阅读说明：本技术 基于碱性中轻度砷污染土壤改良的可持续生产稻米的方法 (Method for continuously producing rice based on alkaline medium and light arsenic-polluted soil improvement ) 是由 史高玲 高岩 李江叶 樊广萍 刘丽珠 童非 陈未 于 2021-08-24 设计创作，主要内容包括：本发明提供了一种基于碱性中轻度砷污染土壤改良的可持续生产稻米的方法,通过优化施肥、结合叶面喷施硅、硒肥和高效的水分管理措施,有效降低稻米对砷的积累,实现了中轻度碱性砷污染农田的安全性高、效率的安全可持续利用,并综合考虑土壤质量、水稻产量和稻米砷含量的影响,综合设计出一种适宜碱性砷污染土壤的安全生产技术模式。(The invention provides a method for continuously producing rice based on alkaline medium-and-light arsenic-polluted soil improvement, which effectively reduces the arsenic accumulation of rice by optimizing fertilization, combining with foliage spraying of silicon and selenium fertilizer and efficient water management measures, realizes the safe and sustainable utilization of the high safety and the efficiency of medium-and-light alkaline arsenic-polluted farmlands, comprehensively considers the influences of soil quality, rice yield and the arsenic content of rice, and comprehensively designs a safe production technical mode suitable for alkaline arsenic-polluted soil.)

1. A method for sustainable rice production based on alkaline moderate-light arsenic-contaminated soil improvement, which is characterized by comprising the following steps in addition to the conventional rice production steps:

applying ferrous sulfate or ferric sulfate as soil conditioner before ploughing;

uniformly applying a base fertilizer at one time after the soil conditioner is stabilized, wherein the nitrogen, phosphorus and potassium fertilizers in the base fertilizer respectively use ammonium sulfate, calcium superphosphate and potassium sulfate fertilizers, and the base fertilizer is uniformly applied at one time after the soil conditioner is stabilized, wherein the application amount is 60-80 kg/mu;

spraying a foliar silicon fertilizer and a foliar selenium fertilizer simultaneously at the later tillering stage and the early grouting stage of the rice respectively, wherein the spraying amount of the foliar silicon fertilizer stock solution and the foliar selenium fertilizer stock solution per mu is respectively 200 mL/mu;

the rice field is advanced 10-15 days, namely deep ditches are dug 25-30 days before the rice is harvested, and water in the rice field is drained.

2. The method for sustainable rice production based on alkaline moderate-light arsenic contaminated soil improvement according to claim 1, wherein the soil conditioner is applied in an amount of 150 kg/acre.

3. The method for continuously producing rice based on alkaline moderate and mild arsenic-polluted soil improvement as claimed in claim 1, wherein the mass ratio of ammonium sulfate, calcium superphosphate and potassium sulfate in the base fertilizer is 3:3: 1.

4. The method for sustainable rice production based on alkaline moderate and mild arsenic contaminated soil improvement according to claim 1, wherein the base fertilizer is applied at an amount of 70 kg/acre.

5. The method for sustainable rice production based on alkaline mild and moderate arsenic contaminated soil improvement according to claim 1, wherein the concentration of silicon in the silicon fertilizer stock solution is SiO in the range of 10% -20%₂The selenium fertilizer stock solution is Se solution with the concentration range of 1.0-1.5%.

6. The method for continuously producing rice based on alkaline moderately and slightly arsenic-polluted soil improvement as claimed in claim 5, wherein when the manual sprayer is used for spraying, the stock solution of the foliar silicon fertilizer and the stock solution of the foliar selenium fertilizer are both diluted by 200 times and then sprayed, and if the unmanned small airplane is selected for spraying, the stock solution of the foliar fertilizer is diluted by 20 times and then sprayed.

7. The method for continuously producing rice based on alkaline mild-moderate arsenic-contaminated soil improvement as claimed in claim 1, wherein ferrous sulfate or ferric sulfate is applied once before tillage, a rotary cultivator is used for turning over the soil, so that the soil conditioner is fully mixed with the soil of the plough layer, the depth is about 20cm, after the soil conditioner is sown, the soil conditioner is soaked in water for more than 4 hours, the soil is flooded for 3-5cm, and the balance is carried out for 2 days.

8. The method for sustainable production of rice based on improvement of alkaline mild and moderate arsenic-contaminated soil according to claim 1, wherein the variety of rice is Sisi 16.

Technical Field

The invention relates to the field of crop cultivation and safe utilization of polluted land, in particular to a method for continuously producing rice based on alkaline medium-light arsenic-polluted soil improvement.

Background

For the remediation of arsenic contaminated soil, the prior art is mainly divided into three types, namely a physical remediation technology, a chemical remediation technology and a biological remediation technology, wherein the physical remediation technology mainly comprises soil replacement, soil coverage, turnover, attenuation and electric remediation, and although the physical technology takes effect quickly, the treatment cost is high, and the technology is not suitable for the remediation of large-area soil; the chemical remediation technology mainly comprises soil cleaning and soil fixation, wherein the soil cleaning, in-situ cleaning and ex-situ cleaning, easily causes secondary pollution, can damage soil components and has extremely high cost; the soil fixation mainly adopts an As fixing agent to reduce the mobility of As in the soil, the fixing agent is unstable when being used alone, the fixation efficiency needs to be monitored for a long time, the total content of arsenic in the soil cannot be reduced fundamentally, and other conditions of the soil, including acid-base property, redox conditions and the change conditions of coexisting ions and organic matters, need to be further considered in the remediation process.

Bioremediation techniques mainly include microbial remediation and phytoremediation, wherein microbial remediation also mainly reduces the bioavailability of arsenic by reducing its mobility in soil; the phytoremediation mainly utilizes ferns to accumulate arsenic from soil, but the mode depends on the growth conditions required by plants, the safe disposal cost of the arsenic-rich biomass is still high, the effective utilization and production of the soil cannot be realized, and the idle of soil resources is caused.

For the utilization of arsenic-polluted farmland, the prior documents and patents disclose a scheme for comprehensively utilizing the remediation technology to remediate arsenic-polluted soil, for example, the patent document with the publication number of CN 109122136A discloses a method for safely producing rice on medium-light heavy metal-polluted soil, which is to apply a passivator to reduce the heavy metal activity of the soil before rice transplanting, and then spray a leaf surface blocking agent in the period from the tillering stage of the rice to the booting stage and the grain filling stage of the rice; the passivating agent comprises bentonite, gypsum powder, lime, biochar, iron-based biochar, slow-release type iron-based biochar, iron-sulfur-silicon composite biochar, a heavy metal cadmium passivating agent for activating the activity of the soil sulfur reducing bacteria in the rice field, a cadmium-arsenic synchronous passivating agent and the like; the leaf surface blocking agent is acidic silica sol, selenium-silicon composite sol, cerium composite silica sol, ferrous modified selenium sol and the like. When the soil is polluted by arsenic or is polluted by arsenic, cadmium and lead in a composite mode, the passivating agent is a cadmium-arsenic synchronous passivating agent, and the leaf surface blocking agent is selenium-doped nano silica sol and ferrous modified selenium sol.

In the patent, the passivator and the leaf surface blocking agent for safely utilizing the arsenic-polluted soil are also suitable for the safe production of rice on the arsenic and cadmium composite polluted soil. However, arsenic is a non-metallic element whose chemical path in paddy soil is generally opposite to cadmium, and for example, by means of water management, planting low accumulating varieties, and adjusting soil pH, it generally decreases the bioavailability of cadmium in soil while increasing the bioavailability of arsenic in soil. Therefore, in order to simultaneously reduce the accumulation of cadmium and arsenic in soil into rice, the soil passivator and the leaf surface blocking agent used need to have multiple functions, and the production and use costs of the soil passivator and the leaf surface blocking agent are increased. China has a lot of arsenic single element polluted soil, wherein a large area of alkaline arsenic polluted farmland exists in the Subei area of Jiangsu province, and aiming at the arsenic single element polluted soil, some low-cost and high-efficiency rice safe production methods should be preferentially adopted.

In addition, arsenic is generally highly effective in alkaline soils, and therefore, for alkaline arsenic contaminated soils, it is necessary to reduce the soil pH appropriately. The innermost cadmium arsenic passivator mentioned in the patent text of CN 109122136A is a hydrogen ion chemical consuming agent, which results in a further increase in soil pH. Thus, the passivator mentioned in the patent text of CN 109122136A may not be suitable for the improvement of alkaline arsenic contaminated soil.

For the restoration of alkaline soil, the conventional restoration means comprises the improvement by adopting an acid fertilizer, but for the comprehensive improvement and utilization of alkaline arsenic-polluted soil, rice safe production cannot be realized only by the acid fertilizer, so how to comprehensively utilize a physical restoration technology, a chemical restoration technology and a biological restoration technology, improve the alkaline arsenic-polluted soil and realize efficient and low-cost sustainable utilization is the technical problem to be solved firstly by the invention.

Disclosure of Invention

The embodiment of the application provides a method for continuously producing rice based on alkaline medium-and-light arsenic-polluted soil improvement, the accumulation of arsenic in rice is effectively reduced by optimizing fertilization, combining with foliar spraying of silicon and selenium fertilizer and efficient water management measures, the safety and the sustainable utilization of the farmland polluted by medium-and-light alkaline arsenic are realized, the influences of soil quality, rice yield and rice arsenic content are comprehensively considered, and a safe production technical mode suitable for alkaline arsenic-polluted soil is comprehensively designed.

A method for sustainable production of rice based on alkaline moderate to mild arsenic contaminated soil remediation, said method comprising the steps of:

applying ferrous sulfate or ferric sulfate as a soil conditioner before ploughing at one time, preferably, the application amount of the soil conditioner is 150 kg/mu, and primarily adjusting the polluted soil;

the base fertilizer adopts ammonium sulfate, calcium superphosphate and potassium sulfate fertilizers, preferably, the mass ratio of the ammonium sulfate to the calcium superphosphate to the potassium sulfate in the base fertilizer is 3:3:1, the base fertilizer is uniformly applied once after the soil conditioner is stabilized, and the application amount is 60-80 kg/mu, which depends on the fertility of the soil;

spraying a leaf surface silicon fertilizer and a leaf surface selenium fertilizer simultaneously at the later tillering stage and the early grouting stage of rice respectively, wherein the spraying amount of a leaf surface silicon fertilizer stock solution and a leaf surface selenium fertilizer stock solution per mu is respectively 200mL, and the concentration range of silicon in the silicon fertilizer stock solution is 10-20% of SiO₂The selenium fertilizer stock solution is a Se solution with the concentration range of 1-1.5%; preferably, the spraying method comprises the following steps: spraying after four o' clock and half afternoon in sunny days or cloudy days, windless days or less wind power, and spraying by using an artificial sprayer after diluting the leaf fertilizer stock solution by 200 times; if the unmanned small airplane is selected for spraying, diluting the leaf fertilizer stock solution by 20 times;

the method is characterized in that the rice field baking period is advanced by 10-15 days, wherein the rice field baking period refers to a water removing field drying period before rice harvesting, the conventional water draining field drying period is generally carried out 10-15 days before rice harvesting, the advancing 10-15 days in the scheme is 10-15 days ahead of the conventional water draining field drying date, namely, deep ditches are dug 25-30 days before rice harvesting, water in the rice field is drained, and the specific normal rice field baking period is carried out according to local conventional management according to local weather and rice field soil property.

One or more technical solutions provided in the embodiments of the present application have at least the following technical effects or advantages:

according to the invention, through soil passivation regulation, optimized fertilization, combined with water management and synergistic effect, the arsenic content in the final rice is reduced while the yield is ensured, the alkaline arsenic-polluted soil is improved, and the sustainable production of the soil is realized.

Firstly, the soil passivation condition adopts ferrous sulfate and ferric sulfate, on one hand, because the sources are wide and the price is low, and in addition, the ferrous sulfate is sprinkled in the drainage state before the farmland, the ferrous sulfate is oxidized into Fe (III) under the condition of oxygen enrichment, and simultaneously H is released⁺The pH value of the soil can be initially reduced, the adsorption and fixation of arsenic are promoted, the influence of the adsorption on the arsenic of the rice can be limited, iron oxide can be reduced along with the flooding of the rice field, the adsorbed arsenic is released into a soil solution, and after the drainage is finished, under the action of soil microorganisms in an anaerobic area, sulfur and iron form FeS minerals which are co-precipitated with the arsenic; meanwhile, Fe (III) in some micro-oxygen areas can oxidize As (III) into As (V), so that the fixation of arsenic is promoted; in the later rice growth process, the rice rhizosphere secretes oxygen, the formation of an iron film on the root surface is promoted by increasing the content of effective iron, and effective arsenic which can be absorbed by plants is adsorbed and fixed; in addition, sulfur increases the synthesis of glutathione and phytochelatin of the rice root system, promotes the transport of arsenic into root system vacuoles, and reduces the transport of arsenic to the overground part;

secondly, the pH of alkaline soil can be further effectively reduced by applying a physiological acid fertilizer for a long time, the nitrogen, phosphorus and potassium sources in the base fertilizer are respectively ammonium sulfate, calcium superphosphate and potassium sulfate, and sulfur in the fertilizer can also be cooperated with a soil conditioner to reduce the effectiveness of arsenic in the soil while the pH of the alkaline soil is improved;

finally, the water management synergistically reduces the arsenic absorption capacity of the rice root system, the filling period is a key period for the arsenic accumulation of rice, and the effectiveness of arsenic in soil can be effectively reduced by advancing the field-baking period by 10-15 days, so that the absorption of the rice root system to arsenic is reduced. Under the condition of drainage, the oxidation-reduction potential of the soil is raised, the paddy soil is changed from an anaerobic state to an aerobic state, arsenic in the soil is mainly As (V) under the aerobic condition, pentavalent arsenic is easily adsorbed to iron manganese oxide and soil colloid particles, and can also react with iron to form ferric arsenate form coprecipitation, so that the bioavailability of the arsenic is reduced. In addition, the rice absorbs trivalent arsenic through a silicon transporter, absorbs pentavalent arsenic through a phosphorus transporter, the rice is a silicon-loving plant, and the root system of the rice has a developed silicon absorption and transport system, so that the absorption capacity of the root system of the rice on the arsenic is reduced after the trivalent arsenic is converted into the pentavalent arsenic.

In conclusion, the water management measures adopted by the method are based on soil passivation and base fertilizer optimization, and the method can play an obvious synergistic effect with other measures only by baking the field 10-15 days in advance under the normal field baking period condition, iron can be oxidized into iron oxide under the aerobic condition, and the adsorption of the iron on arsenic is further promoted. Therefore, based on optimized fertilization and water management, the application amount of ferrous sulfate or ferric sulfate serving as a passivating agent is controlled within a reasonable range, and the arsenic content in rice is further reduced while the rice yield is ensured;

as a more preferable scheme, on the basis of the operation, the accumulation amount of arsenic in rice can be further reduced by increasing the operation of leaf surface resistance control, and the specific principle is as follows: the structure of silicon is similar to that of trivalent arsenic, and by utilizing the co-transport characteristic of Si and As, the expression of Si/As absorption transport protein can be inhibited by spraying silicon fertilizer on the leaf surface, the absorption and the transport of the arsenic by rice are reduced, and the accumulation amount of the arsenic in the rice is reduced.

Detailed Description

The invention will be further illustrated with reference to the following specific examples. These examples are only illustrative and not intended to limit the scope of the present invention. The experimental methods of the following examples, in which specific experimental conditions are not specified, are generally performed according to conventional conditions.

The technical scheme of the invention is further explained by a specific embodiment of treating the soil (located in a certain county of a salt city) of a typical alkaline arsenic-polluted farmland in Jiangsu province.

The underground water level of the implementation area is higher, 2.0-3.0m throughout the year and 1.0-1.5m in summer; the implementation area belongs to the agricultural area of the Haizhou country polder; the implementation area is oil soil; the plowing ground is 5.19 ten thousand mu, which is mainly a paddy field. The south edge of the warm zone (climate, sunshine and rainfall) has obvious marine climate characteristics due to the fact that the people are endangered in the yellow sea, the weather is hot and rainy due to the fact that the people are clear all the year round and are affected by the ocean season wind from the east in summer; the method is influenced by the wind in the south and the lower quarters of the north in winter, and mainly adopts dry and cold weather; the spring and autumn are in the period of alternative conversion of the wind in the north and south, and the weather is changeable in temperature and humidity; the average annual sunshine is 2402.7 hours, the average annual air temperature is 14.5 ℃, the average annual rainfall is 883.6 mm, the annual evapotranspiration is 1393.6-1863.1 mm, and the frost-free period is about 211 days.

102 soil samples are collected before project implementation, and detection results show that the soil in an implementation area is alkaline, the pH value of the soil is greater than 8.2, and the average value is 8.24; only arsenic in the five heavy metals of arsenic, cadmium, lead, chromium and mercury exceeds the farmland soil pollution risk value (20mg/kg, GB15618-2018) specified in China, the average content of arsenic in the soil in the implementation area is 20.7mg/kg, and the pollution of the whole area is relatively uniform.

Each comparative example or example is taken as a treatment group, 3 repetitions are arranged in one treatment group, the implementation area of each repetition is 25 square meters (5 meters in length and 5 meters in width), the cells of different treatment groups are randomly distributed, the ridges among the cells are 50cm, the roads and ditches among two rows of cells are 1 meter, and the width of the protection row is 1 meter. The ridges between the cells are covered with a film to prevent water leakage. The rest of the field management aspects and the like which are not mentioned in each embodiment refer to the conventional management mode of the field.

The content of five heavy metals in the irrigation water collected before implementation is far lower than the farmland heavy metal limit value specified in China, the irrigation water heavy metal limit value standard is reached, and the pH value is 7.5-8.2; the arsenic content is lower than 9 mug/L.

In the implementation process, the heavy metal contents of the used input products, namely arsenic, cadmium, lead, chromium and mercury, are far lower than the related limit values specified by the state, in each input product, only 0.00006% of arsenic is detected from ferrous sulfate, 0.00004% of arsenic is contained in the compound fertilizer, and the rest fertilizers and soil conditioners are not detected, so that the influence of the input products on the final test result is negligible.

The different comparative examples and examples will pass the following key technical point combination tests, the differences being detailed in table 1.

Regarding the planting species: examples 1 to 3 and examples 1 to 4 were all Siza 16;

regarding soil conditioners: in comparative example 1, no soil conditioner is used, in comparative examples 2 to 3 and examples 1 to 4, the specific soil conditioner components shown in the following table 1 are respectively used for soil conditioning, the application amount is 150 kg/mu, the soil conditioner and the soil are fully mixed by rotary tillage once before rice planting, the depth is about 20cm, after the soil conditioner is sowed, the soil conditioner is soaked in water for more than 4 hours and is flooded by 3 to 5cm, and the materials are dissolved in the water and diffused into the soil and are balanced for 2 days.

Regarding the base fertilizer: the base fertilizer in the comparative example 1 is applied according to the conventional planting mode of local rice, and specifically, the compound fertilizer (N-P) is adopted₂O₅-K₂O-16-8) is used as a base fertilizer, and the application amount is 40 kg/mu; in comparative examples 2 to 3 and examples 1 to 4, ammonium sulfate was selected as a nitrogen fertilizer, calcium superphosphate was selected as a phosphate fertilizer, and potassium sulfate was selected as a potassium fertilizer, according to the following formula 3:3:1, the total application amount of the base fertilizer is 70 kg/mu; the base fertilizer is uniformly applied after the soil conditioner is stabilized, and is uniformly applied in the paddy field before the paddy is planted;

concerning the tillering fertilizer and the jointing-pulling and spike-bearing fertilizer: the comparative example and the example both adopt urea, the application amount of the tillering fertilizer is 20 kg/mu, the jointing and booting fertilizers are 15 kg/mu, and the conventional operation is adopted;

regarding foliar fertilizers: in comparative examples 1 to 3 and examples 1 to 2, no foliar fertilizer was applied; in examples 3 to 4, the leaf fertilizer containing silicon and selenium is sprayed once respectively at the late tillering stage and the early grouting stage of rice, and SiO with the mass fraction of 20 percent is sprayed each time₂The leaf surface silicon fertilizer stock solution is 200 mL/mu; spraying 200 mL/mu of a leaf surface selenium fertilizer stock solution with the mass fraction of 2% Se; diluting the foliar silicon fertilizer and the foliar selenium fertilizer respectively by 2Spraying evenly by a sprayer after 00 times, wherein spraying is carried out after five hours in the afternoon every time;

regarding moisture management: comparative examples 1-3 moisture management was performed according to local routine; in examples 1 to 4, the harvest time of the field is advanced by 10 days, and deep ditches are dug for drainage.

Table 1:

sample collection and measurement

Collecting soil samples at the late tillering stage (8 months and 8 days) and the mature stage (11 months and 1 day) of rice respectively, collecting five point samples in each cell by adopting an S-shaped point distribution method, mixing the five point samples into one sample, and analyzing and determining the content of soil organic matters and the content of soil available arsenic. And harvesting plant samples of each cell in the rice maturation period, measuring the harvested yield, and analyzing and measuring the arsenic content in the rice. The soil organic matter is measured according to a potassium dichromate volumetric method (GB 9834-88), the arsenic content in the rice is measured by adopting an inductively coupled plasma mass spectrometry method (GB 5009.268-2016), the soil effective arsenic is extracted by 1mol/L ammonium chloride and then is detected by using atomic fluorescence, and the measurement results are shown in the table 2, and the influence of different treatments on the rice yield, the arsenic content of the rice, the effective arsenic content of the soil and the soil organic matter content is realized.

Table 2:

results and analysis

Regarding the rice yield and the arsenic content of rice, the arsenic content of rice in both examples is lower than 0.10 mg/kg, and is significantly lower than that in comparative examples 1-3, which shows that the scheme in examples 1-2 has significant effect on reducing the accumulation of arsenic content of rice, and has no significant effect on the rice yield; therefore, in the invention, the soil conditioner, the optimized fertilization and the water management are combined with the leaf surface resistance control agent to synergistically and effectively reduce the arsenic content of the rice; the cadmium, mercury, lead and chromium contents of all the sample rice are far below the national specified limit values, and are not described in detail.

With respect to the change in soil organic matter content over the period of time the project was performed, it can be seen from the table that the soil organic matter content in each example did not change significantly under different treatments from the beginning to the end of the project. The organic matter is an important index reflecting the soil fertility, so the result of the organic matter shows that the soil fertility of the project area has no obvious change in the implementation process of the project. The different optimized fertilization and soil conditioner combinations in the scheme have no obvious influence on the organic matter content of the soil, and the sustainable production and utilization of the alkaline medium-light arsenic-polluted soil can be realized.