Comparison of European with West Asian and North African winter barleys in tolerance to boron toxicity

Three plastic-house experiments were conducted to compare the tolerance of European with West Asian and North African (WANA) winter barleys to boron (B) toxicity. Experiment I screened 24 winter barley entries with diverse origins. Experiment III tested 420 random accessions from seven European and seven WANA countries. Plants were screened in a soil mixed with boric acid (50 mg B/kg) and foliar B-toxicity symptom scores were recorded. Lower scores indicated higher B-toxicity tolerance. In Experiment II, five lines/varieties from each of the European and WANA groups were grown in pots with two soil B levels (0 and 25 mg B/kg). The West Asian landrace barleys had a lower mean B-toxicity symptom score than the European ones. The Syrian landrace variety normally grown in drier areas had a lower score than the Syrian landrace variety grown in wetter areas. Dry weights of the European and WANA groups were not different without adding B, but dry weight under 25 mg B/kg was lower for the European group than the WANA group. European accessions had a higher mean B-toxicity symptom score than the WANA accessions. Iranian and Afghan accessions had the lowest mean scores among countries. These results support the hypothesis that European winter barley varieties and accessions are less tolerant to B toxicity than those WANA accessions and varieties developed from local landraces. The lower B-toxicity tolerance could be a factor adversely affecting the performance of European winter barley varieties in the highlands of WANA. This revised version was published online in July 2006 with corrections to the Cover Date.     

钙盐诱导下土壤锰和铁的释放及其对胡椒的生物有效性

Releases of manganese and iron ions from an albic soil (Albic-Udic Luvisol), a yellow-red soil (Hap-Udic Ferrisol) and a yellow-brown soil (Arp-Udic Luvisol) induced by calcium salt addition and their bioavailability to pepper (Capsicum frutescens L.) were studied in a pot experiment. Addition of Ca(NO₃)₂ decreased soil pH and increased both exchangeable and DTPA (diethylenetriamine pentaacetic acid)-extractable Mn and Fe in soils. Meanwhile, total Mn accumulation in the shoots of Capsicum frutescens L. on the salt-treated soils increased significantly (P< 0.01) compared with the control, suggesting that salt addition to soil induced Mn toxicity in Capsicum frutescens L. Although exchangeable and DTPA-extractable Fe increased also in the salt-treated soils, Fe uptake by the shoots of Capsicum frutescens L. decreased. The effect of added salts in soils on dry matter weight of pepper varied with the soil characteristics, showing different buffer capacities of the soils for salt toxicity in an order of yellow-brown soil > albic soil > yellow-red soil. Fe/Mn ratio in shoots of Capsicum frutescens L. decreased with increasing salt addition for all the soils, which was ascribed to the antagonistic effect of Mn on Fe accumulation. The ratio of Fe/Mn in the tissue was a better indicator of the appearance of Mn toxicity symptoms than Mn concentration alone.     

长江三角洲地区城市污泥对蚯蚓的急性毒性效应

应用滤纸法和自然土壤法测定了长江三角洲地区城市污泥及其与青紫泥混合后对蚯蚓的急性致死效应及慢性毒性效应。结果表明:滤纸法测定的污泥对蚯蚓的毒性症状出现快且严重,不同污泥对蚯蚓的毒性大小差别较大,致死中浓度(LC50)相对应的污泥与水比值(Rsw-LC50)范围在0.0010～0.0242之间。在供试的城市污泥中,上海贮泥池污泥对蚯蚓的毒性最大,上海脱水污泥5对蚯蚓的毒性最小。自然土壤法测定的污泥与土壤作用后对蚯蚓的毒性结果为:所有处理蚯蚓死亡率均为0,各污泥处理对蚯蚓体重增长率的影响差别不大,个别污泥处理蚯蚓体重增长率比对照处理低,即对蚯蚓的体重有负增长影响。与滤纸法各处理相比,中毒症状较轻微,仅极个别中毒症状较明显。与污泥的水浸液相比,污泥与土壤作用后对蚯蚓的毒性大大降低。     

Effects of preemergence and postemergence herbicides on urea hydrolysis and nitrification of urea nitrogen in soil

The influence of 5 and 50 mg active ingredient kg^-1 soil of nine preemergence and nine postemergence herbicides on transformations of urea N in soil was studied in samples of two coarse-textured and two fine-textured soils incubated aerobically at 20°C. The effects of each herbicide on soil urea transformations was measured by determining the amounts of urea hydrolyzed and the amounts of NO _inf3 ^sup- and NO _inf2 ^sup- produced at various times after treatment with urea. Applied at the rate of 5 mg active ingredient kg^-1 soil, none of the herbicides retarded urea hydrolysis in the four soils used, but four of the postemergence herbicides (acifluorfen, diclofop methyl, fenoxaprop ethyl) retarded urea hydrolysis in the two coarse-textured soils. All the herbicides tested except siduron retarded nitrification in the two coarse-textured soils when applied at 50 mg of urea N active ingredient kg^-1 soil, and fenoxaprop ethyl and tridiphane markedly retarded nitrification of urea N in all four of the soils when applied at this rate. One-way analysis of variance and correlation analyses indicated that the inhibitory effects of the 18 herbicides tested on nitrification of urea N in soil increased with a decrease in the organic-matter content and an increase in the sand content of the soil. Present address: Department of Soil and Environmental Sciences, University of California, Riverside, CA 92521, USA     

Development of biomarkers inAporrectodea caliginosa andLumbricus rubellus for detecting exposure to benzo[a]pyrene

Objectives and Methods. The sensitivity of two biomarkers, the neutral red retention assay (NRRA) and cytochrome P450 were evaluated in the earthwormAporrectodea caliginosa for their potential to detect exposure to benzo[a]pyrene (BaP). Cytochrome P450 was also evaluated in the earthwormLumbricus rubellus, and measured using the substrate ethoxycoumarin. Optimal assay conditions (pH, and temperature) were determined, followed by exposure of earthworms to 20 mg/kg BaP (a typical concentration at contaminated sites in New Zealand). Ethoxycoumarin-O-dealkylase (ECOD) activity was measured after 7, 14, and 21 days exposure. The NRRA was evaluated in earthworms exposed to 0.2, 20, and 100 mg BaP/kg, and biomarker responses were compared with effects on body weight. Results and Discussion Benzo[a]pyrene failed to induce ECOD activity in either earthworm species, and therefore it is not useful as a biomarker of BaP exposure and was not evaluated further. In all cases, the NRRA was significantly affected in the absence of any effects on earthworm body weight, indicating that this assay can detect exposure to BaP at a range of concentrations comparable to those found at contaminated sites. The NRRA should be linked to reproductive endpoints, then it can be used as an early warning indicator of adverse effects. Establishing biomarker stability under environmental conditions is an important step in biomarker development. Therefore, the effects of soil type (sandy soil, silt loam, and a clay soil), moisture content (15–30%), and temperature (5–20°) on the NRRA were determined. In all cases, there was no effect on the NRRA, indicating that this assay is very stable under varying environmental conditions. Conclusion and Outlook In conclusion, cytochrome P450 activity does not appear to be a useful indicator of PAH exposure in eitherA. caliginosa or L.rubellus, and due to the inherently low activity, it is not suitable as a routine biomarker for detecting environmental contamination by these compounds. In contrast, the NRRA in the earthworm A.caliginosa is a promising indicator of PAH exposure at the concentrations likely to be found in contaminated sites in New Zealand, and therefore has potential for evaluating these contaminated sites. If the NRRA can be linked to ecologically important life-cycle endpoints, such as reproduction, then it could be used as an early warning indicator of adverse effects at contaminated sites, i.e., by measuring biomarker responses in earthworms from a ‘contaminated area’ and comparing these with earthworms from a matched control area.     

石灰处理对红壤中镉形态及其毒性的影响

The effect of liming 4 red soils developed from Quaternary red clay and red sandstone on the cadmium forms and its toxicity were investigated. Liming the acid red soils could greatly reduce Cd toxicity to plants because the soluble Cd and organic Cd in the soils decreased significantly while Cd bound to minerals/oxides and residual Cd increased markedly with increasing lime rates (pH).     

Expression of the Truncated vip3A Gene at the 3'-terminus from Bacillus thuringiensis in Escherichia coli

将苏云金芽孢杆菌(Bacillus thuringiensis)缺失C端154个氨基酸编码区的vip3A基因(vip3T)插入原核表达载体pQE30，构建了重组表达载体pQEvip3T，并转化大肠杆菌(Escherichia coli ) M15进行IPTG诱导表达，比较了完整的Vip3A蛋白和C端缺失的蛋白Vip3T的可溶性和杀虫活性。与Vip3A不同，融合蛋白Vip3T以不可溶的包含体形式存在，诱导表达的菌液中没有检测到可溶性Vip3T蛋白。生物测定结果表明，M15(pOTP)诱导表达的Vip3A蛋白对初孵斜纹夜蛾(Spodoptera litua)和甜菜夜蛾(S. exigua)幼虫具有较高的杀虫活性，其提纯的包含体无毒，但包含体的碱性裂解液却又恢复了对夜蛾科害虫的活性；M15(pQEvip3T)菌液、包含体及其碱性裂解液对这两种昆虫幼虫则完全无毒，说明在大肠杆菌中，Vip3A蛋白C端氨基酸可能对Vip3A蛋白的可溶性和杀虫活性具有重要的影响。     

Promotion of the seed germination and seedling growth of cabbage by root-colonizing fungi isolated from oat and Eucalyptus roots

(Jpn. J. Soil Sci.Plant Nutr., 77, 257–263, 2006)
The symptom of blighted leaves was observed for the melon plants grown on an isolated soil bed after steam sterilization (SS) in a greenhouse in Kochi Prefecture, Japan. To clarify the causes of this symptom, soil and plant analyses were conducted in the first experiment. Manganese concentrations in the leaves with the symptom were higher than 1,000 mg kg−1and exchangeable Mn in the soil was higher than 30 mg kg−1, which indicated the observed symptom was due to Mn excess. In the second experiment, formation of Mn oxide-dissolving substances after SS was examined for several organic amendments, because large amounts of palm chips had been supplied to the soil before SS in the first experiment. As a treatment similar to SS, palm chips, bark compost, and cattle feces manure were autoclaved. The water extracts were collected before and after the autoclave treatment and the Mn oxide-dissolving capacities of the extracts were evaluated. The Mn oxide-dissolving capacity of the water extracts after SS was remarkably higher than before SS, and the value was highest in palm chips, and followed by bark compost, and cattle feces manure. Fractionation and HPLC analysis of the water extracts after SS revealed that the main substance behind Mn oxide reduction in palm tips was arabinose and that in bark manure was malic acid. Further, Mn oxide-dissolving capacities of the water extracts were almost completely explained by the amounts of arabinose or malic acid found in these materials. From these results, it was considered that reducing substances such as arabinose were released by SS from the palm chips which had been applied in large quantity before SS and these reducing substances dissolved the soil Mn oxides and increased the amounts of available Mn, which led to the occurrence of Mn toxicity to the plants.     

The toxic mixing zone of neutral and acidic river water: Acute aluminium toxicity in brown trout (Salmo trutta L.)

Mixing of acid river water containing aluminium (pH 5.1, Al 345 g.l^–1) with neutral water of a lake (pH 7.0, Al 73 g.l^–1) resulted in water (pH 6.4, Al 245 g.l^–1) with a pH (6.4) and Al concentration (245 g.l^–1) expected to have low toxicity to fish on the basis of current Al toxicity models. However, under semi-field conditions the freshly mixed water (a few sec. after mixing) proved to be highly toxic to brown trout. The fish were exposed to the water at different places along a 30 m channel. At the beginning of the channel acid and neutral water were continuously mixed; the mixed water left the channel after 340 sec. The cells of the gills showed a highly increased rate of cell death by apoptosis and necrosis. Intercellular spaces were enlarged, and many leucocytes penetrated in these spaces. Mucus release was stimulated to depletion. Plasma chloride levels were hardly affected. There was a clear gradient in the deleterious effects on the fish along the channel. The fish at the beginning of the channel (about 12 sec. after mixing of the water), were severely affected, whereas the fish kept at the end of the channel (340 sec. after mixing) were only mildly affected. In the natural situation fish will relatively quickly pass through a mixing zone. In our study we therefore focused on the effects on fish after a 60 min exposure to a mixing zone (5 sec after mixing), with subsequent recovery in a region downstream of the confluence and in neutral water with low Al. The recovery in the downstream area (at the end of the channel, i.e. 5 min after mixing) was clearly hampered when compared to the recovery in neutral water with low aluminium. Thus, a short exposure to the toxic mixing zone followed by a stay in water downstream of this zone, as may occur in nature, is detrimental to migrating trout. We conclude that freshly mixed acid and neutral water contain toxic components during the first seconds to minutes after mixing, that can not be explained by current models on aluminium toxicity.