenite in the range below 0.1 μM arsenite (8 μg/l). 
     Example 2 
     Beta-Galactosidase Based Detection 
     The main purpose of producing a whole cell living biosensor for arsenite with the gene for beta-galactosidase as detection system was the potential for a color test kit. The activity of the beta-galactosidase enzyme can be measured in various ways. The easiest one involves the addition of a colorless substrate (X-Gal), which is turned into a blue dye by cleavage with active beta-galactosidase. X-Gal is directly taken up by the bacteria and there is no need to permeabilize or open the cells. 
     The original plasmid pBGD23 did not allow the use of X-Gal as a substrate, since the background beta-galactosidase activity in the bacteria was too high. This means that even without any arsenite present, some beta-galactosidase is synthesized in the cells, which cleaves X-Gal and produces the blue color. The reason for this background activity lays in the nature of the ArsR regulatory system. Thus, a plasmid was produced in which the background activity from the lacZ gene is very low. This was achieved by adding a small DNA fragment containing the binding site for the ArsR protein, in between the end of arsR and the beginning of lacZ. In this way, most of the transcription was blocked after the arsR gene. 
     This new plasmid was constructed in several steps. First, a fragment containing ParsR and arsR was isolated and cloned in front of a promoterless lacZ gene (plasmid pMV132). This plasmid was then opened at a unique restriction site in front of lacZ and a 60-base-pair small DNA piece was inserted which carried the binding site for ArsR. The resulting plasmid was named pMV132-arsR-ABS.  E. coli  cells carrying this plasmid could indeed be used to produce a color gradient of blue at concentrations as low as 0.1 μM in a response time of 1 hour, both in multi-well plate format and on paper strips. 
     Example 3 
     Measuring with Arsenic Biosensors 
     In a first instance, both biosensor variants were tested for their capability to detect arsenite in the environmentally relevant concentration range (0-0.5 mg/l), to test the influence of incubation time on the test result, to determine the reproducibility of the biosensor measurement and the influence of disturbing compounds in the water samples. The arsenite concentration in unknown aqueous samples can be inferred by comparing the light signal to that of a standard curve produced with known arsenite concentrations. Inhibitory effects of other chemical compounds present in the sample can be addressed by addition of a known amount of arsenite to the sample and comparing the observed increase in light emission with the light emission expected from the calibration curve. 
     Example 4 
     Calibration Series with Arsenite 
     Calibration series with arsenite were performed with a stock solution of 1 g/l arsenite, which was diluted in water until the desired concentration range (0.1 to 1 μM—with 1 μM corresponding to 78 μg/l). At first, optimal conditions for the biosensor measurements were used. This involved the use of cell batches, which were frozen at −80° C. and thawed before each measurement. The cells from one frozen batch (0.6 ml) could be divided in 4 portions, in order to perform a complete calibration series with one batch of cells. In some cases, batch-to-batch variations were noticed and, therefore, a protocol of deriving three cell batches was used, thawing and mixing those, and preparing from these three parallel calibration series. Initially, tests were performed in individual glass tubes for each measurement. However, for more convenient and faster measurements, the procedure was changed to using 24-well or 96-well plates. 
     As can be seen from a typical calibration curve as shown in  FIG. 4  the light emission from the cells recorded after 30 minutes incubation time, increases proportionally to the arsenite concentration in the medium. Some background light emission occurs even without arsenite present. The reason for this was the background expression from the ParsR—since the luciferase sensor plasmid was not corrected for its background expression like the beta-galactosidase sensor plasmid. However, the background expression did not interfere with the measurements in the lower range (i.e., below 0.1 μM arsenite). Addition of the second ArsR binding site to the same plasmid resulted in reduction of the background expression (not shown). The absolute light emission from the cells increased when the incubation time with arsenite was prolonged. Therefore, the absolute light emission value should not be taken as an indication for the arsenite concentration, but only in combination with a calibration curve performed simultaneously. Despite this, the reproducibility of the calibration curve prepared from frozen cell batches by different individuals within the same laboratory was good ( FIG. 5 ). 
     The arsenic biosensor expressing the beta-galactosidase was used in a similar way as the luciferase sensor. In such a quantitative test, the activity of beta-galactosidase was analyzed by permeabilizing the sensor cells, adding the substrate for the enzyme (ONPG) and recording the increase in absorption at 420 nm. It was also addressed, however, if the beta-galactosidase induced in  E. coli  strain containing plasmid pMV132-arsR-ABS could be analyzed by the formation of a colored product. In this way, different intensities of blue color were produced which were dependent on the arsenic concentration measured by the cells. However, no absolute assignment could be made to the intensity of the blue color, since this increases during longer incubation times. However, the intensity increase was not a matter of minutes, but rather of half-an-hour or longer, and the differences among incubations with different arsenite concentrations remained similar for incubation periods as long as 12- to 16 hours. Therefore, this sensor can be used to have a quick first screening of samples. The lower detection limit was around 0.1 μM arsenite. 
     Example 5 
     Calibration Series with Arsenate 
     Since arsenite is only one of the various forms in which arsenic contamination can occur, calibration series with arsenate were performed. From previous work it was known that the biosensor strain might also react to arsenate, since many  E. coli  host strains carry the arsenate reductase enzyme. This enzyme reduces arsenate to arsenite within the cell and the produced arsenite triggers the induction of the gene reporter construct. 
     Indeed, in the host strain  E. coli  DH5α, the plasmid pJAMA-arsR resulted in the production of luciferase upon incubation with arsenate. The response was about half as strong as that with arsenite ( FIG. 6 ). The small ‘hill’ in the calibration curve around 0.1 μM was not consistently observed and, therefore, likely is the result of a measurement outlayer. From these measurements it was concluded that the sensor is also sensitive enough to measure arsenate in the range below 0.2 μM. 
     The biosensor strain with the beta-galactosidase reacted similarly to arsenate as to arsenite (not shown). 
     Example 6 
     Disturbances and Cross-Reactivity 
     Since the biosensor measurements were performed with whole cells of living bacteria, several factors other than the target compound could influence the output (the ‘measurement’) of the sensor cells. Of most important concern are those compounds present in the water sample, which are toxic for the bacterial cells or otherwise interfering with the chemical status of arsenic. It is not possible to test each possible combination of compounds on the behaviour of the biosensor cells. Therefore, we focused on the effects of iron—which is a major constituent of groundwater and known to chemically interfere with arsenic, and further compared biosensor and chemical arsenic measurements in a number of imported Bangladesh groundwater samples. 
     As far as biosensor measurements showed, mostly iron II reduced the output from the sensors ( FIGS. 7-9 ). Iron II was tested in a concentration of 0.2 μM (=11 mg/L) and this resulted in about 50% reduction of light emission at the highest arsenite concentration tested. At lower arsenite concentrations, the effect was not so pronounced ( FIG. 7 ). It was suspected that the effect of iron II might have been a complexation with arsenite, thereby reducing the available arsenite fraction, although also samples without arsenite showed a reduced light emission in the presence of 0.2 μM iron (II) ( FIG. 9 ). 
     Cross-reactivity of the arsenite sensor was only observed to antimonite and bismuth. The inductive response to antimonite is as sensitive as that to arsenite (not shown), whereas that to bismuth oxide is 100-fold less sensitive. Therefore, in theory, antimonite and arsenite could interfere and positive measurements may lead to false interpretations when under no other circumstances a confirmation is made by using atomic adsorption spectrometry. 
     Example 7 
     Analysis of Groundwater Samples from Bangladesh and Vietnam 
     Several groundwater samples, which had been taken in Bangladesh, were analyzed by using the luciferase and beta-galactosidase biosensors. Since the water samples had been acidified for storage and transport, they were diluted 10- and 100-fold in phosphate buffer of pH 7. To test for any inhibitory compounds in the water for the biosensor cells, one extra measurement was performed in which the samples were spiked with an additional 0.2 μM arsenite. When no inhibitory factors would be present, the light emission would increase according to the calibration curve (except if the arsenite concentration in the sample would be higher than 1 μM). 
     As can be seen from the results, all samples except B4 contained arsenic in amounts higher than the 10 μg/L limit, except sample B4 (Table 1). The results from the spiked samples indicate that except for the highest value (B1), no inhibitory compounds were present for the biosensor. The water of well B1 is in the range of the maximal response of the biosensor. Therefore, any increase of arsenite concentration will result in a lower light emission, since arsenite starts to become toxic for the cells. For water samples B1, B2 and B3, the total concentration of arsenic by chemical analyses was more ore less in agreement with the concentration determined by the biosensor (B1: 1020 compared to 980, B2: 375 compared to 210, B3: 407 compared to 224). Samples B4 and B7 were clearly higher in the chemical analysis (256 and 265 μg/L, respectively). The reasons for this difference are presently not clear yet. 
     
       
         
               
             
               
               
               
               
               
               
               
             
               
               
               
               
               
               
               
             
           
               
                 TABLE 1 
               
             
             
               
                   
               
               
                 Determination of arsenite-equivalent concentrations in Bangladesh&#39; groundwater 
               
               
                 samples. 
               
             
          
           
               
                   
                   
                   
                   
                 Arsenic 
                 Correction 
                   
               
               
                   
                   
                   
                   
                 concentration 
                 for 
               
               
                   
                   
                   
                   
                 according 
                 dilution 
               
               
                   
                   
                   
                   
                 to AsIII 
                 and 
                 Arsenic 
               
               
                   
                 Light 
                   
                   
                 standard 
                 inhibition 
                 concentration 
               
               
                 Sample 
                 emission 
                   
                   
                 curve 
                 As 
                 As 
               
               
                 nr 
                 Meas 1 
                 Meas 2 
                 Average 
                 As (μM) 
                 corr 
                 (μg/L) 
               
               
                   
               
             
          
           
               
                 B1 
                 10951380 
                 13426902 
                 12189141 
                 0.66 
                 13.2 
                 980 
               
               
                 B2 
                 3693575 
                 3749482 
                 3721529 
                 0.14 
                 2.8 
                 210 
               
               
                 B3 
                 3382199 
                 4382695 
                 3882447 
                 0.15 
                 3.0 
                 224 
               
               
                 B4 
                 1727514 
                 1566010 
                 1646762 
                 0.01 
                 1.22 
                 17 
               
               
                 B7 
                 2208496 
                 1655100 
                 1931798 
                 0.03 
                 0.56 
                 44 
               
               
                 Spiked 
                   
                   
                   
                   
                 Expected 
               
               
                 samples 
                   
                   
                   
                   
                 increase 
               
               
                 B1 
                 7999680 
                 10225318 
                 9112499 
                 0.47 
                 0.86 
               
               
                 B2 
                 6169947 
                 6548613 
                 6359280 
                 0.30 
                 0.34 
               
               
                 B3 
                 8034159 
                 7916240 
                 7975200 
                 0.40 
                 0.35 
               
               
                 B4 
                 4819680 
                 3999806 
                 4409743 
                 0.18 
                 0.21 
               
               
                 B7 
                 6175502 
                 5561221 
                 5868362 
                 0.27 
                 0.23 
               
               
                   
               
             
          
         
       
     
     In the colorimetric test ( FIG. 10 ), tenfold dilutions of the same samples B1, B2, B3, B4 and B7 scored positive at a concentration range between 0.1 and 0.5 μM As (=8 and 50 μg/L). This is in agreement with the chemical analyses, except for sample B1, which is even higher than 0.5 mg/L. 
     Example 8 
     Development of a Storage Protocol 
     One of the critical factors for the use of the biosensor test is its storage. Sufficiently well-equipped laboratories can use the most easy variant of freezing cell batches in 15% glycerol at −80° C. and thawing these before use. Preserved in this manner, the cell batches keep viable and active for at least 1 year. Less well-equipped laboratories can grow the biosensor cells fresh for each measurement and maintain optimal results. In order to provide a possibility to perform the arsenic biosensor test without worrying about preservation or cultivating the bacterial cultures, a storage protocol was developed. The storage protocol was based on studies by Dr. K. Malik from the German Collection of Microorganisms. By using his protocols it was possible to produce dried biosensor cultures, which retained their activity for arsenic measurements during one month storage at room temperature. This may be improved with more optimal storage conditions and optimized drying materials. 
     Example 9 
     Protocol for Liquid Drying 
     The protocol for liquid drying consists of three steps: cultivating the bacterial cells, drying and storage, and testing.
     i) bacterial cultures were grown from a fresh colony in 5 ml liquid medium (Luria Broth) containing ampicillin for 16 h at 37° C. Cells were then harvested by centrifugation and the supernatant removed. The cell pellet was carefully resuspended in a medium containing gelatin, meat extract, sodium ascorbate, raffinose and sodium glutamate. Drops of 50 microliter of culture suspension were transferred to 2 ml glass vials, which were closed with a screw-cap and Teflon seal. The Teflon seal was punctured with a small-gauge needle.   ii) Drying was performed at a constant temperature of 20° C. and gradually lowered vacuum. First, 1 h was dried at 70 mbar, the next hour at 20 mbar, after which the samples were dried at 0.5 mbar for another 12 h. The vacuum chamber was then filled with nitrogen gas and the vials closed. For storage the caps of the vials were sealed with parafilm and the vials were maintained in the dark at room temperature (20-25° C.).   iii) Tests with dried cultures were performed as follows: the dried cells were reconstituted with 0.5 ml water for 20 minutes. Measurement was continued by incubating for 30 minutes, 1 h or 2 h at 37° C., after which light emission was recorded in a luminometer.   

     Example 10 
     Protocol for Paper Drying 
     The protocol for paper drying was similar to that of liquid drying.
     i) bacterial cultures were grown from a fresh colony in 5 ml liquid medium (Luria Broth) containing ampicillin for 16 h at 37° C. Cells were then harvested by centrifugation and the supernatant removed. The cell pellet was carefully resuspended in a medium containing gelatin, meat extract, sodium ascorbate, raffinose and sodium glutamate. Drops of 10 microliter of culture suspension were pipetted on small Whatman 3M paper strips. Up to 6 strips were placed inside a 10 ml sterile tube.   ii) Drying was performed at a constant temperature of 20° C. and gradually lowered vacuum. First, 1 h was dried at 70 mbar, the next hour at 20 mbar, after which the samples were dried at 0.5 mbar for another 12 h. The vacuum chamber was then filled with nitrogen gas and the vials closed. For storage the tubes with were maintained in the dark at room temperature (20-25° C.).   iii) tests with the dried paper cultures were performed as follows. One paper strip was placed in a vial containing 1 ml of water sample and incubated for 30 minutes at a temperature between 30 and 37° C. After 30 minutes the strips were taken out from the vial and placed on a plastic surface. 1 drop of X-Gal substrate solution for the beta-galactosidase enzyme was added to the spot with bacterial cells. After incubating for 15 minutes or longer (depending on the desired intensity of the spots) the blue color development was judged in comparison to a standard series containing zero, 0.1, 0.2 and 0.5 μM arsenite.   

     Example 11 
     Survival and Activity Tests with Dried Biosensor Cultures 
     Dried cultures in glass vials were stored at room temperature for periods up to one month. At regular intervals bacterial pellets were resuspended in water and dilution series prepared, or suspensions used for testing the immediate induction with 0.4 μM arsenite (Table 3). Directly after drying, the viability of the cultures was around 30% compared to before drying, which decreased to about 10% after one week. In some cases, the viability dropped to 1% after 21 days, whereas for other batches viability retained approximately 10% after three weeks. The reasons for this difference are presently not clear. 
     The changes in viability were more or less reflected in the potential to become immediately activated by arsenite (Table 2). The total light emission by the cultures decreased upon prolonged storage times, although the difference (or induction factor) between blanc (no arsenite) and 0.4 μM was retained, even after 21 days storage. For most luminometers, there is no problem to measure even in the range of 1000 to 10000 relative light units. 
     Table 2. Light emission after three induction times of dried cultures stored at room temperature. Test concentrations: zero and 0.4 μM arsenite. 
     
       
         
               
               
               
               
               
             
               
               
               
               
               
               
             
           
               
                   
                   
               
               
                   
                   
                   
                   
                 Induction 
               
               
                   
                 30 min 
                 1 h 
                 2 h 
                 factor(2 h) 
               
               
                   
                   
               
             
             
               
                   
               
             
          
           
               
                   
                 1d 
                   
                   
                   
                   
               
               
                   
                 storage 
               
               
                   
                 0.4 μM 
                 797691 
                 2545974 
                 7264655 
                 2.9 
               
               
                   
                 0 
                 547705 
                 2085406 
                 2487514 
               
               
                   
                 8d 
               
               
                   
                 storage 
               
               
                   
                 0.4 μM 
                 159678 
                 615092 
                 1973606 
                 3.5 
               
               
                   
                 0 
                 107123 
                 230976 
                 557872 
               
               
                   
                 21d 
               
               
                   
                 storage 
               
               
                   
                 0.4 μM 
                 714 
                 7047 
                 50622 
                 7.2 
               
               
                   
                 0 
                 310 
                 1501 
                 6966 
               
               
                   
                   
               
             
          
         
       
     
     Example 12 
     Decontamination 
     One of the concerns with using bacterial biosensors is that they are genetically modified bacteria. For the construction of the arsenic biosensor bacteria, the following precautions were made:
         A poor-surviving well known laboratory strain of  E. coli  was used for cloning, which has a long history of usage all over the world without any known pathogenicity effects and   Mostly isogenous characteristics were used: both arsR and lacZ originate from  E. coli  itself. The luciferase genes originate from  Vibrio harveyi  but do not have pathogenicity characteristics   All plasmids used are non-mobilizable and only replicate in  E. coli.      As selection marker resistance to the antibiotic ampicillin was used, which is not in clinical use and therefore is not considered to lead to increased acquired antibiotic resistance among pathogenic microorganisms.       

     Despite those measures, the question remained as to what should be done with the biosensor strains after their use for a measurement and how decontamination should take place. Considering used paper strip test, the best contamination is to burn them. With respect to liquid biosensor tests, most bacteria were quickly killed by acidifying the water-biosensor-sample with a few drops of lemon juice. This showed that almost immediately a 4-log reduction in viability could be achieved by lowering the pH. Further reduction can be achieved by more regular methods: i.e., exposure to sunlight and heat. In this respect, the used  E. coli  strains are poor survivors, which is also reflected by the difficult efforts to prepare and maintain activity in dried cultures. 
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