Silver get washed into sewerage systems and eventually to wastewater treatment plant (WWTP) due to its utilization in industries. This poses concerns about the toxicity of these particles to microorganisms which are involved in biodegradation of organic wastes in biological WWTP. Pseudomonas species (Biosensor cell A, B, C, D and E) originally isolated from WWTP and modified by incorporating a stable chromosomal copy of the lux operon (lux CDABE) derived from Escherichia coli S17ƛ pir were sensitive immediately upon addition of silver nanoparticles (AgNPs) and bulk silver in short terms of incubation ranging from 0 to 300minutes. Microtitre plate luminometre was used to generate detailed luminescence reduction data for the silver particles tested against the bacterial cells in various concentrations ranging from 9µg/ml to 2500µg/ml. The EC50 values generated at various time points showed that the highest toxicity was observed at time point, 0 of incubation for both AgNPs and bulk silver (158µg/ml and 618µg/ml EC50 values respectively); these EC50 values also indicate that AgNPs are much more toxic than bulk silver. Two putative biosensors, E and D showed proportional responses of bioluminescence reduction with increasing toxicant concentrations up to 2500µg/ml, hence displaying dose-dependent responses, superior operational range and sensing capabilities; good features for toxicity assay. Therefore, the recombinant isolate can be used to assay the toxicity of silver particles.
Published in | Frontiers in Environmental Microbiology (Volume 3, Issue 2) |
DOI | 10.11648/j.fem.20170302.12 |
Page(s) | 30-38 |
Creative Commons |
This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited. |
Copyright |
Copyright © The Author(s), 2017. Published by Science Publishing Group |
Pseudomonas Species, Recombinant, Bioluminescence, Biosensor Cells
[1] | Ahmed, S., Ahmad, M., Swami, B. and Ikram, S. (2016). A review on plant extract mediated synthesis of silver nanoparticles for antimicrobial applications: A green expertise. Journal of Advance Research 7 (1): 17-28. |
[2] | Brar, S., Verma, M., Tyagi, R. and Surampalli, Y. (2010). Engineered nanoparticles in wastewater sludge—evidence and impacts. Wastes Management 30: 504–520. |
[3] | Been, T. and Westerhoff, P. (2008). Nanoparticle silver released into water from commercially available sock fabrics. Environmental Science and Technology. 42: 4133–4139. |
[4] | Kittler, S., Greulich, C., Diendorf, J., Köller, M. and Epple, M. (2010). Toxicity of silver nanoparticles increases during storage because of slow dissolution under release of silver ions. Chemistry of Materials. 22: 4548-4554. |
[5] | Wiles, S., Whiteley, A., Philip, J. and Bailey, M. (2003). Development of bespoke bioluminescent reporters with the potential for in situ deployment within a phenolic remediating wastewater treatment system. Journal of Microbiology Methods 5: 667–677. |
[6] | Blaser, S., Scheringer, M., MacLeod, A., Hungerbühler, K. (2010). Estimation of cumulative aquatic exposure and risk due to silver: contribution of nano-functionalized plastics and textiles. Science of the Total Environment 390: 396–409. |
[7] | Farre, M. and Barcelo, D. (2003). Toxic testing of wastewater and sewage sludge by biosensors, bioassays and chemical analysis. Trends in Analytical Chemistry 22: 299-310. |
[8] | Girotti, S., Ferri, E. N., Fumo, M. G. and Maiolini, E. (2008). Monitoring of environmental pollutants by bioluminescent bacteria. Analytica Chimica Acta 608: 2-29. |
[9] | Pasricha, A., Jangra, S. L., Singh, N., Dilbaghi, N., Sood, K. N. and Arora, K. A. (2012). Comparative study of leaching of silver nanoparticles from fabric and effective effluent treatment. Journal of Environmental Science 24: 852 – 859. |
[10] | Dams. R. I., Biswas, A., Olesiejuk, A., Fernandes, T. and Christofi, N. (2011). Silver nanotoxicity using a light-emitting biosensor Pseudomonas putida isolated from wastewater treatment plant. Journal of Hazardous Materials 195: 68-72. |
[11] | Paulraj, K. and Seung, T. (2013). Synthesis and characterization of pullulan-mediated silver nanoparticles and its antimicrobial activities. Carbohydrate Polymers 97: 421–428. |
[12] | Holt, J. G., Krieg, N. R., Sneath, P. H. A., Stanley J. T and Williams S. T. (1994). Bergey’s manual of determinative Bacteriology. 9th Ed. Williams and Wilkins, pp: 71 – 561. |
[13] | Arnau, C., Francisco, L. and Anicet, R. (2010). Identification of Pseudomonas aeruginosa in water-bottling plants on the basis of procedures included in ISO 16266:2006. Journal of Microbiology 81: 1–5. |
[14] | Piccapietra, F., Sigg, L. and Behra, R. (2012). Colloidal stability of carbonate-coated silver nanoparticles in synthetic and natural freshwater. Environmental Science & Technology 46: 818-825. |
[15] | Farre, M., Gajda-Schrantz, K., Kantiani, L. and Barcelo, D. (2009). Ecotoxicity and analysis of nanomaterials in the aquatic environment. Analytical and Bioanalytical Chemistry 393: 81-95. |
[16] | Brunner, T., Wick, P., Manser, P., Spohn, R., Grass, L., Limbach, A., Bruinink, A. and Stark, W. (2006). In-vitro cytotoxicity of oxide nanoparticles: comparison to asbestos, silica, and the effect of particle solubility. Environmental Science and Technology 40: 4374–4381. |
[17] | Tolaymat, T. M. (2010). Impact of environmental conditions (ph, ionic strength, and electrolyte type) on the surface charge and aggregation of silver nanoparticles suspensions. Environmental Science and Technology 44 (4): 1260-1266. |
[18] | Yang, Y., Chen, Q., Wall, J. D. and Hu, Z. (2012). Potential nano-silver impact on anaerobic digestion at moderate silver concentrations. Water Research 46: 1176-1184. |
[19] | Sinha, R., Karan, R., Sinha, A. and Khare, S. K. (2010). Interaction and nanotoxic effect of ZnO and Ag nanoparticles on mesophilic and halophilic bacterial cells. Bioresource Technology 102 (2): 1516-1520. |
[20] | Badawy, A. M. E., Luxton, T. P., Silva, R. G., Scheckel, K. G., Suidan, M. T. and Tolaymat, T. M. (2010). Impact of environmental conditions (ph, ionic strength, and electrolyte type) on the surface charge and aggregation of silver nanoparticles suspensions. Environmental Science & Technology 44: 1260-1266. |
[21] | Nowack, B. and Bucheli, T. (2007). Occurence, behaviour and effects of nanoparticles in the environment. Environmental Pollution 150: 5–22. |
[22] | Marincs, F. and White, D. W. R. (1994). Immobilization of Escherichia coli expressing the lux genes of Xenorhabdus luminescens. Applied and Environmental Microbiology 60 (10): 3862-3863. |
[23] | Kim, B. and Gu, M. B. (2003). A bioluminescent sensor for high throughput toxicity classification. Biosensors and Bioelectronics 18: 1015-1021. |
[24] | Gil, G. C., Mitchell, R. J., Chang, S. T. and Gu, M. B. (2000). A biosensor for the detection of gas toxicity using a recombinant bioluminescent bacterium. Biosensors & Bioelectronics 15: 23-30. |
[25] | Gondikas, A., Morris, A., Reinsch, B., Marinakos, S., Lowry, G and Hsu-Kim, H. (2012). Cysteine-induced modification of zero-valent silver nanomaterials: implications for particle surface chemistry, aggregation, dissolution, and speciation. Environmental Science and Technology 46: 7037–7045. |
[26] | Hsueh, Y., Lin, K., S, Ke, W. and Chiang, C. (2015). The antimicrobial properties of silver nanoparticles in Bacillus subtilis are mediated by released Ag+ ions. Journal.pone. 0144306. |
[27] | Calabrese, E. J. and Baldwin, L. A. (2001). Hormesis: U-shaped dose responses and their centrality in toxicology. Trends in Pharmacological Sciences 22 (6): 285-291. |
[28] | Puzyn, T., Rasulev, B., Gajewicz, A., Hu, X., Dasari, T., Michalkova, A., Hwang, H., Toropov, A., Leszczynska, D. and Leszczynski, J. (2011). Using nano-QSAR to predict the cytotoxicity of metal oxide nanoparticles. Nature Nanotechnology 6. |
[29] | Tiede, K., Hassellov, M., Breitbarth, E., Chaudhry, Q. and Boxall, A. (2009). Considerations for environmental fate and ecotoxicity testing to support environmental risk assessment for nanoparticles. Journal of Chromatography A 1216: 503–509. |
APA Style
Elizabeth Omolola Oladapo, Fiona Stainsby, Mohammed Sani Abdulsalami, Enimie Endurance Oaikhena. (2017). Development of High-Throughput Methods for Nano- and Bulk Silver Toxicity Assays Using Bioluminescent Recombinant Pseudomonas Wastewater Isolates. Frontiers in Environmental Microbiology, 3(2), 30-38. https://doi.org/10.11648/j.fem.20170302.12
ACS Style
Elizabeth Omolola Oladapo; Fiona Stainsby; Mohammed Sani Abdulsalami; Enimie Endurance Oaikhena. Development of High-Throughput Methods for Nano- and Bulk Silver Toxicity Assays Using Bioluminescent Recombinant Pseudomonas Wastewater Isolates. Front. Environ. Microbiol. 2017, 3(2), 30-38. doi: 10.11648/j.fem.20170302.12
AMA Style
Elizabeth Omolola Oladapo, Fiona Stainsby, Mohammed Sani Abdulsalami, Enimie Endurance Oaikhena. Development of High-Throughput Methods for Nano- and Bulk Silver Toxicity Assays Using Bioluminescent Recombinant Pseudomonas Wastewater Isolates. Front Environ Microbiol. 2017;3(2):30-38. doi: 10.11648/j.fem.20170302.12
@article{10.11648/j.fem.20170302.12, author = {Elizabeth Omolola Oladapo and Fiona Stainsby and Mohammed Sani Abdulsalami and Enimie Endurance Oaikhena}, title = {Development of High-Throughput Methods for Nano- and Bulk Silver Toxicity Assays Using Bioluminescent Recombinant Pseudomonas Wastewater Isolates}, journal = {Frontiers in Environmental Microbiology}, volume = {3}, number = {2}, pages = {30-38}, doi = {10.11648/j.fem.20170302.12}, url = {https://doi.org/10.11648/j.fem.20170302.12}, eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.fem.20170302.12}, abstract = {Silver get washed into sewerage systems and eventually to wastewater treatment plant (WWTP) due to its utilization in industries. This poses concerns about the toxicity of these particles to microorganisms which are involved in biodegradation of organic wastes in biological WWTP. Pseudomonas species (Biosensor cell A, B, C, D and E) originally isolated from WWTP and modified by incorporating a stable chromosomal copy of the lux operon (lux CDABE) derived from Escherichia coli S17ƛ pir were sensitive immediately upon addition of silver nanoparticles (AgNPs) and bulk silver in short terms of incubation ranging from 0 to 300minutes. Microtitre plate luminometre was used to generate detailed luminescence reduction data for the silver particles tested against the bacterial cells in various concentrations ranging from 9µg/ml to 2500µg/ml. The EC50 values generated at various time points showed that the highest toxicity was observed at time point, 0 of incubation for both AgNPs and bulk silver (158µg/ml and 618µg/ml EC50 values respectively); these EC50 values also indicate that AgNPs are much more toxic than bulk silver. Two putative biosensors, E and D showed proportional responses of bioluminescence reduction with increasing toxicant concentrations up to 2500µg/ml, hence displaying dose-dependent responses, superior operational range and sensing capabilities; good features for toxicity assay. Therefore, the recombinant isolate can be used to assay the toxicity of silver particles.}, year = {2017} }
TY - JOUR T1 - Development of High-Throughput Methods for Nano- and Bulk Silver Toxicity Assays Using Bioluminescent Recombinant Pseudomonas Wastewater Isolates AU - Elizabeth Omolola Oladapo AU - Fiona Stainsby AU - Mohammed Sani Abdulsalami AU - Enimie Endurance Oaikhena Y1 - 2017/05/30 PY - 2017 N1 - https://doi.org/10.11648/j.fem.20170302.12 DO - 10.11648/j.fem.20170302.12 T2 - Frontiers in Environmental Microbiology JF - Frontiers in Environmental Microbiology JO - Frontiers in Environmental Microbiology SP - 30 EP - 38 PB - Science Publishing Group SN - 2469-8067 UR - https://doi.org/10.11648/j.fem.20170302.12 AB - Silver get washed into sewerage systems and eventually to wastewater treatment plant (WWTP) due to its utilization in industries. This poses concerns about the toxicity of these particles to microorganisms which are involved in biodegradation of organic wastes in biological WWTP. Pseudomonas species (Biosensor cell A, B, C, D and E) originally isolated from WWTP and modified by incorporating a stable chromosomal copy of the lux operon (lux CDABE) derived from Escherichia coli S17ƛ pir were sensitive immediately upon addition of silver nanoparticles (AgNPs) and bulk silver in short terms of incubation ranging from 0 to 300minutes. Microtitre plate luminometre was used to generate detailed luminescence reduction data for the silver particles tested against the bacterial cells in various concentrations ranging from 9µg/ml to 2500µg/ml. The EC50 values generated at various time points showed that the highest toxicity was observed at time point, 0 of incubation for both AgNPs and bulk silver (158µg/ml and 618µg/ml EC50 values respectively); these EC50 values also indicate that AgNPs are much more toxic than bulk silver. Two putative biosensors, E and D showed proportional responses of bioluminescence reduction with increasing toxicant concentrations up to 2500µg/ml, hence displaying dose-dependent responses, superior operational range and sensing capabilities; good features for toxicity assay. Therefore, the recombinant isolate can be used to assay the toxicity of silver particles. VL - 3 IS - 2 ER -