| #P001 | chemical | treatment | mandatory | benzene | drinking water | requirement | > 99 % | For a drinking water treatment device to be certified to NSF/ANSI Standard 53 for the removal of VOCs | from an influent (challenge) concentration of 0.081 mg/L | high |
| #P002 | chemical | treatment | mandatory | benzene influent (challenge) concentration | drinking water | requirement | 0.081 mg/L | Influent requirement for certification to NSF/ANSI Standard 53 | | high |
| #P003 | chemical | treatment | mandatory | benzene maximum final (effluent) concentration | drinking water | requirement | < 0.001 mg/L | For a drinking water treatment device to be certified to NSF/ANSI Standard 53 for the removal of VOCs | | high |
| #P004 | chemical | treatment | mandatory | VOCs final concentration | drinking water | requirement | < 0.001 mg/L | Reverse osmosis systems certified to NSF/ANSI Standard 58 for the reduction of VOCs | | high |
| #P005 | chemical | treatment | guidance | Benzene effluent concentration (Municipal) | drinking water | treatment_goal | < 1 µg/L | Municipal treatment methods such as GAC adsorption and air stripping are capable of achieving these levels. | Municipal scale treatment | high |
| #P006 | chemical | treatment | guidance | Benzene removal efficiency (Municipal) | drinking water | treatment_goal | 99 % | Feasible removal efficiency for GAC adsorption and packed tower aeration in municipal systems. | Municipal scale treatment | high |
| #P007 | operational | treatment | guidance | Ozone dosage (81% degradation) | drinking water | OG | 6 mg/L | Pilot-scale treatment tests achieving 81% degradation of benzene in distilled water. | From approximately 50 µg/L to 10 µg/L | high |
| #P008 | operational | treatment | guidance | Ozone dosage (94% reduction) | drinking water | OG | 12 mg/L | Ozone dose achieving 94% reduction in distilled water and groundwater matrices. | Wide range of pH | high |
| #P009 | operational | treatment | guidance | PAC dosage | drinking water | OG | 60 mg/L | Pilot-scale studies using a combined jet flocculation/PAC system. | Reducing benzene from 100 to 5 µg/L | high |
| #P010 | design | treatment | guidance | PTA air-to-water ratio | drinking water | requirement | 32.7 ratio | Typical full-scale plant design parameters for reduction of benzene. | Flow rate > 8 ML/day | high |
| #P011 | design | treatment | guidance | PTA air stripper length | drinking water | requirement | 11.05 m | Typical full-scale plant design parameters for reduction of benzene. | Flow rate > 8 ML/day | high |
| #P012 | chemical | treatment | guidance | Reverse osmosis removal efficiency | drinking water | treatment_goal | 94 % | Pilot plant investigations for benzene removal from drinking water. | Influent concentration of 1000 µg/L | high |
| #P013 | operational | treatment | guidance | GAC Empty Bed Contact Time (EBCT) | drinking water | OG | 23.7 minutes | Operating conditions of the GAC filter adsorber demonstrated in full-scale studies. | Influent benzene 10 µg/L to < 0.1 µg/L | high |
| #P014 | operational | treatment | guidance | Carbon use rate | drinking water | OG | 0.013 kg/m3 | Estimated carbon use rate for benzene reduction using GAC. | To reduce influent 100 µg/L to effluent 5 µg/L with EBCT of 15 minutes | high |
| #P015 | design | treatment | guidance | PTA packed column diameter | drinking water | requirement | 2.55 m | Typical full-scale plant design parameters for the reduction of benzene from drinking water. | Flow rate > 8 ML/day | high |
| #P016 | design | treatment | guidance | PTA packing depth | drinking water | requirement | 12.95 m | Modeling to determine cost-effective design criteria for PTA contactors. | Achieving 99% reduction to effluent 1 µg/L | high |
| #P017 | operational | treatment | guidance | Ozone dosage (low range) | drinking water | OG | 0.8-1.5 mg/L | Pilot studies observing degradation of benzene with specific ozone doses. | | high |
| #P018 | operational | treatment | guidance | Hydrogen peroxide dose (photocatalytic) | drinking water | OG | 70 mg/L | Pilot-scale photocatalytic oxidation system utilized for reducing influent benzene. | Combined with UV light and 0.4 mg/L ozone | high |
| #P019 | operational | treatment | guidance | Ozone dose (photocatalytic) | drinking water | OG | 0.4 mg/L | Pilot-scale photocatalytic oxidation system combined with UV and hydrogen peroxide. | Reducing influent 123 µg/L to below 0.5 µg/L | high |
| #P020 | chemical | treatment | guidance | Effluent benzene concentration (photocatalytic) | drinking water | treatment_goal | < 0.5 µg/L | Performance of pilot-scale photocatalytic oxidation system. | Influent concentration of 123 µg/L | high |
| #P021 | chemical | treatment | guidance | Coagulation and filtration benzene reduction | drinking water | requirement | 0 to 29 % | Reported reductions for municipal plants relying on conventional treatment. | May be partially attributed to incidental volatilization | high |
| #P022 | design | treatment | guidance | GAC bed volume | drinking water | OG | 23.8 m3 | Operating conditions of the GAC filter adsorber from full-scale studies. | Full-scale studies of fixed-bed GAC adsorbers | high |
| #P023 | design | treatment | guidance | GAC flow rate (full-scale) | drinking water | OG | 1.5 ML/day | Operating conditions of the GAC filter adsorber from full-scale studies. | | high |
| #P024 | design | treatment | guidance | GAC flow rate (parallel adsorbers) | drinking water | OG | 5 ML/day | Three GAC adsorbers operating in parallel. | Reducing benzene 20 µg/L to 0.2 µg/L | high |
| #P025 | design | treatment | guidance | GAC bed life (parallel adsorbers) | drinking water | OG | 12 months | Three GAC adsorbers operating in parallel. | | high |
| #P026 | design | treatment | guidance | GAC bed life (model) | drinking water | OG | 389 days | Estimated GAC performance using model predictions. | To reduce 100 µg/L to 5 µg/L | high |
| #P027 | operational | treatment | guidance | Silica clay dosage | drinking water | OG | 100 mg/L | Combined jet flocculation/PAC system for benzene removal. | Pilot-scale studies | high |
| #P028 | operational | treatment | guidance | PAC contact time | drinking water | OG | 2-8 minutes | Combined jet flocculation/PAC system for benzene removal. | Pilot-scale studies | high |
| #P029 | design | treatment | guidance | PTA air-to-water ratio (Allan) | drinking water | requirement | 75 ratio | Countercurrentflow PTA for reducing benzene. | Full-scale plant data reducing 30 µg/L to 1.5 µg/L | high |
| #P030 | design | treatment | guidance | PTA air stripper length (Allan) | drinking water | requirement | 5.50 m | Countercurrentflow PTA for reducing benzene. | | high |
| #P031 | design | treatment | guidance | PTA column diameter (Allan) | drinking water | requirement | 1.52 m | Countercurrentflow PTA for reducing benzene. | | high |
| #P032 | design | treatment | guidance | PTA air-to-water ratio (AWWA) | drinking water | requirement | 100 ratio | Full-scale PTA performance. | Reducing 200 µg/L to less than 2 µg/L | high |
| #P033 | design | treatment | guidance | PTA air stripper length (AWWA) | drinking water | requirement | 10.05 m | Full-scale PTA performance. | | high |
| #P034 | design | treatment | guidance | PTA column diameter (AWWA) | drinking water | requirement | 3.05 m | Full-scale PTA performance. | | high |
| #P035 | chemical | treatment | guidance | PTA benzene removal efficiency (Pilot) | drinking water | treatment_goal | 77 to over 99 % | Pilot plant studies for reduction of VOCs in groundwater. | | high |
| #P036 | chemical | treatment | guidance | RO benzene removal (alternative membranes) | drinking water | treatment_goal | < 20 % | Studies evaluating cellulose, polyamide, and thin film composite membranes. | | high |
| #P037 | operational | treatment | guidance | GAC EBCT (parallel adsorbers) | drinking water | OG | 21 minutes | Operating conditions for three GAC adsorbers operating in parallel. | Reducing benzene concentrations of 20 µg/L to 0.2 µg/L | high |
| #P038 | operational | treatment | guidance | GAC EBCT (model prediction) | drinking water | OG | 15 minutes | Model predictions for full-scale GAC performance. | To reduce influent 100 µg/L to effluent 5 µg/L | high |
| #P039 | design | treatment | guidance | PTA air-to-water ratio (Adams and Clark) | drinking water | requirement | 40 ratio | Modeling to determine cost-effective design criteria for PTA contactors. | Associated with packing depth of 12.95 m to achieve 99% reduction | high |
| #P040 | chemical | treatment | guidance | UV/titanium dioxide oxidation removal efficiency | drinking water | treatment_goal | > 99 % | Pilot study performance of UV/titanium dioxide oxidation process. | | high |
| #P041 | chemical | treatment | guidance | Reverse osmosis influent concentration | drinking water | treatment_goal | 1000 µg/L | Influent levels used in pilot plant investigations demonstrating 94% removal. | Pilot plant investigations | high |
| #P042 | operational | treatment | guidance | PTA cost evaluation system size range | drinking water | OG | 1 to 100 ML/day | Range of system sizes evaluated in PTA/GAC cost comparisons. | | high |