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Forest Class & Tree Inspection On: Section 5.1 Subdivision North Pittsboro, NC Chatham County, North Carolina Conducted for: WithersRavenel 55 Grant Drive, Suite D Pittsboro, NC 27312 Inspection Date: June 19, 2017 Prepared By: Matthew L. Wimberly, RF, ACF Registered Forester # 1407 & Adam K. Listerman RF Registered Forester # 1731 Forest Land Resource Consultants P.O. Box 7 West End, NC 27376 (910) 673-0001 office (910) 673-3233 fax [email protected] WalterE.Thomas,RF:RegisteredForester#409•N.C.Broker#44789•[email protected] MatthewL.Wimberly,RF,ACF:RegisteredForester#1407•N.C.Broker#254183•CertifiedBurner#566•[email protected] Adam Listerman,RF: RegisteredForester# 1731•[email protected]•(704)695-2098 TerralH.Hill,RF:NCRegisteredForester#772•SCRegisteredForester#1413•CertifiedArborist#SO- 0882A•[email protected],RF:RegisteredForester#208 •[email protected]•(919)770-6285 Inspection Report Section 5.1 Subdivision North Chatham County, NC This report details the forest type and ecosystems present on the proposed Section 5.1 Subdivision North. A Systematic inventory was taken using a handheld GPS to navigate inspection lines in a northerly and southerly direction. Inventory lines were spaced approximately 175 feet apart to identify any unique trees or timber types within the proposed development area. Notes were collected in the field regarding two different timber types present. Refer to the attached map for identification of the stands. Each stand was delineated using GIS and current aerial photography, and then confirmed during the inspection. Timing of silvicultural practices was determined using aerial photography. 2016 Aerial/Survey Map 2 Historical Aerial Imagery 3 STAND TYPE (1): PINE THINNING 50.7 Acres: Current Conditions: Using historical photography, it was determined that the stand was clear-cut prior to 1993 leaving only the stream buffers. The stand was regenerated with loblolly pine and the stand was thinned in 2012-2013 time frame. The dominant species is loblolly pine (Pinus taeda), with an under and mid story of hardwood species including: white oak (Quercus alba), red oak (Quercus rubra), Sweetgum (Liquidambar styraciflua), yellow poplar (Liriodendron tulipifera), red maple(Acre rubrum), dogwood (Cornus florida), red cedar (Juniperus virginiana), green ash (Fraxinus pennsylvania), winged elm(Ulmus alata), post oak (Quercus stellata), and pignut hickory(Carya tomentosa). The forest floor consists of Chinese Privet (Ligustrum sinense), autumn olive (Elaeagnus umbellate), muscadine grape (Vitis rotundifolia), smilax brier, blackberry brier, and native grasses. The stand was thinned leaving approximately 60-70 square feet of basal area per acre. Tree d.b.h. (diameter at breast height) range from 10-18 inches, and tree heights range between 70-80 feet tall. The stand appears to be growing well with no insect or diseases noted in the field. Along the ridges, there is a denser component of hardwood competition in the understory and pine stocking levels are lower. A second thinning could be performed in some areas on the stand to allow for continued forest heath and tree vigor. During the inspection, no trees where identified to be significant in regard to size or species. Stand Type (1) photo: 1.1 Refer to the pictures below for current condition: 5 Stand Type (1) photo: 1.2 Stand Type (1) photo: 1.1 Stand Type (1) photo: 1.3 Stand Type (1) photo: 1.4 6 STAND TYPE (2): MIXED HARDWOOD CREEK AREAS 11.8 Acres: Current Conditions: This stand contains a variety of hardwood species, and a very small component of southern yellow pine. The hardwood species noted in the stand are: white oak (Quercus alba), red oak (Quercus rubra), Sweetgum (Liquidambar styraciflua), yellow poplar (Liriodendron tulipifera), red maple(Acre rubrum), dogwood (Cornus florida), red cedar (Juniperus virginiana), green ash (Fraxinus pennsylvania), winged elm(Ulmus alata), post oak (Quercus stellata), and pignut hickory(Carya tomentosa). The most prevalent species are yellow poplar, sweetgum and maple. These areas evolved from harvesting operation that where do in the past. Most of the areas have a creek or natural drainage area within the stand. Stand Type (2) photo: 2.1 During the timber inspection, there was no sign of recent silvicultural practices conducted in the stand. Tree d.b.h. range from 6-22 inches, and dominant tree heights are 70-80 feet tall with a significant component of hardwood regeneration that range in height from 40-50 feet tall. During the inspection, no trees where identified to be significant in regard to size or species. Stand Type (2) photo: 2.2 On the forest floor there are significant numbers of natural regeneration from the parent trees on the stand. In addition to the tree species, Chinese Privet (Ligustrum sinense), autumn olive (Elaeagnus umbellate), native grasses and herbaceous weeds can be found on the forest floor. Stand Type (2) photo: 2.3 7 Stand Type (2) photo: 2.4 Stand Type (2) photo: 2.5 Stand Type (2) photo: 2.6 9 Summary: This entire project is contained on what would be or once considered a Dry-Mesic Oak – Hickory Forest. Refer to the following for the classification of this forest type: CLASSIFICATION OF THE NATURAL COMMUNITIES OF NORTH CAROLINA THIRD APPROXIMATION: by Michael P.Schafale and AlanS.Weakley1990 North Carolina Natural Heritage Program Division of Parks and Recreation Department of Environment and Natural Resources MSC 1615 Raleigh, NC 27611 DRY-MESIC OAK--HICKORYFOREST Sites: Mid slopes, low ridges, upland flats, and other dry-mesic upland areas on acidic soils. Soils: A variety of upland soils. Series include Cecil, Pacolet, Wedowee, Georgeville, Tatum, Kalmia (Typic Hapludults), Wagram (Arenic Paleudult), Tallapoosa (Ochreptic hapludult), and Stallings (Aeric Paleudult). Hydrology: Terrestrial, dry-mesic. Vegetation: Forest dominated by mixtures of oaks and hickories, with Quercus alba most prevalent, along with Q. rubra,Q. velutina, Carya alba (tomentosa), C. ovalis, and C. glabra. Pinus species, Liriodendron tulipifera, and Liquidambar styraciflua maybe common. Understoryspecies include Acer rubrum, Cornus florida,Oxydendrumarborem,Ilexopaca,and Nyssa sylvatica. Shrubs include Viburnum rafinesquianum, Vaccinium stamineum, Vaccinium pallidum (vacillans), and Evonymus americana. Vitis rotundifolia and Toxicodendron (Rhus) radicans often are present. Herbs are fairlysparse,with Hexastylis spp., Goodyera pubescens, Chimaphila maculata, Desmodium nudiflorum, and Hieracium venosum common. Dynamics: Disturbed areas have increased amounts of pines and weedyhardwoods such as Acer rubrum and Liquidambar styraciflua, with the amounts depending on the degree of canopy opening. Areas that were cultivatedare generally dominated by even-aged pine stands which are replaced by the climax oaks and hickories onlyas the pines die. Logged areas mayhave a mixture of hardwoods and pines. Under natural conditions these forests are uneven-aged, with old trees present. Reproduction occursprimarilyincanopy gaps. Rare severe natural disturbances such as wind storms mayallow pulses of increased regeneration and allow the less shade tolerant species to remain in the community. However, Skeen, Carter, and Ragsdale (1980) argued that even the shade-intolerant Liriodendron could reproduce enough in gaps to persist in the climax Piedmont forests. 10 The natural fire regime of the Piedmont is not known, but fires certainlyoccurred periodically. Most of the component trees are able to tolerate light surface fires with little effect. Regular fire may have created a more open forest, with gaps persising longer than at present and perhaps forming more frequently. In sandyparts of the Coastal Plain, fires were frequent, apparentlyevery3-5 years. Dry-Mesic Oak--HickoryForestsare confined to areas that are somewhat sheltered from fire spread. With the reduction in fire frequency in the Coastal Plain, many longleaf pine-dominated communities have been invaded by oaks and hickories, though most resemble Dry Oak--Hickory Forests rather than Dry-Mesic Oak--Hickory Forests. Range: Throughout the Piedmont and Coastal Plain, possibly in the lower parts of the Blue Ridge. Associations: Occurs in the topographic moisture gradient, between DryOak-- HickoryForestand MesicMixedHardwoods (Piedmont or Coastal Plain Subtype). May also grade into Piedmont/Coastal Plain Acidic Cliff, Piedmont/Coastal Plain Heath Bluff, Piedmont Monadnock Forest, other upland communities, or floodplain communities. Distinguishing Features: Because the overall moisture level is not easy to determine, upland hardwood forests are most easilydistinguished bythe canopycomposition. Both DryOak--Hickory Forests and Dry-Mesic Oak--HickoryForestsoften have Q. alba as the predominant tree. In Dry- Mesic Oak--HickoryForests trees more mesophytic than Q. alba predominate over those more xeric. Mesic Mixed Hardwood Forest is dominated byQ. rubra, Fagus grandifolia, Liriodendrontulipifera, or other trees more mesic than Q. alba. Dry-Mesic Oak--Hickory Forest is distinguishedfrom Piedmont/CoastalPlainAcidic Cliff and Piedmont/Coastal Plain Heath Bluff by the presence of a naturally closed or nearly closed canopy. It is distinguished from Montane Oak--HickoryForest bythe absence of species typical of the BlueRidgeinNorthCarolina,such as Castanea dentata and Rhododendron calendulaceum. Variation: This type has substantial variation within it, although less than might be expected given its wide geographic range. No variants
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