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Forest monitoring sistem in Romania, dynamics of romanian forest health status over the period 1990-2002

机译:罗马尼亚的森林监测系统,1990-2002年期间罗马尼亚森林健康状况的动态

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During the 1980s, dieback intensified in the European forests. This factconvinced Romania and most of the European countries to develop the evalu-ation and surveying process covering the main factors having an impact onforests. In Romania, research dealing with the elaboration of a technical-organisational concept was developed between 1983 and 1985. This conceptdealt with the surveying system used to control the quality of environmentalfactors in the forestry estate (Patrascoiu et al. 1985). The system had beenexperimented in the following period (1986-1989). In 1990, it was applied tothe entire national forestry estate (Patrascoiu and Badea. 1990).Today, the organization and functioning of the national forest monitoringsystem is ensured by the Ministry of Agriculture, Forests, Waters andEnvironmental, ROMSILVA and Forest Research and Management Institute(ICAS, as National Focal Centre).This system is functioning in accordance with Low no.444/2002 on"Elaboration and Financing of National Monitoring System soil-land for agri-culture and soil-forest vegetation for forestry".The forest condition survey in Romania is done according to Resolutionno.1 and 6 of the Strasbourg Ministerial Conference (1990), Agenda no.21from Rio de Janeiro (1992) and Resolution no.3 of the Helsinki MinisterialConference (1993). At international level, Romania takes part in theInternational Co-operative Programme on Assessment and Monitoring of AirPollution Effects on Forests (ICP-Forests).The main objectives of the forest survey in Romania are achieved with thesupport of investigations at two levels:Level I - a large scale forest condition survey, based on permanent plots(4x4 km) and European (16x16 km) networks, with lower assessment intensi-ty.Level II - studies and research of intensive nature in a non-systematic sur-vey network placed in forest ecosystems suitable for cause-effect relationshipstudies and located where critical threshold values of pollution are likely to bepresent. Results on Romanian forest health status over the period 2000-2002Forest Research and Management Institute, Bucharest, RomaniaAnale I.C.A.S., 46 var currentpos,timer; function initialize() { timer=setInterval("scrollwindow()",10);} function sc(){clearInterval(timer); }function scrollwindow() { currentpos=document.body.scrollTop; window.scroll(0,++currentpos); if (currentpos != document.body.scrollTop) sc();} document.onmousedown=scdocument.ondblclick=initialize222show that for all species the share of damaged trees (classes 2-4) registeredvalues between 9.7% in 1991 and 21.2% in 1994. For conifers the share ofdamaged trees was between 7.0% (1991) and 16.6% (in 1993) and forbroadleaves between 10.4% (in 1991) and 22.9% (in 1994).At species level, Norway spruce (Picea abies) and beech (Fagus sylvati-ca) were the least affected, with shares of damaged trees between 6.4% (in1991) - 15.3% (1993) and 6.3% (1991) - 15.1% (1994), respectively. For sil-ver fir (Abies alba) the percentage of damaged trees registered the lowest valuein 1991 (9.0%) and the highest in 1994 (22.3%). Among broadleaves, the mostaffected species were Quercus pedunculiflora + Quercus pubescens andQuercus frainetto, the share of damaged trees varying between 19.0% (in1990) - 30.5% (in 1994) and 19.0% (in 1990, 1991) - 45.5% (in 1994), respec-tively.Over the entire analyzed period, the forests from the southern and south-eastern part of the country were the most damaged mainly due to the droughtwhich lasted for a long period (the last15-20 years) in these parts
机译:在1980年代,欧洲森林的荒漠化加剧。这一事实说服罗马尼亚和大多数欧洲国家开展评估和调查过程,涵盖影响森林的主要因素。在罗马尼亚,1983年至1985年间进行了有关制定技术组织概念的研究。该概念与用于控制林区环境因子质量的测量系统相得益彰(Patrascoiu et al。1985)。在接下来的时期(1986年至1989年)对该系统进行了实验。 1990年,它被应用到整个国家林业区(Patrascoiu和Badea,1990年)。今天,国家森林监测系统的组织和运作由农业,森林,水和环境部,罗姆西瓦和森林研究与管理研究所确保(ICAS,作为国家重点中心)。该系统根据有关“国家监测系统农业用地和林业用林地植被的建立和融资”的第444/2002号低要求运行。森林状况罗马尼亚的调查是根据1990年斯特拉斯堡部长级会议的第1号和第6号决议,里约热内卢的第21号议程(1992年)和赫尔辛基部长级会议的第3号决议(1993年)进行的。在国际一级,罗马尼亚参加了国际森林空气污染影响评估和监测合作计划(ICP-Forests)。罗马尼亚的森林调查主要目标是在两个层面的调查支持下实现的:一级-基于永久性地块(4x4 km)和欧洲(16x16 km)网络的大型森林状况调查,评估强度较低。​​级别II-放置在非系统性调查网络中的集约性研究适于因果关系研究的森林生态系统,并且可能位于临界污染阈值的位置。罗马尼亚布加勒斯特森林研究与管理研究所2000-2002年期间罗马尼亚森林健康状况的结果Anale I.C.A.S.,46 var currentpos,timer;函数initialize(){timer = setInterval(“ scrollwindow()”,10);}函数sc(){clearInterval(timer); } function scrollwindow(){currentpos = document.body.scrollTop; window.scroll(0,++ currentpos); if(currentpos!= document.body.scrollTop)sc();} document.onmousedown = scdocument.ondblclick = initialize222表明,对于所有物种,受损树木(2-4类)的注册值在1991年的9.7%和2002年的21.2%之间。 1994年。对于针叶树,受损树木的比例在7.0%(1991)和16.6%(1993)之间,而阔叶树的比例在10.4%(1991)和22.9%(1994)之间。在物种级别,挪威云杉(Picea abies)和山毛榉(Fagus sylvati-ca)受到的影响最小,受损树木的比例分别为6.4%(1991)-15.3%(1993)和6.3%(1991)-15.1%(1994)。对于银杉(Abies alba),受损树木的百分比在1991年最低(9.0%),在1994年最高(22.3%)。在阔叶林中,受影响最严重的树种是齿形栎(Quercus pedunculiflora)+毛栎(Quercus pubescens)和菜豆栎(Quercus frainetto),受损树木的比例在19.0%(1990年)-30.5%(1994年)和19.0%(1990年,1991年)-45.5%(1994年)之间。在整个分析期间,该国南部和东南部地区的森林受到的破坏最大,主要是因为这些地区持续了很长时间(过去15-20年)

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