search.noResults

search.searching

dataCollection.invalidEmail
note.createNoteMessage

search.noResults

search.searching

orderForm.title

orderForm.productCode
orderForm.description
orderForm.quantity
orderForm.itemPrice
orderForm.price
orderForm.totalPrice
orderForm.deliveryDetails.billingAddress
orderForm.deliveryDetails.deliveryAddress
orderForm.noItems
currently a fully viable financial market for the material as the price for recycled fibreglass is too low to promote the industry.


The major current options are landfill, though some nations are now restricting the disposal of FRP materials in landfill space. Whilst financially viable options are currently limited, the market is being developed with crushed FRP material being used in, amongst others, concrete, tarmac and also as filler for other FRP items. The market is well intentioned, though as a cost model appears to have limited application, and importantly is more marginal in SIDS due to a


“The main aim is


to achieve end-of- life management leading to either reuse (re- purposing) or recycling.”


lack of infrastructure to recycle. If this model is used on SIDS it will likely incur significant off-island transport costs for FRP material.


Research and trials are considering options that include pyrolysis where material is burned at temperatures to recover fibres for re-use (though resins are lost in combustion) and solvolysis where chemical replacement releases the resins and fibres for re-use; though these processes are expensive and not fully commercially viable at present, researcher and commercial groups are working towards financial feasibility. With regard to achieving financial sustainability to make end-of-life FRP boat disposal viable, instruments such as a levy on manufactures have been suggested and the option of charging users for end-of-life FRP disposal is potentially being trialled in France.


The environmental effects of current disposal options are discussed. Burning, previously practised on some SIDS, is known to release highly toxic compounds with a range of possible effects on biological organisms. Landfill options are largely related to the amount of space taken up, which in SIDS is a significant issue. FRP chemical breakdown and risk in landfill has been considered, though degradation is viewed as unlikely with FRP material, showing little change over time. At sea disposal is less well understood and whilst deliberate scuttling has been used as an option, FRP boats are often just left to decay on abandoned moorings.


MARPOL makes it illegal to discharge plastic at sea, but FRP hulls are not covered as MARPOL is pertinent to shipborne garbage and the London Convention and London Protocol do not explicitly address FRP vessels.


There is limited research on at sea disposal though it is evident that dumped FRP vessels do not make suitable artificial reefs as


they are likely to break up, and may be moved by currents and wave action potentially harming sensitive features (e.g. reefs, seagrass) and communities. In addition, FRP material will ultimately break up to potentially become microplastics with, as yet, poorly understood ecological pathways and direct biological effects, though its known plastics sorb organic and heavy metal pollutants potentially making them more bioavailable to organisms which may ingest plastics.


The problem of end-of-life FRP boat disposal and management has taken global proportions with an increasing number of vessels needing management. This is particularly pertinent to SIDS with space being a significant issue and disposal at sea having wider implications for the marine community on which people may be dependent and possible pathways to humans for plastics and associated pollutants. Some island nations are actively seeking options including pyrolysis and have halted at sea disposal with ongoing plans for FRP wreck management under the Nairobi International Convention on the Removal of Wrecks 2007 but as outlined, other legal instruments have poor applicability and the Nairobi Convention on wreck removal is targeted at vessels greater than 300 tonnes and to date has only been ratified by 41 states.


Research areas relating to management and disposal of end-of-life FRP hulls are numerous. Though current progress may be limited, further research into sustainable options is being addressed due to increasing interest and financial / policy drivers. The main aim is to achieve end-of-life management leading to either reuse (re-purposing) or recycling. With particular emphasis upon islands, these goals require appropriately targeted attention to avoid growing conflict with natural resources and unregulated disposal of FRP waste with potential environmental consequences.


The Report • December 2020 • Issue 94 | 61


Page 1  |  Page 2  |  Page 3  |  Page 4  |  Page 5  |  Page 6  |  Page 7  |  Page 8  |  Page 9  |  Page 10  |  Page 11  |  Page 12  |  Page 13  |  Page 14  |  Page 15  |  Page 16  |  Page 17  |  Page 18  |  Page 19  |  Page 20  |  Page 21  |  Page 22  |  Page 23  |  Page 24  |  Page 25  |  Page 26  |  Page 27  |  Page 28  |  Page 29  |  Page 30  |  Page 31  |  Page 32  |  Page 33  |  Page 34  |  Page 35  |  Page 36  |  Page 37  |  Page 38  |  Page 39  |  Page 40  |  Page 41  |  Page 42  |  Page 43  |  Page 44  |  Page 45  |  Page 46  |  Page 47  |  Page 48  |  Page 49  |  Page 50  |  Page 51  |  Page 52  |  Page 53  |  Page 54  |  Page 55  |  Page 56  |  Page 57  |  Page 58  |  Page 59  |  Page 60  |  Page 61  |  Page 62  |  Page 63  |  Page 64  |  Page 65  |  Page 66  |  Page 67  |  Page 68  |  Page 69  |  Page 70  |  Page 71  |  Page 72  |  Page 73  |  Page 74  |  Page 75  |  Page 76  |  Page 77  |  Page 78  |  Page 79  |  Page 80  |  Page 81  |  Page 82  |  Page 83  |  Page 84  |  Page 85  |  Page 86  |  Page 87  |  Page 88  |  Page 89  |  Page 90  |  Page 91  |  Page 92  |  Page 93  |  Page 94  |  Page 95  |  Page 96  |  Page 97  |  Page 98  |  Page 99  |  Page 100  |  Page 101  |  Page 102  |  Page 103  |  Page 104  |  Page 105  |  Page 106  |  Page 107  |  Page 108  |  Page 109  |  Page 110  |  Page 111  |  Page 112  |  Page 113  |  Page 114  |  Page 115  |  Page 116