BIOTECHNOLOGY IN COIR EXTRACTION AND WASTE UTILIZATION

By Dr.Anita Das Ravindranath(Senior Scientific Officer, CCRI ( CORD Vol XVII No.2, 2001)

 

Coir, the fibre extracted from the mesocarp of  the drupe of the coconut palm  cocos nucifea is used for the production of beautiful products like mats, matting, carpet, handicrafts etc.  (Table 1)  Coir suits very well for geotextiles and insulating materials and being environment friendly has and edge over synthetics for application in environmental operations.

The world production of coconuts is over 54000 million nuts and although great potential exists in the form of the coconut husk less than 25% is exploited for coir production.  Coir can be extracted from the husk by retting or by mechanical extraction.  The former  process involves retting of  the husks yield superior "white fibre" which is in good length, bright in colour and  fine  texture and ideal for the manufacture of coir products.  Mechanical extraction of the husk is instantaneous,  however, yields coir  fibre that initially is bright coloured but is photoxidised, rendering  the fibre of an inconsistent colour .  The texture of this  fibre is  harsh and therefore comparatively  extracted fibre is inferior.

Retting has disadvantages that it is a prolonged process (nine months),  pollutes the retting water through release of phenolic  substances, and is a cumbersome process (steeping of and drawing of each husk out from underwater on completion of retting) .  It is an established fact that the retting of husk is a microbiological  process wherein the binding materials  holding the fibres in the husk are biodegraded leading to the release of the fibre.  The retting process in a natural system was studied  from  April to  December and the changes occurring in the environment have been elucidated.  The pH in the water samples drawn at different stages of retting exhibit a variation, decreasing and increasing to various levels, the minimum pH of 5.5 was recorded in the sample drawn in the fourth month of retting .  (Chart  1).  The salinity was highest at 10 parts per thousand (ppt) in the month before steeping of husks (Zero)  &  ninth month  decreasing significantly to 1 ppt during the fourth, fifth and sixth months.  (Chart 1 )  The polyphenols  identified in the water samples  collected at different stages of retting are resorcinol, pyrogallic acid and catchall.

Application of selected strains  possessing  phenolytic properties have been  successfully conducted to reduce the period of retting of coconut husks to three months,  "COIRRETT" a bacterial cocktail has been able to  reduce the retting period to three months in the natural retting system and improve the  quality of  mechanically extracted fibre in 72 hours  in RCC tanks . The application  of a bacterial consortium grown on  husk leachate in  laboratory scale studies have been observed to yield encouraging  results indicating that coir extraction using biotechnology can eliminate  pollution caused by retting The quality  of the fibre has been observe to be equivalent to retted fibre as tested for light fastness ratings and degree of softness.

Biobleaching of Coir

 

           Bleaching process whitens the coir fibre and is conventionally carried  out  chemical bleaching  agents.  The application of biotechnology may be well adopted  for coir using bacterial and fungal cultures.  Bleaching/brightening of coir  may not reunite on the fibre surface lignin or the phenolic compounds compounds may be effective  if the surface lignin or the phenolic compounds released from the fibre could be destroyed   so that the released phenolic compounds  may not reunite on the fibre surface and  thereby turn more brown.  A biotechnological approach to bleaching involves the use of the enzyme  xylanase.  Fungi naturally produce xylanase to breakdown wood xylans into  carbohydrates.  The carbohydrates then become the energy source for the organism to grow.  The chemistry of xylanse  action is not completely clear but it appears to act by chopping up the  xylan enough to allow entrapped lignin moieties to escape. It has also been theorized  that xylanase breaks lignin moieties to escape.  It has also been theorized that xylanase breaks  lignin-xylan covalent bonds, thereby releasing the lignin.  Therefore microbial cultures eliciting ligninase, xylanase and hemicellulase have potentials for biobleaching of coir.

Biosoftening of Coir

Coir is a hard fibre with a very high content of lignin 40% and high extensibility (about 37%) which distinguish it from  other cellulosic fibres.  The high extensibility of the coir fibre is chiefly because the microfibrils in the cell wall lie in perfect helical spirals, extension of the fibre being related with the changes of the spiral angle, that is the angle which a microfibril element makes with the fibre axis.  Softening of coir can be attempted by application of biological softening agents, which can modify the  surface propertied of fibres and thus improve its physical characteristics and by elimination of the incrusting substance to a desirable extent without adversely affecting the other properties.  Microbial enzymes have potentials in bestowing  the properties of softness to coir and this remains an area for research yet to be  explored in coir .

Decolourisation and detoxification of processing effluents of coir.

The decolourisation  of coir retting effluents has been successfully carried out using chemical means at the Central Coir Research  Institute .   The process has been patented and can be carried out in combination with the COIRRET treatment on husks and fibre.  Biotechnological means for treatment of coir dyeing and  bleaching agents are being experimented at CCRI.  The enzymes produced by white rot fungi have potentials for application in this field.

Biodegradation of coir pith

The extraction of  fibre from husks  liberates huge amounts of dust or "Coir pith " which is lignocellulosic in nature .  The lignin in the pith can be biodegraded by lignin degrading microorganisms (Table lll) to yield an organic soil additive with excellent physical and chemical properties.  Its bountiful availability and ecofriendly nature renders it as an apt substitute for peat moss.

Conclusion 

The principal problem in environmental biotechnology is process control and predictability.  In contrast to contained biotechnology  involving bioreactors, where the process engineer is able to work  with homogeneous or semi-homogeneous systems and  to monitor and control all essential parameters, uncontained environmental applications are generally carried out in heterogeneous systems where critical process parameters may be difficult to monitor and even more difficult to control.  In such uses, processes are governed , more by ecological parameters pertinent to the  particular environment in which the process is carried out .  At present in the field of coir, ecological parameters which determine process efficiency are still being and yet to be studied.  Quantum increase in performance, predictability, spectrum and safety of environmental biotechnological applications for coir  be achieved, through:

                            *    elucidation of critical ecological processes which regulate or influence open biotechnological processes

                            *    development of genetic tools and strategies to  construct performance, and predictable process strains

                            *    investigation of the ecological impacts, including  possible perturbations, of environmental  biotechnology applications.

References

                1.    Abdul Aziz, P.K. and Nair. N.B. (1978)  The nature of pollution in the retting zones of the backwaters of Kerala,Aqua,Biol3pp41.62

               2 .    Das, A.R.1991.Processing of Coir -A biological approach to retting of coconut husks.  CORD Vol. Vll, pp.52-57.

               3.    Das A.R. and  Saema U.S, J.Sci. Ind. Res, Application  of microorganisms to enhance biodegradation of phenolic compounds        

                       and to improve retting of coir .57 (1998)825

               4.    Kirk,  Kent, T. (1984) degradaton of Lignin ,  In : Gibson, T.D.(Ed) Microbial degradation of organic compounds.  microbiology

                      series 13  M.Dekker Inc , New York

                5.    Mathew M, (1996). Coconut by 2010 AD - Problems and prospects. Proceedings of the National Conference on Coconut, 15

                6.    Mukherjee, A.K.(1996) Report on the FAO-UN Sponsored Project on Softening , Bleaching, Dyeing  and Printing of Coir,

                      Alleppey.

 

TABLE  I - Products from Coir

 

       ITEM                                                USE
Mats, Matting ,Mourzouks , Carpets Rugs      Floor Covering
Geotextiles      Protection of road, rail & canal Embankments
Drainage filter material for application as pipe envelopes.      To prevent flooding in grazing meadows, orchards , sport fields & gardens
Ship Requisites      Fender    Rope
Tent Components & Army Requisites      Salitah, Wall bag , Pole  &  Pin bag  Camouflage net , dumping net
Household Articles      House maids Kneeler, scrubber Shopping  bags.
Specialty Articles      Cricket pitch matting , billiard surrounds, golf tee mat, wrestling mat    

      tablemat tealeaf bags.

 

TABLE  II World- Area Under and Production of Coconut in Nut Equivalent in theDifferent Coconut Growing Countries of the World. (1999)

 

SL.No Country Area in million Percentage Share Production in      million nuts Percentage share
     1 F.S.Micronesia      17     0.14       40                    0.07
     2 Fiji       54       0.45       137     0.25
   3 India   1.908     16.03   14.925    27.57
   4 Indonesia   3.712     31.17    13.946    25.76
   5  Malaysia      226       1.91         580      1.07
   6 Papua New Guinea      260       2.81       1.020      1.88
   7 Philippines   3.077     25.83     10.504    10.40
   8 Soma        92       0.77           168           0.34
  9 Solomon Is               59       0.49           318      0.34
10 Sri Lanka 422 3.71 2.828 5.22
11 Thailand 372 3.12 1.108 2.05
12 Vanuatu 96 0.81 346 0.64
13 Vietnam 173 1.45 1.044 1.93
14 Palau 14 0.12 70 0.13
15 Other African Countries 662 5.56 2.294 4.24
16 Other American Countries 577 4.84 3.687 6.82
17 Other Asian Countries 96 0.81 747 1.38
18 Other Pacific Countries 72 0.61 349 0.65
  TOTAL 11.906 100 54.129 100

Source: APCC Statistical Year Book 1999 * Revised Fig. Coconut Development Board

TABLE  III - LIGNIN DEGRADING MICROORGANISMS

 

Microbe Classification Example
Actinomycetes

Soil bacteria

 

Nocardia, Streptomyces

Fungi Imperfecti

Soil fungi

Soft rot fungi

 

Fusarium

papulospora

Ascmycetes

Soft rot fungi

 

Chaetomium

Basidiomycetes Collybia, Mycena
While rot fungi Coriolus, Phanerochaete, Poria
Brown rot Gloeophyllum, Poria