Tuesday 2 June 2015

USE OF BIOPOLYMERS FOR CONTROLLED RELEASE OF PHEROMONES:Pheromoneresources

USE OF BIOPOLYMERS FOR CONTROLLED RELEASE OF PHEROMONES

V. Nandagopal1 A. Prakash1   A. Sasmal2, S. Sasmal1   and P.L.Nayak2

1 Department of Entomology, Central Rice Research Institute, Cuttack-753 006
2 P. L. Nayak Research Foundation, Cuttack-753 006
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INTRODUCTION
During the last two decades, significant advances have been made in the development of biocompatible and biodegradable materials for biomedical applications, and in the case of the latter category, industrial applications, as well. In the biomedical field, the goal is to develop and characterize artificial materials or, in other words, "spare parts" for use in the human body to measure, restore, and improve physiologic function, and enhance survival and quality of life. Typically, inorganic (metals, ceramics, and glasses) and polymeric (synthetic and natural) materials have been used for such items as artificial heart-valves, (polymeric or carbon-based), synthetic blood-vessels, artificial hips (metallic or ceramic), medical adhesives, sutures, dental composites, and polymers for controlled slow drug delivery. The development of new biocompatible materials includes considerations that go beyond non-toxicity to bioactivity as it relates to interacting with and, in time, being integrated into the biological environment as well as other tailored properties depending on the specific "in vivo" application.1-2
The parallel field of "biomimetics" may be described as the "abstraction of good design from nature" or, plainly put, the "stealing of ideas from nature". The goal is to make materials for non-biological uses under inspiration from the natural world by combining them with manmade, non-biological devices or processes. This is fast becoming a new research frontier.
Yolles & Sinclair (1973) first proposed the use of polymers of lactic and glycolic acid as degradable matrices for the sustained released of bioactive substances.  The advantages of the polymers for this purpose are considerable: The polymeric matrix disappears innocuously. The degradation can be tailored to that required for the drug or pesticide by varying the copolymer composition. The half-life of the drug/pesticide is prolonged to provide sustained therapy/duration without toxicity/persistence. The controlled-release device is easily fabricable by solution; or melt-forming operation since the polyesters are thermoplastic and their polar nature allows incorporation and compatibility with polar, bioactive substances.
2. BIODEGRADABLE POLYMERS
One area of intense research activity has been the use of biocompatible polymers for controlled drug delivery. It has evolved from the need for prolonged and better control of drug administration. The goal of the controlled release devices is to maintain the drug in the minimum effective range with just a single dose. In general, release rates are determined by the design of the system and are nearly independent of environmental conditions.
A convenient classification of controlled-release systems is based on the mechanism that controls the release of the substance in question. The most common mechanism is diffusion. Two types of diffusion-controlled systems have been developed; the first is a reservoir device in which the bioactive agent (drug) forms a core surrounded by an inert diffusion barrier (Figure 1). These systems include membranes, capsules, microcapsules, and hollow fibers. The second type is a monolithic device in which the active agent is dispersed or dissolved in an inert polymer (Figure 2). As in reservoir systems, drug diffusion through the polymer matrix is the rate-limiting step, and release rates are determined by the choice of polymer and its consequent effect on the diffusion and partition coefficient of the drug to be released.
In chemically controlled systems, chemical control can be achieved using bioerodible or pendant chains. The rationale for using bioerodible (or biodegradable) systems is that the bioerodible devices are eventually absorbed by the environment and thus need not be removed. Polymer bioerosion can be defined as the conversion of a material that is insoluble in water into one that is water-soluble. In a bioerodible system the drug is ideally distributed uniformly throughout a polymer in the same way as in monolithic systems. As the polymer surrounding the drug is eroded, the drug escapes (Figure 3). In a pendant chain system, the drug is covalently bound to the polymer and is released by bond scission owing to water or enzymes. In solvent-activated controlled systems, the active agent is dissolved or dispersed within a polymeric matrix and is not able to diffuse through that matrix. In one type of solvent-controlled system, as the environmental fluid (e.g., water) penetrates the matrix, the polymer swells and its glass transition temperature is lowered below the environmental temperature. Thus, the swollen polymer is in a rubbery state and allows the drug contained within to diffuse through the encapsulant.3







As material designers confront the fundamental challenges of medical science, the discovery of new biocompatible polymers is creating unprecedented excitement. Like other important scientific concepts that change over time, the notion of biocompatibility has evolved in conjunction with the continuing development of materials used in medical devices. Until recently, a biocompatible material is essentially thought of as one that would "do no harm." The operative principle is that of inertness—as reflected, for example, in the definition of biocompatibility as "the quality of not having toxic or injurious effects on biological systems."

2. 1.  BIODEGRADADION MECHANISM OF BIOPOLYMERS
Most biodegradable polymers are designed to degrade as a result of hydrolysis of the polymer chains into biologically acceptable, and progressively smaller, compounds. In some cases—as, for example, polylactides, polyglycolides, and their copolymers—the polymers will eventually break down to lactic acid and glycolic acid, enter the Krebs’s cycle, and be further broken down into carbon dioxide and water. Degradation may take place through bulk hydrolysis, in which the polymer degrades in a fairly uniform manner throughout the matrix. For some degradable polymers, most notably the polyanhydrides and polyorthoesters, the degradation occurs only at the surface of the polymer, resulting in a release rate that is proportional to the surface area of the drug delivery system 4
2. 1. 1. Factors Affecting Biodegradation of Polymers
  • Chemical structure.
  • Chemical composition.
  • Distribution of repeat units in multimers.
  • Presents of ionic groups.
  • Presence of unexpected units or chain defects.
  • Configuration structure.
  • Molecular weight.
  • Molecular-weight distribution.
  • Morphology (amorphous/semi-crystalline, microstructures, residual stresses).
  • Presence of low-molecular-weight compounds.
  • Processing conditions.
  • Annealing.
  • Sterilization process.
  • Storage history.
  • Shape.
  • Site of implantation (use).
  • Adsorbed and absorbed compounds (water, lipids, ions, etc.).
  • Physicochemical factors (ion exchange, ionic strength, pH).
  • Physical factors (shape and size changes, variations of diffusion coefficients, mechanical stresses, stress- and solvent-induced cracking, etc.).
  • Mechanism of hydrolysis (enzymes versus water).
3. AGROCHEMICALS

Agrochemicals as referred to herein include biologically active ingredients/plant protection products such as insecticides, herbicides, fertilizers, growth regulators, pheromones, biostimulants, acaricides, miticides, nematocides, fungicides and the like. Such agrochemicals are well known and are in common usage for controlling pests and diseases and for promoting plant growth in agriculture. In practice, it is important to make a sufficient amount of such agrochemical or active ingredient available to the biological system in order to control pests or disease or to promote growth. Too much active ingredient, however, is inefficient and not desired because of environmental and economic concerns. Furthermore, higher amounts of active ingredient lead to increased risks of leaching to ground water or surface water. Higher amounts can also lead to phytotoxicity for the crop. Insufficient levels of active ingredients results in lack of control of the pest and increase the risk of resistance

Thus, it is generally known that it is important to deliver the correct amount of active ingredient to the crop for control of the pest or disease and to promote growth over a given period of time. However, multiple applications of active ingredients become labor and cost intensive. With conventional applications of liquid or powder formulations, relatively high amounts of active ingredients are applied several times to assure control of pests over a longer period of time, typically 3-6 times for seasonal control, and users are exposed to the active ingredients during each application, which is undesirable.

3. 1. Slow and controlled-release of agrochemicals

Slow and controlled-release agrochemicals contain a bioactive agent for e.g., a plant nutrient,  in a form which either a) delays its availability for plant uptake and use after application, or b) which is available to the plant significantly longer than a reference ‘rapidly available nutrient fertilizer’ such as ammonium nitrate or urea, ammonium phosphate or potassium chloride 5. There is no official differentiation between slow-release and controlled-release formulations. Also the AAPFCO, the Association of American Plant Food Control Officials, uses both in its Official Terms and Definitions6.

Manufacturing Routes for Slow and Controlled-Release and Stabilized Formulations

In the production of Slow-Release Formulations (SRFs) or Controlled-Release Formulations (CRFs), the slow-release effect may be obtained by various production processes, for example through modification of conventional formulations 7-11. Controlled or slow nutrient release can be achieved through special chemical and physical characteristics. With controlled-release formulations the principal procedure is one whereby conventional soluble agrochemicals are given a protective coating or encapsulation (water insoluble, semi-permeable or impermeable with pores), controlling water penetration and thus the rate of dissolution, and agrochemical release synchronized to the plants’ needs.

3. 2.  Slow and controlled-release agrochemicals

3.2.1.   Materials releasing agrochemicals through low solubility due to a complex/highmolecular weight chemical structure following microbial decomposition.

3.2.2.   Materials releasing agrochemicals through a coated surface (coated fertilizers).

3.2.3.   Materials releasing agrochemicals through a membrane which may or may not itself be soluble (encapsulation).

3.2. 4. Agrochemical-releasing materials incorporated into a matrix which itself may be coated.

3.2. 5. Materials releasing agrochemicals in delayed form due to a small surface-to-volume ratio (super-granules, briquettes, tablets, spikes, plant food sticks etc.).

4.   SLOW AND CONTROLLED-RELEASE AGROCHEMICALS
4.1. Their advantages
Slow and controlled-release or stabilized formulations offer a number of important advantages:

4.1.1. They reduce toxicity (particularly to seedlings), which is caused through high ionic concentrations resulting from the quick dissolution of conventional soluble agrochemicals (in some cases also from ammonia, for instance after application of urea) and thus contribute to improved agronomic safety 12-17.

4.1.2. Due to the reduction of toxicity and the salt content of substrates (4.1.1) they permit the application of substantially larger agrochemical dressings as compared to conventional soluble formulations. This results in significant savings in labour, time and energy, as well as in making the use of the agrochemical more convenient. This latter factor constitutes the greatest advantage for the majority of present consumers of slow- and controlled-release formulations.

4.1.3. They contribute to advanced agrochemical management programme and to innovative farming systems such as no tillage farming with single co-situs agrochemical application7.

4.1.4. They permit the meeting of the full requirements of crops grown under plastic cover (protected crop cultivation), and multi-cropping by a single application.

4.1.5. They significantly reduce possible losses of nutrients, particularly, between applications, and uptake by the plants through a gradual release. They also reduce evaporation losses. This substantially decreases the risk of environmental pollution18-21.

4.1.6. They also contribute to a reduction in relevant gas emissions (N2O) 22-24.

4.2. The possible disadvantages
Slow and controlled-release or stabilized formulations also have possible disadvantages:

4.2.1. There are no standardized methods for reliably determining the pattern of release. Broadly speaking there appears to be a lack of correlation between the data resulting from laboratory testing - which are made available to the consumer - and the actual functioning of the bioactive agent release pattern in field conditions.

4.2.2. With regard to chemical reaction products, such as urea-formaldehyde fertilizers, it appears that a proportion of the nitrogen contained may be released to the soil solution extremely slowly (or not at all).

4.2.3. Some formulations may also exhibit a burst release of the agrochemicals, causing damage to turf or to the crop. Further, this rapid initial release, even if it does not cause damage, is at a higher cost than that of the equivalent amount of conventional (non slow or controlled release) soluble agrochemical. Also, some of the coated granules may be so thickly coated that the agrochemical contained in these granules may not be released during the crop demand period.

4.2.4. Application of coated controlled-release agrochemicals may drastically alter the pH of the soil. For example, in case of sulphur coated Urea (SU) if large amounts of it are applied, since both sulphur and urea contribute to increased acidity.

4.2.5. Polymer coated or encapsulated controlled-release formulations may leave undesired residues of synthetic material on the fields. Their use may thus lead to an undesirable accumulation of plastic residues25. Further, if the polymer ‘shell’ fragments do not compose, the fragments, which are smaller than sand size particles, become part of the soil.

4.2.6. The cost of manufacturing coated or encapsulated controlled release formulations is still considerably higher as compared to the production of their conventional counterparts. Thus their cost benefit ratio at present prevents their wide use in general agriculture7, 9-10, 25-30.

4.2.7. Coated/encapsulated controlled-release formulations call for higher marketing (specialized advisory service) and sales expenses than conventional formulations.

5. SOME EXISTING POLYMER-AGROCHEMICAL FORMULATIONS:
5. 1. Condensation products of urea and aldehydes (methylene ureas)/ nitrogen reaction products

Among the nitrogen reaction products designed mainly for use on professional turf, in nurseries, greenhouses, on lawn, and for garden and landscaping, three types have gained practical importance 9, 31:
Ø  urea-formaldehyde (UF),
Ø  urea-isobutyraldehyde (IBDU®), and
Ø  urea-crotonaldehyde (CDU®).

Whereas the urea-formaldehyde reaction products have the largest share of the slow-release fertilizer market, IBDU® and CDU®-based products are less widely used, due to even greater cost constraints in their production.

5. 1. 1. Urea-Formaldehyde (UF) - 38% N
Among the manufactured slow and controlled-release fertilizers, urea-formaldehyde based products still have the largest share worldwide. This is also the first group on which research concerning slow release of nitrogen was carried out.  Urea-formaldehyde is formed by the reaction of formaldehyde with excess urea under controlled conditions (pH-value, temperature, mol proportion, reaction time etc.) resulting in a mixture of methylene ureas with different long-chain polymers.

The main problem in the manufacture of urea-formaldehyde as a slow-release fertilizer type is to produce condensation-oligomers in a desired proportion. The influence of the proportion of the different methylene ureas on the release of nitrogen and the nitrogen efficiency can be determined by the Activity Index (AI).

Fraction I: cold water soluble - CWS (25°C) containing residual urea, methylene diurea (MDU), dimethylene triurea (DMTU) and other soluble reaction products. The nitrogen of Fraction I is, depending on soil temperature, available slowly (AAPFCO 73, N-29 and N-30).

Fraction II: hot water soluble - HWS (100°C) containing methylene ureas of intermediate chain lengths: slow-acting nitrogen.







Whereas in the past urea-formaldehydes had an AI of about 40 to 50, more recent urea-formaldehyde formulations are reaching AI-values of 55 to 65. The Association of American Plant Food and Control Officials (AAPFCO) are setting an AI of 40 as a minimum with at least 60% of its nitrogen as cold water insoluble nitrogen (CWI N) and a total content of nitrogen of at least 35%. Un-reacted urea nitrogen content is usually less than 15% of total nitrogen. The release pattern of nitrogen from UF fertilizers is a multi-step process (dissolution and decomposition). In general there is some proportion of N slowly released (Fraction I); this is followed by a more gradual release over a period of several (3 to 4) months (Fraction II), depending on the type of product. However, the release pattern is also influenced by the temperature and moisture as well as by soil organisms and their activity.

In general urea-formaldehyde fertilizers show a significant slow release of nitrogen combined with a good compatibility with most crops.

5. 1. 2. Isobutylidene diurea (IBDU®) - 32% N
Isobutylidene diurea is formed as a condensation product by a reaction of isobutyraldehyde (a liquid) with urea. In contrast to the condensation of urea with formaldehyde resulting in a number of different polymer chain lengths, the reaction of urea with isobutyraldehyde results in a single oligomer. However, in order to obtain an optimal proportion of IBDU, it is important that the reaction is stopped by neutralization at the point at which it is yielding most IBDU. The theoretical nitrogen content is 32.18%. The AAPFCO5 definition requires a minimum of 30%, of which 90% is cold water insoluble (prior to grinding). The release mechanism functions by gradual hydrolysis of the sparingly water insoluble IBDU to urea which is transformed to ammonium ions and further to nitrate (by soil bacteria).

5. 1. 3. Crotonylidene diurea (CDU®) - 32.5% N
Chisso Corporation holds the trademark for ‘CDU’ urea-crotonaldehyde slow release nitrogen. Crotonylidene diurea is formed by the acid-catalyzed reaction of urea and acetic aldehyde. When dissolved in water it gradually decomposes to urea and crotonaldehyde. As with IBDU, with CDU also particle size greatly influences the rate of nitrogen release (very delayed release with larger particle size). CDU is decomposed by both hydrolysis and microbial processes in the soil; temperature, soil moisture and biological activity affect the release rate, though even in acid soils the degradation is slower as that of IBDU. The agronomic performance is similar to IBDU. CDU is produced in Japan (Chisso Corp.) according to a production process developed by Chisso (modified BASF production process; BASF: Crotonaldehyde + Urea, Chisso: Acetaldehyde + Urea). In Japan and Europe, its main use is on turf and in speciality agriculture, typically formulated into granulated NPK fertilizers.

5.  2. Coated/encapsulated controlled-release fertilizers
These are conventional soluble fertilizer materials with rapidly available nutrients which after granulation, prilling or crystallization are given a protective (water-insoluble) coating to control the water penetration and thus the rate of dissolution and the nutrient release. A product containing sources of water soluble nutrients, release of which, in the soil is controlled by a coating applied to the fertilizer 5.

There are three different groups of coated/encapsulated controlled release fertilizers, using as coating material:

Ø  Sulphur (O. M. Scott produced a sulphur only coated urea with about 19% S).
Ø  polymeric / polyolefin materials, and
Ø  Sulphur plus polymeric, including wax polymeric materials (As for example according to United States Patent Number 5,599,374, Feb. 4, 1997, John H. Detrick “Process for producing improved sulfur-coated urea slow release fertilizers”).

Agents currently used for coating/materials used in manufacturing fertilizers with controlled release of nutrients are:

Ø  polymers (e.g. PVDC-based copolymers, polyolefins, polyurethane, urea-formaldehyde resin, polyethylene, polyesters, etc., The kind of polymeric material finally used by the individual manufacturer mainly depends on the chemical and physical properties, the cost, the availability and the patent situation.
Ø  fatty acid salts (e.g. Ca-stereate),
Ø  latex, rubber, guar gum, petroleum derived anti-caking agents, wax (The word ‘latex’ originally meant an emulsion of natural rubber, such as is obtained by cutting the bark of rubber trees. However, in chemistry all colloidal dispersions of polymers in an aqueous media are called latex.),
Ø  Ca+Mg-phosphates, Mg-oxide, Mg-ammonium phosphate + Mg potassium phosphate,
Ø  phosphogypsum, rock phosphate, attapulgite clay,
Ø  peat (encapsulating within peat pellets: organo-mineral fertilizers, OMF),
Ø  neemcake/ nimin’-extract (extract from neem cake).

In comparison to urea reaction products, coated fertilizers, particularly those coated with a multi-layer coating of sulphur and a polymeric material, may present more favourable economics. To obtain a further reduction of total fertilizer costs, coated/encapsulated fertilizers are increasingly used in blends with conventional fertilizers in different ratios (mixtures of encapsulated and non-encapsulated N, NP or NPK fertilizers).

Furthermore, coated/encapsulated controlled-release fertilizers offer greater flexibility in determining the nutrient release pattern. They also permit the controlled release of nutrients other than nitrogen. Nyborg et al.34,  have found in greenhouse and field tests that slowing the release of fertilizer P into the soil by coating fertilizer granules (polymer coating) can markedly increase P recovery by the crop and the yield.

5. 3. Sulphur coated urea (SCU)
Within the group of coated fertilizers sulphur coated urea has gained the greatest importance to date. The sulphur coating may be considered to be an impermeable membrane which slowly degrades through microbial, chemical and physical processes. The concentration of nitrogen (and other nutrients) and its release varies with the thickness of the coating in relation to the granule or prill size; it is also influenced by the purity of the urea used35. The basic production process was developed in laboratory and pilot scale tests in 1961 by TVA (Tennessee Valley Authority, Alabama).

There are four reasons favoring the combination of urea and sulphur:
Ø  Urea with 46% N is highly concentrated, thus coating with sulphur still results in a product with 30-40% N.
Ø  Urea is rather liable to leaching and/or to ammonia losses by volatilization; consequently covering urea granules with an impermeable sulphur membrane significantly reduces such losses.
Ø  Sulphur is a low cost product.
Ø  Sulphur is a valuable secondary plant nutrient.

The quality of SCU is characterized by the rate of N released into the soil solution within seven days. This seven-day dissolution rate method (developed by TVA) permits the generating of a leach profile of the tested SCU. Unfortunately, the results obtained cannot be correlated reliably to the release pattern under practical field conditions10, 26. Currently marketed SCU fertilizers have dissolution values of about 40% to 60%. ‘SCU-30’ designates a product with a nitrogen release of 30% within seven days, under prescribed conditions. With such a high dissolution rate a rather rapid initial effect is to be expected. In fact, there have repeatedly been claims of a too-rapid release of nitrogen36.

5. 4. Polymer-coated/encapsulated controlled-release fertilizers
Standard SCU has dominated the market for several years. However, horticultural and lawn-garden markets in particular require a more sophisticated control of nutrient release. Thus a whole series of controlled-release fertilizers has emerged. New and modified coating methods have been developed37-41.

Polymer coatings may be either semi-permeable membranes or impermeable membranes with tiny pores. The main problems in the production of polymer-coated fertilizers are the choice of the coating material and the technical coating process applied 9, 11, 42-45.

Since nutrient release through the polymer membrane/capsule of controlled-release fertilizers is not significantly affected by soil properties, such as pH-value, soil salinity, texture, microbial activity, Redox-potential, ionic strength of the soil solution, but rather depends on temperature and the moisture permeability of the polymer coating, it is possible to predict precisely the nutrient release for a given time 46-47.

Polymer-coated fertilizer technologies vary greatly between producers, depending on the choice of the coating material and the technical coating process applied: the Pursell RLCTM (Reactive Layers Coating) polymer technology (POLYON®) is a polyurethane; this is also the case with Haifa (MULTICOTE®) and Aglukon (PLANTACOTE®); Chisso polymer technology (MEISTER®, NUTRICOTE®) is a polyolefin; Scotts polymer technology (OSMOCOTE®) is an alkyd resin.

Thus, the longevity of the polymer coated product, i.e. the rate of nutrient release can - to a certain extent - be controlled by varying the type and the thickness of the synthetic material used in coating48-49. The quantity of coating material used for polymer coatings of conventional soluble fertilizers depends on the geometric parameters of the basic core material (granules to surface area, roundness, etc.) and the target of longevity. In general the coating material represents 3-4 (RLCTM) to 15% (conventional coating with polymers) of the total weight of finished product. The longer the supply of nutrients needs to last, the smaller has to be the amount of nutrients released per time unit. The producers indicate the period of release, e.g. 70 days release (at constant 25°C), or 140 days release, up to 400 days release.

The problem is that, in order to guarantee the longevity of the polymer coated product, no bio-degradation, chemical-degradation or mechanical destruction of the coating should occur during the active time of the applied fertilizer. Consequently, it is only after the fertilization function of the product, that microbial attack and mechanical destruction of the empty shell should occur to decompose the coating over time27. Polymer coated urea (PCU) consists of urea granules coated with a polymeric resin; it typically contains about forty percent (40-44%) nitrogen. Coating material made of photo degradative polymer is easily decomposed by photochemical process in the soil. However, some polymer coated fertilizers present an as yet unsolved problem of persistence in the soil of the synthetic material used for encapsulation.

5. 5. Sulphur coated/polymer-encapsulated controlled-release fertilizers.
Polymer/sulphur coated fertilizer products (PSCU or PSCFs) have been introduced into the market recently in the United States, with 38.5 - 42% N, 11 - 15% S and less than 2% polymer sealant (LESCO Inc. POLY PLUS® PCSCU 39N, PURSELL TriKote® 9 PCSCU 39-42N and Scott POLY-S® PCSCU 38.5-40N; regular size of all products 1.8 mm to 2.9 mm, nominal 2.4 mm). These products have a primary coating of sulphur and a secondary coating of a polymeric material. The reason for this hybrid coating is to combine the control release performance of polymer-coated fertilizers with the lower cost of sulphur-coated fertilizers48-50.

5. 6. Granular controlled release agrochemical compositions
For example, US Patent No. 6,682,751 discloses a granular pesticide comprising a core material coated with an inner polymer membrane formed in-situ on the core material with a pesticide applied to the inner polymer membrane and an outer controlled release polymer membrane formed in situ on the pesticide to permit controlled release. The pesticide may be incorporated in several "sandwich" layers. Again, the products of US Patent No. 6,682,751, are structurally different from the products of the present invention and fail to exhibit a controlled rate of release of the pesticide over a period greater than about 30 days from the date of initial exposure of the product to moisture in a manner such that essentially all of the pesticide coated on the core is released from the granular composition before the water soluble portion of the core material is released from the product.
Similarly, US Pat. No. 6,080,221 discloses the coating of porous surfaces of fertilizer particles with tenacious pesticide-resin solids to form attrition resistant fertilizer-pesticide combination particles. In this disclosure, the pesticide is dispersed in a resinous matrix, which is subsequently bonded onto and into the fertilizer surface. Patent US Pat. No. 4,971,796 describes another slow release granular product in which the pesticide is matrixed into the coating. The granule comprises one layer of proteinaceous material or more layers of proteinaceous material with intermediate spacing layers. The active, ingredient is in the proteinaceous layer and is released when this layer degrades. The release rate is changed by varying the cross linking or the thickness of the layer. The products of US Patent No. 6,080,221 and 4,971,796 fail to exhibit a controlled rate of release of the pesticide over a period greater than about 30 days from the date of initial exposure of the product to moisture in a manner such that essentially all of the pesticide coated on the core is released from the granular composition before the core material is released from the product.
An EP Patent 0755370 discloses other matrix release products which are mixtures of a nitromethylene or related substances with fertilizers and glue. EP Patent 1063215 describes briquettes that slowly release active ingredients. The slow release is obtained via absorption or adsorption of the active ingredient onto solids with high surface area.
Exemplary of suitable polymers for use in the present invention are such thermoplastic coating materials as vinyl resins such as poly(vinyl acetate), poly(vinyl alcohol), poly(vinyl chloride), poly (vinylidene chloride), polyvinyl pyrrolidone), poly(vinyl acetal), ρoly(vinyl methylacetamide); polyolefines such as polyethylene, polypropylene, polyisobutylene; styrene- based polymers; acrylic polymers; polyesters such as ρoly(alkylene terephthalate), poly(caprolactone); poly(oxy alkylene)s, such as poly(ethylene oxide), poly(propylene oxide); cellulose derivatives, such as celluloseacetate; polyamides;ρolyamines; polycarbonates; polyimides; polysulfones; polysulfides; polysaccharides and the like. Recently, Nayak et. al.,51 India, have reported the use of crosslinked chitosan matrices and chitosan hydrogels for the controlled release of agrochemicals. The same group is also investigating on the potential of biodegradable polymer nanocomposites for controlled release of agrochemicals.

5. 7. Partly polymer-encapsulated controlled-release fertilizers/ Mixtures of encapsulated and non-encapsulated N, NP or NPK fertilizers.
Another possibility in order to combine the advantage of controlled release nutrient supply with the lower cost of conventional fertilizers, is to mix polymer-coated granules for instance in a ratio of 1: 1 with non-encapsulated granules of the same fertilizer type25.

In Germany, an NPK fertilizer (with a minimum content of 3% N, 5% P2O5, 5% K2O), of which only 50% of the granules are polymer coated, is registered under the German fertilizer law52. In 1997 a similar NPK fertilizer type has acquired registration10 with only 25% polymer-coated granules, offering a greater flexibility in use and further improved economy. Such partly polymer encapsulated controlled-release fertilizers, i.e. mixtures of encapsulated and non-encapsulated granules or prills, are also in use in Japan.

5. 8. Neem- or ‘Nimin’-coated urea
The Indian neem tree, Azadirachta indica, has a number of traditional uses, based on the insect repellent and bacteriostatic properties which are contained in its various parts. The oil obtained from its fruits is a valuable raw material for the production of pharmaceuticals and body care products.

The press cake from the production of neem oil has a controlled release and nitrification inhibiting effect, besides other possible uses. It is therefore frequently recommended to add neem cake to the N fertilizer (i.e. urea) to form NCU (neem coated urea) or NICU (nimin = extract from neem cake) coated urea to improve the nitrogen use efficiency and to reduce losses53. However, the use of NCU or NICU is apparently not practiced to any extent by farmers, neither in India where the tree originates, nor in other tropical countries to which it has been brought in the past. The main reason for this might be the difficulty to obtain sufficient quantities of neem cake at village level, the additional labour for blending or the lack of a corresponding technical process. Since the benefits of the practice of using NCU are not always reliable, this might also be an obstacle to the use of neem as controlled release agent or nitrification inhibitor.

Suri54 regrets that no serious attempt has been made to develop technology to coat urea with neem on a commercial scale. The fertilizer particles are incorporated throughout carrier matrices. However, to achieve the desired slow release effect, a large quantity of carrier material is necessary (up to 40%). Therefore only low-grade fertilizer formulations are possible (e.g. NPK 10-10-10 or NPK 5-15-10). In general the carrier material is a mix of molten waxes and of surfactants and polyethylene glycols (polymeric matrices; styrene-butadiene rubber formulations and others).

5. 9. Supergranules and other Controlled-release fertilizers in a matrix
This group of special fertilizer products has been given special attention, particularly in tropical and subtropical regions. Conventional soluble fertilizers are formulated in compacted form, with a relatively small surface-to-volume ratio. This results in a slow release of nutrients, or relatively slower release, into the soil solution. Some of these special formulations also contain urea-formaldehyde (UF) or IBDU®. Whereas in Western Europe such super granules, briquettes, tablets or sticks are preferably used for fertilizing trees and shrubs, as well as some vegetables, such as tomatoes, pot plants etc., in tropical regions the preferred use is in irrigated rice55-57.

5. 10. Microemulsions in agrochemicals
Micro emulsions have a variety of applications in agrochemical industry, of which pesticide-containing systems are relatively old. To minimize the side effects of excessive use of agrochemicals on the ecosystem, chemicals with greater specificity and less persistence are developed. The ease of handling and lower requirement of smelly solvents goes in favour of the use of micro emulsions. However, increased efficacy of insecticides when applied as ‘micro colloidal aqueous emulsion’ instead of micro emulsions has also been demonstrated. O/W micro emulsions of organic, water insoluble phenoxy herbicides optionally dissolved in a hydrocarbon solvent have been shown to be appreciably more effective than the corresponding emulsions in the control of plant growth. Micro emulsions formulated with a hydro tope solubilizing the herbicide can be promising. The choice of hydro tope and the emulsifier could be largely determined by the water solubility of the herbicides. W/O micro emulsions have been suggested to enrich the mineral-deficient crops with respect to trace metals such as iron. The oil medium of the micro emulsion can hold the element in contact with the leaves even during moist conditions, until the trace element is adsorbed.

Since most agrochemicals are water insoluble and become deactivated with water, their formulation in o/w micro emulsion is advantageous. The much finer droplet size of the micro emulsion leads to higher penetrability, much larger contact area of the active substance to the treated surface and a much more even distribution during application. The infinite stability of the micro emulsion and the high concentration of surfactants generally needed for a formulation are advantageous. A definite relationship exists between herbicides and surfactant structures for mixed herbicide penetration.

5. 11. Insecticide-Polymer Formulations

Chitosan, the N-deacetylated derivative of chitin, is a potential biopolysaccharide owing to its specific structure and properties. Scientists have reported on the synthesis of 24 new chitosan derivatives, N-alkyl chitosans (NAC) and N-benzyl chitosans (NBC), that are soluble in dilute aqueous acetic acid. The different derivatives have been synthesized by reductive amination and analyzed by 1H NMR spectroscopy. A high degree of substitution (DS) can obtained with N-(butyl)chitosan (DS 0.36) at a 1:1 mole ratio for NAC derivatives and N-(2,4-dichlorobenzyl)chitosan (DS 0.52) for NBC derivatives. Their insecticidal and fungicidal activities were tested against larvae of the cotton leafworm Spodoptera littoralis (Boisduval) (Lepidoptera: Noctuidae), the grey mould Botrytis cinerea Pers (Leotiales: Sclerotiniaceae) and the rice leaf blast Pyricularia grisea Cavara (Teleomorph: Magnaporthe grisea (Hebert) Barr). The oral feeding bioassay indicated that all the derivatives had significant insecticidal activity at 5 g kg-1 in artificial diet. The most active was N-(2-chloro-6-fluorobenzyl) chitosan, which caused 100% mortality at 0.625 g kg-1, with an estimated LC50 of 0.32 g kg-1. Treated larvae ceased feeding after 2–3 days; the mechanism of action remains unknown. In a radial hyphal growth bioassay with both plant pathogens, all derivatives showed a higher fungicidal action than chitosan. N-Dodecylchitosan, N-(p-isopropylbenzyl) chitosan and N-(2,6-dichlorobenzyl)chitosan were the most active against B cinerea, with EC50 values of 0.57, 0.57 and 0.52 g litre-1, respectively. Against P grisea, N-(m-nitrobenzyl) chitosan was the most active, with 77% inhibition at 5 g litre-1. The effect of different substitutions is discussed in relation to insecticidal and fungicidal activity58.

5. 12. Weedicide-Polymer Formulations
The release of alachlor and atrazine into aqueous solution from controlled-release formulations (CRFs) prepared from alginate and pectin, with and without the addition of clay minerals, was studied. The rate of release of the incorporated herbicides was a function of both the properties of the herbicide and the composition of the CRF. The rate of release of herbicides was related their aqueous solubility; the greater the solubility of a compound, the more rapid its release from a CRF. The rate of release of the chemicals from pectin-based CRFs was generally greater than from alginate-based CRFs. This seems to be related to the relatively large number of methoxy groups in the pectin, which hinders the gelation process and results in a more porous matrix than in the case of alginate. The addition of sodium montmorillonite to these CRFs was found to have a profound inhibitory effect on the release of alachlor. This was attributed to the sorption of the herbicide to the clay mineral. Other clays generally had little or no effect on the rate of release of the active ingredient. Bead radius was observed to have a profound effect on release rates; the smaller the radius, the greater the release rate. Release rates conformed to the Higuchi equation for a diffusion controlled release mechanism from a porous polymer in which the active ingredient is present in excess of its solubility59.

Alachlor was released from a controlled-release formulation (CRF) when applied to a sandy loam soil under conditions of constant temperature and moisture and achieved concentrations of 0.1-0.2 mg/kg after 1 week. Soil concentrations of 0.2-0.8 mg/kg were maintained for at least an additional 8 weeks. A large portion (35-70%) of the active ingredient was still present in the CRFs at the conclusion of the experiment. Application of alachlor as the commercial formulation resulted in 50% dissipation after only 3-4 days. Alachlor released from CRFs with a smaller diameter resulted in higher soil concentrations (1.2 mg/kg) after 18 days. In column leaching studies the leaching of alachlor, atrazine, and trifluralin from CRFs was considerably reduced with respect to leaching of the same compounds from commercial formulations. The release of alachlor from an Al-pillared clay CRF and its subsequent transport in soil columns showed that pillared clays can be used for controlled release of herbicides, but more work is necessary before the effects of the many factors involved in the release of the active ingredients from pillared clays are completely understood60.

6. SLOW AND CONTROLLED-RELEASE FORMULATIONS IN TROPICAL CROPS (RICE)
The possibilities of making use of controlled-release formulations on agricultural field crops in tropical countries should be much greater than in the agriculture of temperate regions. This applies especially to regions with light-textured soils under heavy rainfall or irrigation. Under these conditions losses of agrochemicals from the conventional formulations are high.

Shaviv and Mikkelsen61 list the following issues, regretting that the use of slow and controlled-release formulations is still very limited due to their relatively high cost, in spite of the potential benefits. “Yet there exist several other issues related to the efficient use of SRF/CRF that deserve much more attention and deeper insight. If properly treated, these issues should lead to a more significant contribution of SRF/CRF to agriculture and the environment. Among these are:

ü  Utilization of advanced technologies and development of new concepts for preparing more cost effective SRFs.
ü  Better assessment of expected benefits to the environment from using SRF/CRF. This should include estimates of the economic significance of reducing pollution of ecosystems (air, water, etc.) and sustaining soil productivity.
ü  Quantification of the economic advantages resulting from reduced losses of nutrients and from labour saving.
ü  Improved assessment of economic benefits expected from reduced osmotic stress and specific toxicity as a result of synchronizing release with plant demand.
ü  Induction of synergistic effects between chemical forms of nutrients by controlling the exposure of plants to desired compositions.
ü  Better understanding of the mechanisms controlling release rate and pattern and the major environmental factors (e.g. temperature, moisture, microorganisms, acidity, soil type, etc.) which affect them.
ü  Development of tests for characterizing the release performance of SRF/CRF in order to improve industrial quality control and farmers’ decision making process.
ü  Construction of mechanistic-mechanical models for predicting release of nutrients under laboratory and field conditions and as design tool for the technologist.

Achievements in the above-mentioned directions will greatly depend on the possibility of organizing multi-disciplinary R&D work for dealing with such complex problems, and probably even more on the priority and support given to such work by our society.”

Controlled-release formulations are significantly less sensitive to air humidity and temperature fluctuations (better storage characteristics) and less susceptible to leaching or denitrification.

For example, in rice, the soil-fertilizer regime is completely different from that of other crops, particularly as concerns applied fertilizer nitrogen62-64. Under flooded soil conditions, losses through denitrification may be high. When NO3-N containing fertilizers are applied or if NH4+-N nitrifies prior to flooding, losses through denitrification may be large. NH3-N may also be lost to the atmosphere, when floodwater becomes alkaline during daylight hours, as algae consume all available carbonate65. For this reason, ammonium-N or amide-N containing fertilizers have been given preference in the fertilization of paddy rice. If these types of fertilizers are applied in floodwater, losses may be reduced. However, losses are significantly higher where flooding and drying (lack of irrigation water, cultivation under natural rainfall conditions) alternate.

Where farmers simply broadcast urea into standing floodwater66, urease activity at the flooded soil surface leads to rapid urea hydrolysis, high ammoniacal-N concentrations in the floodwater and potentially high volatilization losses when weather conditions facilitate the removal of NH3 from the water-air interface. Under such conditions slow and controlled-release fertilizers should be much more effective, in particular polymer-coated fertilizers.

In India, in a field trial on rice conducted by Singh and Singh67 neem cake (as a slow-release agent) coated urea (NCU) produced substantially higher yields than prilled urea. Also Budhar et al.68  in a trial on rice achieved a significantly higher yield with NCU as compared to conventional urea. DE et al.66 came to the conclusion that more than 30 kg/ha N can be saved in rice with neem-extract (nimin) coated urea (NICU) in comparison to prilled urea. Also Geetha Devi et al.55 produced higher yields in field experiments in rice with NCU than with prilled urea. However, in these experiments urea super granules gave the highest yield. Also Jena et al.69 and Kumar et al.70 obtained the highest yields in rice with NCU. However, Pandey and Tripathi71 did not obtain improved yields with NICU. Although in the majority of cases neem-coated or nimin-coated urea, NCU or NICU, was equal in yield - or even better - than uncoated or other coated urea fertilizer types, this has apparently not led to commercialization and accordingly, there is no practical use of neem coated urea in the fertilization of rice in India (see section Neemor ‘Nimin’-coated urea).


Fig. 4. Layered application of a controlled release fertilizer (Meister®) in a rice nursery box (from bottom to top: soil - controlled-release fertilizer - rice-seedlings - soil). (Kaneta, Y.)

Kaneta72 and Kaneta et al.73 compared coated urea with a conventional compound fertilizer in one single application in a nursery box of non-tillage rice. In his experiment the absorption of N from coated urea was greater than that from the conventional fertilizer (recovery of 79% of N from coated urea at maturity). This also resulted in a greater number of grains and a higher yield.

7. SOME NOVEL RELEASE SYSTEMS: POLYMERIC-PHEROMONE DISPENSERS
7. 1. Sprayable Pheromones
Microencapsulated pheromones are enclosed in a polymer capsule that controls the pheromone release rate. These capsules are small enough and durable enough to be applied in water through normal airblast sprays in the same manner as conventional pesticides. This makes them very attractive to use by many fruit growers. Residual activity is generally up to 4 to 6 weeks, which gives them some flexibility in pest management programs but also means they may need to be reapplied several times in a season for a target pest. Residual activity may be reduced by rainfall soon after application and a sticker type spray adjuvant is often recommended. Currently, the only effective materials are for the control of Oriental fruit moth (3M Sprayable Pheromone OFM, Check-Mate OFM-F) and peach tree and lesser peach tree borers. Several formulations for codling moth and several species of leaf rollers have been tested and even sold commercially, but they have not given reliable control.

7. 2. Hand-Applied Dispensers
Include systems with an impermeable reservoir fitted with an impermeable membrane for regulating pheromone release. Pheromone-impregnated polymer spirals, ropes, dispensers, or tubes (Isomate products) are currently the most commonly used products. Wires, clips, or circular twin tubes allow these dispensers to be twist-tied, clipped, or draped directly onto the plant. The larger reservoirs of these products allow for longer residual activity ranging from 60 to 140 days. This may allow early season applications to suppress mating for most or all of the growing season depending on the type of dispenser and pest species. Application rates vary from one to several dispensers per tree (5 to 400 dispensers per acre) and can be labor intensive. Costs for these products tend to be significantly higher than the chemical control programs they are replacing, especially in high pest pressure situations where supplemental insecticides would be needed for acceptable control.
8. BIODEGRADABLE POLYMERS: THE CUTTING EDGE MATERIALS
      Are Non toxic.
      Possess Variable biodegradability allows many types of formulations.
      Are easily processable into final product.
      Have an acceptable shelf-life
      Prevents excessive loss of pesticide to run off during rain falls.
      Are finally absorbed & disappeared
      Provide increased handling safety.

9. CONCLUSION

Biodegradable polymers can contribute largely to this technology by adding its own character to the drugs. In this particular approach, the copolymers of PLA, PCL, Starch, Chitosan and Soy Protein can be commonly used, because the copolymers can be prepared in the moderate condition, has the appropriate degradability and has the low crystallinity, enough to be mixed well with many kinds of agrochemicals. There are some formulations for the controlled delivery systems, for example, films, gels, porous matrices, microcapsules, micro spheres, Nano particles, polymeric micelles and polymer-linked drugs.  One of the most important advantages of biomaterials is that linkage can be designed to control where and when the drug is released.

There is no doubt that rice is one of the most interesting agricultural crops for the use of encapsulated controlled-release formulations. Therefore, any further development in practical application (economic blends), in the characteristics of polymer-coated agrochemicals, the granules of which do not float, but sink down immediately on application, and in production processes (mass production) reducing the production costs, will undoubtedly contribute to the use of controlled-release fertilizers in rice also in countries other than Japan. However, further extensive testing under practical field conditions comparing controlled-release fertilizers with the most advanced conventional fertilizer management systems followed by the calculation of the respective benefits (the different value/cost ratios), is indispensable.

The main obstacle to the wider use of controlled-release formulations will remain the high cost of these special agrochemical types, as compared to conventional counterparts. In spite of the advantages of slow or controlled-release formulations in significantly improving nutrient efficiency (mainly of nitrogen), disease resistance, stress tolerance, and minimizing undesirable losses to the environment, unless the cost of slow and controlled-release formulations can be significantly lowered, it is unlikely that these types of formulations will gain widespread use on low cash value (i.e. in conventional agricultural) crops. To achieve widespread use, the value/cost ratio (VCR) would need to be at least 3 to 1. This would indeed be a challenging area of research with unlimited future prospects.

“The drug delivery system was developed for the purposes of bringing, up taking, retaining and releasing the drugs at the right timing, period, dose and place. Slow-release formulations achieve improved efficiency of agrochemical use and minimize the losses to the environment through mechanisms that retard the release of plant available nutrients or bioactive agents in the soil. These products provide important tools in environmentally responsible crop management and protection; therefore, increased use and market share for these products over the next few years is predicted, especially in agricultural crop markets”.

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