• Aucun résultat trouvé

Co-composting of pig slurry with green wastes to prevent environmental impact of pig production in the Wallis archipelago, Pacific Ocean

N/A
N/A
Protected

Academic year: 2021

Partager "Co-composting of pig slurry with green wastes to prevent environmental impact of pig production in the Wallis archipelago, Pacific Ocean"

Copied!
1
0
0

Texte intégral

(1)

Co-composting of pig slurry with green wastes to

prevent environmental impact of pig production in

the Wallis archipelago, Pacific Ocean

I

n the middle of the Pacific ocean, U ve a , t h e

principal island of the archipelago of Wa l l i s c overs 75 kmÇ with 10,070 inhabita n t s . P i g s are present in 67% of the Wa l l i s i a n

households and there would be more than 19,700 pigs on the island. The strong human and animal densities in the coastal fringes are a threat for the water resources which come exc l u s i vely from a

s u rface sheet of water supplied with the infiltration of the ra i n s . To act on the l i m i tation of the pollution ge n e rated by the pig farms, the local Au t h o r i t i e s decided to study the principle of co-composting pig slurry with green wa s t e s .

Materials and methods

• Shredded green waste (tree cutting and lawn mowing), used as a bulking agent, is mixed with pig manure coming from a farm.

• First step: to determine the characteristics of a saturated mixture of green waste with pig slurry. • Second step: to test the composting performances of the liquid/solid mixture

were tested using pilot-scale windrows.

? One windrow (W1) turned 6 times along the active fermentation phase with pig slurry addition for the first four turns. Total pig slurry addition during composting accounted for 60% of the quantity of pig slurry adsorbed in the initial mixture,

? The second one (W2) also turned at the same time, but without pig slurry addition

French Agricultural Research Centre for International Development P h o to 2. Green waste windrow.

P h o to 1. Pig slurry is not recovered and is a threat for the surface sheet of wa t e r.

Results

First step

• Ve ry diluted pig slurry with a dry matter content (DM) of 15 g.kg-1, due to local practices (frequent pig wa s h i n g s ) .

• S h r e dded green waste with a mean DM content of 557 g.kg-1.

• Adsorption capacity at saturation, expressed as liquid vs. solid fraction: 3.0 g.kg-1.

• Suspended matter of the pig slurry retained in free spaces of green waste; DM retention: 0.74 kg.kg-1 DM green wa s t e .

• Characteristics of the mixture: ? water content: 78%

? wet bulk density: 829 kg.m-3 ? calculated free air space: 25% (v/v)

To improve ox y gen renewal during composting, it has been decided to use 60% of this adsorption capacity for the windrow mixture preparation.

Second step

During the active phase of composting, the change of the temperature inside the two windrows is influenced by turning operations (Figure 1). The maximum temperature is higher (63°C) in W2 than in W1 (57°C). But finally in the t wo cases, the temperature falls towards the ambient temperature after 47 days. After a maturation of 60 more days, the compost production rates for W1 and W2 (Ta b l e 1) show a more intensive fermentation in the windrow receiving pig slurry add i t i o n .

Conclusion and prospects

In Wallis, the protection of ground water and lagoon against pollution due to the pig farms should proceed with a maximum valorization by spreading pig slurry on the accessible cultivated zones and a composting treatment for the surpluses. Green waste, constituting the only bulking material available, seems to be a good way. At medium term, the potential of pig slurry

collection would account for 40,000 m3.y-1. The green waste needed will be around 15,000 tons.y-1 and it would be now advisable to check for their deposit flow rate fluctuations along the year. On the other hand, pig slurry collection has to be closely studied because of the high number of pig farms.

J . L . Fa ri n e t1, F. N u t t e n s2, P. Va n a i3

1. CIRAD, UPR « Risque environnemental lié au recyclage »,

TA70/01, avenue Agropolis, 34398 Montpellier Cedex 5, Fra n c e 2. Services territoriaux de l'économie rurale

et de la pêche du territoire des îles Wallis et Futuna,

BP 19, Mata Utu, 98600 Wallis et Futuna, Polynésie fra n ç a i s e

3. Service de l’environnement du territoire des îles Wallis et Futuna, Mata Utu,

98600 Wallis et Futuna, Polynésie fra n ç a i s e

C o r responding author: j e a n - l u c . f a rinet@cirad.fr

Références

Documents relatifs

Estimation des rejets d’azote, de phosphore, de potassium, de cuivre et de zinc des porcs - Infl uence de la conduite alimentaire et du mode de logement des animaux Figure

Meteorological data and ammonia volatilization on bare soil and sugarcane mulch (3 first days) after the application of pig slurry. Concentration Wind speed Wind Wind direction

The present study demonstrated that only 0.2% of total Cu or Zn present in pig slurry was bound to particles smaller than 0.45 μm, while 75% of total Cu and Zn was bound to particles

1 CIRAD, UPR Recyclage et risque, Montpellier, France, 2 CEREGE, CNRS, Université Aix Marseille, IRD, CdF, Europôle Méditerranéen de l’Arbois, Aix-en-Provence, France, 3 CNRS, OSUG,

Mathematical modelling of manure production by pigs: part II NH 3 , N 2 O, and CH 4 emissions and nutrient and matter flows in animal house and during manure storage and treatment.

For pig manure with a dry matter content (DM) of 15 g.kg -1 and crushed green waste with a dry matter content of 557 g.kg -1 , the adsorption capacity at saturation expressed

scapula based on fixed effects estimates only (a), and based on estimates of fixed effects plus genomic predictions, using the first 10 principal components (b)... the same

The total amount of P removed during the 4 year study was 120 kg P ha –1 for the pig slurry treatments, with and without mineral fertilizer, and similar to the quantity of P