David A. Roberts

Dr. David A. Roberts


Research Focus & Metrics

Academic Career Length

25Years (2002-Present)

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

Representative Publications

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1 October 2010 in Water Research
Verified
Journal Article
Closed access
DRDavid A. Roberts
David A. Roberts
EJEmma L. Johnston
Emma L. Johnston
NKNathan A. Knott
Nathan A. Knott

1 June 2009 in Environmental Pollution
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Journal Article
Closed access
EJEmma L. Johnston
Emma L. Johnston
DRDavid A. Roberts
David A. Roberts

1 April 2012 in Environment International
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Journal Article
Closed access
DRDavid A. Roberts
David A. Roberts

9 April 2015 in Scientific Reports
Verified
Journal Article
Open access
DRDavid A. Roberts
David A. Roberts
NPNicholas Paul
Nicholas Paul
Symon DworjanynSymon Dworjanyn
Symon Dworjanyn
MBMichael Bird
Michael Bird
RNRocky de Nys
Rocky de Nys
Seaweed cultivation is a high growth industry that is primarily targeted at human food and hydrocolloid markets. However, seaweed biomass also offers a feedstock for the production of nutrient-rich biochar for soil amelioration. We provide the first data of biochar yield and characteristics from intensively cultivated seaweeds (Saccharina, Undaria and Sargassum – brown seaweeds and Gracilaria, Kappaphycus and Eucheuma – red seaweeds). While there is some variability in biochar properties as a function of the origin of seaweed, there are several defining and consistent characteristics of seaweed biochar, in particular a relatively low C content and surface area but high yield, essential trace elements (N, P and K) and exchangeable cations (particularly K). The pH of seaweed biochar ranges from neutral (7) to alkaline (11), allowing for broad-spectrum applications in diverse soil types. We find that seaweed biochar is a unique material for soil amelioration that is consistently different to biochar derived from ligno-cellulosic feedstock. Blending of seaweed and ligno-cellulosic biochar could provide a soil ameliorant that combines a high fixed C content with a mineral-rich substrate to enhance crop productivity.

9 October 2012 in Global Change Biology
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Journal Article
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DRDavid A. Roberts
David A. Roberts
SBSilvana N. R. Birchenough
Silvana N. R. Birchenough
CLCeri Lewis
Ceri Lewis
MSMatthew B. Sanders
Matthew B. Sanders
TBThi Bolam
Thi Bolam
DSDave Sheahan
Dave Sheahan

22 November 2013 in PLOS ONE
Verified
Journal Article
Open access
PDF file
DRDavid A. Roberts
David A. Roberts
RNRocky de Nys
Rocky de Nys
NPNicholas Paul
Nicholas Paul
The energy, mining and mineral processing industries are point sources of metal-contaminated waste water and carbon dioxide (CO2). Freshwater macroalgae from the genus Oedogonium can be grown in metal-contaminated waste water to generate biomass for bioenergy applications and concomitantly bioremediate metals. However, interactions between CO2 addition and algal growth, which can affect bioremediation, remain untested. The addition of CO2 to algal cultures in the Ash Dam Water (ADW) from a coal-fired power station increased the biomass productivity of Oedogonium sp. from 6.8 g dry weight (DW) m-2 d-1 to a maximum of 22.5 g DW m-2 d-1. The greater productivity increased the rate of bioremediation of most elements. However, over time carbon-amended cultures experienced a decline in productivity. Possible explanations include metal toxicity at low pH or essential trace element limitation as a result of competition between toxic and essential trace elements for uptake into algae. Higher productivity increased bioremediation rate and yielded more biomass for bioenergy applications, making maintenance of maximum productivity the central aim of the integrated culture model. To do so it will be necessary to resolve the mechanisms responsible for declining yields over time in carbon-amended cultures. Regardless, our data demonstrate that freshwater macroalgae are ideal candidates for bioremediation of metal-contaminated waste streams. Algal culture delivered significant improvement in ADW quality, reducing 5 elements that were initially in excess of water quality criteria (Al, As, Cd, Ni and Zn) to meet guidelines within two to four weeks.