CN102603430B - Compost tea for improving soil hardness and preparation method thereof - Google Patents
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Abstract
Description
技术领域 technical field
本发明属于土壤改良技术领域,特别涉及一种改善土壤板结的堆肥茶及其制备方法。The invention belongs to the technical field of soil improvement, in particular to a compost tea for improving soil compaction and a preparation method thereof.
背景技术 Background technique
(1)土壤板结是农业可持续发展过程中面临的一个重要问题(1) Soil compaction is an important problem in the sustainable development of agriculture
随着世界各国对农业可持续发展的日益重视,对土壤生产能力的可持续性提出了更高的要求。特别在我国人口多、耕地少、面临粮食安全的严峻形势下,如何保障土壤的可持续生产能力尤为重要。土壤板结是土壤退化重要表现之一,特别是亚表层土壤板结,限制植物根系向地下生长,在植物生长中后期如遇到降雨少和蒸发大的情况下土壤板结严重影响植物对水分的吸收。干旱可能限制植物生长和产量形成。深耕常被用于减缓土壤板结,但深耕的作用较为短暂且能量和时间成本较高。深耕减缓土壤板结也破坏了多年免耕管理发展起来的表层覆盖,也增加了土壤侵蚀和表土板结的风险。As countries around the world pay more and more attention to the sustainable development of agriculture, higher requirements are put forward for the sustainability of soil production capacity. Especially in the severe situation of my country's large population, little arable land, and food security, how to ensure the sustainable production capacity of soil is particularly important. Soil compaction is one of the important manifestations of soil degradation, especially the subsurface soil compaction, which restricts the growth of plant roots underground. In the middle and late stages of plant growth, if there is little rainfall and high evaporation, soil compaction seriously affects the water absorption of plants. Drought can limit plant growth and yield development. Deep tillage is often used to slow down soil compaction, but the effect of deep tillage is short-lived and has high energy and time costs. Deep tillage to slow soil compaction also destroys the surface cover developed over years of no-till management, and also increases the risk of soil erosion and topsoil compaction.
(2)堆肥茶为板结土壤的改良提供了可能(2) Compost tea provides the possibility for the improvement of compacted soil
堆肥茶指堆制腐熟的有机物料经过发酵获得的水浸提液,不仅含有大量的有益微生物,也含有大量的养分,其原理是在制作堆肥茶过程中添加特定微生物的食物,使得土壤食物网更加健康。近年来,堆肥茶在有机农业中的效果及应用已逐渐被认同,原因在于使用堆肥茶具有如下优点:(1)抑制病害或提高作物抗病性,以增强作物健康和减少对杀虫剂的需求;(2)为植物提供水溶性的养分,以减少肥料需求和降低成本;和(3)增加土壤微生物量和多样性,以改善土壤结构、保水性,促进根系和植物生长。早在20世纪20年代,欧洲园丁们就用堆肥茶来浸种和喷灌以增加土壤肥力,防治碎倒病。直到20世纪80年代中期,美国一些科学家才开始对堆肥茶进行研究,并在一些有机农场中得到应用。目前国外对堆肥茶的研究和应用大都侧重于其对病虫害的防治效果,对于其营养效果的研究尚不多见,其在土壤改良中的报道更加缺乏。Compost tea refers to the water extract obtained by fermenting composted and decomposed organic materials, which not only contains a large number of beneficial microorganisms, but also contains a large amount of nutrients. The principle is to add specific microbial food in the process of making compost tea, making the soil food web more healthy. In recent years, the effect and application of compost tea in organic agriculture has gradually been recognized, because the use of compost tea has the following advantages: (1) inhibit disease or improve crop disease resistance, so as to enhance crop health and reduce exposure to pesticides demand; (2) provide water-soluble nutrients to plants to reduce fertilizer requirements and reduce costs; and (3) increase soil microbial biomass and diversity to improve soil structure, water retention, and promote root and plant growth. As early as the 1920s, European gardeners used compost tea to soak seeds and sprinkle irrigation to increase soil fertility and prevent crushing disease. It was not until the mid-1980s that some scientists in the United States began to study compost tea, and it was applied in some organic farms. At present, the research and application of compost tea in foreign countries mostly focus on its control effect on plant diseases and insect pests, while the research on its nutritional effect is still rare, and the reports on its use in soil improvement are even more scarce.
(3)堆肥茶的制作及其在板结土壤改良中的应用将为农业可持续发展提供新的途径(3) The production of compost tea and its application in compacted soil improvement will provide a new way for the sustainable development of agriculture
鉴于堆肥茶在农业应用的诸多优点,通过制作高质量的堆肥茶进行板结土壤的改良,将为农业可持续发展提供新的途径。由于不同种类的土壤微生物在土壤中扮演的角色不同,对改善土壤结构存在较大的差异,通过调节堆肥茶的配方以制作出有利于改善土壤结构的高质量堆肥茶并优化其施用方法,为解决农业可持续发展过程中出现的土壤板结问题提供新的方法。In view of the many advantages of compost tea in agricultural applications, the improvement of compacted soil by making high-quality compost tea will provide a new way for the sustainable development of agriculture. Because different types of soil microorganisms play different roles in soil, there are great differences in improving soil structure. By adjusting the formula of compost tea to produce high-quality compost tea that is conducive to improving soil structure and optimizing its application method, for It provides a new method to solve the problem of soil compaction in the process of sustainable agricultural development.
发明内容Contents of the invention
本发明针对以上技术问题,设计提供了一种特别适用于改善板结土壤团粒结构的堆肥茶及其制作和施用方法。该方法操作简单方便,成本低,改良效果快。该方法适用于水稻田水改旱,红粘土、砂姜黑土等容重较大土壤的疏松,茶叶、果树等多年生作物的免耕施肥及土壤改良。Aiming at the above technical problems, the present invention designs and provides a compost tea which is especially suitable for improving the aggregate structure of compacted soil and its production and application method. The method is simple and convenient to operate, low in cost and fast in improving effect. The method is suitable for changing water to dryness in paddy fields, loosening soil with large bulk density such as red clay and sandy ginger black soil, no-tillage fertilization and soil improvement of perennial crops such as tea and fruit trees.
本发明所述的适合于板结土壤改良的堆肥茶的制作含材料选择、制作过程和质量指标选取三部分;堆肥茶的施用方法包括施用条件、施用时间和施用量的参数选取。The preparation of the compost tea suitable for compacted soil improvement of the present invention includes three parts: material selection, production process and quality index selection; the application method of compost tea includes the selection of parameters of application conditions, application time and application amount.
本发明所述的改善土壤板结的堆肥茶的制备方法为:The preparation method of the compost tea for improving soil compaction of the present invention is:
步骤1:将堆肥装入网孔直径为0.08-0.50mm的网袋中;Step 1: Put the compost into a mesh bag with a mesh diameter of 0.08-0.50mm;
步骤2:容器中加水,将通气管置于容器底部,1m3水的曝气量为0.2-0.8L/h,通气20-60min,除去氯气后加入质量比为1∶(1.5-5.0)∶(1.5-4.5)的糖蜜、海藻粉和腐殖酸,然后将步骤1中装好堆肥的网袋放入水中,堆肥与水的质量比为1∶(10-40);糖蜜、海藻粉和腐殖酸加入总质量为堆肥质量的1-5%;Step 2: Add water to the container, place the ventilation tube at the bottom of the container, the aeration rate of 1m 3 water is 0.2-0.8L/h, ventilate for 20-60min, after removing the chlorine, add the mass ratio is 1: (1.5-5.0): (1.5-4.5) of molasses, seaweed powder and humic acid, then put the mesh bag of composting in step 1 into water, and the mass ratio of compost and water is 1: (10-40); molasses, seaweed powder and The total mass of humic acid added is 1-5% of the compost mass;
步骤3:浸提发酵过程中避免强光直射,保持溶液中通气,外界气温控制在20-35℃,优选25-30℃,经过24-48小时,制得改善土壤板结的堆肥茶。Step 3: Avoid strong light during the extraction and fermentation process, keep the solution ventilated, and control the outside temperature at 20-35°C, preferably 25-30°C. After 24-48 hours, the compost tea that improves soil compaction is obtained.
所述的堆肥选择满足有机肥NY525-2011和生物有机肥标准NY 884-2004要求的,并且生物指标为:活性细菌≥15μg/mg、全部细菌≥15μg/mg、活性真菌≥10μg/mg和全部真菌≥200μg/mg。The compost is selected to meet the requirements of organic fertilizer NY525-2011 and bio-organic fertilizer standard NY 884-2004, and the biological indicators are: active bacteria ≥ 15 μg/mg, all bacteria ≥ 15 μg/mg, active fungi ≥ 10 μg/mg and all Fungi ≥ 200 μg/mg.
步骤3制得的改善土壤板结的堆肥茶的生物指标为:活性细菌≥10μg/ml、全部细菌≥150μg/ml、活性真菌≥10μg/ml和全部真菌≥20μg/ml。The biological indicators of the compost tea for improving soil compaction prepared in step 3 are: active bacteria ≥ 10 μg/ml, total bacteria ≥ 150 μg/ml, active fungi ≥ 10 μg/ml and total fungi ≥ 20 μg/ml.
步骤3制得的改善土壤板结的堆肥茶的施用方法为:制得的改善土壤板结的堆肥茶6小时内使用完毕,每亩的施用量为10-20L,加入50-250倍质量的水稀释后施用。The application method of the compost tea for improving soil compaction prepared in step 3 is as follows: the prepared compost tea for improving soil compaction is used up within 6 hours, the application amount per mu is 10-20L, and 50-250 times the quality of water is added to dilute after application.
稀释后的堆肥茶直接浇灌到作物根部,或者采用滴灌系统。The diluted compost tea can be watered directly to the roots of the crops, or a drip irrigation system can be used.
有益效果:1)本发明中的堆肥茶制作的材料极易获得,且成本较低,制作过程简单,施用方法简便;2)本发明改良板结土壤的效率高,时间短,堆肥茶浇灌约40-50天后板结土壤的团粒结构显著改善;3)本发明所采用的原料不添加化学合成物质,制作出的堆肥茶溶液对环境无污染,符合农业可持续发展需要。Beneficial effects: 1) The material for making compost tea in the present invention is very easy to obtain, and the cost is low, the production process is simple, and the application method is simple; 2) The efficiency of improving compacted soil in the present invention is high, and the time is short, and the compost tea is watered for about 40 -After 50 days, the aggregate structure of the compacted soil is significantly improved; 3) the raw materials used in the present invention do not add chemical synthetic substances, and the compost tea solution produced has no pollution to the environment and meets the needs of sustainable agricultural development.
附图说明 Description of drawings
图1:实施例2中砂浆黑土土壤添加堆肥茶45天后与未添加堆肥茶的土壤对照样品的土壤标准化平均当量直径NMWD值。Figure 1: The soil normalized mean equivalent diameter NMWD value of the mortar black soil soil in Example 2 after adding compost tea for 45 days and the soil control sample without adding compost tea.
图2:实施例3砖红壤番木瓜果园中番木瓜苗移栽6个月后施用堆肥茶和未施用堆肥茶的树冠内外土壤容重的结果。Fig. 2: The results of soil bulk density inside and outside the canopy of papaya seedlings transplanted 6 months after application of compost tea and no compost tea in papaya orchard in brick red soil in Example 3.
具体实施方式 Detailed ways
实施例1:Example 1:
步骤1:将堆肥装入网孔直径为0.15mm的网袋中;Step 1: Put the compost into a mesh bag with a mesh diameter of 0.15mm;
步骤2:容器中加水,将通气管置于容器底部,1m3水的曝气量为0.2L/h,通气30min,除去氯气后加入质量比为1∶4∶3的糖蜜、海藻粉和腐殖酸,然后将步骤1中装好堆肥的网袋放入水中,堆肥与水的质量比为1∶20;糖蜜、海藻粉和腐殖酸加入总质量为堆肥质量的2%;Step 2: Add water to the container, place the ventilation tube at the bottom of the container, aerate 1m3 of water at a rate of 0.2L/h, ventilate for 30min, and add molasses, seaweed powder and rotten water with a mass ratio of 1:4:3 after removing chlorine gas. Humic acid, then put into the water the mesh bag of composting in step 1, the mass ratio of compost and water is 1: 20; Molasses, seaweed powder and humic acid add total mass and are 2% of composting quality;
步骤3:浸提发酵过程中避免强光直射,保持溶液通气,外界气温控制在25-30℃,经过24小时,制得改善土壤板结的堆肥茶。Step 3: Avoid strong direct sunlight during the extraction and fermentation process, keep the solution ventilated, and control the outside temperature at 25-30°C. After 24 hours, a compost tea that improves soil compaction is obtained.
所述的堆肥选择满足有机肥NY525-2011和生物有机肥标准NY 884-2004要求的,并且生物指标为:活性细菌≥15μg/mg、全部细菌≥15μg/mg、活性真菌≥10μg/mg和全部真菌≥200μg/mg。The compost is selected to meet the requirements of organic fertilizer NY525-2011 and bio-organic fertilizer standard NY 884-2004, and the biological indicators are: active bacteria ≥ 15 μg/mg, all bacteria ≥ 15 μg/mg, active fungi ≥ 10 μg/mg and all Fungi ≥ 200 μg/mg.
上述制得的改善土壤板结的堆肥茶的生物指标为:活性细菌≥10μg/ml、全部细菌≥150μg/ml、活性真菌≥10μg/ml和全部真菌≥20μg/ml。The biological indicators of the above prepared compost tea for improving soil compaction are: active bacteria ≥ 10 μg/ml, total bacteria ≥ 150 μg/ml, active fungi ≥ 10 μg/ml and total fungi ≥ 20 μg/ml.
水稻土施用堆肥茶种植番茄40天后番茄生物量及土壤结构状况:蔬菜种植要求疏松的土壤,而尚未熟化的水稻土通常较为板结不利于蔬菜生长,实验在水稻土上种植番茄,在减少肥料投入50%的情况下浇灌上述制得的堆肥茶,制作好的堆肥茶6小时内使用完毕,每亩的施用量为20L,加入100倍质量的水稀释后直接浇灌到番茄根部,经过40天,番茄的生长状况和生物量与传统施肥(100%化肥)的处理没有统计上的差异,同时,堆肥茶处理的土壤团粒结构明显优于传统施肥处理。实验表明,采用本发明制作的堆肥茶及使用方法在板结土壤上种植蔬菜,不仅能够改良板结土壤(形成良好的土壤团粒结构),而且可以降低化学肥料的投入量。Tomato biomass and soil structure after 40 days of planting tomatoes with compost tea on paddy soil: Vegetable planting requires loose soil, and unripe paddy soil is usually more compacted, which is not conducive to vegetable growth. The experiment is to plant tomatoes on paddy soil to reduce fertilizer input. Water the compost tea prepared above under 50% of the situation, and use up the compost tea made within 6 hours. The amount of application per mu is 20L. Add 100 times the quality of water to dilute it and then directly pour it on the tomato roots. After 40 days, The growth status and biomass of tomato were not statistically different from the treatment with conventional fertilization (100% chemical fertilizer), meanwhile, the soil aggregate structure of the compost tea treatment was significantly better than that of the conventional fertilization treatment. Experiments show that planting vegetables on compacted soil by adopting the compost tea made by the present invention and its use method can not only improve the compacted soil (form a good soil aggregate structure), but also reduce the input amount of chemical fertilizers.
实施例2:Example 2:
步骤1:将堆肥装入网孔直径为0.15mm的网袋中;Step 1: Put the compost into a mesh bag with a mesh diameter of 0.15mm;
步骤2:容器中加水,将通气管置于容器底部,1m3水的曝气量为0.2L/h,通气30min,除去氯气后加入质量比为1∶3∶2的糖蜜、海藻粉和腐殖酸,然后将步骤1中装好堆肥的网袋放入水中,堆肥与水的质量比为1∶10;糖蜜、海藻粉和腐殖酸加入总质量为堆肥质量的3%;Step 2: Add water to the container, place the ventilation tube at the bottom of the container, aerate 1m3 of water at a rate of 0.2L/h, ventilate for 30min, and add molasses, seaweed powder and rotten water with a mass ratio of 1:3:2 after removing chlorine gas. Humic acid, then put the net bag of compost in step 1 into water, the mass ratio of compost and water is 1: 10; Molasses, seaweed powder and humic acid add total mass and are 3% of compost quality;
步骤3:浸提发酵过程中避免强光直射,保持溶液通气,外界气温控制在25-30℃,经过36小时,制得改善土壤板结的堆肥茶。Step 3: Avoid direct sunlight during the extraction and fermentation process, keep the solution ventilated, and control the outside temperature at 25-30°C. After 36 hours, the compost tea that improves soil compaction is obtained.
所述的堆肥选择满足有机肥NY525-2011和生物有机肥标准NY 884-2004要求的,并且生物指标为:活性细菌≥15μg/mg、全部细菌≥15μg/mg、活性真菌≥10μg/mg和全部真菌≥200μg/mg。The compost is selected to meet the requirements of organic fertilizer NY525-2011 and bio-organic fertilizer standard NY 884-2004, and the biological indicators are: active bacteria ≥ 15 μg/mg, all bacteria ≥ 15 μg/mg, active fungi ≥ 10 μg/mg and all Fungi ≥ 200 μg/mg.
上述制得的改善土壤板结的堆肥茶的生物指标为:活性细菌≥10μg/ml、全部细菌≥150μg/ml、活性真菌≥10μg/ml和全部真菌≥20μg/ml。The biological indicators of the above prepared compost tea for improving soil compaction are: active bacteria ≥ 10 μg/ml, total bacteria ≥ 150 μg/ml, active fungi ≥ 10 μg/ml and total fungi ≥ 20 μg/ml.
堆肥茶添加对砂浆黑土土壤结构的影响(土壤培养45天):Effect of compost tea addition on soil structure of mortar black soil (soil cultured for 45 days):
砂姜黑土是典型的板结土壤,其具有土体构造不良,土壤物理性状差,养分含量低等不良属性。其土体构造的特点是耕作层浅(一般12厘米左右)而较疏松,犁底层厚(一般15-20厘米)而紧实,物理性状差的主要表现是,除耕作层为粒状结构外,土体棱状结构发达,土层坚实,土壤容重较大,耕作层1.4g/cm3左右,其余土层都在以上,土壤总孔隙度和通气孔隙度都较小,耕作层分别为47%和8%左右,其余土层分别在45%和2%左右,通透性能很差,犁底层基本上是一层不透水层。在机械组成上,耕作层粘粒含量比犁底层和砂姜层低,平均为22.95%,粉砂层含量较高,一般在57%以上。这种土体构造和物理性状的特点,在农业耕作上的反映是:干时坚硬,湿时泥泞,耕性不良,适耕期短(3-5天)。Shajiang black soil is a typical compacted soil, which has bad properties such as poor soil structure, poor soil physical properties, and low nutrient content. The characteristics of its soil structure are that the plow layer is shallow (generally about 12 cm) and relatively loose, and the plow bottom layer is thick (generally 15-20 cm) and compact. The main manifestations of poor physical properties are that, in addition to the granular structure of the plow layer, The prismatic structure of the soil body is developed, the soil layer is solid, and the soil bulk density is large. The cultivated layer is about 1.4g/ cm3 , and the rest of the soil layers are above. The total soil porosity and air porosity are small, and the cultivated layer is 47% And about 8%, the remaining soil layers are about 45% and 2% respectively, the permeability is very poor, and the plow bottom layer is basically an impermeable layer. In terms of mechanical composition, the clay content of the plow layer is lower than that of the plow bottom layer and the sand ginger layer, with an average of 22.95%, and the content of the silt layer is higher, generally above 57%. The characteristics of this kind of soil structure and physical properties are reflected in agricultural cultivation: hard when dry, muddy when wet, poor plowability, and short suitable tillage period (3-5 days).
标准化平均当量直径(NMWD值)是衡量土壤团聚体稳定性的一个指标,其值越低,表示团聚体稳定性越小。本实施例采用供试土壤-砂姜黑土进行土壤恒温培养实验。称取150g土壤,设置处理为:堆肥茶处理和对照,堆肥茶施用100ml/kg,剩余水分用去离子水补足,将土壤含水量调节至土壤田间持水量的60%,塑料杯用聚乙烯塑料保鲜膜封口,并在保鲜膜中间留一小孔,以便气体交换并防止水分损失过大。将烧杯置于25℃的恒温培养箱中培养,每隔3天称重1次并补充水分,以保持土壤含水量恒定。培养实验共持续45天,风干土壤测试其团粒结构。由图1可看出,堆肥茶添加处理的土壤NMWD值显著高于对照处理,堆肥茶处理的NMWD值比对照处理高出19.3%。本实施例表明,本发明能够在不种植植物的条件下仍然可很好地改良板结土壤(砂姜黑土)的团粒结构。The normalized mean equivalent diameter (NMWD value) is an index to measure the stability of soil aggregates, and the lower the value, the less stable the aggregate. The present embodiment adopts the test soil-Shajiang black soil to carry out the soil constant temperature cultivation experiment. Weigh 150g of soil, set the treatment as: compost tea treatment and control, apply 100ml/kg of compost tea, make up the remaining water with deionized water, adjust the soil water content to 60% of the field water holding capacity of the soil, and use polyethylene plastic for the plastic cup Seal the plastic wrap and leave a small hole in the middle of the plastic wrap to facilitate gas exchange and prevent excessive moisture loss. The beakers were placed in a constant temperature incubator at 25°C for cultivation, and were weighed every 3 days and supplemented with water to keep the soil moisture content constant. The cultivation experiment lasted for 45 days, and the air-dried soil was tested for its aggregate structure. It can be seen from Figure 1 that the soil NMWD value of the compost tea treatment was significantly higher than that of the control treatment, and the NMWD value of the compost tea treatment was 19.3% higher than that of the control treatment. This example shows that the present invention can still improve the aggregate structure of compacted soil (shajiang black soil) well without planting plants.
实施例3:Example 3:
步骤1:将堆肥装入网孔直径为0.50mm的网袋中;Step 1: Put the compost into a mesh bag with a mesh diameter of 0.50mm;
步骤2:容器中加水,将通气管置于容器底部,1m3水的曝气量为0.5L/h,通气30min,除去氯气后加入质量比为1∶2∶2的糖蜜、海藻粉和腐殖酸,然后将步骤1中装好堆肥的网袋放入水中,堆肥与水的质量比为1∶15;糖蜜、海藻粉和腐殖酸加总质量为堆肥质量的1%;Step 2: Add water to the container, place the ventilation tube at the bottom of the container, aerate 1m3 of water at a rate of 0.5L/h, ventilate for 30min, and add molasses, seaweed powder and rotten water with a mass ratio of 1:2:2 after removing chlorine. Humic acid, then put into the water the mesh bag of composting in step 1, the mass ratio of compost and water is 1: 15; The total quality of molasses, seaweed powder and humic acid is 1% of composting quality;
步骤3:浸提发酵过程中避免强光直射,保持溶液通气,外界气温控制在25-30℃,经过48小时,制得改善土壤板结的堆肥茶。Step 3: Avoid strong direct sunlight during the extraction and fermentation process, keep the solution ventilated, and control the outside temperature at 25-30°C. After 48 hours, a compost tea that improves soil compaction is obtained.
所述的堆肥选择满足有机肥NY525-2011和生物有机肥标准NY 884-2004要求的,并且生物指标为:活性细菌≥15μg/mg、全部细菌≥15μg/mg、活性真菌≥10μg/mg和全部真菌≥200μg/mg。The compost is selected to meet the requirements of organic fertilizer NY525-2011 and bio-organic fertilizer standard NY 884-2004, and the biological indicators are: active bacteria ≥ 15 μg/mg, all bacteria ≥ 15 μg/mg, active fungi ≥ 10 μg/mg and all Fungi ≥ 200 μg/mg.
上述制得的改善土壤板结的堆肥茶的生物指标为:活性细菌≥10μg/ml、全部细菌≥150μg/ml、活性真菌≥10μg/ml和全部真菌≥20μg/ml。The biological indicators of the above prepared compost tea for improving soil compaction are: active bacteria ≥ 10 μg/ml, total bacteria ≥ 150 μg/ml, active fungi ≥ 10 μg/ml and total fungi ≥ 20 μg/ml.
砖红壤番木瓜果园堆肥茶施用对土壤容重的影响:Effects of compost tea application on soil bulk density in papaya orchard in brick red soil:
数百年来,犁铧翻耕是旱作农业生产的基础,耕翻在平坦、潮湿和粘重土地得到了广泛应用,但是,在地势起伏地区,频繁的耕翻加剧了土壤侵蚀,导致土壤地力退化。免耕具有减少劳动强度和时间、减少机械损耗降低燃料费用、减少土壤侵蚀、保持土壤水分、改善土壤耕性、改善土壤水渗透性能、增加土壤有机质含量、减少CO2排放和空气污染、耕地连续性使用、增加农民收入等特点。因此,发展免耕技术,是持续和效益农业的最佳选择。多年生果树种植过程深耕容易伤根,为病原菌进入果树提供了机会,从而影响作物的生长。For hundreds of years, plowshare tillage has been the basis of dry farming agricultural production. Tillage has been widely used on flat, wet and sticky land. However, in undulating areas, frequent tillage aggravates soil erosion, resulting in poor soil fertility. degradation. No-tillage has the advantages of reducing labor intensity and time, reducing mechanical loss, reducing fuel costs, reducing soil erosion, maintaining soil moisture, improving soil plowability, improving soil water infiltration performance, increasing soil organic matter content, reducing CO 2 emissions and air pollution, continuous cultivated land Sexual use, increasing farmers' income and other characteristics. Therefore, the development of no-tillage technology is the best choice for sustainable and profitable agriculture. Deep plowing during the planting of perennial fruit trees is easy to damage the roots, which provides opportunities for pathogenic bacteria to enter the fruit trees, thereby affecting the growth of crops.
砖红壤是热带雨林或季雨林中的土壤在热带季风气候下,发生强度富铝和生物富集作用而发育成的深厚红色土壤,其土层深厚,质地粘重,粘粒含量高达60%以上。实验对砖红壤番木瓜果园每个月浇灌2次上述制得的堆肥茶,每亩的施用量为20L,定植后前3个月采用加入200倍质量水稀释堆肥茶后浇灌于番木瓜根部,定植后第4个月开始采用加入100倍质量水稀释堆肥茶后浇灌于番木瓜根部。图2显示番木瓜苗移栽6个月后堆肥茶和对照处理树冠内外土壤容重的结果,采用堆肥茶处理番木瓜树冠内土壤容重显著低于树冠外和对照处理。本实施例表明,新技术能改善砖红壤土壤团粒结构,且在果园免耕中获得良好效果。Brick red soil is a deep red soil developed from the intense aluminum-rich and bio-enrichment of soil in tropical rainforest or monsoon rainforest under tropical monsoon climate. In the experiment, the papaya orchard in brick red soil was irrigated twice a month with the above-mentioned compost tea, and the application rate per mu was 20L. In the first 3 months after planting, 200 times the quality of water was added to dilute the compost tea and then watered on the papaya roots. In the 4th month after planting, add 100 times the quality of water to dilute the compost tea and water it on the papaya roots. Figure 2 shows the results of the soil bulk density inside and outside the canopy of the papaya seedlings treated with compost tea and the control treatment 6 months after transplanting. The soil bulk density inside the canopy of papaya treated with compost tea was significantly lower than that outside the canopy and the control treatment. This example shows that the new technology can improve the soil aggregate structure of brick red soil, and achieve good results in no-tillage in orchards.
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| CN103214285B (en) * | 2013-01-28 | 2015-08-05 | 宁夏大学 | A kind of preparation method of novel full-nutrition compost tea micropore fermentation bag |
| CN105330486B (en) * | 2015-11-30 | 2019-04-12 | 金正大生态工程集团股份有限公司 | A kind of the solanaceous vegetables special nutrient set fertilizer and its method of administration of biological and ecological methods to prevent plant disease, pests, and erosion synergy |
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| CN105367345B (en) * | 2015-12-11 | 2019-06-04 | 金正大生态工程集团股份有限公司 | A kind of the solanaceous vegetables facilities vegetable special nutrient set fertilizer and its method of administration of improvement soil hardening |
| CN105367177B (en) * | 2015-12-11 | 2019-06-25 | 金正大生态工程集团股份有限公司 | A kind of drop sprinkling irrigation solanaceous vegetables facilities vegetable special nutrient set fertilizer and its method of administration |
| CN105384569B (en) * | 2015-12-11 | 2019-02-19 | 金正大生态工程集团股份有限公司 | A kind of the solanaceous vegetables facilities vegetable special nutrient set fertilizer and method of administration of prevention and treatment nematode |
| CN107586215A (en) * | 2017-11-02 | 2018-01-16 | 山西省农业科学院现代农业研究中心 | Prevent and treat the compost tea preparation and application of strawberry Verticillium wilt |
| RU2683529C1 (en) * | 2018-09-10 | 2019-03-28 | Валерий Абрамович Шапиро | Method for producing concentrated soil solution enriched |
| KR102161110B1 (en) | 2018-12-26 | 2020-09-29 | 강원도 | Compost tea using functional compost, method of manufacturing the same and use of the same |
| CN116535251A (en) * | 2023-05-12 | 2023-08-04 | 中国农业科学院农业资源与农业区划研究所 | A kind of biokinetic factor and preparation method thereof |
Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1850739A (en) * | 2006-05-18 | 2006-10-25 | 陕西杨凌华阳化工有限责任公司 | Polar-molecule composite fertilizer additive |
| CN102229515A (en) * | 2011-04-27 | 2011-11-02 | 北京雷力农用化学有限公司 | Organic granular fertilizer and preparation method thereof |
-
2012
- 2012-04-17 CN CN2012101129148A patent/CN102603430B/en active Active
Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1850739A (en) * | 2006-05-18 | 2006-10-25 | 陕西杨凌华阳化工有限责任公司 | Polar-molecule composite fertilizer additive |
| CN102229515A (en) * | 2011-04-27 | 2011-11-02 | 北京雷力农用化学有限公司 | Organic granular fertilizer and preparation method thereof |
Non-Patent Citations (5)
| Title |
|---|
| 张瑞久,逢辰生.美国城市生活垃圾处理现状与趋势(下).《节能与环保》.2007,(第12期),第12-15页. * |
| 牛粪堆肥茶最优发酵条件研究;郭徽等;《安徽农业科学》;20090320;第37卷(第8期);第3613-3614页 * |
| 生态特效肥料"堆肥茶"的科学原理与制作方法;贺淹才;《安徽农业科学》;20031225;第31卷(第6期);第1081-1082页 * |
| 贺淹才.生态特效肥料"堆肥茶"的科学原理与制作方法.《安徽农业科学》.2003,第31卷(第6期),第1081-1082页. |
| 郭徽等.牛粪堆肥茶最优发酵条件研究.《安徽农业科学》.2009,第37卷(第8期),第3613-3614页. |
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