Comparison of Natural Regeneration Establishment in the Forest Stands under Management

Similar documents
Carbon sequestration potential of Eucalyptus and Acacia plantation in central areas of Iran. Seyed Armin Hashemi 1.

A brief introduction to general terms and concepts related to the forestry learning objectives

A Study of Tree Distribution in Diameter Classes in Natural Forests of Iran (Case Study: Liresara Forest)

3. The poor condition of Connecticut s forests in the late 1800s and early 1900s helped spur the conservation movement in CT.

Unit A: Introduction to Forestry. Lesson 2:Understanding Forest Ecology

Plantation Forestry: A Global Look

Vancouver Island Land Use Plan Higher Level Plan Order

Responsible Forest Management IS Wildlife Management

THE EFFECTS OF INVASIVE SPECIES AND HABITAT MANAGEMENT ON NATIVE TREE RECRUITMENT

Forensic Forestry Reading the Land

Mixed-Oak Forest On A Fine-Textured Alfisol

Oriental sweet gum. Liquidambar orientalis. Technical guidelines for genetic conservation and use

Silvicultural practices in the restoration of degraded ecosystems

Forestry. A Big Thanks

Gaining i ground: in a new century

Chapter 13 Private Native Forestry: River Red Gum

Characteristics of Five Climax Stands in New Hampshire

Microbial biomass, ammonium, and nitrate levels in the soil across a northeastern hardwood/mixed conifer chronosequence Abstract Intro

MOTTI USER S GUIDE version 3.3. Natural Resources Institute Finland

MORATORIUM FIRE AND LOGGING INCREASE ABOVE GROUND CARBON STOCK: A CASE STUDY IN BURNT PEAT AREA OF EX-MEGA RICE PROJECT, CENTRAL KALIMANTAN, INDONESIA

Fax: (613) January 16, 2015 L3R 1R2. Dear David, by the City permit to. remove the. will be lost. Table 1. Tree No. 1. D.B.

Author(s) Lu, Yong; Asato, Isao; Zhou, Genmia. 琉球大学農学部学術報告 = The Science Bulletin.

Sustainable Forest Management Plan. Appendix 6: Reforestation Strategy Stocking Standards and Crop Tree Requirements

Outlook Landscape Diversity Project

Northern deciduous forest as wildlife habitat. Tom Paragi Alaska Department of Fish and Game Fairbanks

How would you measure shrub cover here? FOR 274: Forest Measurements and Inventory. Density: What is it?

Seed Dispersal in Tropical Forests

FORESTRY TALK: A GLOSSARY OF COMMON TERMS

Forest and climate change

ORDER UNGULATE WINTER RANGE #U2-005

Red Pine Management Guide A handbook to red pine management in the North Central Region

Study of the North-facing Slope. of the Grand Valley State University Ravines. B.M. Hussey. K.J. Sylvester

Forest Biomes. Chapter 9

Supplemental Figure 1.

PROCESSING SOIL AND PLANT DATA PRINT-OUTS AND RECOMMENDATIONS. V. Sadreika 1/ INTRODUCTION

Potential Income of Community Forests from Forest Carbon Sequestration (A case study of Mahottary district, Nepal) I C Dutta R. A. Mandal Nisa Acharya

National Environmental Standards for Plantation Forestry. Overview of the regulations

Design With Nature: How to Create an Old Growth Forest. Chuck Pettis Earth Sanctuary

The Regeneration of Aspen Stands in Southern Utah

Yield Prediction for Acacia mangium Plantations in Southeast Asia

Timber Stand Improvements TSI

Defining Forests. forestry hardwood log native forest old-growth forest. E-unit: Defining Forests Page 1

Nehalem River Watershed Assessment 1

UNEVEN-AGED MANAGEMENT NORTHWEST CERTIFIED FORESTRY

SCHIRP: Second Broadcast Fertilization Application.

OUR FORESTS, OUR LIFE

Nova Scotia s Code of Forest Practice A Framework for the Implementation of Sustainable Forest Management

Examining Reforestation Practices

WILDLIFE ECOLOGY AND CONSERVATION STUDY NOTES

Evaluation of different sampling method to study of Diameter at Breath Height in the Zagros forest

Information on LULUCF actions by Sweden. First progress report

Ontario Hardwood Overview. Hardwood Tour Oct.19-21

People and the Temperate Region n /-» _ r»» i r. i,,.._ ^^ fen and the Biosphere Program 1991

Practice Plan for Sparta Mountain Wildlife Management Area (WMA) Stand 33: Restore Old Growth

Sustaining Terrestrial Biodiversity: Saving Ecosystems and Ecosystem Services

Intensively Managed Pine Plantations

. HSM904 Timberjack 450C. Archive of SID HSM904. Timber jack- 450C HSM

MANITOBA ENVIROTHON WATER AND AQUATIC ECOSYSTEMS

Understanding the role of biochar in site restoration and carbon sequestration

Mechanical Site Preparation

Planning Commission November 20, 2013 URBAN FORESTRY LANDSCAPING CODE UPDATES

2.4 MANAGING FOR HIGH-VALUE TREES

The use of energy wood

Forest Thinning Scheduler. User s Guide

Dang Thi Tuoi Biodiversity Conservation Agency (BCA) Ministry of Natural Resources and Environment of Vietnam (MONRE)

Visual Management System and Timber Management Application 1

Evaluating the Effects of Projected Climate Change on Forest Fuel Moisture Content

Spacing to Increase Diversity within Stands

Forest Sustainability: An Approach to Definition and Assessment at the Landscape Level Michael P. Amaranthus

Towards FRA 2010 some selected topics. Stein M. Tomter Norwegian Forest and Landscape Institute

Fire & Characteristics of Wildfire

Status of climate change adaptation in agriculture sector for Lao PDR.

The Natural Role of Fire

SILVICULTURE & WILDLIFE HABITAT MANAGEMENT

Primary questions: Incorporating Biomass Harvesting into Sustainable Forest Management: Issues and Guidelines

DEVELOPMENT OF FOREST REGENERATION IN BAVARIA AFTER THE STORM DAMAGES IN 1990

ECOLOGICAL RESTORATION: AN OVERVIEW

SANTA CLARA Protections in place:

Appendix 1: Forest Carbon Emission Offset Project Development Guidance

The invasion of Eupatorium odoratum in secondary tropical monsoon forest in the watershed of Bian-Kumbe in Merauke, Papua Indonesia

Lecture 3.4: Fire effects on vegetation

Terms and definitions used in FRA 2010

Appendix A Silvicultural Prescription Matrix Spruce Beetle Epidemic and Aspen Decline Management Response

12-1. TIMBER ESTIMATION 291

NATURAL RESOURCES FOREST MANAGEMENT

LITTLE PRAIRIE COMMUNITY FOREST: B2B October 12, 2016 Presented by Jeff Beale, RPF

2/24/2009. The factors that determine what type of forest will grow in a region are temperature precipitation growing season soil land forms

ORMCP Technical Paper 7 Identification and Protection of Significant Woodlands

Evaluation of different sampling method to study of tree density (tree/hectare) in the Zagros forest

Habitat Restoration, Longleaf Pine Forests, and the Flatwoods Salamander. Goals of Today s Talk. Habitat Restoration. Habitat Restoration

E8 Forest Management Plan

Taiwan Sugar Corporation s Participation in the Mechanism of Payment for Environmental Services (PES)

Radical Terraces Rwanda - Amaterasi y'indinganire

Effect of cow manure and nitrogen fertilizer on canola in Gorgan area

UNIVERSITY OF CAMBRIDGE INTERNATIONAL EXAMINATIONS International General Certificate of Secondary Education

Conserved Forest Ecosystems: Outreach and Research Cooperative (CFEOR)

Forest Inventory in New Brunswick: A Year with LiDAR. Adam Dick New Brunswick Department of Natural Resources NEMO/SOMENS November 2014

Rufford Small Grant. (for Nature Conservation) In association with the Whitley Laing Foundation REPORT

Forest data services of the Finnish Forest Centre. Juho Heikkilä, Chief Forest Data Specialist, Lic.Sc. (For.) Lahti, Finland, May 31, 2017

Explanation of the Forest Planning and Practices Regulation Amendments to Protect Secondary Structure

Transcription:

World Applied Sciences Journal 12 (4): 465-470, 2011 ISSN 1818-4952 IDOSI Publications, 2011 Comparison of Natural Regeneration Establishment in the Forest Stands under Management Seyed Armin Hashemi Department of Forestry, Islamic Azad University, Lahijan Branch, Iran Abstract: With regard to desired natural regeneration establishment that it is the goal of selection systems. The role of tree and group selection silvicultural systems on the quantity and quality of natural regeneration was conducted at four site of forest. First, 100 circular sample plots has been selected by use of random systematic inventory. Then into the each plots nine micro-plots defined. The results of one way analysis of variance, multiple ranges Tukey-HSD test and Chi square test of seedling showed that there is significant difference in the level of 0.05 between mean of seedlings number, mean of carpinus seedlings number, percent of the health, shining, even and vertical seedlings in tree selection and group selection systems. So in the establishment of natural regeneration the quantity and quality of natural regeneration in tree selection system is more desirable than group selection system. In the bigger cutting sites the stand comes out of climax conditions and in the result it will reduce the establishment percent of original species regeneration. With regard to the desirable results of tree selection system it is necessary to recommend that tree selection system should be write down in forest management plans description. Key words: Natural regeneration Tree selection system Group selection system INTRODUCTION and spread [5]. In fact best indicator and natural result of conducting these plans is young established stands Since environment destruction especially in respect developed by using natural regeneration in another words of forests, decreased forest varea and natural regeneration seedlings established instead of harvested trees [6]. due to performing some silvicultural techniques are critical Then most suitable measure to evaluate success of warnings and among major issues for human, then it's forestry plans is extent of establishment natural life necessary to consider most important factor in survival of restoration [7]. forests namely natural regeneration [1]. Performing group single selection system will Firstly, it must be keep in mind that it is necessary to decrease natural life restoration strength and will bring preserve bio diversity stability by using most suitable down species diversity [4]. Silvicultural system has silvicultural system for forest stands with typical species adverse effects on soil composition. various effects of [2]. Selection and execution of suitable silvicultural silvicultural systems on leaf litter and soil nitrogen system can create a forest stand with good natural mineralization [3]. Regeneration as one of most important regeneration (quantitative and qualitative), normal and measures of evaluating sustainable management of desired structure (normal species composition, normal natural forests [7]. Forest survival has meaningful stand density normal or ordinary blending from, normal dependence on key goal must be considered. diagonal distribution and scattering, existence of all Preserving biodiversity stability through finding germination stages including sapling, seedling, loose and most suitable silvicultural system for stand. Than major spot) [3]. goals of program could be achieved and measurements Then forest's beautiful view, natural form of waterway of developmental periodic evaluation towards these and natural components of habitat will be preserved goals could be performed. According to the fact that wholly with biodiversity stability [4]. Therefore, results natural regeneration is most inexpensive and sustainable of performing forestry plans must be evaluated to regeneration system, then its establishment is major goal recognize process of sustainable forests development of all silvicultural systems. Corresponding Author: Seyed Armin Hashemi, Department of Forestry, Islamic Azad University, Lahijan Branch, Iran, Tel: +9125088328, E-mail: ahashemi_2004@yahoo.com. 465

MATERIALS AND METHODS Chi-square test. Mean frequency of sapling and seedling of various species in tree, group and control single - Study Area: This study performed in district Guilan selection silvicultural system were compared using results province in north of Iran. The area of district is 2145 of one way analysis and multiple - ranges turkey - HSD hectares. Test in significance level of 5%. Studied Plots: 100 circular sample plots (with radius RESULTS AND DISCUSSION 17.8 m and area of 1000 m) and each sample plot containing 9 micro plots (3 3m) totally 900 micro plots. Results of Sapling and Seedling Number Comparison (5-130 cm Height) in Different Treatments: The greatest Sampling Method: Firstly, using random systematic number was in single - selection system with 7246 inventory moved from defined base point on a baseline in seedling in hectare. Number of seedling in single - forest and 100 sample plots were selected with consistent selection system was greater than number of seedling in distribution. 50 sample plots of those plots were centered control (undisturbed system with 6427 seedling in with a log cutt10 years ago with 50cm diameter. (With help hectare) but number of seedling in group single - selection of labor cut related tree). Then 9 micro plots were defined system (5765 seedling in hectare) was lower than number in each plot first micro plot was defined in the centre of of seedlings in single and control single selection system. plot and 2 micro plots with equal distance (3.5m) were There is significant statistical difference between group defined in each of 4 main directions. (Totally 900 micro selection and single selection systems (Figure 1). plots). In addition, additional 50micro plots were selected adjacent to undisturbed or control parts and 9 micro plots Results of Comparing Mean Number of Saplings (5-130 were defined as previously in each sample plot. Finally in cm Height) in Hectare Various Treatments: Results of each micro plot following parameters were measured statistical analysis of one way analysis of variance such as situation of plot, physiographic, soil status, indicated that there is no significant difference between forest stand status, typical plants, qualitative and mean number of sapling in studied system. (d.f = 2 F = quantitative status of maternal trees. 0.0166, P = 0.984). Statistical System of Data Analysis: Processing data Results of Comparing Mean Number of Seedlings (31 - analysis, comparison and evaluation of silvicultural 130 cm Height) in Hectare in Different Treatments: systems were performed by software Excel, SPSS and Statistical analysis was performed by using SPSS and MINITAB. Interpretation or evaluation of regeneration one - way analysis of variance and multiple ranges status results in respect of sapling and seedlings Turkey - HSD tests. Results indicated that the number of frequency (in 2 growing stage), percent of seedlings seedlings in 3 studied treatments was different and there qualitative status (health, shining, even and vertical) is significant statistical difference. (d. f = 2, F = 4.905 were performed using figures resulted from EXCEL and P = 0.011). Fig. 1: Comparison of mean number of saplings and seedling (5-130 cm height) in group and tree single selection system 466

Comparing Percent of Healthy Saplings and Seedlings in Single, Group and Control Treatments: Percent of healthy seedlings in group single - selection (78%) was lower than percent of healthy seedlings in control (undisturbed) (91%) and tree single - selection (92%). results of chi - square test indicated that percent of difference in health of Fig. 2: Structure of qualitative status of seedlings seedlings between 2 treatments is significant in level (healthy percentage) in group single - selection of 5 (Figure 2). and tree single - selection treatments Comparison of Percent of Shining Saplings and Results of Comparing Mean Number of Seedlings and Seedlings in Single, Group and Control Single - Sapling of Fagus in 3 Treatments in Hectare: Results of Selection Treatments: Percents of shining seedlings in analysis of variance indicated that there is significant difference of 5% between mean number of seedlings and saplings of Fagus. Results of Comparing Mean Number of Acer Saplings and Seedling in 3 Treatments in Hectare: Results of analysis of variance indicated that there is a significant difference of 5% between mean number of saplings and seedlings of Acer (d.f = 2 F= 1.204, P = 0.306) Results of Comparing Mean Number of Saplings and Seedling Carpinus in 3 Treatments: According to results of Turkey - HSD test, there is a meaningful difference of 5% in mean number of saplings and seedlings between treatments (d. f = 2, F = 4.31, P = 0.017). Comparison of Mean Number of Seedling Seedlings of Other Species in 3 Treatments: According to results of analysis of variance there is no significant difference in mean number of saplings and seedlings between treatments (d. f = 2, F = 0.459, P = 0.634). single selection system was lower (91%) than control system (undisturbed, 93%) and group single - selection system (93%). Chi-square test indicated that difference between percent of shining seedlings of treatments is significant statistical difference between group and single - selection systems (Figure 3). Comparison of Percent Age of Even Seedlings and Saplings in Single, Group and Control Single - Selection Treatments: Percentage of evenness of seedlings in single selections system was 39%. percentage of evenness of seedlings in group selection system (44%) was lower than percentage of evenness in seedlings of control system (undisturbed 42%). Results of chi - square test indicated that difference between percent of evenness in seedling of treatments is significant in 5%. Fig. 3: Structure of qualitative status of seedlings (percent of shining) in group and single selection systems 467

Fig. 4: Structure of seedlings qualitative status (evenness percentage) in single and group and control treatments) Results of one way analysis of variance indicated that there is no significant difference between mean number of systems (d. f = 2, F = 0.0166, P = 0.984). Total results of turkey - HSD test and one way analysis of variance of three parameters of mean number of saplings and seedlings in Fugues, Acer and carpinus indicated that there is no significant difference between 3 treatment in 5% (Table 1). But according to results of Tukey - HSD test there is significant difference of 5%, between number of saplings and saplings of carpinus. (d. f =2, F = 1.204, P = 0.306). Total Results of All Tests Conducted on Seedlings Fig. 5: Structure of seedlings qualitative status (vertical) Quality: Total results of chi-square test indicated in single and group and control treatments that there is significant difference between percent of healthy, shining, evenness and verticality of In other word, there is significant qualitative difference seedlings in three treatments in 5 %. In other between tree and group single selection systems words, in respect of quality, percentage of health (Figure 4). and shining seedlings in single selection systems is higher than group selection. (Figure 2, 3), reverse Comparison of Percent of Vertical Saplings and (Figures 4,5). Seedlings in Single, Group and Control Single Selection Treatments: Difference in percent of Explanation and Evaluation of Total Results of vertical (seedlings in treatments was significant Tests: According to results of Tukey - HSD, in 5%. In other word there is significant difference difference between mean number of 2 parameters between tree and group single - selection systems in of saplings and seedlings, difference of mean respect of verticality according to chi - square test number of seedlings, mean number of saplings (Figure 5). and seedlings in three treatments is significant in 5%. Then according to these results, final conclusion is Total Results of All Tests Conducted on Seedlings that conducting group selection system not only Quantity: Total tests indicated that there is decreased the number of seedlings in hectare but also significant difference of 5% between means of three decreased the percent of shining and healthy seedlings treatments. (Figure 1, d.f=2, F=4.905 P=0.011). (Figures 2,3). 468

Table 1: Mean frequency of sapling and seedlings of fagus, Acer, Carpinus and other species (Parrotia persica, persimmon, birch, ulmus glabra) in tree group and control single selection systems Fagus seedling Acer seedling Carpinus Otherspecres Kind of management tree in hectare tree in hectare seedlingtree in hectare seedling tree in hectare Single selection system 9395 3043 367 1441 Group selection system 778 2694 998 1295 Control (undisturbed) 1816 2724 612 1275 Mean while, decrease of seedlings numbers number Determine sustainable development level of Belt in hectare is severe in vegetative stage. In relation of forests, single selection system is more suitable than species composition structure, performing group single - group single selection system [9]. Single selection selection system when compared to control caused silvicultural system in mountainous forests is more increase of carpinus saplings and seedlings number. suitable than group selection due to extreme ecological In contrast, seedlings of fugues and Acer have decreased conditions [10]. (Table 1). Final Discussion of All Parameters Influence on Discussion of Influence of Herbaceous Layer of Forest Regeneration: Results indicates that single selection Floor on Regeneration: Results of present study method was completely consistent to nature and indicates that by performing group selection system, increased natural restoration strength (Figure 1). Then, raspberry and herbaceous species. Will cover all area due tree regeneration system's restoration strength is higher to creating larger space then seeds of maternal trees don't than normal. Effects of cutting of tree and group selection reach soil bottom easily, thus a few seedlings will grow systems by performing control system. They funded out (Table 1). that performing group selection system will decrease the In addition greatest carpinus regeneration was number of seedlings of high class species in hectare. observed in herbaceous layer with density of 50-55% and Results of this study also is consistent to previous lowest regeneration of carpinus was observed in study (Figure 1, Table 1). Permissible basal cuttings herbaceous layer with density of 40-45%. without decreased restoration strength of forest may Growing sites where there is competition between be continued for long time [11]. herbaceous species, soil moisture will approach earlier to critical limit due to increase of consumed water amount. Optimum Silvicultural System: Analysis of all results Then water shortage in seedlings establishment soil will and discussion can be used as typical result for tree be slower. single selection system for this forest and other similar forests which is an optimums silvicultural system. At the Influence of Percent of Forest Canopy Layer on end, it is recommended to avoid group selection system Regeneration: Results of this study show influence of in product forests due to decreased regeneration and lighting conditions on quality of Fagus restoration. causing loss of forests production power. Intensity of low light like high light has a negative effect of quality of restoration in Fagus (Table 1). Fagus REFERENCES restoration will decrease in open and closed canopy layer. Essentially, carpinus is a photopia and thermopile 1. Prescott, C.E, 1996.a Field guide to regeneration of spacers. Thus, as soon as creation of a larger window and salal-dominated cedar hemlock sites in the CWH. increase of light in forest floor, conditions for increased Faculty of Forestry, U.B.C.J. For, 97: 4-10. carpinus seedlings will be provided. Results of this 2. Hutcheson, J.W.P. and D. Given, 1999. Potential study confirm this finding. Value of Indicator Conservation and Management of New Zealand Terrestrial Communities. Science for Influence of Altitude from Sea Level on Regeneration: Conservation. Single selection system is completely suitable for severe 3. Prescott, C.E., 1997. Effects of Clear Cutting and conditions of regeneration in mountains [8]. Conducting Alternative Silvicultural Systems on Rates of groupselection system in mountainous forests will Decomposition and Nitrogen Mineralization in a decrease number of seedlings in hectare [4]. Results of Coastal Mountain Forest.forest Ecology and this study were consistent with mentioned study. Management, 95: 253-260. 469

4. Heywood, V.H.P. and R.T. Watson, 1995. Global 8. Burn, F. and B. Gifu, 1998.a Mapping method for Biodiversity Assessment. Published for the United qualitative assessing the overall value of mountain Nation Environment Program. Cambridge University forests. French J., 131: 131-147. Press, pp: 140. 9. Brad, S., J.P. Kimmins, C. Welham and K. Scoullar, 5. Sardar, M.R., 1996. Imprtance of evaluation of 1999. Defining stand level sustainability and forestry projects with refrencesto roural development exploring stand level steward ship. J. Forestry, Pakistan. J. Forestry, 46: 107-114. 97: 4-10. 6. Wang, B.G., G. Chen and H. Cao, 1999. Assessment 10. Przybylska, K., 1999. Avaluing system for assessing of the forest landscape assets of Tianzhu shan mountain forest a adapted to forest management forest park in Xiamen. J. Beiging Forestry University, planning needs. Sylwan, 143: 27-36. 21: 84-88. 11. Marusak, R., 1999. Problems of Expected Growing 7. William, P.J. and P. Veit, 1998. Building capacity for Stock Calculation with Reference to Calculation of sustainable management of natural forests in east Long Range Allowable Cut.acta Facultatis Forestalis Africa. Reader in Natural Resources Management, Zvolen, 40: 131-144. pp: 71-107. 470