大中小型拖拉机压实对土壤坚实度和大豆产量的影响

探讨农业机械压实对土壤坚实度和产量的影响规律，对改善作物生产环境、促进农业机械化向质量型转变具有重要意义。以东北典型黑土区耕地土壤为研究对象，依照随机区组试验原理，选择大、中、小3种型号拖拉机进行6种压实处理，同型拖拉机相同压实次数试验重复3次，采用PV6.08型贯穿阻力仪测量压实轮辙截面土壤坚实度。试验结果表明：土壤坚实度随压实次数增加而逐渐递增，3种拖拉机压实测试截面浅层均出现明显压实核，且压实核内土壤坚实度随压实次数增加而逐渐增大，CASE-210型拖拉机压实对表层土壤坚实度影响程度和范围最大，压实12次时压实核处土壤坚实度达4.0 MPa，JD-280型拖拉机对深层土壤压实影响程度和范围最大，在65~80 cm的土壤深层坚实度的峰值达3.2 MPa；拖拉机压实均导致大豆产量降低，CASE-210、JD-904和JD-280拖拉机压实12次时大豆产量分别降低了21.24%、18.15%和12.38%。     

The installation of underground pipelines: effects on soil properties

Since the 1970s a network of underground pipes, up to 1200 mm diameter, has been installed in the UK to transmit crude oil to refineries and gas from onshore terminals for distribution. Chosen routes are subject to significant constraints. Current techniques for pipe installation involve topsoil removal and storage. Trench depth is set to allow a cover of 1200 mm overburden after pipes have been installed. The heavy machinery involved results in severe compaction of exposed subsoil. Subsoil is loosened comprehensively and topsoil replaced. Existing field drains are reconnected, and, if necessary, new drains with gravel backfill installed. Pipe installation usually takes place between April and October. Preventative measures to limit compaction during installation are not a practical option. If subsequent arable crops or grass are poorer or drainage more defective than before disturbance, the loss is assessed and compensation paid. To determine the cause of the loss >60, investigations have been made throughout the UK. Soil physical properties were assessed in an open trench using visual and tactile methods. Consistently, severe compaction in the subsoil was identified as the cause of poor crop growth or drainage; it was not observed in the topsoil. Specific recommendations for remedial action were made based on location, depth and severity of the compaction. These included the installation of additional land drains, increasing the amount of gravel above the drains, or further subsoil loosening orientated to cross gravel backfill. After appropriate remedial action, net compensation for crop losses was frequently small or negligible.     

The North American long-term soil productivity experiment: Findings from the first decade of research

First decade findings on the impacts of organic matter removal and soil compaction are reported for the 26 oldest installations in the nation-wide network of long-term soil productivity sites. Complete removal of surface organic matter led to declines in soil C concentration to 20 cm depth and to reduced nutrient availability. The effect is attributed mainly to the loss of the forest floor. Soil C storage seemed undiminished, but could be explained by bulk density changes following disturbance and to decomposition inputs of organic C from roots remaining from the harvested forest. Biomass removal during harvesting had no influence on forest growth through 10 years. Soil compaction effects depended upon initial bulk density. Soils with densities greater than 1.4 Mg m⁻³ resisted compaction. Density recovery was slow, particularly on soils with frigid temperature regimes. Forest productivity response to soil compaction depended both on soil texture and the degree of understory competition. Production declined on compacted clay soils, increased on sands, and generally was unaffected if an understory was absent.     

Characteristic site disturbance due to harvesting and extraction machinery traffic on sensitive forest sites with peat soils

The effects of wood harvesting and extraction machinery traffic on sensitive forest sites with peat soils were characterised with the objective of quantifying the threshold levels beyond which significant site impacts (compaction and rutting) would occur. The treatments involved running the machines in selected extraction racks (i.e., 3 m wide machine routes) while conducting normal wood thinning and extraction operations comprising one and two passes by the harvester and the forwarder with full payload, respectively. Soil disturbance thresholds were established by testing the level of significance of the difference in induced soil damage and compaction before and after machine traffic treatments. For volumetric soil water content lying between 10.0 and 14.9%, threshold cone penetration resistance levels for two 600/55–30.5 tyres were found to range from 594 to 640 kPa for deep-raised peat soil with initial strength lying between 524 and 581 kPa. In general, the proportion of the total rut depth data in each rack that exceeded the threshold level of 21.5 cm was about 5%. The threshold value corresponds to sinkage equivalent to 15% of the overall wheel diameter of the harvester, above which machine mobility would be hampered considerably. In addition, after harvester traffic the mean rut depth per unit rack length was 10.2×10⁻² cm/m, and it ranged from 0.7 to 24.7×10⁻² cm/m.     

Regeneration of timber trees in a logged tropical forest in North Bolivia

For sustainable forest management, it is important to know the response of timber species to the change in environment caused by logging. We performed a 2-year study on germination, survival and growth of four timber species, Cedrela odorata, Swietenia macrophylla, Hymenaea courbaril, and Cariniana micrantha, and one non-commercial species Tachigali vasquezii. We sowed seeds of these species in five microenvironments: log landing, gap-crown and gap-trunk, skidder trail and understory, in a tropical lowland moist rain forest in northern Bolivia. We related seed and seedling performance to light availability, soil compaction, and plant competition. Germination did not differ significantly between microenvironments but survival of germinated seeds for most species was significantly higher (P < 0.05) in the log landing (46–100%) than in the understory (0–7%). After 2 years, the tallest plants were always found in the log landing (119–190 cm) and the smallest in the understory (12–26 cm) caused by a higher relative height growth rate (RHGR) in the log landing (0.003–0.004 cm cm⁻¹ per day) compared to the understory (0.000–0.001 cm cm⁻¹ per day). During the first year RHGR was positively related to canopy openness for all species and negatively to the number of overtopping competitors for three species. During the second year also water infiltration explained observed variation to RHGR. These results show that abandoned log landings and logging gaps are suitable environments for the regeneration of timber species studied. This finding suggests that the removal of competitors in log landings and logging gaps combined with leaving seed trees near these microenvironments or sowing seeds, will improve regeneration of timber species in tropical forests.     

林地土壤压实对土壤呼吸影响的数学模型研究

介绍土壤呼吸对于林地树木生长的重要性。分析人工干扰等外力作用导致土壤压实,使土壤容重增加,改变土壤孔隙度和二氧化碳浓度等。通过对影响因素和机理的分析,从微观角度利用微分原理,推导出土壤压实对土壤呼吸影响的数学模型,并就各主要影响因素对土壤呼吸的影响进行简要分析。     

农田土壤机械压实的发生、影响及改良

近几十年,随着农田机械的发展,农田土壤机械压实已成为农业机械化发展所不可回避的问题。农田土壤机械压实对土壤物理、化学、生物以及作物生长发育均有明显的负效应。为此,系统分析了近年来国内外在土壤压实起因、压实危害以及减轻压实的技术措施等方面取得的研究成果。同时,介绍了减轻土壤压实作用的技术策略。分析结果有助于进一步了解农田机械进行田间作业时对土壤压实的影响,以便在生产中寻找实用有效的技术,破除土壤压实。     

非饱和重塑黏土在不同击实条件下的土水特征曲线试验研究

采用压力板仪对非饱和重塑黏土在2种不同击实条件下的土水特征曲线进行了研究。即对该重塑土样开展标准击实试验,在击实曲线上取同一干密度对应的不同击实含水率的试样和击实曲线上最优含水率处的试样,并通过增加击实次数,得到另外2种击实干密度的试样,对上述试样进行土水特征曲线测试,并采用常用的土水特征曲线模型Van Genuchten模型、Fredlund 3参数模型、Fredlund 4参数模型对实测试样的土水特征曲线进行了拟合,其拟合结果较好。研究发现,击实干密度越大,空气进入值越高,试样持水能力越强。击实含水率越大,试样可塑性越好,持水能力越强,空气进入值也越大。     

不同载荷对土壤压实的试验研究

在沙壤土上对常用的3种载荷进行了压实试验,测出了土壤压实前后的参数.结果表明:在0～100mm土壤深度处,载荷大于3000kg时,使容重增大较剧烈;载荷大于2000kg时,使湿度损失较严重,4400kg时损失了20%,使坚实度的增量增加剧烈,4400kg时增加了59%,而使最大坚实度增加了114%,并且大载荷对深层(大...