109Chapter 8FORESTRY, BIODIVERSITYAND PROTECTED AREAS8.1 Main developments since the first<strong>Environmental</strong> <strong>Performance</strong> <strong>Review</strong>Since the first EPR, national legislation related t<strong>of</strong>orestry, biological diversity and protected areas hasbeen improved. Currently, the most importantnational policy development related to forestry andforest management is the transfer <strong>of</strong> ownership,rights to use and responsibilities for the management<strong>of</strong> what is ultimately planned to be 60 per cent <strong>of</strong><strong>Albania</strong>’s forests and pastures to local communes.8.2 Forests and forestryForest coverAccording to the 2005 Law on Forests and theForestry Service, No. 9385, forest is defined as anarea covered at least 30 per cent by dense trees onmore than one tenth <strong>of</strong> a hectare, while open forest orforest land is defined as an area covered 5-30 per centby forest vegetation, unregistered in another land-usecadastre. In 2009 the forestry lands (high forests, lowforests/coppices, shrubs and other areas with forestvegetation) encompassed 1,071,880.2 ha, whichaccounts for 37.28 per cent <strong>of</strong> the territory <strong>of</strong><strong>Albania</strong>. The structure <strong>of</strong> the <strong>Albania</strong>n forestresources (forest fund), namely its division intodifferent forest types, surface covered and standvolume for the dominant forest species is presentedin table 8.1.The deciduous high forest tree species (in particularbeech and oak) were prevailing in <strong>Albania</strong>’s forestresources in 2009, both in terms <strong>of</strong> surface covered(56.8 per cent) and stand volume (69.6 per cent),while coniferous forest stands (mostly black pine, firand maritime pine) accounted for only 16.4 per cent<strong>of</strong> the total forest land area and for 21.1 per cent <strong>of</strong>the total forest stand volume. Areas overgrown bybushes accounted for some 24 per cent <strong>of</strong> the totalforest area and 9.3 per cent <strong>of</strong> the total timbervolume.Almost three quarters <strong>of</strong> the territory extendsbetween 200 and 2,000 m above sea level, with amean value <strong>of</strong> 708 m, which is twice the average forEurope. Forests are distributed over most <strong>of</strong> thecountry but, due to the agricultural use <strong>of</strong> lowlands,are predominantly on hilly and mountainous areaswith steep and partly unstable slopes. According tothe data collected for the 2005 national forestinventory, 42.36 per cent <strong>of</strong> the sample forest plotswere located not higher than 800 m above sea level,4.47 per cent <strong>of</strong> plots were located at an altitudebetween 0 and 200 m, and 13.79 per cent between 0and 400 m. Some 44.4 per cent <strong>of</strong> sample plotsrepresented mountain forests, with the altitudinalrange between 400 and 1,000 m. As much as 41.8 percent <strong>of</strong> forest plots were located at elevated areaswith altitudes between 1,000 and 2,000 m.Importantly, the 2005 national forest inventory showsthat on the slope gradient in afforested areas, themajority (62.15 per cent) <strong>of</strong> forest sample plots werelocated on terrain with a slope gradient exceeding 40per cent where forest management, and in particularforest harvesting, should not take place. Only 2.61per cent <strong>of</strong> sample plots were in the 0-10 per centgradient category most suitable for forestmanagement practices and a further 35.24 per cent inthe 11-40 per cent category where the management <strong>of</strong>forests, including harvesting, can still beeconomically sustainable. As much as 49.75 per cent<strong>of</strong> plots were in the 41-70 per cent slope gradientcategory, which is not suitable for sustainableforestry management and which, due to the highexposure <strong>of</strong> such slopes to the erosion <strong>of</strong> the verythin layer <strong>of</strong> fertile organic strata <strong>of</strong> mountain topsoils could be further intensified as a result <strong>of</strong> anyforestry operations. Finally, 12.4 per cent <strong>of</strong> forestplots were in extremely steep mountain areas wherethe slope gradient exceeds 70 per cent, indeedscarcely accessible areas, no longer suitable for anykind <strong>of</strong> management.In addition, the accessibility <strong>of</strong> forest stands whichare suitable for management is further limited by thegenerally underdeveloped network <strong>of</strong> forestry roads.Consequently, forest management practices, inparticular logging (both authorized and illegal),concentrate on the most accessible areas, directlyadjacent to existing regular transport roads.In spite <strong>of</strong> the above limiting factors, the conditionsfor growing forests in <strong>Albania</strong> are favourable, due to
110 Part III: Integration <strong>of</strong> environmental concerns into economic sectors and promotion <strong>of</strong> sustainable developmentthe prevailing Mediterranean climate conditions witha relatively short and very humid winter, and a long,hot and very dry summer, providing for a longvegetation season when the tree stands benefit fromtheir exposure to sunlight. In 2009, as much as 80.6per cent (840,908.8 ha) <strong>of</strong> forest surface areaharbouring some 77.2 per cent (estimated at 584,771ha) <strong>of</strong> the total timber stock was classified asproductive forests, while the remaining 19.4 per cent(201,881.2 ha) with 22.8 per cent (estimated at172,490 ha) <strong>of</strong> the timber volume was classified asnon-productive forests. However, forest productivityis estimated to be much lower than in some otherEuropean countries, partly due to different forestdegradation factors and human pressures on forestecosystems.ForestryOver the last 70 years, <strong>Albania</strong>n forestry has sufferedsignificant changes, as a result <strong>of</strong> which the forestarea has been reduced by more than 300,000 hamostly due to clearance for agriculture (Table 8.2).Moreover, the more accessible forest stands havebeen significantly degraded through overharvestingand overgrazing, which has changed the forest agestructure and species composition, and reduced theforest underwood. For several years tree felling hasexceeded the net annual increment, which hasresulted in a decrease in the growing stock. Usually,such practice creates forests that are younger, moreeven in age structure, biologically less diverse andeconomically less productive. Other adverse effectsare a decrease in natural water retention capacity,increased threat <strong>of</strong> forest fires, and the disappearance<strong>of</strong> wildlife and bird species which require largerundisturbed forest complexes.Between 1990 and 2009 the total surface <strong>of</strong> forestland increased by some 27,200 ha (Table 8.2).Simultaneously, the surface area classified as highforest decreased by some 32,300 ha (6.6. per cent <strong>of</strong>the high forest surface in 1990) and in 2009accounted for 42.37 per cent <strong>of</strong> the total surface.However, depending on the statistical method usedfor forest area and forest type classification, availabledata on forest structure may differ. For instance, datafrom the 2004 national forest inventory project,Special Study on Forest and Pasture General Plan,following the categorization method later confirmedby the 2005 Law on Forests and the Forestry Service,estimates the high forest surface at 294,957 ha (19.68per cent <strong>of</strong> the total forest area) with a breakdowninto areas covered by coniferous high forest (84,461ha) and broad-leafed high forest (210,496 ha), whilethe acreage <strong>of</strong> coppice forest is estimated at 405,016ha (27.02 per cent), <strong>of</strong> shrubs at 241,724 ha (16.13per cent), and <strong>of</strong> open forest at 557,260 ha (37.17 percent). The 2005 Law on Forests and the ForestryService determines the total forest fund areas to be1,498,957 ha.The current age structure <strong>of</strong> forests clearly reflectsthe results <strong>of</strong> overharvesting in the past, as the greaterpart <strong>of</strong> high forest stands has not yet reached cuttingmaturity, irrespective <strong>of</strong> dominant tree speciescomposition and habitat, which determine theoptimal felling age for particular species. In the highforest stands the first four age classes (trees agedbetween 0 and 80 years) are predominant, accountingfor as much as 65 per cent <strong>of</strong> the high forest surface,with 48 per cent <strong>of</strong> tree stands aged below 60 years.The vast majority (73 per cent) <strong>of</strong> the low foreststands is below 20 years in age. On the other hand,the old-growth forest stands (aged above 140 years),either already protected or in need <strong>of</strong> protection, stillaccount for 4 per cent <strong>of</strong> the high forests.Forestry and agriculture are two importantcomponents <strong>of</strong> land use in rural areas <strong>of</strong> <strong>Albania</strong>,closely interrelated throughout history. As the forestssurrounding villages are used for grazing, no cleardistinction can be made between these two differentland-use forms. Official statistics <strong>of</strong>ten aggregatedata on forest surface with the surface <strong>of</strong> pastures.Moreover, this is also reflected in the institutionalstructure <strong>of</strong> MoEFWA, in which both land uses areamong the competencies <strong>of</strong> one department, theDirectorate <strong>of</strong> Forests and Pastures (DFP).Wood is commonly used for heating and cookingpurposes, not only in rural areas and remotely locatedmountain settlements but also peri-urban zones,whenever households have no access to other fuelsources, e.g. through communal gas pipelineinstallations. Therefore, timber consumption byhouseholds has always been higher than by industryin <strong>Albania</strong>. In 2003, some 415 wood processingplants processed about 360,000 m³ <strong>of</strong> timber, whilesimultaneously the documented level <strong>of</strong> fuel-woodconsumption was 1.6 million m³ per year. The latternumber may correspond to the current un<strong>of</strong>ficialestimates for illegal cuts per year (between 0.5 and2.0 million m³ <strong>of</strong> timber volume).Illegal cuts <strong>of</strong>ten have no commercial purpose (thusnot all cases should be classified as “unauthorizedcommercial logging”). They result from thesubsistence needs <strong>of</strong> the rural population andcommonly understood traditional right to use thenatural resources <strong>of</strong> the area, to a large extenttolerated by the authorities despite the legallyimposed sanctions and fines for such lawinfringements. The intensity <strong>of</strong> such illegal practices
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UNITED NATIONS ECONOMIC COMMISSION
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vPrefaceThe second EPR of Albania b
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viiLIST OF TEAM MEMBERSMr. Antoine
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ixMinistry of Agriculture, Food and
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xiCONTENTSForeword ................
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8.3 Biological diversity ..........
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1Introduction I.1 Physical contextA
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for 2004 was prepared within the St
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163Chapter 6: WATER MANAGEMENTRecom
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173Chapter 12: HUMAN HEALTH AND THE
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178Worldwide agreementsYear1979 (BO
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183Land resources and soil 2002 200
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188Law on Local Tax System, No. 963
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