Aluminium: The Need for a Re-Evaluation of Its Toxicity and Solubility in Mature Forest Stands

Aluminium (Al) is a key element in critical loadcalculations for forest. Here, we argue for re-evaluating theimportance of Al. Effects of two levels of enhanced Alconcentrations and lowered Ca:Al ratios in the soil solutionin a field manipulation experiment in a mature spruce stand(1996–1999) on tree vitality parameters were tested. Inaddition, Al solubility controls were tested. Various loads ofAl were added to forest plots by means of an irrigationsystem. Potentially toxic Al concentrations and criticalratios of Ca to inorganic Al were established. The ratio of Cato total Al was not a suitable indicator for unfavourableconditions for plant growth. No significant effects on crowncondition, tree growth and fine root production were observedafter three years of treatment. In 1999, foliar Mg content inthe highest Al addition treatment had declined significantly.This agreed with the known response to Al stress of seedlingsin nutrient solution experiments. No support was found forusing the chemical criterion Ca:Al ratio in soil solution,foliar and root tissue as an indicator for forest damage dueto acidification. Al solubility was considerably lower thanimplied by the assumption of equilibrium with gibbsite,particularly in the root zone. The gibbsite equilibrium iscommonly used in critical load models. Substitution of thegibbsite equilibrium with an Al-organic matter complexationmodel to describe Al solubility in soil water may have largeconsequences for calculation of critical loads. The resultsindicate that critical load maps for forests should bereconsidered.     

An Analysis of the Structure of the Simple Mass Balance Equation: Implications for Testing National Critical Loads Maps

The critical loads concept is used by the UN-ECEConvention on Long Range Transboundary Air Pollution(CLRTAP) for setting pollution reduction targets.Increasing numbers of countries are adopting the SimpleMass Balance equation (SMB) to calculate critical loads ofacidifying S and N for forest soils. The equation is madeup of a series of mass balances each of which is used tocalculate a leaching flux. The assumptions in the SMBequation were investigated by testing its ability topredict current sulphur load and by comparing each of thecalculated leaching fluxes to measured rates. It was notpossible to predict current sulphur load at our sites usingthe SMB equation. The leaching tests demonstrated that,primarily due to its steady state assumptions, the SMBequation generates critical loads that are theoretical longterm estimates of risk, and are untestable. Thesimplifying assumptions sometimes lead to illogicalresults. Some of these can be improved by adding a final,simple but dynamic, calculation step to determine theexpected time until effects are observed. Theacceptability of combining annual average data, which bestapproximates steady state, with a biological indicator isquestionable. It is not possible to test critical loadscalculated using the SMB equation when applied with all ofits assumptions but it is possible to test its fundamentalapproach using non steady state data.     

Mobility and Methylation of Mercury in Forest Soils Development of an In-Situ Stable Isotope Tracer Technique and Initial Results

A method for investigating in-situmethylation and mobility of mercury has beendeveloped and applied to forest soil. The methodis based on additions of stable ¹⁹⁹Hgisotopes to forest soil plots followed bysampling and analysis of isotope ratios of totalmercury and MeHg using ICP-MS. Initial resultsindicate that a fraction (30%) of the mercuryadded to the forest soils is immobilised over atime scale of 16 months. A small but significantfraction of the mercury is methylated during thesame time scale. Higher methylation rates werefound in wetland soil than in dry forest podzolsoil.     

我国森林资源产品流动及其变化特征分析

论文运用物流分析的基本思想,基于我国森林资源产品产量、贸易量统计资料,采用统一单位“原木当量”(m₃),估算了1981～2000年森林资源采伐和产品加工环节的资源流量,进而分析我国森林资源产品流动的变化特征。结果表明,我国从“六五”(1981～1985年)到“九五”(1996～2000年)期间,消耗森林资源量分别为10230×104、11678×104、13444×104和16962×104m₃/a,呈加速增长趋势。其中,来自国外的资源流量占总流量的比重呈增加趋势,“六五”期间占19.1%,到“九五”期间上升为48.3%。流入资源以原木、木浆、纸及纸板、胶合板为主,它们主要来自北美、东亚、东南亚地区,有来源多地区化的变化趋向。森林资源在“六五”期间主要流向原木锯材类产品加工,随着产品流向结构的逐步改善,更多的资源流向人造板类产品的生产消费;纸类产品生产消费的资源流量增加迅速,但主要来自国外。     

补贴对林业生产及森林生态效益影响的经济学分析:一个定量分析模型

不同的林业补贴产生不同的效果:可能提高社会福利,也可能降低社会福利。出现这种差别的原因是补贴使林业生产收益流发生了变化,从而使得林业生产收益最大净现值到来的时间相对于社会最优时间提前或延后。论文建立了一个以林木吸收碳来衡量森林生态效益的林业生产收益定量模型,并通过该模型对华东某市的一项林场补贴政策进行分析。分析结果是,在没有补贴的情况下,该林场最优砍伐时间为第19年,当存在补贴的情况下,林场的最优砍伐时间提前到第11年,而随着碳价格从0增加至1000元/t,社会最优砍伐时间从第19年增加到第31年,造成的社会净损失从7750元/hm²增加到17704元/hm²。鉴于此,合理的林业补贴要能够促使私人效益与社会效益相统一。     

采伐影响下森林景观服务功能变化研究

文章以大兴安岭呼中林业局亚里河林场为研究区,以遥感数据、林相图和采伐设计资料为信息源,选择水源涵养、固土保肥、固定CO2和释放O2四项服务功能,运用景观生态学原理,引用相应模型,估算了研究区1989年和2000年服务功能价值及其空间分布变化;建立历年采伐分布图,计算采伐造成的服务功能价值损失,揭示该损失值与木材生产的经济效益之间的关系,并分析了服务功能价值在各管理区域内的分布。结果表明,1989年服务功能价值为1.85×108元,2000年为1.37×108元,价值20×104元h/m₂以上的面积明显下降。生态服务功能的下降由采伐导致,1989至1999年采伐导致的生态损失价值为0.71×108元,是木材生产获利的1.9倍,采伐损失价值与年出材量呈现相同的变化趋势。最后证明了管理等级区划和限制采伐量,即“天保工程”,将有利于森林植被恢复,大幅度提高整个亚里河林场的生态服务功能。     

黑龙江大兴安岭森林绿色核算研究

在对国内外森林绿色核算研究综述的基础上,对黑龙江大兴安岭1997-2003年森林资源的实物量、价值量和森林绿色GDP等进行了核算。核算结果表明:黑龙江大兴安岭森林的eaGDP(environmentallyadjustedGDP)1997年为38.19×108元,2003年为57.34×108元,年均增长7.01%;森林的eaNDP(environmentallyadjustedNDP)1997年为25.70×108元,2003年为43.96×108元,年均增长9.36%。在森林绿色GDP核算的基础上,进行了资产负债和财富核算。结果表明,1997-2003年,黑龙江大兴安岭林地、林木存量价值呈减少的趋势;森林环境效益呈增加的趋势,反映在社会经济发展中对林地、林木存量的过度开发和利用。森林绿色GDP占GDP的比重和森林资源占国民财富的比重也呈下降的趋势,说明黑龙江大兴安岭虽然在天然林保护工程后,全面禁止天然林采伐,森林的生长量大于消耗量,表现为流量价值有所增加,反映森林是可持续的经营,但从存量上看对国民经济发展的支撑力是下降的。最后,研究指出,应加强生态补偿政策的研究,积极落实森林可持续经营对策和建议加强绿色财富政策的制定,以保证黑龙江大兴安岭森林的可持续发展和绿色财富的增长。     

秦皇岛森林资源现状与可持续发展对策探讨

森林是生态系统的主体,森林资源是人类的宝贵财富和社会发展的基础。本文论述了森林可持续发展的重要意义,分析了秦皇岛森林资源现状,以及开发利用中存在的问题,探讨了秦皇岛森林资源可持续发展的对策。     

CHANNEL RESPONSE FROM SHRUB DOMINATED RIPARIAN COMMUNITIES AND ASSOCIATED EFFECTS ON SALMONTD HABITAT1

ABSTRACT: We surveyed first‐to third‐order streams (channel widths from 1.4 to 10 m) in the southeastern slopes of the Cascade Range of Washington and found two distinct endpoints of riparian vegetation. Where the forest overstory is dominated by park‐like Ponderosa pine (Pinus ponderosa), channels are commonly bordered with a dense scrub‐shrub vegetation community. Where fire suppression and/or lack of active riparian zone management have resulted in dense encroachment of fir forests that create closed forest canopies over the channel, scrub‐shrub vegetation communities are virtually absent near the channel. Other factors being equal, distinct differences in channel morphology exist in streams flowing thru each riparian community. The scrub‐shrub channels have more box‐like cross‐sections, lower width‐to‐depth ratios, more pools, more undercut banks, more common sand‐dominated substrates, and similar amounts of woody debris (despite lower tree density). Temperature comparisons of forest and scrub‐shrub sections of two streams indicate that summer water temperatures are slightly lower in the scrub‐shrub streams. We surmise that these morphology and temperature effects are driven by differences in root density and canopy conditions that alter dynamic channel processes between each riparian community. We suspect that the scrub‐shrub community was more common in the landscape prior to the 20th century and may have been the dominant native riparian community for these stream types. We therefore suggest that managing these streams for dense riparian conifer does not mimic natural conditions, nor does it provide superior in‐stream habitat.     

INUNDATION TOLERANCES OF RIPARIAN WILLOWS AND COTTONWOODS1

ABSTRACT: Throughout western North America, willows and cottonwoods are dominant woody plants in riparian zones, streamside areas that are periodically flooded. This study compared tolerances of willows‐Salix discolor, S. exigua, and S. lutea‐and cottonwoods‐Populus angustifolia, P balsamifera, and P deltoides‐to water inundation, one component of stream flooding. Rooted cuttings were grown for 152 days in 10 cm tall pots in water depths from 2.5 to 10 cm (inundated). Shoot and root elongation growth of the inundated cottonwoods were reduced 23 and 45 percent, while S. lutea was relatively unaffected and the inundated sandbar willow, S. exigua, displayed 72 and 43 percent increases in shoot and root elongation. The inundation reduced transpiration in P deltoides and for mature P balsamifera trees that were flooded by a small reservoir on Willow Creek, Alberta. Those flooded trees died in their second year of inundation. The greater inundation tolerance of willows versus cottonwoods is consistent with observations along Midvale Creek, Montana, where beaver dams created a pond in which P trichocarpa died while willows thrived after five years. These patterns of inundation tolerance are consistent with elevational zones of occurrence as willows‐and particularly the sandbar willow—occur at low elevations close to the stream. The understanding of inundation tolerances should assist in the provision of hydrologic patterns that will conserve and restore these shrubs and trees along streams and could permit their establishment along artificial reservoirs.