PMID-sentid	Pub_year	Sent_text		comp_official_name	comp_offsetprotein_name	organism	prot_offset
21327803-11	2011	RDX biodegradation activity by the T7 isolate was inhibited in the presence of nitrate or ammonium concentrations above 1.6 and 5.5 mM, respectively (100 mg l(-1)) while the T9N isolate"s activity was retarded only by ammonium concentrations above 5.5 mM.	Nitrates	79-86	radixin	Homo sapiens	0-3	
28442008-0	2017	Biotransformation of RDX and HMX by Anaerobic Granular Sludge with Enriched Sulfate and Nitrate.	Nitrates	88-95	radixin	Homo sapiens	21-24	
28442008-2	2017	The present study investigated the biotransformation of RDX and HMX by anaerobic granular sludge under sulfate- and nitrate-enriched conditions.	Nitrates	116-123	radixin	Homo sapiens	56-59	
28442008-3	2017	The results showed that RDX and HMX could be transformed by anaerobic granular sludge when nitrate was present.	Nitrates	91-98	radixin	Homo sapiens	24-27	
28442008-4	2017	However, the biotransformation of RDX and HMX was negatively influenced, especially with high nitrate concentrations.	Nitrates	94-101	radixin	Homo sapiens	34-37	
28442008-6	2017	The removal of RDX and HMX under both nitrate- and sulfate-enriched conditions was facilitated by the use of glucose as additional substrate.	Nitrates	38-45	radixin	Homo sapiens	15-18	
23215531-2	2013	The detection of vapors from the low volatility explosive compound RDX was achieved through selective atmospheric pressure chemical ionization using nitrate reactant ions (NO(3)(-)) and NO(3)(-) HNO(3) adducts generated in an electrical discharge source.	Nitrates	149-156	radixin	Homo sapiens	67-70	
23215531-6	2013	Recorded signals were observed for RDX concentrations below 25 ppq using selected ion monitoring (SIM) of the RDX-nitrate adduct at m/z 284.	Nitrates	114-121	radixin	Homo sapiens	35-38	
23215531-6	2013	Recorded signals were observed for RDX concentrations below 25 ppq using selected ion monitoring (SIM) of the RDX-nitrate adduct at m/z 284.	Nitrates	114-121	radixin	Homo sapiens	110-113	
21327803-13	2011	RDX-degrading activity by the Rhodococcus species isolate T9N may have important implications for the bioremediation of nitrate-rich RDX-contaminated aquifers.	Nitrates	120-127	radixin	Homo sapiens	0-3	
21327803-13	2011	RDX-degrading activity by the Rhodococcus species isolate T9N may have important implications for the bioremediation of nitrate-rich RDX-contaminated aquifers.	Nitrates	120-127	radixin	Homo sapiens	133-136	
12153019-9	2002	The presence of nitrate reversibly halted RDX metabolism, whereas ammonium had no discernible effect, which implies that: (i) nitrate, which commonly occurs in RDX-contaminated groundwater, may inhibit in situ RDX metabolism, and (ii) although RDX may act as both a nitrogen source and cometabolic electron sink, the latter role predominates, as RDX reduction will proceed regardless of whether or not a more favorable nitrogen source is present.	Nitrates	16-23	radixin	Homo sapiens	42-45	
18499297-9	2008	Dissolved RDX samples were degraded in the laboratory and results showed that all reproduced degradation processes released nitrate with a strong fractionation.	Nitrates	124-131	radixin	Homo sapiens	10-13	
18499297-10	2008	Laboratory isotopic values for RDX-derived NO(3)(-) produced a trend of high delta(18)O-low delta(15)N to low delta(18)O-high delta(15)N, and groundwater samples with nitrate concentrations above the expected background level appeared along this trend.	Nitrates	167-174	radixin	Homo sapiens	31-34	
18499297-11	2008	Our results thus point toward a characteristic field of isotopic ratios for nitrate being derived from the degradation of RDX.	Nitrates	76-83	radixin	Homo sapiens	122-125	
12153019-9	2002	The presence of nitrate reversibly halted RDX metabolism, whereas ammonium had no discernible effect, which implies that: (i) nitrate, which commonly occurs in RDX-contaminated groundwater, may inhibit in situ RDX metabolism, and (ii) although RDX may act as both a nitrogen source and cometabolic electron sink, the latter role predominates, as RDX reduction will proceed regardless of whether or not a more favorable nitrogen source is present.	Nitrates	126-133	radixin	Homo sapiens	160-163	
12153019-9	2002	The presence of nitrate reversibly halted RDX metabolism, whereas ammonium had no discernible effect, which implies that: (i) nitrate, which commonly occurs in RDX-contaminated groundwater, may inhibit in situ RDX metabolism, and (ii) although RDX may act as both a nitrogen source and cometabolic electron sink, the latter role predominates, as RDX reduction will proceed regardless of whether or not a more favorable nitrogen source is present.	Nitrates	126-133	radixin	Homo sapiens	160-163	
12153019-9	2002	The presence of nitrate reversibly halted RDX metabolism, whereas ammonium had no discernible effect, which implies that: (i) nitrate, which commonly occurs in RDX-contaminated groundwater, may inhibit in situ RDX metabolism, and (ii) although RDX may act as both a nitrogen source and cometabolic electron sink, the latter role predominates, as RDX reduction will proceed regardless of whether or not a more favorable nitrogen source is present.	Nitrates	126-133	radixin	Homo sapiens	160-163	
12153019-9	2002	The presence of nitrate reversibly halted RDX metabolism, whereas ammonium had no discernible effect, which implies that: (i) nitrate, which commonly occurs in RDX-contaminated groundwater, may inhibit in situ RDX metabolism, and (ii) although RDX may act as both a nitrogen source and cometabolic electron sink, the latter role predominates, as RDX reduction will proceed regardless of whether or not a more favorable nitrogen source is present.	Nitrates	126-133	radixin	Homo sapiens	42-45	
12153019-9	2002	The presence of nitrate reversibly halted RDX metabolism, whereas ammonium had no discernible effect, which implies that: (i) nitrate, which commonly occurs in RDX-contaminated groundwater, may inhibit in situ RDX metabolism, and (ii) although RDX may act as both a nitrogen source and cometabolic electron sink, the latter role predominates, as RDX reduction will proceed regardless of whether or not a more favorable nitrogen source is present.	Nitrates	126-133	radixin	Homo sapiens	160-163	
35065174-0	2022	Enhanced bioremediation of RDX and Co-Contaminants perchlorate and nitrate using an anaerobic dehalogenating consortium in a fractured rock aquifer.	Nitrates	67-74	radixin	Homo sapiens	27-30	
35065174-2	2022	Bioremediation of RDX is feasible through biostimulation of native microbes with an organic carbon donor but may be less efficient, or not occur at all, in the presence of the common co-contaminants perchlorate and nitrate.	Nitrates	215-222	radixin	Homo sapiens	18-21	
35065174-7	2022	In microcosms with groundwater containing perchlorate and nitrate, RDX degradation began without delay when bioaugmented with 10% WBC-2.	Nitrates	58-65	radixin	Homo sapiens	67-70	
16345884-6	1981	Anaerobic treatment of RDX wastewaters, which also contain high nitrate levels, would permit the denitrification to occur, with concurrent degradation of RDX ultimately to a mixture of hydrazines and methanol.	Nitrates	64-71	radixin	Homo sapiens	23-26	
8632501-1	1996	BACKGROUND: Hexogen (cyclonite, RDX) nitrate explosive is an infrequent cause of poisoning.	Nitrates	37-44	radixin	Homo sapiens	32-35