A survey of antennal responses by five species of coniferophagous bark beetles (Coleoptera: Scolytidae) to bark volatiles of six species of angiosperm trees

Summary. Using Porapak Q traps, we collected the bark volatiles of six angiosperm trees native to British Columbia: black cottonwood, Populus trichocarpa Torr. & A. Gray (Salicaceae), trembling aspen, P. tremuloides Michx. (Salicaceae), paper birch, Betula papyrifera Marsh. (Betulaceae), bigleaf maple, Acer macrophyllum Pursh (Aceraceae), red alder, Alnus rubra Bong. (Betulaceae), and Sitka alder, A. viridis ssp. sinuata (Regel) á. L?ve & D. L?ve (Betulaceae). Utilising coupled gas chromatographic-electroantennographic detection analysis, the captured volatiles were assayed for antennal responses in five species of coniferophagous bark beetles (Coleoptera: Scolytidae), sympatric with most or all of the angiosperm trees: the Douglas-fir beetle, Dendroctonus pseudotsugae Hopkins, the mountain pine beetle, D. ponderosae Hopkins, the spruce beetle, D. rufipennis (Kirby), the western balsam bark beetle, Dryocoetes confusus Swaine, and the pine engraver, Ips pini (Say). The identities of 25 antennally-active compounds were determined by coupled gas chromatographic-mass spectroscopic analysis, and co-chromatographic comparisons with authentic chemicals. The compounds identified were: hexanal, (E)-2-hexenal, (Z)-3-hexen-1-ol, 1-hexanol, heptanal, α-pinene, frontalin, benzaldehyde, β-pinene, 2-hydroxycyclohexanone, 3-carene, limonene, β-phellandrene, benzyl alcohol, (E)-ocimene, salicylaldehyde, conophthorin, guaiacol, nonanal, methyl salicylate, 4-allylanisole, decanal, thymol methyl ether, (E)-nerolidol, and dendrolasin. A number of these compounds are known semiochemicals that are active in the behaviour of other organisms, including bark beetles, suggesting a high degree of semiochemical parsimony. Antennally-active compounds ranged from seven in A. viridis to 17 in P. trichocarpa. The fewest number of compounds (9) were detected by I. pini and the largest number (24) were detected by D. pseudotsugae. Six compounds excited the antennae of all five species of bark beetles. The large number of antennally-active compounds detected in common by numerous bark beetles and present in common in numerous nonhost trees supports the hypothesis of olfaction-based recognition and avoidance of nonhost angiosperm trees during the process of host selection by coniferophagous bark beetles. Received 13 December 1999; accepted 14 March 2000     

微孔曝气与覆盖对城市重污染河道底泥磷形态分布及释放过程的影响

采用自行研发的泥-水界面微孔曝气系统,开展了底泥表面曝气和覆盖对城市重污染河道底泥磷释放及形态分布规律的影响研究.结果表明,微孔曝气能够有效提高上覆水的溶解氧(DO)和沉积物的氧化还原电位(Eh),能够将泥-水界面Eh维持在-100 m V左右,DO提高到6 mg·L-1以上.与对照比较,原位覆盖处理的上覆水DO和Eh有一定提高,但仍明显低于微孔曝气处理.与对照相比较,微孔曝气处理均有效降低上覆水中总磷(TP)和溶解性正磷酸盐(PO3-4)的含量.试验结束时,微孔曝气(A)和微孔曝气+原位覆盖处理(A+C)上覆水中TP含量由初始的0.201 mg·L-1分别降至0.062 mg·L-1和0.050 mg·L-1;上覆水中PO3-4含量由0.086 mg·L-1和0.078 mg·L-1分别降至0.026 mg·L-1和0.023 mg·L-1.与对照相比,微孔曝气处理明显降低了底泥间隙水中TP的浓度,在整个培养期间,其TP含量平均下降38.8%(A)和47.9%(A+C).底泥原位覆盖处理对抑制泥-水界面磷释放能力要弱于微孔曝气处理,而且在试验后期(50 d),上覆水中TP和PO3-4的含量均有所反弹.不管有无覆盖,泥-水界面微孔曝气处理均显著改变了表层底泥磷形态分布特征,显著降低了底泥中铁铝结合态磷(Fe/Al-P)组分比例,而钙结合态磷(Ca-P)含量比例却出现明显增加.单一的表面覆盖处理对底泥磷形态分布特征没有显著影响(P0.05).研究表明,与单一的处理效果相比较,泥-水界面纳米微孔曝气处理,并结合底泥原位覆盖,更有利于抑制城市重污染河道泥-水界面中磷的释放风险.     

淹水对酸性红壤磷吸附解吸特性的影响——以江西省旱地红壤和水稻土为例

采用室内培养法研究了淹水对2种酸性红壤（旱地红壤、水稻土）磷吸附解吸特性及草酸可提取态P的影响。淹水培养实验中,2种土壤分别淹水0（对照）,1、2、3、4、8周,淹水培养结束后进行P吸附解吸实验,解吸实验结束后测定土样中草酸可提取态P。结果表明：与氧化状态相比,淹水后旱地红壤P吸附量减少,水稻土淹水1、2、3周P吸附量高于氧化状态,继续淹水4和8周后P吸附量减少。淹水前后旱地红壤P吸附量均大于水稻土。用简单Langmuir方程拟合P等温吸附曲线,除淹水4周外,P最大缓冲容量（MBC）随淹水时间延长而降低。结合能常数（K）淹水前后的变化规律性差。2种土壤P解吸量随加入P量增加而增加。氧化、还原状态下,2种土壤酸性草酸铵可提取P均远远大于CaCl2解吸P,虽然水稻土吸附P量低于旱地红壤,但P解吸量无论是CaCl2解吸P还是酸性草酸铵可提取P均大于旱地红壤,主要原因在于水稻土全P及速效P含量大于旱地红壤。淹水后草酸可提取态P增加,吸附P的释放和被新近形成的铁氧化物再吸附是淹水后草酸可提取态P增加的主要原因。     

Phytoremediation of polyaromatic hydrocarbons, anilines and phenols

Phytoremediation technologies based on the combined action of plants and the microbial communities that they support within the rhizosphere hold promise in the remediation of land and waterways contaminated with hydrocarbons but they have not yet been adopted in large-scale remediation strategies. In this review plant and microbial degradative capacities, viewed as a continuum, have been dissected in order to identify where bottle-necks and limitations exist. Phenols, anilines and polyaromatic hydrocarbons (PAHs) were selected as the target classes of molecule for consideration, in part because of their common patterns of distribution, but also because of the urgent need to develop techniques to overcome their toxicity to human health. Depending on the chemical and physical properties of the pollutant, the emerging picture suggests that plants will draw pollutants including PAHs into the plant rhizosphere to varying extents via the transpiration stream. Mycorrhizosphere-bacteria and -fungi may play a crucial role in establishing plants in degraded ecosystems. Within the rhizosphere, microbial degradative activities prevail in order to extract energy and carbon skeletons from the pollutants for microbial cell growth. There has been little systematic analysis of the changing dynamics of pollutant degradation within the rhizosphere; however, the importance of plants in supplying oxygen and nutrients to the rhizosphere via fine roots, and of the beneficial effect of microorganisms on plant root growth is stressed. In addition to their role in supporting rhizospheric degradative activities, plants may possess a limited capacity to transport some of the more mobile pollutants into roots and shoots via fine roots. In those situations where uptake does occur (i.e. only limited microbial activity in the rhizosphere) there is good evidence that the pollutant may be metabolised. However, plant uptake is frequently associated with the inhibition of plant growth and an increasing tendency to oxidant stress. Pollutant tolerance seems to correlate with the ability to deposit large quantities of pollutant metabolites in the 'bound' residue fraction of plant cell walls compared to the vacuole. In this regard, particular attention is paid to the activities of peroxidases, laccases, cytochromes P450, glucosyltransferases and ABC transporters. However, despite the seemingly large diversity of these proteins, direct proof of their participation in the metabolism of industrial aromatic pollutants is surprisingly scarce and little is known about their control in the overall metabolic scheme. Little is known about the bioavailability of bound metabolites; however, there may be a need to prevent their movement into wildlife food chains. In this regard, the application to harvested plants of composting techniques based on the degradative capacity of white-rot fungi merits attention.     

应用AERMOD计算卫生防护距离方法探讨

针对目前环评工作中计算确定工业企业卫生防护距离几种常见方法的不足和局限性,本文提出应用美国环保局推出的第二代法规模式AERMOD模型计算卫生防护距离的方法,并比较三种计算方法的优劣,提出确定工业企业卫生防护距离的最终可行方案。     

固定化藻类去除氮、磷的研究进展

综述了近20年来固定化藻类去除氮、磷的主要研究,归纳分析了相关的研究数据和结果,分别从固定化技术、藻类的生理特征、去除机理、影响因素、生物反应器等方面做了具体介绍.     

嘉兴农村不同土地利用方式下沟渠底泥中的氮磷形态分布特征

沟渠是农田氮、磷营养物质排入地表水体的通道. 对嘉兴大田、集约化菜地、集约化果园、集约化养殖场4种土地利用方式下的农村沟渠0～5 cm表层底泥氮、磷的形态分布特征进行了研究. 结果表明:67个沟渠底泥样品的w(全氮)为1 560～7 480 mg/kg,其中w(交换态氮)为31.15～704.38 mg/kg,占w(全氮)的1.29%～10.01%;交换态氮中以铵态氮为主,占w(交换态氮)的62.15%～100%. 沟渠底泥样品的w(全磷)为580～6 420 mg/kg,w(碳酸氢钠溶解磷)为19.53～359.72 mg/kg,占w(全磷)的2.05%～18.96%;w(水溶性磷)为0.29～18.88 mg/kg,占w(碳酸氢钠溶解磷)的1.11%～14.63%. 土地利用方式对沟渠底泥氮、磷的形态分布有显著影响(P<0.01),集约化养殖场沟渠底泥中的w(全氮), w(交换态氮),w(铵态氮), w(硝态氮), w(交换态氮)/w(全氮), w(全磷), w(水溶性磷), w(碳酸氢钠溶解磷)均显著高于其他土地利用方式. 底泥w(全氮), w(交换态氮), w(铵态氮)和w(硝态氮)两两间以及w(全磷), w(水溶性磷), w(碳酸氢钠溶解磷)两两间均在α0.01时显著相关,w(全磷)与w(碳酸氢钠溶解磷)的相关性(r0.81,P<0.01)好于与w(水溶性磷)的相关性(r0.51,P<0.01).      

美洲商陆和籽粒苋对接种伯克氏菌的生理生化响应及其对富集铯的影响

利用盆栽试验研究一株具有重金属耐性的伯克霍尔德氏菌(Burkholderia sp.D54)对美洲商陆和籽粒苋生长及对铯富集的影响.结果表明,接种菌株D54,美洲商陆和籽粒苋总干物重分别比对照处理增加19.8%～33.4%和22.9%～76.6%,美洲商陆和籽粒苋地上部铯含量分别增加4.9%～22.4%和8.1%～19.4%,根中铯含量分别增加6.8%～15.7%和1.1%～10.8%.同时,接种微生物还增加了植物对钾的吸收,提高供试植物的光合反应速率、气孔导度、蒸腾速率和水分利用率,增加铯胁迫条件下植物的抗氧化酶CAT、POD、SOD的活性,降低了MDA的含量.     

游离附生假单胞菌对铜绿微囊蓝细菌中32P释放的影响

采用同位素示踪法，分析游离附生假单胞菌(Pseudomonas sp-)对富集^32P的铜绿微囊蓝细菌(Microcystis aeruginosa)中磷释放的影响．研究结果表明：在微囊蓝细菌生长的延迟期和对数期．游离附生假单胞菌的加入抑制了微囊蓝细菌中^32P的释放，而对蓝细菌的生长没有明显的影响；在微囊蓝细菌生长的稳定期和衰减期，假单胞菌促进其蓝细菌细胞内^32P的释放，同时也加速微囊蓝细菌的衰亡．假单胞菌对微囊蓝细菌^32P释放的促进作用是由于自身的吸磷能力导致的．假单胞菌的吸磷量由假单胞菌生物量和细胞内磷浓度决定，假单胞菌在微囊蓝细菌的整个生长阶段生物量不断增加，而体内^32P浓度在开始阶段很低．直到微囊蓝细菌进入稳定期才达到相对稳定。     

植物N/P与土壤pH值对湿地植物物种丰富度的影响

通过人工控制模拟试验,研究了植物中全氮与全磷之比(植物N/P)和土壤pH值与湿地植物物种丰富度的关系.结果表明,湿地物种丰富度与植物N/P之间呈单峰变化关系,当2.09.5时,氮、磷供应平衡系统可能被破坏,湿地物种逐渐减少.物种丰富度与土壤pH值表现为显著的正相关关系(R²=0.526),当pH值为5.6～6.8时,物种丰富度随着土壤pH值增加而增加.通过方差分析,土壤pH值和植物N/P对物种丰富度的影响分别为37.96%和15.29%.