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Article

An Investigation of the Potential Adoption of Anaerobic Digestion for Energy Production in Irish Farms

1
Department of Environmental Science, Institute of Technology Sligo, F91 YW50 Sligo, Ireland
2
Sustainable Infrastructure Research and Innovation Research Group, Department of Civil, Structural and Environmental Engineering, Cork Institute of Technology, T12 P928 Cork, Ireland
3
Agri-Environment Branch, Agri-Food and Biosciences Institute, Large Park, Hillsborough BT26 6DR, UK
*
Author to whom correspondence should be addressed.
Submission received: 30 November 2020 / Revised: 9 January 2021 / Accepted: 20 January 2021 / Published: 27 January 2021
(This article belongs to the Special Issue Small-Scale Anaerobic Digestion for Biogas Production)

Abstract

:
Anaerobic digestion (AD) has been recognised as an effective means of simultaneously producing energy while reducing greenhouse gas (GHG) emissions. Despite having a large agriculture sector, Ireland has experienced little uptake of the technology, ranking 20th within the EU-28. It is, therefore, necessary to understand the general opinions, willingness to adopt, and perceived obstacles of potential adopters of the technology. As likely primary users of this technology, a survey of Irish cattle farmers was conducted to assess the potential of on-farm AD for energy production in Ireland. The study seeks to understand farmers’ motivations, perceived barriers, and preferred business model. The study found that approximately 41% of the 91 respondents were interested in installing AD on their farming enterprise within the next five years. These Likely Adopters tended to have a higher level of education attainment, and together, currently hold 4379 cattle, potentially providing 37,122 t year−1 of wastes as feedstock, resulting in a potential CO2 reduction of 800.65 t CO2-eq. year−1. Moreover, the results indicated that the primary consideration preventing the implementation of AD is a lack of information regarding the technology and high investment costs. Of the Likely Adopters and Possible Adopters, a self-owned and operated plant was the preferred ownership structure, while 58% expressed an interest in joining a co-operative scheme. The findings generated provide valuable insights into the willingness of farmers to implement AD and guidance for its potential widespread adoption.

1. Introduction

To combat the potentially disastrous consequences of climate change, the European Union (EU) has set a goal of reducing its greenhouse gas (GHG) emissions by 80–95%, relative to 1990 levels by the year 2050 [1]. Crucial legislative milestones in place in order to achieve this goal include the EU 2020 Climate and Energy Package and the EU 2030 Climate and Energy Framework, both of which set binding emission reduction targets for all EU states [2,3]. One country that has struggled to meet its climate change obligations is Ireland, where the country is projected to only reduce their GHG emissions by 2–4%, relative to their 20% 2020 target [4]. A significant factor to this problem is the country’s large agriculture sector, which has consistently remained the single largest emitter, producing 33.9% of total emissions in 2018 [5]. Contributing to this is the country’s large livestock population, consisting of 7.21 million cattle and 1.62 million pigs [6]. The dairy sector, in particular, has grown significantly in recent years, where Ireland is now the 10th largest dairy exporter in the world [7]. Much of this growth has stemmed from the removal of the European-wide milk production quotas in 2015. The removal of the quotas saw a rapid growth in the milk processed in the country, increasing from 6.2 billion L in 2014 to 8.7 billion L in 2019 [8]. The country currently faces mounting pressure to maintain strong economic growth in its agriculture sector while still meeting emission reduction targets imposed by the EU.
Of the European Union member states, the circumstances surrounding the agriculture sector in Ireland places the country in a unique situation for the potential widespread adoption of anaerobic digestion (AD) technology. Despite the apparent benefits of AD, Ireland has been slow to adopt the technology, ranking 20th in AD deployment among the EU-28 countries [9]. To date, the vast majority of AD installations implemented in Ireland have been for wastewater treatment plants, with only fourteen plants using an agriculture feedstock [10]. Considering that 40 million tonnes of animal manures are produced from Irish livestock annually, the potential for AD adoption is clear [11]. These slurry and manure feedstock streams are theoretically available, but the lack of decentralised AD infrastructure has limited the implementation of the technology to date. [9]. While significant research has been carried out to address technical, political, and environmental concerns related to the development of AD [12,13,14,15,16,17], relatively little attention has been paid to the motivations and characteristics of the potential adopters of the technology. In comparison, studies addressing this research area internationally are widespread [18,19,20,21]. Since Ireland’s AD market is still maturing, an increased understanding of the factors influencing the stakeholder adoption process could be particularly beneficial. Furthermore, such information is necessary for policymakers to develop adequate implementation strategies, capable of overcoming obstacles identified and encouraging widespread use. Of the farming types, cattle farmers are particularly promising for the implementation of AD, due to the size of the national herd, the quantity of feedstock available, existing demand for on-site electricity and thermal energy, and the need for emission reduction [12,22].
The focus of this study was to identify Irish cattle farmers’ perspectives, motivations and perceived obstacles to the adoption of AD on their farming enterprise and to characterise potential “Likely Adopters” of the technology. The study’s findings offer valuable insights into the motivations of likely AD adopters, providing guidance for academics, policymakers, and stakeholders on future implementation strategies.

2. Materials and Methods

To address the study’s objectives, a survey methodology was utilised. Data collection took place between January 2019 and October 2019. The survey circulated to the participants has been included in the Supplementary Material. The targeted population of the survey were farmers specialising in cattle (beef, dairy, and mixed) in Ireland.
The survey was designed after conducting a detailed literature review and through discussions with academics, farmers and those employed in the agriculture industry. An initial pilot study with several farmers was conducted to finalise the design of the survey. The eventual survey consisted of a cover letter and three pages with twelve questions. These questions were categorised into six sections, each with a specific goal. Section 1 of the survey aimed to collect relevant demographical information, such as the respondent’s age, educational attainment, location, farmland, and farming enterprise operation. The second part of the survey sought to assess the respondent’s previous interaction with renewable energy (RE) technologies and reasoning (if applicable) for implementation. Section 3 was designed to assess the respondent’s likelihood of adopting AD technology on their own farming enterprise. Section 4 focused on understanding the respondent’s preferred plant operating conditions if they were to implement the technology. Section 5 used Likert-scale questioning to explore the participant’s perception of AD, including the perceived benefits and barriers to its implementation. The final section (section 6) provided an opportunity for respondents to provide any other comments and contact information to receive the results of the study.
Considering the low uptake of farm-scale AD plants in Ireland to date, it was assumed that many of the participants would be unfamiliar with the technology. This assumption was confirmed during the pilot study and initial discussions with farming representatives, who were largely unaware of the technology and its features. It was therefore deemed useful to include a brief, unbiased explanation of the AD concept and technology for respondents to give them an introduction to AD, and aid in them answering Section 3 of the survey accurately. Figure 1 presents the explanation and diagram included in the survey to provide the participants with an informed understanding of the technology.
The study mainly used two distribution methods to maximise the possible responses. Method A consisted of distributing a paper-based copy of the survey at three large-scale farming-related events; two dairy farm workshops and one industry event. Method B entailed distributing the survey electronically through established mailing lists via a popular service (SurveyMonkey.com).
A total of 95 surveys were returned, of which four responses were deemed as ineligible as they did not engage in cattle farming, leaving 91. Of the eligible responses, 68 were gained through Method A and 23 from Method B. Statistical analyses was carried out using the software packages IBM Statistical Package for the Social Sciences (SPSS) (IBM SPSS Statistics for Windows, v26.0. Armonk, NY, USA: IBM Corp) and Microsoft Office Excel (Microsoft Office 2016, Microsoft Corporation, Redmond, WA, USA). To identify data trends, statistical techniques were utilised, such descriptive statistics, frequency tables, chi squared tests, and means t-tests. In comparison to the national average, the sample of respondents generally had a larger herd and farm size (as shown in Table 1).

3. Results

3.1. Demographical Characteristics and Rate of Adoption

Table 1 provides a comparison between the respondent’s characteristics and the national average in terms of personal attributes and the farming enterprise operation. When the respondents were asked, “Would you consider installing an anaerobic digestion plant on your farm in the next five years?” of the 91 participants, 40.7% (n = 37) responded “yes”, followed by 37.4% (n = 34) that responded “maybe”, and 22.0% (n = 20) expressed no interest. For ease of analysis, in interpreting the results, three groups were created, which were “Likely Adopters” (“yes” respondents), “Possible Adopters” (“maybe” respondents), and “Non-Adopters” (“no” respondents).
Differences in contextual characteristics between the respondents in terms of adoption preference can be seen in Table 1. It was found that the mean total herd size of the “Likely Adopters” (125.1 animals) was generally greater than the “Non-Adopters” (76.1 animals). Of the farming types surveyed, dairy farmers were the most probable to be Likely Adopters (40.5%), followed by mixed cattle farmers (37.8%), and beef farmers expressing the least interest (21.6%). This was anticipated as dairy and mixed cattle farmers would typically need to deal with larger quantities of wastes emanating from their processes, unlike beef farmers (where the cattle may graze for longer periods). The average farm size was larger than the national average (43.2 ha) at 62.3 ha (7 ha–243 ha) [24]. A chi-squared test for association was used to test respondent’s attributes for statistically significant differentiators for being a “Likely Adopter” of AD. Of the variables tested, the level of educational attainment yielded a statistically significant result (p = 0.001).
In addition to examining the farmers’ characteristics and their farming operations, the study also investigated the respondents’ previous experiences with renewable energy (RE) technologies (if any) and used that as a potential indicator for future AD adoption. This is especially relevant since there is little information currently available to date on the motivations and uptake of RE technologies within the Irish agriculture context. Figure 2 presents the uptake rates of various RE technologies amongst the participants. Of the 91 participants surveyed, the existing adoption of RE technologies proved generally high (17.6%) in comparison to other countries (in Europe) [25,26]. It emerged that solar panels were the most popular technology with an uptake rate at 14.3% of the total surveyed. With the exception of solar panels, poor uptake rates were reported for all other RE technologies. Issues cited include complications connecting to the national grid, insufficient government grant support, difficulties securing an electricity tariff, and a lack of awareness [12].
Interestingly, of the farmers that had already implemented RE technologies on their farms, these mainly fell under those that were categorised as “Non-Adopters” (37.5%) rather than “Likely Adopters” (31.3%) and of “Possible Adopters” (31.3%) of AD. However, the sample size which this conclusion is based on is relatively small (n = 16) with one respondent having installed two RE technologies. Moreover, respondents that indicated that they had implemented RE technologies, were then asked to disclose the motivating factor from several possible options. Of the factors listed, the following were indicated as contributors: to reduce farm business costs (45%); to reduce greenhouse gas emissions (20%); to add another source of revenue (15%); to exploit government grants (15%); and other motivations (5%). Respondents were also given the opportunity to write-in other motivating factors, where the generation of renewable energy was listed. These results align with previous research conducted on farmers in the United Kingdom [26], where an uptake rate of 14% was observed, with solar panels also being the dominant RE technology implemented.

3.2. Motivations to Implement the Technology

Farmers were asked to rate the importance of several benefits that could be gained through the implementation of AD on their farming enterprise using Likert-scale from 1 (indicating that it was very important) to 4 (indicating it was unimportant). Table 2 summarises the responses received, where the mean and standard deviation are presented. Of the benefits presented to participants, factors relating to the plant’s economics proved to be the most important. Interestingly, environmental benefits were also deemed important, but to a lesser extent. While “Likely Adopters”, “Possible Adopters”, and “Non-Adopters” differed in the level of importance given to items, there was a general agreement on the order of selection.
The respondents were also asked their opinion on several potential obstacles that could prevent them from implementing AD on their farming enterprise. Participants were asked to rate their agreement on several statements using a Likert-scale from 1 (indicated that they strongly agree) to 5 (indicating they strongly disagreed). A summary of the responses provided by the participants is shown in Table 3. Of the options presented, the largest obstacles for both “Likely Adopters” and “Possible Adopters” was that there was not enough information about the technology, while “Non-Adopters” deemed the potentially high investment cost the largest barrier. These findings concur with previous studies conducted internationally [27,28,29,30]. In comparison, the least likely obstacle to AD adoption for adopter types was that the individual’s rental agreement would not allow it. A likely contributing factor to this is the large portion of respondents who reported to wholly own (> 75% of farmland) their farmland at 73.6%. “Likely Adopters” and “Possible Adopters” generally agreed on the order of selection, while differing in the level of importance given to items. In addition, to gain an increased understanding, respondents were also given the opportunity to write-in other perceived obstacles to AD adoption. The responses received commented on the low electricity feed-in tariff (FIT) currently available, the high financial cost of gaining a grid connection, and the time necessary to monitor and operate the plant.

3.3. Preferred Operating Conditions

Much debate has taken place in the literature between the use of small-scale anaerobic digestion (SSAD) plants and the more centralised medium to large-scale co-operative AD plants. Co-operative plants generally consist of multiple feedstock suppliers feeding a centralised AD plant, while SSAD plants typically consist of a single supplier feeding and operating a plant of lesser capacity. While co-operative plants have the benefits of greater economies of scale and reduced financial risk, SSAD plants provide greater control over feedstock quality and minimise multiple stakeholder involvement. This study aimed to provide a greater understanding of Irish cattle farmers’ potential preferred AD plant operating arrangements if they were to implement the technology. Figure 3 shows the respondents preferred plant ownership and operating structures if they were to implement the technology in their own farming enterprise. “Non-Adopter” respondents were not included in the results, as they were deemed irrelevant. The reasoning for their exclusion is that they were unlikely to potentially operate or part-take in an AD enterprise. Of the choices available, “self-owned and operated” was the preferred option (40.3%), followed by “self-owned and third party operated” (29.9%), then “third-party owned and operated” (16.4%), and finally “third-party owned and self-operated” (13.4%).
Figure 4 provides a breakdown of the participants’ responses when asked, “would you consider taking part in a co-operative scheme where 2 to 5 local farmers’ feed slurry into an anaerobic digestion plant?”. Similar to Figure 3, the responses from “Non-Adopter” were not included, as they were unlikely to operate or partake in an AD based enterprise. The results from the questioning were as follows, 58.0% responded “yes” (n = 40), followed by 33.3% (n = 23) that responded “maybe”, and 8.7% (n = 6) answered “no”. Of the examined respondents, two participants chose not to answer the question. The findings showed a large willingness of all categories to engage in AD based co-operative schemes.

3.4. Broader Implications

Table 4 provides a rough estimate of the potential technical and environmental implications if the “Likely Adopters” (n = 37) identified in this study were to implement AD technology. These calculations are based solely on the collection of cattle manure and exclude the likely co-digestion of other feedstocks types such as energy crops, industry waste, or food waste. The inclusion of such feedstocks would likely increase the potential methane yield considerably. The total slurry available is based on an average yield of 52.2 kg day−1 per head of cattle [31]. The collection of slurry for use as AD feedstock is based on animals being housed over the 16-week winter period (100% collection) and left out to graze for the remainder of the year (20% collection) [12,32]. Energy generation is based on the utilisation of combined heat and power (CHP) units, which are typically the most economically viable and widely used biogas utilisation technology available for agriculture based SSAD plants [17]. The potential electricity production is based on an estimated methane yield of 16.0 ± 0.9 m3 CH4 t−1 FW, a methane energy density of 37.78 MJ/m3, and a CHP electrical efficiency of 35% [33,34].
The potential environmental benefits are calculated based on all electricity produced being exported to the national grid with this displaced energy on average producing 0.367 t CO2 MWh−1 [35]. Table 4 shows that significant energy generation and GHG emission savings are achievable from the Irish cattle industry. It is worth noting that the CO2 savings presented are likely to be an underestimate, as it excludes the use of the thermal (heat) energy generated and the release of methane to the atmosphere during storage and land application. The CO2 savings presented (800.65 t CO2-eq. yr1), is equivalent to the displacement of 300,538 L of diesel annually or taking 238.71 cars off the road, assuming diesel consumption is 1259 L year−1 and emissions of 2.67 kg CO2 litre−1 [36]. Over the life span of the AD plants (20 years), the CO2 reduction possible from the total farms was calculated to be 16,013 t CO2-eq [37,38,39].

4. Discussion

This study attempts to understand the motivations and opinions of Irish farmers in regard to the uptake and operation of farm-scale AD through a detailed analysis of a qualitative questionnaire. Although the research findings do not represent the views of the entire agricultural community, they do provide meaningful insights for the development of an Irish bioenergy industry. The study’s analysis focuses on the economic and social dimensions apparent in the development and adoption of AD plants nationally. In this way, it complements existing literature on the topic, which has largely focused on the technical aspects. The study is one of the first academic contributions to identify farmer’s opinions and readiness to adopt AD technologies within the Irish context.
This research has provided evidence that the willingness of Irish cattle farmers to implement or supply feedstock to AD plants to be relatively high and in line with earlier studies carried out in other European countries [18,19]. The demographical characteristics of “Likely Adopters” supported findings from previous studies, confirming age and educational attainment to be significant factors in respondents’ willingness to engage with RE enterprises [18,40,41,42].
Of the farming types examined, the results showed dairy and mixed cattle farmers to be most likely to implement AD plants (40.5%), with the least interest being expressed by beef farmers (21.6%). It is likely that differences in profitability between these farming types may be a contributing factor as larger (more profitable) agriculture enterprises have been reported to be more inclined to introduce new technologies and equipment [18]. This subsequently influences the farming types examined, as dairy and mixed cattle farms generally exhibit higher net margins in Ireland [43]. In addition, respondents exhibited a high level of confidence in their ability to operate a biogas plant after sufficient training. These preferred operating and ownership structures could be invaluable to inform Irelands gas networks strategy, where Gas Networks Ireland (semi-state body) has set a goal for the national gas network to be net-zero carbon by 2050 [44].
Perceived outcomes (benefits and obstacles) proved to correlate highly with the respondent’s willingness to implement AD technology. The findings from the Likert-scale questioning shown in Table 2, found that the main factors that motivated adoption was first to improve farm profitability (1.49 ± 0.69), followed closely by a wish to add another revenue source (1.57 ± 0.64). These results confirm findings obtained from earlier studies, where it was hypothesised that farmers/feedstock suppliers would be motivated to engage with RE technologies if they were likely to contribute to the economic growth of the farming enterprise [26,45,46,47]. In addition to economic benefits, environmental advantages were also identified as motivating factors. This was anticipated, as farmers are increasingly facing regulatory and societal pressure to implement strategies and technologies to mitigate GHG emissions and to reduce their dependence on fossil fuels [3,48,49].
After reflecting on the obstacles identified in the analysis, the authors do not present a hierarchy of barriers but rather a set of issues that must be addressed holistically. While adoption was driven primarily by economic factors, the single largest barrier identified was a lack of awareness and inadequate information regarding the technology. A key strategy to overcome this difficulty is the use of early adopters or local champions to increase awareness and to promote the technologies positive attributes, therefore, demonstrating the positive contribution possible to the performance of the farming enterprise as well as acting as a model for other farmers to duplicate [26,50]. Similar initiatives enacted by policymakers have proved effective in increasing awareness and adoption rates in other countries (e.g., United Kingdom, Belgium, and the Netherlands,) [26,51,52,53]. A recent Irish initiative following this methodology is the EIP Small Biogas Demonstration Project, which aims to promote SSAD through informative workshops, feasibility studies, and the provision of capital grants for the construction of three biogas plants [54]. When completed, it is envisioned that these plants will act as demonstration projects, which will potentially address or lessen the obstacles highlighted by respondents.
Other barriers identified include the potentially high investment costs and uncertainty in regard to the technology’s financial returns. Stakeholder concerns regarding the economics of RE enterprises have been commonly reported in the existing literature [28,55]. In an effort to overcome such difficulties, many governments have introduced incentives (e.g., electrical feed-in tariffs, capital grants, and heat tariffs), which can prove vital to the financial viability of RE projects, especially for early adopters [56,57]. In an effort to increase the generation of energy from RE sources, the Irish government have recently introduced an initiative named the Support Scheme for Renewable Heat [58]. The scheme is designed to increase the energy generated from RE sources, where it provides two tariffs to biogas plant operators of 2.95 cEUR kWh−1 (plants generating less than 1000 MWh year−1) and 0.50 cEUR kWh−1 (plants generating 1000 to 2400 MWh year−1) for heat generated that displaces conventional fossil fuel alternatives [58].
Although the study has generated considerable new insights, some potential limitations need to be addressed. It should be noted that the sample size had a larger herd and farm size then the national average. The authors believe that a potential contributing factor may have been the audience and platforms used for the collection of data, favouring a greater receipt of responses from larger sized (than national average) farms. The reasoning being that such dissemination platforms mainly attract farmers actively engaged in farming full-time, which are more likely to have larger farms. This is opposed to the overall farming sector landscape captured in the national registry, which also includes smaller farm holdings, managed by part-time farmers. Other potential contributing factors include the respondents’ biases to report favourable figures, and the relatively small sample size captured by the study. For future research, we suggest that a more in-depth analysis is needed of Irish farmers willingness to adopt AD technologies based on the technical, environmental, and economic conditions specific to their own farming enterprise. Moreover, further research is needed to how greater value creation and environmental benefits can be achieved through plant analysis and AD-based biorefinery platforms, subsequently accelerating the development of a circular economy [16,59,60,61,62].
Looking forward, it is anticipated as the consequences of climate change become increasingly apparent; there will be growing social and political pressure to mitigate the negative environmental impacts of all industries. Of the RE technologies available, AD holds considerable potential for the generation of renewable energy and the reduction of GHG emissions, particularly in the agriculture sector. It is hoped that through the increased understanding provided, that the results will positively influence the development of the industry by guiding future initiatives in regard to farmers’ preferences and concerns.

5. Conclusions

Farm-scale AD can play a considerable role in reducing the negative environmental impacts associated with small to medium-sized agriculture enterprises. In addition, to GHG reduction, plants afford other benefits such as on-site energy generation, the provision of a nutrient-rich fertiliser from the digester effluents, and the reduction of odour and pathogen loads. Therefore, to provide a greater understanding of the technology’s potential within the Irish context, this study investigated cattle farmers’ perception and willingness to adopt the technology. The results revealed that 41% of participants responded “yes” when asked would they consider implementing AD on their farming enterprise within the next five years. These “Likely Adopters” were generally characterised by having a higher level of educational attainment in comparison to other respondents. High investment costs and a lack of information regarding the technology were found to be the leading barriers to implementation, while its potential to improving farm profitability was the greatest perceived benefit. Of the “Likely Adopters” and “Possible Adopters”, 58% were interested in partaking in a co-operative scheme where two to five farmers feed a centralised AD plant, while a “Self-owned and operated” business model was the preferred business model (40.3%). The study estimates that if all “Likely Adopters” identified, implemented the technology, a CO2 reduction of 800.65 t CO2-eq. year−1 and electricity production of 2182 MWh year−1 was potentially achievable. The broader implications of this work highlight the potential willingness of farmers to implement AD or to supply feedstock to a centralised plant. Going forward, it is hoped that the insights developed in this study will guide researchers, policymakers and AD operators in furthering the development of an indigenous bioenergy industry.

Supplementary Materials

The following are available online at https://0-www-mdpi-com.brum.beds.ac.uk/2076-3298/8/2/8/s1, Survey questions.

Author Contributions

Conceptualisation, S.O., E.E., and J.B.; validation, S.O., E.E., S.C.P., N.P., G.A.L. and J.B.; writing—original draft preparation, S.O.; writing—review and editing, S.O., E.E., S.C.P., N.P., G.A.L. and J.B.; supervision, E.E., S.C.P. and J.B. All authors have read and agreed to the published version of the manuscript.

Funding

The research leading to these results has received funding from the European Union’s INTERREG VA Programme, managed by the Special EU Programmes Body (SEUPB), with match funding provided by the Department for the Economy (Northern Ireland) and Department of Enterprise, Trade and Employment (Republic of Ireland), grant number IVA5033. The views and opinions expressed in this article do not necessarily reflect those of the European Commission or the Special EU Programmes Body (SEUPB).

Informed Consent Statement

Informed consent was obtained from all subjects involved in the study.

Data Availability Statement

The data presented in this study are available on request from the corresponding author.

Conflicts of Interest

The authors declare no conflict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results.

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Figure 1. Explanation of AD included in the survey.
Figure 1. Explanation of AD included in the survey.
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Figure 2. Farmer’s previous implementation of renewable technologies.
Figure 2. Farmer’s previous implementation of renewable technologies.
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Figure 3. Survey responses preferred AD plant operating conditions.
Figure 3. Survey responses preferred AD plant operating conditions.
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Figure 4. Survey responses willingness to partake in a co-operative scheme.
Figure 4. Survey responses willingness to partake in a co-operative scheme.
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Table 1. Differences in characteristics between Likely Adopters, Possible Adopters, and Non-Adopters.
Table 1. Differences in characteristics between Likely Adopters, Possible Adopters, and Non-Adopters.
CharacteristicsNational AverageAll ResponsesLikely AdoptersPossible AdoptersNon-Adopters
Livestock (means)
All farms (mean animals)66 a113.7125.1110.376.1
Dairy farms (mean animals)80.0 b118.3120.3118.4113.3
Beef farms (mean animals)36.7 b63.357.359.272.1
Mixed cattle farms (mean animals)-161.9163.9163.3120.0
Livestock (adopter type %)
All farms (%)-100 (n = 91)40.7 (n = 37)37.4 (n = 34)22.0 (n = 20)
Dairy farms (%)-37.8 (n = 34)40.5 (n = 15)32.4 (n = 11)40.0 (n = 8)
Beef farms (%)-32.2 (n = 30)21.6 (n = 8)35.3 (n = 12)50.0 (n = 10)
Mixed cattle farms (%)-30.0 (n = 27)37.8 (n = 14)32.4 (n = 11)10.0 (n = 2)
Farm size (means)
Total area farmed (ha)26.49 a62.356.664.469.3
Area owner-occupied (ha)22.18 a54.244.057.167.2
Area rented (ha)4.31 a18.221.617.78.4
Age of respondents (%)
Less than 35 years (%)5 a15.6 (n = 14)27.0 (n =10)8.8 (n = 3)5.3 (n = 1)
35–44 years (%)16 a21.1 (n = 19)16.2 (n = 6)26.5 (n = 9)21.1 (n = 4)
45–54 years (%)24 a27.8 (n = 25)27.0 (n = 10)32.4 (n = 11)21.1 (n = 4)
55–64 years (%)25 a28.9 (n = 26)24.3 (n = 9)29.4 (n = 10)36.8 (n = 7)
65 years and over (%)30 a6.7 (n = 6)5.4 (n = 2)2.9 (n = 1)15.8 (n = 3)
Education Attainment (%)
Primary or below-3.3 (n = 3)0.0 (n = 0)0.0 (n = 0)15.8 (n = 3)
Secondary Level-41.1 (n = 37)27.0 (n = 10)38.2 (n = 13)73.7 (n = 14)
Third Level College/Institution-43.3 (n = 39)56.8 (n = 21)50.0 (n = 17)5.3 (n = 1)
Postgraduate degree-4.4 (n = 4)8.1 (n = 3)2.9 (n = 1)0.0 (n = 0)
Apprenticeships-6.7 (n = 6)5.4 (n = 2)8.8 (n = 3)5.3 (n = 1)
Did not undertake formal study-1.1 (n = 1)2.7 (n = 1)0.0 (n = 0)0.0 (n = 0)
a Estimated, based on data sourced from [23]. b Estimated, based on data sourced from [24]. Note that some respondents declined to provide details on livestock figures.
Table 2. Summary of survey responses to Likert-scale questions on the importance of various AD benefits.
Table 2. Summary of survey responses to Likert-scale questions on the importance of various AD benefits.
CategoryAll ResponsesLikely AdoptersPossible AdoptersNon-Adoptersap-Value
To improve farm profitability1.49 ± 0.691.34 ± 0.551.48 ± 0681.76 ± 0.900.0628
To reduce greenhouse gas emissions1.92 ± 0.911.82 ± 0.851.93 ± 0.812.17 ± 1.270.3028
To add another revenue stream1.57 ± 0.641.48 ± 0.571.57 ± 0.631.82 ± 0.870.1626
To reduce farm pollution1.80 ± 0.621.69 ± 0.591.82 ± 0.392.09 ± 1.040.0959
To reduce farm business costs1.67 ± 0.731.61 ± 0.611.63 ± 0.612.00 ± 1.250.1248
ap-value results for t-test comparisons between Non-adopters and other adopter types.
Table 3. Summary of survey responses to Likert-scale questions on the importance of potential AD obstacles.
Table 3. Summary of survey responses to Likert-scale questions on the importance of potential AD obstacles.
CategoryAll ResponsesLikely AdoptersPossible AdoptersNon-Adoptersap-Value
I do not have enough information1.75 ± 0.901.78 ± 1.011.42 ± 0.52.5 ± 1.000.0012
Investment costs are too high1.89 ± 0.831.84 ± 0.851.97 ± 0.871.86 ± 0.770.8581
It would be too difficult to operate3.05 ± 0.903.25 ± 0.842.96 ± 0.892.77 ± 1.010.2205
The financial returns seem uncertain2.19 ± 0.912.17 ± 0.872.35 ± 0.891.93 ± 1.000.2376
I do not believe the technology has been proven3.22 ± 0.983.14 ± 1.193.44 ± 0.822.91 ± 0.540.2567
My rental agreement would not allow it3.4 ± 0.903.33 ± 0.763.5 ± 0.953.25 ± 1.160.6230
It would be difficult to gain planning permission2.71 ± 0.962.77 ± 1.032.52 ± 1.013.00 ± 0.60.2477
ap-value results for t-test comparisons between Non-adopters and other adopter types.
Table 4. Estimated feedstock availability and annual methane potential from “Likely Adopters” of AD.
Table 4. Estimated feedstock availability and annual methane potential from “Likely Adopters” of AD.
Dairy FarmsBeef FarmsMixed Cattle FarmsTotal Farms
Number of livestock (animals)168440122944379
Fresh weight slurry yield (t year−1)14,276339919,44737,122
Methane yield (m3 year−1)228,41254,390311,150593,952
Potential electricity production via CHP (kWh year−1)838,969199,7781,142,8722,181,619
CO2 savings (t CO2-eq. year−1)307.9073.32419.43800.65
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O’Connor, S.; Ehimen, E.; Pillai, S.C.; Power, N.; Lyons, G.A.; Bartlett, J. An Investigation of the Potential Adoption of Anaerobic Digestion for Energy Production in Irish Farms. Environments 2021, 8, 8. https://0-doi-org.brum.beds.ac.uk/10.3390/environments8020008

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O’Connor S, Ehimen E, Pillai SC, Power N, Lyons GA, Bartlett J. An Investigation of the Potential Adoption of Anaerobic Digestion for Energy Production in Irish Farms. Environments. 2021; 8(2):8. https://0-doi-org.brum.beds.ac.uk/10.3390/environments8020008

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O’Connor, Sean, Ehiaze Ehimen, Suresh C. Pillai, Niamh Power, Gary A. Lyons, and John Bartlett. 2021. "An Investigation of the Potential Adoption of Anaerobic Digestion for Energy Production in Irish Farms" Environments 8, no. 2: 8. https://0-doi-org.brum.beds.ac.uk/10.3390/environments8020008

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