Managing birch woodlands for the production of quality timber

Interest in silver birch (Betula pendula Roth) and downy birch(Betula pubescens Ehrh.) has greatly increased in recent yearspartly as a result of pressures to restore and expand nativewoodlands but also due to renewed interest in birch as a treecapable of producing quality timber. Despite the many advantagesof birch as a commercial timber tree—ease of establishment,fast growth on good sites, high value timber and a short rotation,it has a poor reputation in Britain largely as a result of thepoor form of the existing, mainly unmanaged resource. The followingpoints need to be considered if stands of quality birch treesare to be produced in an economical timescale. (1) Sites: silverbirch needs good sites that are relatively well drained withlight mineral soils. Downy birch does well on moist to wet sites.(2) Regeneration: natural regeneration through a shelterwoodis the preferred system of regenerating birch as some overheadprotection is beneficial to germination success. About 20–40seed trees should be left per hectare. Good ground preparationand control of grazing are essential. The vast majority of seedlingsare recruited in the first year of the regeneration cycle thereforeplanting should be considered if the initial regeneration successis poor. Direct seeding is also a successful method of regeneration.Birch readily regenerates naturally into suitably prepared openareas next to existing birch woods but these should not be toobig, e.g. gaps or strips 20–60 m wide have been suggestedin the literature. (3) Maintenance: density of regenerationneeds to be reduced to about 2500–3000 stems ha^–1by the time the trees are about 3–6 m tall. Birch seedlingsmust always be taller than the competing vegetation. (4) Thinning:thinning should begin when the mean height of the stand is about8–10 m. At this point at least half the number of treesshould be removed with the emphasis on retaining dominants andco-dominants of good form. The aim is to maintain about halfthe height of the tree as living crown to sustain a high rateof growth. Additional thinnings will be required at intervalsof 5 to 7 years and final thinning should leave around 300–500stems ha^–1. (5) Rotation: a rotation of 40–50 yearsis possible on good sites and perhaps 50–55 years on lessfavourable sites.     

Sweet chestnut: silviculture, timber quality and yield in the Forest of Dean

The silviculture, performance and value of sweet chestnut (Castaneasativa Miller) are reviewed in the light of experience in theForest of Dean in Gloucestershire. The many advantages of includingthe species within broadleaved woodland include its ease ofestablishment, fast growth rate, and the high value of its timber.Veneer and first quality planking material fetch premium prices.That it is not more widely planted is mainly due to the widelyheld view that it is difficult or impossible to grow chestnutlogs that are not shaken. Shake is shown to be mainly a problemof overmature trees. Ink disease (Phytophthora sp.) is not regardedas a major limitation, especially in new plantings. Guidanceis given on the conversion of chestnut coppice to high forest.Yield tables are presented which may be applied to chestnuthigh forest of coppice origin in the Forest of Dean, and withcaution elsewhere in southern England. The data for the bettersites in the Forest of Dean indicate possible yields of up to11 m³ ha^–1 a^–1, and a dominant diameter incrementof up to 1 cm a^–1.     

Effect of half-systematic and systematic thinning on the increment of Scots pine and Norway spruce in Finland

Diameter, height and volume increment of Scots pine (Pinus sylvestrisL.) and Norway spruce (Picea abies (L.) Karst.) stands wereinvestigated in long-term thinning experiments in southern Finland.The measurement period was on average 19 years, and thinningsconsisted of five different treatments: (1) unthinned; (2) selectivethinning from below where thinning intensity was determinedaccording to the number of stems; (3) selective thinning frombelow where thinning intensity was determined according to standbasal area; (4) systematic thinning where corridors were openedat regular intervals in the stand; and (5) half-systematic thinningwhere corridors were opened at regular intervals and the remainingstrips thinned from below, i.e. a combination of selective andsystematic thinning. The selective (basal area) thinning ofScots pine resulted in a volume growth reduction of about 12per cent, but in Norway spruce it resulted in no marked reductioncompared with the unthinned plots. In both tree species, volumeincrement in the half-systematic and selective (basal area)thinning differed only slightly from each other. The systematicthinning resulted in the lowest volume increment. In the systematicthinning, the total yield (m³ ha^–1) somewhat decreasedwith increasing corridor width. In half-systematic thinning,on the other hand, the total yield was not clearly related tocorridor width. A corridor accelerated the diameter incrementof the edge trees. The edge effect progressively diminishedwhen moving deeper into the strip and ended at a distance ofabout 3–4 m from the corridor edge. After the thinning,the height increment first decreased, but later on it recovered.The unthinned plots had more dead trees than the other treatments,but there were no significant differences between the othertreatments. It can be concluded that the prevailing thinningmethod in the Nordic countries, i.e. half-systematic thinning,most probably results in no significant growth and yield losses.     

Oak in Wessex An Account of Field Studies 1982-4

The Wessex Silvicultural Group spent three years studying themanagement and silviculture of the oaks (Quercus robur L andQ petraea (Matt) Leibl) in the Wessex area. Low input methodsof establishment including the use of tree shelters and thetending and thinning of younger oak stands together with controlof timber quality were examined in twenty-one forests and estates.Environmental values were acknowledged. While Q robur has previouslypredominated, Q petraea is now generally preferred.     

Growth and mortality in underplanted tree seedlings in response to variations in canopy closure of Norway spruce stands

Six broadleaved tree species and Picea abies (L.) Karst. wereplanted under spruce plantations of varying densities, in Sweden.Treatments included control (994 stems ha^–1), dense (538stems ha^–1), sparse (294 stems ha^–1) and gap (0stems ha^–1) overstory treatments. There was an increasein height and diameter growth from control to sparse overstorytreatment of all underplanted tree species except for ash (Fraxinusexcelsior L.) and Norway maple (Acer platanoides L.). Site conditionsmay have hampered the growth of these species, as well as wildcherry (Prunus avium L.). Both oak (Quercus robur L.) and sprucehad greater growth in the gap treatment, relative to the othertreatments. Insecticide application did not influence seedlinggrowth or survival. The performance of beech (Fagus sylvaticaL.), lime (Tilia cordata Mill.), spruce and oak was consistentwith shade tolerance ranking. Beech and lime had a very highsurvival rate, even under the densest canopy. The growth andmortality of ash, maple and wild cherry differed significantlyfrom what was expected. This experiment demonstrated significantvariation in interspecific growth and mortality between sevenplanted tree species in relation to canopy density. Correctsite and species selection is crucial when underplanting inshelterwood systems.     

Stem volume equations and basic density for grey alder and common alder in Sweden

The objective was to determine stem volume models for grey andcommon alders and, based on the models, stand volume for naturallyregenerated grey and common alder stands was summarized. Basicdensity for grey and common alders and mean annual growth forstands was estimated. Net volume accretion data were collectedfrom 24 stands of grey alder (Alnus incana (L.) Moench) and31 stands of common alder (Alnus glutinosa (L.) Gaertner) inSweden. The stands ranged in latitude from 58 to 64° N andfrom 56 to 62° N for grey and common alder, respectively.The mean age of grey and common alder stands was 41 years and48 years, respectively, the mean stand density 1726 stems ha^–1and 1078 stems ha^–1, and the mean diameter at breast height(over bark) was 20 cm and 21 cm. Stem volume equations weredeveloped for grey and common alders. The adopted model forgrey alder was based on diameter at breast height and height.For common alder, crown height was added to diameter and height.Mean standing volume (over bark) for grey and common alder standswas 428 and 374 m³ ha^–1. Mean annual growth for grey andcommon alder stands was 12.0 m³ and 8.4 m³ a^–1 ha^–1,respectively. Basic density (under bark), for grey and commonalder stems was 359 and 427 kg m^–3, respectively. Thebasic density (under bark) for the lowest twigs in the crownand in the lateral part of the crown was 415 and 421 kg m^–3for grey alder and 423 and 423 kg m^–3 for common alder.     

Comparing the financial performance of traditionally managed beech and oak stands with roomy established and pruned stands

Beech and oak stands are normally established with high numbers of plants. On one hand, this costs a lot, but on the other hand, knot-free timber may be expected only in this way. This study analyses whether roomy establishment and, as a result, lower timber quality lead to financial advantages over the normal treatment. In addition to this, it is tested if pruning of roomy established beech and oak stands is financially advantageous. For this valuation, conventionally managed stands were simulated with the forest growth simulator Silva and for the roomy established stands, data from trial plots were completed with Silva. The development of the pruned oak stands followed the yield table of Jobling and Pearce (Free growth of oak, Forest record number 113, Forestry Commission HMSO, London, 1977), while for beech the development of the diameters orientated to an investigation of Hasenauer et al. (Österr Forstztg 105:28–29, 1994). Based on the assortments contained in the stands, a valuation of the different treatments was done with annuities within a Monte Carlo simulation, thereby including the volatility of timber prices and the risk of natural hazards. Additionally, the imputed costs per cubic meter of produced timber and the minimum share of high-value assortments on the pruned trunks were calculated for the required rates of return of 1, 2 and 3%. The conventionally managed beech and oak stands were found to be inferior from the financial point of view. Even the non-pruned stands with roomy establishment were superior despite the lower timber quality. The minimum share of high-value assortments on the pruned trunks were between 6 and 410%. Particularly in the case of high values of the land, the maximum volume of high-value assortments was not sufficient to achieve certain rates of return. Nevertheless, the stands with pruning and low-density management were more profitable. In addition to this, it was ascertained that pruning of beech and oak is possible and does not hinder the production of high-value assortments.     

Growth response of young lodgepole pine to thinning and repeated fertilization treatments: 10-year results

This study was designed to test the hypothesis that large-scalepre-commercial thinning (PCT) to various stand densities, atages 12–14 years, combined with repeated fertilization,would, over a 10-year treatment period, enhance productivityof lodgepole pine (Pinus contorta Dougl. ex Loud. var. latifoliaEngelm.) crop trees. Study areas were located near Summerland,Kelowna and Williams Lake in south-central British Columbia,Canada. Each study area had nine treatments: four pairs of standsthinned to densities of 250 (very low), 500 (low), 1000 (medium)and 2000 (high) stems ha^–1, with one stand of each pairfertilized five times at 2-year intervals, and an unthinnedstand. The very low, low- and medium-density stands were alsopruned to a 3-m lift 5 years after thinning. At the tree level,fertilization treatments significantly increased diameter atbreast height (DBH), basal area (BA) and volume growth and heavyPCT significantly increased DBH and BA growth. Pruning may mitigatesome of the negative stem form and wood quality attributes associatedwith fast-growing trees without adversely affecting stem growth.At the stand level, PCT to very low and low densities significantlydecreased the volume growth compared with high-density stands.The potential beneficial impacts that PCT and repeated fertilizationtreatments have for mitigating timber supply shortfalls, aswell as potentially minimizing crop tree losses due to mountainpine beetle (Dendroctonus ponderosae Hopk.), are also discussed.     

Effects of pruning and stand density on the productionof new epicormic shoots in young stands of pedunculate oak (Quercus robur L.)

Context

Avoidance or control of epicormic shoots is among the major silvicultural challenges for the production of high-quality oak timber. In northern Europe, contemporary oak silviculture aims to produce valuable timber on a relatively short rotation, applying early, heavy thinning combined with artificial pruning.

Aims

The aim of this study was to analyse the effects of pruning and stand density on the production of new epicormic shoots on young trees of pedunculate oak (Quercus robur L.).

Methods

The study was based on two field experiments in even-aged stands of pedunculate oak subjected to different thinning practices and early selection of potential future crop trees. From ages 13 to 15 years, stem density was reduced to 300 trees ha^?1, 1,000 ha^?1 or stands remained unthinned. Pruning was conducted on selected trees at ages 22–24 years. At that age, the stem density in unthinned control plots ranged from 2,500 to 3,100 ha^?1. All treatments were replicated twice within each experiment.

Results

Pruning led to an overall increase in the total production of new epicormic shoots. More epicormic shoots were produced in the lower part of the stem (0–3 m in height) than in the upper part (3–6 m). The number of new epicormic shoots increased with increasing stand density.

Conclusion

Early, heavy thinning combined with high pruning at regular intervals may help shorten the rotation length for pedunculate oak without further reduction in wood quality than that which is caused by wider annual growth rings.     

Optimal management of Korean pine plantations in multifunctional forestry

Korean pine is one of the most important plantation species in northeast China.Besides timber,it produces edible nuts and plantations sequester carbon dioxide from the atmosphere.This study optimized the management of Korean pine plantations for timber production,seed production,carbon sequestration and for the joint production of multiple benefits.As the first step,models were developed for stand dynamics and seed production.These models were used in a simulation–optimization system to find optimal timing and type of thinning treatments and optimal rotation lengths.It was found that three thinnings during the rotation period were optimal.When the amount or profitability of timber production is maximized,suitable rotation lengths are 65–70 years and wood production is 5.5–6.0 m~3 ha~(-1) a~(-1).The optimal thinning regime is thinning from above.In seed production,optimal rotation lengths are over 100 years.When carbon sequestration in living biomass is maximized,stands should not be clear-cut until trees start to die due to senescence.In the joint production of multiple benefits,the optimal rotation length is 86 years if all benefits(wood,economic profits,seed,carbon sequestration) are equally important.In this management schedule,mean annual wood production is 5.5 m~2 ha~(-1) and mean annual seed yield 141 kg ha~(-1).It was concluded that it is better to produce timber and seeds in the same stands rather than assign stands to either timber production or seed production.     

The tolerance of newly emerged broadleaved tree seedlings to the herbicides clopyralid, cycloxydim and metazachlor

In direct-seeded woodlands and nursery seed-beds, weeds canrapidly invade newly sown areas, leading to death or suppressionof tree seedlings. Hand weeding is usually expensive, and thesafe use of broad-spectrum contact herbicides is seldom possible.Hence in the work reported here, the tolerance of young treeseedlings to the potentially more selective, post-emergenceherbicides clopyralid, cycloxydim and metazachlor, was tested.Seedlings of Fraxinus excelsior L. (ash) with two to four expandedtrue leaves (2–4 ETL), Fagus sylvatica L. (beech) (2–4ETL), Acer pseudoplatanus L. (sycamore) (4–6 ETL), Prunusavium L. (cherry) (6–8 ETL) and Quercus robur L. (oak)(6–8 ETL) appeared to tolerate applications of cycloxydimat a rate of 0.45 kg a.i. ha^–1. Applications of 0.2 kga.i. ha^–1 clopyralid or 1.25 kg a.i. ha^–1 metazachloralso appeared to be generally tolerated, but did cause somesuppression of annual growth increment in Q. robur, P. avium,F. sylvatica and A. pseudoplatanus, particularly where repeatapplications were made to the earliest growth stages. Seedlingsurvival was unaffected by any herbicide treatment. Mixturesof all three herbicides were no more damaging than the sameherbicides applied separately. Therefore, depending on treespecies and growth stage, it appears that clopyralid could potentiallybe safely used to control a range of herbaceous weed species,metazachlor a variety of seedling or germinating weeds and cycloxydima range of established grass weed species, in direct sown woodlandsor nursery seed-beds, although further research is advisableto confirm crop safety.     

The growth of young oak trees in shelters

Shelters are 1.2 m tall plastic tubes which protect trees fromanimal damage and improve growth by creating a ‘greenhouseeffect’ round each tree. After 3 years the mean heightgrowth of sessile oak transplants in shelters was 142 cm comparedwith 45 cm in a mesh guard and 27 cm for unprotected trees andthe average stem volume was 118, 37 and 19 cm³ respectively.There was no difference in growth in a range of sizes of conicaland cylindrical shaped shelters and an 8 cm diameter cylinderis large enough for oak. Other experiments have confirmed thatshelters made from a variety of plastics are equally effectivebut many lack adequate durability. Work continues to developimproved shelters and it appears that for oak a shelter effectfor 2 to 3 years, support for 5 years and deer protection for8 years would be ideal. In 1983/84 about a million shelterswere used in Britain and trials have started in other countries.     

Simulated yield and quality distribution of sawn timber from final felling in a Norway spruce [Picea abies (L.) Karst.] stand with varying thinning regimes: A case study

Abstract

An integrated simulation tool, formed by integrating the InnoSIM sawing simulation system with the RetroSTEM simulator, was used to convert available wood raw materials from final felling into sawn timber, allowing for calculation of the three-dimensional wood properties of individual stems (stem geometry, heartwood formation, knottiness) as well as the volume, quality and value of sawn timber in a Norway spruce stand with different thinning regimes (unthinned, normal and intensively thinned). Based on the input data of sawing patterns, the simulations indicate that there are relatively small differences (<8%) in the volume yield (m³ha^?1) of sawn goods resulting from sawlogs available from final felling with different thinning practices. However, intensive thinning yielded the largest stem diameters and the greatest volumes (m³ha^?1) of large-sized centre goods (thickness: 50, 63, 75 mm) of rather poor quality. Normal thinning yielded the largest volume of A-grade side boards and centre goods (m³ha^?1), as well as the best total value ([euro]ha^?1) of sawn timber. Differences observed in sawn timber quality distribution can contribute to even more significant variation in value yields, if pricing mechanisms of timber products change to favour higher grade timber products.     

Productivity and thinning effects in hybrid aspen (Populus tremula L. x P. tremuloides Michx.) stands in southern Sweden

The productivity of hybrid aspen stands in southern Sweden,originating from clone selections performed during the 1980s,was investigated. Thirteen former research and demonstrationsites were included. Repeated measurements of tree diametersand heights were taken, from which yields were estimated. Theresults indicate that the mean annual increment, obtained withoutany artificial addition of fertilizers or irrigation, will exceed20 m³ of stem wood ha^–1 a^–1 during a 20–25-yearrotation period. This corresponds to a total average woody biomassproduction, including branches, of over 8 tonnes dry matterha^–1 a^–1. These production levels show that hybridaspen is a competitive alternative for short rotation forestryin Sweden, and that the clone selection programme has greatlyenhanced productivity, compared with published growth ratesof the material previously used. For comparison, two standsthat regenerated via root suckers from material used in thebreeding programme up to the 1960s were included. They showedhigher growth than the 13 planted stands, mainly due to higherstem density and faster height development. This indicates thateven further increases in hybrid aspen yield are possible instands derived from suckers of the most recently selected clones.Thinning studies, including three different weights of thinning,were carried out on five of the sites. Five years after thestart of the treatments, stands given no thinning showed significantlyhigher current annual increment, but significantly smaller meanstem diameter than stands in which thinning was applied. However,the faster diameter development (and thus higher volumes ofvaluable wood assortments) associated with heavier thinningsmay compensate economically under current market conditionsfor the loss in total volume production.     

Efficiency of Tree Crowns and Stemwood Production at Different Canopy Leaf Densities

Variation in the unit leaf rate in trees, i.e. the weight ofwood increment per unit of leaf area, arises from disproportionatechanges in their rates of net photosynthesis and in the allocationof carbohydrates. Changes in unit leaf rate in response to variationsin canopy density were investigated in a thinning experimentestablished in a 36 year-old Douglas fir forest. Tree growthwas estimated from increment cores and leaf area by linear correlationwith sapwood basal area. Net assimilation and mean growth ofindividual trees expressed as basal area and volume decreasedin direct proportion to increase in canopy density from 3.6to 12.0 m²m^–2 of projected leaf area. These relationshipswere linear with multiple correlation coefficients (r²)0.97. Net stand increment, in contrast to unit leaf rate, culminatedas projected leaf area approached 6 m²m^–2 and decreasedat the higher canopy densities due to mortality. The approachdeveloped in this paper could be applicable in predicting growthin response to various silvicultural treatments.     

Drought response of upland oak (<Emphasis Type="Italic">Quercus</Emphasis> L.) species in Appalachian hardwood forests of the southeastern USA

Key message

In Appalachian hardwood forests, density, stem size, and productivity affected growth during drought for red oak, but not white oak species. Minor effects of density suggest that a single low thinning does little to promote drought resilience for oaks in the region.

Context

Management is increasingly focused on promoting resilience to disturbance. Because stand density can modulate climate-growth relationships, thinning may be an adaptation strategy that promotes resistance/resilience to drought.

Aims

We examined how density, manipulated via thinning, stem size, and site productivity, influences the drought response of northern red, black, chestnut, and white oak.

Methods

We modeled the role of density, stem size, and site productivity on resistance, recovery, and resilience during two drought events.

Results

Chestnut and white oak displayed greater resistance, recovery, and/or resilience than did northern red and black oak. For black oak, density and stem size negatively affected resistance during the first and second drought, respectively. Density, stem size, and site productivity had no effect on chestnut and white oak.

Conclusion

The lack of sensitivity of chestnut and white oak to the ranges of density, stem size, and site productivity observed in this study and generally better resistance, recovery, and resilience suggests that management focused on the maintenance of these species, as opposed to a single silvicultural low thinning, may be a possible strategy for sustaining the growth and productivity of oak species in Appalachian hardwood stands. Drought response as affected by alternative thinning interventions should be evaluated.

     

Silviculture of ash in southern England

In 1992 the Wessex Silvicultural Group held a number of meetingsto study the silviculture of ash, during which 16 sites throughoutcentral southern England were visited. Ash can produce valuabletimber on relatively short rotations, and to take full advantageof this potential stands must be carefully managed. The mainpoints to consider are: (1) site selection: ash is site demandingand grows best on moist calcareous barns of pH 6 to 7. Sitesprone to frost should be avoided. (2) Spacing: if timber productionis an important objective, ash should be established with atleast 2500 stems ha^-1 on bare land and 2000 stems ha^-1 on restockingsites. It is sensitive to exposure when young and requires sideshelter making it unsuitable for pure planting on exposed ground.(3) Weed control: this is essential for successful establishment.It is recommended that an area of at least 1 m² around eachtree should be kept weed free for at least 3 years. (4) Protection:the species is relatively free from squirrel damage but is palatableto voles, rabbits, hares and deer. Protection using appropriateindividual tree protection or fencing is essential. (5) Thinning:once a height of 6–7 m has been reached ash should havefrequent crown thinnings to maintain a live crown over at leastone-third the height of the tree. Under-thinning was by farthe most common fault in the stands visited.     

The tolerance of young trees to applications of clopyralid alone and in mixture with foliar-acting herbicides

The selective herbicide clopyralid is often used to controlcompeting Cirsium arvense in newly planted woodlands. When appliedas an overall spray at different dates in the spring (at 0.2kg acid equivalent (a.e.) ha^–1) to 10 tree species (Fraxinusexcelsior, Prunus avium, Quercus robur, Acer pseudoplatanus,Populus x canadensis cv. ‘Ghoy’, Pseudotsuga menziesii,Pinus nigra ssp. laricio, Larix kaempferi, Picea abies and Piceasitchensis) it did not reduce survival, and had little effecton growth. However, some species showed distortion of the youngestsprayed leaves or needles for several weeks after treatment,particularly F. excelsior, L. kaempferi and P. x canadensis.Sequential applications of clopyralid (first at 0.1 kg a.e.ha^–1 followed by 0.2 kg a.e. ha^–1 after 3 weeks),which are often required to control C. arvense, did not leadto increased leaf damage or growth reduction. Mixtures of clopyralidwith selective graminicides (cycloxydim at 0.45 kg active ingredient(a.i.) ha^–1; fluazifop-p-butyl at 0.38 kg a.i. ha^–1and propaquizafop at 0.15 kg a.i. ha^–1) did not causesignificant adverse effects on survival or growth of any species.If herbicides are required to control mixed stands of susceptibleproblem weeds such as C. arvense and grasses which are overtoppingyoung trees, these herbicide mixtures, applied as overall sprays,are less likely to cause damage to trees than attempts to usedirected applications of broad-spectrum foliar-acting herbicides.     

Carbon storage and sequestration in the forests of Northern Ireland

The rate of accumulation of carbon in forests and woodlandsin Northern Ireland was estimated using the record of forestplanting since 1900 and a model that calculated the flow ofcarbon from the atmosphere to trees, litter, soil, wood productsand back to the atmosphere. It was assumed that all coniferforests had the carbon accumulation characteristics of Piceasitchensis, and upper and lower estimates of carbon storagewere calculated assuming Yield Class 16 m³ha^–1 a^–1unthinned and Yield Class 14 m³ ha^–1 a^–1 thinned.Broadleaved woodlands were assume to have the carbon accumulationcharacteristics of Fagus sylvatica, Yield Class 6 m³ha^–1a^–1. Northern Ireland currently has about 78 300 ha offorest, 83 per cent of which is coniferous, 77 per cent state-owned,mostly planted since 1945, with peak planting in 1960–1975.In 1990, conifer forests contained 3–4 MtC (trees + litter)and broadleaved wdlands contained about 0.8 MtC (trees + litter+ new forest soil). In 1990, conifer forests were sequestering0.15–0.20 MtC a^–1 and broadleaved woodlands about0.025 MtC a^–1. To maintain these sink sizes, new coniferforests need to be planted at 1500–2000 ha a^–1,and new broadleaved woodland at100–150 ha a^–1 inaddition to full restocking. Current carbon sequestration byNorthern Ireland forests represents around 6.5–8.2 percent of the total for UK forests and is greater per hectar thanin Britain because the average forest age is younger in NorthernIreland