Shamali De Silva

Dr. Shamali De Silva


Research Focus & Metrics

Academic Career Length

11Years (2016-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 January 2016 in Environmental Pollution
Verified
Journal Article
Closed access
SSShamali De Silva
Shamali De Silva
ABAndy Ball
Andy Ball
THTrang Huynh
Trang Huynh
SRSuzie Reichman
Suzie Reichman

1 January 2021 in Chemosphere
Verified
Journal Article
Closed access
SSShamali De Silva
Shamali De Silva
ABAndrew S. Ball
Andrew S. Ball
DIDemidu V. Indrapala
Demidu V. Indrapala
SRSuzie M. Reichman
Suzie M. Reichman

ZGZhuyun Gu
Zhuyun Gu
SSShamali De Silva
Shamali De Silva
SRSuzie Reichman
Suzie Reichman
Rice-based products are widely used to feed infants and young children. However, the association of rice-based products and high arsenic (As) concentrations have been investigated in a number of studies, but there is limited information from Australia. Therefore, the purpose of this study was to determine the As concentration and dietary exposure in infant rice milk, cereal, crackers and pasta as well as to investigate the relationship between As concentration and rice content, rice type and product origin. Total arsenic (tAs) concentrations were determined by nitric acid digestion and ICP-MS while inorganic arsenic (iAs) was determined by acid extraction, followed by ICP-MS with an interfaced hydride generation system. Nearly 75% of samples had inorganic As exceeding the EU maximum levels for infants and children (0.1 mg kg−1) and the mean iAs percentage of total reached as high as 84.8%. High tAs concentration was positively correlated with rice content and also related to brown (wholegrain). Estimates of dietary exposure showed that infants consuming large amounts of rice pasta or crackers will have an increased risk of health impact associated with excess intake of As through dietary exposure. Moreover, the current Australian guidelines for As in rice (1 mg kg−1) are above the WHO or EU guideline and therefore, will be less protective of high sensitivity consumers like infants and children.

1 August 2019 in Environmental Pollution
Verified
Journal Article
Closed access
SKSlavica Kandic
Slavica Kandic
STSusanne J. Tepe
Susanne J. Tepe
EBEwan W. Blanch
Ewan W. Blanch
SSShamali De Silva
Shamali De Silva
HMHannah G. Mikkonen
Hannah G. Mikkonen
SRSuzie Reichman
Suzie Reichman

1 May 2021 in Environmental Pollution
Verified
Journal Article
Closed access
SSShamali De Silva
Shamali De Silva
ABAndrew S. Ball
Andrew S. Ball
ESEsmaeil Shahsavari
Esmaeil Shahsavari
DIDemidu V. Indrapala
Demidu V. Indrapala
SRSuzie Reichman
Suzie Reichman

15 October 2020 in Environments
Verified
Journal Article
Open access
PDF file
SSShamali De Silva
Shamali De Silva
THTrang Huynh
Trang Huynh
ABAndy Ball
Andy Ball
DIDemidu V. Indrapala
Demidu V. Indrapala
SRSuzie Reichman
Suzie Reichman
Finding a reliable method to predict soil metal bioavailability in aged soil continues to be one of the most important problems in contaminated soil chemistry. To investigate the bioavailability of metals aged in soils, we used roadside soils that had accumulated metals from vehicle emissions over a range of years. We collected topsoil (0–10 cm) samples representing new-, medium- and old-aged roadside soils and control site soil. These soils were studied to compare the ability of the diffusive gradients in thin films technique (DGT), soil water extraction, CaCl2 extraction, total metal concentrations and optimised linear models to predict metal bioavailability in wheat plants. The response time for the release of metals and the effect on metal bioavailability in field aged soils was also studied. The DGT, and extractable metals such as CaCl2 extractable and soil solution metals in soil, were not well correlated with metal concentrations in wheat shoots. In comparison, the strongest relationships with concentrations in wheat shoots were found for Ni and Zn total metal concentrations in soil (e.g., Ni r = 0.750, p = 0.005 and Zn r = 0.833, p = 0.001); the correlations were still low, suggesting that total metal concentrations were also not a robust measure of bioavailability. Optimised linear models incorporating soil physiochemical properties and metal extracts together with road age as measure of exposure time, demonstrated a very strong relationship for Mn R2 = 0.936; Ni R2 = 0.936 and Zn R2 = 0.931. While all the models developed were dependent on total soil metal concentrations, models developed for Mn and Zn clearly demonstrated the effect of road age on metal bioavailability. Therefore, the optimised linear models developed have the potential for robustly predicting bioavailable metal concentrations in field soils where the metals have aged in situ. The intrinsic rate of release of metals increased for Mn (R2 = 0.617, p = 0.002) and decreased for Cd (R2 = 0.456, p = 0.096), Cu (R2 = 0.560, p = 0.083) and Zn (R2 =0.578, p = 0.072). Nickel did not show any relationship between dissociation time (Tc) and road age. Roadside soil pH was likely to be the key parameter controlling metal aging in roadside soil.