Rhododendron maximumimpacts seed bank composition and richness followingTsuga canadensisloss in riparian forests

Ecosphere - Tập 9 Số 4 - 2018
Tristan M. Cofer1,2, Katherine J. Elliott3, J. K. Bush2, Chelcy Ford Miniat3
1Department of Entomology, Pennsylvania State University, 201 Old Main, University Park, Pennsylvania, 16801 USA
2Environmental Science Academic Program, University of Texas at San Antonio, One UTSA Circle, San Antonio, Texas, 78249 USA
3USDA Forest Service, Southern Research Station, Center for Forest Watershed Research, Coweeta Hydrologic Laboratory, 3160 Coweeta Lab Road, Otto, North Carolina, 28763 USA

Tóm tắt

Abstract

Southern Appalachian riparian forests have undergone changes in composition and function from invasive pathogens and pests.Castanea dentatamortality in the 1930s from chestnut blight (Cryphonectria parasitica) andTsuga canadensismortality in the 2000s from the hemlock woolly adelgid (Adelges tsugae) have led to the expansion and increased growth ofRhododendron maximum, an evergreen subcanopy shrub. A better understanding of seed bank characteristics and the various abiotic and biotic factors that affect the seed bank may be useful in determining the restoration potential of forest communities following invasion‐related disturbances. We compared the seed bank of two deciduous forest types: hardwood forests with a denseR. maximumsubcanopy (hereafter,RR) and hardwood forests withoutR. maximum(hereafter,HWD). We evaluated numerous microenvironmental variables through principal component analysis (PCA) and correlated the derivedPCAaxes scores to seed bank density and richness across forest types. We found that seed bank density was comparable between the forests types; however, seed bank richness was much lower inRRthanHWDand the species composition was dissimilar between forest types. Twenty‐eight of 64 (44%) species in the seed bank ofHWDwere not found in the seed bank ofRR. Species that were represented in both forest types were often found in contrasting densities. Most notably, seed bank densities of several woody species were considerably higher inRR(85%) thanHWD(45%), while herbaceous seed bank density was lower inRR(11%) thanHWD(50%). Mineral soilpH, soil nutrient availability, and soil moisture were lower, and organic soil (Oi + Oe + Oa) depth and mass were greater in theRRthanHWDforest type.PCAcorrelations revealed thatPCA4 (represented by understory density and Oe + Oa phosphorus and carbon/nitrogen ratio) was negatively correlated with total seed bank density.PCA1 (represented by Oe + Oa cations and phosphorus, understory richness, ground‐layer cover, and mineral soilpH) andPCA4 were positively correlated with total seed bank richness. These results suggest that the soil seed bank will not be the primary mode of recruitment to establish a diverse and herbaceous‐rich community if a RR is present.

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Tài liệu tham khảo

10.1016/S1146-609X(01)01104-3

10.1111/j.1438-8677.1996.tb00806.x

Baskin C. C., 2001, Seeds: ecology, biogeography and evolution of dormancy and germination

10.1139/x00-075

10.1046/j.1365-2435.1998.00238.x

10.24266/0738-2898-9.1.5

Boring L. R. andW. T.Swank.1986.Hardwood biomass and net primary production following clearcutting in the Coweeta Basin. Pages43–50inR. T.BrooksJr. editor. Proceedings of the 1986 Southern Forest Biomass Workshop 16–19 June 1986 Knoxville Tennessee.Tennessee Valley Authority Norris Tennessee USA.

Brown C., 2015, Procedures for chemical analysis

10.2307/2256652

Chatterjee S., 2015, Regression analysis by example

10.1890/0012-9658(1999)080[1475:SDNAFP]2.0.CO;2

Clinton B. D.1995.Temporal variation in photosynthetically active radiation (PAR) in mesic southern Appalachian hardwood forest with and without rhododendron understories. Pages534–540inK. W.GottschalkandS. L.Fosbroke editors. Proceedings of the 10th Central Hardwood Forest Conference 5–8 March 1995 Morgantown West Virginia. NE GTR‐197.USDA Forest Service Northeastern Forest Experiment Station Radnor Pennsylvania USA.

10.2307/2426587

10.1007/978-1-4612-3732-7_10

10.1139/X08-171

10.1002/ieam.1840

10.1139/x02-009

10.1016/j.foreco.2005.02.064

10.1016/j.foreco.2010.03.010

10.3159/TORREY-D-11-00076.1

10.1007/s10021-014-9825-x

10.3159/TORREY-D-13-00054.1

10.1890/1540-9295(2005)003[0479:LOFSCF]2.0.CO;2

10.1111/j.1600-0706.2011.19622.x

10.1017/CBO9780511623332

10.1641/B571007

10.1093/biosci/biv165

10.21135/893273651.001

10.1890/02-3114

10.1890/03-0685

10.2179/08-016R3.1

10.1177/001316446002000116

10.1656/058.011.0407

10.1038/nature06777

10.2166/nh.2012.067

10.1016/j.ecolind.2012.07.026

Leck M. A., 1989, Ecology of soil seed banks

10.1139/b99-176

10.1007/s11258-005-9058-3

10.1086/342711

10.1007/s00027-016-0501-4

Littell R. C., 2004, SAS system for mixed models

10.1890/15-1176

10.1111/1365-2664.12973

10.1007/s10530-017-1538-6

10.1080/713610860

10.1139/x98-146

10.1007/BF02393620

10.1023/A:1009793119466

10.2307/2996415

10.2307/2937357

10.1674/0003-0031(2001)145[0325:DRMLER]2.0.CO;2

10.1046/j.1365-2699.2002.00765.x

Poland T. M., 2006, Emerald ash borer: invasion of the urban forest and the threat to North America's ash resource, Journal of Forestry, 104, 118, 10.1093/jof/104.3.118

10.1007/s00267-009-9317-5

10.1139/x06-025

10.1079/9781780641836.0263

10.2737/NRS-RP-9

10.1155/2010/419482

Staaf H., 1987, Buried germinative seeds in mature beech forests with different herbaceous vegetation and soil types, Holarctic Ecology, 10, 268

Tabachnick B. G., 2001, Using multivariate statistics

Thomas D., 1996, Soil survey of Macon County, North Carolina

10.1111/j.1469-8137.1987.tb04680.x

10.2307/2259220

10.1890/12-1899.1

10.1674/0003-0031(2007)157[11:SGLBAN]2.0.CO;2

10.1016/j.pedobi.2006.10.001

10.1111/j.1365-2745.2009.01487.x