寅街镇森林火灾预防措施及野外火源管理对策

在“被动扑救森林火灾”向“以预防为主”的森林火灾预防机制转变过程中,通过对寅街镇20年来森林火灾发生规律、起火原因、地域和时间分布进行分析,指出93％属人为野外用火引起,森林火灾造成的经济损失主要为非生产性用火中故意纵火、外区烧入、上坟等造成的,野外火源是导致寅街镇森林火灾的主要原因。提出落实责任,加强宣传,完善巡查力度,实施计划烧除,抓好森林火灾保险,严格火源管理等寅街镇森林火灾预防对策及加强野外火源管理的_几点建议。     

Initial Responses to Fertilizing Eucalyptus grandis at Planting are Sustained until Harvesting

The results of six fertilizer experiments with Eucalyptus grandis are discussed and the development of various tree parameters with age are studied. It is shown that in the initial years of growth mean height and breast height diameter are increased as a result of fertilizing at the time of planting, but the absolute differences between fertilized and unfertilized trees remain more or less constant with increasing age. Fertilizing increases total basal area also, and consequently timber yield, but this increase becomes greater up to at least nine years of age or final felling. These increases in timber yield economically justify fertilizing at planting. Brief recommendations are given of how best to conduct field experiments designed to study fertilizer application.     

How many common reptile species are fire specialists? A replicated natural experiment highlights the predictive weakness of a fire succession model

Species with strong preferences for early or late successional stages after fire may be extinction prone under current fire regimes. However, the extent of specialisation to time since fire is poorly understood, and, for reptiles, succession models for predicting responses are in the development phase. In this study we tested predictions of a reptile succession model, and identified species that may be fire specialists. Reptiles were sampled in five burnt and unburnt mallee Eucalyptus woodlands, Australia. Two, 400 m transects within each burn treatment were sampled using 11 pairs of pitfall-traps that were opened for five weeks over two summers. A habitat accommodation model of succession that was previously developed for mallee reptiles correctly predicted the observed responses of three of 16 common reptile species. A further four species showed non-significant trends in the predicted direction. However, eight other species showed unexpected responses. One species showed a strong interaction between burn age and location, requiring a two-dimensional successional model in contrast with the usual linear models explaining reptile responses to fire. One third of common species were not affected by fire and so may not have increased risks of extinction due to the fire suppression/incineration cycle. However, approximately half to two-thirds of common reptiles did have a fire response, so the risk of deterministic extinction in small fragments may be substantial. Further model development is needed to better predict fire responses and to assist the design of fire mosaics that can accommodate early and late successional fire specialists.     

Prescribed Summer Fire and Seeding Applied to Restore Juniper-Encroached and Exotic Annual Grass-Invaded Sagebrush Steppe

Western juniper (Juniperus occidentalis Hook.) encroachment and exotic annual grass (medusahead [Taeniatherum caput-medusae L. Nevski] and cheatgrass [Bromus tectorum L.]) invasion of sagebrush (Artemisia L.) communities decrease ecosystem services and degrade ecosystem function. Traditionally, these compositional changes were largely confined to separate areas, but more sagebrush communities are now simultaneously being altered by juniper and exotic annual grasses. Few efforts have evaluated attempts to restore these sagebrush communities. The Crooked River National Grassland initiated a project to restore juniper-encroached and annual grass-invaded sagebrush steppe using summer (mid-July) applied prescribed fires and postfire seeding. Treatments were unburned, burned, burned and seeded with a native seed mix, and burned and seeded with an introduced seed mix. Prescribed burning removed all juniper and initially reduced medusahead cover but did not influence cheatgrass cover. Neither the native nor introduced seed mix were successful at increasing large bunchgrass cover, and 6 yr post fire, medusahead cover was greater in burned treatments compared with the unburned treatment. Large bunchgrass cover and biological soil crusts were less in treatments that included burning. Exotic forbs and bulbous bluegrass (Poa bulbosa L.), an exotic grass, were greater in burned treatments compared with the unburned treatment. Sagebrush communities that are both juniper encroached and exotic annual grass invaded will need specific management of both juniper and annual grasses. We suggest that additional treatments, such as pre-emergent herbicide control of annuals and possibly multiple seeding events, are necessary to restore these communities. We recommend an adaptive management approach in which additional treatments are applied on the basis of monitoring data.     

The Effect of Rangeland Fires on Cattle Tick Infestation in Western Zambia

Tropical Animal Health and Production -     

室内燃煤及烹调用天然气污染分析

用ＧＤＸ－１０１吸附剂对室内空气中的挥发性有机化合物进行了定性分析,结果表明,定夺内燃煤空气中挥发性有机化合物共７４种,含苯系物,酞酸,酯,醛,酮,醇、酸、胺、脂肪烃和多环芳烃１０类,苯系物和多环芳烃各１１种,占较大比例;     

农地非农化过程中的社会燃烧理论研究

协调经济发展和农地保护之间的矛盾需要对农地非农化进行合理的调控.论文运用社会燃烧理论分析了农地非农化过程的发生,认为农地非农化是在“燃烧物质”——人口增长、资源禀赋、经济发展,“助燃剂”——农地比较经济效益低、农地非农化收益分配不合理、土地产权、权能模糊和地方政府的短期行为,“点火温度”——城市土地使用制度的第一次革命和快速城市化下共同作用的结果.其中,农地比较经济效益低、农地非农化收益分配不合理、土地产权、权能模糊和地方政府的短期行为是当前调控农地非农化应该重点解决的问题.     

阻燃处理木材燃烧残余物的热分解特征

为了弄清楚阻燃处理木材燃烧残余物的热分解特征,将阻燃处理木材在模拟的典型火灾中燃烧后,取距燃烧表面不同位置的试样,采用热失重法研究了阻燃处理木材燃烧残余物的热分解过程,结果表明:①阻燃处理木材及其燃烧残余物的热分解开始温度没有明显的差别,未处理木材燃烧残余物的热分解开始温度比未燃烧木材高;②阻燃处理木材中阻燃剂的热分解峰值温度为200℃,随着燃烧过程的进行,归属于阻燃剂的峰消失;③阻燃处理木材燃烧残余物热分解温度曲线中,在230℃附近归属于半纤维素的峰消失,在210～240℃出现了一个缓慢的肩;④阻燃处理木材及其燃烧残余物的质量损失速度曲线主峰温度比未处理木材及其燃烧残余物降低100℃,质量损失速度大幅度减少;⑤阻燃处理木材在600℃时的热分解残存质量比未处理木材显著增大,随着燃烧时受热温度的增高,燃烧残余物热分解的残余质量显著增大;⑥阻燃处理木材及其燃烧残余物的热分解温度区间,与未处理木材及其燃烧残余物存在显著差异.      

Effects of forest restoration treatments on the abundance of bark beetles in Norway spruce forests of southern Finland

Restoration of protected areas in boreal forests frequently includes creating substantial volumes of dead wood. While this benefits a wide range of dead wood dependent invertebrate species, some of these are regarded as forest pests. Therefore, the risk of elevated levels of tree mortality in surrounding commercial forests must be considered. In a large-scale field experiment in southern Finland, we studied the effects of restoration treatments on the abundance of bark beetles within and in the vicinity of restored areas, in particular focusing on Ips typographus and Pityogenes chalcographus. The treatments applied to managed Norway spruce forests were controlled burning and partial harvesting combined with retaining 5, 30 or 60 m³/ha of cut down wood. We found that the abundance of bark beetles increased by both burning and harvesting with down wood retention, being highest where burning and harvesting had been combined. The actual volume of down wood retention had no significant effect. The effect of burning on the number of bark beetles along host tree boles was negative which suggests that burnt spruces provided a less suitable resource for bark beetles than unburnt dead spruces. The abundance of bark beetles along host trees also decreased with increasing volume of down wood retention. The abundance of P. chalographus was slightly elevated up to 50 m outside restored areas but the abundance was very low compared to that within the areas. The abundance of I. typographus was extremely low outside restored areas. We conclude that restoration treatments increase the abundance of bark beetles via increased availability of resources, but that the effect of burning is likely to be counteracted by decreased resource quality. Thus, burning might be the “safest” way to produce large quantities of dead wood. Furthermore, the fact that only few beetles were collected in adjacent areas suggests that restored areas pose little threat of serving as refugia in which bark beetle populations increase in sufficient numbers to attack live trees in adjacent forests. However, restoration actions repeated at consecutive years within a small area might enable the populations to grow to outbreak levels.     

The role of disturbance severity and canopy closure on standing crop of understory plant species in ponderosa pine stands in northern Arizona,USA

Concerns about the long-term sustainability of overstocked dry conifer forests in western North America have provided impetus for treatments designed to enhance their productivity and native biodiversity. Dense forests are increasingly prone to large stand-replacing fires; yet, thinning and burning treatments, especially combined with other disturbances such as drought and grazing, may enhance populations of colonizing species, including a number of non-native species. Our study quantifies plant standing crop of major herbaceous species across contrasting stand structural types representing a range in disturbance severity in northern Arizona. The least disturbed unmanaged ponderosa pine stands had no non-native species, while non-native grasses constituted 7–11% of the understory plant standing crop in thinned and burned stands. Severely disturbed wildfire stands had a higher proportion of colonizing native species as well as non-native species than other structural types, and areas protected from grazing produced greater standing crop of native forbs compared to grazed unmanaged stands. Standing crop of understory plants in low basal area thinned and burned plots was similar to levels on wildfire plots, but was comprised of fewer non-native graminoids and native colonizing plants. Our results also indicate that size of canopy openings had a stronger influence on standing crop in low basal area plots, whereas tree density more strongly constrained understory plant standing crop in dense stands. These results imply that treatments resulting in clumped tree distribution and basal areas <10 m² ha⁻¹ will be more successful in restoring native understory plant biomass in dense stands. Multiple types and severity of disturbances, such as thinning, burning, grazing, and drought over short periods of time can create greater abundance of colonizing species. Spreading thinning and burning treatments over time may reduce the potential for non-native species colonization compared to immediately burning thinned stands.