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LITERATURE: REFORESTATION OF MINED LANDS
Contact information: Jack Nawrot (618) 536-7766
jnawrot@siu.edu
OSM library -
To Locate copies of the following publications, contact:
Debbie McGinnis, OSM Librarian, (303) 844-1436 dmcginni@osmre.gov.
Andrews, J. A., J. E. Johnson, J. L. Torbert, J. A. Burger, and
D. L. Kelting. 1998. Minesoil and site properties associated with early
height growth of eastern white pine. J. Environ. Qual. 27:192-199.
Thirty two minesoil physical and chemical properties were
investigated for impact on tree growth. Rooting depth was the minesoil
property most strongly related to height growth. The most important
chemical property affecting white pine growth was total soluble salts.
The second most important soil chemical property was extractable P.
Generally, height declined when exchangeable Mn levels exceeded 20
Mg/kg. Height growth was greater on steeper slopes where compaction was
less.
Ashby, W. C. 1998. Reclamation with trees pre- and post-SMCRA in
southern Illinois, Intl. J. Surface Mining Recl. and Envir. 12:117-121.
Survival and heights of trees of similar ages planted pre-law and
post-law are compared. Survival of some species was adversely affected
on post-SMCRA sites. Minesoils with non-toxic coarse fragments can
provide short-term benefits for water retention and erosion control and
as the coarse fragments weather, progressively greater long-term
benefits for tree performance.
Ashby, W.C. and W.G. Vogel. 1993.
Tree planting on Mined Lands
in the Midwest. A Handbook (7.4MB pdf file). Coal Research Center, Southern Illinois
University at Carbondale. 115p.
A how to manual for tree planting on mined lands in the Midwestern
U.S. It includes chapter on: (1) Reclamation with trees; (2) The
Midwest Coal Region; (3) Factors Affecting Reclamation Success; (4)
Pre-planting Site Preparation and Management; (5) Types of Plants for
Reclamation; (6) Annotated Listing of Recommended Species; (7) Plant
Materials and Handling; (8) Planting Practices; (9) Suggested Land Uses
and Species Selections; and (10) Summary of Dos and DON'Ts for
Reclamation with Trees.
Ashby, W. C., W. G. Vogel, C. A. Kolar, and G. R. Philo. 1984.
Productivity of stony soils on stripmines. p. 31-44 In J.D. Nichols et
al. (eds). Erosion and productivity of soils containing rock fragments.
Special Publication 13. Soil Science Society of America. Madison WI.
Mine soils with course fragments may have productivity equal to or
greater than pre-mining soils. Removal of stones from potato soils in
Maine and New Brunswick resulted in reduced infiltration rates, more
runoff and erosion, less soil water, lower temperature, and greater
compactability. Excellent tree growth has been observed on uncompacted
stony mine soils.
Ashby, W. C., 1982. Is good for trees good for corn? Seminar:
Postmining Productivity with Trees. Southern Illinois Univ. Carbondale,
pp15-18.
The author argues that salvaging soil and grading under SMCRA results
in a compacted substrate that retards tree growth.
Burger, James A., 1999. Reforestation and Forestry Land Uses of
Reclaimed Mined Land, Research Summary, Powell River Project, Dept. of
Forestry, Virginia polytechnic Institute and State University,
Blacksburg, VA 24061, 18p.
Documents the value of mined lands properly reclaimed to forest and
contrasts that with low value of land improperly reclaimed with grasses
and legumes and then abandoned. The authors give proven techniques for
the establishment of productive forests and document the differential
impact of substrate quality on tree growth and forage production.
Projections of the value of timber grown on average post SMCRA reclaimed
sites, average Appalachian sites and good minesoil in Virginia are
given.
Burger, James A., Daniel L. Kelting, and Carl Zipper, 1998.
Maximizing the value of forests on reclaimed mined land, Powell River
Project, Reclamation guidelines for Surface-Mined Land in Southwest
Virginia, Pub. No. 460-138, 9p.
The value of second-growth forests is resurging in Appalachia.
Reforestation of land that has been surfaced mined for coal can result
in high-value commercial forests. However, since the passage of the
Surface Mining Control and Reclamation Act in 1977 fewer acres have been
reclaimed to forest than was the case before passage. The authors
summarize research demonstrating techniques for establishment of
productive forests at costs that are $200 to $500 per acre less than
typical reclamation costs.
Burger, James A. and John L. Torbert, 1997. Reclamation
Guidelines for Surface-Mined Land in Southwest Virginia, Restoring
Forests on Surface-Mined Land, Pub. No. 460-123, Virginia Cooperative
Extension.
The purpose of the paper is to provide practical, cost-effective
guidelines for reclaiming surface-mined land to forest. The paper
addresses spoil selection, grading, tree-compatible groundcover, tree
species selection, hydroseeding trees, seedling handling and planting
techniques, establishing trees in dense ground cover, cost of
reforestation and importance of mine soil quality for forests. Forests
can be established on reclaimed mined lands with little or no additional
effort or expense. The cost per acre may be substantially less than for
other reclamation alternatives.
Bussler, B. H., W. R. Byrnes, P. E. Pope, and W. R. Chaney. 1984.
Properties of mine soil reclaimed for forest land use. Soil Sci. Soc.
Am. J. 48:178-184.
Physical and chemical properties of minesoils reclaimed for forest
land use in southwestern Indiana were evaluated to determine suitability
for reforestation. Properties of reconstructed minesoils and unmined
reference soils were compared. Both the reclaimed mineland site and
reference site supported mixed upland hardwood trees and shrub
vegetation prior to surface mining. Chemical properties of minesoils
were similar to or more favorable for plant growth than unmined
reference soils. However, physical properties of the rooting zone were
less favorable in minesoils than reference soils. Minesoils had higher
bulk density, lower porosity, lower permeability, higher coarse fragment
and clay content, and lower available water-holding capacity than
reference soils at comparable depths.
Daniels, W. Lee and Carl E. Zipper. 1997. Creation and management
of productive mine soils. VA Cooperative Extension Publication 460-121,
12p.
Selective handling of soil and overburden materials are described
that will result in productive mine soils for forage production or
forests. The limitation and proper interpretation of soil testing
procedures are described. Techniques for identifying proper strata and
avoidance of excessive compaction are discussed. When properly
constructed minesoils can be more productive than many of the
Appalachian region’s natural soils.
Schoenholtz, S. H., and J. A. Burger. 1984. Influence of cultural
treatments on survival and growth of pines on strip-mined sites.
Reclamation and Revegetation Research 3:223-237.
The effects of cultural treatments, including ectomycorrhizal
inoculation, chemical weed control and slow-release fertilization on
survival and growth of container-grown Pinus strobus L., Pinus
taeda L., and Pinus virginiana Mill, seedlings were studied
on a re-contoured and a flat-bench strip-mine site in southwestern
Virginia. Chemical weed control and fertilization increased growth of
all three species. Inoculation with Pisolithus tinctorius enhanced
seedling growth to some extent, but high amounts of natural
ectomycorrhizal colonization probably masked some of the effects.
Torbert, John L., James A. Burger and James E. Johnson, 1996.
Commercial Forestry as a Post-mining Land Use, Virginia Cooperative
Extension, Publication Number 460-136.
The value of forests to landowners and society ultimately depends on
the quality of land reclamation procedures used by the coal mining
company. While it is possible to achieve a level of forest productivity
for minesoils that exceeds the average for native soils in the region,
surface-mined land in the Appalachians is reclaimed to a level of
productivity for below the potential for the region. The primary reason
for the reduced productivity is excessive compaction of the minesoils .
Techniques for producing commercial forest land are described.
Torbert, John L., James A. Burger, James E. Johnson and Jeffrey
A. Andrews, 1994. Final Report, Indices for Indirect Estimates of
Productivity of Tree Crops, OSM Cooperative Agreement GR996511, College
of Forestry and Wildlife Resources, Virginia polytechnic Institute and
State University, 22p. (Report is available from the National Technical
Information Service, 5285 Port Royal Road, Springfield, VA. 22161, NTIS
number PB98-133770)
Mathematical modeling showed that tree growth was primarily a
function of available rooting volume, mine soil pH, total salts, and
available phosphorus. An attempt was made to use the model as a
predictive tool. The model was able to account for 40% of the variation
in tree growth in the test data set. A bioassay procedure was developed
using white pine as the test tree. A bioassay test procedure and
productivity standard is recommended.
Torbert, J. L., and J. A. Burger, 1994. Influence of grading
intensity on ground cover establishment, erosion and tree establishment
on steep slopes, p. 226-231. In Proc. 16th Int. Land
Reclamation & Mine Drainage Conf., Vol. III, Reclamation and
Regeneration, USDI Bureau of Mines Spec. Publ. 06C-94, USDI, Pittsburgh,
PA.
A study was established in eastern Kentucky to evaluate the effect of
surface grading intensity on ground cover development, erosion, and tree
establishment. Three grading treatments were established and five
species of trees were planted and the area was hydroseeded with a
"tree-compatible" ground cover. Erosion was highest on the
intensively graded plots. Tree survival varied by species with sycamore
performing the best (83%) and white pine the poorest (11%). The growth
of sycamore and loblolly pine was significantly reduced by intensive
grading.
Torbert, J. L., J. A. Burger, and W. L. Daniels. 1990. Pine
growth variation with overburden on a reclaimed surface mine in
Virginia. J. Environ. Qual. 19:88-92.
ABSTRACT. "This study was designed to compare the effects of two
overburden spoil types and various mixtures of the two spoils on the
performance of pitch X loblolly hybrid pine (Pinus X rigitaeda).
Sandstone and siltstone overburden were used to create five rock mix
treatments: pure sandstone (SS), pure siltstone (SiS), a 2:1 SS/SiS mix,
a 1:1 SS/SiS mix, and a 1:2 SS/SiS mix. Tree survival was not affected
by rock mix, but growth was greatly affected. The greatest growth
response occurred on the SS treatment and decreased as the amount of
siltstone increased in the rock mix. The average stem volume of trees on
the SS treatment was nearly five times greater than trees on the SiS
treatment. The coarse fragment content of the SS (52%) was much lower
than the SiS (72%), thus providing a greater volume of fine earth
(<2mm) for water retention and root exploitation. The pH of the SS
was much lower than SiS (5.7 vs 7.1), and the available Mn was higher in
the SS than in the SiS (540 vs 160 mg kg-1 foliar Mn). The
results of this study demonstrated the need to consider the effects of
various overburden types on tree growth when forest land is the
designated post-mining land use."
Torbert, J. L., and J. A. Burger. 1990. Guidelines for
establishing productive forest land on reclaimed surface mines in the
central Appalachians p. 273-278. In Proceedings, 1990 Mining and
Reclamation Conference and Exhibition, Charleston, West Virginia.
National meeting of the American Society for Surface Mining and
Reclamation.
Coal mining and reclamation in the Appalachian region of Virginia,
West Virginia, and Kentucky presents a good opportunity to create
productive forests on land that is often too steep or remote to be used
for crop production, grazing or commercial development. Unfortunately,
this land is seldom reclaimed in a fashion that will result in
productive forests. In order to develop productive forest land, special
considerations must be given to the requirements of forest tree species.
Preliminary results indicate that for the best tree establishment and
long-term growth, moderately-acidic sandstone overburdens should be used
as topsoil substitutes when topsoil is not recoverable, grading and
tracking-in should be minimized to avoid compaction, and a
tree-compatible ground cover of acid-tolerant, short grasses and legumes
should be used for revegetation.
Torbert, J. L., A. R. Tuladhar, J. A. Burger and J. C. Bell.
1988. Minesoil property effects on the height of ten-year-old white
pine. J. Environ. Qual. 17:189-192.
Thirty-four 10-year-old white pines (Pinus strobus L.) growing
on reclaimed minesoils in Virginia were selected to evaluate the effects
of selected minesoil properties on tree growth. The minesoil variable
that had the greatest influence on tree growth was rooting volume index,
defined as depth to a restrictive layer times the soil-sized fraction
(%) of the surface 10 cm. The next most influential minesoil property
was soluble salt content. A linear regression equation describing white
pine site index as a function of the square root of depth to a
restrictive layer was highly significant.
Torbert, J. L., J. A. Burger, and W. L. Daniels. 1986. Effect of
overburden type and Pisolithus tinctorius on the growth of pines on a
reclaimed surface mine. In Proceedings, Better Reclamation with Trees
Conference, June 5-7, 1985, Carbondale, Illinois. (Hosted by Dept. of
Botany, Southern Illinois University)
The effect of rock mix, sandstone and siltstone, and infection with Pisolithus
tinctorius on the growth and survival of loblolly pine (Pinus
taeda) and pitch X loblolly pine hybrids (Pinus xrigitaeda)
was studied on a reclaimed surface mine in Southwestern Virginia. After
two years the best growth occurred in pure sandstone and the worst in
pure siltstone. Mycorrhizal colonization of seedlings did not enhance
growth in this study.
Torbert, J. L., J. A. Burger, and W. L. Daniels. 1984. Effect of
overburden type and organic amendments on the growth of pines on a
reclaimed surface mine p. 369-374. In E. Shoulders (ed). Proceedings of
the Third Biennial Southern Silvicultural Research Conference. U.S.D.A.
For. Ser. Gen. Tech. Rep. SO-54.
ABSTRACT. "A Rock Mix Study and a Surface Treatment Study were
designed to evaluate the effects of various sandstone (SS)/siltstone (SiS)
overburden mixtures, several surface treatments (topsoil, sawdust, and
municipal sludge), and infection with Pisolithus tinctorius on the
growth and survival of loblolly pine. ( Pinus taeda L.) and pitch X
loblolly pine hybrids (Pinus xrigitaeda) on a reclaimed surface mine in
Southwestern Virginia. After two years, the best growth in the Rock Mix
Study occurred in the pure sandstone plots and the worst growth was in
the pure siltstone plots. In the Surface Treatment Study, seedlings
planted in 12 inches of topsoil showed no growth differences from those
planted in an unamended 2:1 SS:SiS spoil. Seedlings growth was increased
by application of municipal sewage sludge at rates of up to 25 t/acre,
but higher application of sludge had detrimental effects. The best
surface treatment was sawdust: (25 t/acre). Mycorrhizae improved
seedling growth in the Surface Treatment Study where fertilizer pellets
were not applied. Pitch loblolly pine hybrids survived better and began
growth earlier in the Spring than loblolly pine."
Vogel, W. G., and B. Gray, 1987. Will trees survive on topsoil
surface mines? in Proceedings of the National Symposium on Mining,
Hydrology, Sedimentology and Reclamation, University of Kentucky,
Lexington, pp 302-305.
Trees planted on surface mines reclaimed to meet post SMCRA
requirements often fail to survive. This problem seems to be related to
the excessive compaction especially of salvaged soil materials. The
survival of pine seedlings was compared on topsoiled and non-topsoiled
areas. High mortality on the topsoiled areas was attributed to dry
conditions in late summer and the greater compaction of soil materials
as compared to spoil.
Williamson, D. L., and R. B. Gray. 1996. Evaluation of natural
succession on reclaimed coal mine land in western Kentucky. P. 629-636.
In: W. L. Daniels, J. A. Burger, and C. E. Zipper (ed.) Proc. 13th Ann.
Mtg. Am. Soc. for Surface Mining and Reclamation, Princeton, WV.
As a rule, pre-law ungraded or strike-off sites are in some sort of
tree cover, either planted or naturally regenerated. Conversely, graded
sites are dominated by herbaceous plants or remnants of tree and shrub
plantings and herbaceous plants. Erosion control became the primary
responsibility of reclamation managers when it became apparent that
these graded, highly compacted sites were subject to severe erosion;
especially those where topsoil was replaced. The combination of
compaction and ground cover made reforestation nearly unattainable for
post mining land use.
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