Andrew Smallbone

Dr. Andrew Smallbone

Engineering Department, Durham University, Durham DH1 3LE, UK
orcid

Research Focus & Metrics

Academic Career Length

23Years (2004-Present)

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

Representative Publications

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1 November 2017 in Energy Conversion and Management
Verified
Journal Article
Open access
Andrew SmallboneAndrew Smallbone
Andrew Smallbone
VJVerena Jülch
Verena Jülch
RWRobin Wardle
Robin Wardle
ARAnthony Paul Roskilly
Anthony Paul Roskilly

1 June 2010 in Combustion and Flame
Verified
Journal Article
Closed access
NMNeal Morgan
Neal Morgan
Andrew SmallboneAndrew Smallbone
Andrew Smallbone
ABAmit Bhave
Amit Bhave
MKMarkus Kraft
Markus Kraft
Roger CracknellRoger Cracknell
Roger Cracknell
GKGautam Kalghatgi
Gautam Kalghatgi

1 November 2016 in Desalination
Verified
Journal Article
Open access
MAM. Sarai Atab
M. Sarai Atab
Andrew SmallboneAndrew Smallbone
Andrew Smallbone
ARA.P. Roskilly
A.P. Roskilly
Desalination is a method for producing water for human consumption, irrigation or industrial utilisation. In this study, a reverse osmosis (RO) system for brackish water desalination was theoretically investigated to produce both potable drinking and agricultural water with a lower overall and specific energy consumption. As a case study, the Main Outfall Drain in Iraq is used as the brackish water source. A numerical model based on solution-diffusion theory was developed in Matlab Simulink and used to analyse the design and performance of an RO system. The effect of feed water temperature, pressure, salinity and recovery ratio on the efficiency of the whole RO system was investigated for a wide range of design considerations. The design of an RO system for this application was optimised and economic assessment carried out. Results show that with boosting recovery ratio from 30% to 60%, the specific energy of desalinated water production below 400ppm was reduced from 2.8kWh/m3 to a more economically favourable value of 0.8kWh/m3, when utilizing a pressure exchanger as a recovery device. Salt rejection was reduced from 97% to 88% to obtain large quantities of water for irrigation with an acceptable salinity (<1600ppm), for agricultural use. The reduction in salt rejection is influenced by the feed water temperature and pressure; also the average pore diameter of the RO membrane and in turn determines the reduction in system energy consumption. It was found that the total cost to produce 24,000m3/d of water from a feed salinity of 15,000ppm and a water quality of <400ppm would be 0.11£/m3 with a corresponding investment cost of £14.4million for the drinking water, and for irrigation) obtained product <1600ppm) are £0.9/m3 and £11.3million

1 July 2019 in Applied Energy
Verified
Journal Article
Open access
LJLong Jiang
Long Jiang
ADAbigail Gonzalez Diaz
Abigail Gonzalez Diaz
JLJ. Ling-Chin
J. Ling-Chin
ARA.P. Roskilly
A.P. Roskilly
Andrew SmallboneAndrew Smallbone
Andrew Smallbone

1 January 2011 in Proceedings of the Combustion Institute
Verified
Journal Article
Closed access
AKA.P. Kelley
A.P. Kelley
Andrew SmallboneAndrew Smallbone
Andrew Smallbone
DZD.L. Zhu
D.L. Zhu
CLC.K. Law
C.K. Law

1 March 2017 in Applied Energy
Verified
Journal Article
Open access
ABAmit Bhave
Amit Bhave
RTRichard H.S. Taylor
Richard H.S. Taylor
PFP. Fennell
P. Fennell
WLWilliam R. Livingston
William R. Livingston
NSNilay Shah
Nilay Shah
JAJethro Akroyd
Jethro Akroyd
Biomass-based power generation combined with CO2 capture and storage (Biopower CCS) currently represents one of the few practical and economic means of removing large quantities of CO2 from the atmosphere, and the only approach that involves the generation of electricity at the same time. We present the results of the Techno-Economic Study of Biomass to Power with CO2capture (TESBiC) project, that entailed desk-based review and analysis, process engineering, optimisation as well as primary data collection from some of the leading pilot demonstration plants. From the perspective of being able to deploy Biopower CCS by 2050, twenty-eight Biopower CCS technology combinations involving combustion or gasification of biomass (either dedicated or co-fired with coal) together with pre-, oxy- or post-combustion CO2 capture were identified and assessed. In addition to the capital and operating costs, techno-economic characteristics such as electrical efficiencies (LHV% basis), Levelised Cost of Electricity (LCOE), costs of CO2 captured and CO2 avoided were modelled over time assuming technology improvements from today to 2050. Many of the Biopower CCS technologies gave relatively similar techno-economic results when analysed at the same scale, with the plant scale (MWe) observed to be the principal driver of CAPEX (£/MWe) and the cofiring % (i.e. the weighted feedstock cost) a key driver of LCOE. The data collected during the TESBiC project also highlighted the lack of financial incentives for generation of electricity with negative CO2 emissions