Skip to main content
Translational Animal Science logoLink to Translational Animal Science
. 2024 Aug 3;8:txae116. doi: 10.1093/tas/txae116

Effect of SeaFeed, a canola oil infused with Asparagopsis armata, on methane emissions, animal health, performance, and carcass characteristics of Angus feedlot cattle

Melissa M George 1,, Samuel V Platts 2, Brent A Berry 3, Markus F Miller 4, Anna M Carlock 5, Taylor M Horton 6, Matthew H George 7
PMCID: PMC11347879  PMID: 39192875

Abstract

The objectives of this project were to measure the effect of SeaFeed, a canola oil infused with Asparagopsis armata, on methane emissions, animal health, performance, and carcass characteristics of feedlot cattle. Angus steers (n = 160) with an initial body weight of 474.4 kg were fed a steam-flaked wheat and barley ration for 200 d in a large, commercial feedlot. A single-blinded randomized complete block design compared two treatments including control and SeaFeed included at a rate of 25 mg bromoform per kg dry matter intake (DMI). Monthly testing of bromoform levels in the canola demonstrated that SeaFeed maintained a stable bromoform concentration for 6 mo. The inclusion of SeaFeed had no effect on daily DMI. However, steers fed SeaFeed were more efficient with a 6.6% higher (P < 0.01) gain-to-feed ratio as compared to control steers over the 200-d feeding period. This improved efficiency resulted in 0.094 kg higher (P < 0.01) average daily gain and 19.7 kg higher (P < 0.01) live exit weight in steers fed SeaFeed as compared to control steers. Steers fed SeaFeed produced 51.7% less (P < 0.01) methane and yielded 50.5% less (P < 0.01) methane over the 200-d feeding period as compared to cattle fed the control ration. Peak methane inhibition occurred on day 29 on feed with 90.6% less methane production in cattle fed SeaFeed as compared to control animals. SeaFeed reduced (P < 0.01) methane intensity by 55.4% over the 200-d feeding period. Hot carcass weight tended (P = 0.097) to be 6.9 kg heavier in cattle fed SeaFeed as compared to controls. Cattle fed SeaFeed had similar (P > 0.20) marbling, meat color, eye muscle, area, and ultimate pH to control cattle. Interestingly, cattle fed SeaFeed tended (P = 0.054) to have slightly higher fat color scores. Rumen papillae from cattle fed SeaFeed were more (P < 0.01) gray in color and more oval (P < 0.01) in shape as compared to control animals; however, rumen damage was not different between treatment groups. In regards to food safety and residues, all muscle, fat, and kidney samples were free from bromoform residues. Bromine residues in kidney and meat samples were higher (P < 0.01) in the SeaFeed group as compared to controls. Cattle fed SeaFeed produced strip loin steaks similar (P > 0.05) in eating quality to control cattle. These results demonstrate that SeaFeed reduced methane emissions, improved performance, and produced safe beef with similar eating quality to conventional beef.

Keywords: Asparagopsis, cattle, feedlot, methane, seaweed


SeaFeed, a bromoform-containing canola oil infused with the red seaweed Asparagopsis armata , reduced methane emissions, improved performance, and produced safe beef with similar eating quality to conventional beef.

Graphical Abstract

Graphical Abstract.

Graphical Abstract

Introduction

Practical strategies to reduce enteric methane emissions from cattle are urgently required to achieve global methane reduction goals. Methane emissions associated with beef production are a priority with accelerated efforts focused on the development and commercialization of mitigation strategies (Stackhouse-Lawson et al., 2012). Enteric fermentation in cattle is the largest contributor of methane from beef cattle (Glasson et al., 2022). Several enteric methane mitigation strategies have been identified (Hegarty et al., 2021) and developed, including the commercially available SeaFeed (Sea Forest Ltd, Triabunna, Tasmania, Australia), an Asparagopsis armata infused canola oil containing bromoform. While several candidate feed additives are safe and effectively mitigate methane emissions, commercial trials that measure the effects on performance and carcass characteristics are lacking in the literature. Feeding cattle to achieve optimal performance requires excellent formulation skills by doctoral-level ruminant nutritionists, but equally important are the daily execution of consistent grain processing, ration mixing and delivery, and strict adherence to animal health, comfort, and welfare parameters. This project demonstrates a unique collaborative effort between the government, a commercial feedlot, veterinarians, nutritionists, meat scientists, and a science-based technology company to seriously address the challenge of climate change in a commercial environment.

Asparagopsis armata is a red macroalgae that has been shown to reduce methane emissions in cattle (Roque et al., 2019). Although Asparagopsis is known to contain a wide range of organobromine compounds, the bioactive metabolite, bromoform, has been identified as the primary metabolite responsible for the activity of Asparagopsis in the reduction of methane emissions (Glasson et al., 2022). A novel method to stabilize the secondary metabolites of Asparagopsis, particularly bromoform, in a vegetable oil carrier by steeping Asparagopsis in canola oil was described (Magnusson et al., 2020). This process was shown to maintain the stability of bromoform over 6 mo in the canola oil carrier (Tan et al., 2023). SeaFeed is a commercially available canola oil that has been infused with A. armata, resulting in the stabilization of the oil-soluble metabolites such as bromoform in the canola oil. Vegetable oils are commonly fed to feedlot cattle and hence inclusion of a methane mitigation feed technology in the form of a vegetable oil is a valid delivery mechanism and solution to reduce methane emissions of feedlot cattle (Ridoutt et al., 2022).

Inhibition of methanogenesis by bromoform is due to the blocking of key metalloenzymes of the Wolfe cycle (Glasson et al., 2022). Specifically, bromoform and other halogenated alkanes react competitively with substrates of coenzyme M transferase and methyl coenzyme M reductase to block steps six and seven of the Wolfe Cycle of methanogenesis (Glasson et al., 2022). The human food safety of consuming products from cattle fed bromoform has been evaluated as methanogens in the rumen metabolize bromoform through reductive dehalogenation, which in combination with minimally effective inclusion levels of bromoform limits the transfer of bromoform to animal tissues and food products (Glasson et al., 2022). While mechanistically it is understood that food products from cattle fed bromoform should be free of bromoform residues, this trial provided highly sensitive residue data on a large number of animals fed SeaFeed for an extended period of time to fully answer the questions of potential residues.

Originally, the scientific community postulated that redirection of energy lost as methane would result in improved feed utilization and improved animal productivity (Patra, 2012). Unfortunately, many of the published articles have not identified performance benefits associated with methane mitigation feed additives in feedlot cattle (Alemu et al., 2020, 2023; Almeida et al., 2023; Araújo et al., 2023; Cowley et al., 2024). This is possibly due to the experimental design of many of the trials and the observation that the feed intake was unlikely maximized in several of the trials due to experimental design constraints. For example, many of the previous trials were performed in respiration chambers which limit natural behaviors and feed intake. The objective of this trial was to utilize commercial feedlot nutritional formulations, commercial ration adaptation protocols, consistency of feed preparation and delivery, pen conditions, and experimental design to achieve maximal feed intake and performance parameters to evaluate if there is truly a performance benefit to feeding methane mitigation feed technologies such as SeaFeed. While the methanogenesis inhibitory activity of bromoform and Asparagopsis have been well-established, the effect of SeaFeed on methane production, intensity, and yield has not been established in high-performing Angus cattle over a 200-d period. The results of this study provide daily individual animal methane emissions, intake, and body weight to allow important insights in regards to the effect of methane mitigation on performance parameters over an extended feeding period.

Consumer eating experiences can be significantly impacted by differences in flavor, tenderness, and juiciness. Hence, the addition of feed additives such as those derived from Asparagopsis raises questions in regards to impacts on consumer eating experience. This study was designed to answer important questions through an extensively trained sensory panel evaluation. The results of this trained sensory panel are essential for branded beef program owners, restaurants, retailers, and cattle producers to ensure the quality of the eating experience consumers will experience if cattle have been fed the mitigant.

Thus, the objectives of this project were to measure the effect of SeaFeed on methane emissions, animal health, performance, and carcass characteristics of Angus cattle fed for 200 d in a large, commercial feedlot. The authors hypothesized that cattle fed SeaFeed would produce less methane and hence have increased feed efficiency resulting in increased performance with no difference in carcass characteristics.

MATERIALS AND METHODS

Animal Ethics

This project was completed under the approval of the Queensland Government Department of Agriculture and Fisheries Animal Ethics Committee (Animal Ethics Committee Reference Number: SA 2022/12/865) by the registered scientific user of animals in Queensland, Bovine Dynamics (Registration Number: SUR001552).

Experimental Design

A single-blinded randomized complete block design was conducted to evaluate the effect of SeaFeed (Sea Forest Ltd), a bromoform-containing canola oil on methane emissions, performance, animal health, and carcass characteristics of Angus feedlot cattle. Individual animal was the experimental unit as the pens contained individual feed intake, weight, and methane emissions monitoring systems. Individual steers (n = 160) were sequentially allocated to one of four groups of cattle with 40 individuals per group as they completed induction processing to the feedlot. Four pens were blocked by row with two adjacent pens in the same row allocated to each block. Within a block, a random number generator was used to allocate pen to treatment. A random number generator was used to assign four groups of 40 individuals to one of the four pens. The study was powered to detect a 2.0-kg hot standard carcass weight response at 80% power between control and SeaFeed treatments.

Cattle Processing

Angus steers (n = 160) were sourced from a single vendor in Northern New South Wales, Australia. Steers arrived to the trial site on April 6, 2023, were scanned using individual RFID ear tags, individually weighed in a calibrated hydraulic chute (Sumo, Thompson Longhorn, Goombura, Queensland, Australia), vaccinated with Rhinogard Bovine Herpesvirus 1 Live Intranasal Vaccine for Cattle (Zoetis, Parsippany, NJ, USA, 2 mL, intranasal) and Bovishield MH One Mannheimia Haemolytica Vaccine for Cattle (Zoetis, 2 mL, subcutaneous), treated with Dectomax V Dual Combination Injection for Cattle (Zoetis, 5 mg/mL doramectin, 150 mg/mL levamisole, 20 mL, subcutaneous), Flukare C (Virbac Australia, Milperra, New South Wales, Australia, 120 g/L triclabendazole, 50 mL), and backgrounded for 28 d days prior to the commencement of the trial. Steers gained 1.28 kg/d over the backgrounding phase.

Steers were individually weighed on a calibrated scale that was tested with 200 kg of certified weights prior to processing on May 2, 2023. Steers were held overnight on an arrival ration. Steers were reweighed on May 3, 2023 to produce an average induction weight over 2 d. Steers were inducted to a 20,000-head commercial feedlot in south-eastern, Queensland, Australia on May 3, 2023.

At induction processing, steers were tagged in the ear with individual visual identification and lot number, Rhinogard Bovine Herpesvirus 1 Live Intranasal Vaccine for Cattle (Zoetis, 2mL, intranasal) and Bovilis MH Mannheimia Haemolytica Vaccine for Cattle (Coopers Animal Health, East Bendigo, Victoria, Australia, 2 mL, subcutaneous), treated with Dectomax V Dectomax V Dual Combination Injection for Cattle (Zoetis, 5 mg/mL doramectin, 150 mg/mL levamisole, 21 mL, subcutaneous) and Nitrofluke (Virbac Australia340 g/L nitroxynil, 67 g/L clorsulon, 17 mL, subcutaneous), and orally drenched with Lactipro Advance (Axiota Animal Health, Fort Collins, CO, USA, Megasphaera eldensii, 50 mL, oral). Steers (n = 160) selected for study enrollment were within a body weight range of 476 to 522 kg with a mean of 502.2 and 11.87 kg SD. Steers were excluded from the group if outside the targeted body weight range or had an average daily gain of less than 0.6 kg/d during the backgrounding phase.

Pen Designs and Monitoring Systems

Feedlot pens were cleaned at the commencement of the trial and water troughs were cleaned twice a week. There were a total of four feedlot pens with 40 heads per pen. Each pen was equipped with eight Feed Intake Nodes (Vytelle, Lenexa, KS, USA) to measure the dry matter intake (DMI) of individual animals. Pens also contained in-pen weighing position scales (Vytelle) associated with the water troughs. Two pens in a single row contained GreenFeed Pasture Systems (C-Lock, Rapid City, SD, USA) to allow emissions monitoring for control and SeaFeed-treated cattle. The 200-d feeding period commenced at the time when cattle were placed into the pens with the feed intake nodes.

Ration Formulations and Feeding

A mixing test was performed with a 2-tonne batch of feed (as-fed) which demonstrated coefficients of variation for fat, zinc, and moisture of 4.3%, 7.8%, and 3.5%, respectively, demonstrating the ration was adequately mixed to provide consistent levels of the active ingredient, bromoform, throughout the ration delivery.

Following processing, steers were transitioned onto finisher ration using a three-step program over 18 d with each of the three rations fed for 6 d (Supplementary Table S1). For the SeaFeed cattle, the inclusion level of the SeaFeed canola oil containing bromoform was increased in each ration resulting in a bromoform level of 0 mg bromoform/kg dry matter for days 1 to 6, 8.15 mg/kg for days 7 to 12, 16.56 mg/kg for days 13 to 18, and 25.06 mg/kg from days 19 to 200.

Cattle were fed steam-flaked wheat and barley diets including a vitamin and trace mineral supplement that exceeded recommended requirements (NASEM, 2016). The ingredient and nutrient composition of the finishing rations are provided in Table 1. Feed bunks were evaluated visually at approximately 0600 hours and a residual feed estimate was made and cattle were adjusted using the standard bunk procedure to maintain ad libitum feed intake. Orts were removed and weighed to ensure the feed bunk was clean every other day to maintain fresh feed free of spoilage. Feed was delivered one time daily at 0630 hours using a truck mounted with a Roto-Mix 920 delivery box.

Table 1.

Composition and analyzed nutrient content (DM basis) of diets

Item Dietary treatment SeaFeed
Control
Finisher ration ingredient, %
 Steam-flaked wheat 52.87 52.87
 Steam-flaked barley 25.17 25.17
 Corn silage 6.88 6.88
 Finisher supplement1 5.15 5.15
 Vegetable oil 3.82 3.82
 Cereal hay 2.50 2.50
 Spent grains 2.25 2.25
 Protein meal 0.88 0.88
 Control canola oil 0.49 0.00
 SeaFeed canola oil 0.00 0.49
Active ingredient concentration
 Bromoform, mg/kg 0.00 25.00
Finisher ration formulated composition, %
 Nem, Mcal/kg 2.18 2.18
 Neg, Mcal/kg 1.49 1.49
 Metabolizable energy, MJ/kg 13.36 13.36
 Crude protein, % 13.50 13.50
 Calcium, % 0.73 0.73
 Phosphorus, % 0.37 0.37
Finisher ration analyzed composition, %
 Dry matter, % (as-fed basis) 72.13 71.93
 Neutral detergent fiber, % 20.70 20.51
 Crude protein, % 14.35 14.53
 Fat, % 6.75 6.74
 Ash, % 5.71 5.75
 Crude fiber, % 6.01 5.84
 Metabolizable energy, MJ/kg 13.58 13.57

1Finisher supplement contained vitamins, minerals, and monensin at 23.99 PPM.

Samples of steam-flaked wheat, steam-flaked barley, and finisher ration were collected daily from the feed bunk, and subsamples of the ration were dried at 100 °C to determine the daily dry matter of the ration. Monthly control and SeaFeed ration samples were collected and submitted for proximate analysis. Daily dry matters were averaged weekly and used to calculate dry matter.

Pellets were used as an attractant to the GreenFeed Pasture Systems in two pens (one control pen and one SeaFeed pen). The ingredient and nutrient composition of the pellets are provided in Supplementary Table S2. Daily feed intake of pellets was monitored and accounted for in daily feed intakes.

Testing for Bromoform Concentration of Water, Canola Oil, and Rations

Samples were tested by gas chromatography-mass spectrometry. Duplicate samples of the control and SeaFeed canola oils and control and SeaFeed finisher rations were submitted monthly to two laboratories (Analytical Services Tasmania, New Town, Tasmania, Australia and National Measurement Institute, Port Melbourne, Victoria, Australia) for testing of bromoform concentration. Water was tested in duplicate and bromoform levels were less than 1.0 mg/kg. Monthly bromoform levels for canola oil and rations are displayed in Table 2.

Table 2.

Bromoform and iodine levels in control and SeaFeed canola oil and rations over 6 mo1

Item Canola Oil Rations
Control2 SeaFeed Control SeaFeed
Bromoform, mg/kg
 Month 1 43.3 5,700.0
 Month 2 <10.00 6,290.0 <1.00 7.00
 Month 3 11.0 6,170.0 <1.00 10.00
 Month 4 26.0 6,070.0 <1.00 7.00
 Month 5 29.0 5,660.0 <1.00 10.00
 Month 6 13.0 6,290.0 2.00 10.00
Iodine, mg/L
 Month 1 <0.01 1.70 0.71 0.70
 Month 2 <0.01 1.40 0.51 0.48
 Month 3 <0.01 1.40 0.66 0.65
 Month 4 0.01 1.60 0.70 0.68
 Month 5 <0.01 1.60 0.54 0.56
 Month 6 <0.01 1.40 0.64 0.54

1Iodine levels were tested by inductively coupled plasma mass spectrometry at the National Measurements Institute. Bromoform levels were tested by gas chromatography-mass spectrometry at Analytical Services Tasmania.

2Bromoform was detected in control canola oil and was determined to be a likely result of the canola oil extraction procedure. The result was not a result of contamination.

Testing for Iodine Concentration of Water, Canola Oil, and Rations

Iodine level testing was performed by the NATA-accredited method (VL345) at the National Measurement Institute. Samples were homogenized and extracted with a solution of 25% tetramethylammonium hydroxide at 90 °C for 3 h. Following dilution and filtration, the iodine level in the solution was determined by Inductively Coupled Plasma Mass Spectrometry. The limit of reporting was 0.01 mg/kg. Water was tested in duplicate and the iodine level was 0.075 mg/L. Monthly iodine levels for canola oil and rations are displayed in Table 2.

Animal Health

Animal health was monitored daily by trained pen riders. Animals expressing clinical signs of morbidity were taken to the hospital for further evaluation, and treatment was performed according to the feedlot health protocol designed by a veterinarian. Tulathromycin plus ketoprofen (Draxxin KP Plus Ketoprofen Injectable Solution for Cattle, Zoetis, 1 mL/40 kg, subcutaneous) was the first line of treatment for Bovine Respiratory Disease. Oxytetracycline dihydrate (Bivatop 200 Long Acting Injectable, Boehringer Ingelheim Animal Health, Ingelheim, Germany, 1mL/10 kg, subcutaneous) was the second line of treatment for Bovine Respiratory Disease. There were two mortalities in the trial. The causes of death as confirmed by a field necropsy were acidosis (n = 1) and broken leg (n = 1). Two animals were diagnosed with severe polioencephalomalacia. These animals were treated, improved, and completed the feeding period, but never fully recovered in terms of growth and productivity and hence were removed from the study as the disease was unrelated to treatment. Importantly, during this period there was an increased number of polioencephalomalacia cases in the Australian feedlot industry associated with very high feed intakes and animal performance.

Emissions

Methane emissions were measured using the GreenFeed Pasture systems with one system placed in a control pen and one system placed in a SeaFeed pen within the same row for the 200-d duration of the trial. The GreenFeed Pasture systems were fitted with auto-calibration and hence there was no need for system rotation between pens. The GreenFeed Pasture systems were protected by metal paneling around the perimeter of the trailer and paneling and wood panels positioned at the alley to ensure that only a single animal could access the system at one time. Settings for the GreenFeeder Pasture systems were: 8 maximum drops per feeding period, 30-s drop interval, 18,000-s feeding period duration, 5 maximum feeding periods per day, 40 maximum drops per day per animal, and head proximity sensor at 800. Weekly maintenance included cleaning the primary air filter, refilling the bin with pellets, cleaning the head proximity sensor, cleaning the air inlet with a wire brush, and cleaning the solar panels. Carbon dioxide recoveries were performed monthly. Auto-calibrations were performed every 3 d.

Daily DMI of pellets was recorded by the number of drops animals received according to the system and multiplied by the mass of the drop and corrected for dry matter. The intake of the pellets was included in the total DMI. The average daily methane emission rate per animal was calculated. Methane was expressed as yield (g methane/kg DMI) by dividing the average daily emission by the DMI for the animal.

Feed Intake

The DMI of each animal was calculated as the sum of the dietary dry matter consumed from the basal diets offered from the Feed Intake Nodes and the dry matter consumed of the pellets from the GreenFeed Pasture Systems. Daily feed delivered per pen according to truck weights was also recorded.

Live Weight Gain

Initial body weight was calculated as the average body weight across 2 d at the commencement of the trial (May 2, 2023 and May 3, 2023). Individual live weight was measured daily for 200 d by in-pen weighing position scales (Vytelle). Cattle were weighed over a calibrated group weigh bridge and a calibrated truck weighbridge at the exit.

Carcass Data

Cattle exited the feedlot at 0600 hours on November 19, 2023. Cattle remained on full feed until the time of exit. Cattle were transported 130 km (2 h) to the processing plant. Cattle remained on water in shaded lairage pens overnight. Cattle were processed from 0600 to 0900 hours on November 20, 2023. This resulted in a total time off feed prior to slaughter of approximately 24 h and a lairage duration of 22 h. Carcass data were collected by trained personnel from Bovine Dynamics Pty Ltd (Kenmore, Queensland, Australia). Individual animal visual identification tag was recorded and affixed to the harvest sequence number for each carcass. The time of stun was recorded manually. Electronic RFID tags were recorded at the time of stun.

Rumen gross pathology was scored using a published scoring rubric for papillae color, papillae shape, and damage in the ventral sac (Jonsson et al., 2020). Carcasses were dressed to AUS-MEAT carcass standards and hot standard carcass weight (kg) was measured after evisceration and trimming (AUS-MEAT, 2005).

Carcasses were chilled overnight for approximately 22 h, ribbed between the 12th and 13th ribs, and then graded by a single qualified Meat Standards Australia grader (Polkinghorne et al., 2008). Carcass characteristics measured include eye muscle area of the longissimus thoracic et lumborum at the carcass quartering site (cm2), rib fat depth (mm) of subcutaneous fat of the longissimus thoracic et lumborum at the carcass quartering site, P8 fat depth (mm) of subcutaneous fat aligned with the crest of the third sacral vertebra, Meat Standards Australia marbling score which is the amount of fat between muscle fibers within the muscle of the longissimus thoracic et lumborum at the carcass quartering site (cm2), Aus-Meat meat color of the longissimus thoracic et lumborum at the carcass quartering site, Aus-meat fat color of intermuscular fat lateral to the longissimus thoracic et lumborum at the carcass quartering site, Meat Standards Australia Index calculated using a predictive model of eating quality, and ultimate pH of the longissimus thoracic et lumborum (AUS-MEAT, 2005; Polkinghorne et al., 2008). Aus-Meat meat color was scored as 1A = 1.00, 1B = 1.33, 1C = 1.67, 2 = 2.00, 3 = 3.00, 4 = 4.00, 5 = 5.00, and 6 = 6.00.

Trained Sensory Evaluation

Striploin sections (International Meat Purchasing Specifications 180, 8-cm length) were shipped chilled to the Gordon W. Davis Meat Laboratory at Texas Tech University. Striploins were wet-aged for 32 d and then frozen at −20 °C until sensory testing. Each striploin section was cut into two face steaks, one 2.8-cm sensory steak, and one 2.8-cm extra steak. Steaks for trained sensory evaluation were thawed for 24 to 48 h at 2°C and reached an internal temperature of 0 to 4.3 °C at the time of cooking. Groups of steaks (n = 4) were singly layered and cooked on a grill grate (Model SCC WE 61 E; Rational, Landberg am Lech, Germany) centrally located in a combi-oven (Model SCC WE 61 E; Rational) at 204 °C, 0% relative humidity, and default fan speed. Steak temperature was monitored in the cooking process using an oven core temperature probe (Model SCC WE 61 E; Rational) placed in the geometric center of a steak representative of the cooking group for size and shape. Steaks were removed from the oven at 69°C to target a peak internal temperature of 71°C. Peak internal temperature was measured in the geometric center of each steak using a calibrated type K thermocouple thermometer (AccuTuff 340, model 34040, Cooper-Atkins Corporation, Middlefield, CT, USA) and recorded. A raw weight (prior to cooking) and cooked weight (after cooking) were collected for each of the steaks.

Panelists were trained to identify and quantify attributes associated with beef according to the lexicon developed by for beef flavor in intact muscle (Adhikari et al., 2011). A continuous 100-point line scale (0 = tough, dry, not present; 100 = tender, juicy, extremely intense) was adapted and used to quantify attributes: tenderness, juiciness, beef flavor identity, browned, roasted, fat-like, buttery, grassy, liver-like, sour, overall beef flavor. Upon training, a sensory test was used to qualify a pool of 7 trained panelists for sensory evaluation. After peak internal steak temperature was measured, each steak was held on a cooling rack in an electric, insulated food transport box (Model UPCH400110, Cambro Manufacturing Company, Huntington Beach, CA) maintained at 55°C until serving. Cooked steaks were served to panelists within 15 min of their removal from the oven. Each of the 4 panel sessions consisted of 15 steaks (n = 60). No panelist served on more than 2-panel sessions per day, and a minimum of 1 h existed between the end of each session and the start of another. Panelists were seated in individual cubicles in a dark room under red incandescent lighting. Distilled water, apple juice, and unsalted saltine crackers were supplied as palate cleansers. Immediately before serving, cooked steaks were trimmed of any remaining external fat and connective tissue and cut into cubes (1 cm × 1 cm × steak thickness). Each panelist received 3 cubes for evaluation. Study samples were evaluated every 3.5 to 4 min by 6 to 7 panelists per session. Panelist responses were recorded on an electronic ballot generated by an online survey software (Qualtrics Surveys, Provo, UT) using a tablet (iPad, Apple, Inc., Cupertino, CA). Intensity ratings for each attribute were averaged among panelists for each sample.

Bromoform, Bromine, and Iodine Residue Testing in Kidney, Fat, and Muscle

Kidney samples (n = 30 control, n = 30 SeaFeed) of approximately 70 g of tissue were obtained at the time of removal from the carcass. Subcutaneous fat samples (n = 30 control, n = 30 SeaFeed) of approximately 70 g of tissue were obtained from the ventral brisket region of the carcass. Lean skeletal muscle samples (n = 30 control, n = 30 SeaFeed) of approximately 70 g of tissue were obtained from the foreshank including the flexor carpi ulnaris and superficial digital flexor muscles.

All tissue samples were stored in sterile containers, chilled with ice bricks, and transported chilled overnight to the laboratory. Bromoform testing was completed by gas chromatography-mass spectrometry (Analytical Services Tasmania). Bromine and Iodine testing was completed by the NATA-accredited method (VL345) at the National Measurement Institute.

Statistical Analyses

The experimental unit was defined as the individual animal for all outcome variables. The fixed effect of treatment and random effect of block were included in the model. Statistical significance of interactions and main effects were defined at P < 0.05 and a trend at P < 0.10 levels. Variables were analyzed using a linear mixed model, PROC MIXED SAS version 9.4 (SAS Institute Inc., Cary, NC, USA).

The experiment was analyzed with dead cattle removed as the cause of death was not associated with treatment. One individual was euthanized due to a broken leg which was not associated with treatment and hence was removed from the study. The other mortality was diagnosed as acidosis on postmortem examination and was removed from the study. Two additional animals with severe polioencephalomalacia were removed from the study and details of these animals are included above.

RESULTS AND DISCUSSION

Stability of Bromoform in SeaFeed Canola Oil and Ration Over Six Months

The level of bromoform in the SeaFeed canola oil was stable over the 6-mo experimental phase of the trial (Table 2). A low level, less than 50 mg/kg, of bromoform was detected in the control canola oil. It was confirmed that this low level of detection was not due to contamination, but a result of the extraction process used in canola oil manufacturing.

The level of bromoform in the SeaFeed and control rations are summarized in Table 2, demonstrating detection of bromoform in total-mixed rations using gas chromatography-mass spectrometry is possible. Bromoform levels in rations with SeaFeed were consistent over the 6 mo.

Iodine Levels in SeaFeed Canola Oil and Ration Over Six Months

The level of iodine in control and SeaFeed canola oil and rations was reported over 6 mo (Table 2). Iodine was not detected in the control canola oil. However, iodine levels ranged from 1.4 to 1.7 mg/L in the SeaFeed canola oil. Levels of iodine in control and SeaFeed rations were similar.

Animal Performance

Animal performance data including body weights and DMI are provided in Table 3. By experimental design, initial body weight did not differ between treatments (P = 0.64). DMI throughout the feeding period was not different between treatments (P = 0.67). The final body weight was 19.7 kg heavier (P < 0.01) for SeaFeed cattle as compared to control cattle. Average daily gain was 0.09 kg/d higher (P < 0.01) in cattle fed SeaFeed as compared to control cattle over the 200-d feeding period. Gain:feed was 0.01 higher (P < 0.01) for steers fed SeaFeed as compared to controls.

Table 3.

The effect of SeaFeed canola oil on performance of Angus steers

Item Treatment SEM P-value
Control SeaFeed
Steers, n 78 78
Body weight, kg
 Initial 473.9 474.9 1.40 0.64
 Day 50 609.4 623.7 8.34 <0.01
 Day 100 701.7 718.0 8.21 <0.01
 Day 150 765.8 783.9 7.51 <0.01
 Final 817.3 837.0 7.58 <0.01
Average daily gain, kg
 Days 1 to 50 2.71 2.98 0.152 <0.01
 Days 51 to 100 1.82 1.84 0.040 0.67
 Days 101 to 150 1.28 1.32 0.033 0.44
 Days 151 to 200 1.00 1.03 0.038 0.58
 Days 1 to 100 2.28 2.43 0.075 <0.01
 Days 1 to 150 1.95 2.06 0.046 <0.01
 Days 1 to 200 1.72 1.81 0.035 <0.01
Daily DMI, kg per individual
 Days 1 to 50 10.90 10.98 0.396 0.69
 Days 51 to 100 12.37 12.32 0.270 0.76
 Days 101 to 150 11.23 11.08 0.354 0.40
 Days 151 to 200 10.47 10.36 0.321 0.46
 Days 1 to 100 11.64 11.65 0.329 0.95
 Days 1 to 150 11.50 11.46 0.336 0.78
 Days 1 to 200 11.24 11.19 0.331 0.67
Gain:feed
 Days 1 to 50 0.249 0.271 0.0050 <0.01
 Days 51 to 100 0.147 0.150 0.0034 0.52
 Days 101 to 150 0.114 0.121 0.0047 0.07
 Days 151 to 200 0.093 0.098 0.0040 0.27
 Days 1 to 100 0.196 0.209 0.0023 <0.01
 Days 1 to 150 0.169 0.181 0.0019 <0.01
 Days 1 to 200 0.153 0.163 0.0020 <0.01

Animal Health

There were two mortalities in the trial, both in the control group. Causes of death as confirmed by a field necropsy were acidosis (n = 1) and broken leg (n = 1). There was no difference (P = 0.52) in morbidity between the treatment groups. Bovine respiratory disease was the most common ailment with both treatment groups treating 44.9% of the cattle (35/78 individuals). Two animals were diagnosed with severe polioencephalomalacia. These animals were treated, improved, and completed the feeding period, but never fully recovered in terms of growth and productivity and hence were removed from the study as the disease was unrelated to treatment. Importantly, during this period there was an increased number of polioencephalomalacia cases in the Australian feedlot industry associated with very high feed intakes and animal performance.

Methane Emissions

GreenFeed Pasture System visitation data are provided in Supplementary Table S3. A total of 17,687 valid observations with a mean duration of 3 min 51 sec were included in the data set. Of the 76 individuals with access to the GreenFeed Pasture systems, 71 provided acceptable data, demonstrating a visitation rate of 93.4% of animals. The average number of observations per day was 88, 53.5 in the control pen, and 34.9 in the SeaFeed pen.

Methane emissions data are provided in Table 4. Steers fed SeaFeed produced 51.7% less (P < 0.01) methane and yielded 50.5% less (P < 0.01) methane over the 200-d feeding period as compared to cattle fed the control ration. Peak methane inhibition occurred on day 29 on feed with 90.6% less methane production in cattle fed SeaFeed as compared to control animals. Over the entire feeding period, methane production for control Angus steers was 133.74 g methane per individual per day and steers fed SeaFeed produced 65.54 g methane per individual per day. SeaFeed reduced (P < 0.01) methane intensity by 55.4% over the 200-d feeding period.

Table 4.

The effect of SeaFeed canola oil on emissions of Angus steers

Item Treatment Reduction (%) SEM P-value
Control SeaFeed
Steers with valid observations, n 37 34
Methane production, g CH4/d
 Days 1 to 20 (adaptation) 136.72 72.06 47.3 9.604 to 9.787 <0.01
 Days 1 to 50 152.56 49.31 67.7 5.977 to 6.376 <0.01
 Days 51 to 100 133.49 58.03 56.5 5.758 to 5.586 <0.01
 Days 101 to 150 123.58 68.19 44.8 4.516 to 4.584 <0.01
 Days 151 to 200 122.5 78.54 35.9 4.841 <0.01
 Days1 to 100 141.99 56.23 60.4 5.388 to 5.469 <0.01
 Days1 to 150 137.39 59.67 56.6 4.690 to 4.759 <0.01
 Days 1 to 200 133.74 64.54 51.7 4.392 to 4.582 <0.01
Methane yield, g CH4/kg total DM intake
 Days 1 to 20 (adaptation) 13.49 7.55 44.0 0.953 to 0.971 <0.01
 Days 1 to 50 13.10 4.94 62.3 0.620 to 0.661 <0.01
 Days 51 to 100 11.32 5.01 55.8 0.477 to 0.484 <0.01
 Days 101 to 150 11.10 6.02 45.8 0.421 to 0.428 <0.01
 Days 151 to 200 11.84 7.55 36.2 0.497 <0.01
 Days 1 to 100 12.14 5.23 56.9 0.479 to 0.487 <0.01
 Days 1 to 150 11.84 5.36 54.7 0.420 to 0.426 <0.01
 Days 1 to 200 11.86 5.87 50.5 0.389 to 0.406 <0.01
Methane intensity, g CH4/kg liveweight gain
 Days 1 to 20 (Adaptation) 70.97 21.54 69.6 8.500 to 8.662 <0.01
 Days 1 to 50 61.79 18.50 70.1 2.687 to 2.733 <0.01
 Days 51 to 100 71.84 34.13 52.5 3.618 <0.01
 Days 101 to 150 99.42 57.87 41.8 5.857 to 6.223 <0.01
 Days 151 to 200 162.49 88.19 45.7 17.455 <0.01
 Days1 to 100 66.79 24.72 63.0 2.424 to 2.499 <0.01
 Days1 to 150 73.35 29.70 59.5 2.472 to 2.508 <0.01
 Days 1 to 200 82.73 36.86 55.4 2.794 to 2.914 <0.01

Carcass Characteristics

Carcass grading data and rumen gross pathology scores are provided in Table 5. Steers fed SeaFeed tended (P = 0.097) to produce carcasses with 6.9 kg additional hot carcass weight as compared to cattle fed control rations. There was no difference (P > 0.10) in marbling, meat color, eye muscle area, rib fat, ultimate pH, or MSA index. Cattle fed SeaFeed tended (P = 0.054) to have higher fat color scores than control carcasses; however, the magnitude of this difference was only 0.18 units on a 9-point scale. Rumen papillae of steers fed SeaFeed were more gray in color (P < 0.01) and more oval in shape (P < 0.01) as compared to steers fed control rations.

Table 5.

The effect of SeaFeed canola oil on carcass weight and characteristics of Angus steers

Item Treatment SEM P-value
Control SeaFeed
Carcasses, n 78 78
Hot carcass weight, kg 463.7 470.6 2.903 0.097
MSA marbling 568.3 549.3 25.668 0.26
Aus-Meat marbling 3.4 3.2 0.232 0.38
Meat color1 1.7 1.6 0.038 0.30
Fat color 0.5 0.6 0.065 0.054
Eye muscle area, cm2 74.4 75.3 1.021 0.51
Rib fat, mm 8.3 8.2 0.144 0.57
P8 fat, mm 28.3 28.7 1.255 0.74
Chiller assessment pH 5.48 5.48 0.005 0.47
MSA index 64.89 64.84 0.280 0.83
Ossification, cold 158.1 154.7 1.605 0.14
Dentition 2.8 2.7 0.171 0.46
Rumen papillae color 0.43 0.91 0.139 <0.01
Rumen papillae shape 0.75 1.22 0.133 <0.01
Rumen papillae damage 0.01 0.01 0.016 1.00

1Meat color was scored as 1A = 1.00, 1B = 1.33, 1C = 1.67, 2 = 2.00, 3 = 3.00, 4 = 4.00, 5 = 5.00, 6 = 6.00.

Residue Testing for Bromoform, Iodine, and Bromine

In regards to food safety and residues, all muscle, fat, and kidney samples were free from bromoform residues to a limit of detection of 0.05 mg/kg bromoform in 30 control and 30 SeaFeed animals (Table 6). Bromine residues in kidney samples were higher (P < 0.01) in the SeaFeed group as compared to controls. While bromine residues in meat samples were higher (P < 0.01) in the SeaFeed group as compared to controls, residues were much lower than those found in kidney samples. There was no difference (P = 0.66) in bromine levels in fat. Iodine levels were higher (P = 0.03) in fat samples from control animals as compared to samples from SeaFeed animals. There was no difference (P > 0.50) in iodine levels of kidney and muscle.

Table 6.

The effect of SeaFeed canola oil on bromoform, bromine, and iodine residues of Angus steers1

Item Treatment SEM P-value
Control SeaFeed
Carcasses, n 30 30
Bromoform, mg/kg
 Fat <0.05 <0.05 0.000 1.00
 Kidney <0.05 <0.05 0.000 1.00
 Muscle <0.05 <0.05 0.000 1.00
Bromine, mg/kg
 Fat 2.88 2.98 0.164 to 0.167 0.66
 Kidney 14.73 21.66 0.295 to 0.296 <0.01
 Muscle 5.2 7.4 0.171 to 0.174 <0.01
Iodine, mg/kg
 Fat 0.0036 0.0004 0.00101 to 0.00103 0.03
 Kidney 0.0774 0.0782 0.00155 to 0.00157 0.72
 Muscle 0.0180 0.0183 0.000591 to 0.000601 0.68

1Results presented on wet matter basis.

Trained Panel Sensory Characteristics

Results of the trained sensory panel analyses are provided in Table 7. Cattle fed SeaFeed produced strip loin steaks that were similar (P > 0.05) in eating quality to control cattle.

Table 7.

Sensory characteristics of striploin steaks (n = 60) from Angus steers fed SeaFeed canola oil

Attribute Treatment SEM P-value
Control SeaFeed
Tenderness 55.70 53.40 0.849 0.07
Juiciness 50.40 48.80 0.908 0.22
Flavor attributes
 Beef 54.10 53.60 0.340 0.27
 Browned 50.90 51.00 0.425 0.90
 Roasted 52.30 52.10 0.352 0.58
 Fat-like 11.90 11.30 0.377 0.30
 Buttery 1.19 1.22 0.250 0.93
 Grassy 3.61 2.95 0.300 0.13
 Liver-like 1.42 1.08 0.219 0.28
 Sour 1.73 1.63 0.253 0.77
 Overall beef flavor 53.00 52.70 0.681 0.79

DISCUSSION

These results demonstrate that SeaFeed is a safe and effective methane mitigant with performance benefits when fed to Angus cattle at a rate of 25 mg bromoform/kg dry matter for 200 d. The stability of the active metabolite, bromoform, in canola oil was demonstrated over the 6-mo duration of the project which is consistent with recent studies (Magnusson et al., 2020; Tan et al., 2023; Cowley et al., 2024).

While the stability of bromoform levels in the oil is established and consistent with the results of the present study, laboratory analyses of bromoform levels in total-mixed rations containing Asparagopsis-infused vegetable oil have not been previously published. Importantly, this study demonstrated consistent detection of bromoform in the ration throughout the study. While levels presented are lower than expected, this may be due to the volatility of bromoform during mixing, feeding, sampling, transport to the laboratory, and final testing. Additionally, it may be possible that the levels are extremely low and hence difficult to accurately detect the true level with current analysis methods. Nevertheless, the efficacy of the bromoform was clearly evident in the emissions reduction results.

The inhibitory effect of SeaFeed on methane emissions was evident in the results throughout the duration of the feeding period with 51.7% reduction in methane emissions. As the cattle were adapted to the finisher diet, the level of inclusion of bromoform and total daily DMI increased and hence methane inhibition increased. The peak reduction in methane production occurred on day 29 of the feeding period with 90.6% less methane production in cattle fed SeaFeed as compared to control animals. SeaFeed also reduced methane intensity and yield. Over the 200-d duration of the feeding trial, it is evident that the inhibitory effect on methane emissions was reduced over time. This observation was identified by Cowley et al. (2024) in the low Asparagopsis inclusion group where bromoform was included at 17 mg bromoform/kg DMI. Cowley et al. (2024) explained that adaptation leading to loss of antimethanogenic efficacy has not occurred in published studies where Asparagopsis products have been fed at the higher end of the range of effective inclusion levels. There are several hypotheses for this observation which have been noted in other work. It is quite possible that methanogens develop tolerance to the bromoform over continuous exposure and hence their activity levels and efficacy decrease over time. An alternative hypothesis that the authors particularly support is that the dose rate of bromoform (mg bromoform/kg body weight) is associated with the efficacy of the mitigant and hence as cattle become heavier and feed intake is reduced, the dose rate of bromoform is reduced and hence the inhibitory effect is reduced. More research is required to determine the true mechanism behind the moderation in methane inhibition over the feeding period and to develop strategies to extend the mitigation effects of the additive. Further research should be completed on the effect of the dose rate of bromoform, not simply the dose delivered.

Originally, the scientific community postulated that redirection of energy lost as methane would result in improved feed utilization and improved animal productivity (Patra, 2012). Specifically, a 22% increase in average daily gain was identified in Brahman-Angus cross steers fed 0.2% organic matter Asparagopsis taxiformis over 90 d (Kinley et al., 2020). The present study identified a significant performance response with an additional 19.7 kg in live weight gain, 0.09 kg average daily gain, and 0.01 kg gain:feed when cattle were fed SeaFeed. However, recent publications have not identified a performance response to feeding Asparagopsis or vegetable oil products containing active metabolites of Asparagopsis (Li et al., 2018; Stefenoni et al., 2021; Cowley et al., 2024). It is likely that many of the recent trials had experimental design constraints such as the use of chambers or small sample sizes that limited feed intake and natural behaviors of cattle and hence performance was unlikely maximized. The authors believe that this trial allowed the cattle to reach their true performance potential due to the commercial realities of the trial being performed in a large, commercial feedlot. Specifically, the trial was completed with professional ration formulation, consistent feed preparation and delivery, excellent pen conditions, and reliable daily execution to achieve maximal feed intake and performance parameters.

This study identified mild changes in rumen color and shape associated with feeding SeaFeed; however, all rumens in the study were healthy and did not show signs of damage. The minor changes in the papillae shape and color are not alarming.

Meat, kidney, and fat from cattle fed SeaFeed for 200 d were free from bromoform residues, demonstrating the safety of feeding SeaFeed for extended periods of time. These results are consistent with previous work (Kinley et al., 2020; Cowley et al., 2024). This is the most extensive data set with 30 treated and 30 control animals tested, demonstrating a much more thorough level of evidence than most toxicology studies. Since methanogens in the rumen metabolize bromoform through reductive dehalogenation, these results were expected (Glasson et al., 2022). Bromine levels were 6.92 mg/kg higher in the kidneys of cattle fed SeaFeed as compared to controls. Bromine levels were 2.2 mg/kg higher in the muscle of cattle fed SeaFeed as compared to controls. These elevated levels of bromine in cattle fed bromoform are consistent with previous publications (Cowley et al., 2024). Bromine is excreted via the urinary system and hence the elevated levels in the kidneys were expected. Importantly, the levels of bromine observed in the muscle and kidney products are well below the acceptable daily intakes for bromine given expected serving sizes and hence do not represent a human food safety risk (Cowley et al., 2024).

CONCLUSION

This 200-d study completed in a commercial feedlot demonstrates that supplementing a steam-flaked wheat and barley diet with SeaFeed (25 mg bromoform/kg DMI) reduced methane emissions by 51.7%, improved performance with an additional 19.7 kg of live exit weight, and produced safe beef with similar eating quality to conventional beef.

Supplementary Material

txae116_suppl_Supplementary_Table_S1
txae116_suppl_Supplementary_Table_S2
txae116_suppl_Supplementary_Table_S3

Acknowledgments

The authors would like to sincerely thank the Australian Government for their generous support of this research through the Methane Emissions Reduction in Livestock Grant (MERL 000026). The authors would like to express their sincere gratitude to the project advisory board including Chair Sarah Zeljko, Dr. Rocky de Nys, Dr. Matthew George, and Jim Cudmore for dedicating their time and expertise to the successful completion of this research project. Finally, the authors would like to recognize the significant contributions of Stockyard Beef Pty Ltd for providing the cattle, facility, feed, and staff to perform this highly intensive research project, demonstrating their commitment to completion of quality research to solve the challenge of climate change. Specifically, the authors would like to recognize Lachie Hart, Lisa Sharp, Marcus Doumany, Sarah Duffield, Molly Sage, and all of the outstanding staff from Stockyard Beef Pty Ltd for their commitment to this project. This research was supported by the Australian Government Methane Emissions Reduction in Livestock program (MERL000026).

Glossary

Abbreviations

CH4

methane

DM

dry matter

kg

kilogram

Mcal

megacalorie

mg

milligram

MJ

megajoule

Neg

net energy of gain

Nem

net energy of maintenance

PPM

parts per million

SeaFeed

Asparagopsis armata infused canola oil

Contributor Information

Melissa M George, Bovine Dynamics Pty Ltd, Kenmore, Queensland, 4069 , Australia.

Samuel V Platts, Bovine Dynamics Pty Ltd, Kenmore, Queensland, 4069, Australia.

Brent A Berry, Bovine Dynamics Pty Ltd, Kenmore, Queensland, 4069, Australia.

Markus F Miller, Department of Animal and Food Sciences, Davis College of Agricultural Sciences and Natural Resources, Texas Tech University, Lubbock, TX 79409, USA.

Anna M Carlock, Department of Animal and Food Sciences, Davis College of Agricultural Sciences and Natural Resources, Texas Tech University, Lubbock, TX 79409, USA.

Taylor M Horton, Department of Animal and Food Sciences, Davis College of Agricultural Sciences and Natural Resources, Texas Tech University, Lubbock, TX 79409, USA.

Matthew H George, Bovine Dynamics Pty Ltd, Kenmore, Queensland, 4069, Australia.

Conflict of interest statement

None declared.

References

  1. Adhikari, K., Chambers E. IV, Miller R., Vazquez-Araujo L., Bhumiratana N., and Philip C... 2011. Development of a lexicon for beef flavor in intact muscle. J. Sens. Stud. 26:413–420. doi: 10.1111/j.1745-459X.2011.00356.x [DOI] [Google Scholar]
  2. Alemu, A. W., Gruninger R. J., Zhang X. M., O’Hara E., Kindermann M., and Beauchemin K. A... 2023. 3-Nitrooxypropanol supplementation of a forage diet decreased enteric methane emissions from beef cattle without affecting feed intake and apparent total-tract digestibility. J. Anim. Sci. 101:skad001. doi: 10.1093/jas/skad001 [DOI] [PMC free article] [PubMed] [Google Scholar]
  3. Alemu, A. W., Shreck A. L., Booker C. W., McGinn S. M., Pekrul L. K. D., Kindermann M., and Beauchemin K. A... 2020. Use of 3-nitrooxypropanol in a commercial feedlot to decrease enteric methane emissions from cattle fed a corn-based finishing diet. J. Anim. Sci. 99:1. doi: 10.1093/jas/skaa394 [DOI] [PMC free article] [PubMed] [Google Scholar]
  4. Almeida, A. K., Cowley F., McMeniman J. P., Karagiannis A., Walker N., Tamassia L. F. M., McGrath J. J., and Hegarty R. S... 2023. Effect of 3-nitrooxypropanol on enteric methane emissions of feedlot cattle fed with a tempered barley-based diet with canola oil. J. Anim. Sci. 101:skad237. doi: 10.1093/jas/skad237 [DOI] [PMC free article] [PubMed] [Google Scholar]
  5. Araújo, T. L. R., Rabelo C. H. S., Cardoso A. S., Carvalho V. V., Acedo T. S., Tamassia L. F. M., Vasconcelos G. S. F. M., Duval S. M., Kindermann M., Gouvea V. N.,. et al. 2023. Feeding 3-nitrooxypropanol reduces methane emissions by feedlot cattle on tropical conditions. J. Anim. Sci. 101:skad225. doi: 10.1093/jas/skad225 [DOI] [PMC free article] [PubMed] [Google Scholar]
  6. AUS-MEAT. 2005. Handbook of Australian meat. 7th ed. Brisbane, Australia: Aus-Meat. [Google Scholar]
  7. Cowley, F. C., Kinley R. D., Mackenzie S. L., Fortes M. R. S., Palmieri C., Simanungkalit G., Almeida A. K., and Roque B. M... 2024. Bioactive metabolites of Asparagopsis stabilized in canola oil completely suppress methane emissions in beef cattle fed a feedlot diet. J. Anim. Sci. 102:skae109. doi: 10.1093/jas/skae109 [DOI] [PMC free article] [PubMed] [Google Scholar]
  8. Glasson, C. R. K., Kinley R. D., de Nys R., King N., Adams S. L., Packer M. A., Svenson J., Eason C. T., and Magnusson M... 2022. Benefits and risks of including the bromoform containing seaweed Asparagopsis in feed for the reduction of methane production from ruminants. Algal Res. 64:102673. doi: 10.1016/j.algal.2022.102673 [DOI] [Google Scholar]
  9. Hegarty, R. S., Cortez Passetti R. A., Dittmer K. M., Wang Y., Shelton S., Emmet-Booth J., Wollenberg E., McAllister T., Leahy S., and Beauchemin K. N. G... 2021. An evaluation of emerging feed additives to reduce methane emissions from livestock. A report coordinated by Climate Change, Agriculture and Food Security (CCAFS) and the New Zealand Agricultural Greenhouse Gas Research Centre (NZAGRC) initiative of the Global Research Alliance (GRA).
  10. Jonsson, N. N., Ferguson H. J., Koh-Tan H. H. C., McCartney C. A., Cernat R. C., Strachan E. M., Thomson W., Snelling T. J., Harvey C. D., Andonovic I.,. et al. 2020. Postmortem observations on rumen wall histology and gene expression and ruminal and caecal content of beef cattle fattened on barley-based rations. Animal. 14:1447–1460. doi: 10.1017/S1751731119002878 [DOI] [PubMed] [Google Scholar]
  11. Kinley, R. D., Martinez-Fernandez G., Matthews M. K., de Nys R., Magnusson M., and Tomkins N. W... 2020. Mitigating the carbon footprint and improving productivity of ruminant livestock agriculture using a red seaweed. J. Clean Prod. 259:120836. doi: 10.1016/j.jclepro.2020.120836 [DOI] [Google Scholar]
  12. Li, X., Norman H. C., Kinley R. D., Laurence M., Wilmot M., Bender H., de Nys R., and Tomkins N... 2018. Asparagopsis taxiformis decreases enteric methane production from sheep. Anim. Prod. Sci. 58:681–688. doi: 10.1071/an15883 [DOI] [Google Scholar]
  13. Magnusson, M., Vucko M. J., Neoh T. L., and de Nys R.. ,2020. Using oil immersion to deliver a naturally-derived, stable bromoform product from the red seaweed Asparagopsis taxiformis. Algal Res. 51:102065. doi: 10.1016/j.algal.2020.102065 [DOI] [Google Scholar]
  14. National Academies of Sciences, E., Medicine. 2016. Nutrient requirements of beef cattle. 8th revised ed. The National Academies Press, Washington, DC. [Google Scholar]
  15. Patra, A. K. 2012. Enteric methane mitigation technologies for ruminant livestock: a synthesis of current research and future directions. Environ. Monit. Assess. 184:1929–1952. doi: 10.1007/s10661-011-2090-y [DOI] [PubMed] [Google Scholar]
  16. Polkinghorne, R., Thompson J. M., Watson R., Gee A., and Porter M... 2008. Evolution of the Meat Standards Australia (MSA) beef grading system. Aust. J. Exp. Agric. 48:1351–1359. doi: 10.1071/ea07177 [DOI] [Google Scholar]
  17. Ridoutt, B., Lehnert S. A., Denman S., Charmley E., Kinley R., and Dominik S... 2022. Potential GHG emission benefits of Asparagopsis taxiformis feed supplement in Australian beef cattle feedlots. J. Clean Prod. 337:130499. doi: 10.1016/j.jclepro.2022.130499 [DOI] [Google Scholar]
  18. Roque, B. M., Salwen J. K., Kinley R., and Kebreab E... 2019. Inclusion of Asparagopsis armata in lactating dairy cows’ diet reduces enteric methane emission by over 50 percent. J. Clean Prod. 234:132–138. doi: 10.1016/j.jclepro.2019.06.193 [DOI] [Google Scholar]
  19. Stackhouse-Lawson, K. R., Rotz C. A., Oltjen J. W., and Mitloehner F. M... 2012. Carbon footprint and ammonia emissions of California beef production systems1. J. Anim. Sci. 90:4641–4655. doi: 10.2527/jas.2011-4653 [DOI] [PubMed] [Google Scholar]
  20. Stefenoni, H. A., Räisänen S. E., Cueva S. F., Wasson D. E., Lage C. F. A., Melgar A., Fetter M. E., Smith P., Hennessy M., Vecchiarelli B.,. et al. 2021. Effects of the macroalga Asparagopsis taxiformis and oregano leaves on methane emission, rumen fermentation, and lactational performance of dairy cows. J. Dairy Sci. 104:4157–4173. doi: 10.3168/jds.2020-19686 [DOI] [PubMed] [Google Scholar]
  21. Tan, S., Harris J., Roque B. M., Askew S., and Kinley R. D... 2023. Shelf-life stability of Asparagopsis bromoform in oil and freeze-dried powder. J. Appl. Phycol. 35:291–299. doi: 10.1007/s10811-022-02876-y [DOI] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

txae116_suppl_Supplementary_Table_S1
txae116_suppl_Supplementary_Table_S2
txae116_suppl_Supplementary_Table_S3

Articles from Translational Animal Science are provided here courtesy of Oxford University Press

RESOURCES