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. 2024 Jun 19;29(12):2910. doi: 10.3390/molecules29122910

Table 2.

Recent studies presenting the degradation of antimicrobial agents using CAPP-based methods.

CAPP System Operational Conditions * Target Antibiotic Removal Efficacy (%) Degradation Products Ion Masses (m/z) Reference
Nanosecond pulsed DBD reactor CV = 26.6 kV, f = 200 Hz,
A = ambient air, 1 L min−1,
DP = 0.93 W, V = 8.5 mL, T = 20 min, stationary system
Enrofloxacin in water,
40 mg L−1
100 374, 356, 311, 243, 315, 362, 193, 293 [83]
Nanosecond pulsed DBD reactor CV = 17.4 kV, f = 200 Hz,
A = ambient air, 1.0 L mins−1,
DP = 1.21 W, T = 3 min, stationary system
Ciprofloxacin in soil,
200 mg kg−1
99 412 (α-hydroperoxy amide and dihydroxy subset) [84]
DBD reactor
(with or without FeMn/activated carbon catalyst)
CV = 8.5 kV, A = ambient air, 3 L min−1, V = 500 mL, T = 15 min, stationary system Tetracycline hydrochloride in wastewater, 50 mg L−1 73.4 (DBD alone),
98.8 (DBD/Fe-Mn/activated carbon)
461, 477, 448, 496, 416, 480, 405, 306, 274 [85]
DBD reactor CV = 36.5 kV, SFR = 4 L min−1,
T = 31 min, semi-flowing system
Amoxicillin in wastewater, 27.8–31.6 mg L−1 98.1 Several degradation pathways proposed (theoretical modelling) [87]
DBD reactor f = 600 Hz, A = air or oxygen, DP = 12.9 W, V = 100 mL, T = 40 min, circulating system Amoxicillin, 100 mg L−1
sulfamethazole, 80 mg L−1
in water
100 NA [92]
DBD reactor DP = 8.9 W, f = 60 Hz, A = dry air, V = 1000 mL, T = 20 min, stationary system Lincomycin,
ciprofloxacin,
enrofloxacin,
chlortetracycline,
oxytetracycline,
sulfathiazole,
sulfamethoxazole,
sulfamethazine,
trimethoprim,
in wastewater, 5 mg L−1
100 NA [93]
DBD reactor CV = 10 kV, A = ambient air,
1 L min−1, stationary system
Oxytetracycline in wastewater, 100 mg L−1 93.6 476.4, 432.3, 388.3, 340.3, 288.3, 239.3 [94]
Pulsed DBD reactor with falling film CV = 22 kV, f = 100 Hz,
A = ambient air, 3.5 L min−1,
SFR = 0.5 L min−1, T = 30 min, circulating system
Tetracycline in water,
50 mg L−1
92.3 416, 428, 461, 477, 384, 224
DBD reactor CV = 20 kV, f = 9.22 kHz,
I = 1.05 A, V = 200 mL, SFR = 2 L min−1, A = ambient air, 3 L min−1,
DP = 95.2 W, T = 20 min,
circulating system
Tetracycline in water,
200 mg L−1
96.5 416.1, 418.1, 303.1, 365.1, 406.1 [96]
DBD reactor DP = 90 W, f = 9.1 Hz,
A = atmospheric air, V = 20 mL,
T = 5 min, stationary system
Chloramphenicol, 30 mg L−1,
furazolidone, 30 mg L−1,
either in water or wastewater
Both 99.0 Amino-functionalized moieties of antibiotics [110]
Pulsed CD reactor SFR = 4.5 L min−1, DP = 60 W,
T = 24 min, circulating system
Sulfamethizole in water,
50 mg L−1
100 OH-sulfamethizole,
3 OH-sulfamethizole,
4 OH-sulfamethizole, carboxy-sulfamethizole
[99]
CD above surface1,
air bubbling CD2
CV = 3 kV, f = 5 kHz, I = 3 mA,
A = ambient air, 1 L min−1,
V = 50 mL, T1 = 90 min, T2 = 20 min, stationary system
Oxytetracycline hydrochloride, 50 mg L−1,
doxycycline hyclate, 50 mg L−1, in water
70 (coxytetracycline1)
97 (doxycycline1)
100 (oxytetracycline2)
100 (doxycycline2)
NA [101]
Pulsed CD reactor CV = 22 kV, I = 180 A,
SFR = 4.5 L min−1, circulating system
Amoxicillin, doxycycline, in water, 50 mg L−1 both 100 OH-amoxicillin, amoxicillin penicilloic acid
OH-doxycycline and
2-OH-doxycycline
[100]
Nanosecond pulsed CD CV = 30 kV, f = 150 Hz,
A = argon or air, 200 mL min−1, DP = 1.03 W, V = 15 mL, T = 50 min, stationary system
Trimethoprim in water,
40 mg L−1
94.6 short-chain carboxylic acids, CO2, H2O, NH4+, NO3 [102]
Air bubbling CD CV = 8 kV, f = 8 kHz,
A = ambient air, 0.5 L min−1,
V = 40 mL, T = 50 min, stationary system
Amoxicillin in water, 1 mg L−1 99.9 CO, CO2, H2O, diketopiperazine
366, 349, 196, 147, 79, 115, 90, 60
[103]
Pulsed CD with natural soil particles f = 75 Hz,
A = air, 6.0 L min−1,
V = 300 mL, T = 10 min, circulating system
Tetracycline in wastewater,
50 mg L−1
59.30 for black soil particles 444, 461, 416, 400, 274, 238, 209, 149 [104]
CD reactor CV = 30 kV, A = ambient air,
4 L min−1, V = 600 mL, T = 15 min, stationary system
Ofloxacin, 41.2 mg L−1,
ciprofloxacin, 1.0 mg L−1,
cefuroxime, 0.3 mg L−1,
amoxicillin, 23.6 mg L−1,
in wastewater
72.1
99.6
99.2
75.8
NA [86]
Argon APPJ f = 670 Hz, DP = 32.6 W,
A = argon, 2.5 L h−1, V = 30 mL,
T = 24 min, stationary system
Ciprofloxacin in wastewater, 10 mg L−1 93.4 363, 307, 263, 261, 347, 288 [106]
pm-rf-APGD f = 50 kHz, A = ambient air
SFR = 2.8 mL min−1, continuous flow system
Doxycycline in water,
51.5 mg L−1
79.0 417.1649, 461.1541 [108]
pm-rf-APGD f = 2300 Hz, duty cycle = 30%,
A = ambient air,
SFR = 3.0 mL min−1, continuous flow system
Bisphenol A,
bisphenol S,
dexamethasone, benzophenone,
2-nitrophenol,
17-alpha-ethinylestradiol, dapsone,
in the 7-component mixture in water, 1 mg mL−1
58.8
28.2
28.5
74.5
61.7
71.5
92.8
NA [109]
dc-APGD CV = 1200 V, I = 30 mA, A = ambient air, SFR = 3.0 min−1, continuous flow system Bisphenol A,
bisphenol S,
dexamethasone, benzophenone,
2-nitrophenol,
17-alpha-ethinylestradiol, dapsone,
in the 7-component mixture in water, 1 mg mL−1
58.6
36.9
35.4
68.6
58.0
75.0
69.0
NA [109]
APPJ plasma brush f = 66 kHz, duty cycle = 52%,
A = helium, 7.0 L min−1,
SFR = 1.0 mL min−1, continuous flow system
Ofloxacin
doxycycline
ampicillin
chloramphenicol
in water, 10 mg mL−1
39.77
51.37
72.33
34.33
Detailed degradation pathways proposed for each antibiotics [67]

* CV, current voltage; I, discharge current; DP, discharge power; f, frequency; A, atmosphere; V, treated volume; T, treatment time, SFR, solution flow rate.