- Volumes 84-95 (2024)
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Volumes 72-83 (2023)
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Volume 83
Pages 1-258 (December 2023)
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Volume 82
Pages 1-204 (November 2023)
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Volume 81
Pages 1-188 (October 2023)
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Volume 80
Pages 1-202 (September 2023)
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Volume 79
Pages 1-172 (August 2023)
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Volume 78
Pages 1-146 (July 2023)
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Volume 77
Pages 1-152 (June 2023)
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Volume 76
Pages 1-176 (May 2023)
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Volume 75
Pages 1-228 (April 2023)
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Volume 74
Pages 1-200 (March 2023)
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Volume 73
Pages 1-138 (February 2023)
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Volume 72
Pages 1-144 (January 2023)
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Volume 83
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Volumes 60-71 (2022)
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Volume 71
Pages 1-108 (December 2022)
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Volume 70
Pages 1-106 (November 2022)
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Volume 69
Pages 1-122 (October 2022)
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Volume 68
Pages 1-124 (September 2022)
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Volume 67
Pages 1-102 (August 2022)
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Volume 66
Pages 1-112 (July 2022)
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Volume 65
Pages 1-138 (June 2022)
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Volume 64
Pages 1-186 (May 2022)
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Volume 63
Pages 1-124 (April 2022)
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Volume 62
Pages 1-104 (March 2022)
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Volume 61
Pages 1-120 (February 2022)
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Volume 60
Pages 1-124 (January 2022)
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Volume 71
- Volumes 54-59 (2021)
- Volumes 48-53 (2020)
- Volumes 42-47 (2019)
- Volumes 36-41 (2018)
- Volumes 30-35 (2017)
- Volumes 24-29 (2016)
- Volumes 18-23 (2015)
- Volumes 12-17 (2014)
- Volume 11 (2013)
- Volume 10 (2012)
- Volume 9 (2011)
- Volume 8 (2010)
- Volume 7 (2009)
- Volume 6 (2008)
- Volume 5 (2007)
- Volume 4 (2006)
- Volume 3 (2005)
- Volume 2 (2004)
- Volume 1 (2003)
• Variability in dispersion characteristics of TiO2 nanopowder between protocols was assessed.
• The results highlighted the current comparability problem between many nanoecotoxicology studies.
• Concentration of nanomaterial was the largest source of variation in the protocols studied.
• Nanomaterial sampling and sonication time were also significant factors.
There is a need to standardize methods associated with the dispersion of nanomaterials in nano(eco)toxicological investigations. The first step toward this goal is to understand the degree of variability that exists in nanomaterial dispersions prepared by using different protocols. Using two case studies, the degree of variability in TiO2 nanomaterial dispersions was assessed by differential centrifugal sedimentation (DCS) methods. Case study 1 addresses the variability that arises from variations within one protocol, investigating the effects of dispersion aging, sonication exposure time, sonication in the presence/absence of an ice bath, material subsampling, particle concentration and having a pre-wetting step. Case study 2 addresses the variability between four different protocols developed through past research activities and projects. The results indicate that there is a large degree of variability (relative standard deviation (RSD) of mean particle diameter = 26%) in the dispersion of TiO2 nanomaterials between the four different protocols studied and that several steps in a dispersion protocol are potential sources of variation, with final particle concentration being the most significant. The implication of this study is clear: for the purpose of data comparability, there is a need to provide the exact details of all steps involved in a dispersion protocol.