短柄五加濒危趋势和致濒因素的初步分析

研究了短柄五加种群致濒的因素和机制 .1)通过环境筛分析 ,认为短柄五加种群在 5～ 8a和 11～ 12a两个年龄阶段受到强烈的环境筛过滤作用 ,这两个阶段可能是濒危的关键阶段 .2 )通过对短柄五加种群生物量增长过程中关键因子的分析 ,确定了影响种群生物量的主导生境因子 ,主要是群落类型、群落郁闭度和坡度、坡向等 .影响种群增长的主导生境因子的脆弱性 ,增大了短柄五加种群濒危的趋势 .3)通过对短柄五加种子生态及生殖生态的初步分析 ,认为种群实生苗更新失败是短柄五加种群濒危的重要因素 .4)放牧、采挖和对次生落叶阔叶林的砍伐等人类活动 ,加快了短柄五加种群濒危的速度 .图 1表 3参 11     

南方红豆杉种子的化学成分分析

对南方红豆杉种子 (种仁 )的化学成分分析表明 :南方红豆杉干重 (DW)种子粗蛋白、粗脂肪、淀粉、可溶性糖的质量分数wDW分别为 9.92g (10 0g) -1,72 .86g (10 0g) -1,4 .15g (10 0g) -1,0 .38g (10 0g) -1;氨基酸的wDW为 9.10g (10 0g) -1,其中必需氨基酸占总氨基酸量的 2 8.0 5 % ;种子油脂肪酸组成以不饱和的油酸和亚油酸为主 ,其相对含量为 4 8.4 %和 4 2 .2 % ;种子元素质量分数分别为 :wDW(N) =15 87.2mg (10 0g) -1,wDW(P) =5 6 5 .4mg (10 0g) -1,wDW(K) =2 6 1.1mg(10 0g) -1,wDW(Ca) =18.4mg (10 0g) -1,wDW(Mg) =35 0 .5mg (10 0g) -1,其余微量元素含量由多到少依次为Zn >Fe>Na>Cu >Mn .表 4参 6     

Seed treatment and inhibition of plantpathology by chitosan

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The transfer of active ingredients of insecticides and fungicides from an orchard to beehives

This investigation was undertaken to determine whether active ingredients (AIs) of currently recommended plant protection products (PPPs) could be transferred to beehives from apple and pear trees. A field trial was carried out with apple trees of Ligol and Idared variety, and pear trees of Conference variety. For pest and diseases control of fungal origin, recommended PPPs were applied. Samples of flowers from the above-mentioned varieties of fruit trees, of bees, brood and honey from beehives located in their direct neighborhood were collected regularly and analyzed for the presence of lambda-cyhalothrin (an insecticide) and cyprodinil, captan, fluopyram, kresoxim-methyl, penthiopyrad and trifloxystrobin (fungicides). In samples of flowers of Ligol variety, fluopyram residues (on average 0.621 µg single flower^?1) were at the highest levels, whereas in samples of pear flowers of Conference variety, and in flowers of Idared variety, captan residues (on average, respectively, 0.705 and 165.7 µg single flower^?1). In samples of bees and honey, residues of five AIs were detected, and in brood six AIs, whereby in each case captan residues prevailed, respectively, up to 585.2, 51.52 and 126.5 µg kg^?1 bees and honey. In the honey, significantly larger residues of captan were found out than maximum residue level (MRL) for this AI – 103.04% MRL. In the case of any AI, the daily intake did not exceed 0.002% acceptable daily intake (ADI).     

Responses of Seed‐Dispersing Birds to Amount of Rainforest in the Landscape around Fragments

Habitat loss and fragmentation alter the composition of bird assemblages in rainforest. Because birds are major seed dispersers in rainforests, fragmentation‐induced changes to frugivorous bird assemblages are also likely to alter the ecological processes of seed dispersal and forest regeneration, but the specific nature of these changes is poorly understood. We assessed the influence of fragment size and landscape forest cover on the abundance, species composition, and functional properties of the avian seed disperser community in an extensively cleared, former rainforest landscape of subtropical Australia. Bird surveys of fixed time and area in 25 rainforest fragments (1–139 ha in size across a 1800 km² region) provided bird assemblage data which were coupled with prior knowledge of bird species’ particular roles in seed dispersal to give measurements of seven different attributes of the seed disperser assemblage. We used multimodel regression to assess how patch size and surrounding forest cover (within 200 m, 1000 m, and 5000 m radii) influenced variation in the abundance of individual bird species and of functional groups based on bird species’ responses to fragmentation and their roles in seed dispersal. Surrounding forest cover, specifically rainforest cover, generally had a greater effect on frugivorous bird assemblages than fragment size. Amount of rainforest cover within 200 m of fragments was the main factor positively associated with abundances of frugivorous birds that are both fragmentation sensitive and important seed dispersers. Our results suggest a high proportion of local rainforest cover is required for the persistence of seed‐dispersing birds and the maintenance of seed dispersal processes. Thus, even small rainforest fragments can function as important parts of habitat networks for seed‐dispersing birds, whether or not they are physically connected by vegetation. Respuestas de Aves Dispersoras de Semillas al Incremento de Selvas en el Paisaje Alrededor de Fragmentos     

建立优质种苗示范基地，加快发展海南椰子产业

通过对海南椰子生产现状的分析，本文指出了建立优质良种椰子种苗生产示范基地的必要性和重要性，并针对一些需要解决的问题，提出了加快海南椰子产业发展的建议。     

Application of natural oil in IPM of grapevine with special regard to predatory mites

Abstract

Oil products are widely used in orchards and on grapevine as pesticides, or adjuvants to pesticides. We aimed to get information on the efficacy of formulated rape seed oil against phytophagous mites in grapevine and its effect on predatory mites. Formulated rape seed oil (TELMION^R) from the Temmen GmbH, Germany was used in field trials at 0.5% and 1 %.

For phytophagous mites TELMION^R had an efficacy of 90,1% and 91,2% for 05% and for 1%, respectively. For Phytoseiidae there was no side effect at 0.5% and 1%. For Tydeiidae there was no side effect at 0.5% and a moderate toxicity (43.1%) at 1%. On the basis of our results TELMION^R seems to fit well into Integrated Pest Management or Organic Production in grapevine.     

土壤中芘、菲、萘、苯对小麦的生态毒性影响

采用生物培养和物理化学试验,研究了芘、菲、萘、苯对土壤中小麦的生态毒性.结果表明,芘对小麦根毒害的敏感区间浓度为0～300mg/kg;土壤中芘的50%小麦根伸长抑制率浓度为500mg/kg.PAHs的生态毒性与其溶解度和结构有关,且随着溶解度的增大和苯环数目的减少而增加.PAHs会降低土壤的土水势,土水势降低的程度随着PAHs溶解度的增大而增大.     

The persistence of insecticidal chemicals in soils treated with granular formulations of aldicarb and their uptake by potato plants

Abstract

Potatoes were grown in Plainfield sand and muck treated, in furrow, with aldicarb (Temik 15G, 3.36 kg Al/ha). .Soils were contained in 2 m^z field plots and had not been treated previously with pesticides. Soil, seed pieces, foliage and tubers were analyzed for the insecticide and its sulfoxide and sulfone metabolites during the 12 wk following planting. The disappearance of aldicarb from the soil was accompanied by partial conversion to the sulfoxide and sulfone. After increasing rapidly during the first 2 wk, the aldicarb concentration in the seed piece declined and a similar concentration of aldicarb sulfoxide accumulated which subsequently slowly disappeared. Aldicarb sulfoxide was the major insecticidal material in the new foliage. High initial concentrations, observed at 3–4 wk, declined by about 90% after 6 wk. Aldicarb sulfoxide residues of 2–4 ppm in the first new tubers at 6 wk declined by 90% by 12 wk. Potatoes were also grown under greenhouse conditions in Plainfield sand treated with Temik 10G at rates equivalent to 1.68, 3.36 and 6.72 kg Al/ha. Maximum aldicarb sulfoxide concentrations in soil, seed piece and foliage increased with application rate. The sulfoxide was much more persistent in the soil and foliage than in the field experiment indicating the importance of environmental factors to its behaviour in both soil and potato plants.     

The effect of multiple soil applications of disulfoton on enhanced microbial degradation in soil and subsequent uptake of insecticidal chemicals by potato plants

Abstract

Potatoes were grown during 1992 in 2 m² plots of loam which had received 1, 2 or 3 annual treatments of Di‐Syston 15G, equivalent to 3.36 kg AI/ha, in furrow at planting. The presence of enhanced degradative activity to the sulfoxide and sulfone metabolites of disulfoton in the soil treated in the previous two years was confirmed by laboratory tests prior to the 1992 treatments. Soil, seed potato and foliage from the three treatments were analyzed for disulfoton and its sulfoxide and sulfone metabolites for 12 wk following planting/treatment. Disulfoton was the major insecticidal component of the soil, a minor component of the seed piece and was not detected (<0.02 ppm) in potato foliage. Disulfoton concentrations in each of the three substrates sampled were similar for the three treatments. Disulfoton sulfoxide and sulfone were the major insecticidal components of the seed piece and foliage. Their maximum concentrations in 1st year soil, seed pieces and foliage were ca. 2x, 2x and 6x, respectively, those measured in the 2nd and 3rd year treatments. The results demonstrate that enhanced microbial degradation of relatively minor insecticidal compounds in the soil can profoundly affect insecticide levels in the plant when these compounds are the major insecticidal components accumulated. The broader implications for crop protection using soil‐applied systemic insecticides are discussed.