Pedogenesis of plinthite during early Pliocene in the Mediterranean environment: Case study of a buried paleosol at Podere Renieri,central Italy

A complex buried paleosol at Podere Renieri at Montalcino (central Italy) formed during a series of continental episodes within an interval of Pliocene marine sediments from about 4.1 to 4.8 My BP. The aim of this work was to document the kind of pedogenesis which occurred throughout this time and, in particular, the plinthite formation. Plinthite (soft and hard) is poor in organic carbon, neutral or subalkaline, dominated by illite, and enriched in iron and chromium. The main differences between soft and hard plinthite are attributed to soil structure, which is absent in hard plinthite, and to the abundance of iron depleted zones, which are much larger in soft plinthite. Variations in mineralogy, chemistry and genesis of soft and hard plinthite can be ascribed to the specific environment of plinthite formation, close to the Pliocene sea. Pedogenetic evidence indicates that plinthite evolved in a hot and humid paleoclimate, showing a progressive increase in seasonality, and that low-grade plinthite formation occurred in a time span of a few hundred thousand years. Soils with low-grade plinthite have agronomic value in their suitability for the production of high quality Brunello di Montalcino wine.     

Pedogenesis of plinthite during early Pliocene in the Mediterranean environment: Case study of a buried paleosol at Podere Renieri, central Italy

A complex buried paleosol at Podere Renieri at Montalcino (central Italy) formed during a series of continental episodes within an interval of Pliocene marine sediments from about 4.1 to 4.8 My BP. The aim of this work was to document the kind of pedogenesis which occurred throughout this time and, in particular, the plinthite formation. Plinthite (soft and hard) is poor in organic carbon, neutral or subalkaline, dominated by illite, and enriched in iron and chromium. The main differences between soft and hard plinthite are attributed to soil structure, which is absent in hard plinthite, and to the abundance of iron depleted zones, which are much larger in soft plinthite. Variations in mineralogy, chemistry and genesis of soft and hard plinthite can be ascribed to the specific environment of plinthite formation, close to the Pliocene sea. Pedogenetic evidence indicates that plinthite evolved in a hot and humid paleoclimate, showing a progressive increase in seasonality, and that low-grade plinthite formation occurred in a time span of a few hundred thousand years. Soils with low-grade plinthite have agronomic value in their suitability for the production of high quality Brunello di Montalcino wine.     

Pedogenesis of plinthite during early Pliocene in the Mediterranean environment: Case study of a buried paleosol at Podere Renieri,central Italy

A complex buried paleosol at Podere Renieri at Montalcino (central Italy) formed during a series of continental episodes within an interval of Pliocene marine sediments from about 4.1 to 4.8 My BP. The aim of this work was to document the kind of pedogenesis which occurred throughout this time and, in particular, the plinthite formation. Plinthite (soft and hard) is poor in organic carbon, neutral or subalkaline, dominated by illite, and enriched in iron and chromium. The main differences between soft and hard plinthite are attributed to soil structure, which is absent in hard plinthite, and to the abundance of iron depleted zones, which are much larger in soft plinthite. Variations in mineralogy, chemistry and genesis of soft and hard plinthite can be ascribed to the specific environment of plinthite formation, close to the Pliocene sea. Pedogenetic evidence indicates that plinthite evolved in a hot and humid paleoclimate, showing a progressive increase in seasonality, and that low-grade plinthite formation occurred in a time span of a few hundred thousand years. Soils with low-grade plinthite have agronomic value in their suitability for the production of high quality Brunello di Montalcino wine.     

Podzolization as a deferralitization process: a study of an Acrisol–Podzol sequence derived from Palaeozoic sandstones in the northern upper Amazon Basin

Morphological, geochemical and mineralogical studies were carried out in a representative soil catena of the low‐elevation plateaux of the upper Amazon Basin to interpret the steps and mechanisms involved in the podzolization of low‐activity clay soils. The soils are derived from Palaeozoic sandstones. They consist of Hydromorphic Podzols under tree savannah in the depressions of the plateaux and predominantly of Acrisols covered by evergreen forest elsewhere. Incipient podzolization in the uppermost Acrisols is related to the formation of organic‐rich A and Bhs horizons slightly depleted in fine‐size particles by both mechanical particle transfer and weathering. Weathering of secondary minerals by organic acids and formation of organo‐metallic complexes act simultaneously over short distances. Their vertical transfer is limited. Selective dissolution of aluminous goethite, then gibbsite and finally kaolinite favour the preferential cheluviation of first Fe and secondly Al. The relatively small amount of organo‐metallic complexes produced is related to the quartzitic parent materials, and the predominance of Al over Fe in the spodic horizons is due to the importance of gibbsite in these low‐activity clay soils. Morphologically well‐expressed podzols occur in strongly iron‐depleted topsoils of the depression. Mechanical transfer and weathering of gibbsite and kaolinite by organic acids is enhanced and leads to residual accumulation of sands. Organo‐metallic complexes are translocated in strongly permeable sandy horizons and impregnate at depth the macro‐voids of embedded soil and saprolite materials to form the spodic Bs and 2BCs horizons. Mechanical transfer of black particulate organic compounds devoid of metals has occurred later within the sandy horizons of the podzols. Their vertical transfer has formed well‐differentiated A and Bh horizons. Their lateral removal by groundwater favours the development of an albic E horizon. In an open and waterlogged environment, the general trend is therefore towards the removal of all the metals that have initially accumulated as a response to the ferralitization process and have temporarily been sequestrated in organic complexes in previous stages of soil podzolization.     

Transformation of haematite and Al-poor goethite to Al-rich goethite and associated yellowing in a ferralitic clay soil profile of the middle Amazon Basin (Manaus, Brazil)

The red and yellow colours of ferralitic soils in the tropics have for long intrigued pedologists. We have investigated the upward yellowing in a 10-m thick profile representative of the Ferralsols of the plateaux of the Manaus region of Brazil. We determined changes in the nature and crystal chemistry of their Fe oxides by optical and Mössbauer spectroscopy as well as Rietveld refinement of X-ray diffraction patterns. We attribute the upward yellowing of the soil to a progressive transformation of the Fe oxides at nearly invariant iron contents. Aluminium in contrast is strongly mobilized in the uppermost clay-depleted topsoil where there is preferential dissolution of kaolinite and crystallization of gibbsite. Haematite decreases from 35 to 10% of the Fe oxides from the bottom to the top of the profile and the particles become smaller (75–10 nm). Its Al for Fe-substitution remains almost unchanged (10–15 mol %). The average Al-substitution rate of goethite increases from 25 to 33 mol %, and its mean crystal diameter remains in the range 20–40 nm. The proportion of Al-rich goethite (33 mol %) increases at the expense of less Al-substituted Fe oxides (haematite and goethite). This conversion with restricted transfer of iron means that the amount of Al stored in Fe oxides gradually increases. Kaolinite, haematite and Al-poor goethite are thus witnesses of earlier stages of ferralitization of the soil. In contrast, Al-rich goethite and gibbsite initiate the alitization (or bauxitization) of the soil. They correspond to the last generation of soil minerals, which most likely reflects the present-day weathering conditions. The progressive replacement of kaolinite, haematite and Al-poor goethite by new generations of Al-rich goethite and gibbsite attests to greater activities of water and aluminium and smaller activity of aqueous silica in the topsoil than in the subsoil. We interpret this as a consequence of longer periods of wetting in the topsoil that could result from soil aging, more humid climate or both.     

不同开垦年限水稻土还原性物质含量及其分布

以辽宁省各地棕壤型、草甸土型水稻土为研究对象,探讨了不同开垦年限的棕壤型、草甸土型水稻土中还原性物质总量、活性还原性物质、络合态铁、水溶性亚铁、水溶性亚锰含量及其分布状况。结果表明,不同开垦年限供试水稻土随着开垦年限增加表层还原性物质总量、活性还原性物质、络合态铁、水溶性亚铁和水溶性亚锰含量明显增加,且均随土壤深度增加而减少,其积累主要集中在土壤上层。土壤络合态铁与还原性物质总量和活性还原性物质均呈极显著正相关,表层土壤有机质对铁、锰的络合减少了铁、锰元素向剖面下层的迁移数量。开垦10年以上,水稻土耕层中还原性物质就明显积累,直至60年,其积累量仍不断增加,因此生产上必须采取措施抑制水稻土中还原性物质的累积。     

Subsoil rhizosphere modification by chickpea under a dry topsoil: implications for phosphorus acquisition

Chickpea (Cicer arietinum L.) roots exude carboxylates. While chickpea commonly grows where the topsoil dries out during crop growth, the importance of carboxylate exudation by the roots and mobilization of soil P from below the dry topsoil has not been examined. The study investigates the response of carboxylate exudation and soil P mobilization by this crop to subsoil P fertilizer rate. In constructed soil columns in the glasshouse, the P levels (high, low, and nil P) were varied in the well‐watered subsoil (10–30 cm), while a low level of P in the dry topsoil (0–10 cm) was maintained. At flowering, rhizosphere carboxylates and rhizosphere soil from topsoil and subsoil roots were collected separately and analyzed. The concentration of total carboxylates per unit rhizosphere mass in the subsoil was nearly double that of the topsoil. Plants depleted sparingly soluble inorganic P (P_i), NaOH‐P_i, and HCl‐P_i, along with the labile P_i (water soluble and NaHCO₃‐Pi). The P depletion by plants was greater from the subsoil than the topsoil. The study concluded that depletion of sparingly soluble P from the chickpea rhizosphere in the subsoil was linked with the greater levels of carboxylates in the rhizosphere. These findings indicate that chickpea, with its deep rooting pattern, can increase its access to subsoil P when the topsoil dries out during crop growth by subsoil rhizosphere modification.     

Vertical distribution of soil properties under short‐rotation forestry in Northern Germany

Short‐rotation forestry (SRF) on arable soils has high potentials for biomass production and leads to long‐term no‐tillage management. In the present study, the vertical distributions of soil chemical and microbial properties after 15 y of SRF with willows and poplar (Salix and Populus spp.) in 3‐ and 6‐year rotations on an arable soil were measured and compared to a pertinent tilled arable site. Two transects at different positions in the relief (upper and lower slope; transect 1 and 2) were investigated. Short‐rotation forestry caused significant changes in the vertical distribution of all investigated soil properties (organic and microbial C, total and microbial N, soil enzyme activities), however, the dimension and location (horizons) of significant effects varied. The rotation periods affected the vertical distribution of the soil properties within the SRF significantly. In transect 1, SRF had higher organic‐C concentrations in the subsoil (Bv horizon), whereas in transect 2, the organic‐C concentrations were increased predominantly in the topsoil (Ah horizon). Sufficient plant supply of P and K in combination with decreased concentrations of these elements in the subsoil under SRF pointed to an effective nutrient mobilization and transfer from the deeper soil horizons even in the long term. In transect 1, the microbial‐C concentrations were higher in the B and C horizons and in transect 2 in the A horizons under SRF than under arable use. The activities of β‐glucosidases and acid phosphatases in the soil were predominantly lower under SRF than under arable use in the topsoil and subsoil. We conclude, that long‐term SRF on arable sites can contribute to increased C sequestration and changes in the vertical distribution of soil microbial biomass and soil enzyme activities in the topsoil and also in the subsoil.     

Field-scale study of the variability in pesticide biodegradation with soil depth and its relationship with soil characteristics

The extent of within-field spatial variability of pesticide degradation was characterised in topsoil and subsoil, using the compounds isoproturon, bentazone and mecoprop, which are major contaminants of groundwater and surface freshwater in Europe. Twenty topsoil samples from 0 to 15 cm depth and twenty subsoil samples from 50 to 60 cm depth were collected from a single agricultural field within a 160×90 grid. It was shown that degradation rates of all compounds declined with soil depth. Variability of pesticide degradation rates, pesticide sorption and formation of non-extractable pesticide residues was higher in subsoil relative to topsoil. Furthermore, in the subsoil, there was variation in large scale soil physicochemical composition, which did not occur in topsoil. The greater variability in pesticide degradation rates in subsoil relative to topsoil could be the result of a greater range of degradation kinetics, which could reflect greater spatial variability in the distribution and/or activities of pesticide metabolising communities.     

Lateritic and redoximorphic features in a faulted landscape near Manaus, Brazil

The soils and sediments of the uplands in the Manaus region are described and analysed along a representative cross‐section. There are two broad types of features, lateritic and redoximorphic. Their formation is linked to two main processes acting under contrasted hydrological regimes. The first process, acting under well‐drained conditions, is lateritization. It has transformed strongly weathered sediment into soil and led to depletion of silica (mainly quartz) as well as to relative accumulation of both kaolinite and iron oxides (haematite and goethite). Crystallographic changes observed in the latter have resulted from alternating dissolution and crystallization cycles without significant transfer of iron and alumina. However, in the uppermost soil, dissolution of kaolinite has prevailed over crystallization, leading to depletion of clay and the formation of tiny crystals of gibbsite disseminated throughout the groundmass. The second process results from the development of reducing conditions in groundwater giving redoximorphic features in lateritic soils and sediments. In the sediments, iron has been depleted by regional aquifers to form a pallid zone. In the soil, large amounts of iron and minor amounts of alumina, mainly from aluminous goethite, have been mobilized at first in small patches, which with further mobilization and vertical transfer of these elements have increased in size and have led to the formation of bleached horizons over thin iron pans. Iron has crystallized predominantly as haematite in the iron pans and alumina as large crystals of gibbsite in soil voids. Formation of impervious iron pans holds up fluctuating perched groundwater in the overlying horizons depending on rainfall events. Neotectonic events (formation of uplifted blocks and small grabens) have markedly altered the hydrological regimes. In the uplifted blocks, the soil has been deeply truncated and iron loss has been checked in the uppermost sediment. By contrast, mobilization of iron has been initiated at various places in the soil of the small grabens. In this way tectonic events have checked mobilization of iron in sediments but activated it in soils, leaving spectacular fingerprints on the landscape.     

Distribution and fractionation of heavy metals in pairs of arable and afforested soils in Denmark

Afforestation of sandy arable soils in northern Europe is likely to lead to an increase in the soil's acidity and changes in the behaviour of the organic matter, and this might affect the ability of the soil to retain heavy metals. It is important to assess the impact of such a change in the land use on the solubility of the heavy metals and to assess the risk of leaching to surface‐ and groundwater and the possible entrapment of heavy metals in the tree canopy. The impact of afforestation was assessed by excavating soil profiles in adjacent 34‐year‐old Norway spruce stands and arable plots at four different sites. We found that after 34 years the pH had decreased and cations were depleted in the topsoil under forest. The aqua regia‐extractable heavy metals were determined, and the heavy metal binding within the soil was assessed using a modified version of the BCR (Community Bureau of Reference) sequential extraction procedure. Higher contents of heavy metal were found in the arable plots in the loamy sand soils. Cadmium was found only in the most mobile fractions. The content of Pb in the subsoil was strongly correlated with the clay content, but not in the topsoil, which suggested that Pb had been added to the topsoil. We found strong correlations between the clay content and the Cu, Ni and Zn in the residual fraction, leading us to conclude that much of the Cu, Ni and Zn is of geological origin. No significant differences in the heavy metal fractionation between forest and arable soil were found, presumably because 34 years of different land use is not long enough to produce such differences.     

EXTRACTABLE SESQUIOXIDES IN SIX MEDITERRANEAN SOILS DEVELOPED ON BASALT AND SCORIA

Iron, Al, and Mn were extracted by oxalate and dithionite from two Brown Mediterranean Soils, two Red Mediterranean Soils, one Vertisol and one Gley soil, all derived from basalt or scoria in the sub-humid and humid Mediterranean regions of the Golan Heights. Ratios of oxalate: dithionite extracted iron (Fe_o:Fe_d) were low in all soils, indicating that the predominant form of free iron is crystalline. Fe_o accumulates in the argillic B horizons of the Mediterranean soils, while Fe_d accumulates in the surface horizons. A large part of the free iron oxide in the surface horizons of Mediterranean soils is associated with non-clay fractions. While manganese behaves in a manner somewhat similar to that of iron, no definite trends could be discerned in the vertical distribution of free aluminium. In the Vertisol, Fe_o and Mn_o accumulate in the subsoil. Fe_d and Mn_d increase slightly with soil depth. In the Gley soil, amorphous iron accumulates in the surface horizon, total free iron in the bottom horizon. Both amorphous and total free Mn had been depleted from the upper horizons of the Gley soil.     

Microbial biomass and respiration in soils derived from lignite ashes: a profile study

Microbial biomass C and soil respiration measurements were made in 17–20 yr old soils developed on sluiced and tipped coal‐combustion ashes. Topsoil (0–30 cm) and subsoil (30–100 cm) samples were collected from three soil profiles at two abandoned disposal sites located in the city area of Halle, Saxony‐Anhalt. Selected soil physical (bulk density and texture) and chemical (pH, organic C, total N, CEC, plant available K and P, and total Cd and Cu) properties were measured. pH values were significantly lower while organic C and total N contents and the C : N ratio were significantly higher in the topsoil than in the subsoil indicating the effects of substrate weathering and pedogenic C accumulation. Likewise, microbial biomass C, K₂SO₄‐extractable C, and soil respiration with median values of 786 μg biomass C g^–1, 262 μg K₂SO₄‐C g^–1, and 6.05 μg CO₂‐C g^–1 h^–1, respectively, were significantly higher in the topsoil than in the subsoil. However, no significant difference was observed in metabolic quotient between the topsoil and the subsoil. Metabolic quotient with median values of 5.98 and 8.54 mg CO₂‐C (g biomass C)^–1 h^–1 for the 0–30 cm and 30–100 cm depths, respectively, was higher than the data reported in the literature for arable and forest soils. Microbial biomass C correlated significantly with extractable C but no relationship was observed between it and total N, Cd, and Cu contents, as well as plant‐available K and P. We conclude that the presence of the remarkable concentration of extractable C in the weathered lignite ashes allowed the establishment of microbial populations with high biomass. The high metabolic quotients observed might be attributed to the heavy‐metal contamination and to the microbial communities specific to ash soils.     

Release of interlayer potassium in Norwegian grassland soils

Potassium (K) release from sources that are not initially exchangeable is attributed to depletion of interlayer K of micas and clay minerals or weathering of feldspars. The aim of the present study was to estimate the K release from interlayer K. Soil samples from 17 field experiments in ley on a range of mineral soils in Norway were used in the study. The change in K‐fixation capacity was used as an estimate of depletion of interlayer K. It was assumed that the increase in K‐fixation capacity during 3 yr of cropping was equivalent to the amount of K depleted from the interlayer positions. Mean K fixation increased in the majority of the soils during 3 yr of grass cropping both with and without K application. The increase in K fixation indicated that without K application, the K uptake from interlayer K amounted to 43%, 28%, and 26% of the K yield for clay soils, high‐K sandy soils, and low‐K sandy soils, respectively. Including K uptake from exchangeable K in the topsoil and from subsoil, the explained K uptake amounted to 79%, 69%, and 81% for the three groups of soil, respectively. Simple linear‐regression analyses showed that the change in K fixation during 3 yr of grass cropping was best explained by the percentage of clay in the soil.     

Review of modelling crop growth, movement of water and chemicals in relation to topsoil and subsoil compaction

Soil compaction influences crop growth, movement of water and chemicals in numerous ways. Mathematical modelling contributes to better understanding of the complex and variable effects. This paper reviews models for simulating topsoil and subsoil compaction effects. The need for including both topsoil and subsoil compaction results from still increasing compactive effect of vehicular pressure which penetrates more and more into the subsoil and which is very persistent. The models vary widely in their conceptual approach, degree of complexity, input parameters and output presentation. Mechanistic and deterministic models were most frequently used. To characterise soil compactness, the models use bulk density and/or penetration resistance and water content data. In most models root growth is predicted as a function of mechanical impedance and water status of soil and crop yield—from interactions of soil water and plant transpiration and assimilation. Models for predicting movement of water and chemicals are based on the Darcy/Richards one-dimensional flow equation. The effect of soil compaction is considered by changing hydraulic conductivity, water retention and root growth. The models available allow assessment of the effects of topsoil and subsoil compaction on crop yield, vertical root distribution, chemical movement and soil erosion. The performance of some models was improved by considering macro-porosity and strength discontinuity (spatial and temporal variability of material parameters). Scarcity of experimental data on the heterogeneity is a constraint in modelling the effects of soil compaction. Suitability of most models was determined under given site conditions. Few of the models (i.e. SIBIL and SIMWASER) were found to be satisfactory in modelling the effect of soil compaction on soil water dynamics and crop growth under different climate and soil conditions.     

Wasser- und Elementtransport in einem Stagnogley am Hang der Bärhalde (Schwarzwald,Deutschland)

Water and Element Movement in a Stagnogley on the Slope of the Bärhalde Range (Black Forest, Germany) The soil water balance of this stagnogley (planosolic humic gleysol) is dominated by the very humid and cool climate, by the indurated subsoil and the solid parent granite as well as by its position on the lower slope of the Bärhalde ridge. Inspite of the high saturated water conductivity the drainage is impeded causing permanent waterlogging (average watertable at 55 cm below surface). Lateral flow through the soil exceeds seepage by 150 times. Inspite of the high input by lateral flow from the higher podzol area most of the major elements show reasonable losses throughout the profile. Other elements have losses in the topsoil which are compensated in the subsoil by gain from the lateral flow (Al, Be, Si). Especially elements with a mobility independent from redoxpotential have been accumulated throughout the entire period of soil formation (Pb, Zn). Some other trace elements accumulate recently because of increasing immissions (Cd, Cu, Co). Over all elements lateral flow through the profile exceeds vertical transport by 30 to 400 times.     

The effect of pre‐industrial charcoal kilns on chemical properties of forest soil of Wallonia,Belgium

In Wallonia, Belgium, intensive in situ charcoal production that was linked closely to pre‐industrial smelting and steel‐making affected a large part of the forested area in the late eighteenth century. Charcoal kiln relics can be detected under forest as domes of about 10 m in diameter, with the topsoil greatly enriched with charcoal residues. We sampled 19 charcoal kiln sites and the adjacent reference soil by soil horizon on four different soil types (Arenosols, Luvisols, Cambisols and Podzols). Data were analysed with linear mixed models to assess the effect of the charcoal kiln site on soil properties in relation to depth and soil conditions. We also addressed the evolution of soil properties over time by a comparison of the soil characteristics at a currently active kiln site. The charcoal‐rich topsoil has a larger C:N ratio and cation exchange capacity (CEC) per unit of organic carbon than the reference soil. The largest CECs per unit of carbon were observed on soil with coarser textures. On acidic soil, the increase in base saturation in the subsoil reflects the past liming effect of ash produced by wood charring, whereas the topsoil is re‐acidified. The acidity of carbonate‐rich Cambisols, however, is not reduced. Regardless of soil type, the kiln topsoil is greatly depleted in exchangeable K⁺ and available P, which may be attributed to the small affinity of the exchange complex of charcoal for K⁺ and a decrease in P availability with time. Therefore, we recommend further research on the long‐term effects of biochar on the dynamics of plant nutrients.     

Microbial activity as a major factor in the mobilization of iron in the humid tropics

The relation between the biodegradation and mineralization of soil organic matter and the bacterial solubilization and mobilization of iron in soils of the humid tropics is not clear. We therefore studied how microbial activity mobilized iron in a typical swamp soil of the humid tropics using two complementary approaches. By analysing soil water we found that the swamps (20% of the catchment) are the major sites of mineral weathering. Bacteria caused the solubilization of ferrous iron, produced ammonium, released organic soluble compounds, and caused the disappearance of nitrate. The waterlogged soil of the swamp (Gleysol) degraded and mineralized organic matter, producing CO₂ and NH₄⁺, and the amount of that activity depended on the amount, availability and quality of the organic matter. The nature and biomass of autochthonous bacteria were also important. The solubilization of iron was detected in the upper horizons (L1, 0–30 cm; L2, 30–70 cm; L3, 70–100 cm), where both iron and organic matter are available. Highly significant correlations were found between mineralization of organic matter and iron reduction. Quantitatively, we found that 100 µg of organic C being mineralized could reduce and dissolve 38, 97 and 115 µg Fe²⁺ in the L1, L2 and L3 horizons, respectively, during 30 days. After 30 days, there was a marked change in the relation, suggesting that lack of iron limited reduction. The coupling of iron reduction to the carbon cycle (soil organic matter biodegradation) is significant.     

Soil pore system evaluated from gas measurements and CT images: A conceptual study using artificial,natural and 3D-printed soil cores

Combining digital imaging, physical models and laboratory measurements is a step further towards a better understanding of the complex relationships between the soil pore system and soil functions. Eight natural 100-cm³ soil cores were sampled in a cultivated Stagnic Luvisol from the topsoil and subsoil, which we assumed had contrasting pore systems. Artificial 100-cm³ cores were produced from plastic or from autoclaved aerated concrete (AAC). Eight vertical holes of each diameter (1.5 and 3 mm) were drilled for the plastic cylinder and for one of the two AAC cylinders. All natural and artificial cores were scanned in an X-ray CT scanner and printed in 3D. Effective air-filled porosity, true Darcian air permeability, apparent air permeability at a pressure gradient of 5 hPa and oxygen diffusion were measured on all cores. The active pore system characteristics differed between topsoil (sponge-like, network of macropores of similar size) and subsoil (dominated by large vertical macropores). Active soil pore characteristics measured on a simplified pore network, that is, from artificial and printed soil cores, supported the fundamental differences in air transport by convection and diffusion observed between top- and subsoil. The results confirm the suitability of using the conceptual model that partitions the pore system into arterial, marginal and remote pores to describe effects of soil structure on gas transport. This study showed the high potential of using 3D-printed soil cores to reconstruct the soil macropore network for a better understanding of soil pore functions.     

上海市某大型再开发场地土壤重金属污染特征、评价及来源分析

[目的]研究土壤中重金属污染与生态风险状况,为保障城市更新改造过程中土地的合理利用提供科学依据。[方法]以上海市某大型再开发利用场地为研究对象,采集了102个点位的表层(0-0.5 m)和下层(1.5-2.0 m)土壤样品,测定10种重金属(As,Be,Cu,Pb,Ni,TI,Zn,Cd,Cr和Hg)浓度,采用地累积指数、内梅罗指数和潜在生态风险指数进行土壤重金属污染和生态风险评价,并进一步利用多元统计分析方法揭示土壤中重金属的来源情况。[结果]①测试土壤中重金属均未超过《土壤环境质量建设用地土壤污染风险管控标准(试行)》(GB36600-2018)第二类用地风险筛选值,但6.9%,24.5%,25.5%,37.3%和63.7%的采样点土壤中As,Cu,Pb,Zn和Hg浓度超过土壤元素背景值,存在不同程度的累积现象。内梅罗指数评价结果表明研究区域土壤整体处于尚清洁到轻度污染状态,分别有11.8%和3.84%的表层区域与2.64%和0.63%的下层区域土壤呈中度污染和重度污染状态。②表层土壤综合潜在生态风险指数均值为89.91,处于中等风险水平,Hg为研究区域主要的生态风险因子。③土壤中Ni,Cr,Be和TI浓度主要受成土母质风化作用的自然源控制,Pb,Zn,Cu,As和Hg主要受交通运输源和历史农业活动源的影响,其中自然源对表层土壤中的As和下层土壤中Cu也有相当比例的贡献,而表层土壤中Hg更多受到除交通运输源以外的其他人类活动源影响。[结论]后续土地利用过程应注重Hg的生态风险管控,并提高对外来交通源引起的重金属累积效应的关注。