Jeff Skousen

Dr. Jeff Skousen

West Virginia University
orcid

Research Focus & Metrics

Academic Career Length

37Years (1990-Present)

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

Representative Publications

View All Publications
27 September 2016 in Mine Water and the Environment
Verified
Journal Article
Open access
PDF file
JSJeff Skousen
Jeff Skousen
CZCarl E. Zipper
Carl E. Zipper
ARArthur Rose
Arthur Rose
PZPaul F. Ziemkiewicz
Paul F. Ziemkiewicz
Robert NairnRobert Nairn
Robert Nairn
RKRobert L. Kleinmann
Robert L. Kleinmann
When appropriately designed and maintained, passive systems can provide long-term, efficient, and effective treatment for many acid mine drainage (AMD) sources. Passive AMD treatment relies on natural processes to neutralize acidity and to oxidize or reduce and precipitate metal contaminants. Passive treatment is most suitable for small to moderate AMD discharges of appropriate chemistry, but periodic inspection and maintenance plus eventual renovation are generally required. Passive treatment technologies can be separated into biological and geochemical types. Biological passive treatment technologies generally rely on bacterial activity, and may use organic matter to stimulate microbial sulfate reduction and to adsorb contaminants; constructed wetlands, vertical flow wetlands, and bioreactors are all examples. Geochemical systems place alkalinity-generating materials such as limestone in contact with AMD (direct treatment) or with fresh water up-gradient of the AMD. Most passive treatment systems employ multiple methods, often in series, to promote acid neutralization and oxidation and precipitation of the resulting metal flocs. Before selecting an appropriate treatment technology, the AMD conditions and chemistry must be characterized. Flow, acidity and alkalinity, metal, and dissolved oxygen concentrations are critical parameters. This paper reviews the current state of passive system technology development, provides results for various system types, and provides guidance for sizing and effective operation.

1 November 2003 in Mine Water and the Environment
Verified
Journal Article
Closed access
PDF file
PZP. F. Ziemkiewicz
P. F. Ziemkiewicz
JSJeff Skousen
Jeff Skousen
JSJ. Simmons
J. Simmons

1 July 1997 in Journal of Environmental Quality
Verified
Journal Article
Closed access
PDF file
PZP. F. Ziemkiewicz
P. F. Ziemkiewicz
JSJeff Skousen
Jeff Skousen
DBD. L. Brant
D. L. Brant
PSP. L. Sterner
P. L. Sterner
RLR. J. Lovett
R. J. Lovett

1 November 2002 in Journal of Environmental Quality
Verified
Journal Article
Closed access
PDF file
JSJeff Skousen
Jeff Skousen
JSJ. Simmons
J. Simmons
LML. M. McDonald
L. M. McDonald
PZP. Ziemkiewicz
P. Ziemkiewicz

1 June 2014 in International Journal of Coal Science & Technology
Verified
Journal Article
Open access
PDF file
JSJeff Skousen
Jeff Skousen
CZCarl E. Zipper
Carl E. Zipper
Surface coal mines prior to 1950 in the USA were generally left without any reclamation. As government regulations advanced since then, mine operators were required to backfill the area and plant grasses or trees. After the federal Surface Mining Control and Reclamation Act (SMCRA) was passed in 1977 in the USA, mine operators were required to conduct pre-mining analyses of the site and to designate a land use that could be achieved after mining. Successful reclamation, as needed to satisfy today’s societal demands, requires engineering, design, and purposeful reconstruction of the full mining disturbance, not just its surface, and control of waters leaving the mine site. Effective reclamation on modern American coal mines is fully integrated with the mining operation. A suitable and effective post-mining land use that is sustainable for future generations is crucial to the long-term success and profitability of the mining business and to the future economic benefits of the landowner. Accepted post-mining land uses in the USA are: (1) prime farmland, (2) hay land and pasture, (3) biofuel crops, (4) forestry, (5) wildlife habitat, and (6) building site development. Policies and regulations for each post-mining land use were developed and practices to achieve successful and sustainable land uses were established. Post-mining conditions should provide ecosystem services and produce lands capable of supporting societal needs in the future.

11 August 2023 in Minerals
Verified
Journal Article
Open access
PDF file
Abdulmannan RouhaniAbdulmannan Rouhani
Abdulmannan Rouhani
JSJeff Skousen
Jeff Skousen
FTFilip Tack
Filip Tack
Coal remains a very important source of energy for the global economy. Surface and underground coal mining are the two major methods of coal extraction, and both have benefits and drawbacks. Surface coal mining can have a variety of environmental impacts including ecosystem losses, landscape alteration, soil destruction, and changes to surface and groundwater quality and quantity. In addition, toxic compounds such as heavy metals, radioactive elements, polycyclic aromatic hydrocarbons (PAHs), and other organic contaminants are released in the environment, ultimately affecting the health of ecosystems and the general population. Underground mining has large impacts on underground water supplies and water quality, but generally has less visual surface impacts such as leaving waste and tailings on the surface and subsidence problems. In response to the concern about these environmental issues, many strategies have been developed by scientists and practitioners to minimize land degradation and soil pollution due to mining. Reclamation laws passed in numerous countries during the past 50 years have instituted practices to reduce the impacts of soil pollution including burying toxic materials, saving and replacing topsoil, and vegetating the land surface. While modern mining practices have decreased the environmental impacts, many sites are inadequately reclaimed and present long-lasting soil pollution problems. The current review summarizes progress in comprehending (1) coal mining impacts on soil pollution, (2) the potential risks of soil pollution associated with coal mining, and (3) different types of strategies for remediating these contaminated soils. Research and prospective directions of soil pollution in coal mining regions include refinements in assessing pollutant levels, the use of biochars and other amendments, phytoremediation of contaminated soils, and the release of toxic elements such as mercury and thallium.