https://ogma.newcastle.edu.au/vital/access/ /manager/Index en-au 5 https://ogma.newcastle.edu.au/vital/access/ /manager/Repository/uon:15864 Wed 11 Apr 2018 18:14:17 AEST ]]> https://ogma.newcastle.edu.au/vital/access/ /manager/Repository/uon:18776 Wed 11 Apr 2018 10:37:58 AEST ]]> https://ogma.newcastle.edu.au/vital/access/ /manager/Repository/uon:40661 Thu 28 Jul 2022 11:59:38 AEST ]]> https://ogma.newcastle.edu.au/vital/access/ /manager/Repository/uon:48034 Thu 16 Feb 2023 10:43:07 AEDT ]]> https://ogma.newcastle.edu.au/vital/access/ /manager/Repository/uon:7713 Sat 24 Mar 2018 08:41:37 AEDT ]]> https://ogma.newcastle.edu.au/vital/access/ /manager/Repository/uon:30613 −, toxic contaminants CN⁻ and AsO₃³⁻/AsO₄³⁻, and anionic fluorosurfactants. The anionic fluorosurfactants mainly include perfluorooctane sulfonate (PFOS) and perfluorooctanoic acid (PFOA), both of which have recently been listed as emerging contaminants and categorised as persistent organic pollutants. This review addresses recent advancements in the development of gold nanoparticle-based nano-sensors for such anions and outlines their performance limitations towards on-site applications.]]> Sat 24 Mar 2018 07:28:26 AEDT ]]> https://ogma.newcastle.edu.au/vital/access/ /manager/Repository/uon:35728 TRIM >DV55. Meanwhile, in contrast with the observations in HMC-MIP, there was an enhancement on the fluorescent signal generated by BAP-MIP in the presence of template molecules. In addition, changing the molar ratio of EGDMA in MIP and NIP prepared from BAP functional monomer also could influence the fluorescence intensities. Results suggest that both MIP and NIP prepared using a molar ratio of 1:4:10 (DNT:BAP:EGDMA) generated the highest fluorescence intensity as compared to samples with ratio 1:4:20 and 1:4:30 (DNT:BAP:EGDMA).]]> Mon 11 Nov 2019 13:02:32 AEDT ]]>