NZ758696B2 - Method for creating nutrient rich biologically active soils and horticulture media with predetermined characteristics - Google Patents
Method for creating nutrient rich biologically active soils and horticulture media with predetermined characteristics Download PDFInfo
- Publication number
- NZ758696B2 NZ758696B2 NZ758696A NZ75869617A NZ758696B2 NZ 758696 B2 NZ758696 B2 NZ 758696B2 NZ 758696 A NZ758696 A NZ 758696A NZ 75869617 A NZ75869617 A NZ 75869617A NZ 758696 B2 NZ758696 B2 NZ 758696B2
- Authority
- NZ
- New Zealand
- Prior art keywords
- media
- porosity
- nutrients
- aging
- meal
- Prior art date
Links
- 235000015097 nutrients Nutrition 0.000 title claims abstract description 85
- 239000002689 soil Substances 0.000 title claims abstract description 85
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- 238000000034 method Methods 0.000 claims abstract description 89
- 230000032683 aging Effects 0.000 claims abstract description 71
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 43
- 239000001301 oxygen Substances 0.000 claims abstract description 43
- MYMOFIZGZYHOMD-UHFFFAOYSA-N oxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 claims abstract description 43
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- 239000002609 media Substances 0.000 claims description 206
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Classifications
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05B—PHOSPHATIC FERTILISERS
- C05B17/00—Other phosphatic fertilisers, e.g. soft rock phosphates, bone meal
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
- C05D9/00—Other inorganic fertilisers
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F11/00—Other organic fertilisers
- C05F11/08—Organic fertilisers containing added bacterial cultures, mycelia or the like
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/20—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation using specific microorganisms or substances, e.g. enzymes, for activating or stimulating the treatment
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/80—Separation, elimination or disposal of harmful substances during the treatment
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/90—Apparatus therefor
- C05F17/964—Constructional parts, e.g. floors, covers or doors
- C05F17/971—Constructional parts, e.g. floors, covers or doors for feeding or discharging materials to be treated; for feeding or discharging other material
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/90—Apparatus therefor
- C05F17/964—Constructional parts, e.g. floors, covers or doors
- C05F17/971—Constructional parts, e.g. floors, covers or doors for feeding or discharging materials to be treated; for feeding or discharging other material
- C05F17/979—Constructional parts, e.g. floors, covers or doors for feeding or discharging materials to be treated; for feeding or discharging other material the other material being gaseous
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/141—Feedstock
- Y02P20/145—Feedstock the feedstock being materials of biological origin
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
Abstract
process is disclosed for creating biologically active soil or horticulture media for growing plants, wherein a fibrous carbon source such as coconut coir in a predetermined particulate form is mixed with fertilizers and other biological nutrients, inoculated with a biologically active substance such as worm castings and then aged or cured in an oxygen rich aerobic process. After which additional nutrients can be added to tailor the aged media for a specific sue. Various apparatus with which to conduct the aging process are also described. In a variation of the process used soil or horticulture media is recharged by first composting at a high temperature to remove harmful and unwanted items, its contents are evaluated, nutrients are added, and it is then aged in an aerobic process. ch as worm castings and then aged or cured in an oxygen rich aerobic process. After which additional nutrients can be added to tailor the aged media for a specific sue. Various apparatus with which to conduct the aging process are also described. In a variation of the process used soil or horticulture media is recharged by first composting at a high temperature to remove harmful and unwanted items, its contents are evaluated, nutrients are added, and it is then aged in an aerobic process.
Description
METHOD FOR CREATING NUTRIENT RICH BIOLOGICALLY ACTIVE
SOILS AND HORTICULTURE MEDIA WITH PREDETERMINED
CHARACTERISTICS
CROSS-REFERENCE TO RELATED APPLICATIONS
This application claims the benefit of priority under 35 U.S.C. § 120 of:
Provisional Application Serial No. 62/322,586 filed on April 14, 2016 the content of
which is relied upon and incorporated herein by reference in its entirety; and US
Patent Application Serial No. 15/477550 filed on April 3, 2017 the content of which is
relied upon and incorporated herein by reference in its entirety.
FIELD OF INVENTION
The present invention relates to a system and method to create biologically
active nutrient dense horticultural media with predetermined nutrient compositions
and nutrient and water supply characteristics. More particularly it explains how to
combine various substances and also process them to create the desired soil or
horticulture media characteristics
BACKGROUND OF INVENTION
A key aspect of growing plants and achieving desired growing
characteristics and features of the plant is the characteristics of the soil it is grown in
and the nutrients, water and biological environment that the growing plant
experiences. Many plants are grown in artificial soils and horticultural practices
involve cultivation in soilless media. Such media are referred to with terms such as
“horticultural media”, “potting soil”, compost, soil or soilless media. Media may be
derived from organic materials such as peat, coconut coir, wood products, compost,
manures and inorganic materials such as sand, perlite, and vermiculite.
There have been many attempts to enhance and improve horticultural media to
maximize growth and crop production characteristics. This can include adding,
wetting agents, fertilizer nutrients, lime, gypsum, other chemicals, and biological
inoculants.
Additionally, where a plant is grown to maturity in horticultural media (e.g
tomatoes, cannabis, strawberries, etc.) the costs of disposal of the used horticultural
media can be significant. There is considerable interest in the potential to re-use
horticulture media, but there are significant challenges and risks associated with re-
use. There may be carryover of pests and diseases from one crop to the next and
nutrients may become depleted or imbalanced affecting plant growth.
BRIEF SUMMARY OF THE INVENTION
The invention provides methods, devices and systems to create biologically
active, nutrient dense horticultural media with pre-determined nutrient release of
water supply characteristics and microbial populations.
One aspect of the invention involves using containers with air permeable
surfaces to facilitate the flow of oxygen into the soil media during biological
activation of horticultural medium. The oxygen supply can be actively augmented by
using a system to actively inject oxygen into the horticultural medium or to mix the
materials to expose surfaces and biological populations to oxygen.
The containers may be processed either as batches or as a continuous flow
system.
Another aspect of the invention involves the use of diverse microbial
populations stabilized as a living culture to activate the horticultural or soil media.
Another aspect involves the addition of materials to the horticulture or soil
media that influence viability of microbial populations during periods of water stress.
Another aspect of the invention includes blending organic and inorganic
nutrient sources in specific ratios into the horticultural or soil media to achieve
desired nutrient supply characteristics. Other aspects of the invention involve the
introduction of activated charcoal or biochar to influence the availability of nutrients.
Another aspect of the invention involves the introduction of activated charcoal
or biochar to influence microbial activity and populations.
Another aspect of the invention involves manipulating the composition of the
horticultural medium so as to affect the porosity of the medium and the water
availability.
To achieve objectives of the invention it includes a method for creating
biologically active nutrient dense plant growth media consisting of the steps of: a)
forming a mixable base media with a specified porosity; b) mixing into the base
media nutrients; c) activating the base media and nutrients by introducing biological
inoculants to form an active media; d) aging the active media in an oxygen rich
environment to thereby maintain biological aerobic activity; and e) blending in
additional ingredients after the aging process is completed to thereby create a plant
growth media tailored to desired nutrient and water supply characteristics.
In a further aspect it includes forming the mixable base media comprises
hydrating coir of at least one particle size to create a loose mixable base. In another
aspect of the invention step of forming the base further comprises varying a particle
size of the mixable base media from less than 0.05 mm to more than 12.5 mm. In a
further aspect of the invention the step of forming the mixable base media includes
selecting and mixing one or more materials from a group consisting of coconut coir,
sphagnum moss, pine bark, rice hulls, wood chips, sawdust, molasses, corn stover,
wheat straw, barley straw, spent brewers grains, perilite, and, sand. In yet another
aspect of the invention the step of mixing into the base media nutrients comprises
introducing nitrogen, phosphorous, and potassium in a predetermined ratio to each
other.
In yet a another aspect of the invention the step of mixing in nutrients includes
mixing in one or more of substances taken from a group consisting of animal and
plant derive protein meals, mineral trace elements, azomite, greensand, soluble humic
and fulvic acids, poultry litter , diatomaceous earth, epsom salt (Mg SO4), gypsum
(CaSO4), humates, peanut meal, phosphate rock, soft rock phosphate, sodium nitrate,
sulphate of potash, alfalfa meal, peanut meal, cottonseed meal, rye grass, neem meal,
corn forage, green manures, clover, buckwheat, vetch, mustard, oil seed rape, kelp
meal, feather meal, fish hydrolysate, blood meal, bone meal, bat and seabird guanos,
langbenite, calcitic lime, dolomitic lime, ferrous sulfate, aluminum sulphate, and
sulphur.
In yet another aspect of the invention, the step of aging the active media in an
oxygen rich environment using a passive method of aeration. In a further aspect the
step of using a passive method of aeration comprises a step of aging the active media
in air permeable containers. In a further aspect of the step of aging the active media
in air permeable containers involves use of air permeable containers made of air
permeable fabric that is open at the top. In yet a further aspect of the invention, the
step of aging the active media in an oxygen rich environment involves the step of
relying on passive aerationwhen the temperature during the aging step remains in a
range of between 70 to 130 degrees Fahrenheit for a period of 3 or more days before
returning to ambient temperature.
In another aspect of the invention the step of aging in an oxygen rich
environment involves the step of actively aerating the active media. In yet a further
aspect of the invention the step of aging the active media in an oxygen rich
environment involves the step of actively aerating when the temperature of the active
media is 130 to 180 degrees Fahrenheit for a period of 3 days or more . In yet another
aspect of the invention the step of actively aerating uses a step selected from the
group including the following: inserting air conduits into the base and blowing air into
the active media, turning of the active media using an auger within a vessel, turning
the active media in windrows using a commercial windrow machine, turning of the
active media in piles using equipment such as a front end loader, and turning the
active media using a rotary composter.
In another aspect of the invention the step of introducing an inoculant is
selected from a group including one or more of the following to activate the system:
Introducing worm castings, introducing a predetermined amount of base previously
made with this method, or introducing a predetermined amount of soil or introducing
a consortia of biology including, bacteria, fungal populations and beneficial
organisms.
In another aspect of the invention it includes a step of monitoring the oxygen
content of the aging active media and injecting additional oxygen if the level
monitored falls below a threshold necessary to maintain an aerobic aging process.
In yet another aspect of the invention the step of forming a base media with a
specified porosity includes forming a base media with a combination of water
porosity and air porosity. In yet another aspect the step of forming a base media with
combination of water porosity and air porosity can include selecting it from a group
consisting of a) 16% air porosity and 68% water porosity for a total of 84% porosity,
b) 16% air porosity and 63% water porosity for a total of 79% porosity, and c) 31%
air porosity and 58% water porosity for a total of 89% porosity. In a further aspect of
this step water porosity can vary from 10% to 50% and air porosity can vary from
% to 50% and total porosity can vary from 10% to 90% depending on the
combination of air and water porosity.
In yet another aspect of the invention it includes a step of adding biochar as an
ingredient.
The present invention also includes method for recharging used growth media
for plant propagation includes the steps of: a) assessing the composition of used
growth media for preselected physical, chemical and biological characteristics; b)
composting the used growth media to obtain a temperature of at least 140° or more for
a period of days to sterilize the growth media; c) adding base media as needed or
desired; e) blending preselected nutrients into the growth media; f) activating the
growth media by introducing at least one biological inoculant; g) aging the activated
growth media in an oxygen rich environment to assure a purely aerobic aging process;
and h) blending into the growth media additional nutrients and ingredients to thereby
create a plant growth media tailored with desired nutrient and water supply
characteristics. In yet another aspect of the invention the growth media being
recharged is selected from a group consisting of horticulture media and soil media.
BRIEF DESCRIPTION OF THE DRAWINGS
The accompanying drawings are included to provide a further understanding,
and are incorporated in and constitute a part of this specification. The drawings
illustrate one or more embodiment(s), and together with the description serve to
explain principles and operation of the various embodiments.
Fig. 1 is a flow chart that provides an overview of the steps of one method of
the present invention used to create the desired soil or horticulture media;
Fig. 2 is perspective view of a bin based aging system that uses a porous bag
held by a frame to age the horticulture media;
Fig. 3 is a side view of the aging bin depicted in Fig. 2 with an aeration
conduit inserted into the horticulture media;
Fig. 4 is a perspective view of another system used to age the horticulture
media that uses an auger designed to move about a bin and thus agitate and thereby
aerate the soil or horticulture media during the aging process;
Fig. 5 depicts the auger/bin based system of Fig. 4 with the bin filled with
horticulture media;
Fig. 6 is a flow chart of a second process for recharging used soil or
horticulture media for reuse as a growth medium;
Fig. 7 a rotary composter that might be used with the present invention; and
Fig. 8 a windrow system with a commercial windrow machine that would turn
the active media to aerate it.
DETAILED DESCRIPTION
I. Creation of Horticultural or Soil Media
a. Overview
The flow chart in Fig. 1 provides an overview of one process of the present
invention. In the preferred embodiment in the initial step 21 coconut coir of specified
particle size or sizes is hydrated and/or processed to create a base media for the
horticulture media. Although coconut coir is the preferred base material other similar
materials can be used to from the base media. The next step 23 involves mixing into
the base various nutrients, such as fertilizer and other nutrients that will promote
biological activity. In the next step 25 activation of the base with nutrients to create
the active media begins with introduction of biological inoculants, such as worm
castings or microbial cultures, the inoculant starts to react with the nutrients in the
media and the oxygen rich environment provided through either passive or active
means. During the fourth step 27 the aging process starts and an oxygen rich
environment is maintained through either passive or active means to promote the
aerobic aging or curing of the base. In the final step 29 additional ingredients are
added to the base to produce a final horticulture growth media that has the desired
water retention, nutrient and nutrient release characteristics. The order of the steps of
this invention can be varied as needed or desired. The order in Fig. 1 is thus not
necessary to practice the invention and is only presented in the order shown for the
purpose of clearness and ease of discussing the method of the invention. Although
the terms soil media and horticulture media have slightly different meaning they have
been used interchangeably herein since the methods as described herein can be used
to create both as a final product. At times they will be referred to collectively as
growth media or plant growth media herein.
b. Preparing the Base Media
As noted with respect to the first step 21 in Fig. 1 the preferred horticulture
base material is coconut coir. However, alternative materials could include any
material or combination of materials with an appropriate carbon content and air space.
Such other alternative horticulture base media include sphagnum moss, peat moss,
pine bark, rice hulls, wood chips, corn stover, wheat straw, barley straw, spent
brewers grains, perlite, and sand. The last two perlite and sand would need a carbon
source. The coconut coir or other alternatives would naturally be shredded, ground or
pulverized to create a flowable dry media of a specific particle size or sizes. As
discussed in detail below the porosity of the particular base media used is significant
for at least one of the systems used during the aging process. Although the discussion
below uses coconut coir as the example any of the above alternatives would be
processed or prepared in a similar fashion.
Coir is a natural fiber obtained from the husks of coconuts, the fibrous
material located between the hard internal shell and the outer surface of the coconut.
Coconut coir has a neural pH, has excellent water holding capacity, air space and is
disease resistant. The present invention uses coir which has been milled to varying
sizes depending on the application. Commercially available coir comes in
compressed blocks in a powdered from where the coconut fibers have been ground
down to a specific particle size.
As will be discussed in detail below one of the innovative features of the
process described herein is that it maintains the biological aging or curing step as a
wholly aerobic process. Assuring a sufficient oxygen supply to the media during the
aging process is of paramount importance. One of the factors that can effect
providing sufficient oxygen supply is the porosity of the media. Porosity of the
horticulture growth media is also of concern with respect to the use it will be put to by
the end use customer. Thus, at the beginning the porosity selected for the media will
be driven by the needs of the aging or curing process, but upon completion will be
adjusted for the needs of the customer that will be using the horticulture growth
media.
The coir used is ground down into a specific particle size and then compressed
into a dry block. Blocks of coir come dry compressed blocks with particle sizes that
range from greater than 12.5mm to less than .5mm. The processing step commences
with the selection of coir of one or more particle sizes. The coir can be processed
either in a dry or wet state. Processing the dry compressed coir blocks in a dry state
involves breaking apart the compressed blocks by mechanical means. An alternative
is to hydrate the coir blocks as part of the processing. This may be done either by a
static or dynamic means, an example of a static method is laying the blocks on a flat
surface and then spraying water on them to hydrate them. As the blocks absorb water
they break down. Once they have absorbed sufficient water to reach the desired state
of hydration they can be easily broken up into their individual particle size. An
alternative dynamic method of processing involves breaking the blocks up in a large
mixer such as a horizontal forage mixer or cement mixer and adding water to achieve
the desired level of hydration to create a dry bulk flowable mixture that is easy to
work with and facilitates the mixing in of additional ingredients as desired and
needed.
As noted previously, porosity of the horticulture media is also of concern with
respect to the process of the invention described herein as well as the needs of the end
consumer of the product. The porosity of the base media has two aspects water
porosity and air porosity. The following table sets forth examples of porosity used in
batches of base media made for the process of this invention:
Soil Air Porosity Water Porosity Total Porosity
Porosity 1 16% 68% 84%
Porosity 2 21% 63% 84%
Porosity 3 31% 58% 89%
These are only examples and depending on the application and method of aeration
and aging of the horticulture media used to achieve the final product, the water and air
porosity can be significantly varied and the invention still practiced. A significant
point to keep in mind is that varying the size or sizes of the particles of coir affects the
water retention characteristics of the horticulture media being created as well as its air
flow characteristics.
c. Adding Nutrients
The next step 23, Fig 1, involves blending into the base media formed in step
21 various nutrients. The nutrients can vary significantly given the desired use of the
horticulture or soil media being created. Typically, it would start with a base of
fertilizer consisting of nitrogen, phosphorous and potassium (NPK). The formula for
the combination for these three ingredients is given as ratio such as 43, 07, 2
4, etc. The numbers as is common knowledge in the industry indicate the
proportionate amount of nitrogen, phosphorus and potassium in the fertilizer. The
possible sources of nutrients in organic or inorganic forms and combinations of
amounts of each of the ingredients in the NPK can vary greatly depending on the
intended use of the horticulture media. The possible variations are too numerous to
recite, but the uses of the possible different variations would be understandable to
those skilled in the art.
In addition to the use of one or more of the NPK ingredients, those skilled in
the art know of a plethora of additional secondary or tertiary micronutrients that can
be added, again depending on the intended use of the final horticulture or soil media
to be produced. Secondary micronutrients that might be added include: calcium (Ca),
magnesium (Mg), and sulphur (S). Additional micronutrients that could be added
include: copper (Cu), iron (Fe), manganese (Mn), molybdenum (Mo), zinc (Zn),
boron (B), and of possible use here are silicon (Si), cobalt (Co), and vanadium (V)
plus rare mineral catalysts. In addition to the foregoing elements the following
substances are often used as biological nutrients in soil or horticulture growth media:
diatomaceous earth, feather meal, gypsum, humate, poultry litter, peanut meal,
phosphate rock, and sulfate of potash. The list of possible additional nutrients that
can also include: Azomite, bone meal, Soluble Humic and Fulvic acids, Poultry litter ,
Diatomaceous earth, epsom salt (Mg SO4), gypsum (CaSO ), humates, peanut meal,
phosphate rock, soluble Sulphate of Potash, alfalfa meal, peanut meal, cottonseed
meal, kelp meal, feather meal and dolomitic lime.
Carbon sources may also be added in addition to that already in the base
media. Such carbon sources can include but are not limited to the following: rice
hulls, wood chips (various species of trees, brush and shrubs can provide the source),
sawdust, coconut coir, molasses, corn stover, wheat straw, barley straw, spent brewers
grains, glycerol.
An additional ingredient that can be added is biochar. Biochar differs from
most of the ingredients listed above. Biochar is a solid generally of at least 60%
carbon material created by heating organic matter in the absence, or reduced supply of
oxygen. Equipment exists for the pyrolysis or gasification of biomass and artisanal
systems can be devised to create biochar. The biomass sources for making biochar
include such organic materials as animal manure, animal remains or bones, crop
residue, root mass, natural vegetation and bio-solids, which are then subjected to a
pyrolysis or gasification process. While the carbon in biochar is stable and can
endure in soil for thousands of years it can enhance soil fertility, improve soil water
use, retain organic and inorganic nutrients and increase soil water retention and
resistance of a growing plant to water stress.. Since biochar achieves the above but
retains its structure it remains in the soil or horticulture media after use.
d. Activating the Base Media with Nutrients
In step 25, Fig. 1, the base is biologically activated by the addition of a
biological inoculant or innoculants. One of the preferred inoculants is earth worm
castings. Earth worm castings add beneficial fungi, bacteria and other microbes to the
base media. The nature of the castings may also be influenced by the organic and
inorganic materials fed to the worms that produce the castings and through
inoculation with microbial innoculants. Also, biologically activated horticultural
media containing a diverse microbial population may be used as an inoculant to
introduce biological active agents such as fungi, bacteria and other organisms. One
source of such a horticulture media is media produced by the invention process
described herein. Alternatively a soil or combination of soil types could be selected
for use.
The biological activity of the bacteria, fungi and other microbes produce heat,
carbon dioxide and ammonium (NH ) among other products as they grow. Available
ammonium may be further converted into nitrates (NO3) through the process of
nitrification. Additionally, various fungi and other so called microbes grow in the
media producing organic acids and metabolites that influence the physical, biological
and chemical characteristics of media and also combine with the surfaces of biochar.
These organic materials and their interactions contribute to and determine nutrient
supply.
While this process may appear analogous to composting, it differs in a number
of significant ways. The range and complexity of organic substrates being broken
down differs. Target thermal parameters for process conditions may differ from those
used in composting.
Composting focuses on managing the air/water balance to maintaining high
temperatures (135°-160° Fahrenheit / 50° - 70° Celsius) over a sufficient time
anywhere from 3 days to 15 days, primarily to ensure pathogens, weed seeds and
other undesirable items are destroyed or neutralized are killed due to the high
temperatures. The high temperatures indicate a high degree of biological activity.
Control of pathogens and weed seeds is not the primary focus of the activation
process. In the present invention all of the ingredients used are controlled and do not
have pathogens, weed seeds or other undesirable items. Additionally, the objective of
the activation and aging stages is to ensure that an adequate microbial population and
the desired diversity in this population is established and stabilized in the horticultural
media or soil media and to ensure the desired nutrient supply characteristics and
performance.
As noted above the objective then entails creating a stable living soil or
horticulture media wherein the nutrients will be broken down and made available over
a period of time to vegetation planted in the media. Initially, the microbes, bacteria
and fungi start to grow and multiply on the available carbon in the raw materials. As
they begin multiply rapidly they use nutrients that are available to them. These
nutrients may be immediately available in mineral form or released from the
breakdown of organic materials. Given the abundance of this biological activity the
temperature of the media rapidly rises indicating the tremendous biological activity
taking place. The rising temperature indicates that the available oxygen is being used
Once the temperature passes 110° to 120° or so experience shows that there is
a risk that oxygen supply may be exhausted and the process may turn anaerobic due to
the lack of oxygen. Anaerobic processes can produce unwanted byproducts and kills
the beneficial aerobic bacteria, fungi and microbes which the present invention
encourages.
Sufficient supply of oxygen to maintain an aerobic process may be achieved in
various ways. Passive supply of a sufficient air flow generally can be used when the
volume of the aging container is sufficiently small volume. The rate of diffusion can
be influenced by manipulation of the total, air and water filled porosity of the
materials. Alternatives to passive aeration involve the injection of air or mechanical
turning or mixing of the material.
When the temperatures range goes higher to 140° to 150° the base needs to be
actively aerated. Active aeration such as the injection of air into the media during the
aging process is the means used to provide sufficient oxygen to the bacteria, fungi and
other beneficial microbes in the media.
e. Aging the Media
The next step 27, Fig. 1, is the aging or curing process. As detailed above of
particular importance in the aging process of the present invention is that it provide
sufficient oxygen to the media as it ages.
The aging process typically lasts for two or three weeks, but may take as little
as 4 days. Additional curing may last for up to several months. During the aging
process a key requirement as noted is that it proceeds as an aerobic process.
In the present invention as noted above the aging step must be maintained as
an aerobic process. The intent is to create a living sustainable culture of aerobic
bacteria, fungi and microbes. By maintaining the process as an aerobic one after the
initial feeding frenzy the raw nutrients are used up and the temperature drops as the
bacteria, fungi and microbes start feeding off of each other. After stabilization it
reaches a steady state where bacteria, fungi and other microbes that are produced feed
off of dead bacteria, fungi and other microbes as well as the added substrates in a
cyclical process.
Once activated the aging or curing process can be conducted in several
different ways to achieve the desired outcome of the present invention. In one
variation of the aging process of the present invention the soil media is placed in air
permeable hoppers or bins which are approximately 1 meter square to provide a static
aging process 49 Fig. 2. As can be seen in Fig. 2 the bins are fabric bags that are air
permeable with an open top to allow the free flow of air. This generally provides
sufficient air flow to keep the soil media sufficiently oxygenated to maintain an
aerobic process, when the temperatures remain the 90° to 120° range this is the case.
If the temperatures increase to the 140° to 150° range active processes to inject an air
flow can be used. One method is to insert pipes into the soil media during the aging
process and blow air into the soil media to assure sufficient oxygen levels to maintain
the process as an aerobic process.
Fig. 2 is a perspective view of such a bin where bag 51 is open at its top 53.
Bag 51 is held up and in place by frame 55. Frame 55 is metal tubing with an upper
support portion 57 consisting of two metal tubes welded together along their center
portion and struts or legs 59 welded to the end of the upper portion tubes 57. Bag 51
attaches by straps 61 to the upper frame formed by the tubing of upper support section
57. The aging horticulture media 63 in bag 51 fills it almost to its top. Bag 51 is
made of a porous woven plastic strand or nylon type material that allows air to freely
pass through the side 65 of bag 51 but retains the media. A thermometer or
temperature probe 67 can be inserted into media 63 to monitor temperature.
Fig. 3, a side view of the aging bin of the present invention shows the end of
an aeration conduit 69 inserted into media 63. Conduit 69 might have apertures 71 in
that portion of it buried in media 63 to facilitate the injection of air into the soil or
horticulture media 63. Thus, if the temperature of the media during the aging process
rises above 110° or so air can be injected into media 63 to assure the bacteria, fungi
and microbes have an adequate oxygen supply to keep the process an aerobic one.
Air can be injected into conduit 69 with a standard air blower unit or in any other
number of standard ways.
In another variation of the aging process the soil media may be mixed within a
vessel designed for either batch or continuous mixing using an auger or augers to mix
the horticultural media to ensure that the materials are exposed to an adequate amount
of oxygen and that moisture content is controlled.
Fig. 4 depicts such an auger based system 81. The auger based system
81consists of an aging vessel 83 which has sides 85A and 85B and ends 86A and 86B,
a bottom 87 and an open top 89. Auger 91 attaches to bar 93 with motor 95
connects to the top of the auger. Bar 93 at each end 97A and 97B rests on rails 99A
and 99B respectively. Bar 93 can move in direction 101A and 101B between ends
86A and 86B along rails 99A and 99B. Additionally, auger 91 can move along bar 93
in direction 103A and 103B between ends 97A and 97B of bar 93. Referring to Fig.
, vessel 83 is now filled with soil or horticulture media 105 into which nutrients and
biological inoculants 108 have been added. The system 81 which is controlled by an
appropriately programmed computer or controller, not shown, moves auger 91 around
the entire area of vessel 83 as auger 91 churns up media 105. Churning auger 91
moves at a pace such that soil or horticulture media 105 is adequately aerated to
maintain the aging process as an aerobic one.
In another variation in rotary composting or processing equipment 107 Fig. 7
may be used to ensure that the growth media is exposed to adequate oxygen and that
moisture content is controlled. In rotary composter 107 is driven by a motor which
turns drum 111, which is a hollow cylinder. The growth media to be processed is
loaded through chute 109. The rotary processing equipment includes a temperature
sensor; air is introduced through the opening into the rotating drum 111. The rate of
rotation of the drum and amount of air vented into the drum during operation would
be a factor of the aeration of the growth media and temperature necessary to achieve
the purely aerobic process and results discussed above to create the growth media of
the present invention.
In another variation materials could be processed as windrows 115 Fig. 8 and
turned by windrow turning equipment 117 or other equipment such as a standard front
end loader not shown. As can be seen in Fig. 8 as windrow turner 117 moves down
windrow 115, agitates and mixes the growth media in the portion of the row 115A and
redeposits it in reformed the windrow 115B after having thoroughly mixed the growth
media. The number of times this is done and the speed with which this is done is a
factor of the aeration and temperature of the growth media necessary to achieve the
purely aerobic process and results discussed above to create the growth media of the
present invention. .
Any number of techniques can be used to measure oxygen levels in the aging
media and assuring that sufficient oxygen is supplied to the aging media to assure it is
an aerobic process. Monitoring temperature with probe 67 Fig. 2 is one possibility as
discussed above. You can also measure the oxygen levels by directly measuring the
oxygen contact with an appropriate sensor. You can measure methane concentrations
with an appropriate sensor. The production of methane being an indicator that the
process is going anaerobic. A less sensitive but possible measure would be ratios of
ammoniacal and nitrate forms of nitrogen. Ammonium is a precursor of nitrate.
Ammonium can be produced under anaerobic conditions, but nitrate cannot. This last
measure can also be used as an index of the maturity of the aging process.
f. Fine Tuning the Media
As noted, at some point during the process various ingredients are blended
into the base or soil media to alter the ratio between the carbon available to the
microbial population and nutrients required for the growth. Nutrients are added both
to ensure adequate microbial growth and to adjust the nutrient supplying characteristic
of the final soil media.
This step appears at 29 Fig. 1 for convenience of illustration, but it can be
done at any desired point during the process described above. For example lime
might be added to the soil media to change its pH. Biochar may also be added as
needed or desired. In fact any of the nutrients listed or discussed above in section I. c.
can be added to the soil or horticulture media to tailor the final soil or horticulture
media to the intended use.
In an additional aspect of the invention mites are added to the soil media
during or after the aging process to remove deleterious matter and keep the soil media
in balance. Oribatid mite is a type of soil mite that is commonly found in wooded
areas where it often assists in the breakdown of organic matter. The Hypoaspis mite
is a small (0.5 mm) light brown mite that lives in the top ½ in layer of soil.
In addition to feeding on organic matter biological control can be used to
control pests that may enter. For example fungus gnats are small flies known to infest
horticultural media. Their larvae primarily feed on fungi and organic matter, but also
chew roots and can be a problem in greenhouses, nurseries, potted plants and interior
plantscapes. Biological control measures are effective to control fungus gnat
populations. For example Nematodes such as Steinernema nematodes and Bacillus
thuringiensis subspecies israelensis (Bti) used as a soil drench can all be used as
natural predators of fungus gnat pupae.
As another example Trichoderma species such as T. harzianum, T. viride and
T. hamatum can be added to the soil. Trichoderma are used to control fungal root
diseases and their presence can be established in horticultural media.
II. Recharging Used Soil or Horticulture Media:
In another aspect of the invention used soil or horticulture media is recharged
and reformulated for use again. Used soil or horticulture media can provide a base for
the creation of reusable soil or horticulture media using a modified version of the
present invention. Fig. 6 provides a flow chart of the overall process used in the
present invention for recharging used soil or horticulture media. The first step 31 is to
assess the composition of the used soil or horticulture media, in another step 33. In
step 33 the soil or horticulture media is composted with the objective of obtaining a
temperature during the composting process of at least 140 degrees Fahrenheit to kill
unwanted plant life, weed seeds and pests and pathogens.
After the composting step the method of creating new soil or horticulture
media discussed above and outlined in Fig. 1 is followed with some modifications.
Referring to Fig. 6 additional base media, such as coconut coir, can be added as
needed to achieve desired consistency and porosity of the media step 35. Additional
nutrients can also be added as needed, step 37. To assure activation of the aging
process one can add an inoculant step 39, such as worm castings or new soil or
horticulture media which has been created with the method outlined in Fig. 1 and
discussed above. Referring to Fig. 6 again the aging process step 41 is conducted as
discussed above with the objective of keeping it an aerobic process. In the final step
43 additional nutrients, base media or other additives can be blended into the
reconstituted soil or horticulture media to create the final media with desired nutrient,
air flow and water supply characteristics. It should be noted that the order of the steps
of the process outlined in Fig. 6. The order of the steps can be varied without
departing from the spirit of the invention.
a. Assessing the Composition of the Used Media:
The first step 31 is the determination of the composition of the subject used
soil or horticulture media. The process of recharging the used soil and its recharging
is also dependent on what the desired use for the used soil is. During this step the
physical, biological and chemical characteristics of the used soil or horticultural
media can be determined. There are many ways to assess the physical, biological and
chemical characteristics of soil or horticulture media. Too many to itemize here. The
characteristics and measuring techniques discussed in the following paragraphs are
offered only a few of the possible examples of possible ways to measure the
characteristics of the soil or horticulture media.
Physical characteristics measured can include the bulk density of the soil or
horticulture media (mass per unit volume). This can be measured using widely
established procedures and compared to defined thresholds. An important physical
criterion is total porosity of the horticultural media and the portion that will drain
under gravity after the soil is saturated.
Chemical characteristics are also measured by these include the soil pH and
the nutrient supplying characteristic of the media. In a nutrient dense horticultural
media the challenge is to predict the potential of the horticultural or soil media to
supply nutrients over time. This represents a challenge because standard measures
such as the widely adapted saturated media extract procedure provides a point in time
measurement of nutrients in soil solution. However in a nutrient dense soil a measure
of the potential to release nutrients due to the mineralization (breakdown) of organic
materials is required.
In this invention we compare measured nutrient release from used horticultural
media against target profiles and amend with nutrient containing materials as
required. In one variation samples of the media may be leached with pure water
(prepared by distillation, deionization, reverse osmosis or similar process) or a dilute
salt solution such as potassium chloride (KCl) or potassium sulphate (K SO ) to
create a baseline, the material can then be incubated over a period of time (days to
weeks) at a standard temperature and moisture content and the nutrients mineralized
can be determined by measuring nutrients released in a subsequent leaching. In
another variation nutrients released may be recovered using anion or cation exchange
resins.
b. Reprocessing of Used Media:
At some point the used soil is composted 33 to sterilize and purge it of pests,
pathogens or disease in the soil. The composting is typically raises the temperature to
at least 140° F or more. Any number of different composting methods can be used.
The important aspect of this step is that the temperature is equal to or exceeds that
needed to kill pathogens, weed seeds and other undesirable items in the used soil or
horticulture media. Use of the media to grow plants or for other purposes can easily
have introduced undesirable items. During this composting step the fact that it turns
anaerobic is not of concern. Purging the used growth media of unwanted items such
as pathogens, weed seeds and other undesirable items is important. Figs. 4, 7 and 8
depict three different methods that can be used to compost the used media to sterilize
the used media. The primary difference from that used in creating the new media
described above is the aeration and temperature control has a different. For example
achieving and maintaining an adequate sterilization temperature to control pathogens
is required and air flow may be modified to achieve the desired process conditions
with the rotary system of Fig. 7 or vessel of Fig. 4 maybe as few as three days. On
the other hand using the windrow method it can take up to 15 days of maintaining the
necessary anaerobic process for sterilization. In the preferred embodiment at least a
temperature of 140° F is necessary.
c. Adding more Base Media:
Once the physical characteristics of the growth media are assessed and it is
composted to eliminate unwanted pathogens, weed seeds and other undesirable items
there may be a need to adjust them to meet the new use envisioned for it or to prepare
for the next steps in the recharging process. One of the aspects that may be adjusted is
the porosity of the growth media. There may be a need to adjust it to meet air and
water porosity requirements. The aspect of porosity and related issues was discussed
extensively above at I. b. Preparing the Base Media and is applicable to this step. It
may not be necessary to add base media material, such as coir at this step if the used
growth media meets the requirements at this point.
d. Adding Nutrients:
Once the soil is assessed and a profile of the physical, chemical and biological
characteristics of the soil is determined the option of adding nutrients is considered.
In most instances there will be a need to do this. Although it is conceivable that this
might not be necessary in some rare cases. In any event the step of adding nutrients is
exactly the same as that described at I.c. Adding Nutrients above.
e. Injecting Inoculants:
At this step if necessary an inoculant is added, as discussed above at 1. d. such
as worm casting or horticulture or soil media prepared by the process outlined in Fig.
1. The intent being to initiate the aging or curing process.
f. Aging:
The aging process conducted in the process of recharging soil is the same as
that discussed at I. e. Aging the Media, above.
g. Blending in Additional Ingredients:
The step of blending in additional ingredients to tailor the recharged
horticulture media or soil media is essentially the same as that discussed at I. f. Fine
Tuning the Media, above. This may happen before, after or during the aging process.
Unless otherwise expressly stated, it is in no way intended that any method set
forth herein be construed as requiring that its steps be performed in a specific order.
Accordingly, where a method claim does not actually recite an order to be followed
by its steps or it is not otherwise specifically stated in the claims or descriptions that
the steps are to be limited to a specific order, it is no way intended that any particular
order be inferred.
It will be apparent to those skilled in the art that various modifications and
variations can be made without departing from the spirit or scope of the invention.
Since modifications combinations, sub-combinations and variations of the disclosed
embodiments incorporating the spirit and substance of the invention may occur to
persons skilled in the art, the invention should be construed to include everything
within the scope of the appended claims and their equivalents.
Claims (29)
1. A method for creating biologically active nutrient dense plant growth media, the method comprising: preparing particles with a specified particle size; forming a mixable base media from the prepared particles, the mixable base media having a specified combination of water porosity and air porosity for allowing sufficient oxygen supply to be added during an aging process; mixing nutrients into the mixable base media; after mixing nutrients into the mixable base media, activating the mixable base media and the nutrients by introducing biological inoculants to form an active media; aging for four days to three weeks the active media in an oxygen rich environment to maintain biological aerobic activity to reach a stabilized steady state wherein the bacteria, fungi and microbes start feeding off of each other in a cyclical process; and blending in additional ingredients after the aging process is completed to create a plant growth media tailored with desired nutrient and water supply characteristics, wherein said mixable base media, said nutrients, said biological inoculants and said additional ingredients are controlled and do not have pathogens or weed seeds.
2. The method of claim 1, wherein forming the mixable base media comprises hydrating coconut coir of at least one particle size to create a loose mixable base.
3. The method of claim 1, wherein forming the mixable base media comprises selecting and mixing one or more materials from a group consisting of coconut coir, sphagnum moss, pine bark, rice hulls, wood chips, wood mulch, sawdust, molasses, corn stover, wheat straw, barley straw, spent brewers grains, perlite, vermiculite and sand.
4. The method of claim 1, wherein mixing nutrients into the mixable base media comprises introducing nitrogen, phosphorous and potassium.
5. The method of claim 1, wherein mixing in nutrients into the mixable base media and blending in additional ingredients includes mixing in one or more of substances selected from a group consisting of: animal and plant derived protein meals, mineral trace elements, azomite, greensand, soluble humic and fulvic acids, poultry litter, diatomaceous earth, epsom salt, gypsum, humates, peanut meal, phosphate rock, soft rock phosphate, sodium nitrate, sulphate of potash, alfalfa meal, cottonseed meal, rye grass, neem meal, corn forage, green manures, clover, buckwheat, vetch, mustard, oil seed rape, kelp meal, feather meal, fish hydrolysate, blood meal, bone meal, bat and seabird guanos, langbenite, calcitic lime, dolomitic lime, ferrous sulfate, aluminum sulphate, urea, ammonium nitrate, ammonium sulphate and sulphur.
6. The method of claim 1, wherein aging the active media in the oxygen rich environment comprises using a passive method of aeration.
7. The method of claim 6, wherein using the passive method of aeration comprises aging the active media in at least one air permeable container.
8. The method of claim 7, wherein aging the active media in at least one air permeable container comprises using at least one air permeable container made of air permeable fabric that is open at the top.
9. The method of claim 1, wherein aging the active media in the oxygen rich environment comprises relying on passive aeration when the temperature during the aging step remains in a range of between 70 to 130 degrees Fahrenheit (21 to 54 degrees Celsius).
10. The method of claim 1, wherein aging in the oxygen rich environment comprises actively aerating the active media.
11. The method of claim 10, wherein aging the active media in the oxygen rich environment comprises actively aerating the active media when the temperature of the active media during aging is 110 degrees Fahrenheit (43 degrees Celsius) or more.
12. The method of claim 10, wherein actively aerating the active media comprises any one of: inserting air conduits into the active media and blowing air into the active media, and turning or mixing the active media.
13. The method of claim 1, wherein activating the base media and nutrients by introducing biological inoculants comprises any one of: introducing worm castings, introducing plant growth media previously made with this method, and introducing soil.
14. The method of claim 1, further comprising monitoring the oxygen content of the aging active media and injecting additional oxygen if the level monitored falls below a threshold necessary to maintain an aerobic aging process.
15. The method of claim 1, wherein the combination of water porosity and air porosity comprises selecting the air porosity and water porosity, respectively, from a group consisting of a) 16% air porosity and 68% water porosity for a total of 84% porosity, b) 16% air porosity and 63% water porosity for a total of 79% porosity, and c) 31% air porosity and 58% water porosity for a total of 89% porosity.
16. The method of claim 1, wherein said water porosity can vary from 10% to 50% and said air porosity can vary from 10% to 50% and a total combined porosity can vary from 10% to 90% depending on the combination of said air porosity and said water porosity.
17. The method of claim 1, further comprising adding biochar as an ingredient.
18. The method of claim 12, wherein turning or mixing the active media comprises any one of: turning or mixing the active media in a vessel using an auger, turning or mixing the active media in windrows using a windrow machine, turning or mixing the active media in piles using equipment such as a front end loader, turning the active media using rotary processing equipment, and turning the active media using a rotary composter.
19. The method of claim 1, further comprising adding organisms to the plant growth media to remove potentially deleterious matter and deleterious organisms.
20. The method of claim 19, wherein adding organisms comprises adding organisms selected from a group consisting of: Oribatid mites, Hypoaspis mites, Steinernema nematodes, Bacillus thuringiensis subspecies israetensis, T. harzianum, T. viride and T. hamatum.
21. A method for recharging used growth media for plant propagation, the method comprising: assessing the composition of used growth media for physical, chemical and biological characteristics; composting the used growth media to obtain a temperature for a period of time sufficient to sterilize the growth media; preparing particles with a specified particle size; adding base media formed from the prepared particles such that the growth base media has a specified combination of water porosity and air porosity for allowing sufficient oxygen supply to be added to the growth media during an aging process; blending nutrients into the growth media; after blending nutrients into the growth media, activating the growth media by introducing at least one biological inoculant; aging for four days to three weeks the activated growth media in an oxygen rich environment to assure a purely aerobic aging process is maintained to reach a stabilized steady state wherein the bacteria, fungi and microbes start feeding off of each other in a cyclical process; and blending into the growth media additional nutrients and ingredients to create a plant growth media tailored with desired nutrient and water supply characteristics, to create a new recharged growth media, wherein said base media, said nutrients, said at least one biological inoculant and said additional nutrients and ingredients are controlled and do not have pathogens or weed seeds.
22. The method of claim 21, wherein the growth media being recharged is selected from a group consisting of horticulture media, potting soil, and soilless media.
23. The method of claim 21, further comprising adding organisms to the growth media to remove deleterious matter and deleterious organisms.
24. The method of claim 23, wherein adding organisms comprises adding organisms selected from a group consisting of: Oribatid mites, Hypoaspis mites, Steinernema nematodes, Bacillus thuringiensis subspecies israelensis, T. harzianum, T. viride and T. hamatum.
25. The method of claim 21, wherein the period of time is three days if composted in a vessel.
26. The method of claim 21, wherein the period of time is fifteen days if composted in a windrow.
27. The method of claim 21, wherein composting the used growth media to obtain the temperature for the period of time sufficient to sterilize the growth media comprises obtaining a temperature of at least 140 degrees Fahrenheit (60 degrees Celsius).
28. The method of claim 21, wherein the step of composting the used growth media to obtain the temperature for the period of time sufficient to sterilize the growth media comprises conducting it as an anaerobic process.
29. The method of claim 21, wherein said additional nutrients and ingredients includes mixing in one or more of substances selected from a group consisting of: nitrogen, phosphorous, animal and plant derived protein meals, mineral trace elements, azomite, greensand, soluble humic and fulvic acids, poultry litter, diatomaceous earth, epsom salt, gypsum, humates, peanut meal, phosphate rock, soft rock phosphate, sodium nitrate, sulphate of potash, alfalfa meal, cottonseed meal, rye grass, neem meal, corn forage, green manures, clover, buckwheat, vetch, mustard, oil, seed rape, kelp meal, feather meal, fish hydrolysate, blood meal, bone meal, bat and seabird guanos, langbenite, calcitic lime, dolomitic lime, ferrous sulfate, aluminum sulphate, urea, ammonium nitrate, ammonium sulphate, and sulphur.
Applications Claiming Priority (5)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US201662317595P | 2016-04-03 | 2016-04-03 | |
US201662322586P | 2016-04-14 | 2016-04-14 | |
US15/477,550 | 2017-04-03 | ||
US15/477,550 US10125055B2 (en) | 2016-04-03 | 2017-04-03 | Method for creating nutrient rich biologically active soils and horiculutre media with predetermined characteristics |
PCT/US2017/027609 WO2017180996A1 (en) | 2016-04-14 | 2017-04-14 | Method for creating nutrient rich biologically active soils and horiculutre media with predetermined characteristics |
Publications (2)
Publication Number | Publication Date |
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NZ758696A NZ758696A (en) | 2021-04-30 |
NZ758696B2 true NZ758696B2 (en) | 2021-08-03 |
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