Next Article in Journal
Identifying the Restoration Stages of Degraded Alpine Meadow Patches Using Hyperspectral Imaging and Machine Learning Techniques
Previous Article in Journal
Improvement in Natural Antioxidant Recovery from Sea Buckthorn Berries Using Predictive Model-Based Optimization
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

Advancements in Real-Time Monitoring of Enteric Methane Emissions from Ruminants

1
IMaR Research Centre, Munster Technological University, V92 CX88 Tralee, Ireland
2
Moonsyst, Kinsale, P17T183 Cork, Ireland
*
Author to whom correspondence should be addressed.
Agriculture 2024, 14(7), 1096; https://doi.org/10.3390/agriculture14071096
Submission received: 5 June 2024 / Revised: 27 June 2024 / Accepted: 2 July 2024 / Published: 8 July 2024
(This article belongs to the Section Farm Animal Production)

Abstract

:
The agricultural sector is responsible for a significant proportion of global anthropogenic methane (CH4) emissions, with enteric CH4 produced from ruminant livestock representing approximately 28% of the total. The development of effective mitigation strategies necessitates the accurate and actionable monitoring of CH4 emissions. However, a considerable research gap remains concerning real-time monitoring techniques capable of supporting on-farm enteric CH4 mitigation strategies. To bridge this research gap, this study explores the current status of real-time enteric CH4 emission monitoring techniques and technologies for ruminants. The study achieves this by reviewing key biomarkers and proxies for ruminant emissions, examining established animal-based measurement techniques, exploring emerging technologies, and critically assessing technological limitations and opportunities. By shedding light on this research area, this study aims to assist stakeholders in developing a viable pathway for on-farm emission monitoring, with the hope of facilitating a meaningful reduction in GHG emissions from the livestock sector.

1. Introduction

The growing global population has put increasing pressure on the agricultural sector to increase food production. Simultaneously, the pressing issues of climate change and resource scarcity requires the urgent development of sustainable and efficient farming technologies and practices. For instance, the agricultural sector has consistently accounted for approximately 12% of total global greenhouse gas (GHG) emissions and 11% within the European Union (EU) [1,2]. These emissions have been predominantly driven by the release of methane (CH4), largely attributable to bovine and ovine enteric fermentation, and nitrous oxide (N2O), stemming from the application of manure and animal excreta onto pasture [3]. Notably, livestock enteric fermentation alone represented 43% of total EU agricultural emissions in 2020 [1]. Having the majority of sector emissions originating from biogenic sources presents a unique challenge, as emissions derived from agriculture sources do not easily allow for technological solutions as would exist or evolve within other sectors [4]. Consequently, there is an urgent need for the development and adoption of technologies and strategies to mitigate these GHG emissions, while ensuring maximum sustainable agriculture productivity.
Precision livestock farming (PLF) has emerged as a promising mechanism to assist with the challenges facing the agriculture sector, where it utilises a range of technologies, including sensors, data analysis, and automation, to enhance farm management practices and foster data-driven decision making [5]. One particularly promising innovation emerging from the PLF field is the real-time monitoring of enteric CH4 emissions from ruminants, where it can offer researchers and farmers actionable insights into animal environmental footprints, health, and welfare under various conditions [6]. By precisely quantifying farm emissions, stakeholders can make data-driven decisions that simultaneously reduce their carbon footprint while optimising herd care, due to the association between enteric emissions and key health factors such as feed intake, dietary chemical composition, digestive health, and animal management [7]. Moreover, the real-time data generated hold significant promise in accelerating the development and refinement of targeted emission mitigation strategies. Such strategies include selective breeding for low-emission animals and evaluating the effectiveness of precision feeding, dietary changes, and farming practices interventions. Furthermore, the implementation of such mitigation strategies, combined with verifiable emission measurements, could underpin the creation of traceable carbon credit markets within the livestock sector, potentially rewarding farmers financially for their GHG mitigation efforts. Such mitigation efforts could have a meaningful and lasting impact on the livestock industry, as underscored by recent research showing a variation in emissions by over 30% among similar animals under similar conditions, suggesting significant potential for reduction [8].
Despite the potential of real-time monitoring technologies to accurately quantify individual ruminant emissions, a significant research gap remains in the development of practical, on-farm techniques that can effectively inform and support CH4 mitigation strategies within the livestock sector. Therefore, this study contributes to the current literature by reviewing the existing and emerging real-time monitoring techniques for enteric CH4 emissions in ruminants. Through a critical analysis and discussion of these approaches, this study aims to assist stakeholders in establishing a viable pathway for on-farm emission monitoring, ultimately contributing to a reduction in GHG emissions from the livestock sector. To achieve this goal, the following objectives were put forward: (i) to review and critically assess the key biomarkers and proxies indicative of CH4 emissions from ruminants; (ii) to comprehensively examine and evaluate established animal-based techniques for measuring enteric CH4 emissions; (iii) to explore emerging technologies and techniques for real-time enteric emission monitoring; and (iv) to critically evaluate the major technological limitations and future opportunities for accurate on-farm CH4 monitoring.

Enteric CH4 Emissions

On a worldwide basis, enteric CH4 produced from ruminant livestock is a substantial source of anthropogenic CH4 emissions, representing approximately 28% of the global total [9]. Enteric CH4, a colourless and odourless gas, is produced as a by-product of the microbial fermentation process within the digestive systems of ruminant animals (e.g., cattle, swine, and sheep). During this fermentation process, carbohydrates are broken down by microbes into simple molecules, facilitating absorption into the bloodstream. A major by-product is CH4, formed when methanogenic archaea combine carbon dioxide (CO2) and hydrogen (H2) [10]. The vast majority of this CH4 (97%) is released through the mouth and nostrils during breathing and eructation, with a significantly smaller amount (3%) emitted from the hindgut as flatus (see Figure 1) [11,12].
Understanding and measuring enteric CH4 production can play an essential role in the evaluation of ruminant livestock productivity, as methanogenesis plays a key role in their energy metabolism. Methanogens play an important role in the rumen by reducing CO2 to CH4 and water (H2O), utilising excess H2 that would otherwise negatively impact fermentation rates and microbial growth [13]. Therefore, reducing enteric methanogenesis holds the potential of simultaneously improving livestock production efficiencies and reducing environmental impact. This is evidenced by the significant energy loss ruminants experience through enteric CH4 production, ranging from 2% to 12% of gross energy intake, depending on diet [14]. Thus, the accurate measurement of ruminant enteric CH4 emissions could be essential to facilitating improvements in livestock productivity, improved health, and the development of CH4 mitigation strategies.
Figure 1. Processes of methane production in ruminants. Source [15].
Figure 1. Processes of methane production in ruminants. Source [15].
Agriculture 14 01096 g001

2. Monitoring of Biomarkers and Proxies for Ruminant Health and CH4 Emissions

The use of biomarkers and proxies to assess ruminant health and CH4 emissions is a rapidly developing field with the potential to transform livestock management. These indicators offer alternatives to direct CH4 measurement, providing valuable insights into the complex mechanisms of ruminant digestion. This growing interest has largely been driven by recent advancements in animal-based monitoring and sensors capable of real-time health and emission measurement. Specifically, these real-time data can be critical in reducing the occurrence of animal health issues, thereby decreasing incidents of reduced productivity, morbidity, and mortality in livestock [16]. Subsequently, such advancements contribute to the reduction of animal emission levels by directly improving livestock health and productivity. This section examines the specific behavioural and physiological parameters used for the real-time monitoring of ruminants, particularly focusing on biomarkers and proxies for ruminant health and emission levels.

2.1. Feed Intake and Feeding Behaviour

Feed intake is a complex trait influenced by a multitude of factors including animal genetics, rumen function, feed availability and quality, and overall health. Given that enteric CH4 is a by-product of microbial fermentation originating from the rumen and hindgut, both feed intake and diet quality have long been recognised as key parameters in enteric CH4 production [17]. Consequently, associated characteristics such as dry matter intake, metabolisable energy intake, and feed efficiency are often used as essential inputs in various emission modelling algorithms and techniques [7,17]. However, these emission estimates can vary significantly (+35%) for a particular diet, reflecting the complexity of factors influencing enteric CH4 production [18]. The influence of feed intake is supported in the experimental literature, with Ellis et al. (2007) demonstrating that dry matter intake predicted CH4 production in dairy cattle with an R2 of 0.64 and metabolizable energy intake with an R2 of 0.53 [17,19]. These results are consistent with earlier findings by Mills et al. (2003), who demonstrated similar predictions of CH4 production with dry matter intake (R2 of 0.60) and metabolisable energy intake (R2 of 0.55) [17]. Expanding on these findings, Moraes et al. (2014) reported gross energy intake as a major explanatory variable for predicting CH4 emissions, achieving a root mean squared prediction error of 3.01 MJ/day [17]. Feed efficiency is another influential factor affecting enteric CH4 production, where it represents the difference between a cow’s energy expenditure (milk production, maintenance, growth, and reproduction) and the energy it gains from consumed nutrients. Recent research has revealed significant variations in the ability of individual animals to digest various feedstuffs, challenging the previous assumption that digestibility was relatively similar across cows [20]. This greater understanding highlights the potential of targeted breeding programmes, where the selection of animals with low residual feed intake (high feed efficiency) could simultaneously lower CH4 output while improving feed efficiency [21]. To facilitate such CH4-mitigating programmes, a suite of technological advancements has emerged, enabling the precise monitoring of livestock feed intake and feeding behaviour. These real-time data empower stakeholders to make informed adjustments to feeding strategies, tailor diets to meet individual nutritional needs, reduce waste, and closely monitor animal feeding patterns. Such technologies have been widely reported in the literature, with many commercialised, including electronic rumen boluses, smart feeders with radio frequency identification (RFID)-embedded ear tags, acoustic monitoring, AI-embedded cameras, and behaviour-sensing neck collars. Notably, noseband pressure sensors have also been utilised to estimate the duration of eating and ruminating in cattle and to determine the number and frequency of chews and bites [22,23]. They typically work by using pressure sensors to measure the size and rate of bites by analysing the frequency and amplitude of ‘peaks and troughs’ in the data collected during eating [23]. Braun et al. (2013) assessed rumination behaviour using a noseband pressure sensor and found a significant correlation between the results obtained from the sensor and those from visual observations [24]. Similarly, Leiber et al. (2016) attempted to measure the feed intake of dairy cows fed a high-forage total mixed ration using noseband sensors, based on daily eating time and rumination [25]. However, this was unsuccessful due to significant differences in feeding behaviours among animals. The RumiWatch System (Itin+Hoch GmbH, Liestal, Switzerland), integrated into a cow halter, combines data from a pressure sensor with information from a triaxial accelerometer to identify various behavioural characteristics in dairy cows [26]. Various studies have utilised this system to study a range of behavioural characteristics in cows, including bolus counts, chews per bolus, number of rumination chews, prehension bites, and number of eating chews along with derived durations such as rumination time, eating time, and prehension time [26,27].
Acoustic monitoring techniques have also been used to a limited degree in the measuring of livestock feeding behaviour. Galli et al. (2011) successfully estimated dry matter intake during short feeding sessions in sheep with a relatively high accuracy (R2 = 0.92) using acoustic monitoring; they did so by calculating both the chewing energy per bite and the total energy expended in chewing [23,28]. Similarly, a Hi-Tag system (SCR Engineers Ltd., Netanya, Israel) has been successfully shown to provide accurate measurements of rumination time, the intervals between regurgitation of boluses, and the chewing rate in cattle [29,30]. The Hi-Tag logger, positioned on a neck collar, records and processes the distinctive sounds produced by regurgitation and rumination using a microphone. The software then defines the start of a rumination event when the system detects the sound associated with regurgitation [29]. Schirmann (2009) validated the system’s accuracy, reporting a high correlation between its results and those obtained from direct observation (r = 0.93, R2 = 0.87, n = 51) [30]. Overall, it is evident that such feeding behaviour-monitoring technologies have significant potential to optimise sustainable farming practices while empowering CH4-mitigating strategies and breeding programmes.
Another feeding behaviour-monitoring technique garnering increasing attention in both academic and industrial circles is electronic rumen boluses, due to their proficiency in accurately and continuously monitoring the internal rumen environment of ruminants, particularly cattle [31]. This established technology, offered by commercial providers such as Moonsyst (Cork, Ireland), extends beyond the monitoring of ruminant drinking behaviour to encompass a wide range of vital parameters, including animal health, heat detection and optimisation, disease detection, calving prediction and detection, and overall animal activity [32]. Administered orally using a bolus applicator, these devices settle in the reticulum due to gravity and remain there throughout the animal’s life. These devices consist of a cylindrical ceramic capsule containing an internal battery, a data transmission transmitter, and specialised sensors such as temperature, pH, and accelerometer sensors, tailored to the specific monitoring needs [29,33]. They operate by gathering real-time data and transmitting them wirelessly to a central processing unit. These data are then uploaded to cloud-based storage, enabling users to access and analyse the information conveniently via a smartphone or computer [34]. Due to its stable placement, the rumen bolus offers lifelong animal monitoring, with a battery lasting for months to years and the ability to wirelessly transmit data at adjustable intervals.

2.2. Rumination Time

Ruminating time, characterised by cattle regurgitating and chewing previously ingested food, plays an important role in aiding nutrient absorption and digestion. It also serves as an indicator of a cow’s health, as a decrease in rumination time is often observed in animals experiencing illness, pain, hunger, or maternal anxiety [35]. Typically, cattle ruminate for about 30 min to 1 h across 10–17 daily periods, producing 30–60 boluses per period, with each rumination cycle involving 30–60 chews and lasting around 40 s [35,36]. However, a variety of factors can alter these rumination times and patterns, such as changes in diet composition, feeding management practices, health issues, the onset of calving, and environmental conditions.
Rumination time can indirectly influence methane emissions in dairy cows, largely due to its role in stabilising the pH of rumen fluid. Stable ruminal pH is critical because it directly impacts the activity of methanogenic microorganisms within the rumen, which may affect methane synthesis [34,37]. Mikuła (2022) successfully demonstrated a correlation between longer rumination time and reduced methane emissions per unit of milk in high-yielding dairy cows [34]. This study included 365 high-yielding Polish Holstein–Friesian multiparous dairy cows, covering a lactation period ranging from 24 to 304 days. The data collected from the cows were segmented into three categories according to their daily rumination durations: those in the low-rumination group ruminated for up to 412 min per day; the medium-rumination group included cows ruminating between 412 and 527 min per day; and the high-rumination group comprised cows ruminating for more than 527 min per day. The results showed that cows in the high-rumination group emitted 2.9% less methane per unit of milk than those in the medium-rumination group, and 4.6% less compared to the low-rumination group.

2.3. Rumen Status

The rumen ecosystem within ruminants offers significant research opportunities, particularly regarding mitigating its considerable impact on the environment, improving animal health, and contributing to feeding a growing global population. Specifically, the process of fibre fermentation in the rumen serves as a crucial mechanism, enabling ruminants to transform low-grade, human-inedible materials into high-quality protein suitable for human consumption [38]. Given its crucial role, this section explores the literature examining the rumen’s role in real-time health and emission monitoring.

2.3.1. Reticulo-Ruminal pH

The real-time monitoring of the rumen pH is a promising approach for tackling animal health disorders, specifically in determining and preventing acute acidosis or sub-acute ruminal acidosis (SARA). This technology has attracted significant attention for its capacity to produce sensory pH data that highly correlate with readings from calibrated laboratory pH probes [29,39]. Moreover, the continuous or intermittent monitoring of rumen pH allows for the early detection of suboptimal rumen conditions, thus enabling the implementation of timely intervention strategies including adjustments to diet formulation, feeding management, and the monitoring of feeding behaviour [23,40]. Due to the rumen’s non-homogenous nature, significant fluctuations in ruminal pH may occur throughout the day, depending on the quantity and composition of the diet as well as changes in feeding behaviour [41]. As previously mentioned, the pH value has been shown to be a reliable indicator of the onset of SARA. The reported pH thresholds for SARA vary as they are influenced by several influencing factors such as the timing of sample collection, the frequency of measurements, and the location of sampling. In a recent study, a cumulative period exceeding 3 h per day with ruminal pH values below 5.6 was found to be sufficient for diagnosis [42]. Another study has proposed that a single occurrence of rumen pH dropping below a threshold of 5.5 is a fitting measure [42,43].
Recent advancements have led to the development and commercial availability of various rumen pH sensors, such as the reticulo-ruminal pH boluses [31,32]. These devices have revolutionised the data collection process by continuously transmitting pH data wirelessly to a central processing unit, thus greatly simplifying data collection and analysis [33]. For data interpretation, animal ruminal acidosis and feeding behaviours can be evaluated using various factors, including the average ruminal pH, the pattern of ruminal pH over time, the variation in the pattern of ruminal pH, and the duration of suboptimal ruminal pH [44]. It is essential to accurately interpret these data to account for the variations in pH observed at different locations within the rumen and reticular. A notable limitation of pH boluses is their susceptibility to significant drift over time, coupled with a relatively short lifespan and the impossibility of easily recovering the device [45]. Despite this, the potential to incorporate pH sensing into broader, wireless multi-parameter rumen monitoring systems presents a promising avenue for enhancing the comprehensiveness and accuracy of animal health assessments.

2.3.2. Reticulo-Ruminal Temperature

The real-time monitoring of body temperature changes in ruminants offers an effective method for the early detection of inflammatory conditions, oestrus, and diseases such as mastitis [31,46,47,48]. Core temperature monitoring has traditionally relied on the use of rectum and vaginal thermometers [49]. These methods are often considered low in functionality due to their labour-intensive nature and the time-consuming requirement of manually checking each animal individually [38]. Given these constraints, there is a growing trend of adopting automated monitoring technologies [49]. Among these, reticulo-ruminal temperature sensors have received significant attention, due particularly to the use of electronic boluses that facilitate the continuous monitoring of ruminal temperature variations throughout an animal’s lifespan [38]. This technology has been particularly effective in detecting the onset of oestrus and as a useful predictor of calving in cows [50,51,52].
In the context of calving, constant monitoring is especially beneficial, as such vigilance can significantly decrease the mortality rate of newborns by up to 50% and mitigate losses caused by dystocia [49]. Precision technologies, such as temperature sensors, can serve as reliable predictors of calving. Several studies have observed decreases of up to 1 °C in body temperature during the period preceding calving, predominantly attributed to the thermogenic effect of progesterone [53,54,55]. Research has consistently shown variations in reticulo-rumen temperature (Trr) in cows before calving. Kim et al. (2021) report that in Hanwoo (Bos taurus coreanae) cows, Trr can decrease by 0.5 °C from 24 h to 3 h before calving, in comparison to 48 h prior to parturition [56]. Cooper-Prado et al. (2011) [55] observed similar trends in Angus cows, where they documented a reduction of up to 0.33 °C in Trr two days before calving using temperature-sensing boluses placed in the rumen. Costa Jr. et al. (2016) [49] also employed this technique in Holstein cows and recorded Trr decreases of 0.32 °C in primiparous and 0.36 °C in multiparous cows 24 h before calving. Furthermore, Kovács et al. (2017) investigated crossbred Holstein–Japanese Black cows and noted that the extent of Trr reduction varied with the calving condition, ranging from 0.23 °C in distocic cows to 0.48 °C in eutocic cows [57]. The variance in these results is likely due to differences in the methods applied, including factors such as the biological characteristics of the animal, the site of body temperature measurement, and environmental variables [58].
As previously mentioned, monitoring changes in ruminal temperature and the cow’s overall activity can facilitate the early detection of oestrus. The accurate identification of oestrus is key as failing to inseminate at the appropriate time can result in failure to conceive or pregnancy loss, thus impacting revenue [59]. Researchers have established a positive correlation between rumen temperature and the onset of oestrus [38]. This relationship is primarily attributed to hormonal fluctuations during the oestrus cycle, which can lead to fluctuations in the cow’s body temperature. Notably, one study highlighted that body temperature increases by approximately 0.4 °C during oestrus in cows [60]. Moreover, the overall activity level of a cow can be a reliable indicator of the onset of oestrus, characterised by a notable rise in movement and restlessness [38,59]. Such behavioural changes are predominantly influenced by a surge in oestrogen levels during oestrus, which triggers the cows’ natural mating instincts and results in increased overall activity. Recognising this, several manufacturers have brought to market ruminal boluses that incorporate accelerometers and temperature sensors for oestrus detection [42]. These devices enable more timely breeding interventions, thus facilitating better management of the reproductive cycle and enhancing overall production efficiency.
While reticulo-ruminal temperature monitoring can offer valuable insights into animal health and behaviour, it is important to acknowledge the challenge of determining accurate readings. Factors such as ambient temperature, water temperature and consumption, rumen fermentation, and fibre-related diseases can significantly influence rumen temperature measurements [29,61]. For instance, Bewley et al. (2008) observed that drinking water could lower rumen temperature by up to 8.5 °C, with a recovery to core body temperature levels taking up to two hours [38,62]. Despite these challenges, such interference can also present opportunities, where reticulo-ruminal boluses can be used to monitor drinking events and investigate factors influencing cattle drinking behaviour [29]. These temperature fluctuations can provide insights into the daily distribution of water drinking events, and while they may not precisely measure the quantity of water consumed, they can indicate changes in drinking patterns [38]. Such changes can be vital for identifying potential health issues or stress, enabling farm managers to take timely action to maintain herd health and wellbeing.

2.3.3. Reticulo-Rumen Motility

Monitoring the frequency and amplitude of ruminal contractions, known as motility, plays a crucial role in diagnosing various metabolic diseases in cattle [30,38]. Conditions such as ruminal acidosis and hypocalcemia, along with other ailments that induce stress or impact productivity, directly influence these contractions [63,64]. Consequently, measuring changes in the rate and strength of these contractions can be a key indicator of animal health, welfare, and overall production performance [38].
Bovines have a distinctive digestive system comprising four chambers specifically adapted for efficient cellulose digestion. This process, known as alloenzymatic digestion, utilises microbial enzymes for the effective digestion of cellulose-rich complex carbohydrates, rather than relying on enzymes produced by the host animal. The first chamber provides an anaerobic environment essential for microbial fermentation of ingesta, a key step in feed breakdown. The reticulum, as the initial compartment, separates particulate matter from liquid and acts as a sump to trap heavy foreign bodies, protecting the digestive system [38]. Following this is the rumen, the largest chamber, which is primarily responsible for the fermentation and digestion of organic matter [38]. These chambers, jointly known as the reticulo-rumen, undergo periodic contractions, facilitating fluid and material movement and enabling regurgitation for rumination, a vital part of digestion. These contractions occur in two distinct phases and are central to the fermentation process and the efficiency of nutrient breakdown and assimilation (see Figure 2) [65]. The primary contraction cycle, known as the A-wave, begins with a biphasic contraction of the reticulum, which may become triphasic during rumination [66,67]. This cycle starts in the reticulum and moves through the rumen in a cranio-caudal direction [66,67]. These contractions are crucial for several digestive functions, including the mixing of digesta, its passage through the reticulo-omasal orifice, and regurgitation [66]. The secondary contraction cycle, known as the B-wave, is crucial in facilitating eructation, a process vital for managing the gas produced during fermentation [68]. Starting in the rumen’s caudal sac after the A-wave cycle, it progresses forward independently of reticular contractions [66]. In healthy cattle, the vagus nerve regulates ruminal contraction at a rate of three to four times per two-minute interval [65,69]. Several studies have indicated possible correlations between bovine contraction cycles and various aspects of animal behaviour, including feeding, stress response, and periods of rest [30,70].
Historically, the assessment of rumen motility has relied on physiological evaluations using strain gauge force transducers or ultrasonography techniques [71,72]. However, these methods are limited by significant drawbacks, including being labour-intensive, costly, and impractical for regular use on most farms [30]. For instance, the force transducer method requires a surgical procedure in which the device is sutured onto the serosa of the dorsal sac of the rumen [38]. The ultrasonography technique is constrained for long-term use as it requires the device to be consistently positioned against the animal’s body wall [38]. Recent developments in wireless forestomach motility sensors have been recognised as a reliable, practical, and long-lasting solution for monitoring rumen health [73,74]. These sensors can effectively detect rumen atony and, through advanced data processing, can continuously track ruminal motility patterns such as rumination. Moreover, the latest advancements in technology have facilitated the enhancement of bolus wireless sensors, which can streamline rumen motility monitoring, allowing for long-term observation periods. Several research groups have utilised boluses equipped with accelerometers to continuously monitor reticulo-rumen motility [42,50,75]. Boluses with integrated accelerometers are capable of detecting the motion of the reticulo-rumen, thus capturing essential data on the contractions and relaxations that occur during the digestive process. A study by Arai (2019) demonstrated a significant positive correlation between the ruminal contractions measured by force transducers and the acceleration detected by the bolus sensor (p < 0.01) [76]. Furthermore, these accelerometers can identify movement patterns associated with rumination, enabling the measurement of both its frequency and duration. On the other hand, pressure sensors are effective in measuring the internal pressure changes within the reticulo-rumen, which are closely linked to muscular contractions that facilitate digestion. Notably, significant variations in pressure patterns can serve as an indicator of digestive issues, such as bloat in cattle [33]. Considerable opportunity exists in the integration of such motility data with other complementary sets of information, such as pH, temperature, volatile fatty acids, or other data, which could together provide a more comprehensive understanding of reticulo-rumen motility and yield practical insights for on-farm application.

3. Animal-Based Techniques for Measuring Enteric CH4

Within the livestock sector, the development and deployment of reliable methods and devices to quantify enteric CH4 emissions are becoming increasingly critical for improving animal productivity and environmental impact. Such monitoring is often facilitated by data generated via wireless wearable sensors, which offer continuous, automated analysis, providing stakeholders with precise information to inform and enhance farm management decisions. With a rapidly growing market of CH4-monitoring techniques, each with its own advantages and limitations, stakeholders now have a wider range of options to choose from, as illustrated in Figure 3. To assist with this, this section provides a comprehensive review and critical discussion of the most prevalent techniques reported in the literature for the real-time measurement of enteric CH4 emissions.

3.1. Respiration Chambers

Respiration chambers are among the most widely utilised techniques in the measurement of CH4 emissions released from ruminants, often regarded as the “gold standard” due to their integral use in the development of predictive models and equations that inform national inventories [77,78,79]. While the design of chambers may differ, the fundamental principle remains the same: a sealed and environmentally controlled chamber is used to determine an individual test animal’s heat balance and gaseous exchange [7,77]. There are two main categories of respiration chambers: open-circuit chambers and closed-circuit chambers. The more commonly used open-circuit chambers feature an air inlet and exhaust, creating a one-way stream of air through which the animal breathes [80]. The sampling of incoming and outgoing air streams is conducted using either gas analysers, infrared photoacoustic monitors, or gas chromatography systems [81,82,83]. In contrast, closed-circuit chambers, now seldom used, analyse the composition of air that accumulates over time. By employing these methodologies, it is possible to estimate the whole-body metabolic rate of the animal through the measurement of CH4, gaseous exchanges (including oxygen (O2) consumption and carbon dioxide (CO2) production), and evaluation of additional trace gases [77].
A significant constraint of using respiration chambers is that the approach may alter the natural behaviours of free-ranging animals due to its artificial environment, thus resulting in an inaccurate estimation of actual emissions compared to farm conditions [84]. To mitigate potential behavioural changes, research trials typically employ acclimatisation periods prior to measurement, along with the use of transparent chambers to enable the animal to maintain visual contact [85,86]. Moreover, this method can require significant financial and labour resources and is constrained by its capacity to monitor only one animal at any one time, making it impractical for large-scale assessments [14,21,87,88]. Currently, respiration chambers are primarily utilised by governmental agricultural agencies within a research setting rather than by individual farmers; this is due to the substantial capital investment associated with their use. Efforts to address this have focused on incorporating more accessible measurement techniques as the primary testing mechanism, with respiration chambers used to validate the results obtained [89]. Despite these limitations, respiration chambers continue to be considered the most accurate and precise method available for gathering air composition data over an extended period of time.

3.2. Sulphur Hexafluoride (SF6) Tracer Method

Tracer techniques have attracted considerable attention for their use in determining CH4 emissions in ruminants, particularly for free-range cattle, as they allow monitoring without constraining the animals’ behaviour [77]. This method involves the insertion of a permeation tube or bolus in the reticulo-rumen, where a tracer (such as sulphur hexafluoride (SF6) or deuterated CH4 (13CH3D)) is released at a known rate [90,91]. After the tracer is administered, the cow can resume its normal grazing activities. During this period, the animal’s breath is continuously sampled using a tube placed near the animal’s nostril, typically attached to a halter, and directed into an evacuated cylinder for collection [10,13,80]. When SF6 is used as the tracer gas, the calculation of enteric CH4 emission rates is conducted by multiplying the established SF6 release rate with the ratio of CH4 to SF6 concentrations found in the collected samples [92,93]. The concentration of SF6 and CH4 in the collected samples is quantified using gas chromatography [94]. SF6 has been shown to be an ideal tracer gas as it is easily detectable, traceable at low concentrations, and synthetic in origin [77]. However, the SF6 tracer gas utilised is a highly potent greenhouse gas with a global warming potential of 22,800 [92,95]. While this technology offers key benefits, such as being non-invasive and enabling simultaneous monitoring of multiple animals, its accuracy can be affected by several factors. These include equipment malfunctions, background concentrations of emission sources in ambient air, the high-level expertise required, and the variability in the tracer gas’s release rate [13,96]. Such limitations in accuracy and applicability can be mitigated by integrating the method with other established enteric emission measurement technologies. Furthermore, integrating the SF6 tracer method with additional PLF technologies, such as electronic rumen boluses, behaviour-monitoring neck collars, RFID-embedded ear tags, and smart feeders, presents opportunities for enhancing the accuracy and comprehensiveness of the generated results. This integration opens up significant research opportunities in applying artificial intelligence (AI) to effectively mange and identify patterns from such complex datasets resulting from diverse sensors, ultimately providing more unified and accurate understanding of an animal’s enteric emissions over its lifespan [97].

3.3. Spot Sampling

Spot sampling, also known as the “sniffer” technique, involves the direct measurement of the CH4 concentration in an individual animal’s breath over a short duration [13,98]. The CH4 concentrations in the breath samples are measured and used to calculate the animal’s CH4 emission rate. Typically, these sampling visits last for 3 to 10 min, with the CH4 concentrations being expressed as either the overall mean or the mean of eructation peaks [10]. Sufficient data collection allows for the derivation of a repeatable estimate of the CH4 emission rate and the extrapolation of short-term emission rates to whole-day CH4 emissions [92,94]. This approach is generally non-intrusive, automated, and non-invasive, thus enabling the efficient measurement of emissions from a large number of animals [92]. However, studies using the sniffer method have reported it to be significantly less precise than respiration chambers, owing to considerable variation in CH4 concentrations within and between animals’ breath [13,99,100]. Additionally, other potential sources of error, such as cow head position, number of measurements, and proximity to the sampling point, need to be considered for accurate emission estimates.
A device that has attracted significant attention in the literature is the patented GreenFeed® system (C-Lock Inc., Rapid City, USA), which operates similarly to the sniffer technique, combining an automatic feeding system with advanced gas-flux quantification capabilities [7,92,99]. The system attracts animals using a small amount of pelleted concentrate as “bait” and measures emissions (including CH4, CO2, H2, O2, and H2S) over periods of 3–6 min repeatedly throughout the day [7]. A key advantage of GreenFeed lies in its ability to estimate an animal’s daily average methane emission by aggregating multiple short-term measurements taken during each visit to the unit [79]. However, the method is limited by the need for multiple short-term measurements and the reliance on an “bait” to draw the animal to the device, which alters the measured results [23,92,98].
Interestingly, several start-up companies are gaining traction in the field, aiming to commercialise more affordable spot-sampling devices. For instance, Agri Data Analytics (Offaly, Ireland)has developed a portable, solar-powered “sniffer” device that attaches to feed troughs, allowing for automated, continuous monitoring of CH4 emissions [101]. The device utilises laser spectroscopy to measure CH4 concentrations in real time and transmit the data wirelessly to a cloud-based platform for analysis. Meanwhile, Zelp (London, UK), has taken an alternative approach by creating a wearable device for cattle that captures CH4 emissions directly from the animal’s nostrils [102]. This halter-like device utilises a catalyst to oxidize methane into carbon dioxide and water, thereby mitigating emissions while simultaneously quantifying them. Both technologies, while still in their early stages of development and commercialisation, represent promising advancements in the ongoing effort to monitor and mitigate methane emissions from livestock.

3.4. Laser CH4 Detectors

Lasers, using infrared absorption spectroscopy, have long been used for CH4 gas detection across various industries, including environmental, air quality monitoring, healthcare, security, and agriculture [92,103]. In the context of agricultural research, these handheld devices have been used to measure CH4 concentrations in the exhaled air of individual animals [11,104,105]. These CH4 concentrations are manually measured using a portable device positioned 1–3 m from the cow’s nostrils for 2–4 min, ensuring minimal disturbance to the animal’s behaviour [13,79,105,106]. The technique works by emitting infrared light, which is selectively absorbed by the CH4 molecules in the cow’s breath. It then measures the intensity of light absorption, allowing it to accurately calculate the concentration of methane present. From the data acquired, it is possible to segregate the CH4 concentrations based on the physiological activity being performed by the animal, such as ruminating, sleeping, and feeding [13]. Typically, higher CH4 concentrations are observed during eructation, in contrast to lower concentrations noted during respiration. While this method relies on spot sampling of an animal’s breath, these initial measurements can then be extrapolated to represent daily CH4 production [7,13]. However, such scaling typically requires an impressive number of assumptions [3]. This method offers some advantages over traditional enteric CH4 measurement techniques by providing a rapid response, allowing for real-time measurements and offering a non-invasive process without requiring physical contact [11,92]. The results of this technique can be affected by external factors, such as temperature, wind velocity, humidity, atmospheric pressure, and the proximity of other animals [92,104,107,108]. While some studies, such as Chagunda and Yan (2011), have found strong agreement between measurements from laser CH4 detectors and those in respiration chambers (r = 0.8), others like Ricci et al. (2014) have reported inconsistencies, highlighting the method’s variability under different conditions [11,13,105,109]. Chagunda et al. (2012) visually illustrates this variability between individual CH4 concentration measurements in Figure 4 [11]. Although the absolute values between the laser CH4 detector and the respiration chamber differ, the trends over time showed good agreement.

3.5. Open-Path Laser

Open-path lasers are a novel method developed for quantifying CH4 concentrations from herds of animals using a system of lasers and detectors. These systems are already utilised for both research and commercial applications in whole-farm ruminant enteric methane measurements across various countries, including the United States [110,111,112], Australia [113,114], New Zealand [115], China [116], and Canada [117,118]. Central to this system is the tuneable infrared diode laser, part of a programmable unit that can direct the laser beam across various paths [18]. This technique operates by sending tuneable infrared diode lasers to a retro reflector along a direct path, which then reflects the beam back to a detector [7]. The intensity of the reflected light received by the detector reveals the CH4 concentration along the path [7,92]. Depending on the configuration, the herd can either act as a collective surface source or, with GPS-collared individual animals, as separate point sources [92]. Most recently, the technique has been enhanced through the integration of various analysers and atmospheric parameters into drones and aircraft, leading to consistent and encouraging results [119]. Moreover, this technology has been proven capable of detecting ammonia (NH3) and CH4 from distances up to 7 km and 25 km, respectively, when originating from a high-strength source [13,119]. While the technology remains promising, it still has limitations, such as sensitivity to environmental conditions, complex setup and operation, and high capital costs [7,92,120].

4. Emerging Technologies and Techniques

4.1. Portable Accumulation Chamber

An emerging technology for measuring emissions from individual animals is portable accumulation chambers (PACs). These systems generally consist of an airtight polycarbonate chamber without airflow, which operates by trapping all exhaled gases during a 1 to 2 h sampling period [92]. During this time, the O2 content inside the chamber is gradually depleted, and a portable air sampler is used to retrieve a single measurement of CH4 taken at the end of the sampling period [92]. These systems have garnered significant commercial and academic interest due to their automated operation, portability, ability to screen a large throughput of animals, and relative affordability, making them a useful technology in identifying high-emitting animals for targeted mitigation strategies [7]. Specifically, PACs have primarily been utilised in research settings by governmental agricultural agencies across various countries to identify ruminants with high and low CH4 emissions [121,122]. In Ireland, the agricultural research agency (Teagasc) has employed PACs as the primary ruminant CH4 measurement technique, with results validated by the SF6 tracer method and respiration chambers [89]. By combining various measurement techniques, researchers can leverage the key advantages of PACs, such as their portability and ability to assess multiple animals efficiently, while minimising the technologies shortcomings including limited accuracy, limited chamber size, timing of measurements relative to animal feeding, and the influence of external environmental factors [7,92,123].

4.2. CO2 Tracer Method

Most recently, CO2 tracers have become an emerging technique to quantify CH4 emissions from livestock [13,80]. This approach differs from traditional methods such as using externally added SF6 instead of relying on the naturally emitted CO2 from cattle [124]. Central to this approach is understanding the relationship between CO2 production and several other factors such as heat produced by the animals, the energy content of their feed, and the ration consumption [93]. By continuously monitoring and sampling the exhaled air for its CO2 and CH4 content, usually using Fourier transform infrared detection, it is then possible to determine the concentration of both gases [78]. The estimation of total enteric CH4 production is then derived from the measured ratio of CO2 to CH4 in the exhaled air [125,126]. In contrast to the traditional respiration chambers method, the CO2 tracer technique exhibits a comparatively higher level of variability, with the coefficient of determination between the two methods being 0.4 [80,126,127]. Consequently, CO2 tracers are not considered suitable for precisely quantifying CH4 emission changes in cattle, limiting their application to scenarios where an approximation is appropriate [92]. Despite these challenges, the method’s ability to be easily applied to many animals makes it possible to reduce the standard error in large-scale experiments [10,78,128]. Moreover, it utilises a naturally occurring tracer (CO2), thereby simplifying the data collection process and reducing the stress on the animals. Looking forward, there is significant opportunity in integrating AI algorithms with CO2 tracer methods

4.3. Optical Gas Imaging (OGI)

Optical gas imaging (OGI) cameras offer a promising, non-invasive, real-time approach to quantifying enteric CH4 emissions from livestock. While traditionally used in the oil and gas industry for detecting leaks, air pollutants and fugitive emissions [129], their capabilities translate well to the agricultural context. OGI uses specialised thermal infrared cameras to visualise gases, including CH4 and various other organic compounds, based on their unique spectral absorption properties [130,131]. Highlighting this potential, Huang (2023) explored the OGI’s ability to quantify CH4 emissions, employing a physical respiratory simulator to replicate cattle breaths under controlled laboratory conditions [129]. The study established a strong positive correlation between detected CH4 intensity and the actual CH4 concentration within the breath (1000–4000 ppm), demonstrating the potential of OGI for providing quantitative insights into enteric emissions. However, as this technology is still in its early stages of development, considerable challenges still remain, including establishing its suitability with live animals, reducing costs for wider adoption, and validating its accuracy in real-word conditions. While the technology is still emerging, significant opportunities exist for enhancing its capabilities, including integrating it with established techniques such as SF6 tracers and expanding its already established integration with drone technology to measure herd emissions at a larger scale [132,133].

5. Discussion and Future Outlook

CH4 emissions from enteric fermentation in ruminant livestock are a major contributor to the agricultural sector’s global environmental footprint [134]. In light of such environmental concerns, substantial efforts have been made in the development of reliable methods and devices to quantify enteric CH4 emissions, which are essential in the creation of national inventories, genetic selection, and the assessment of mitigation strategies [135].
As illustrated in Table 1, a diverse range of techniques and methodologies are now available, with new options continuously emerging. It is evident that each approach encompasses a range of application scopes, advantages, and limitations; thus, no single technique can be deemed universally superior [13]. While some methods are more suited to small-scale and others to large-scale applications, this distinction does not guarantee their universal applicability. Consequently, the technique selected should be chosen based on the intended purpose and the required precision, as its incorrect use may result in the overestimation or underestimation of CH4 emissions [13,80]. Among these current methods, many demonstrate high accuracy compared to respiration chambers, the traditional gold standard. Notably, hand-laser CH4 detectors and open-path lasers have emerged as promising tools when effectively accounting for atmospheric variations such as air humidity, wind speed, and atmospheric pressure. Despite these advancements, it is important to acknowledge that all measurement techniques inherently possess uncertainties due to random factors such as fluctuations in animal diets, management practices, and environmental conditions [97]. Thus, the development of robust and accurate estimation methods remains crucial for effectively addressing the environmental impact of livestock emissions.
The multifaceted nature of ruminant enteric CH4 production was highlighted in Section 2, identifying animal physiology, behaviour, feed intake, and management as key contributors. Although the enteric CH4-monitoring techniques presented in Section 3 and Section 4 can offer valuable insights, their accuracy and applicability can often be constrained by sensor types, algorithm selection, and short-term monitoring periods. To address these limitations, the authors propose sensor fusion as an effective approach to providing a complete understanding of ruminant’s health and environmental footprint over their entire lifespan. This approach would involve the merging of data from a diverse range of sensors and sources, creating a unified and more accurate depiction of an animal’s enteric CH4 emissions, productivity, and overall health. Initial progress can be achieved by integrating CH4-monitoring systems with market-ready PLF technologies, such as electronic rumen boluses, behaviour-monitoring neck collars, RFID-embedded ear tags, and smart feeders. However, the successful implementation of such enteric emission-monitoring and mitigation strategies necessitates a collaborative approach among diverse stakeholders, including farmers, researchers, policy makers, and technology providers. This collaborative effort is essential to ensure that collected data are effectively translated into tailored mitigation measures that are both practical and sustainable for implementation at the farm level. Over time, the authors anticipate that the continued evolution of Internet of Things (IoT) devices combined with the integration of machine learning will greatly enhance and accelerate the adoption of such data fusion techniques.

6. Conclusions

Given the livestock sector’s key role in global GHG production, this review underscores the importance of real-time quantification of enteric CH4 emissions from ruminant livestock. The accurate and actionable insights gained from such monitoring are essential for the rapid development and implementation of effective GHG mitigation strategies, especially considering the inherent complexities of livestock farming. Based on the literature, this study first examines the biological basis of current and potential biomarkers and proxies relevant to ruminant emissions. Next, it critically evaluates a diverse range of existing and emerging methods for monitoring ruminant enteric CH4 emissions. While there are many techniques available, it is clear that they all have limitations, with their appropriateness heavily dependent on the intended purpose and the level of precision required. This analysis compares their strengths and limitations, revealing that significant progress has been made towards achieving an accurate, cost-effective, and rapid mechanism for enteric CH4 monitoring. Looking forward, it is hoped that the insights generated will assist in accelerating the widespread adoption of real-time enteric CH4 monitoring, enabling the development of data-driven CH4 mitigation strategies and selective breeding programmes.

Author Contributions

Conceptualisation, S.O. and F.N.; validation, S.O., F.N., D.S. and J.W.; writing—original draft preparation, S.O.; writing—review and editing, S.O., F.N., D.S. and J.W.; supervision, F.N., D.S. and J.W.; project administration, F.N. and D.S.; funding acquisition, F.N. and J.W. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Enterprise Ireland and Agri IoT Limited under the Innovations Partnership Program (IP/2023/1039E).

Conflicts of Interest

Author Desmond Savage was employed by the company Moonsyst. The remaining authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

References

  1. European Environment Agency. Progress and Prospects for Decarbonisation in the Agriculture Sector and Beyond; European Environment Agency: Brussels, Brussels, 2022.
  2. Statista Agriculture Emissions Worldwide—Statistics & Facts. Available online: https://www.statista.com/topics/10348/agriculture-emissions-worldwide/#topicOverview (accessed on 24 June 2024).
  3. Environmental Protection Agency. Ireland’s National Inventory Report 2021; Environmental Protection Agency: Wexford, Ireland, 2021.
  4. O’Connor, S. Meeting Ireland’s Sustainability Challenges and Obligations: The Potential and Viability of Small-Scale Anaerobic Digestion; Atlantic Technological University Sligo: Sligo, Ireland, 2022. [Google Scholar]
  5. O’Connor, S.; Ehimen, E.; Pillai, S.C.; Black, A.; Bartlett, J. Biogas Production from Small-Scale Anaerobic Digestion Plants on European Farms. Renew. Sustain. Energy Rev. 2021, 139, 110580. [Google Scholar] [CrossRef]
  6. Helwatkar, A.; Riordan, D.; Walsh, J. Sensor Technology For Animal Health Monitoring. In Proceedings of the International Journal On Smart Sensing and Intelligent Systems, Liverpool, UK, 2–4 September 2014. [Google Scholar]
  7. Goopy, J.P.; Chang, C.; Tomkins, N. A Comparison of Methodologies for Measuring Methane Emissions from Ruminants. In Methods for Measuring Greenhouse Gas Balances and Evaluating Mitigation Options in Smallholder Agriculture; Springer: Berlin/Heidelberg, Germany, 2016; pp. 97–117. [Google Scholar] [CrossRef]
  8. Raynor, E.J.; Schilling-Hazlett, A.; Place, S.E.; Martinez, J.V.; Thompson, L.R.; Johnston, M.K.; Jorns, T.R.; Beck, M.R.; Kuehn, L.A.; Derner, J.D.; et al. Snapshot of Enteric Methane Emissions from Stocker Cattle Grazing Extensive Semiarid Rangelands. Rangel. Ecol. Manag. 2024, 93, 77–80. [Google Scholar] [CrossRef]
  9. Beauchemin, K.A.; Kreuzer, M.; O’Mara, F.; McAllister, T.A. Nutritional Management for Enteric Methane Abatement: A Review. Aust. J. Exp. Agric. 2008, 48, 21–27. [Google Scholar] [CrossRef]
  10. Bačėninaitė, D.; Džermeikaitė, K.; Antanaitis, R. Global Warming and Dairy Cattle: How to Control and Reduce Methane Emission. Animals 2022, 12, 2687. [Google Scholar] [CrossRef] [PubMed]
  11. Chagunda, M.G. Opportunities and Challenges in the Use of the Laser Methane Detector to Monitor Enteric Methane Emissions from Ruminants. Animal 2013, 7, 394–400. [Google Scholar] [CrossRef] [PubMed]
  12. Muñoz, C.; Yan, T.; Wills, D.A.; Murray, S.; Gordon, A.W. Comparison of the Sulfur Hexafluoride Tracer and Respiration Chamber Techniques for Estimating Methane Emissions and Correction for Rectum Methane Output from Dairy Cows. J. Dairy Sci. 2012, 95, 3139–3148. [Google Scholar] [CrossRef] [PubMed]
  13. Tedeschi, L.O.; Abdalla, A.L.; Álvarez, C.; Anuga, S.W.; Arango, J.; Beauchemin, K.A.; Becquet, P.; Berndt, A.; Burns, R.; De Camillis, C.; et al. Quantification of Methane Emitted by Ruminants: A Review of Methods. J. Anim. Sci. 2022, 100, skac197. [Google Scholar] [CrossRef] [PubMed]
  14. Moraes, L.E.; Strathe, A.B.; Fadel, J.G.; Casper, D.P.; Kebreab, E. Prediction of Enteric Methane Emissions from Cattle. Glob. Chang. Biol. 2007, 20, 2140–2148. [Google Scholar] [CrossRef] [PubMed]
  15. Džermeikaitė, K.; Krištolaitytė, J.; Antanaitis, R. Relationship between Dairy Cow Health and Intensity of Greenhouse Gas Emissions. Animals 2024, 14, 829. [Google Scholar] [CrossRef]
  16. Bobade, M.; Khune, V.; Mishra, S.; Dubey, A.; Yadav, A.; Soni, A.; Bhagat, S.; Das, S.; Krishnan, K. New Age Dairy Farming: Precision Dairy Farming (PDF): A Review. Int. J. Chem. Stud. 2020, 8, 1041–1046. [Google Scholar] [CrossRef]
  17. Negussie, E.; de Haas, Y.; Dehareng, F.; Dewhurst, R.J.; Dijkstra, J.; Gengler, N.; Morgavi, D.P.; Soyeurt, H.; van Gastelen, S.; Yan, T.; et al. Large-Scale Indirect Measurements for Enteric Methane Emissions in Dairy Cattle: A Review of Proxies and Their Potential for Use in Management and Breeding Decisions. J. Dairy Sci. 2017, 100, 2433–2453. [Google Scholar] [CrossRef] [PubMed]
  18. Tomkins, N.W.; McGinn, S.M.; Turner, D.A.; Charmley, E. Comparison of Open-Circuit Respiration Chambers with a Micrometeorological Method for Determining Methane Emissions from Beef Cattle Grazing a Tropical Pasture. Anim. Feed Sci. Technol. 2011, 166–167, 240–247. [Google Scholar] [CrossRef]
  19. Ellis, J.L.; Kebreab, E.; Odongo, N.E.; McBride, B.W.; Okine, E.K.; France, J. Prediction of Methane Production from Dairy and Beef Cattle. J. Dairy Sci. 2007, 90, 3456–3466. [Google Scholar] [CrossRef] [PubMed]
  20. Lovendahll, P.; Difford, G.F.; Li, B.; Chagunda, M.G.G.; Huhtanen, P.; Lidauer, M.H.; Lassen, J.; Lund, P. Review: Selecting for Improved Feed Efficiency and Reduced Methane Emissions in Dairy Cattle. Animal 2018, 12, s336–s349. [Google Scholar] [CrossRef] [PubMed]
  21. Negussie, E.; Lehtinen, J.; Mäntysaari, P.; Bayat, A.R.; Liinamo, A.E.; Mäntysaari, E.A.; Lidauer, M.H. Non-Invasive Individual Methane Measurement in Dairy Cows. Animal 2017, 11, 890–899. [Google Scholar] [CrossRef] [PubMed]
  22. Zehner, N.; Umstätter, C.; Niederhauser, J.J.; Schick, M. System Specification and Validation of a Noseband Pressure Sensor for Measurement of Ruminating and Eating Behavior in Stable-Fed Cows. Comput. Electron. Agric. 2017, 136, 31–41. [Google Scholar] [CrossRef]
  23. Gonzalez, L.A.; Kyriazakis, I.; Tedeschi, L.O. Review: Precision Nutrition of Ruminants: Approaches, Challenges and Potential Gains. Animal 2018, 12, S246–S261. [Google Scholar] [CrossRef] [PubMed]
  24. Braun, U.; Trösch, L.; Nydegger, F.; Hässig, M. Evaluation of Eating and Rumination Behaviour in Cows Using a Noseband Pressure Sensor. BMC Vet. Res. 2013, 9, 164. [Google Scholar] [CrossRef] [PubMed]
  25. Leiber, F.; Holinger, M.; Zehner, N.; Dorn, K.; Probst, J.K.; Spengler Neff, A. Intake Estimation in Dairy Cows Fed Roughage-Based Diets: An Approach Based on Chewing Behaviour Measurements. Appl. Anim. Behav. Sci. 2016, 185, 9–14. [Google Scholar] [CrossRef]
  26. Rombach, M.; Münger, A.; Niederhauser, J.; Südekum, K.H.; Schori, F. Evaluation and Validation of an Automatic Jaw Movement Recorder (RumiWatch) for Ingestive and Rumination Behaviors of Dairy Cows during Grazing and Supplementation. J. Dairy Sci. 2018, 101, 2463–2475. [Google Scholar] [CrossRef]
  27. Zehner, N.; Niederhauser, J.J.; Nydegger, F.; Grothmann, A.; Keller, M.; Hoch, M.; Haeussermann, A.; Schick, M. Validation of a New Health Monitoring System (RumiWatch) for Combined Automatic Measurement of Rumination, Feed Intake, Water Intake and Locomotion in Dairy Cows. In Proceedings of the International Conference of Agricultural Engineering CIGR-Ageng 2012, Valencia, Spain, 8–12 July 2012. [Google Scholar]
  28. Galli, J.R.; Cangiano, C.A.; Milone, D.H.; Laca, E.A. Acoustic Monitoring of Short-Term Ingestive Behavior and Intake in Grazing Sheep. Livest. Sci. 2011, 140, 32–41. [Google Scholar] [CrossRef]
  29. Hajnal, É.; Kovács, L.; Vakulya, G. Dairy Cattle Rumen Bolus Developments with Special Regard to the Applicable Artificial Intelligence (AI) Methods. Sensors 2022, 22, 6812. [Google Scholar] [CrossRef] [PubMed]
  30. Arai, S.; Okada, H.; Sawada, H.; Takahashi, Y.; Kimura, K.; Itoh, T. Evaluation of Ruminal Motility in Cattle by a Bolus-Type Wireless Sensor. J. Vet. Med. Sci. 2019, 81, 1835–1841. [Google Scholar] [CrossRef]
  31. Gesler, P. Chapter 10: Rumen Bolus Technology at Commercial Farms. In Practical Precision Livestock Farming: Hands-on Experiences with PLF Technologies in Commercial and R&D Settings; Waheningen Academic Publishers: Wageningen, The Netherlands, 2022; pp. 165–173. [Google Scholar] [CrossRef]
  32. Moonsyst International Ltd. Available online: https://moonsyst.com/home (accessed on 17 May 2024).
  33. Mottram, T.; Lowe, J.; McGowan, M.; Phillips, N. Technical Note: A Wireless Telemetric Method of Monitoring Clinical Acidosis in Dairy Cows. Comput. Electron. Agric. 2008, 64, 45–48. [Google Scholar] [CrossRef]
  34. Mikuła, R.; Pszczola, M.; Rzewuska, K.; Mucha, S.; Nowak, W.; Strabel, T. The Effect of Rumination Time on Milk Performance and Methane Emission of Dairy Cows Fed Partial Mixed Ration Based on Maize Silage. Animals 2022, 12, 50. [Google Scholar] [CrossRef]
  35. Paudyal, S. Using Rumination Time to Manage Health and Reproduction in Dairy Cattle: A Review. Vet. Q. 2021, 41, 292–300. [Google Scholar] [CrossRef]
  36. Lindgren, E. Validation of Rumination Measurement Equipment and the Role of Rumination in Dairy Cow Time Budgets; Swedish University of Agricultural: Uppsala, Sweden, 2009. [Google Scholar]
  37. Huang, H.; Szumacher-Strabel, M.; Patra, A.K.; Ślusarczyk, S.; Lechniak, D.; Vazirigohar, M.; Varadyova, Z.; Kozłowska, M.; Cieślak, A. Chemical and Phytochemical Composition, in Vitro Ruminal Fermentation, Methane Production, and Nutrient Degradability of Fresh and Ensiled Paulownia Hybrid Leaves. Anim. Feed Sci. Technol. 2021, 279, 115038. [Google Scholar] [CrossRef]
  38. Han, C.S.; Kaur, U.; Bai, H.; Roqueto dos Reis, B.; White, R.; Nawrocki, R.A.; Voyles, R.M.; Kang, M.G.; Priya, S. Sensor Technologies for Real-Time Monitoring of the Rumen Environment. J. Dairy Sci. 2022, 105, 6379–6404. [Google Scholar] [CrossRef]
  39. Penner, G.B.; Aschenbach, J.R.; Gäbel, G.; Oba, M. Technical Note: Evaluation of a Continuous Ruminal PH Measurement System for Use in Noncannulated Small Ruminants. J. Anim. Sci. 2009, 87, 2363–2366. [Google Scholar] [CrossRef]
  40. González, L.A.; Manteca, X.; Calsamiglia, S.; Schwartzkopf-Genswein, K.S.; Ferret, A. Ruminal Acidosis in Feedlot Cattle: Interplay between Feed Ingredients, Rumen Function and Feeding Behavior (a Review). Anim. Feed Sci. Technol. 2012, 172, 66–79. [Google Scholar] [CrossRef]
  41. Dijkstra, J.; Van Gastelen, S.; Dieho, K.; Nichols, K.; Bannink, A. Review: Rumen Sensors: Data and Interpretation for Key Rumen Metabolic Processes. Animal 2020, 14, s176–s186. [Google Scholar] [CrossRef] [PubMed]
  42. Hamilton, A.W.; Davison, C.; Tachtatzis, C.; Andonovic, I.; Michie, C.; Ferguson, H.J.; Somerville, L.; Jonsson, N.N. Identification of the Rumination in Cattle Using Support Vector Machines with Motion-Sensitive Bolus Sensors. Sensors 2019, 19, 1165. [Google Scholar] [CrossRef] [PubMed]
  43. DePeters, E.J.; George, L.W. Rumen Transfaunation. Immunol. Lett. 2014, 162, 69–76. [Google Scholar] [CrossRef] [PubMed]
  44. Singh, S.P. Precision Dairy Farming: The Next Dairy Marvel. J. Vet. Sci. Technol. 2014, 5. [Google Scholar] [CrossRef]
  45. Lee, M.; Seo, S. Wearable Wireless Biosensor Technology for Monitoring Cattle: A Review. Animals 2021, 11, 2779. [Google Scholar] [CrossRef] [PubMed]
  46. Burnett, T.A.; Kaur, M.; Polsky, L.; Cerri, R.L.A. Rumen-Reticular Temperature During Estrus and Ovulation Using Automated Activity Monitors in Dairy Cows. Front. Vet. Sci. 2020, 7, 597512. [Google Scholar] [CrossRef] [PubMed]
  47. Alzahal, O.; Alzahal, H.; Steele, M.A.; Van Schaik, M.; Kyriazakis, I.; Duffield, T.F.; McBride, B.W. The Use of a Radiotelemetric Ruminal Bolus to Detect Body Temperature Changes in Lactating Dairy Cattle. J. Dairy Sci. 2011, 94, 3568–3574. [Google Scholar] [CrossRef]
  48. Kim, H.; Min, Y.; Choi, B. Real-Time Temperature Monitoring for the Early Detection of Mastitis in Dairy Cattle: Methods and Case Researches. Comput. Electron. Agric. 2019, 162, 119–125. [Google Scholar] [CrossRef]
  49. Costa, J.B.G.; Ahola, J.K.; Weller, Z.D.; Peel, R.K.; Whittier, J.C.; Barcellos, J.O.J. Reticulo-Rumen Temperature as a Predictor of Calving Time in Primiparous and Parous Holstein Females. J. Dairy Sci. 2016, 99, 4839–4850. [Google Scholar] [CrossRef]
  50. Ahn, G.; Ricconi, K.; Avila, S.; Klotz, J.L.; Harmon, D.L. Ruminal Motility, Reticuloruminal Fill, and Eating Patterns in Steers Exposed to Ergovaline. J. Anim. Sci. 2020, 98, skz374. [Google Scholar] [CrossRef]
  51. Ammer, S.; Lambertz, C.; Gauly, M. Is Reticular Temperature a Useful Indicator of Heat Stress in Dairy Cattle? J. Dairy Sci. 2016, 99, 10067–10076. [Google Scholar] [CrossRef] [PubMed]
  52. Lees, A.M.; Lees, J.C.; Lisle, A.T.; Sullivan, M.L.; Gaughan, J.B. Effect of Heat Stress on Rumen Temperature of Three Breeds of Cattle. Int. J. Biometeorol. 2018, 62, 207–215. [Google Scholar] [CrossRef]
  53. Aoki, M.; Kimura, K.; Suzuki, O. Predicting Time of Parturition from Changing Vaginal Temperature Measured by Data-Logging Apparatus in Beef Cows with Twin Fetuses. Anim. Reprod. Sci. 2005, 86, 1–12. [Google Scholar] [CrossRef] [PubMed]
  54. Cooper-Prado, M.J.; Long, N.M.; Wright, E.C.; Goad, C.L.; Wettemann, R.P. Relationship of Ruminal Temperature with Parturition and Estrus of Beef Cows. J. Anim. Sci. 2011, 89, 1020–1027. [Google Scholar] [CrossRef] [PubMed]
  55. Humer, E.; Ghareeb, K.; Harder, H.; Mickdam, E.; Khol-Parisini, A.; Zebeli, Q. Peripartal Changes in Reticuloruminal PH and Temperature in Dairy Cows Differing in the Susceptibility to Subacute Rumen Acidosis. J. Dairy Sci. 2015, 98, 8788–8799. [Google Scholar] [CrossRef] [PubMed]
  56. Kim, D.; Ha, J.; Kwon, W.S.; Moon, J.; Gim, G.M.; Yi, J. Change of Ruminoreticular Temperature and Body Activity before and after Parturition in Hanwoo (Bos Taurus Coreanae) Cows. Sensors 2021, 21, 7892. [Google Scholar] [CrossRef] [PubMed]
  57. Kovács, L.; Kézér, F.L.; Ruff, F.; Szenci, O. Rumination time and reticuloruminal temperature as possible predictors of dystocia in dairy cows. J. Dairy Sci. 2017, 100, 1568–1579. [Google Scholar] [CrossRef] [PubMed]
  58. Firk, R.; Stamer, E.; Junge, W.; Krieter, J. Automation of Oestrus Detection in Dairy Cows: A Review. Livest. Prod. Sci. 2002, 75, 219–232. [Google Scholar] [CrossRef]
  59. Vicentini, R.R.; Bernardes, P.A.; Ujita, A.; Oliveira, A.P.; Lima, M.L.P.; El Faro, L.; Sant’Anna, A.C. Predictive Potential of Activity and Reticulo-Rumen Temperature Variation for Calving in Gyr Heifers (Bos Taurus Indicus). J. Therm. Biol. 2021, 95, 102793. [Google Scholar] [CrossRef] [PubMed]
  60. Vicentini, R.R.; Oliveira, A.P.; Veroneze, R.; Montanholi, Y.R.; Lima, M.L.P.; Ujita, A.; Alves, S.F.; de Lima, A.C.N.; El Faro, L. Reticulo-Rumen Temperature as a Predictor of Estrus in Dairy Gir Heifers. In Proceedings of the 11th World Congress on Genetics Applied to Livestock Production, Auckland, New Zealand, 11–16 February 2018. [Google Scholar]
  61. Boehmer, B.H.; Pye, T.A.; Wettemann, R.P. Ruminal Temperature as a Measure of Body Temperature of Beef Cows and Relationship with Ambient Temperature. Prof. Anim. Sci. 2015, 31, 387–393. [Google Scholar] [CrossRef]
  62. Bewley, J.M.; Grott, M.W.; Einstein, M.E.; Schutz, M.M. Impact of Intake Water Temperatures on Reticular Temperatures of Lactating Dairy Cows. J. Dairy Sci. 2008, 91, 3880–3887. [Google Scholar] [CrossRef]
  63. Haubro Andersen, P. Bovine Endotoxicosis--Some Aspects of Relevance to Production Diseases. A Review. Acta Vet. Scand. Suppl. 2003, 98, 141–155. [Google Scholar] [CrossRef]
  64. Rose, M.K. Metabolic Alterations in Buffaloes Suffering from Digestive Disorders. Haryana Vet. 2013, 52, 71–72. [Google Scholar]
  65. Song, X.; van der Tol, P.P.J.; Groot Koerkamp, P.W.G.; Bokkers, E.A.M. Hot Topic: Automated Assessment of Reticulo-Ruminal Motility in Dairy Cows Using 3-Dimensional Vision. J. Dairy Sci. 2019, 102, 9076–9081. [Google Scholar] [CrossRef]
  66. McSweeney, C.S.; Kennedy, P.M.; John, A. Reticulo-Ruminal Motility in Cattle (Bos Indicus) and Water Buffaloes (Bubalus Bubalis) Fed a Low Quality Roughage Diet. Comp. Biochem. Physiol. A Physiol. 1989, 94, 635–638. [Google Scholar] [CrossRef]
  67. Scheurwater, J.; Hostens, M.; Nielen, M.; Heesterbeek, H.; Schot, A.; van Hoeij, R.; Aardema, H. Pressure Measurement in the Reticulum to Detect Different Behaviors of Healthy Cows. PLoS ONE 2021, 16, e0254410. [Google Scholar] [CrossRef]
  68. Braun, U.; Rauch, S. Ultrasonographic Evaluation of Reticular Motility during Rest, Eating, Rumination and Stress in 30 Healthy Cows. Vet. Rec. 2008, 163, 571–574. [Google Scholar] [CrossRef]
  69. Foster, D. Disorders of Rumen Distension and Dysmotility. Vet. Clin. N. Am. Food Anim. Pract. 2017, 33, 499–512. [Google Scholar] [CrossRef]
  70. Okine, E.K.; Mathison, G.W.; Kaske, M.; Kennelly, J.J.; Christopherson, R.J. Current Understanding of the Role of the Reticulum and Reticulo-Omasal Orifice in the Control of Digesta Passage from the Ruminoreticulum of Sheep and Cattle. Can. J. Anim. Sci. 2011, 78, 15–21. [Google Scholar] [CrossRef]
  71. Braun, U.; Schweizer, A. Ultrasonographic Assessment of Reticuloruminal Motility in 45 Cows. Schweiz. Arch. Tierheilkd 2015, 157, 87–95. [Google Scholar] [CrossRef] [PubMed]
  72. Arai, S.; Haritani, M.; Sawada, H.; Kimura, K. Effect of Mosapride on Ruminal Motility in Cattle. J. Vet. Med. Sci. 2019, 81, 1017. [Google Scholar] [CrossRef]
  73. Nogami, H.; Arai, S.; Okada, H.; Zhan, L.; Itoh, T. Minimized Bolus-Type Wireless Sensor Node with a Built-In Three-Axis Acceleration Meter for Monitoring a Cow’s Rumen Conditions. Sensors 2017, 17, 687. [Google Scholar] [CrossRef]
  74. Humer, E.; Aschenbach, J.R.; Neubauer, V.; Kröger, I.; Khiaosa-ard, R.; Baumgartner, W.; Zebeli, Q. Signals for Identifying Cows at Risk of Subacute Ruminal Acidosis in Dairy Veterinary Practice. J. Anim. Physiol. Anim. Nutr. 2018, 102, 380–392. [Google Scholar] [CrossRef]
  75. Andersson, L.M.; Arai, S.; Okada, H. Orally Administrable Wireless Activity and PH Probe for Cattle Reticulum. Sens. Mater. 2018, 30, 3029–3038. [Google Scholar] [CrossRef]
  76. Rose-Dye, T.K.; Burciaga-Robles, L.O.; Krehbiel, C.R.; Step, D.L.; Fulton, R.W.; Confer, A.W.; Richards, C.J. Rumen Temperature Change Monitored with Remote Rumen Temperature Boluses after Challenges with Bovine Viral Diarrhea Virus and Mannheimia Haemolytica. J. Anim. Sci. 2011, 89, 1193–1200. [Google Scholar] [CrossRef]
  77. Hill, J.; McSweeney, C.; Wright, A.D.G.; Bishop-Hurley, G.; Kalantar-zadeh, K. Measuring Methane Production from Ruminants. Trends Biotechnol. 2016, 34, 26–35. [Google Scholar] [CrossRef]
  78. Storm, I.M.L.D.; Hellwing, A.L.F.; Nielsen, N.I.; Madsen, J. Methods for Measuring and Estimating Methane Emission from Ruminants. Animals 2012, 2, 160–183. [Google Scholar] [CrossRef]
  79. Hammond, K.J.; Waghorn, G.C.; Hegarty, R.S. The GreenFeed System for Measurement of Enteric Methane Emission from Cattle. Anim. Prod. Sci. 2016, 56, 181–189. [Google Scholar] [CrossRef]
  80. Rosenstock, T.S.; Rufino, M.C.; Butterbach-Bahl, K.; Wollenberg, E.; Richards, M. Methods for Measuring Greenhouse Gas Balances and Evaluating Mitigation Options in Smallholder Agriculture; Springer Nature: Berlin/Heidelberg, Germany, 2016; pp. 1–203. [Google Scholar] [CrossRef]
  81. Klein, L.; Wright, A.D.G. Construction and Operation of Open-Circuit Methane Chambers for Small Ruminants. Aust. J. Exp. Agric. 2006, 46, 1257–1262. [Google Scholar] [CrossRef]
  82. Grainger, C.; Clarke, T.; McGinn, S.M.; Auldist, M.J.; Beauchemin, K.A.; Hannah, M.C.; Waghorn, G.C.; Clark, H.; Eckard, R.J. Methane Emissions from Dairy Cows Measured Using the Sulfur Hexafluoride (SF6) Tracer and Chamber Techniques. J. Dairy Sci. 2007, 90, 2755–2766. [Google Scholar] [CrossRef] [PubMed]
  83. Goopy, J.P.; Donaldson, A.; Hegarty, R.; Vercoe, P.E.; Haynes, F.; Barnett, M.; Oddy, V.H. Low-Methane Yield Sheep Have Smaller Rumens and Shorter Rumen Retention Time. Br. J. Nutr. 2014, 111, 578–585. [Google Scholar] [CrossRef]
  84. Huhtanen, P.; Ramin, M.; Hristov, A.N. Enteric Methane Emission Can Be Reliably Measured by the GreenFeed Monitoring Unit. Livest. Sci. 2019, 222, 31–40. [Google Scholar] [CrossRef]
  85. Hellwing, A.L.F.; Lund, P.; Weisbjerg, M.R.; Brask, M.; Hvelplund, T. Technical Note: Test of a Low-Cost and Animal-Friendly System for Measuring Methane Emissions from Dairy Cows. J. Dairy Sci. 2012, 95, 6077–6085. [Google Scholar] [CrossRef] [PubMed]
  86. McGinn, S.M.; Beauchemin, K.A.; Flesch, T.K.; Coates, T. Performance of a Dispersion Model to Estimate Methane Loss from Cattle in Pens. J. Environ. Qual. 2009, 38, 1796–1802. [Google Scholar] [CrossRef]
  87. Kebreab, E.; Clark, K.; Wagner-Riddle, C.; France, J. Methane and Nitrous Oxide Emissions from Canadian Animal Agriculture: A Review. Can. J. Anim. Sci. 2011, 86, 135–158. [Google Scholar] [CrossRef]
  88. Negussie, E.; González-Recio, O.; Battagin, M.; Bayat, A.R.; Boland, T.; de Haas, Y.; Garcia-Rodriguez, A.; Garnsworthy, P.C.; Gengler, N.; Kreuzer, M.; et al. Integrating Heterogeneous Across-Country Data for Proxy-Based Random Forest Prediction of Enteric Methane in Dairy Cattle. J. Dairy Sci. 2022, 105, 5124–5140. [Google Scholar] [CrossRef]
  89. Teagasc. TResearch Autumn 2022: Cleaning the Air; Teagasc: Carlow, Ireland, 2022. [Google Scholar]
  90. Boadi, D.A.; Wittenberg, K.M. Methane Production from Dairy and Beef Heifers Fed Forages Differing in Nutrient Density Using the Sulphur Hexafluoride (SF6) Tracer Gas Technique. Can. J. Anim. Sci. 2011, 82, 201–206. [Google Scholar] [CrossRef]
  91. Machmüller, A.; Hegarty, R.S. Alternative Tracer Gases for the ERUCT Technique to Estimate Methane Emission from Grazing Animals. Int. Congr. Ser. 2006, 1293, 50–53. [Google Scholar] [CrossRef]
  92. Bekele, W.; Guinguina, A.; Zegeye, A.; Simachew, A.; Ramin, M. Contemporary Methods of Measuring and Estimating Methane Emission from Ruminants. Methane 2022, 1, 82–95. [Google Scholar] [CrossRef]
  93. Garnsworthy, P.C.; Difford, G.F.; Bell, M.J.; Bayat, A.R.; Huhtanen, P.; Kuhla, B.; Lassen, J.; Peiren, N.; Pszczola, M.; Sorg, D.; et al. Comparison of Methods to Measure Methane for Use in Genetic Evaluation of Dairy Cattle. Animals 2019, 9, 837. [Google Scholar] [CrossRef] [PubMed]
  94. Broucek, J. Methods of Methane Measurement in Ruminants. Anim. Sci. 2014, 47, 51–60. [Google Scholar]
  95. Pinares-Patiño, C.; Gere, J.; Williams, K.; Gratton, R.; Juliarena, P.; Molano, G.; MacLean, S.; Sandoval, E.; Taylor, G.; Koolaard, J. Extending the Collection Duration of Breath Samples for Enteric Methane Emission Estimation Using the SF6 Tracer Technique. Animals 2012, 2, 275–287. [Google Scholar] [CrossRef] [PubMed]
  96. Lassey, K.R. Livestock Methane Emission: From the Individual Grazing Animal through National Inventories to the Global Methane Cycle. Agric. For. Meteorol. 2007, 142, 120–132. [Google Scholar] [CrossRef]
  97. Ghassemi Nejad, J.; Ju, M.S.; Jo, J.H.; Oh, K.H.; Lee, Y.S.; Lee, S.D.; Kim, E.J.; Roh, S.; Lee, H.G. Advances in Methane Emission Estimation in Livestock: A Review of Data Collection Methods, Model Development and the Role of AI Technologies. Animals 2024, 14, 435. [Google Scholar] [CrossRef] [PubMed]
  98. Hegarty, R.S. Applicability of Short-Term Emission Measurements for on-Farm Quantification of Enteric Methane. Animal 2013, 7 (Suppl. S2), 401–408. [Google Scholar] [CrossRef] [PubMed]
  99. Huhtanen, P.; Cabezas-Garcia, E.H.; Utsumi, S.; Zimmerman, S. Comparison of Methods to Determine Methane Emissions from Dairy Cows in Farm Conditions. J. Dairy Sci. 2015, 98, 3394–3409. [Google Scholar] [CrossRef] [PubMed]
  100. Bell, M.J.; Saunders, N.; Wilcox, R.H.; Homer, E.M.; Goodman, J.R.; Craigon, J.; Garnsworthy, P.C. Methane Emissions among Individual Dairy Cows during Milking Quantified by Eructation Peaks or Ratio with Carbon Dioxide. J. Dairy Sci. 2014, 97, 6536–6546. [Google Scholar] [CrossRef]
  101. Agri Data Analytics. Available online: https://agridataanalytics.com/ (accessed on 25 June 2024).
  102. Zelp. 2024. Zelp Website. Available online: https://www.zelp.co/ (accessed on 23 May 2024).
  103. Van Well, B.; Murray, S.; Hodgkinson, J.; Pride, R.; Strzoda, R.; Gibson, G.; Padgett, M. An Open-Path, Hand-Held Laser System for the Detection of Methane Gas. J. Opt. A Pure Appl. Opt. 2005, 7, S420. [Google Scholar] [CrossRef]
  104. Hristov, A.N.; Kebreab, E.; Niu, M.; Oh, J.; Bannink, A.; Bayat, A.R.; Boland, T.M.; Brito, A.F.; Casper, D.P.; Crompton, L.A.; et al. Symposium Review: Uncertainties in Enteric Methane Inventories, Measurement Techniques, and Prediction Models. J. Dairy Sci. 2018, 101, 6655–6674. [Google Scholar] [CrossRef]
  105. Ricci, P.; Chagunda, M.G.G.; Rooke, J.; Houdijk, J.G.M.; Duthie, C.A.; Hyslop, J.; Roehe, R.; Waterhouse, A. Evaluation of the Laser Methane Detector to Estimate Methane Emissions from Ewes and Steers. J. Anim. Sci. 2014, 92, 5239–5250. [Google Scholar] [CrossRef]
  106. Sorg, D.; Muhlbach, S.; Rosner, F.; Kuhla, B.; Derno, M.; Meese, S.; Schwarm, A.; Kreuz, M.; Swalve, H. The Agreement between Two Next-Generation Laser Methane Detectors and Respiration Chamber Facilities in Recording Methane Concentrations in the Spent Air Produced by Dairy Cows. Comput. Electron. Agric. 2017, 143, 262–272. [Google Scholar] [CrossRef]
  107. Sorg, D. Measuring Livestock CH4 Emissions with the Laser Methane Detector: A Review. Methane 2021, 1, 38–57. [Google Scholar] [CrossRef]
  108. Patra, A.K. Recent Advances in Measurement and Dietary Mitigation of Enteric Methane Emissions in Ruminants. Front. Vet. Sci. 2016, 3, 39. [Google Scholar] [CrossRef] [PubMed]
  109. Johnson, K.A.; Johnson, D.E. Methane Emissions from Cattle. J. Anim. Sci. 1995, 73, 2483–2492. [Google Scholar] [CrossRef] [PubMed]
  110. Weerasekara, C.; Morris, L.C.; Malarich, N.A.; Giorgetta, F.R.; Herman, D.I.; Cossel, K.C.; Newbury, N.R.; Owensby, C.E.; Welch, S.M.; DePaola, B.D.; et al. Using Open-Path Dual-Comb Spectroscopy to Monitor Methane Emissions from Simulated Grazing Cattle. EGUsphere 2024, 1181. [Google Scholar] [CrossRef]
  111. Sun, K.; Tao, L.; Miller, D.J.; Zondlo, M.A.; Shonkwiler, K.B.; Nash, C.; Ham, J.M. Open-Path Eddy Covariance Measurements of Ammonia Fluxes from a Beef Cattle Feedlot. Agric. For. Meteorol. 2015, 213, 193–202. [Google Scholar] [CrossRef]
  112. Herman, D.I.; Weerasekara, C.; Hutcherson, L.C.; Giorgetta, F.R.; Cossel, K.C.; Waxman, E.M.; Colacion, G.M.; Newbury, N.R.; Welch, S.M.; DePaola, B.D.; et al. Precise Multispecies Agricultural Gas Flux Determined Using Broadband Open-Path Dual-Comb Spectroscopy. Sci. Adv. 2021, 7, 9765–9796. [Google Scholar] [CrossRef] [PubMed]
  113. Bai, M.; Loh, Z.; Griffith, D.W.T.; Turner, D.; Eckard, R.; Edis, R.; Denmead, O.T.; Bryant, G.W.; Paton-Walsh, C.; Tonini, M.; et al. Performance of Open-Path Lasers and Fourier Transform Infrared Spectroscopic Systems in Agriculture Emissions Research. Atmos. Meas. Tech. 2022, 15, 3593–3610. [Google Scholar] [CrossRef]
  114. Phillips, F.A.; Naylor, T.; Forehead, H.; Griffith, D.W.T.; Kirkwood, J.; Paton-Walsh, C. Vehicle Ammonia Emissions Measured in An Urban Environment in Sydney, Australia, Using Open Path Fourier Transform Infra-Red Spectroscopy. Atmosphere 2019, 10, 208. [Google Scholar] [CrossRef]
  115. Laubach, J.; Kelliher, F.M. Methane Emissions from Dairy Cows: Comparing Open-Path Laser Measurements to Profile-Based Techniques. Agric. For. Meteorol. 2005, 135, 340–345. [Google Scholar] [CrossRef]
  116. Gao, Z.; Desjardins, R.L.; Flesch, T.K. Assessment of the Uncertainty of Using an Inverse-Dispersion Technique to Measure Methane Emissions from Animals in a Barn and in a Small Pen. Atmos. Environ. 2010, 44, 3128–3134. [Google Scholar] [CrossRef]
  117. DeBruyn, Z.J.; Wagner-Riddle, C.; VanderZaag, A. Assessment of Open-Path Spectrometer Accuracy at Low Path-Integrated Methane Concentrations. Atmosphere 2020, 11, 184. [Google Scholar] [CrossRef]
  118. Baldé, H.; Vander Zaag, A.; Smith, W.; Desjardins, R.L. Ammonia Emissions Measured Using Two Different GasFinder Open-Path Lasers. Atmosphere 2019, 10, 261. [Google Scholar] [CrossRef]
  119. Hacker, J.M.; Chen, D.; Bai, M.; Ewenz, C.; Junkermann, W.; Lieff, W.; McManus, B.; Neininger, B.; Sun, J.; Coates, T.; et al. Using Airborne Technology to Quantify and Apportion Emissions of CH4 and NH3 from Feedlots. Anim. Prod. Sci. 2016, 56, 190–203. [Google Scholar] [CrossRef]
  120. Loh, Z.; Chen, D.; Bai, M.; Naylor, T.; Griffith, D.; Hill, J.; Denmead, T.; McGinn, S.; Edis, R. Measurement of Greenhouse Gas Emissions from Australian Feedlot Beef Production Using Open-Path Spectroscopy and Atmospheric Dispersion Modelling. Aust. J. Exp. Agric. 2008, 48, 244–247. [Google Scholar] [CrossRef]
  121. O’Connor, E.; Mchugh, N.; Boland, T.M.; Dunne, E.; Mcgovern, F.M. Investigation of Intra-Day Variability of Gaseous Measurements in Sheep Using Portable Accumulation Chambers. J. Anim. Sci. 2021, 99, skab132. [Google Scholar] [CrossRef] [PubMed]
  122. Levrault, C.M.; Difford, G.F.; Steinheim, G.; Groot Koerkamp, P.W.G.; Ogink, N.W.M. Validation of the Methane Production Measurement Accuracy and Ranking Capacity of Portable Accumulation Chambers for Use with Small Ruminants. Biosyst. Eng. 2023, 236, 201–211. [Google Scholar] [CrossRef]
  123. Robinson, D.L.; Goopy, J.P.; Hegarty, R.S.; Oddy, V.H. Comparison of Repeated Measurements of Methane Production in Sheep over 5 Years and a Range of Measurement Protocols. J. Anim. Sci. 2015, 93, 4637–4650. [Google Scholar] [CrossRef] [PubMed]
  124. Muñoz-Tamayo, R.; Ramírez Agudelo, J.F.; Dewhurst, R.J.; Miller, G.; Vernon, T.; Kettle, H. A Parsimonious Software Sensor for Estimating the Individual Dynamic Pattern of Methane Emissions from Cattle. Animal 2019, 13, 1180–1187. [Google Scholar] [CrossRef]
  125. Lassen, J.; Løvendahl, P.; Madsen, J. Accuracy of Noninvasive Breath Methane Measurements Using Fourier Transform Infrared Methods on Individual Cows. J. Dairy Sci. 2012, 95, 890–898. [Google Scholar] [CrossRef]
  126. Madsen, J.; Bjerg, B.S.; Hvelplund, T.; Weisbjerg, M.R.; Lund, P. Methane and Carbon Dioxide Ratio in Excreted Air for Quantification of the Methane Production from Ruminants. Livest. Sci. 2010, 129, 223–227. [Google Scholar] [CrossRef]
  127. Hellwing, A.; Lund, P.; Madsen, J.; Weisberg, M.R. Comparison of Enteric Methane Production from the CH4/CO2 Ratio and Measured in Respiration Chambers. Adv. Anim. Biosci. 2013, 4. [Google Scholar] [CrossRef]
  128. Huhtanen, P.; Bayat, A.R.; Lund, P.; Hellwing, A.L.F.; Weisbjerg, M.R. Short Communication: Variation in Feed Efficiency Hampers Use of Carbon Dioxide as a Tracer Gas in Measuring Methane Emissions in on-Farm Conditions. J. Dairy Sci. 2020, 103, 9090–9095. [Google Scholar] [CrossRef] [PubMed]
  129. Huang, Z.Q. Assessing Bovine Methane Emissions: Respiratory Simulation and Optical Gas Imaging Methods; Massachusetts Institute of Technology: Cambridge, UK, 2023. [Google Scholar]
  130. Kang, R.; Liatsis, P.; Kyritsis, D.C. Emission Quantification via Passive Infrared Optical Gas Imaging: A Review. Energies 2022, 15, 3304. [Google Scholar] [CrossRef]
  131. Ravikumar, A.P.; Wang, J.; Brandt, A.R. Are Optical Gas Imaging Technologies Effective for Methane Leak Detection? Environ. Sci. Technol. 2017, 51, 718–724. [Google Scholar] [CrossRef] [PubMed]
  132. Asadzadeh, S.; de Oliveira, W.J.; de Souza Filho, C.R. UAV-Based Remote Sensing for the Petroleum Industry and Environmental Monitoring: State-of-the-Art and Perspectives. J. Pet. Sci. Eng. 2022, 208, 109633. [Google Scholar] [CrossRef]
  133. Moonen, A.J.; Sufian, B.A. Introducing New Drone-Based Inspection Technologies to Safely and Consistently Deliver High Value Results. In Proceedings of the Offshore Technology Conference Asia 2020, OTCA 2020, Kuala Lumpur, Malaysia, 27 October 2020. [Google Scholar]
  134. Gerber, P.J.; Steinfeld, H.; Henderson, B.; Mottet, A.; Opio, C.; Dijkman, J.; Falcucci, A.; Tempio, G. Tackling Climate Change through Livestock—A Global Assessment of Emissions and Mitigation Opportunities; Food and Agriculture Organization of the United Nations (FAO): Rome, Italiy, 2013. [Google Scholar]
  135. Appuhamy, J.A.D.R.N.; France, J.; Kebreab, E. Models for Predicting Enteric Methane Emissions from Dairy Cows in North America, Europe, and Australia and New Zealand. Glob. Chang. Biol. 2016, 22, 3039–3056. [Google Scholar] [CrossRef] [PubMed]
Figure 2. Reticular contractions during eating and rumination. Relative pressure differences illustrating two minutes of primary biphasic reticular contractions during eating (a), with a third contraction during rumination (b). Source [56].
Figure 2. Reticular contractions during eating and rumination. Relative pressure differences illustrating two minutes of primary biphasic reticular contractions during eating (a), with a third contraction during rumination (b). Source [56].
Agriculture 14 01096 g002
Figure 3. Schematics of different ruminant enteric CH4-monitoring techniques: (a) respiration chamber; (b) sulphur hexafluoride (SF6) tracer method; (c) spot sampling; and (d) laser CH4 detector.
Figure 3. Schematics of different ruminant enteric CH4-monitoring techniques: (a) respiration chamber; (b) sulphur hexafluoride (SF6) tracer method; (c) spot sampling; and (d) laser CH4 detector.
Agriculture 14 01096 g003
Figure 4. Profile of CH4 measurements for a cow taken from a respiration chamber (solid dot) and a laser CH4 detector (grey dots). Source: [11].
Figure 4. Profile of CH4 measurements for a cow taken from a respiration chamber (solid dot) and a laser CH4 detector (grey dots). Source: [11].
Agriculture 14 01096 g004
Table 1. Comparison of different methods to monitor and estimate enteric CH4 emissions.
Table 1. Comparison of different methods to monitor and estimate enteric CH4 emissions.
Technique CostApplicationSuitability AdvantagesDisadvantages
Respiration chamberGenerally highResearchRequires controlled conditions; measurements are limited to a single animal at a time.Highly accurate data collection using a controlled environment; individual animal monitoring; precise measurement of dry matter intake. Expensive to construct and maintain; requires an animal acclimation period; may disrupt animal normal behaviour.
Sulphur hexafluoride (SF6) tracer methodModerateResearchApplicable for grazing animals; suitable for a large number of individual animals.Provides accurate data; suitable for enclosed and free-range animals; few interferences by other gases; far less intrusive than respiration chambers. Relies on a highly potent GHG; high risk of equipment failure; depends on spot concentration measurements; may disrupt animal normal behaviour.
Spot samplingModerateResearch and CommercialApplicable for grazing animals; suitable for multiple animals at once. More affordable and simpler than SF6 tracer and respiration chamber methods; non-invasive technique. Restricted measurement periods; the GreenFeed method requires an animal bait.
Laser CH4 detectorModerateResearch and CommercialRequires semi-controlled conditions; suitable for a large number of individual animals. Immediate results; reduced labour requirement; minimal stress on the animal. Sensitive to environmental factors; animal needs to stay relatively still.
Open-path laserHighResearchSuitable for grazing animals; able of collecting measurements from a large herd of animals; emissions cannot be attributed to a single animal.Non-intrusive; large-scale monitoring; suitable for enclosed and free-range animals. Requires expensive equipment; utilises sensitive instrumentation; sensitive to environmental factors; requires animal cooperation.
Portable accumulation chamberModerateResearch Requires controlled conditions; measurements are limited to a single animal at a time.Relatively simple and portable; short-term measurement. Restricted measurement periods; may disrupt animal normal behaviour.
CO2 tracer methodModerateResearchApplicable for a large number of individual animals.Suitable for enclosed and free-range animals; far less intrusive than respiration chambers.Less accurate for short-term variations, sensitive to background CO2, requires careful calibration.
Optical gas imaging (OGI) HighResearchRequires controlled conditions; applicable for a large number of individual animals.Non-intrusive; minimal animal discomfort, suitable for enclosed and free-range animals. Requires expensive equipment; technology is still under development; sensitive to environmental factors.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

O’Connor, S.; Noonan, F.; Savage, D.; Walsh, J. Advancements in Real-Time Monitoring of Enteric Methane Emissions from Ruminants. Agriculture 2024, 14, 1096. https://doi.org/10.3390/agriculture14071096

AMA Style

O’Connor S, Noonan F, Savage D, Walsh J. Advancements in Real-Time Monitoring of Enteric Methane Emissions from Ruminants. Agriculture. 2024; 14(7):1096. https://doi.org/10.3390/agriculture14071096

Chicago/Turabian Style

O’Connor, Seán, Flannagán Noonan, Desmond Savage, and Joseph Walsh. 2024. "Advancements in Real-Time Monitoring of Enteric Methane Emissions from Ruminants" Agriculture 14, no. 7: 1096. https://doi.org/10.3390/agriculture14071096

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop