Open Access
Volume 22, Number 6, November-December 2015
Article Number D611
Number of page(s) 9
Section Dossier: Flax and hemp / Lin et chanvre
Published online 02 October 2015

© M. Doreau and A. Ferlay, Published by EDP Sciences, 2015

Licence Creative Commons
This is an Open Access article distributed under the terms of the Creative Commons Attribution License (, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

1 Introduction

Although linseed is not commonly used nowadays in ruminant feeding, this is an ancient feedstuff which has been used from the nineteenth century, as crude seed or cake (Grandeau, 1876). In the first part of the twentieth century, linseed expeller cake has been used especially for beef fattening, and was used not really for nutritional benefits but for giving a shiny coat, and also a tasty meat (Dumont et al., 1997). The development of the use of fat sources in ruminant feeding in the 1990s as a mean to increase energy density of the diet concerned first palm oil, animal fat derivatives, and commonly used seeds such as cottonseed, soybean and rapeseed. A significant use of linseed is very recent and due to its richness in alpha-linolenic acid (18:3 n-3, or cis-9, cis-12, cis-15 18:3), potentially allowing an increase in omega-3 fatty acids (FA) in milk and meat. However, the extent of increase in omega-3 FA in these products is limited because of the wide biohydrogenation of polyunsaturated FA in the rumen, prior to absorption. A few years ago, an additional interest for linseed has been put forward: linseed FA have been shown to significantly decrease enteric methane production by ruminants (Martin et al., 2010). Methane mitigation is a major issue for decreasing greenhouse gases emissions from livestock. The Bleu-Blanc-Coeur initiative, born in France and aiming to develop omega-3 FA in human foods through promoting feeding animals with omega-3, considers this double interest of linseeds. Linseeds are now used essentially as an extruded mixture of 50–70% linseeds and 30–50% other feeds such as bran, in order to obtain a product which is easy to handle and to incorporate in concentrates. This paper presents an overview of the interest of the incorporation of linseed in diets for providing omega-3 FA to ruminants, then of the use of linseed for methane mitigation. In the last part, the perspectives of increase in linseed use for animal feeding are discussed.

2 Linseed, a provider of omega-3 for ruminants

Linseeds varieties fed to animals contain a high level of oil (40%) with 55% of 18:3 n-3 (Glasser et al., 2008a, Petit, 2010). Adding linseeds to ruminant diets is susceptible to increase the concentration of polyunsaturated FA in dairy products and beef. Ruminant products contain a variety of FA. Some of them may be of potential benefits to human health, including polyunsaturated FA of the omega-3 FA series. The main omega-3 FA in milk fat is 18:3 n-3. In beef, omega-3 FA are composed of both 18:3 n-3 and 20- and 22-carbon FA. The omega-3 FA, and more particularly 20- and 22-carbon FA, can reduce the risk of cardiovascular diseases (Mills et al., 2011). Details on omega-3 FA effects on human health are reported in a paper by Mourot (this issue).

A specificity of digestive processes in ruminants is an extensive biohydrogenation of dietary FA in the rumen, prior to absorption which occurs in the small intestine. As a consequence, the amount of omega-3 FA reaching the small intestine is much lower than the dietary intake of omega-3 FA, resulting in a quantitatively low transfer of these FA in milk and meat, compared to monogastric animals (Doreau et al., 2011). Forage FA are in the form of galactolipids, and to a lesser extent, of phospholipids, glycerides and free FA. In concentrates, FA are in the form of phospholipids and cholesterol esters in membranes, and of glycerides as storage lipids; oilseeds are thus rich in triglycerides. In addition, additives providing fats and oils are sometimes given as triglycerides or as calcium salts. In the rumen, which is the first digestive compartment where feed fermentation and metabolism occur, lipids are first hydrolysed by microbial enzymes. Free FA are then hydrogenated and isomerised by other microbial enzymes, to a large extent in the case of polyunsaturated FA, incompletely in the case of monounsaturated FA. These processes are detailed in Doreau et al. (2012). Disappearance of 18:3 n-3 is close to 90%. Few 18:2 FA reach the intestine, but, besides significant amounts of stearic acid (18:0), a very large panel of cis- and trans-18:1 FA is found (Glasser et al., 2008c). The major one is vaccenic acid (trans-11 18:1), but 12 other trans isomers and 5 cis isomers, mainly oleic acid (cis-9 18:1) reach the intestine and are thus absorbed and available for transfer into milk and meat. Different attempts have been made to decrease biohydrogenation through protection of lipids. The only one which has been proved to be efficient is the encapsulation of lipids in a coat of proteins treated with formaldehyde (Doreau et al., 2011; Fievez et al., 2007). However this technique is not used, in particular owing to its cost, to the use of formaldehyde, and to possible adverse effects of excessive amounts of polyunsaturated fats on animal health and product quality.

Concerning the FA metabolism, 18:3 n-3 represents on average 1.9% of 18-carbon FA reaching the duodenum because of its extensive biohydrogenation in the rumen. Nevertheless, the transfer rate from duodenum to milk is lower for 18:3 n-3 than that for other 18-carbon FA (Glasser et al., 2008b). In mammary gland and in muscle, an important de novo synthesis occurs from plasma acetate and butyrate, leading to a variety of short- and medium chain FA in milk fat. Moreover, the activity of a Δ9-desaturase leads to the formation of cis-9, trans-11 18:2 (rumenic acid) from vaccenic acid. In addition, a specific metabolic pathway occurs in the muscle, but not in the mammary gland: the elongation and desaturation of 18:3 n-3, leading to the formation of eicosapentaenoic acid (EPA, 20:5 n-3) and docosapentaenoic acid (DPA, 22:5 n-3) in muscle. However, the last step of desaturation towards docosahexaenoic acid (DHA, 22:6 n-3) is of very low extent in vertebrates (Doreau et al., 2011).

The general responses of milk FA composition to linseeds feeding concern saturated FA, trans-18:1, conjugated and non-conjugated isomers of 18:2 and 18:3 n-3. The extent of change in milk FA concentration is generally proportional to the level of inclusion of linseeds in the diet (Ferlay et al., 2013; Glasser et al., 2008a). The effects of increasing amounts of extruded linseeds in the diet have been studied by different authors (Brunschwig et al., 2010; Ferlay et al., 2013; Hurtaud et al., 2010). The major changes concern increases in trans-18:1 and total conjugated linoleic acid (CLA) concentrations in milk. Feeding linseeds increases the milk concentrations of different isomers of CLA: cis-9, trans-11 18:2, trans-11, cis-13 18:2, trans-12, trans-14 18:2, and trans-12, cis-14 18:2) (Chilliard et al., 2007, Lerch et al., 2012c). These FA concentrations increased linearly with increasing amounts of linseeds whereas 18:3 n-3 concentration increased slightly (Ferlay et al., 2013), confirming that this FA was highly biohydrogenated in the rumen. The relationship between 18:3 n-3 intake and 18:3 n-3 as a proportion of milk FA is linear (Fig. 1). The transfer of 18:3 n-3 from diet to milk is close to 4.5%. Only Kennelly et al. (1996) reported a higher transfer when cows fed a protected linseed oil, with a milk concentration of 18:3 n-3 higher than 20% of total FA. Moreover, the milk saturated FA decreased linearly with increasing amounts of linseed. For the same level of cis-9, trans-11 18:2 in the milk fat, linseed supplementation increased the milk concentration of trans FA other than trans-11 18:1 and cis-9, trans-11 18:2 more than grazed grass (Ferlay et al., 2008, 2013). Significant increases were observed for cis-9, trans-13 and trans-11, cis-15 18:2 with linseed or linseed oils because these FA are main intermediates of ruminal biohydrogenation of 18:3n-3 (Chilliard et al., 2009; Ferlay et al., 2013; Glasser et al., 2008c; Lerch et al., 2012b). Lerch et al. (2012c) studied the effects of long-term supplementation (2.5 to 3% of oil in DM) with extruded linseed over 2 consecutive lactations, successively on a grass silage-based diet and at pasture. Compared to control diet, linseeds resulted in the enrichment of different isomers of CLA and conjugated linolenic acids, particularly cis-9, trans-11, trans-13 18:3, identified for the first time in bovine milk fat.

thumbnail Fig. 1

Effect of increasing amounts of 18:3 n-3 intake from linseeds on milk 18:3 n-3 proportion (from Chilliard et al., 2009; Ferlay et al., 2013; Hurtaud et al., 2010). Equation of linear regression is: Y = 0.0018X + 0.38 (R2 = 0.59), where Y is milk 18:3 n-3 proportion (g/100 g of total FA) and X is 18:3 n-3 intake (g/d).

Supplying linseeds for beef production has the same global consequences on FA meat composition as on milk, but with some particularities. The increase in 18:3 n-3, EPA and DPA has been demonstrated in all trials where linseeds were used (e.g. Corazzin et al., 2012; Scollan et al., 2005). Due to ruminal biohydrogenation, the proportion of 18:3 n-3 in percentage of total FA remains low. For example in Longissimus thoracis, it increases from 0.5 to 0.9–1.6% (Normand et al., 2005, 5 trials), from 0.4 to 1.9% (Mach et al., 2006), from 0.4 to 0.8% (Barton et al., 2007), from 0.6 to 2.0% (Herdmann et al., 2010), from 1.2 to 1.6% (Corazzin et al., 2012), from 0.4 to 0.6% (Habeanu et al., 2014), from 0.9 to 1.4% (Mialon et al., 2015). Differences in the extent of the increase depend more on the amount of added fat and their processing than on the duration of distribution before slaughter. It can also be noted that pasture feeding, which is another source of 18:3 n-3, increases 18:3 n-3 in meat, although generally to a lower extent (Scollan et al., 2005). The increase in muscle 18:3 n-3 concentration is significantly higher with extruded linseeds than with rolled linseeds (Normand et al., 2005), and higher in ground or rolled linseeds than with whole linseeds (Maddock et al., 2006). The increase in 18:3 n-3 was higher in Longissimus thoracis than in Rectus abdominis and Semitendinosus in a trial by Mialon et al. (2015), but this difference was not observed in trials by Normand et al. (2005) and by Habeanu et al. (2014). Despite elongation process, very long-chain FA are present in muscle in low proportions whatever the diet: less than 0.7 and 0.4% of total FA for DPA and EPA, respectively, and this proportion is either unchanged or moderately increased by linseed supply (Barton et al. 2007; Corazzin et al., 2012; Habeanu et al., 2014; Herdmann et al., 2010; Mialon et al., 2015). These three latter authors also observed an increase in CLA, but the two former authors did not. In any case, the CLA concentration in beef is too low for a possible effect on human health. Beef trans-18:1 FA comprise a significant amount of isomers other than trans-11, but few studies are available about the effect of linseeds on this pattern. With diets based on 30% straw and 70% concentrates, extruded linseed did not change the proportion of trans-11 (33%) but trans-12, -13, -14 and -15 increased at the expense of trans-9 and -10 (Habeanu et al., 2014).

There has been a steady decline of fertility in major dairy cow breeds associated with the improvement of genetic merit for milk production (Barbat et al., 2010; Butler, 2003). Part of this decline is due also to extended period of negative energy balance and intense mobilisation of body reserves during early lactation. The relationships among energy balance, body condition score and reproductive function are well documented (e.g. infrequent LH pulses, delayed ovarian activity, abnormal estrous cycles, poor follicular response to gonadotropins, reduction of oocyte quality and embryo survival (Butler, 2003, Chagas et al., 2007). Recent interest on lipid feeding to cows has focused on reproduction because of their high energy density and a supply of specific FA. Lipid supplementation could influence reproduction by altering the size of the dominant follicle, shortening the interval between calving and the first postpartum ovulation, increasing progesterone concentration during the luteal phase of the oestrous cycle, modulating uterine prostaglandin synthesis, and improving oocyte and embryo quality and maintenance of pregnancy (Santos et al., 2008). The omega-6 and omega-3 polyunsaturated FA seem to have the major effects on reproductive responses. Nevertheless, results from feeding linseeds on reproductive variables are inconsistent. Some authors reported an improved increased follicular and corpus luteum growth (Santos et al., 2008), oocyte (Moallem et al., 2013; Zachut et al., 2010) and embryo quality (Thangavelu et al., 2007), decreased pregnancy loss (Ambrose et al., 2006), reduced plasma prostaglandin (Petit et al., 2002), and increased serum progesterone concentration (Jahani-Moghadam et al., 2015), reduced interval from calving to ovulation (Colazo et al., 2009). In contrast, others noted no changes in milk progesterone concentration or corpus luteum activity (Ponter et al., 2006), or oocyte quality (Bilby et al., 2006, Fouladi-Nashta et al., 2009). The inconsistencies among these studies could be due to differences in the amounts of lipid supplements, duration of supplementation, and season. The global effect on cow fertility has not been evidenced: no effect of linseed feeding has been reported on conception rate (Ambrose et al., 2006; Bork et al., 2010; Petit and Twagiramungu, 2006; Petit et al., 2008), or pregnancy rate (Jahani-Moghadam et al., 2015). Further studies with a larger number of animals are necessary to be conducted in order to confirm these results.

3 Linseed, a way to mitigate methane emissions by ruminants

Among greenhouse gases, which are responsible of global warming, methane is the major contributor for livestock activities: more than 40% of greenhouse gases, when they are expressed as carbon dioxide-equivalents. The major part of methane is produced in the digestive tract of ruminants, especially in the rumen, which is the main site of digestion. In the rumen, dietary carbohydrates are fermented by bacteria and protozoa in volatile fatty acids, which are the main energy source for ruminants. During fermentation, hydrogen is produced, then is converted in methane by the action of another type of microbes, archaea methanogens. The abatement of methane emissions is a challenge for scientists.

Dietary lipids are considered now by the scientific community as the best way for enteric methane mitigation (reviews by Hristov et al., 2013; Martin et al., 2010). Although their effect on methane emission is not systematic, lipids present advantages compared to other dietary options: chemicals and additives such as nitrates raise the issue of acceptability by consumers, tannins often reduce animal performances, high-cereal diets question about the use of large amounts of cereals in ruminant feeding. When lipids are given in substitution to carbohydrates, methane is reduced because it is produced from carbohydrates, but not from lipids. In addition, some lipid sources decrease rumen protozoa which are important producers of hydrogen, which is the precursor of methane. The strongest decrease in rumen protozoa is obtained with linseeds on one hand, and coconut and palm kernel oil on the other hand. These latter lipid sources have the drawback to be rich in medium-chain saturated FA (12:0 and 14:0), which are considered as deleterious for human health. As a consequence, linseeds could be the best choice for methane mitigation. Review of experimental data shows that on average linseeds reduce more methane emission than saturated sources (calcium salts of palm oil, tallow), and unsaturated sources containing oleic acid (rapeseed) or linoleic acid (sunflower, cottonseed) (Martin et al., 2010). However, between-experiments variability of response is high, so that some authors do not distinguish fat sources for their effect on methane emission (Grainger and Beauchemin, 2011). It has been shown that the effect of linseeds remains at least for one year after starting their distribution to cows (Martin et al., 2011). This long-term effect is especially interesting because products which decrease methane often have a short-term effect, due to the adaptation of rumen microbes to dietary changes. Increasing the proportion of linseeds in the diet until 5% additional fat results in a strong decrease in methane (Fig. 2). In practical conditions, a lower addition of linseeds is recommended, to avoid any risk of disturbances of fibre digestibility, which often occurs for high linseed supply, and any risk of excessive increase in some trans FA in products which may have a negative effect of human health. Although most results evidence the effect of linseed for methane mitigation, for an unknown reason, linseeds did not decrease methane emission in some experiments (Van Zijderveld et al., 2011).

thumbnail Fig. 2

Effect of increasing amounts of extruded linseeds (EL) on methane emission in two different diets (from Martin et al., 2009).

For any option aiming to decrease methane emission by animals, it is mandatory to check that the decrease is not compensated for by an increase in the other greenhouse gases, carbon dioxide and nitrous oxide. For linseeds, there is a compensation for a minor part, due to the higher carbon footprint for linseed than for cereals that they replace. The effect of introducing linseeds in the diet has been calculated by life cycle assessment for the whole farming system, for beef cattle (Nguyen et al., 2012) and for dairy cattle (Nguyen et al., 2013). In these studies, linseed supply was of limited extent and given to high-producing animals (2% additional fat to lactating cows in winter for dairy, 3% of additional fat to the bull fattening herd for beef), corresponding to present practices in France for farmers who use linseeds. In both types of farms, the use of linseeds slightly decreases greenhouse gases emissions, and slightly increases other environmental impacts as energy use, due to extrusion process, and land use, because crop yield per hectare is lower for linseeds than for cereals that linseeds replace. If strong public policies for decreasing greenhouse gases are implemented, all ruminants receiving concentrates could be fed lipids all year long, in order to provide 3.5% additional fat. In this case, lipid supply can reduce total greenhouse gases emissions from cattle by 6%. However, this option is expensive at present due to the higher cost of oleagineous seeds compared to cereals (Doreau et al., 2014).

4 Increasing the use of linseed: potential and limits

Use of linseed in ruminant feeding could be developed if linseed crops are developed. In several countries, the use of linseed in crop rotations is limited by a lower yield per ha than cereals, and by the relative price of cereals and linseeds. Among crops which are frequently used in rotations in Europe, rapeseed is competitive, and grain legumes allow the decrease in N fertilisation in the multiannual system. This is not the case of linseed, for which average yield stagnates at 20 q/ha. For France, national linseed production covers one half of present needs for animal nutrition. The potential of increase in surfaces is high, but a significant rise requires a strong coordination of actors of the food chain (Charrier et al., 2013). Ways of improvement which may lead in the short-term to tripling French surfaces (30 000 ha instead of 10 000 ha now) have been proposed by Labalette et al. (2011), and include a larger choice of varieties, better rotation choices and higher prices relative to cereals. This latter can be achieved by feed industry, but the price of milk and meat enriched in omega-3 should also be higher. This is possible by a selective milk collection, which is already organised in some dairy factories, by the development of dairy and beef brands for niche markets, and by the promotion and lobbying such as the Bleu-Blanc-Cœur initiative, which is positively received by consumers. Incentives related to public policies can be thought, owing to the environmental interest on linseed use for the abatement of methane emission by ruminants.

The positive effect of linseeds on omega-3 FA in milk and beef, and the methane abatement, are two arguments for using linseeds at a large scale. However, this practice will increase only if animal performances (milk yield and composition for dairy cows, liveweight gain and carcass characteristics) are unchanged or improved. Lipid incorporation in diets may decrease fibre digestibility, due to possible disturbances in rumen microbial ecosystem and fermentation. However, most scientists agree that this risk is negligible when FA content of diets does not exceed 5% of dry matter; this corresponds to 3.5% added FA from linseeds in diet DM. Higher proportion sometimes decreases digestibility (Petit, 2010).

Table 1

Effect of linseed supply on beef liveweight gain.

A range of experiments has been carried out in dairy cows, using linseeds in different forms and amounts. During most short-term studies, feeding up to 15% linseed in diet dry matter (DM) did not change DM intake (Ferlay et al., 2013; Petit, 2010). In early lactation, discrepancies among experiments on the effect of whole or processed linseed supplementation on milk yield could result from differences in diet composition and length of experiment (Petit, 2010). The whole linseed supplementation did not modify milk yield and milk fat content and yield in mid- or late lactation (Petit, 2010). Nevertheless, linseed micronisation or extrusion results in variable effects on milk fat concentration, with a possible decrease. One explanation could be the possible increasing rate of oil release from extruded seeds into the rumen compared to whole seeds, which could result in an increased production of trans FA in rumen and then a decrease in milk fat content (Chilliard et al., 2009). A decrease in milk fat yield with linseed oil feeding is often reported (Glasser et al., 2008a). Generally, feeding diets with whole or crushed or micronized linseed had no effect on the milk protein content in mid lactation (Petit, 2010) whereas a decrease in protein content (0.5 g/kg) was observed with extruded linseed (Brunschwig et al., 2010). Concerning the long-term linseed supplementation, during the first year of experimentation, linseed diet had no effect on the milk and fat yields compared to the control diet. Linseed supplement decreased the milk protein content, without changing protein yield. Thus, long-term effects of supplementation with linseeds were similar to those observed during short-term (1 to 3 months) studies (Lerch et al., 2012a). With a moderate linseed incorporation in the diet (less than 3% additional fat), milk yield is unchanged and the risk of decrease in milk fat or protein yield is low.

Linseed supply to diets has also been studied in fattening cattle. Table 1 summarizes 20 comparisons between control and supplemented diets. On average, animal liveweight gain is higher by 9% with linseed-supplemented diets than with control diet, differences ranging between +25% and –15%. Within experiment, differences are often non-significant. Difference between experiments is due to the level of linseed supply, the experimental design (addition of linseeds or substitution to carbohydrates and protein) and the characteristics of substitution, leading to differences in diet energy value between control and supplemented diet. Five comparisons between rolled and extruded linseeds have been performed by Normand et al. (2005): differences are very low (Tab. 2). Whole linseeds have been used by Maddock et al. (2006) and Corazzin et al. (2012). Results suggest that linseed hull does not limit a normal digestion of the seed. It can be concluded that the incorporation of linseeds for finishing cattle has no effect or a slightly positive effect on performances. Although it has been shown that lipid supply in fattening diets generally increases carcass fat proportion (Clinquart et al., 1995), available data for linseed supply do not fully support this statement: linseeds may increase (Dufrasne et al., 1991) or not (Maddock et al., 2006; Normand et al., 2005; Razminowicz et al., 2008) carcass fatness. The reality of a difference between linseed and other lipid sources needs further research.

It is sometimes argued that linseeds contain cyanogenic compounds which could be toxic for animals. They are present as glycosides, and are likely to vary more with cultivar than with location or year (Oomah et al., 1992). Seed treatments can decrease cyanides. Pelleting decreases total cyanides, especially at high and prolonged temperatures (Feng et al., 2003). Extrusion divided cyanhydric acid by 4, whereas rolling divided them by 2 (one comparison, Normand et al., 2006); a very pronounced decrease in cyanhydric acid was observed with another extrusion technology: 10 mg/kg for extruded linseeds vs. 165 to 240 mg/kg for rolled linseeds (6 comparisons, Normand et al., 2005). However, cyanhydric acid content in plasma is not increased by rolled or extruded linseed inclusion in the diet, suggesting a possible detoxification in the rumen (Normand et al., 2006). Nevertheless, cyanogenic compounds are transferred to a low extent in milk, but according to Petit (2010), milk concentrations are too much low to result in a toxic effect for humans, if taking account the daily doses which are considered as safe by health authorities.

Due to their high amount of polyunsaturated FA, linseeds may be subject to oxidation. During a 120-day conservation, peroxide value and vitamin E content are stable for rolled linseeds, whereas the former increases and the latter decreases for extruded linseeds (Normand et al., 2005). It is recommended to use new batches of extruded linseeds every 2 months if there is no incorporation of antioxidant, in order to prevent a possible decrease in intake by animals. A concern related to the use of polyunsaturated FA is the susceptibility of lipids to oxidation (Durand et al., 2005). Milk and beef lipid oxidation may occur, when linseeds are incorporated in diets, but often there is no increased susceptibility to oxidation, for example when rolled or extruded linseeds are fed to fattening cattle in moderate amounts (750 g/day) (Normand et al., 2005). However, lipid oxidation may occur when animals have been submitted to oxidative stress during their lifetime, after inflammatory or infectious events, or in the pre-slaughter period, after an emotional or physical stress (Durand et al., 2013). For this reason, an additional supply of vitamin E or of vegetal antioxidants in the diet may reduce milk susceptibility to oxidation (Focant et al., 1998) and in beef meat after carcass ageing and meat display on shelfs (Gobert et al., 2010).

Published literature does not mention flavour problems of milk from cows fed linseeds. When linseeds are given as formaldehyde-treated seeds, protecting them from rumen degradation and resulting in high 18:3 n-3 absorption, a fish taste in meat, an increase in rancidity and in a decrease in overall liking are observed (Scollan et al., 2005). Rancidity is due to oxidation, and fishy taste is likely due to components related to 20- and 22-carbon FA produced by FA elongation. This negative judging is not observed when linseeds are unprotected (Normand et al., 2005; Wood et al., 2003), i.e. when biohydrogenation normally occurs. It can be concluded that at normal levels of incorporation, linseeds do not affect milk or beef taste.

5 Conclusion

The major interest of linseeds in ruminant nutrition is the increase in omega-3 FA in milk and beef with a moderate supply in cattle diet. Although this increase in quantitatively slight, due to rumen biohydrogenation, it contributes to enhance milk and beef nutritional quality, and the image of these products for the consumer. This positive role of linseeds in ruminant nutrition is reinforced by their role for enteric methane mitigation. However, an excessive incorporation in diets may increase some trans FA in products or decrease milk fat and protein contents, and feed efficiency of the diet. It could be recommended to limit linseed incorporation to ca. 3% additional fat in the diet. However, a large increase in the use of linseeds for feeding ruminant is limited by the possibilities of increase in linseed cropping.


Linseed use in ruminant nutrition can be developed in the future owing to interest in improving fatty acid composition of milk and meat, and also in decreasing methane emissions. Incorporation in diets up to 3% is possible without negative side effects on animal performance. An increase in linseed use requires an increase in areas devoted to linseed crops.


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Cite this article as: Michel Doreau, Anne Ferlay. Linseed: a valuable feedstuff for ruminants. OCL 2015, 22(6) D611.

All Tables

Table 1

Effect of linseed supply on beef liveweight gain.

All Figures

thumbnail Fig. 1

Effect of increasing amounts of 18:3 n-3 intake from linseeds on milk 18:3 n-3 proportion (from Chilliard et al., 2009; Ferlay et al., 2013; Hurtaud et al., 2010). Equation of linear regression is: Y = 0.0018X + 0.38 (R2 = 0.59), where Y is milk 18:3 n-3 proportion (g/100 g of total FA) and X is 18:3 n-3 intake (g/d).

In the text
thumbnail Fig. 2

Effect of increasing amounts of extruded linseeds (EL) on methane emission in two different diets (from Martin et al., 2009).

In the text

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