CN106612849A - Method for application of organic fertilizer substituting chemical fertilizer in quantitative manner - Google Patents
Method for application of organic fertilizer substituting chemical fertilizer in quantitative manner Download PDFInfo
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- 239000003895 organic fertilizer Substances 0.000 title claims abstract description 82
- 239000003337 fertilizer Substances 0.000 title claims abstract description 62
- 238000000034 method Methods 0.000 title claims abstract description 42
- 239000000126 substance Substances 0.000 title claims abstract description 35
- 239000000618 nitrogen fertilizer Substances 0.000 claims abstract description 98
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims abstract description 89
- 230000009418 agronomic effect Effects 0.000 claims abstract description 46
- 229910052757 nitrogen Inorganic materials 0.000 claims abstract description 45
- 239000002689 soil Substances 0.000 claims abstract description 38
- 238000006467 substitution reaction Methods 0.000 claims abstract description 34
- 235000015097 nutrients Nutrition 0.000 claims abstract description 24
- 230000004044 response Effects 0.000 claims abstract description 22
- 230000035558 fertility Effects 0.000 claims abstract description 11
- 241000209094 Oryza Species 0.000 claims description 75
- 235000007164 Oryza sativa Nutrition 0.000 claims description 75
- 235000009566 rice Nutrition 0.000 claims description 75
- 240000008042 Zea mays Species 0.000 claims description 36
- 235000002017 Zea mays subsp mays Nutrition 0.000 claims description 36
- 241000209140 Triticum Species 0.000 claims description 24
- 235000021307 Triticum Nutrition 0.000 claims description 24
- 235000005824 Zea mays ssp. parviglumis Nutrition 0.000 claims description 23
- 235000005822 corn Nutrition 0.000 claims description 23
- 238000012360 testing method Methods 0.000 claims description 10
- 238000009406 nutrient management Methods 0.000 claims description 4
- 230000008901 benefit Effects 0.000 abstract description 4
- 238000011002 quantification Methods 0.000 abstract description 4
- 235000021049 nutrient content Nutrition 0.000 abstract 1
- 238000002474 experimental method Methods 0.000 description 15
- 238000011282 treatment Methods 0.000 description 14
- 235000016383 Zea mays subsp huehuetenangensis Nutrition 0.000 description 13
- 235000009973 maize Nutrition 0.000 description 13
- 210000003608 fece Anatomy 0.000 description 12
- 239000010871 livestock manure Substances 0.000 description 12
- 238000004458 analytical method Methods 0.000 description 7
- 238000009355 double cropping Methods 0.000 description 7
- 230000004720 fertilization Effects 0.000 description 7
- 238000009335 monocropping Methods 0.000 description 7
- 240000000359 Triticum dicoccon Species 0.000 description 6
- 244000144972 livestock Species 0.000 description 6
- 244000144977 poultry Species 0.000 description 6
- 238000005516 engineering process Methods 0.000 description 4
- 238000012271 agricultural production Methods 0.000 description 3
- 238000004364 calculation method Methods 0.000 description 3
- 230000007423 decrease Effects 0.000 description 3
- 235000013305 food Nutrition 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 238000012851 eutrophication Methods 0.000 description 2
- 238000003306 harvesting Methods 0.000 description 2
- 230000007774 longterm Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 201000004569 Blindness Diseases 0.000 description 1
- 241000287828 Gallus gallus Species 0.000 description 1
- 229910002651 NO3 Inorganic materials 0.000 description 1
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 1
- 241001494479 Pecora Species 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000003905 agrochemical Substances 0.000 description 1
- 239000003242 anti bacterial agent Substances 0.000 description 1
- 229940088710 antibiotic agent Drugs 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000004927 clay Substances 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 235000021393 food security Nutrition 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 238000009336 multiple cropping Methods 0.000 description 1
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 230000020477 pH reduction Effects 0.000 description 1
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- 229910052698 phosphorus Inorganic materials 0.000 description 1
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- 239000002699 waste material Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
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- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01C—PLANTING; SOWING; FERTILISING
- A01C21/00—Methods of fertilising, sowing or planting
- A01C21/007—Determining fertilization requirements
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Abstract
本发明属于肥料施用技术领域,具体为一种有机肥定量替代化肥的施用方法,具体步骤如下:S1、依据作物生长环境,以当地以往若干年该作物平均产量来估算某一田块最佳养分管理措施下的可获得产量;S2、分别计算氮肥农学效率和达到可获得产量所需要的总氮素用量;S3、按照有机肥氮素养分定量替代化肥氮素养分的原则,分别计算有机肥推荐施用量和有机替代后的氮肥用量;S4、以计算得到的有机肥推荐施用量对该田块施肥。本发明的方法具有轻简化、定量化、合理化等优点,只需评估作物生长环境和土壤肥力状况,利用可获得产量、氮肥反应指数和有机肥替代指数等关键参数,快速、准确地预估氮肥和有机肥的施用总量,有效提高作物产量和氮肥利用率。
The invention belongs to the technical field of fertilizer application, and specifically relates to an application method for quantitatively replacing chemical fertilizers with organic fertilizers. The specific steps are as follows: S1. According to the crop growth environment, the optimal nutrient content of a certain field is estimated based on the local average yield of the crop in the past several years Achievable yield under management measures; S2, respectively calculate the agronomic efficiency of nitrogen fertilizer and the total nitrogen amount required to achieve the achievable yield; S3, calculate the recommended organic fertilizer according to the principle of replacing nitrogen nutrient quantitatively with organic fertilizer nitrogen nutrient Application rate and nitrogen fertilizer application rate after organic substitution; S4. Fertilize the field with the calculated recommended application rate of organic fertilizer. The method of the present invention has the advantages of light simplification, quantification, and rationalization. It only needs to evaluate the crop growth environment and soil fertility status, and quickly and accurately predict nitrogen fertilizer by using key parameters such as yield, nitrogen fertilizer response index, and organic fertilizer substitution index. And the total amount of organic fertilizer application, effectively improving crop yield and nitrogen use efficiency.
Description
技术领域technical field
本发明属于肥料施用技术领域领域,具体涉及一种有机肥定量替代化肥的施用方法。The invention belongs to the technical field of fertilizer application, and in particular relates to an application method for quantitatively replacing chemical fertilizers with organic fertilizers.
背景技术Background technique
化肥是粮食安全的重要保障,对粮食增产的贡献占40%-50%。上世纪八十年代以来,我国化肥使用总量从1600万吨(折纯)增长到2014年的5990万吨,增长了270%,即使是近10年,我国的化肥使用量仍然以每年2.7%的速度在增长。目前,我国单位面积耕地化肥用量为329公斤/公顷,是美国的2.6倍,欧盟的2.5倍。然而,我国肥料养分利用率低,氮肥当季利用率仅为30%-35%,磷肥仅为10%-20%。大量的养分排放到环境中,已成为地表水富营养化、地下水和农产品硝酸盐超标、土壤酸化的重要原因,对生态环境造成了严重的危害。因此,我国农业生产亟需从过度依赖化肥投入转变为保护环境的绿色增产增效施肥模式。Chemical fertilizers are an important guarantee for food security, contributing 40%-50% to the increase in food production. Since the 1980s, the total amount of chemical fertilizers used in my country has increased from 16 million tons (converted to pure) to 59.9 million tons in 2014, an increase of 270%. Even in the past 10 years, my country's chemical fertilizer use is still at 2.7% per year speed is growing. At present, the amount of chemical fertilizer per unit area of cultivated land in my country is 329 kg/ha, which is 2.6 times that of the United States and 2.5 times that of the European Union. However, the utilization rate of fertilizer nutrients in my country is low. The seasonal utilization rate of nitrogen fertilizer is only 30%-35%, and that of phosphorus fertilizer is only 10%-20%. The discharge of a large amount of nutrients into the environment has become an important cause of eutrophication of surface water, excessive nitrate of groundwater and agricultural products, and acidification of soil, causing serious harm to the ecological environment. Therefore, my country's agricultural production urgently needs to change from an over-reliance on chemical fertilizer input to a green and environmentally friendly fertilization model that increases production and increases efficiency.
目前,有机肥部分替代化肥是减少农业化肥施用量的重要途径,但由于缺乏轻简化、定量化、合理化的有机肥施用技术,农民施用有机肥的盲目性很大,针对性不强,造成我国丰富的有机肥养分资源未能充分利用,畜禽有机肥还田率不到50%,有机肥养分资源浪费严重。At present, the partial replacement of chemical fertilizers by organic fertilizers is an important way to reduce the amount of agricultural chemical fertilizers used. However, due to the lack of simplified, quantitative, and rationalized organic fertilizer application technologies, farmers use organic fertilizers blindly and are not targeted. Abundant organic fertilizer nutrient resources have not been fully utilized, and the return rate of livestock and poultry organic fertilizer is less than 50%, which is a serious waste of organic fertilizer nutrient resources.
中国发明专利CN 201510771958.5公开了一种在农田施用有机肥的方法,虽然该方法可以确定有机肥的施用量,但应用该方法的前提条件是获得目标营养元素的施用总量,以及不同种植模式下化肥养分定量替代有机肥养分的适宜比例。上述两个参数是有机肥合理施用的关键,实际农业生产过程中,如何快速得到上述两个参数是有机肥轻简化、定量化、合理化施用的基础。Chinese invention patent CN 201510771958.5 discloses a method of applying organic fertilizer on farmland. Although this method can determine the application amount of organic fertilizer, the prerequisite for applying this method is to obtain the total application amount of the target nutrient elements, and the The appropriate ratio of chemical fertilizer nutrients to quantitatively replace organic fertilizer nutrients. The above two parameters are the key to the rational application of organic fertilizers. In the actual agricultural production process, how to quickly obtain the above two parameters is the basis for light, simplified, quantitative and rational application of organic fertilizers.
目前,精准获得目标营养元素的施用总量往往需要通过繁琐的土壤测试和复杂的计算过程,例如测土配方施肥技术,需要大量的人力、物力和财力对土壤养分进行测定。我国小麦、玉米、水稻生产主要以小农户经营为主体,复种指数高,作物种植茬口紧,依据土壤测试指导农民合理施用有机肥存在测试推荐不及时和成本高等难题,小农户为主体的经营模式很难做到这一点。At present, accurate acquisition of the total application amount of target nutrients often requires cumbersome soil testing and complex calculation processes, such as soil testing and formula fertilization technology, which requires a lot of manpower, material and financial resources to measure soil nutrients. The production of wheat, corn and rice in my country is mainly operated by small farmers, with a high multiple cropping index and tight stubble crops. According to the soil test to guide farmers to rationally apply organic fertilizer, there are problems such as untimely test and recommendation and high cost. Small farmers are the main business model. It's hard to do that.
不同种植模式下化肥养分定量替代有机肥养分的最佳比例是有机肥合理施用的关键参数。目前一般采用短期试验得到这一参数,然而,研究表明有机肥残留养分对粮食作物的增产效果至少在3年以上。因此,中长期定位试验数据得到的化肥养分定量替代有机肥养分比例是维持作物高产稳产的重要保障。此外,如果该替代比例失调,极易造成作物减产、土壤重金属污染、以及抗生素等有害物质在土壤中大量积累。The optimal ratio of chemical fertilizer nutrients quantitatively replacing organic fertilizer nutrients under different planting patterns is a key parameter for rational application of organic fertilizers. At present, short-term experiments are generally used to obtain this parameter. However, studies have shown that the residual nutrients of organic fertilizers can increase the yield of food crops for at least 3 years. Therefore, the quantitative replacement of organic fertilizer nutrient ratio by chemical fertilizer nutrient obtained from medium and long-term positioning test data is an important guarantee for maintaining high and stable crop yield. In addition, if the replacement ratio is out of balance, it is very easy to cause crop yield reduction, soil heavy metal pollution, and a large amount of harmful substances such as antibiotics to accumulate in the soil.
目前,本领域对上述问题并未提供系统化的解决方案,过往研究均未能充分考虑如何快速预估目标营养元素的施用总量,未能根据作物种类和种植区域提出长期稳定的化肥养分定量替代有机肥养分的适宜比例,导致有机肥不合理现象普遍存在。因此,亟需一种轻简化、定量化、合理化的有机肥施用方法。At present, this field has not provided a systematic solution to the above problems. Previous studies have not fully considered how to quickly estimate the total application of target nutrients, and have not proposed long-term stable fertilizer nutrient quantification according to crop types and planting areas. The appropriate proportion of nutrients replaced by organic fertilizers has led to the widespread existence of unreasonable organic fertilizers. Therefore, there is an urgent need for a simplified, quantitative, and rationalized method of applying organic fertilizers.
发明内容Contents of the invention
本发明提供一种适用于小麦、玉米、水稻种植的有机肥定量替代化肥的施用方法。该方法具有轻简化、定量化、合理化等优点,只需要通过评估作物生长环境和土壤肥力状况,利用可获得产量、氮肥反应指数和有机肥替代指数等关键参数,快速、准确地预估氮肥和有机肥的施用总量,有效提高作物产量和氮肥利用率,减少环境污染,提升土壤肥力水平,是一种高效易行、适用广泛的环境保护性有机肥施用技术。The invention provides an application method for quantitatively replacing chemical fertilizers with organic fertilizers suitable for planting wheat, corn and rice. This method has the advantages of light simplification, quantification, and rationalization. It only needs to evaluate the crop growth environment and soil fertility status, and use key parameters such as available yield, nitrogen fertilizer response index, and organic fertilizer substitution index to quickly and accurately estimate nitrogen fertilizer and organic fertilizer. The total amount of organic fertilizer application can effectively increase crop yield and nitrogen fertilizer use efficiency, reduce environmental pollution, and improve soil fertility level. It is an efficient, easy, and widely applicable environmental protection organic fertilizer application technology.
本发明提供一种有机肥定量替代化肥的施用方法,具体步骤如下:The invention provides a method for applying organic fertilizers to quantitatively replace chemical fertilizers, the specific steps are as follows:
S1、依据作物生长环境,以当地以往若干年该作物平均产量来估算某一田块最佳养分管理措施下的可获得产量;S1. According to the crop growth environment, use the local average yield of the crop in the past few years to estimate the yield available under the best nutrient management measures for a certain field;
S2、按照公式(1)、公式(2)分别计算氮肥农学效率和达到可获得产量所需要的总氮素用量:S2. According to formula (1) and formula (2), respectively calculate the agronomic efficiency of nitrogen fertilizer and the total nitrogen consumption required to achieve the yield:
氮肥农学效率=A×(可获得产量×INS)2+B×(可获得产量×INS)+C (1)Nitrogen Fertilizer Agronomic Efficiency = A×(Achievable Yield×INS) 2 +B×(Achievable Yield×INS)+C (1)
其中,INS是指氮肥反应指数,其数值根据土壤肥力状况确定;氮肥农学效率的单位为kg/kg,A为二次项系数,B为一次项系数,C为常数项,A、B、C的数值通过拟合作物以往试验数据二项式曲线确定;Among them, INS refers to the nitrogen fertilizer response index, and its value is determined according to the soil fertility status; the unit of nitrogen fertilizer agronomic efficiency is kg/kg, A is the quadratic coefficient, B is the first coefficient, C is the constant term, A, B, C The value of is determined by fitting the binomial curve of the previous test data of the crop;
总氮素用量=(可获得产量×INS)÷氮肥农学效率×1000 (2)Total Nitrogen Application = (Achievable Yield × INS) ÷ Agronomic Efficiency of Nitrogen Fertilizer × 1000 (2)
其中,总氮素用量的单位为kg N/ha;Among them, the unit of total nitrogen consumption is kg N/ha;
S3、按照有机肥氮素养分定量替代化肥氮素养分的原则,以公式(3)、公式(4)分别计算有机肥推荐施用量和有机替代后的氮肥用量:S3, according to the principle of organic fertilizer nitrogen nutrient quantitatively replacing chemical fertilizer nitrogen nutrient, calculate the recommended application amount of organic fertilizer and the amount of nitrogen fertilizer after organic replacement respectively with formula (3) and formula (4):
有机肥推荐施用量=(总氮肥用量×有机肥替代指数)÷有机肥氮素含量÷1000 (3)Recommended application amount of organic fertilizer = (total nitrogen fertilizer amount × organic fertilizer substitution index) ÷ organic fertilizer nitrogen content ÷ 1000 (3)
其中,有机肥推荐施用量的单位为t/ha,有机肥替代指数根据作物的多年定位数据计算获得;Among them, the unit of recommended application rate of organic fertilizer is t/ha, and the organic fertilizer substitution index is calculated based on the multi-year positioning data of crops;
有机替代后的氮肥用量=总氮肥用量×(1-有机肥替代指数) (4)Nitrogen fertilizer amount after organic substitution = total nitrogen fertilizer amount × (1-organic fertilizer substitution index) (4)
其中,有机替代后的氮肥用量的单位为kg/ha;Among them, the unit of nitrogen fertilizer amount after organic substitution is kg/ha;
S4、以计算得到的有机肥推荐施用量对该田块施肥。S4. Fertilize the field with the calculated recommended application rate of organic fertilizer.
S1所述作物生长环境为气候条件、土壤条件中的任一种或几种。The crop growth environment described in S1 is any one or more of climate conditions and soil conditions.
S1所述可获得产量的估算方式为:划分生长环境的风险等级,针对各等级梯度设置合理的最佳养分管理措施下的预期产量,根据当地情况评定作物生长环境风险,相应等级的预期产量即为可获得产量;预期产量≥当地以往若干年该作物平均产量。The method of estimating the obtainable yield in S1 is: divide the risk level of the growth environment, set the expected yield under the reasonable best nutrient management measures for each grade gradient, and assess the risk of the crop growth environment according to the local conditions. The expected yield of the corresponding level is It is the yield that can be obtained; the expected yield ≥ the local average yield of the crop in the past several years.
当作物为小麦时,所述可获得产量为根据当地气候条件出现干旱、低温、霜冻等自然灾害的频率评定生长环境风险后进行估算,标准为(根据以往5年的实验结果总结):When the crop is wheat, the available yield is estimated based on the frequency of natural disasters such as drought, low temperature, and frost in the local climatic conditions after assessing the risk of the growth environment. The standard is (summarized based on the experimental results of the past 5 years):
当地经常(每两年总次数≥3次)发生自然灾害的为高风险生长环境,可获得产量等于当地以往若干年小麦平均产量;A high-risk growth environment where natural disasters frequently occur (the total number of times every two years ≥ 3 times) is a high-risk growth environment, and the obtainable yield is equal to the local average wheat yield in the past several years;
当地有时(每两年总次数=2次)发生自然灾害的为中风险生长环境,可获得产量为在当地以往若干年小麦平均产量的基础上增加0.5t/ha;A medium-risk growing environment where natural disasters sometimes occur locally (total number of times per two years = 2 times), and the obtainable yield is an increase of 0.5t/ha on the basis of the local average wheat yield in the past several years;
当地很少(每两年总次数≤1次)发生自然灾害的为低风险生长环境,可获得产量为在当地以往若干年小麦平均产量的基础上增加1.0t/ha。A low-risk growing environment where natural disasters rarely occur (the total number of times every two years ≤ 1) is a low-risk growth environment, and the obtainable yield is an increase of 1.0t/ha on the basis of the local average wheat yield in the past several years.
当作物为玉米时,所述可获得产量为根据当地气候条件发生涝害、旱害等自然灾害的频率和田块土壤条件评定生长环境风险后进行估算,标准为(根据以往5年的实验结果总结):When the crop is corn, the available yield is estimated after assessing the risk of the growth environment based on the frequency of natural disasters such as waterlogging and drought under local climate conditions and the soil conditions of the field. The standard is (summarized based on the experimental results in the past 5 years) ):
当地经常(每两年总次数≥3次)发生自然灾害或者田块为障碍性土壤,为高风险生长环境,可获得产量为在当地以往若干年玉米平均产量的基础上增加0.5t/ha;Natural disasters frequently occur in the local area (the total number of times ≥ 3 times every two years) or the field is obstructed soil, which is a high-risk growth environment, and the obtainable yield is an increase of 0.5t/ha on the basis of the local average corn yield in the past several years;
当地有时(每两年总次数=2次)发生自然灾害或者田块土层厚度较浅,为中风险生长环境,可获得产量为在当地以往若干年玉米平均产量的基础上增加1.0t/ha;Sometimes natural disasters occur locally (total number of times every two years = 2 times) or the soil layer of the field is shallow, which is a medium-risk growth environment, and the obtainable yield is an increase of 1.0t/ha on the basis of the local average corn yield in the past several years ;
当地很少(每两年总次数≤1次)发生自然灾害,为低风险生长环境,可获得产量为在当地以往若干年玉米平均产量的基础上增加1.5t/ha。Natural disasters rarely occur in the local area (total frequency ≤ 1 time every two years), and it is a low-risk growth environment. The obtainable yield is an increase of 1.5t/ha on the basis of the local average corn yield in the past several years.
当作物为水稻时,所述可获得产量为根据土壤条件评定生长环境风险后进行估算,标准为(根据以往5年的实验结果总结):When the crop is rice, the obtainable yield is estimated after assessing the risk of the growth environment based on soil conditions, and the standard is (summarized based on the experimental results of the past 5 years):
田块土壤有障碍因子,为高风险生长环境,可获得产量等于当地以往若干年水稻平均产量;The field soil has obstacle factors, which is a high-risk growth environment, and the obtainable yield is equal to the local average rice yield in the past several years;
田块土壤无障碍因子,为低风险生长环境,可获得产量为在当地以往若干年水稻平均产量的基础上增加0.5t/ha。The barrier-free factor of the field soil is a low-risk growth environment, and the obtainable yield is an increase of 0.5t/ha on the basis of the local average rice yield in the past several years.
所述土壤有障碍因子指土壤为盐渍土、泥炭土、酸性硫酸盐土中的任何一种。The soil obstacle factor refers to that the soil is any one of saline soil, peat soil and acid sulfate soil.
S1所述若干年为5-10年,优选为5年。The number of years mentioned in S1 is 5-10 years, preferably 5 years.
S2所述氮肥反应指数依据表1确定:The nitrogen fertilizer response index described in S2 is determined according to Table 1:
表1不同土壤肥力状况下作物氮肥反应指数Table 1 Crop nitrogen response index under different soil fertility conditions
当作物为小麦时,A为-0.2406,B为3.985,C为4.9974。小麦可适用于河南小麦-玉米轮作体系和湖北水稻-小麦轮作体系。When the crop is wheat, A is -0.2406, B is 3.985, and C is 4.9974. Wheat can be applied to Henan wheat-corn rotation system and Hubei rice-wheat rotation system.
当作物为夏玉米时,A为-0.0559,B为2.7026,C为5.8266。夏玉米可适用于河南小麦-玉米轮作体系。When the crop is summer corn, A is -0.0559, B is 2.7026, and C is 5.8266. Summer maize can be applied to Henan wheat-corn rotation system.
当作物为春玉米时,A为-0.1118,B为3.5435,C为6.7919。春玉米可适用于黑龙江春玉米单作体系。When the crop is spring corn, A is -0.1118, B is 3.5435, and C is 6.7919. Spring maize can be applied to Heilongjiang spring maize monocropping system.
当作物为中稻时,A为-0.5002,B为7.5038,C为0.5747。中稻可适用于湖北水稻-小麦轮作体系。When the crop is middle rice, A is -0.5002, B is 7.5038, and C is 0.5747. Mid-season rice can be applied to Hubei rice-wheat rotation system.
当作物为早稻或晚稻时,A为-0.5003,B为8.0034,C为0.6522。早稻或晚稻可适用于江西双季稻连作体系。When the crop is early rice or late rice, A is -0.5003, B is 8.0034, and C is 0.6522. Early rice or late rice can be applied to Jiangxi double-cropping rice continuous cropping system.
不同作物的有机肥替代指数见表2:The organic fertilizer substitution index of different crops is shown in Table 2:
表2不同作物有机肥替代指数Table 2 Organic fertilizer substitution index for different crops
S3所述有机肥氮素含量按如下方式确定:The nitrogen content of the organic fertilizer described in S3 is determined as follows:
当所用有机肥为商品肥料时,商品肥料氮素含量即为有机肥氮素含量;When the organic fertilizer used is a commercial fertilizer, the nitrogen content of the commercial fertilizer is the nitrogen content of the organic fertilizer;
当所用有机肥为畜禽粪肥,以实际测试值确定,或者根据我国畜禽粪肥平均氮素含量估算。When the organic fertilizer used is livestock and poultry manure, it shall be determined based on the actual test value, or estimated based on the average nitrogen content of livestock and poultry manure in my country.
我国畜禽粪肥平均氮素含量可参见表3:The average nitrogen content of livestock and poultry manure in my country can be seen in Table 3:
表3畜禽粪肥中氮素平均质量百分含量Table 3 Average mass percentage content of nitrogen in livestock and poultry manure
S4所述施肥,以基肥的形式施入。The fertilization described in S4 is applied in the form of base fertilizer.
所述以基肥的形式施入,为在整地前施入田间,使用旋耕机将有机肥在0-20cm土层内混匀。Said application in the form of basal fertilizer is to apply to the field before soil preparation, using a rotary tiller to mix the organic fertilizer evenly in the 0-20cm soil layer.
本发明的方法优点如下:Method advantage of the present invention is as follows:
1、与现有技术相比,本发明的方法可以在不进行土壤测试的条件下定量施用有机肥,只需要评估作物生长环境和土壤肥力状况,具有轻简化、定量化、合理化等优点,可操作性强,降低了农民施用有机肥的盲目性。1. Compared with the prior art, the method of the present invention can apply organic fertilizer quantitatively without soil testing, and only needs to evaluate the crop growth environment and soil fertility status, which has the advantages of light simplification, quantification, rationalization, etc., and can It has strong operability and reduces the blindness of farmers applying organic fertilizer.
2、本发明的方法在优化小麦、玉米、水稻氮肥施用量的基础上,合理施用有机肥。即减少了化肥的过量施用,也通过合理施用有机肥改善土壤结构,提高土壤微生物多样性、促进土壤养分良性循环。因此,有效降低了农业面源污染和水体富营养化的风险。2. The method of the present invention rationally applies the organic fertilizer on the basis of optimizing the amount of nitrogen fertilizer applied to wheat, corn and rice. That is to say, the excessive application of chemical fertilizers is reduced, and the soil structure is improved through the rational application of organic fertilizers, the diversity of soil microorganisms is increased, and the virtuous cycle of soil nutrients is promoted. Therefore, the risks of agricultural non-point source pollution and water eutrophication are effectively reduced.
3、本发明的方法适用范围涉及我国三大粮食作物(小麦、玉米、水稻)种植区,包括华东双季稻连作体系、华中水稻-小麦轮作体系、华北小麦-玉米轮作体系、东北春玉米单作体系,适用范围广泛。通过5年定位试验得到了不同作物的最佳有机肥替代指数。3. The scope of application of the method of the present invention relates to my country's three major food crops (wheat, corn, rice) planting areas, including the double-cropping rice continuous cropping system in East China, the rice-wheat rotation system in Central China, the wheat-corn rotation system in North China, and the spring corn single cropping system in Northeast China. The system has a wide range of applications. The best organic fertilizer substitution index of different crops was obtained through 5-year positioning experiment.
4、与常规施肥相比,本发明的方法显著提高作物千粒重、结实率、氮素回收利用率和收获指数,例如水稻千粒重和结实率分别提高13.14%和3.7%,水稻氮素回收利用率和收获指数分别提高41.24%和8.3%。利用本发明的方法提高了小麦、玉米和水稻产量,降低了农业生产成本,增加了农民收入,实现了有机肥的科学利用。4. Compared with conventional fertilization, the method of the present invention significantly improves crop thousand-grain weight, seed-setting rate, nitrogen recycling rate and harvest index, such as rice thousand-grain weight and seed-setting rate improve respectively by 13.14% and 3.7%, rice nitrogen recycling rate and The harvest index increased by 41.24% and 8.3% respectively. The method of the invention improves the output of wheat, corn and rice, reduces the cost of agricultural production, increases farmers' income, and realizes the scientific utilization of organic fertilizers.
附图说明Description of drawings
图1为预实验1中的小麦氮肥反应指数分析图。Fig. 1 is the analysis chart of wheat nitrogen fertilizer response index in preliminary experiment 1.
图2为预实验1中的玉米氮肥反应指数分析图。Fig. 2 is an analysis chart of nitrogen fertilizer response index of maize in preliminary experiment 1.
图3为预实验1中的水稻氮肥反应指数分析图。Fig. 3 is an analysis chart of rice nitrogen fertilizer response index in preliminary experiment 1.
图4为预实验2中的小麦氮肥农学效率与可获得产量和INS之间的二项式曲线关系图。Fig. 4 is a binomial curve relationship graph between the agronomic efficiency of wheat nitrogen fertilizer and the available yield and INS in the pilot experiment 2.
图5为预实验2中的夏玉米氮肥农学效率与可获得产量和INS之间的二项式曲线关系图。Fig. 5 is a binomial curve relationship graph between the agronomic efficiency of summer maize nitrogen fertilizer and the available yield and INS in the pre-experiment 2.
图6为预实验2中的春玉米氮肥农学效率与可获得产量和INS之间的二项式曲线关系图。Fig. 6 is a binomial curve relationship diagram between the agronomic efficiency of spring maize nitrogen fertilizer and the available yield and INS in the pre-experiment 2.
图7为预实验2中的北方一季稻和南方中稻氮肥农学效率与可获得产量和INS之间的二项式曲线关系图。Fig. 7 is a binomial curve relationship graph between the agronomic efficiency of nitrogen fertilizer and the available yield and INS of the northern one-crop rice and the southern mid-season rice in the pre-experiment 2.
图8为预实验2中的南方早、晚稻氮肥农学效率与可获得产量和INS之间的二项式曲线关系图。Fig. 8 is a binomial curve relationship graph between the agronomic efficiency of nitrogen fertilizer and available yield and INS of southern early and late rice in pre-experiment 2.
图9为本发明有机肥定量替代化肥的施用方法的流程图。Fig. 9 is a flow chart of the application method of quantitatively replacing chemical fertilizer with organic fertilizer according to the present invention.
具体实施方式detailed description
下面结合实施例,对本发明的具体实施方式作进一步详细描述。以下实施例用于说明本发明,但不用来限制本发明的范围。Below in conjunction with the examples, the specific implementation of the present invention will be further described in detail. The following examples are used to illustrate the present invention, but are not intended to limit the scope of the present invention.
预实验1氮肥反应指数的计算Calculation of Nitrogen Fertilizer Response Index in Pre-Experiment 1
氮肥反应指数INS,Nitrogen response index INS,
INS=1-不施肥作物产量÷施肥作物产量INS = 1 - crop yield without fertilization ÷ crop yield with fertilization
利用6102个数据点(通过5年的试验获得)分析了小麦、玉米和水稻在不施氮肥条件下和施用氮肥条件下的产量,每种作物的样本数在2000个以上,通过上述公式计算得到高产田(INS排序靠前第25%的数据点)、中产田(INS排序中间第50%的数据点)、低产田(INS排序靠后第25%的数据点)氮肥反应指数,小麦氮肥反应指数分析图见图1、玉米氮肥反应指数分析图见图2、水稻氮肥反应指数分析图见图3,最终统计得到的小麦、玉米和水稻氮肥反应指数见的表1。Using 6102 data points (obtained through 5 years of experiments) to analyze the yield of wheat, corn and rice under the condition of no nitrogen fertilizer and nitrogen fertilizer application, the number of samples of each crop is more than 2000, calculated by the above formula High-yielding fields (the top 25% data points in the INS ranking), medium-yielding fields (the middle 50% data points in the INS ranking), low-yielding fields (the bottom 25% data points in the INS ranking) nitrogen fertilizer response index, wheat nitrogen fertilizer response See Figure 1 for the index analysis chart, Figure 2 for the nitrogen fertilizer response index analysis chart for corn, and Figure 3 for the nitrogen fertilizer response index analysis chart for rice, and see Table 1 for the nitrogen fertilizer response indices of wheat, corn and rice obtained from the final statistics.
表1不同土壤肥力状况下作物氮肥反应指数Table 1 Crop nitrogen response index under different soil fertility conditions
预实验2氮肥农学效率的计算Calculation of Nitrogen Fertilizer Agronomic Efficiency in Pre-experiment 2
在预实验1中6102个数据点的基础上,通过合并区间数据点,进一步拟合氮肥农学效率与可获得产量和INS之间的二项式曲线关系,发现小麦、夏玉米、春玉米、北方一季稻和南方中稻、南方早稻和晚稻的氮肥农学效率与可获得产量、INS之间存在很好的一元二次方程关系,决定系数R2均为0.99以上。所述一元二次方程为:Based on the 6102 data points in the pre-experiment 1, by merging interval data points, and further fitting the binomial curve relationship between the agronomic efficiency of nitrogen fertilizer and the available yield and INS, it was found that wheat, summer maize, spring maize, northern There was a good one-variable quadratic relationship between the agronomic efficiency of nitrogen fertilizer and the available yield and INS of the first-crop rice and southern middle rice, southern early rice and late rice, and the coefficient of determination R 2 was above 0.99. The quadratic equation of one yuan is:
氮肥农学效率=A×(可获得产量×INS)2+B×(可获得产量×INS)+C (1)Nitrogen Fertilizer Agronomic Efficiency = A×(Achievable Yield×INS) 2 +B×(Achievable Yield×INS)+C (1)
其中A为二次项系数,B为一次项系数,C为常数项。Among them, A is the coefficient of the quadratic term, B is the coefficient of the first term, and C is the constant term.
当作物为小麦时,计算氮肥农学效率的公式为:When the crop is wheat, the formula for calculating the agronomic efficiency of nitrogen fertilizer is:
氮肥农学效率=-0.2406×(可获得产量×INS)2+3.985×(可获得产量×INS)+4.9974 (5)Nitrogen Fertilizer Agronomic Efficiency = -0.2406×(Achievable Yield×INS) 2 +3.985×(Achievable Yield×INS)+4.9974 (5)
具体见图4,A为-0.2406,B为3.985,C为4.9974,R2=0.999。See Figure 4 specifically, A is -0.2406, B is 3.985, C is 4.9974, and R 2 =0.999.
小麦可适用于河南小麦-玉米轮作体系和湖北水稻-小麦轮作体系。Wheat can be applied to Henan wheat-corn rotation system and Hubei rice-wheat rotation system.
当作物为夏玉米时,计算氮肥农学效率的公式为:When the crop is summer corn, the formula for calculating the agronomic efficiency of nitrogen fertilizer is:
氮肥农学效率=-0.0559×(可获得产量×INS)2+2.7026×(可获得产量×INS)+5.8266 (6)Nitrogen fertilizer agronomic efficiency = -0.0559×(available yield×INS) 2 +2.7026×(available yield×INS)+5.8266 (6)
具体见图5,A为-0.0559,B为2.7026,C为5.8266,R2=0.9977。夏玉米可适用于河南小麦-玉米轮作体系。See Fig. 5 specifically, A is -0.0559, B is 2.7026, C is 5.8266, and R 2 =0.9977. Summer maize can be applied to Henan wheat-corn rotation system.
当作物为春玉米时,计算氮肥农学效率的公式为:When the crop is spring corn, the formula for calculating the agronomic efficiency of nitrogen fertilizer is:
氮肥农学效率=-0.1118×(可获得产量×INS)2+3.5435×(可获得产量×INS)+6.7919 (7)Nitrogen fertilizer agronomic efficiency = -0.1118×(available yield×INS) 2 +3.5435×(available yield×INS)+6.7919 (7)
具体见图6,A为-0.1118,B为3.5435,C为6.7919,R2=0.9985。春玉米可适用于黑龙江春玉米单作体系。See Fig. 6 specifically, A is -0.1118, B is 3.5435, C is 6.7919, and R 2 =0.9985. Spring maize can be applied to Heilongjiang spring maize monocropping system.
当作物为中稻时,计算氮肥农学效率的公式为:When the crop is mid-season rice, the formula for calculating the agronomic efficiency of nitrogen fertilizer is:
氮肥农学效率=-0.5002×(可获得产量×INS)2+7.5038×(可获得产量×INS)+0.5747 (8)Nitrogen Fertilizer Agronomic Efficiency = -0.5002×(Achievable Yield×INS) 2 +7.5038×(Achievable Yield×INS)+0.5747 (8)
具体见图7,A为-0.5002,B为7.5038,C为0.5747,R2=0.9999。中稻可适用于湖北水稻-小麦轮作体系。See Fig. 7 specifically, A is -0.5002, B is 7.5038, C is 0.5747, and R 2 =0.9999. Mid-season rice can be applied to Hubei rice-wheat rotation system.
当作物为早稻或晚稻时,计算氮肥农学效率的公式为:When the crop is early rice or late rice, the formula for calculating the agronomic efficiency of nitrogen fertilizer is:
氮肥农学效率=-0.5003×(可获得产量×INS)2+8.0034×(可获得产量×INS)+0.6522 (9)Nitrogen fertilizer agronomic efficiency = -0.5003×(available yield×INS) 2 +8.0034×(available yield×INS)+0.6522 (9)
具体见图8,A为-0.5003,B为8.0034,C为0.6522,R2=0.9999。早稻或晚稻可适用于江西双季稻连作体系。See Figure 8 for details, A is -0.5003, B is 8.0034, C is 0.6522, and R 2 =0.9999. Early rice or late rice can be applied to Jiangxi double-cropping rice continuous cropping system.
实施例1江西省高安市双季稻试验Example 1 Double-cropping rice experiment in Gao'an City, Jiangxi Province
本实施例按照图9的流程进行,于2013年-2015年在江西省高安市渡埠农村进行,种植制度为双季稻连作。种植作物前对试验站点往年的产量情况和自然气候条件进行调查,得到农户过去5年的晚稻平均产量水平为8t/ha,早稻平均产量水平为7t/ha。农田土壤无障碍因子,水稻的可获得产量为农户过去5年的平均产量水平基础上增加0.5t/ha。因此,晚稻可获得产量=8t/ha+0.5t/ha=8.5t/ha;早稻可获得产量=7t/ha+0.5t/ha=7.5t/ha。This embodiment is carried out according to the flow chart in Figure 9, and was carried out in Dubu Village, Gao'an City, Jiangxi Province from 2013 to 2015, and the planting system is double-cropping rice continuous cropping. Before planting crops, the yield and natural climate conditions of the test site in previous years were investigated, and it was found that the average yield of late rice in the past 5 years was 8t/ha, and the average yield of early rice was 7t/ha. Farmland soil accessibility factor, the available yield of rice is an increase of 0.5t/ha on the basis of the average yield level of farmers in the past 5 years. Therefore, the available output of late rice = 8t/ha + 0.5t/ha = 8.5t/ha; the available output of early rice = 7t/ha + 0.5t/ha = 7.5t/ha.
当地土壤类型为粘土,有机质含量偏低,其过去5年的平均产量低于全国25%的水稻种植区产量,将其土壤肥力状况归为低等,根据表1得到水稻氮肥反应指数(INS)为0.37。可以基于本发明的方法计算氮肥农学效率,早晚稻氮肥农学效率(kg/kg)=-0.5003×(可获得产量×0.37)2+8.0034×(可获得产量×0.37)+0.6522。因此,晚稻氮肥农学效率为20.87kg/kg,早稻氮肥农学效率为19.01kg/kg。The local soil type is clay, and the organic matter content is low. Its average yield in the past five years is lower than that of 25% of the rice planting areas in the country, and its soil fertility status is classified as low. According to Table 1, the nitrogen fertilizer response index (INS) of rice is obtained is 0.37. The agronomic efficiency of nitrogen fertilizer can be calculated based on the method of the present invention, and the agronomic efficiency of nitrogen fertilizer in early and late rice (kg/kg)=-0.5003×(available yield×0.37) 2 +8.0034×(available yield×0.37)+0.6522. Therefore, the agronomic efficiency of nitrogen fertilizer in late rice is 20.87kg/kg, and that of early rice is 19.01kg/kg.
可以基于本发明的方法计算总氮素用量,总氮素用量(kg N/ha)=(可获得产量×0.37)÷氮肥农学效率×1000。因此,晚稻总氮素用量为150.69kg N/ha,早稻总氮素用量为145.98kg N/ha。The total nitrogen application amount can be calculated based on the method of the present invention, and the total nitrogen application amount (kg N/ha)=(obtainable yield×0.37)÷nitrogen fertilizer agronomic efficiency×1000. Therefore, the total nitrogen application rate of late rice is 150.69 kg N/ha, and that of early rice is 145.98 kg N/ha.
江西省高安市渡埠农村有机肥主要以腐熟猪粪为主,腐熟猪粪样品实测氮素含量为1.86%。根据表2可得水稻替代指数为0.2。有机肥推荐施用量(t/ha)=(总氮素用量×有机肥替代指数)÷有机肥氮素含量÷1000,有机替代后的氮肥用量=总氮肥用量×(1-有机肥替代指数)。因此,晚稻有机肥推荐施用量为1.62t/ha;早稻有机肥推荐施用量为1.57t/ha,晚稻有机替代后的氮肥用量为120.55kg N/ha;早稻有机替代后的氮肥用量为116.78kgN/ha。The organic fertilizer in Dubu Village, Gaoan City, Jiangxi Province is mainly decomposed pig manure, and the measured nitrogen content of the decomposed pig manure sample is 1.86%. According to Table 2, the substitution index of rice can be obtained as 0.2. Recommended application amount of organic fertilizer (t/ha) = (total nitrogen amount × organic fertilizer substitution index) ÷ organic fertilizer nitrogen content ÷ 1000, nitrogen fertilizer amount after organic substitution = total nitrogen fertilizer amount × (1-organic fertilizer substitution index) . Therefore, the recommended application rate of organic fertilizer for late rice is 1.62t/ha; the recommended application rate of organic fertilizer for early rice is 1.57t/ha, and the amount of nitrogen fertilizer after organic substitution for late rice is 120.55kg N/ha; / ha.
同时,本实施例设置两个对照处理,用于与本发明的方法进行对比,具体处理如下:Simultaneously, the present embodiment is provided with two control treatments for comparing with the method of the present invention, and the specific treatments are as follows:
CK(不施氮肥,不施用有机肥)CK (no nitrogen fertilizer, no organic fertilizer)
FP(高氮肥处理,晚稻氮肥用量为195kg N/ha;早稻氮肥用量为156kg N/ha,均不施用有机肥)FP (high nitrogen fertilizer treatment, the amount of nitrogen fertilizer for late rice is 195kg N/ha; the amount of nitrogen fertilizer for early rice is 156kg N/ha, no organic fertilizer is applied)
各处理早晚稻总产量及氮肥利用率分析:Analysis of the total yield and nitrogen use efficiency of early and late rice in each treatment:
从表4可见,与不施氮肥处理相比,应用本发明的方法下早晚稻总产量增加82%。与高氮肥处理相比,在减少41%的氮肥用量条件下,应用本发明的方法可以使早晚稻总产量与高氮肥处理产量持平,无显著差异。It can be seen from Table 4 that compared with the treatment without nitrogen fertilizer application, the total yield of early and late rice increases by 82% under the method of the present invention. Compared with high-nitrogen fertilizer treatment, under the condition of reducing the amount of nitrogen fertilizer by 41%, applying the method of the invention can make the total yield of early and late rice equal to that of high-nitrogen fertilizer treatment without significant difference.
本发明的方法与高氮肥处理相比,水稻地上部总氮积累量差异不显著,但应用本发明的方法使得水稻氮肥农学利用率和表观利用率显著高于高氮肥处理。与高氮肥处理相比,应用本发明的方法使得水稻氮肥农学利用率和表观利用率分别提高2.85kg/kg和8.11个百分点。Compared with the high-nitrogen fertilizer treatment, the method of the invention has no significant difference in the total nitrogen accumulation in the aboveground part of rice, but the application of the method of the invention makes the agronomic utilization rate and apparent utilization rate of rice nitrogen fertilizer significantly higher than the high-nitrogen fertilizer treatment. Compared with the high-nitrogen fertilizer treatment, the application of the method of the invention increases the agronomic utilization rate and the apparent utilization rate of the rice nitrogen fertilizer by 2.85kg/kg and 8.11 percentage points respectively.
上述结果表明,本发明的方法在显著降低氮肥用量的前提条件下,能够保持水稻高产,且明显提高水稻氮肥农学利用率和表观利用率。The above results show that the method of the present invention can maintain the high yield of rice under the precondition of significantly reducing the amount of nitrogen fertilizer, and can obviously improve the agronomic utilization rate and apparent utilization rate of nitrogen fertilizer in rice.
表4不同施肥处理早晚稻年际总产量及氮肥利用率Table 4 Interannual total yield and nitrogen use efficiency of early and late rice under different fertilization treatments
注:同列数字之间如果字母相同表示无显著性差异(P<0.05)Note: If the letters in the same column are the same, there is no significant difference (P<0.05)
实施例2本发明的技术在河南、湖北、黑龙江、江西5年应用情况Embodiment 2 Technology of the present invention is applied in Henan, Hubei, Heilongjiang, Jiangxi 5 years
本实施例按照图9的流程进行,于2013年-2015年分别在河南省原阳县原阳基地、湖北省荆门市五三农场、黑龙江省哈尔滨市道外区民主乡、江西省高安市高安基地进行。其中河南省原阳基地种植制度为小麦-玉米轮作,湖北省五三农场种植制度为水稻-小麦轮作,黑龙江省民主乡种植制度为春玉米单作,江西省高安基地种植制度为双季稻连作。This example was carried out according to the flow chart in Figure 9, and was carried out in Yuanyang Base, Yuanyang County, Henan Province, Wusan Farm, Jingmen City, Hubei Province, Minzhu Township, Daowai District, Harbin City, Heilongjiang Province, and Gaoan Base, Gaoan City, Jiangxi Province from 2013 to 2015. conduct. Among them, the planting system of Yuanyang Base in Henan Province is wheat-corn rotation, the planting system of Wusan Farm in Hubei Province is rice-wheat rotation, the planting system of Minzhu Township in Heilongjiang Province is single cropping of spring corn, and the planting system of Gaoan Base in Jiangxi Province is double cropping rice continuous cropping .
类似于实施例1,种植作物前对每个试验站点往年的产量情况进行调查,根据农户过去5年的平均产量水平以及当地自然气候条件估算可获得产量,根据不同土壤肥力状况估算作物氮肥反应指数,根据可获得产量和作物氮肥反应指数计算出氮肥农学效率,根据上述参数计算出总氮肥用量(见表5)。Similar to Example 1, before planting crops, investigate the yield of each experimental site in previous years, estimate the available yield according to the average yield level of farmers in the past 5 years and the local natural climate conditions, and estimate the nitrogen fertilizer response index of crops according to different soil fertility conditions , the agronomic efficiency of nitrogen fertilizer was calculated according to the available yield and crop nitrogen fertilizer response index, and the total nitrogen fertilizer application amount was calculated according to the above parameters (see Table 5).
为说明本发明的方法的合理性,不同作物有机肥替代指数分别设定为0、0.1、0.2、0.3、0.4、0.5,即每个作物共5个处理(见表5)。In order to illustrate the rationality of the method of the present invention, the organic fertilizer substitution index of different crops is respectively set to 0, 0.1, 0.2, 0.3, 0.4, 0.5, that is, a total of 5 treatments for each crop (see Table 5).
由表5可知,与有机肥替代指数为0处理(即全部施用化肥)比较,河南和湖北冬小麦在有机肥替代指数为0.3时(即有机肥氮素替代30%化肥氮素)小麦4-6季平均产量无显著下降,表明小麦有机肥氮素替代化肥氮素的适宜替代率为30%,证明了本发明涉及的小麦有机肥替代指数为0.3的合理性(见表2);It can be seen from Table 5 that when the organic fertilizer substitution index is 0.3 (that is, organic fertilizer nitrogen replaces 30% of chemical fertilizer nitrogen), wheat 4-6 Season average yield does not have significant decline, shows that the suitable substitution rate of wheat organic fertilizer nitrogen substitution chemical fertilizer nitrogen is 30%, proves that the wheat organic fertilizer substitution index that the present invention relates to is the rationality (seeing table 2) of 0.3;
由表5可知,与有机肥替代指数为0处理(即全部施用化肥)比较,江西双季稻和湖北中稻在有机肥替代指数为0.2时水稻4-6季平均产量无显著下降,表明水稻有机肥氮素替代化肥氮素的适宜替代率为20%,证明了本发明涉及的水稻有机肥替代指数为0.2的合理性(见表2)。It can be seen from Table 5 that, compared with the treatment with an organic fertilizer substitution index of 0 (that is, all chemical fertilizers were applied), the average yield of rice in the 4th to 6th seasons of Jiangxi double-cropping rice and Hubei mid-season rice did not decrease significantly when the organic fertilizer substitution index was 0.2, indicating that rice organic The suitable replacement rate of fertilizer nitrogen to replace chemical fertilizer nitrogen is 20%, which proves that the rice organic fertilizer replacement index involved in the present invention is reasonable (see Table 2).
由表5可知,与有机肥替代指数为0处理(即全部施用化肥)比较,河南夏玉米和黑龙江春玉米在有机肥替代指数为0.3时玉米4-6季平均产量无显著下降,表明玉米有机肥氮素替代化肥氮素的适宜替代率为30%,证明了本发明涉及的玉米有机肥替代指数为0.3的合理性(见表2)。It can be seen from Table 5 that compared with the treatment with an organic fertilizer substitution index of 0 (i.e., all application of chemical fertilizers), the average yield of corn 4-6 seasons did not decrease significantly when the organic fertilizer substitution index was 0.3 in Henan summer maize and Heilongjiang spring maize, indicating that the organic fertilizer The suitable replacement rate of fertilizer nitrogen to replace chemical fertilizer nitrogen is 30%, which proves that the substitution index of corn organic fertilizer involved in the present invention is 0.3 (see Table 2).
表5畜禽粪肥定量替代化肥对作物产量的影响(kg/ha,4-6季平均)Table 5 The impact of livestock and poultry manure quantitatively replacing chemical fertilizers on crop yield (kg/ha, 4-6 season average)
注:同行数字之间如果字母相同表示无显著性差异(P<0.05)Note: If the same letter between numbers in the same row means no significant difference (P<0.05)
虽然,上文中已经用一般性说明及具体实施方案对本发明作了详尽的描述,但在本发明基础上,可以对之作一些修改或改进,这对本领域技术人员而言是显而易见的。因此,在不偏离本发明精神的基础上所做的这些修改或改进,均属于本发明要求保护的范围。Although the present invention has been described in detail with general descriptions and specific embodiments above, it is obvious to those skilled in the art that some modifications or improvements can be made on the basis of the present invention. Therefore, the modifications or improvements made on the basis of not departing from the spirit of the present invention all belong to the protection scope of the present invention.
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