干热河谷石漠化区火龙果地不同耕作方式的土壤矿质元素特征

为探讨不同耕作方式的土壤矿质元素含量变化特征,促进火龙果生长发育和品质改良,该研究采用套种紫花苜蓿(Medicago sativa)、施用有机肥和化肥与农药、地膜覆盖和无措施五种耕作方式,以每种方式土壤的22种矿质元素为评价指标,比较不同耕作方式的矿质元素含量差异,阐明土壤矿质元素之间的相关关系。结果表明:(1)与无措施相比,其他耕作方式的Ca、Si、Mn等元素含量呈增加趋势,Fe、Mg、Al等元素含量则降低,Na含量无显著差异。(2)施用有机肥的矿质元素含量最丰富,地膜覆盖次之,套种紫花苜蓿最低。(3)相关性分析表明,火龙果地土壤矿质元素间多存在显著相关性,Al、Si、S、Ni与其他元素的相关性较密切,其次为Fe、Mg、Na、Mn、Cu和Co,均达到显著或极显著水平。(4) Ca、Fe、Mg、Mn、Cu、Zn和B之间多呈负相关,存在拮抗效应。干热河谷石漠化区在火龙果栽培时,应首选有机肥作为养分添加方式,并及时补充不同耕作方式造成的土壤矿质养分亏缺,尤其是Fe、Mg、Al、Na、Cu、Zn等元素。     

新疆绿洲农田土壤-棉花系统9种矿质元素生物循环特征

在新疆绿洲区,对不同连作棉田土壤中9种矿质元素含量、棉花植株的吸收和富集特性以及棉田养分收支量等进行分析,研究了农田土壤-棉花系统矿质元素的生物循环特征。结果表明:棉田土壤中微量元素和大量元素均有一定程度的贫化趋势,以Mo的耗竭最为严重。棉株不同器官累积矿质元素的能力有明显差异,叶片中Ca、Mg和Mn的含量较高,根、茎中K、Na、Fe、Mo含量较高,棉籽中Zn和Cu含量最高;不同产品器官对矿质元素的吸收和富集能力不同,秸秆为:MoKMgCaCuZnNaMnFe,纤维:MoKMgZnCuCaNaMnFe,棉籽:MoZnKMgCuCaMnNaFe。棉花对Mo的吸收能力最强,长期连作导致土壤中Mo耗竭较为严重;随籽棉的收获,从棉田移出Zn、Cu的比例和数量较高,大量元素中移出Mg、K较多;棉花对Mn、Fe、Ca、Na的吸收量虽然较多,然而大部分富集在秸秆中,随着棉花秸秆的还田作用,将归还于耕作层并有大量富集,消耗量不大。新疆棉花长期单一种植,应重点补充Mo、Zn和Cu微量元素肥料,酌情补充Mg、K等大量元素肥料。棉田Ca、Na含量较新疆土壤背景低,预示着棉田土壤在向着脱盐碱方向发展,然而两元素在秸秆中的比例较高,因此棉花长期连作农田,应注意防止耕作层土壤向次生盐碱化方向发展。     

湘西地区木通果实微量元素的测定

采用马弗炉干法灰化消化样品,火馅原子吸收法连续测定白木通Akebia trifoliata var.australis (Cieli._Kehd、三叶木通A.trifoliata(Thumb.)Koidz、木通A.quinata Decne.果实中微量金属元素,检测出K,Ca,Na,Mg,Fe,Zn,Mn,Cu等8种元素含量。3种植物果实中K,Ca,Mg含量较高(＞0．1000mg/g),其中K元素远高于其他元素,Na,Cu含量较低(＜0．0100mg/g)。Fe,Zn,Mn的含量处于中等水平。白木通果实中K,Me,Zn,Mn 4种矿质元素高于三叶木通和木通。木通果实中Ca,Fe两种元素稍高于白木通、三叶木通。Na,Cu两种微量元素在3种果实中含量基本相拟。     

红花对土壤矿质元素的吸收和积累

采用电感耦合等离子体原子发射光谱法(ICP-AES)检测红花不同部位和时期以及栽培土壤中K、Ca、Na、Mg、Fe、Cu、Zn、Mn、Cr、Cd、Pb、Ba、Ni和Al元素的含量。结果表明:红花各部位矿质元素含量差异明显。在红花各不同部位中K、Fe、Zn元素在幼苗中含量最高,Ca、Mg元素在成熟叶中含量最高,Cu元素在种子中含量最高;而K和Ca元素在种子中含量最低,Mg、Fe、Cu和Zn元素分别在花、茎、成熟叶和茎中含量最低。红花的幼苗和花对K元素吸收积累明显,幼苗和种子对Cu元素吸收积累明显,Ca元素在成熟叶中积累较多,相应元素含量远比土壤中相应的元素含量高。红花对土壤不同矿质元素的吸收利用差异较大,在长期栽培红花的土壤中应注意对吸收利用多的元素结合施肥进行补充。     

浙江雪胆几种金属元素分布及其与土壤养分之间的关系

对浙江雪胆各器官主要金属元素分布及其与土壤养分之间的关系进行了研究,结果表明,1)浙江雪胆原生土壤中Fe元素的含量最高,其次是K元素,Mn和Zn含量较低;2)植物的各器官中,均以K元素含量最高,其次是Ca和Mg,微量元素Fe、Mn和Zn含量均相对较低;3)Fe、Mn和Zn 3种微量元素均以根中含量为最高,Mg和Ca元素均以块茎中较高,K则以叶中最高;4)同一器官元素分布均呈正相关,而不同器官之间的元素分布整体上呈负相关;5)根中Mg、K和Ca均与土壤元素含量整体上呈负相关,块茎中元素均与土壤元素含量均呈正相关,叶中除Fe元素外,其他元素均与土壤元素含量均呈负相关;6)各器官大量元素的富集系数较高。     

高山森林林窗和生长基质对苔藓植物氮和磷含量的影响

苔藓在森林生态系统养分富集和循环方面有重要作用,苔藓植物在氮磷循环中的作用可能受到森林更新和生长基质的影响.为理解苔藓在森林生态系统养分循环中的作用,研究了高山森林不同位置(林窗中心、林窗边缘、林下)和不同生长基质(活立木、倒木、枯立木、大枯枝、根桩、地表)上的苔藓植物氮磷含量.结果表明:地表苔藓氮含量(3.12 mg·g^-1)显著低于其他生长基质上的苔藓,尽管枯立木附生苔藓氮含量高达17.41 mg·g^-1,但倒木、大枯枝、枯立木和活立木苔藓氮含量差异不显著;最高(1.09 mg·g^-1)和最低(0.61 mg·g^-1)的磷含量分别出现在森林地表和枯立木的苔藓,且森林地表的苔藓磷含量显著高于其他生长基质上的苔藓,但倒木、大枯枝、根桩和活立木上的苔藓磷含量差异不显著.林窗位置显著影响了倒木和大枯枝上的苔藓氮、磷含量,林窗内倒木和大枯枝上的苔藓氮、磷含量显著高于林窗边缘.粗木质残体的类型、腐烂等级对苔藓氮、磷含量的影响存在差异,两者交互作用的影响显著;第Ⅴ腐烂等级倒木上的苔藓氮含量显著高于其他腐烂等级;第Ⅲ腐烂等级大枯枝上的苔藓氮含量显著高于其他腐烂等级;第Ⅱ腐烂等级倒木上的苔藓磷含量显著高于其他腐烂等级;第Ⅳ腐烂等级枯立木上的苔藓磷含量显著高于其他腐烂等级.可见,森林林窗更新和粗木质残体腐解过程会影响苔藓植物的氮、磷含量,同时影响森林生态系统的养分循环过程.     

川西亚高山森林林窗不同时期土壤转化酶和脲酶活性的特征

为了解川西亚高山森林林窗对不同时期土壤生态过程的影响,于2012年6月—2013年5月期间,根据温度动态过程,对比研究了生长季节(土壤完全融化期、生长季节前期和生长季节后期)与非生长季节(冻结初期、深冻期和融化期)川西亚高山粗枝云杉(Picea asperata)人工林林窗中心、林缘和林下土壤有机层和矿质土壤层转化酶和脲酶活性变化过程。结果表明:林窗不同区域中,土壤有机层转化酶活性均高于矿质土壤层;在生长季节,土壤有机层和矿质土转化酶活性表现为:林窗中心林下林缘,而脲酶活性表现为:林窗中心林缘林下。冻结初期和深冻期林窗中心土壤转化酶活性均高于林缘和林下,而在融化期林下转化酶活性高于林窗中心和林缘;冻结初期和融化期林下土壤脲酶活性显著高于林窗中心和林缘,而在深冻期林窗不同区域土壤脲酶活性没有显著差异。林窗不同区域在不同时期对土壤转化酶和脲酶活性的响应有着深刻影响。     

江苏东山山地枇杷果实品质与果园土壤、叶片和果实矿质元素的关系

以江苏省苏州吴中区山地种植的24个枇杷果园的‘白玉’枇杷为研究对象,采用典型相关分析法研究土壤、叶片和果实矿质元素间及其与果实品质指标的相关性,应用多元线性回归分析法筛选影响枇杷果实品质的土壤、叶片和果实的主要矿质元素和影响叶片矿质元素的主要土壤矿质养分因子,为改善枇杷果实品质的果园营养管理技术提供理论参考依据。结果表明:(1)枇杷果实品质指标在不同果园间存在较大差异。(2)枇杷果实品质主要受其叶片和果实矿质元素含量影响,其中:枇杷单果质量与叶片中N含量呈显著正相关,与果实中N含量呈显著负相关;可溶性固形物含量与叶片中N和Mg元素含量呈极显著正相关,与果实中P、Mn元素含量呈极显著正相关,与果实中Ca、Mg元素含量呈极显著负相关;可滴定酸含量与叶片中N和Zn元素含量呈显著负相关,与果实中N、Mn元素含量呈显著负相关,与果实中Ca元素含量呈显著正相关。(3)果实品质指标与土壤矿质养分含量的相关性较弱,土壤矿质养分主要通过影响叶片矿质元素含量,进而间接影响果实品质,其中土壤中P、K、Ca、Mn、Cu元素对叶片中矿质元素含量影响较大。研究认为,提高土壤中P、K、Zn含量并减少土壤Ca含量是东山山地枇杷果园土壤管理的关键技术途径;提高叶片中N含量以及果实中N、P、Mn含量和减少果实中Ca、Mg含量是改善东山山地枇杷果实品质的关键措施。     

珍稀濒危植物矮牡丹体内矿质元素的研究

采用原子吸收分光光度法测定了矮牡丹体内的10种矿质元素,即K、Mg、Mn、Fe、Ni、Zn、Cu、Cd、Cr、Pb。分析了矿质元素在矮牡丹体内的分布规律及矮牡丹对各种元素的富集能力。结果表明:在不同器官中的矿质元素含量有显著差异, K、Mg、Mn、Ni、Cd、Cr、Pb以叶中为高, Fe、Zn、Cu分别以根、茎、叶柄中含量最高;大多数元素在叶柄中含量最低。矮牡丹对K、Mg、Mn、Fe、Zn有较强的吸收富集能力,一般叶的富集系数较其它器官为高。元素间相关分析表明:Zn、Cd、Cr、Pb、Mn、Fe、Ni、Cu之间有显著的相关性, K、Mg之间的相关性显著。此外,土壤与植物体内元素含量表现出显著的相关性。     

微波消解-FAAS法分析并比较旱芹(Apium graveolens L.)不同部位八种金属元素的含量

采用微波消解法处理旱芹根、茎、叶,并用火焰原子吸收法测定其中的Na、K、Ca、Mg、Fe、Mn、Zn、Cu 8种金属元素的含量。结果表明:旱芹中富含人体必需的Na、K、Mg、Fe、Ca等元素,各元素在不同部位含量有一定差异。Fe元素在旱芹根中含量为883.57μg.g-1,明显高于茎和叶;Ca、Zn和Mn元素在旱芹叶中的含量分别为11 103.74,214.04,88.07μg.g-1,明显高于茎和根;K、Na和Mg元素在旱芹茎中的含量高于根和叶中,Cu元素含量在各部位差异不大。方法的加标回收率为96.8%～105.8%,相对标准偏差(RSD)≤3.36%。     

Element concentrations in boreal,coniferous forest humus layers in relation to moss chemistry and soil factors

Concentrations of 15 elements (Al, Ca, Cd, Cr, Cu, Fe, K, Mg, Mn, Na, Ni, P, Pb, S and Zn) in the current annual growth increments of the ectohydric feather moss, Hylocomium splendens, were compared with those in the humus layer (Of+Oh) of coniferous forests at 353 sites throughout Finland. Moss concentrations in the moss increments were considered measures of atmospheric deposition of these elements. Concentrations in both moss and humus layer samples were negatively correlated with latitude, except Mn (moss) and Cr and Ni (humus layer), indicating a direct effect of deposition. Spearman correlations between concentrations in moss and humus layer samples were significant (P<0.05) for all elements; that for Pb concentrations was the highest (r_s=0.60) while those for the other elements were ≤0.48. Using thickness and organic matter content of the humus layer, clay content of the mineral soil (5–20 cm layer) and the concentration in the moss explained between 8% (Cd) and 44% (Cr, Mg) of the variation in the concentrations in the humus layer samples. It was concluded that, for most elements, concentration in the humus layer are a poor indicator of current atmospheric deposition levels, at least in relatively unpolluted regions such as Finland.     

西藏色季拉山暗针叶林凋落物层化学性质研究

The storage and chemical properties of the forest litter in dark coniferous forest of Sejila Mountain were studied. The results showed that the existing storage was 5. 863t·hm^-2 and the annual litter fall was 0. 3205 t·hm^-2 It implied that the forest litter decomposed slowly and accumulated quickly, and the turnover of nutrient circles was slow. The contents of N, Ca, Na, and Mn nutrient elements in litter layer were in the order of un-decomposed layer (U layer) > semi-decomposed layer (S layer) > decomposed layer (D layer), those of K, Fe, and Mg were in the order of D layer > S layer > U layer, and P element content was in the order of U layer > D layer> S layer. The pool of elements was 78. 483 kg·hm^-2 N, 3. 843 kg·hm^-2P, 48. 205 kg·hm^-2 K, 23.115 kg·hm^-2 Ca, 13. 157 kg·hm^-2 Na, 30.554 kg·hm^-2 Fe, 2. 113 kg·hm^-2 Mn and 27. 513 kg·hm^-2 Mg. The turnover of forest litter was the total of nutrient release accumulation. K, Fe, and Mg were enriched, and N,Ca, Na, Mn, and P were released with the turnover rate in the order of N > Ca > Na > Mn >P.     

Nutrient cycling and foliar status in an urban pine forest in Athens, Greece

The nutrient cycling and foliar status for the elements Ca, Mg, K, N, P, S, Fe, Mn, Zn and Cu were investigated in an urban forest of Aleppo pine (Pinus halepensis) in 2004 in Athens, Greece in order to draw conclusions on the productivity status and health of the ecosystem. The fluxes of bulk and throughfall deposition were characterized by the high amounts of Ca, organic N and sulfate S. The magnitude of the sulfate S fluxes indicated a polluted atmosphere. The nutrient enrichment in throughfall was appreciable for ammonium N, P and Mn. The mineral soil formed the largest pool for all the elements followed by the forest floor, trunk wood and trunk bark. The understory vegetation consisting of annual plants proved important for storing N, P and K. Compared to current year needles of Aleppo pine in remote forests of Spain, the needles of the Aleppo pine trees in Athens had significantly higher concentrations of Ca, N, P and Cu and significantly lower concentrations of Mg and Zn. The soil had a high concentration of calcium carbonate and accordingly high pH values. When all inputs to the forest floor were taken into account, the mean residence time of nutrients in the forest floor followed the order Fe > Mn > Cu > Ca > Mg > P > Zn > N > K > S.     

Element concentrations in mosses and surface waters of western Canadian mires relative to precipitation chemistry and hydrology

Concentrations of N, P, S, Na, K, Mg, Ca, Mn, Fe, Cu, Cd, Zn, Pb, Al, and AIA (acid insoluble ash) m mosses (three Sphagnum species and Tomenthypnum nitens, all hummock species) from a variety of mires, both ombrotrophic and minerotrophic, in the coastal western and central parts of Canada are considered in relation to surface water pH and concentrations of Na⁺, K⁺, Mg²⁺, Ca²⁺, Cl⁻, and SO₄^2- Distinct west-east concentration gradients were present for most elements in both mosses and water, but there were correlations between surface water and moss concentrations only for Ca and Mg
On ombrotrophic sites and sites characterized by poor fen vegetation, wet deposition is the main source of elements in the surface water On rich fen sites, additional Ca and Mg from surrounding soils change the elemental proportions We conclude that hydrochemically the limit between poor and rich fen sites is more decisive than between bog and fen The increase in Ca may give brown mosses a competitive advantage over Sphagnum
Moss concentrations of Na and Mg are the only ones decreasing inland The constancy or inland increase of moss elemental concentrations may depend on either an increasing atmospheric supply (e g Pb), differences in moss growth rates (especially N, P, and K) or site conditions related to the water regime (e g Fe and Al)     

Mineral Elements in Root of Wild Saposhnikovia divaricata and Its Rhizosphere Soil

Mineral elements are important components of medicinal herbs, and their concentrations are affected by many factors. In this study, Ca, Mg, Na, K, Fe, Mn, Cu, and Zn concentrations in wild Saposhnikovia divaricata and its rhizosphere soil collected from seven locations at two different times in China were measured, and influences of rhizosphere soil on those minerals in plant were evaluated. The results showed that mean concentrations of eight minerals in plant samples decreased in the order: Ca > Mg > Na > K > Fe > Zn > Mn > Cu, and those in the soil samples followed the following order: Na > Fe > Ca > K > Mg > Mn > Zn > Cu. Mean concentrations of Ca, Na, Mg, and K in plants were higher than those in soils, while higher mean concentrations of the other four minerals were found in soils. It was found that there was a positive correlation of Mg, Na, and Cu concentrations in the plant with those in the soil respectively, but a negative correlation of Mn concentration in plant with that in the soil. Except Ca, K, and Mn, the other five minerals in plant were all directly affected by one or more chemical compositions of soil. The results also indicate that pH value and concentrations of total nitrogen, Mg, Mn, and Cu in soil had significant correlations with multimineral elements in plant. In a word, mineral elements uptake of S. divaricata can be changed by adjusting the soil fertility levels to meet the need of appropriate quality control of S. divaricata.     

Leaf-litter and changing nutrient levels in a seasonally dry tropical hardwood forest,Belize, C.A.

Summary Total above ground plant biomass in a 45 year old seasonally dry tropical hardwood forest was estimated to be approximately 56,000 kg/ha oven dry weight. Nutrients immobilized in the standing vegetation were: N, 203 kg/ha; P, 24 kg/ha; K, 234 kg/ha; Ca, 195 kg/ha; Mg, 47 kg/ha; Na, 9 kg/ha; Mn, 1 kg/ha; Cu, 0.5 kg/ha; Zn, 3 kg/ha; Fe, 4 kg/ha. Total nutrients returned each year through the litter were: N, 156 kg/ha; P, 9 kg/ha; K, 59 kg/ha; Ca, 373 kg/ha; Mg, 32 kg/ha; Na, 5 kg/ha; Mn, 1 kg/ha; Al, 21 kg/ha; Zn, 0.3 kg/ha; Fe, 9 kg/ha. Half of the nutrients immobilized in the standing vegetation were found in the leaves and are returned annually to the soil. Although litter fall is interrupted during the year, the mean nutrient content of the litter was high –5.2%.A decomposition rate of 0.48 percent per day was considered high for a seasonally dry tropical hardwood forest. Fluctuations in soil nutrient levels showed a sharp increase at the start of the rainy season. Later during the dry season nutrient levels decreased to concentrations similar to what they were just prior to the rainy season. Soil organic matter levels were very high –20% in the top 12 cm.     

中国南方生长于不同基质的天然林植物叶片元素含量特征比较

对比中国南方两个热带喀斯特森林、一个热带红树林和来自文献的一个亚热带常绿阔叶林植物叶片元素含量和计量特点。结果表明,受碳酸盐岩的影响,西双版纳和弄岗喀斯特森林植物叶片普遍富含Ca、Mg元素,因岩性差异,含有一定白云岩的弄岗地区的植物富集更多的Mg。西双版纳喀斯特森林存在K、Fe、Na、Zn元素的缺乏状况;由于白云岩矿物成分的特殊性和缓慢的风化速度,弄岗喀斯特植物有更高的叶片K、Zn、S含量。红树林植物富集P、Ca、Mg、Na、S元素,海水环境中大量的离子进入土壤被植物吸收利用,提高了红树的养分含量,并且在高盐环境下Na在叶片中大量富集。但是,红树植物表现缺乏Fe、Si、Zn。亚热带常绿阔叶林植物受酸性土影响大,Mn元素大量富集,P与Na的含量缺乏,并且相比其他生境,常绿阔叶林的N、P、Ca、Mg含量较低。西双版纳和弄岗的喀斯特森林植物叶片N/P比分别为14.27和18.26,说明前者受到N、P的共同限制,后者主要为P限制;红树植物N/P比为13.12,受N限制;常绿阔叶林植物本身严重缺P,N/P比为26.27,表现出明显的P限制。所研究的不同基质上的植物,叶片N与P元素之间均呈显著正相关,这种稳定的协同关系是植物适应环境的普遍规律。Ca与Mg两个二价阳离子元素在喀斯特森林和常绿阔叶林中为协同关系,而在红树林中则不存在相关性,分析表明Na盐胁迫下增加了Mg的吸收,改变了Ca、Mg的平衡关系。N与K元素在红树林和常绿阔叶林中为协同关系,而由于喀斯特环境中Ca、Mg协同影响了K的吸收,改变了N、K的协同关系。P与Zn在喀斯特森林和红树林中都表现出协同关系,这与两种元素在植物代谢过程中都参与了酶的合成有关。红树植物表现K和Mn的拮抗关系,而在喀斯特森林和常绿阔叶林中均未有相关性。S与P元素在弄岗喀斯特森林中表现出正相关,这种协同性可以帮助喀斯特植物缓解缺P的症状,而在高P的红树植物中没有相关性。研究结果对于森林生态系统的生物地球化学循环模拟和生态系统管理有重要参考意义。     

贵州喀斯特山区典型人工林土壤矿质元素特征

为了阐明群落水平上的土壤矿质元素特征,该研究以贵州喀斯特山区典型人工林为对象,以金属元素和非金属元素进行类型划分,探讨了土壤矿质元素含量特征及其相关性。结果表明:该区典型人工林土壤矿质元素含量存在较大差异,且同一元素在不同树种之间的变化幅度各异,锌、铬、铁、钛、铝、镁、镍、钴等的变化规律较为一致,钙、锶等的变化趋势较为相似,砷、硒、硅在桉树(Eucalyptus robusta)林、柏木(Cupressus funebris)林和枇杷(Eriobotrya japonica)林中的含量较高,硫、钠、氯等元素含量则相反;不同矿质元素随林分类型的变化规律不完全一致,表明植物根系对养分的提取和富集能力存在差异;矿质元素之间表现出一定程度的相关性,存在此消彼长的关系,不同矿质元素之间的相关关系各异,表现出增强或抑制效应,尤其以铁、钙等元素与其他元素的关系更为密切;矿质元素之间的互作效应及其计量平衡关系是分析元素特征的关键,是未来值得深入研究的科学问题。该研究结果有利于掌握养分元素积累特征与调控规律,对于该区域典型人工林土壤养分管理具有较强的理论和实践意义。     

Wood-ash recycling affects forest soil and tree fine-root chemistry and reverses soil acidification

Wood ash was applied to a forest ecosystem with the aim to recycle nutrients taken from the forest and to mitigate the negative effects of intensive harvesting. After two years, the application of 8,000 kg ha⁻¹ of wood ash increased soil exchangeable Ca and Mg. Similarly, an increase in Ca and Mg in the Norway spruce fine roots was recorded, leading to significant linear correlations between soil and root Ca and soil and root Mg. In contrast to these macronutrients, the micronutrients Fe and Zn and the toxic element Al decreased in the soil exchangeable fraction with the addition of wood ash, but not in the fine roots. Only Mn decreased in soil and in fine roots leading to a significant linear correlation between soil and root Mn. In soil, as well as in fine roots, strong positive correlations were found between the elements Ca and Mg and between Fe and Al. This indicates that the uptake of Mg resembles that of Ca and that of Al that of Fe. With the wood ash application, the pH increased from 3.2 to 4.8, the base saturation from 30% to 86%, the molar basic cations/Al ratio (BC/Al) of the soil solution from 1.5 to 5.5, and the molar Ca/Al ratio of the fine roots from 1.3 to 3.7. Overall, all below-ground indicators of soil acidification responded positively to the wood ash application within two years. Nitrate concentrations increased only slightly in the soil solution at a soil depth of 75–80 cm, and no signs of increased heavy metal concentrations in the soils or in the fine roots were apparent. This suggests that the recycling of wood ash could be an integral part of sustainable forest management because it closes the nutrient cycle and reverses soil acidification.