1. Introduction
Methane (CH
4) is a major contributor to global climate change [
1]. About 40% of greenhouse gas emissions from livestock production can be attributed to ruminant CH
4 production, which accounts for approximately 6% of global anthropogenic greenhouse gas emissions [
2]. Ruminal CH
4 production does not only concern greenhouse gas emissions, but also relates to energy loss for ruminants (up to 12% of the total energy intake) [
3]. The rumen is rich in bacteria, protozoa, fungi and methanogens, which can ferment coarse feedstuffs to produce volatile fatty acids, carbon dioxide and CH
4. Hydrogen (H
2) is an important intermediate in most of those biochemical processes [
4]. CH
4 is generally produced through the utilization of CO
2 and H
2 by methanogenic archaea in the rumen [
5]. The accumulation of H
2 could affect the normal rumen fermentation, therefore, CH
4 generation plays an important role in H
2 elimination in the rumen.
Strategies like the use of feed additives, nutrition management and animal genetic improvement have been proposed for use in reducing CH
4 emissions from ruminants [
6,
7,
8]. Chemicals such as sulfate, nitrate and fumarate were studied for their potential to reduce rumen CH
4 emissions [
9,
10,
11]. The CH
4 inhibitor 3-nitrooxypropanol [
12,
13] and the macroalga
Asparagopsis taxiformis [
14,
15] were recently developed as promising rumen CH
4-mitigating agents. However, the inhibition of methanogenic activity usually results in abnormal rumen fermentation caused by H
2 accumulation. Therefore, it is necessary to devise an alternative means of eliminating H
2 when inhibiting the activity of methanogens. Fumarate is a metabolic intermediate and can be reduced to succinate by H
2 in the rumen. Succinate is then decarboxylated into propionate, which is a major energy source for ruminants [
16]. Fumarate is a promising H
2-comsuming chemical in the rumen. Nitroglycerin, targeting methanogens, has the same functional group as the chemical 3-nitrooxypropanol, which was reported as being an effective means of reducing ruminal CH
4 emissions in in vitro and in vivo studies [
17,
18]. Its metabolic end products are propionate and ammonia in the rumen.
This study hypothesized that fumarate would alleviate the abnormal rumen fermentation when methanogenesis was inhibited by nitroglycerin. The objective of this study was to investigate the effects of fumarate and nitroglycerin on rumen fermentation, CH4 and H2 production and microbiota in an in vitro rumen trial. The results of this study could help to develop an alternative means of mitigating rumen CH4 emissions.
2. Materials and Methods
2.1. Animals
Three rumen-fistulated Chinese Hu sheep were fed on a maintenance diet for a period of 30 days. On day 31, 500 mL of rumen fluid was collected 2 h before the sheep were fed. The diet of the 3 sheep was prepared in accordance with the maintenance requirements (NY/Y 816-2004; Ministry of Agriculture of China, 2004), including 70% Chinese wild rye, 20% corn, 7% soybean meal, 1.5% CaHPO4, 0.5% stone powder, 0.5% NaCl and 0.5% additives (Vitamin and mineral mix contained the following ingredients per kilogram of diet: vitamin A, 22.5 KIU/kg; vitamin D3, 5.0 KIU/kg; vitamin E, 37.5 IU/kg; vitamin K3, 5.0 mg/kg; Mn, 63.5 mg/kg; Zn, 111.9 mg/kg; Cu, 25.6 mg/kg; and Fe, 159.3 mg/kg), and comprised 94.01% dry matter, 10.01% crude protein, 2.39% ether extract, 51.48% neural detergent fiber, 30.94% acid detergent fiber and 7.73% crude ash on a dry-matter basis. Sheep were fed a total mixed ration twice daily (08:00 and 17:00) and had free access to fresh water.
2.2. Experimental Design
In vitro rumen fermentation was carried out with a completely randomized design (CRD) for 4 treatments: control (CON), fumarate at 12 mmol/L (FA), nitroglycerin at 99 μmol/L (NG) and fumarate at 12 mmol/L plus nitroglycerin at 99 μmol/L (FN). The dosages of FN and NG used in this study were determined according to previous studies [
19,
20] and the results of the pre-experiments. Three replicates were prepared for each treatment. Additionally, three independent incubation runs were performed at different times [
21]. Each run consisted of 4 treatments with 3 replicates and 4 blanks containing only the inoculum. The experimental procedure was conducted according to the study of Martínez-Fernández et al. [
22]. The rumen fluid was collected from 3 Hu sheep before the morning feeding was performed, and this fluid was then pooled and filtered through 4 layers of cheesecloth. The filtered rumen fluid and buffer were mixed thoroughly (1:3 [
vol/
vol]) in a water bath at 39 °C under anaerobic conditions. Additionally, each 100 mL of the mixture was dispensed into a 180 mL serum bottle containing 1.0 g substrate and chemicals (fumarate or nitroglycerin). All serum bottles were sealed and incubated at 39 °C for 24 h at 80 rpm. After 24 h of incubation, all the fermentation flasks were taken out and put into ice water to terminate the fermentation. Samples were collected and stored for subsequent analysis. The buffer was composed of 8.75 g NaHCO
3, 1.00 g NH
4HCO
3, 1.43 g Na
2HPO
4, 1.55 g KH
2PO
4, 0.15 g MgSO
4·7H
2O, 0.52 g Na
2S, 0.017 g CaCl
2·2H
2O, 0.015 g MnCl
2·4H
2O, 0.002 g CoCl
2·6H
2O, 0.012 g FeCl
3·6H
2O and 1.25 mg resazurin per liter [
23]. The composition of the substrate was the same as the diet provided to sheep. The substrate was dried at 65 °C for 48 h and passed through a 1 mm screen with a Wiley mill (Arthur H. Thomas, Philadelphia, PA, USA). The fumarate (disodium fumarate) was purchased from Shanghai Macklin Biochemical Co., Ltd. (Shanghai, China). Nitroglycerin was purchased from Beijing Yimin Pharmaceutical Co., Ltd. (Beijing, China).
2.3. Sample Collection and Chemical Analysis
At the end of the fermentation, the pH value was measured using a pH meter (Ecoscan pH 5, Thermo Fisher Scientific Inc., Singapore). Then, the bottles were immediately put into ice water to stop fermentation. The supernatant of the fermentation fluid was collected and stored at −20 °C for the determination of volatile fatty acids (VFAs), lactate, microbial crude protein (MCP) and ammonia nitrogen (NH3-N). The mixture of the substrate and fermentation fluid was collected and stored at −80 °C for the analysis of the microbiota.
2.4. Sample Collection and Chemical Analysis
Gas production was assessed using a pressure transducer [
24]. Methane (CH
4) and hydrogen (H
2) production were measured following the gas measurement procedure using a GC-TCD instrument (Agilent 7890B, Agilent Technologies Inc., Santa Clara, CA, USA). Gases were separated on packed GC columns (Porapak Q packing & MolSieve 5A packing, Agilent Technologies Inc., CA, USA) at a column temperature of 80 °C, a 200 °C injection temperature and a 200 °C TCD detector temperature. N
2 was the carrier gas. The VFAs were determined according to Jin et al. [
17]. Each 1.0 mL sample was mixed with 0.2 mL deproteinization–acidification solution [metaphosphoric acid (25%
w/
v) and crotonic acid (0.65%
w/
v)] before undergoing analysis via gas chromatography (Agilent 7890B instrument, Agilent Technologies Inc., CA, USA). The sample was separated using a fused silica capillary column (Supelco, Bellefonte, PA, USA) with a programmed heating process (110 °C for 3 min, 110–150 (40 °C/min)). The injection temperature was 200 °C. The flame ionization detector temperature was 220 °C. The carrier gas was nitrogen. Lactate was measured using an assay kit in accordance with the instructions of the manufacturer (Jiancheng Bioengineering Research Institute, Nanjing, China). Microbial crude protein was determined with a commercial reagent kit (BCA Protein Assay Kit, Tiandz Inc., Beijing, China) in accordance with manufacturer instructions. The concentration of NH
3-N was analyzed using an indophenol method with an acidified procedure [
25].
2.5. DNA Extraction and Real-Time PCR
Genomic DNA was extracted from a 1.0 mL sample using a bead-beating and phenol-chloroform–isopentanol extraction method [
26]. Each DNA sample was divided into two parts to perform sequencing and real-time PCR.
Archaea, bacteria, anaerobic fungi and protozoa were quantified using an Applied Biosystems 7300 Real time PCR system (Applied Biosystems, Thermo Fisher Scientific Inc., Foster City, CA, USA). The primers for the 4 microbial populations are listed in
Table A1. An SYBR
® Premix Ex Tag TM (TaKaRa, Dalian, China) was used to prepare the reaction mixture. The copy number of DNA in each sample was measured in triplicate, and the average value was calculated. The external standards were prepared with plasmid DNA of clones of each microbial population. The results are expressed as the number of copies of marker genes per milliliter of fermentation liquid.
2.6. 16S rRNA Gene Sequencing and Data Analysis
The 16S rRNA genes of bacteria were amplified with a primer pair 341F (5′-CCTAYGGGRBGCASCAG-3′) and 806R (5′-GGACTACNNGGGTATCTAAT-3′). The 16S rRNA genes of archaea were amplified with a primer pair Met86F (5′-GCTCAGTAACACGTGG-3′) and Met471R (5′-GWRTTACCGCGGCKGCTG-3′). The amplicons were subjected to double-ended sequencing (paired sequencing) using an Illumina MiSeq PE250 platform produced by BIOZERON Biotechnology Co., Ltd. (Shanghai, China). The raw data were stored in the Sequence Read Archive (SRA) database of the National Biotechnology Information Center (NCBI) (accession number: PRJNA913631, bacteria; PRJNA913641, archaea).
Fastp (version 0.20.0) and FLASH (version 1.2.7) were used to filter and merge 16S rRNA sequences, and the chimeras were filtered to obtain effective reads [
27]. UPARSE (version 7.1) was used to pick up the operational taxonomic unit (OTU) with a 97% similarity truncation value [
28]. Taxonomic assignment was performed for bacteria using RDP classifier (version 2.11) based on the SILVA database (version 138), and via the RIM-DB database for methanogens [
18]. QIIME 2 was used for alpha diversity analysis. The principal coordinate analysis (PCoA) was conducted based on Bray–Curtis distance [
29]. The significance of the differences among groups was assessed with ANOSIM using the vegan package in R.
2.7. Statistical Analysis
The analyses of the in vitro fermentation parameters and the real-time PCR data were performed using the MIXED procedure of SAS 9.4 version (SAS Institute, Inc., Cary, NC, USA), and the data were tested to determine their normality using the Shapiro–Wilk test of SAS. The model used for data analysis was Yijk = μ + Pi + Sj + PSij + eij, where Yijk is the observed value, μ is the overall mean, Pi is the fixed effect of treatment with nitroglycerin, Sj is the fixed effect of treatment with fumarate, PSij is the interaction effect of nitroglycerin * fumarate and eij is the random error. The variables that had non-normal distributions were analyzed using the Kruskal–Wallis test procedure. The Tukey test was used to identify differences (p < 0.05) between means.
4. Discussion
The inhibition of methanogenic activities usually results in H
2 accumulation and causes depressed rumen fermentation [
30]. This can affect the animal production performance. The results of this study showed that the addition of fumarate alleviated H
2 accumulation and improved the depressed rumen fermentation parameters when methanogenesis was inhibited by nitroglycerin. Nitroglycerin was demonstrated to be effective at reducing rumen methane production in several in vitro and in vivo studies [
17,
18,
20]. It was able to completely inhibit methane production and caused an accumulation of hydrogen in in vitro rumen fermentation [
17,
20]. Moreover, the final metabolites of nitroglycerin were propionate and ammonia in the rumen, which have no negative effect on rumen fermentation. Therefore, nitroglycerin was used to successfully establish a model of methane depression and hydrogen accumulation in this study. Nitroglycerin caused about 4.8% hydrogen of accumulation (% total gas production). The current experiment also observed that nitroglycerin inhibited methane production, but did not affect the abundance of archaea compared with the control. This result is consistent with that of a previous study [
20]. In another study, an opposite result was observed, whereby the abundance of archaea declined when the methane production was depressed by nitroglycerin [
17], which was consistent with the research on the other methanogenic inhibitors [
31,
32]. However, the mechanisms of the different results for archaeal abundance in different studies are unclear and further work is needed to elucidate this point.
Fumarate is an intermediate in the rumen metabolism and is finally reduced to propionate [
33]. The reduction of fumarate has a lower H
2-consuming threshold (0.02 ppm) and produces more Gibbs free energy than the methanogenesis of H
2 and CO
2. The fumarate reduction should be more effective than methanogenesis in the rumen [
34,
35,
36]. Therefore, fumarate was used as a rumen CH
4-mitigation agent in many previous studies [
37,
38,
39]. However, the effects of fumarate on rumen CH
4 mitigation were found to be inconsistent. Bayaru et al. [
37] observed that CH
4 production in steers was reduced by 23% when fumarate was added to the complete diet at 20 g/kg dry matter. In contrast, no effect was observed in steers fed barley silage and concentrate with fumarate (12 g/kg dry matter) [
38] and in lambs fed dried alfalfa with fumarate (100 g/kg dry matter) [
39]. Fumarate increased CH
4 production in sheep fed a mixed diet [
19], which is consistent with the current study. Fumarate increased the abundance of archaea, methane production and acetate with the absence of nitroglycerin. Fumarate was expected to consume H
2 and reduce methane production; the increase in methane production was not expected. Fumarate can be metabolized into acetate via the malate–pyruvate pathway in the rumen [
19]. In this process, there is net [H] produced (C
4H
4O
4 + 2H
2O→C
2H
4O
2 + 2CO
2 + 4H), which could account for the increase in the abundance of archaea and methane production. The increased concentration of acetate supported this speculation. Moreover, Gibbs free energy calculation shows that the production of acetate from fumarate under rumen conditions is thermodynamically feasible even at very low fumarate concentrations [
35]. Fumarate was metabolized into acetate instead of propionate, which could have occurred as the microbial populations that reduce fumarate to succinate/propionate had not yet been completely established. It may also give an explanation for the inconsistent results obtained in different studies on fumarate.
Fumarate and nitroglycerin altered the relative abundance of Bacteroides and Firmicutes as well as
Streptococcus and several unclassified genera to the two phyla. The relative abundance of
Streptococcus was increased by nitroglycerin, but restored to the level of that in CON by the addition of fumarate. The underlying mechanism of the changes in
Streptococcus is unclear. However,
Streptococcus had been reported to produce bacteriocin, which could inhibit methane production [
40].
Succinivibrio, belonging to Proteobaceria, produces succinate [
41]. The relative abundance of
Succinivibrio was decreased by the combination of fumarate and nitroglycerin. Mao et al. [
42] reported that the relative abundance of
Succinivibrio dextrinisolvens was increased in the rumen of goats fed disodium fumarate. It seems that the combination of the two chemicals had an opposite impact on
Succinivibrio.
Treponema, belonging to Spirochaetae, produces succinate, formate and acetate [
43]. The relative abundance of
Treponema was restored by the addition of fumarate. Jin et al. [
44] observed an increase in
Treponema due to disodium fumarate in an in vitro rumen fermentation. Therefore,
Treponema might play a role in the restoration of the propionate concentration in FN.
Ruminobacter, belonging to Proteobacteria, is associated with ruminal fiber degradation [
45]. Nitroglycerin decreased the proportion of
Ruminobacter, suggesting the inhibition of fiber degradation. It might be partly related to the decrease in acetate concentration caused by nitroglycerin.
Bifidobacteria, belonging to the phylum of Actinobacteria, were known fermenters of starch and simple sugars [
46]. The addition of nitroglycerin increased the relative abundance of
Bifidobacteria, but fumarate restored it. The mechanism underlying the changes in
Bifidobacteria is unclear.
The most dominant methanogens belonged to Methanobacteriales and Methanomassiliicoccales, which was consistent with the results of previous studies [
17,
18]. Fumarate decreased the relative abundance of Methanobacteriales and increased that of Methanomassiliicoccales. Members of the Methanobacteriales primarily use H
2 and CO
2 to produce CH
4, which generates lower amounts of Gibbs free energy and has a higher H
2-utilizing threshold than fumarate reduction [
35]. The fumarate reduction might have decreased the H
2 concentration, which depressed the growth of Methanobacteriales. Members of the Methanomassiliicoccales are H
2-dependent methyltrophic methanogens which produce more Gibbs free energy and have a lower H
2-utilizing threshold than Methanobacteriales. Moreover, the repair system of Methanomassiliicoccales seems to be more resilient than that of Methanobacteriales in the presence of nitroglycerin [
47]. This might explain the changes in the relative abundance in the two methanogenic orders.