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. 2020 Aug 12;68(39):10456–10488. doi: 10.1021/acs.jafc.0c02894

Table 5. Overview of Biodegradation Studies on HILsa.

anion cation biodegradation ref
MCPA tebuconazole OECD 301 F test: cation, 88 ± 4%; anion, 0 ± 0% (40)
MCPA propiconazole OECD 301 F test: cation, 58 ± 3%; anion, 3 ± 0% (40)
MCPA tetraalkylammonium BOD5/COD ratio (t = 0–360 min, 0.4 = limit of biodegradability): electrochemical oxidation process, 0.25–0.35; electro-Fenton process, 0.35–0.65 (49)
MCPA tetraalkylammonium electrochemically treated, 28–57%; nontreated, 0–8% (50)
MCPA betainium OECD 301 F test, 69% (61)
MCPA N-alkylbetainium OECD 301 F test, 59–62% (45)
MCPA carnitinium OECD 301 F test, 59% (61)
MCPA acetylcholine OECD 301 F test, 80% (62)
MCPA [2-(methacryloyloxy)-ethyl]trimethylammonium, [2-(acryloyloxy)-ethyl]trimethylammonium OECD 301 F test, 29–37% (63)
MCPA dialkanoyloxyethyl-dimethylammonium OECD 301 F test, 63% (63)
2,4-D tebuconazole OECD 301 F test: cation, 94 ± 3%; anion, 0 ± 0% (40)
2,4-D propiconazole OECD 301 F test: cation, 65 ± 3%; anion, 0 ± 1% (40)
2,4-D betainium OECD 301 F test, 87% (61)
2,4-D N-alkylbetainium OECD 301 F test, 72–73% (45)
2,4-D carnitinium OECD 301 F test, 76% (61)
2,4-D acetylcholine OECD 301 F test, 70% (62)
2,4-D 4,4-dialkylmorpholinium OECD 301 F test with microbiota isolated from different environmental niches: river sludge, 9–10%; garden soil, 13–19%; agricultural runoff stream, 18–25%; agricultural soil, 14–24%; waste repository, 20–31% (73)
2,4-D 4,4-dialkylmorpholinium Primary biodegradation for microbiota isolated from different environmental niches: river sludge, cation 52–58%, anion 9–11%; garden soil, cation 74–77%, anion 25–31%; agricultural runoff stream, cation 87–90%, anion 60–61%; agricultural soil, cation 88–92%, anion 60%; waste repository, cation 91–94%, anion 51–55% (73)
MCPP tebuconazole OECD 301 F test: cation, 89 ± 4%; anion, 0 ± 1% (40)
MCPP propiconazole OECD 301 F test: cation, 68 ± 3%; anion, 0.5 ± 0% (40)
MCPP betainium OECD 301 F test, 57% (61)
MCPP N-alkylbetainium OECD 301 F test, 51–55% (45)
MCPP carnitinium OECD 301 F test, 49% (61)
dicamba tebuconazole OECD 301 F test: cation, 100 ± 5%; anion, 44 ± 2% (40)
dicamba propiconazole OECD 301 F test: cation, 56 ± 2%; anion, 40 ± 2% (40)
dicamba N-alkylbetainium OECD 301 F test, 42–47% (45)
dicamba acetylcholine OECD 301 F test, 90% (62)
dicamba 4,4-dialkylmorpholinium OECD 301 F test with microbiota isolated from different environmental niches: river sludge, 0%; garden soil, 0–1%; agricultural runoff stream, 1–2%; agricultural soil, 2%; waste repository, 2% (73)
dicamba 4,4-dialkylmorpholinium Primary biodegradation for microbiota isolated from different environmental niches: river sludge, cation 38–55%, anion 0%; garden soil, cation 56–77%, anion 0%; agricultural runoff stream, cation 77–81%, anion 32%; agricultural soil, cation 75–79%, anion 29–35%; waste repository, cation 83–86%, anion 34–36%  
pelargonate tetraalkylammonium OECD 301 F test, 0–83% (33)
pelargonate alkylbis(n-ethoxylated) methylammonium OECD 301 F test, 68% (33)
pelargonate N-alkylbetainium OECD 301 F test, 85% (33)
pelargonate dialkanoyloxyethyl-dimethylammonium OECD 301 F test, 52% (33)
MCPA/dicamba (oligomeric) alkylbis(n-ethoxylated) methylammonium OECD 301 F test, 0–6.6% (43)
MCPA/dicamba (oligomeric) betainium OECD 301 F test, 65–66% (61)
MCPA/glyphosate (oligomeric) tetraalkylammonium OECD 301 F test, 0% (42)
MCPA/glyphosate (oligomeric) alkylbis(n-ethoxylated) methylammonium OECD 301 F test, 0% (42)
MCPA/glyphosate (DSHIL) tetraalkylammonium OECD 301 F test, 0% (42)
MCPA/glyphosate (DSHIL) alkylbis(n-ethoxylated) methylammonium OECD 301 F test, 0% (42)
dicamba/glyphosate (DSHIL) tetraalkylammonium OECD 301 F test, 0% (42)
dicamba/glyphosate (DSHIL) tetraalkylphosphonium OECD 301 F test, 0% (42)
dicamba/glyphosate (DSHIL) alkylbis(n-ethoxylated) methylammonium OECD 301 F test, 0% (42)
a

Table does not include salts with melting points greater than 100 °C.