About: Pine barrens is a research topic. Over the lifetime, 659 publications have been published within this topic receiving 13971 citations. The topic is also known as: Pinus forests & Pine barrens.
TL;DR: Pollen and plant macrofossil studies at 11 sites in New Jersey, southern and eastern Pennsylvania, West Virginia, and Virginia, USA reveal the character of the stable vegetation of the unglaciated eastern United States while the Wisconsin ice sheet was still at its outer limit.
Abstract: Pollen and plant macrofossil studies at 11 sites in New Jersey, southern and eastern Pennsylvania, West Virginia, and Virginia, USA reveal the character of the stable vegetation of the unglaciated eastern United States while the Wisconsin ice sheet was still at its outer limit Grass—dominated tundra with dwarf shrubs was present 60 km south of the ice front at Longswamp, Pennsylvania Sedge tundra covered the higher mountains of central Appalachia In southern Pennsylvania, New Jersey (including the Pine Barrens), and northern Virginia, Picea (black or white spruce) was common, with Betula glandulosa (dwarf birch) and tall herbs, especially Sanguisorba canadensis (burnet) This is interpreted as forest tundra In North and South Carolina and in northwest Georgia, forests of Picea and Pinus banksiana (jack pine) were present, with few deciduous trees No site is yet known where broad—leaved trees formed the predominant vegetation cover anywhere on the Coastal Plain or in the Florida peninsula With climatic warming, dwarf birch and spruce expanded into the tundra in unglaciated Pennsylvania At Crider's Pond in southern Pennsylvania a Picea/Betula glandulosa assemblage with tall herbs was present from 15 000 to 13 000 yr BP The associated aquatic flora was species poor About 13 000 yr BP Abies balsamea (fir), Pinus banksiana, and Alnus cf rugosa (speckled alder) invaded, together with diverse tree and shrub species, an assemblage like the southern boreal forest today Betula populifolia (grey birch) occurs in this assemblage at Longswamp; there the aquatic flora is species rich The increase in species diversity is evidence of marked climatic warming about 13 000 yr BP in southern and eastern Pennsylvania Picea rubens (red spruce) arrived at Crider's Pond shortly before 11 500 yr BP, followed soon after by Pinus strobus (white pine) At Tannersville in glaciated eastern Pennsylvania an invasion series Picea—Abies—Pinus banksiana—Betula papyrifera (paper birch)—Larix laricina (tamarack)—Pinus strobus—Betula populifolia—Pinus rigida (pitch pine) can be demonstrated between 13 000 and 9000 yr BP The stable flora of the periglacial region was different from the pioneer flora of the deglaciated area and from the vegetation of the modern tundra As the ice withdrew, Tsuga (hemlock) and other tree species for which there is little or no fossil record at the height of the glaciation appeared in large populations in central Appalachia and the northern coastal plain, from which they invaded the deglaciated region at different rates Castanea (chestnut), a slow migrant, took 5000 yr to reach southern New England from central Appalachia Persistent tundra made the higher mountains of central Appalachia an important phytogeographical barrier to tree migration until about 12 500 yr BP It explains differences in forest history west and east of the mountains Tamarack seems to have migrated eastward from a glacial refuge south of the Great Lakes region The distinctive modern vegetation of the Pine Barrens was assembled after about 10 000 yr BP Climatically the periglacial region was cold, dry, and windy The early Holocene from 10 000 to 6000 yr BP was warmer and drier than now, although not so dry as the Late Wisconsin It can be identified as the Hypsithermal Interval The subsequent expansion of Pinus may be attributed to a wetter climate, which caused increased bog and swamp formation and possibly also replacement of deciduous trees by pines as storm and fire frequency increased and soils were progressively leached of nutrients
TL;DR: Results indicate that a mix of forest litters (oak and pine) optimizes retention of scarce nutrients such as nitrogen and phosphorus, which is an important step in identifying linkages between biodiversity of this group and ecosystem functions.
Abstract: The influence of litter quality on root growth, ectomycorrhizal communities and decay processes was investigated through a litter bag experiment. Litter bags containing either pine needles, oak leaves or oak+pine mix were placed within the O horizon of a lowland pitch pine (Pinus rigida) forest in the New Jersey Pinelands. Upon retrieval, ingrown pine roots were removed and quantified for total length and percent ectomycorrhizal colonization by morphotype. Phosphatase activity was determined for dominant morphotypes. In addition, litter decay rates and N and P litter content were measured. Mixed litter (oak+pine) had highest total pine root ingrowth. Dominant ectomycorrhizal morphotypes differed in response to litter type. A tuberculate form dominated (35%) in pine litters while distinctly different nontuberculate morphotypes dominated in oak and mixed litters. High phosphatase activity of morphotypes was correlated with high phosphorus immobilization during oak leaf decay. Results indicate that a mix of forest litters (oak and pine) optimizes retention of scarce nutrients such as nitrogen and phosphorus. The diverse chemical environment of these different litter types induces different ectomycorrhizal community development which show functional differences in the way phosphorus is likely to be cycled. The influence of litter type on diversity and function of ectomycorhizae is an important step in identifying linkages between biodiversity of this group and ecosystem functions.
TL;DR: In this article, Anderson et al. discuss the ecology and conservation of Florida scrub, including the characteristics of the sand shinnery oak (Quercus havardii) communities of the Llano Estacado: history, structure, ecology and restoration.
Abstract: List of contributors Introduction Roger C. Anderson, James S. Fralish, and Jerry M. Baskin Part I. Eastern/Southeastern Region: 1. Ecology and conservation of Florida scrub Eric S. Menges 2. Southeastern pine savannas William J. Platt 3. New Jersey pine plains: the 'true barrens' of the New Jersey pine barrens David J. Gibson, Robert A. Zampella and Andrew G. Windisch 4. Vegetation, flora, and plant physiological ecology of serpentine barrens of eastern North America R. Wayne Tyndall and James C. Hull 5. The mid-Appalachian shale barrens Suzanne H. Braunschweig, Eric T. Nilsen and Thomas F. Weiboldt 6. Eastern granite outcrops Donald J. Shure 7. High-elevation outcrops and barrens of the southern Appalachian mountains Susan K. Wiser and Peter S. White Part II. Central/Midwest Region: 8. Dry soil oak savanna in the Great Lakes region Susan Will-Wolf and Forest Stearns 9. Deep-soil savannas and barrens of the Midwestern United States Roger C. Anderson and Marlin L. Bowles 10. Open woodland communities of southern Illinois, western Kentucky and middle Tennessee James S. Fralish, Scott B. Franklin and David D. Close 11. The big barrens region of Kentucky and Tennessee Jerry M. Baskin, Carol C. Baskin and Edward W. Chester 12. Cedar glades of southeastern United States Jerry M. Baskin and Carol C. Baskin 13. Savanna, barrens and glade communities of the Ozark Plateaus Province Alice Long Heikens 14. The cross timbers B. W. Hoagland, I. H. Butler, F. L. Johnson and S. Glenn Part III. Western/Southwestern Region: 15. Ponderosa and limber pine woodlands Dennis H. Knight 16. The sand shinnery oak (Quercus havardii) communities of the Llano Estacado: history, structure, ecology and restoration Shivcharn S. Dhillion and Michelle H. Mills 17. Oak savanna in the American Southwest Mitchel P. McClaran and Guy R. McPherson 18. Juniper-Pinon savannas and woodlands of western North America Neil E. West 19. Serpentine barrens of western North America A. R. Kruckeburg 20. California oak savanna Barbara Allen-Diaz, James W. Bartolome and Mitchell P. McClaran Part IV. Northern Region: 21. Jack pine barrens of the northern Great Lakes region Kurt S. Pregitzer and Sari C. Sanders 22. The cliff ecosystem of the Niagara escarpment D. W. Larson, U. Mattes-Sears and P. E. Kelley 23. Alvars of the Great Lakes region Paul M. Catling and Vivian R. Brownell 24. The flora and ecology of southern Ontario granite barrens Paul M. Catling and Vivian R. Brownell 25. The aspen parkland of Canada O. W. Archibold 26. Subarctic lichen woodlands E. A. Johnson and K. Miyanishi Index of plants Index of animals Topic index.
TL;DR: The present investigation of local distribution of P. cinereus was carried out in 2 habitat types during the summers of 1957 and 1958 to understand the factors affecting microdistribution of such a eurytopic species.
Abstract: The Red-backed salamander, Plethodon cinereus Green, has a broad geographical distribution reaching from the Gaspe Peninsula to northern Minnesota, then south to Georgia and South Carolina (Grobman 1944, Bishop 1947). It occurs in a variety of habitats including northern hardwoods (Creaser 1944, Test 1952), oakhickory forest (Test and Bingham 1948, Test 1955), pine barrens (Burger 1935), and birch and mixed forests (Cochran 1911). It is found under stones, in and under logs, and within the leaf litter and other organic layers of the forest floor. In order to understand the factors affecting microdistribution of such a eurytopic species, it is desirable to carry out studies in different habitats where different restrictive conditions are likely to be operating. The present investigation of local distribution of P. cinereus was carried out in 2 such habitat types during the summers of 1957 and 1958.
TL;DR: In this article, the authors used eddy covariance to measure net CO2 exchange with the atmosphere (NEE), and biometric measurements to characterize net ecosystem productivity (NEP) in oak- and pine-dominated forests that were defoliated by Gypsy moth (Lymantria dispar L.) in the New Jersey Pine Barrens.
Abstract: Invasive insects can impact ecosystem functioning by altering carbon, nutrient, and hydrologic cycles. In this study, we used eddy covariance to measure net CO2 exchange with the atmosphere (NEE), and biometric measurements to characterize net ecosystem productivity (NEP) in oak- and pine-dominated forests that were defoliated by Gypsy moth (Lymantria dispar L.) in the New Jersey Pine Barrens. Three years of data were used to compare C dynamics; 2005 with minimal defoliation, 2006 with partial defoliation of the canopy and understory in a mixed stand, and 2007 with complete defoliation of an oak-dominated stand, and partial defoliation of the mixed and pine-dominated stands. Previous to defoliation in 2005, annual net CO2 exchange (NEEyr) was estimated at � 187, � 137 and � 204gCm � 2 yr � 1 at the oak-, mixed-, and pine-dominated stands, respectively. Annual NEP estimated from biometric measurements was 108%, 100%, and 98% of NEEyr in 2005 for the oak-, mixed-, and pine-dominated stands, respectively. Gypsy moth defoliation strongly reduced fluxes in 2006 and 2007 compared with 2005; NEEyr was � 122, 1103, and � 161gCm � 2 yr � 1 in 2006, and 1293, 1129, and � 17gCm � 2 yr � 1 in 2007 at the oak-, mixed-, and pine-dominated stands, respectively. At the landscape scale, Gypsy moths defoliated 20.2% of upland forests in 2007. We calculated that defoliation in these upland forests reduced NEEyr by 41%, with a 55% reduction in the heavily impacted oakdominated stands. ‘Transient’ disturbances such as insect defoliation, nonstand replacing wildfires, and prescribed burns are major factors controlling NEE across this landscape, and when integrated over time, may explain much of the patterning of aboveground biomass and forest floor mass in these upland forests.