David A Dzombak

Dr. David A Dzombak

Carnegie Mellon University
orcid

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 June 2011 in Elements
Verified
Journal Article
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KGKelvin B. Gregory
Kelvin B. Gregory
Radisav D. VidicRadisav D. Vidic
Radisav D. Vidic
David A DzombakDavid A Dzombak
David A Dzombak
Development of unconventional, onshore natural gas resources in deep shales is rapidly expanding to meet global energy needs. Water management has emerged as a critical issue in the development of these inland gas reservoirs, where hydraulic fracturing is used to liberate the gas. Following hydraulic fracturing, large volumes of water containing very high concentrations of total dissolved solids (TDS) return to the surface. The TDS concentration in this wastewater, also known as “flowback,” can reach 5 times that of sea water. Wastewaters that contain high TDS levels are challenging and costly to treat. Economical production of shale gas resources will require creative management of flowback to ensure protection of groundwater and surface water resources. Currently, deep-well injection is the primary means of management. However, in many areas where shale gas production will be abundant, deep-well injection sites are not available. With global concerns over the quality and quantity of fresh water, novel water management strategies and treatment technologies that will enable environmentally sustainable and economically feasible natural gas extraction will be critical for the development of this vast energy source.

26 February 2018 in Green Chemistry
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Journal Article
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JCJonathan C. Callura
Jonathan C. Callura
KPKedar M. Perkins
Kedar M. Perkins
CNClinton W. Noack
Clinton W. Noack
NWNewell R. Washburn
Newell R. Washburn
David A DzombakDavid A Dzombak
David A Dzombak
AKAthanasios K. Karamalidis
Athanasios K. Karamalidis
Rare earth elements (REE) are essential components of equipment used for renewable energy, green technologies, and more traditional sectors such as chemical catalysis and metallurgy. Interest has been growing in alternative REE sources to supplement current ore sources and related refining, which have historically supplied the bulk of REE oxides. This study investigated the capability of adsorbent silica particles functionalized with three different ligands – phosphonoacetic acid (PAA), N,N-bisphosphono(methyl)glycine (BPG), and diethylenetriaminepentaacetic dianhydride (DTPADA) – to selectively extract REE from acidic to circumneutral aqueous brine solutions in equilibrium conditions. Maximum REE removal from 0.5 M NaCl solutions was displayed at pH 7 for PAA, pH 2 for DTPADA, and in both acidic and basic conditions for BPG functionalized materials. The REE adsorption performance for functionalized materials was largely unimpeded by the presence of competing ions (Ca, Mg, Zn, Fe, Al). Tests with real brines (I ∼ 3 M) showed >90% efficiency in REE recovery, which improved at higher temperatures (up to 100 °C). Effective elution of REE was accomplished with 0.7 N HNO3, and performance of the adsorbents improved with additional usage cycles.

1 June 2009 in Journal of Environmental Engineering
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Journal Article
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SKSameer Khaitan
Sameer Khaitan
David A DzombakDavid A Dzombak
David A Dzombak
GLGregory V Lowry
Gregory V Lowry
Bauxite residue (red mud), an alkaline slurry from alumina refining, is produced in large volumes and disposed of in large surface impoundments. The objectives of this study were to measure the extent of neutralization of bauxite residue by carbon dioxide as a function of C O2 partial pressure and to determine the geochemical reactions responsible for carbon sequestration. Bauxite residue was exposed to carbon dioxide (C O2 ) at partial pressures ranging from 10−3.5 to 1 atm and the residue pore-water pH was measured until a steady state pH was achieved. Using pure C O2 ( PC O2 =1 atm) , a steady state pH of 7.7 was established in 1 day while it took 9 days to reach a pH of 9.8 at PC O2 = 10−3.5 atm . The pH rebounded to 9.9 after 1 day when bauxite residue first neutralized at PC O2 of 1, 0.1, or 0.01 atm for 10 days was subsequently exposed to PC O2 = 10−3.5 atm , indicating that the pH change during short-term carbonation (t⩽10 days) was due to reactions of carbonic acid and O H− in the pore water. A l...

1 October 2010 in Journal of Environmental Engineering
Verified
Journal Article
Closed access
SKSameer Khaitan
Sameer Khaitan
David A DzombakDavid A Dzombak
David A Dzombak
PSPeter Swallow
Peter Swallow
KSKeith Schmidt
Keith Schmidt
JFJaw Fu
Jaw Fu
GLGregory V Lowry
Gregory V Lowry
The objective of this study was to investigate the mechanisms and extent of bauxite residue (red mud) neutralization at the residue surface in field impoundments as a result of long-term reaction with atmospheric CO2 and addition of amendments to promote vegetation. The results showed that carbonation from atmospheric carbon dioxide reduces the pH of red mud from 12.5 to about pH 9.3 at the surface of storage cells, with the depth of neutralization dependent on the age of the stored residue (up to 1.2 m in 35 years). The presence of vegetation further lowered residue pH to about pH 8.5, with the depth of neutralization dependent on depth of root penetration. Sewage and yard-waste amendments accelerated neutralization and the establishment of vegetation and further lowered the residue pH to about pH 6.7, likely due to organic acid leaching. For vegetated areas, the root density (g roots/g soil) was proportional to the extent of neutralization of residue, with root density higher in near-surface residue tha...

1 December 2010 in Water Environment Research
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Journal Article
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MHMing‐Kai Hsieh
Ming‐Kai Hsieh
HLHeng Li
Heng Li
SCShih‐Hsiang Chien
Shih‐Hsiang Chien
JMJason D. Monnell
Jason D. Monnell
ICIndranil Chowdhury
Indranil Chowdhury
Radisav D. VidicRadisav D. Vidic
Radisav D. Vidic

1 December 2019 in Journal of Colloid and Interface Science
Verified
Journal Article
Closed access
JCJonathan C. Callura
Jonathan C. Callura
KPKedar M. Perkins
Kedar M. Perkins
JBJohn P. Baltrus
John P. Baltrus
NWNewell R. Washburn
Newell R. Washburn
David A DzombakDavid A Dzombak
David A Dzombak
AKAthanasios K. Karamalidis
Athanasios K. Karamalidis