Table 1.
Study | Location | Sample source | Volume used (mL) | Removal of large debris and suspended solids | Concentration method | Detection ratea | qPCR assay | |
---|---|---|---|---|---|---|---|---|
(Medema et al., 2020b) | The Netherlands | WWTP Influent | 100–200 | Centrifugation | Ultrafiltration: Centricon® Plus-70 | 14/18 | CDC N1, N2, N3, E_Sarbeco | |
(F. Wu et al., 2020) | Boston, MA, USA | WWTP Influent | 40 | Filtration | Precipitation-flocculation: PEG 8000 + NaCl + 0.22 μm Filter | 10/10 | CDC N1, N2, N3 | |
(Wurtzer et al., 2020b) | Paris, France | WWTP Influent | 11 | None | Ultracentrifugation | 18/18 | E_Sarbeco | |
WWTP Treated | 6/8 | |||||||
(Ahmed et al., 2020a) | Brisbane, Australia | WWTP Influent | 100–200 | None | Electronegative membrane filtrationb | 1/8 | N_Sarbeco, NIID_2019-nCoV | |
Sewer Network | 0/1 | |||||||
WWTP Influent | Centrifugation | Ultrafiltration: Centricon® Plus-70 | 1/8 | |||||
Sewer Network | 0/1 | |||||||
(Nemudryi et al., 2020) | Bozeman, MT, USA | WWTP Influent | 500 | Sequential filtration (20, 5, 0.45 μm filters) | Ultrafiltration: Corning® Spin-X® UF concentrators | 5/5 | CDC N1, N2 | |
WWTP Influent | 2/2 | |||||||
(Randazzo et al., 2020a) | Valencia, Spain | WWTP Influent | 200 | None | Precipitation-flocculationb: AlCl3 | 12/14 | CDC N1, N2 | |
WWTP Treated | 0/9 | |||||||
(Bar-Or et al., 2020) | Israel | WWTP Influent | 400 | Centrifugation | Precipitation-flocculation + Ultrafiltration | PEG 8000 + 0.22 μm filter + Amicon® Ultra-15 | 3/17 | E_Sarbeco |
Sewer Network | 200 | 7/9 | ||||||
WWTP Influent | 400 | Alum +0.22 μm filter + Amicon® Ultra-15 | 1/2 | |||||
Sewer Network | 200 | 1/3 | ||||||
(Rimoldi et al., 2020) | Milan, Italy | WWTP Influent | 500 | Sequential filtration (0.7, 0.2 μm filters) | None | 4/8 | Liferiver, N, E_Sarbeco, ORF1ab, | |
WWTP Treated | 0/4 | |||||||
Surface water | 3/4 | |||||||
(Kocamemi et al., 2020a) | Istanbul, Turkey | WWTP Influent | 250 | Centrifugation + Sequential filtration (0.45, 0.22 μm filters) | Precipitation-flocculationb: PEG 8000 + NaCl | 5/7 | RdRp | |
Sewer Network | 2/2 | |||||||
(Wurtzer et al., 2020a) | Paris, France | WWTP Influent | 11 | None | Ultracentrifugation | 30/30 | E_Sarbeco, RdRp | |
(La Rosa et al., 2020) | Milan & Rome, Italy | WWTP Influent | 250 | Centrifugation | Precipitation-flocculation: PEG 8000 + Dextran | 6/12 | ORF1ab, Spike | |
(Kocamemi et al., 2020b) | Istanbul, Turkey | WWTP Sludge | 250 | Centrifugation + Sequential filtration (0.45, 0.22 μm filters) | Precipitation-flocculationb: PEG 8000 + NaCl | 9/9 | RdRp | |
(Randazzo et al., 2020b) | Murcia, Spain | WWTP Influent | 200 | None | Precipitation-flocculationb: AlCl3 + Beef extract | 35/43 | CDC N1, N2, N3 | |
WWTP Treated | 3/30 | |||||||
(Medema et al., 2020a) | The Netherlands | WWTP Influent | 36–150 | Centrifugation | Ultrafiltration: Centricon® Plus-70 | 20/22 | CDC N1, N2, N3, E_Sarbeco | |
(Peccia et al., 2020) | New Haven, CT, USA | WWTP Sludge | 2.5 | None | None | 43/43 | CDC N1, N2 | |
(Green et al., 2020) | Syracuse, NY, USA | WWTP Influent | 20 | None | Ultracentrifugation: sucrose cushion (50% sucrose in TNE buffer) | 6/12 | RdRp (IP2, IP4) | |
Sewer Network | 20 | 7/10 | ||||||
(Balboa et al., 2020) | Ourense, Spain | WWTP Influent | 100 | Centrifugation | Ultrafiltration: Amicon® Ultra-15 | 5/5 | Allplex N, E_Sarbeco, RdRp | |
WWTP Treated | 1/10 | |||||||
WWTP Sludge | 50 | None | Precipitation-flocculation + Ultrafiltration: PEG 8000 + Glycin buffer +0.45 μm PES membrane + NaCl |
14/35 | ||||
(Haramoto et al., 2020) | Yamanashi, Japan | WWTP Influent | 200 | None | Adsorption-elution: MgCl2 + 0.8 μm cellulose-ester membrane + elution buffer +0.45 μm filter + Centriprep YM-50 | 0/5 | CDC N1, N2, N_Sarbeco, NIID_2019-nCoV | |
WWTP Treated | 5000 | 1/5 | ||||||
Surface Water | 5000 | 0/3 | ||||||
WWTP Influent | 200 | Electronegative filtration: MgCL2 + 0.8 μm cellulose-ester membrane | 0/5 | |||||
WWTP Treated | 5000 | 0/5 | ||||||
Surface Water | 5000 | 0/3 | ||||||
(Sharif et al., 2020) | Pakistan | Sewer Network | 500 | Centrifugation | Precipitation-flocculation: PEG 8000 + dextran + chloroform | 21/78 | E_Sarbeco, ORF1ab, N-gene | |
(Sherchan et al., 2020) | Louisiana, USA | WWTP Influent | 250 | None | Ultrafiltration: Centricon® Plus-70 | 2/2 | CDC N1, N2 | |
WWTP Treated | 250 | 0/1 | ||||||
WWTP Effluent | 250 | 0/1 | ||||||
WWTP Influent | 100 | Adsorption-elution: MgCl2 + 0.45 μm electronegative membrane + H2SO4 + NaOH + Centriprep YM-50 | 0/2 | |||||
WWTP Treated | 750 | 0/1 | ||||||
WWTP Effluent | 750 | 0/1 | ||||||
(Kumar et al., 2020) | Ahmedabad, India | WWTP Influent | 50 | Centrifugation + filtration (0.22 μm) | Precipitation-flocculation: PEG 9000 + NaCl | 2/2 | ORF1ab, N-gene, S-gene | |
WWTP Treated | 50 | 0/2 |
Only samples collected after the first case are counted.
pH adjustment.