CA1047784A - Soil treatment method - Google Patents

Soil treatment method

Info

Publication number
CA1047784A
CA1047784A CA218,048A CA218048A CA1047784A CA 1047784 A CA1047784 A CA 1047784A CA 218048 A CA218048 A CA 218048A CA 1047784 A CA1047784 A CA 1047784A
Authority
CA
Canada
Prior art keywords
algae
soil
nitrogen
growth
nutrients
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired
Application number
CA218,048A
Other languages
French (fr)
Other versions
CA218048S (en
Inventor
William W. Walker (Jr.)
Patricia L. Foster
Samuel Fogel
Paula Schenck
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
American Bioculture Inc
Original Assignee
American Bioculture Inc
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Family has litigation
First worldwide family litigation filed litigation Critical https://patents.darts-ip.com/?family=23723796&utm_source=google_patent&utm_medium=platform_link&utm_campaign=public_patent_search&patent=CA1047784(A) "Global patent litigation dataset” by Darts-ip is licensed under a Creative Commons Attribution 4.0 International License.
Application filed by American Bioculture Inc filed Critical American Bioculture Inc
Application granted granted Critical
Publication of CA1047784A publication Critical patent/CA1047784A/en
Expired legal-status Critical Current

Links

Classifications

    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G33/00Cultivation of seaweed or algae
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/80Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in fisheries management

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Marine Sciences & Fisheries (AREA)
  • Environmental Sciences (AREA)
  • Soil Conditioners And Soil-Stabilizing Materials (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Fertilizers (AREA)
  • Cultivation Of Plants (AREA)

Abstract

ABSTRACT OF THE DISCLOSURE
Culturing an algae with known flocculant production capability on the soil for the purposes of aggregating soil particles is disclosed.
According to the disclosure flocculant producing algae are grown in liquid culture as disclosed in United States Patent No. 3,958,364. The nitrogen in the culture medium is maintained so that cellular nitrogen does not fall below 10%. The algae are then inoculated onto soil which is provided with supplemental nutrients and moisture sufficient to produce a multiplication on the order of several hundred fold. The nutrients other than nitrogen are provided in sufficient quantity to permit a further period of growth during which algal flocculants are produced which have the property of binding soil particles into workable aggregates.

Description

. --~047784 As in our United States Patent No. 3,958,364, the invention relates to the production and use of algae as a source of polymeric materials displaying StrQng flocculating activity.
According to the invention, soil to be treated is inoculated with flocculant producing algae and grown in the presence of nitrogen, other nutrients and sufficient moisture so as to cause the algae to multiply on the soil. After a period of multiplication, the algae are cultured for a further period of time under conditions which promote flocculant production.
These algal flocculants improve soil structure by binding soil particles into workable aggregates.
More particularly, the present invention provides a method of conditioning soil by binding the particles thereof into small workable aggregates which comprises inoculating the soil with a flocculant producing algae, maintaining in the inoculated soil available nitrogen, other nutrients and moisture in sufficient quantites so that the algae continue to multiply on the soil for a period of time until a predetermined population density is reached, and thereafter maintaining in the inoculated soil plant nutrients other than nitrogen in quantities which are not growth limiting so that the algae continue to grow in a nitrogen deficient state in which soil aggregating compounds are produced.
As indicated in our United States Patent No. 3,958,364 utilization of bacterial polysaccharides as flocculating agents, especially for aggregating soil particles, thereby improving soil structure is known. United States Patents such as No. 2,780,888 and No. 2,901,864 teach the application of these bacterially produced biopolymers to the soil as a means for promoting soil aggregation, thereby producing a granular structure which is sufficiently porous to allow air, water, and plant roots to penetrate through the soil.
According to these patents, sucrose as a raw material is converted to dextran by inoculating a nutrient medium containing sucrose with a dextran synthesizing bacteria such as Leuconostoc mesenteroides. The dextran may ___ _ ___ _____ be used in granular form or in solution in an aqueous medium and applied to .

soil .
In addition to the foregoing, long chain synthetic polymers useful as soil conditioning agents which are capable of aggregating soils and useful for other applications where flocculating activity is required, are disclosed in the art. Examples of synthetic polymeric materials useful for increasing aggregation in surface soil are disclosed in Hedrick et al patent no. 2,651,885. According to the Hedrick et al patent, water soluble polymeric electrolytes having a molecular weight of at least 10,000, including polymers of acrylic acid, copolymers of maleic anhydride and the like are provided. These polymeric materials are effective in improving soil structure but their use has been somewhat limited in view of their high cost.
Various researches have also recognized that algae found in the soil influence the soil in a variety of ways. Shields and Durrell (L. M.
Shields and L. W. Durrell, BOTANICAL REVIEW, 30, 1964, pp. 92-128) in a systematic and thorough review of soil algae literature have described eight major contributions which algae make to soil. These include:
1. colonization of denuded soils with formation of a soil crust which acts as a substrate for later successional species; that is, seed germination on an algae substrate.
2. formation of a soil humus resulting from the microbial decomposition of algae and subsequent formation of protein-polysaccharide-clay and sand aggregates.
3. improving water infiltration through algal covered surfaces as a result of water stable aggregate formation as well as a reduction of runoff and erosion.
4. maintenance of a reserve supply of nutrients in a partially available form for higher plants.
5. prevention of nitrate nitrogen from leaching and ammonia nitrogen from volatilizing by converting them to organic formsO
6. fixation of atmospheric nitrogen by blue-green soil algae with significant increases noted in soil nitrogenO

., .
~ -2-
7. production of both nitrogen and oxygen in rice agriculture.
8. maintenance of high soil moisture levels as a result of surface cover through which germinated seeds can penetrate.
It has also been observed that algae organic matter occuring on soil contribute to soil structure by binding soil particles. It has been reported that surface algae growths in Oklahoma, Kansas, and Texas reduced erosion losses due to their aggregating effect on soils. Water infiltration was increased in algae covered plots over exposed surfaces. Algal invasion of the rain-crust has been seen to result in improved infiltration, decreased erosion, and has aided in the establishment of plant seedlings under vigorous desert conditions.
OBJECTS OF THE INVENTION
_____ _ _______ The primary object of this invention is the provision of a treatment method involving the application of flocculant producing algae to the soil for the purpose of promoting soil particle aggregation.
A related object of the invention is the provision of a soil ~ -treatment method involving the growth of flocculant producing algae on the soil, thereby producing multiplication of the algae and production of flocculants, These and other objects achieved by the present invention, are based on our discovery that algae can be cultured so as to favor the production of flocculants. The present invention further involves the production of algae which are inherently good flocGulant producers, culturing these algae under conditions favoring cell multiplication on the soil until a desired population density is reached and thereafter continuing the culturing under conditions which favor the production of flocculants for a time sufficient to achieve the desired soil aggregating properties.
These and various other objects of the invention will become apparent from the following detailed description of the invention when taken in reference with the accompanying drawings in which:
; Figure 1 is a plot showing the increase in the ratio of chlorophyll ~ -3-`
iO4 versus time;
Figure 2 is a plot illustrating algae growth on unfertilized soil for various application levels;
Figure 3 is a plot illustrating algae growth on highly fertilized soils for various inoculation levels.
Figure 4 is a plot of algae growth for various fertilizer levels;
` Figure 5 is a plot of percent change in soil particle size versus pounds of chlorophyll extracted from flocculant producing algae grown on soil, and Figure 6 is a plot of penetration resistance versus pounds of chlorophyll extracted from flocculant producing algae grown on soil.
The ability of the algae to significantly improve soil structure - depends upon proper application of nutrients and upon the maintenance of soil isture within appropriate limits. As taught in our United States Patent No. 3,958,364, when nitrogen levels are high enough so that cellular nitrogen is at about 10% by weight, and the cells have an additional supply of other nutrients, Chlamydomonas mexicana are maintained in a vegetative growth state in which the cells rapidly multiply. By proper application of nutrients to the soil, dosages of from .5 to 5 lbs/acre of cells having a 10% nitrogen level will be maintained in the vegetative state for a number of days and the cell populations will increase several hundred fold resulting in from about 50 to 200 pounds of algae per acre. Toward the end of this period, cellular nitrogen levels fall to about 5% and the algae shift to a flocculant pro-duction phase during which up to 80% by weight of cell substance or about 25 to 160 pounds is an active flocculant. Significant soil improvement results even at the lower end of this range.
Example I
In order to show the production of polysaccharide flocculants by algae on the soil, a sterile soil consisting of 70% sand and 30% clay, was prepared with no organic material being present in the sample so that the effect of background matter was eliminated. The samples were inoculated 1047~84 with a fertilizer medium formulated as disclosed in our United States Patent No. 3,958,364. Nitrogen as NH4N03 was present in amount of 9.3 pounds N/acre and soil mositure was adjusted to 15% moisture content. Chlamydo nas - mexicana was sprayed onto this soil at a dose level of about 0.7 lbs of algae per acre. Growth on the soil was monitored by analysis of chlorophyll a and soil polysaccharide ~flocculant) over a twelve day period. Surface soil samples were obtained daily using a 1 cm diameter cork borer. Polysaccharide analysis was by the procedure outlined in our United States Patent No.
3,958,364. Chlorophyll a was determined by the method described in Standard Methods for Examination of Water and Waste Water, 13th Edition, modified by ___ _ _ _ _ _ _ , extraction in methanol rather than acetone. The ratio of saccharide to chlorophyll is plotted in Figure 1. As can be seen in Figure 1, the ratio of saccharide to chlorophyll a increased by day 4 and continued to increase with time as increased flocculant was produced and accumulated. Based on the nitrogen applied and the pounds of algae determined, the algae had a 10%
nitrogen content until day 3 and became progressively more nitrogen deficient with time.
Exam~

_ The following trials show the influence of various factors on soil 2Q algae growth and consequent soil structure improvement. In carrying out the trials, the algal species Chlamydo nas mexicana was cultured as described _ in our United States Patent No. 3,958,364 in liquid culture medium with sufficient nitrogen in the medium so that cellular nitrogen was maintained above 10% so that the cultures as applied to the soil were in a vegetative state. The primary variables in the trials were algae inoculum doses (3 levels), fertilizer doses (3 levels), and irrigation methods and rates C4 levels). A total of 26 combinations of the above factors were investigated, each treatment being replicated three times. The irrigation methods employed were drip and spray. The field plot plan was a split plot, randomized block design. Each test plot was 81 ft in areau Test plot soils were of a loam or sandy loam texture.

1~47784 Chorophyll determination was used as the basic measurement of algae growth. Difficulties were encountered in measuring algae growth in the field plotsO Although chlorophyll content is correlated with algae population densities to a certain degree, this relationship does not give a complete picture of population density of cultures in the flocculant producing state since chlorophyll content is decreasing in these cultures. Thus, it can be expected that algae in much larger numbers were present in inoculated plots during the later days of the trials than the data shows. Ten surface samples were obtained per plotO These were pooled, extracted and the pounds of chlorophyll a and chlorophyll b determined. Samples were taken approximately every three days for the duration of the trial (one month)O The pounds of algae were computed based on a known average chlorophyll content of 1~75%o The basic measurement of soil structure utilized was wet sieving, a test designed to differentiate the water stability of soil aggregates under mechanical agitation. The parameter derived from the results of the wet sieving test is mean particle size, calculated as the weight average diameter of the tested soil as distributed between sieves of specified sizes. Measure-ments of mean particle size on field samples were taken before and after the algae growth phase of the example. A secondary indication of soil structure was derived from penetration resistance measurements. With the aid of a commercially available soil Penetrometer, produced by Soil Test, Inc., Evanston, Illinois, determinations of the force necessary to push a conically-tipped probe a distance of two inches into dry soil were madeO This measure-ment is an indication of soil compaction and moisture, both of which are related to soil structure.
Although other irrigation methods may be employed, of the methods we have examined we have found that spray irrigation provides optimal algae growth and soil structure improvements. An application rate of approximately 1 inch/day of water was found to be optimal for the mid-summer Arizona 3Q temperatures and humidities in which the tests were conducted. The results indicate that algae growth on soil is closely coupled with the dynamics of soil, water and nitrate transport. As is recognized in the art, excessive watering rates lead to nutrient depletion through leaching, while deficient watering rates lead to high surface temperatures and growth retardation.
~nder less severe climate conditions, the watering requirements would be lower and of less critical determination in the overall processO As a guide, it can be said that soil moisture should be held at between about 40% and 80% of moisture holding capacity. This level of moisture may be most easily main-tained with the use of irrigation during seasons of moderate temperatures and high humidities. Irrigation methods which provide for uniform dispersion over the area treated should be employed.
The algae growth data obtained with the optimum watering scheme are shown in Figures 1, 2 and 3. Between days 12 and 17 in the example, the water system was shut off. On day 17 irrigation was resumed and the plots re-inoculated. An analysis of variance indicates that algae levels were signi-ficantly influenced by both inoculum and fertilizer dose levels (95% level).
In order to demonstrate that the inoculated algae species was the one that actually grew, the effect of inoculum size on subsequent algae growth on unfertilized plots was studied. Results are presented in Figure 2. These data show that the amount of algae present was greatest on those plots inoculated with the highest algae levels. Further, these results indicated that the inoculated algae was chiefly responsible for the observed growth.
It is surmised that growth on the uninoculated plots result from a combination of factors, namely from contamination of the inoculated plots as well as with the growth of indigenous algae.
Figure 3 shows the effect of fertilizer on algae growth on plots inoculated with 0.5 and 5 pounds per acre of C. mexicana. The results show that between day 3 and 12 the density of algae was greatest on the inoculated plots ~0.5 and 5 pounds per acre). It can also be seen that 0.5 pounds per acre inoculum resulted in final algae densities equal to that of the 5 pounds 3~ inoculum. The decrease in chlorophyll levels of day 12 is attributed to the commonly observed effect of nitrogen limitation on algae growth. It is known ~ .

~)47784 that a nitrogen limitation (in this case caused by cellular uptake and leach-ing~ results in a decrease in a chlorophyll content of algae. It can also be seen from data present in Example I and from our United States Patent NoO
3,958,364 that C. mexicana biomass continues to increase when cells are placed under a nitrogen limitation. As a result, estimations of biomass based on chlorophyll determinations will be low during nitrogen deficiencyO The small differences between the 0 algae dose and the .5 and 5 lb/acre dose seen between days 17 to 31 can be attributed to the gradual buildup of the algae ~ flora during the first two weeks of the experiment.
- 10 The effect of varying nitrogen fertilizer levels on algae growth is shown in Figure 4O The results clearly show an effect on algae densities.
For standing crops of algae less than about 25 lb/acre, doubling times on the order of .5 - 8 days were observed. For standing crops between 50 and 150 lb/acre, doubling times on the order of eight days were observed in the fertilized plots. The decrease in growth rate with increasing population can be explained by a number of factors, including depletion of nitrogen supply and surface crowding effects. The algae growth data indicated that with proper watering fertilization and inoculation at about .5 lb/acre, standing crops of algae of 50-lO0 lb/acre within a period of one to three weeks are achievedO As will be brought out hereinbelow, crops within this range of magnitude produce significant improvement in soil structure.
Figures 2 and 3 also show that algae grew on plots which were not inoculated in considerable quantities. Samples of the algae which grew on the uninoculated plots were cultured in the laboratoryO The algae were identified as C amydomonas mexicana and Nostoc commune, a nitrogen fixing blue-green algae. It is surmised that contamination from the inoculated plots occurred during spray inoculation, although species of Chlamydomonas are native to the area where the tests were conducted and may have initially been present in the soilO However, the soil structure effects noted during 3Q the trials were mainly associated with the inoculated cultures as shown by penetration and particle size measurementsO

~047 784 The results of soil structure measurements are shown in Figures 5 and 6. Figure 5 is a plot of the percent change in mean particle size (0-3" depth sample) vsO total density of chlorophyll ~lb/acre). The data shown are typical values for each spray irrigated treatmentO A least squares fit of the date indicates that an algae growth of 100 lb/acre can be associated with an 28% increase in mean particle size.
This change in size produces a significant increase on soil pore size, and thus, improved soil aeration and infiltration capacity.
The results of the penetration measurements are shown in Figure 6.
A least squares fit of the data indicates that a growth of 100 lb/acre corresponds to a 32% decrease in penetration resistance, as compared with no algae growth. The measurements were made two weeks after the irrigation system had been shut off. All plots were essentially bone dry, so the measurements reflect primarily soil compaction.
The results indicate that field-grown algae can have a significant effect on sail structure. Under controlled irrigation and with proper fertilization, sufficient algae can be grown from an inoculum of 0.5 lb/acre to result in a 28% increase in particle size and a 32% decrease in soil penetration resistance within a period of about three weeks. With these improvements in soil structure, marked increase in soil pore space, infiltra-tion rates and improved soil aeration will result.
Chart I shows the increases in average particle size (mm) in all plots inoculated at 0, .5 and 5 pounds per acre under the optimal irrigation scheme.
CHART I

Nitrogen Dose Inoculum Algae Dose (lb N/acre) (lb/acre) 0 0.5/acre 5/acre _ _ _ _ _ _ _ __ _ _ _ .
0 .008 .069 .043 - * *O079 .023 oll6 O054 * These algae and fertilizer combinations were not investigated.

_g_ ~047784 Plots were spray irrigated with 1 inch of water per day. All values are arithmetic means of three replications measured in mm. Average particle size before treatment was .344 mm.
From Chart I it can be seen that the inoculated cultures produce a significant effect on particle size as compared with the indigenous algae populations. Based on our analysis of the data we have gathered we have concluded that inoculum levels as low as 0.05 lb/acre produce growth levels similar to those disclosed herein and consequently will significantly influence soil structure.
lQ In summary, flocculant producing algae of which a preferred genus is Chlamydomonas, especially the species Chlam~_ monas me ana are cultured in nurse pools on liquid nutrient medium under conditions which produce logarithmic or exponential growth. The cultures are harvested and applied to fields at application densities between .05 and 0.5 pounds per acre. If desired to facilitate handling, transportation and application at the required density, excess water may be removed by centrifuging, however, cultures of at least 0.5 grams/liter can be obtained in nurse pools using the nutrient mediums and culturing procedures described in our United States Patent No.
3,958,3640 Application to fields should be made in a manner best suited to 2Q obtain substantially uniform dispersion of the algae over the plot being treated and may be by aerial spray or by application in admixture with irrigation water.
The amount of nitrogen and other nutrients added to the field will vary somewhat due to a large number of factors such as surface runoff, competition with other forms of plant life and nutrients in the soil but as a starting point it may be stated that lO pounds of nitrogen should theore-tically produce lO0 pounds of algae with a cellular nitrogen content of 10%.
In field trialsJ as indicated by results included herein and other data, we have found that applications from 20 to 60 pounds of nitrate nitrogen per 3Q acre to previously untreated and unfertilized fields results in a lO0 fold ; or greater increase in the amount of algae at initial inoculation rates of ,.. ~

, ~47784 about Q.5 to 5 pounds per acre when soil moisture is maintained at between 40 to 80% of moisture holding capacity. During the course of growth in the soil under this regime, the algae shift from a vegetative phase of growth to a flocculant producing phase as the cells become nitrogen deficient, provided moisture is present in adequate quantities and other nutrients are not limiting. Increase in particle size, and resultant increase in soil pore space, infiltration capacity and soil aeration result.

Claims (4)

THE EMBODIMENTS OF THE INVENTION IN WHICH AN EXCLUSIVE
PROPERTY OR PRIVILEGE IS CLAIMED ARE DEFINED AS FOLLOWS:
1. A method of conditioning soil by binding the particles thereof into small workable aggregates which comprises inoculating the soil with a flocculant producing algae, maintaining in the inoculated soil available nitrogen, other nutrients and moisture in sufficient quantities so that the algae continue to multiply on the soil for a period of time until a predeter-mined population density is reached and thereafter maintaining in the inoculated soil plant nutrients other than nitrogen in quantities which are not growth limiting so that the algae continue to grow in a nitrogen deficient state in which soil aggregating compounds are produced.
2. A method according to claim 1 wherein the algae is of the genus Chlamydomonas.
3. A method according to claim 2 wherein the algae is Chlamydomonas mexicana.
4. A method according to claim 3 wherein rate of application of algae is at least .5 lb dry weight per acre with nitrogen being provided so that it is present in the soil in amounts of at least 20 lb per acre at the time of algae application.
CA218,048A 1974-01-17 1975-01-16 Soil treatment method Expired CA1047784A (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
US43433274A 1974-01-17 1974-01-17

Publications (1)

Publication Number Publication Date
CA1047784A true CA1047784A (en) 1979-02-06

Family

ID=23723796

Family Applications (1)

Application Number Title Priority Date Filing Date
CA218,048A Expired CA1047784A (en) 1974-01-17 1975-01-16 Soil treatment method

Country Status (13)

Country Link
JP (1) JPS50105455A (en)
AU (1) AU508621B2 (en)
BE (1) BE824455R (en)
BR (1) BR7500256A (en)
CA (1) CA1047784A (en)
DE (1) DE2501856A1 (en)
ES (1) ES433859A1 (en)
FR (1) FR2258127B2 (en)
GB (1) GB1501491A (en)
IL (1) IL46450A0 (en)
IT (1) IT1049345B (en)
NL (1) NL7500536A (en)
ZA (1) ZA75342B (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AT399078B (en) * 1993-07-16 1995-03-27 Edinger Othmar BIOLOGICAL METHOD FOR IMPROVING AGRICULTURAL SOILS
CN111819938A (en) * 2020-05-06 2020-10-27 中国水利水电科学研究院 Method for reducing soil moisture evaporation and anti-evaporation additive

Also Published As

Publication number Publication date
ES433859A1 (en) 1976-11-16
BR7500256A (en) 1976-10-26
IT1049345B (en) 1981-01-20
FR2258127A2 (en) 1975-08-18
IL46450A0 (en) 1975-04-25
FR2258127B2 (en) 1977-10-14
BE824455R (en) 1975-05-15
GB1501491A (en) 1978-02-15
AU7731475A (en) 1976-07-15
ZA75342B (en) 1976-01-28
NL7500536A (en) 1975-07-21
JPS50105455A (en) 1975-08-20
DE2501856A1 (en) 1975-07-24
AU508621B2 (en) 1980-03-27

Similar Documents

Publication Publication Date Title
US3969844A (en) Soil treatment methods
Dommergues et al. Non-symbiotic nitrogen fixation in the rhizospheres of rice, maize and different tropical grasses
EP0246281B1 (en) Microbial compositions and methods for treating soil
CN110305671B (en) Soil biological improver for continuous cropping of greenhouse vegetables and preparation and use methods thereof
Roper Field measurements of nitrogenase activity in soils amended with wheat straw
Guidi et al. Variations of soil structure and microbial population in a compost amended soil
Martin Status Report on Soil Conditioning Chemicals. I.
CN111499435A (en) Special solid organic fertilizer for tobacco and preparation method thereof
CN115340968A (en) Novel application and method of pseudomonas spinosa, pseudomonas spinosa 21.1.9.2-14 and product thereof
Ball et al. Assessment of the potential of a novel newspaper/horse manure-based compost
Quastel Soil conditioners
CN113892317B (en) Application of rhamnolipid in treatment of saline-alkali soil and improvement of yield of cotton in saline-alkali soil
CN109365506B (en) Heavy metal passivator suitable for medium-alkaline cadmium contaminated soil and application thereof
CN107821088B (en) Corncob fermentation substrate and preparation method and application thereof
CA1047784A (en) Soil treatment method
Gaffar et al. Effect of farmyard manure and sand on the performance of sorghum and sodicity of soils
Al‐Harbi et al. Impact of irrigation regime and addition of a soil conditioner on tomato seedling growth
Preve et al. Influence of mine spoil type, fertilizer, and mycorrhizae on pines seeded in greenhouse trays
JP2002212560A (en) Method for preparing super high-density antimicrobial basic material
Girma et al. Influence of manuring on certain soil physical properties in the Middle Awash area of Ethiopia
CN110373209A (en) A kind of method of the dedicated water-retaining agent of sweet potato and water-saving culture sweet potato
KHAN et al. Quantifying maize phenology using beneficial microorganisms and residue management under deep tillage system.
LU502870B1 (en) Compound Microbial Inoculum for Saline-alkali Soil Improvement, Preparation Method and Application Thereof
JPH0798712B2 (en) Multi-stage fermentation method of oil dregs and fermentation organic fertilizer
CN114788485B (en) Rice-algae symbiotic management method for promoting straw decomposition