Freshly collected effluent was treated with 2 ml formalin per litre and used to replace 150 g/kg of the dry matter of an all-meal control diet of bacon pigs. Diets containing effluent from either unwilted or wilted crops were compared with the control diet which was also given wet by adding water. Liveweight gains of 10 pigs per treatment from 65 to 86 kg on diets containing effluents from unwilted and wilted crops and on the control diet were 753, 715 and 719 ± 16.8 g/day, respectively, and in the same order feed conversion ratios (corrected to dry matter content of the control diet) were 2.94, 3.10 and 3.07 ± 0.075. None of these differences were significant. There were no significant differences in killing-out yield, in hardness of subcutaneous back-fat when measured by a penetrometer or in abnormal odour rating of subcutaneous back-fat. Formalin at levels of 1 and 2 ml/l and formic acid at levels of 1, 2 and 6 ml/l were added as potential preservatives to 1000 ml quantities of freshly collected silage effluent, which was then stored at 23°C. The 2 ml/l level of formalin and 6 ml/l level of formic acid prevented mould growth for 26 and 19 days, respectively. Freshly collected effluent was stored for 3.5, 14, 28, 56, 112 and 240 days after treatment, with formalin at the rate of 3 ml/l, and used in a pig-feeding trial. Pigs were fed either on a control all-meal diet or an equal dry matter intake of 150 g/kg effluent DM and 850 g/kg meal DM. A total of 120 animals were individually penned and fed twice daily on the experimental diets from 33 kg to slaughter at 82 kg liveweight. Overall mean liveweight gains for effluent and control diets were 646 and 656 ± 7.5 g/day, respectively, and the corresponding feed conversion ratios (DM basis) were 2.69 and 2.64 ± 0.030, neither of the differences being significant. Animal performance did not deteriorate with increasing period of effluent storage. No significant differences were found in carcase lean, back-fat thickness nor hardness of back-fat. A digestibility study was carried out on freshly collected effluent from another source. The level of dietary inclusion was equal to that in the previous experiments and the digestibility of dry matter was 0.831 and 0.819, and of nitrogen 0.822 and 0.827 for the control and effluent diets, respectively. A value of 11.4 MJ/kg dry matter was calculated by difference for the digestible energy of this effluent. In a further digestibility trial, digestible energy values of 14.6 and 14.2 MJ/kg dry matter were calculated by difference for effluents stored for 3.5 and 300 days, respectively.
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