Evaluation of a Greenhouse Ecosystem to Treat Craft Beverage Wastewater
Abstract
:1. Introduction
2. Materials and Methods
- Design a greenhouse ecosystem for craft beverage wastewater, using the literature values from other high-strength wastewaters.
- Choose the best native, non-invasive plants to use for the greenhouse ecosystem.
- Determine the characteristics of winery, brewery, and cidery wastewaters to develop synthetic wastewaters (SWWs). SWWs were used to determine the effect of specific wastewater constituents on treatment and plants.
- Collect and treat actual winery, brewery, and cidery wastewater to determine if any constituents that were not in the SWW negatively impact the greenhouse ecosystem.
2.1. Loading and System Configuration
2.2. Plant Choice and Health Monitoring
2.3. Research Phases
- Phase 1: 3/20/23–4/6/23
- o
- All trains managed identically, receiving SWW
- Phase 2: 4/13/23–5/17/23
- o
- Train 1: SWW
- o
- Train 2: SWW with COD spike to mimic winery wastewater
- o
- Train 3: SWW with nutrient spike to mimic brewery wastewater
- Phase 3: 5/31/23–6/22/23
- o
- Train 1: SWW
- o
- Train 2: SWW spiked with COD and nutrients, representing winery wastewater
- o
- Train 3: SWW spiked with nutrients and salt spike, representing cidery wastewater
- Phase 4: 7/14/23–8/21/23
- o
- Train 1: SWW
- o
- Train 2: actual winery wastewater
- o
- Train 3: actual cidery wastewater
- Phase 5: 10/20/23–11/15/23
- o
- Train 1: SWW
- o
- Train 2: actual brewery wastewater
- o
- Train 3: SWW, recovery after actual cidery wastewater
2.4. Analytical Methods
2.5. Statistical Analysis
3. Results and Discussion
3.1. COD Analysis
3.2. Nitrogen Analysis
3.2.1. Total Nitrogen
3.2.2. Ammonia Analysis
3.2.3. Nitrite Analysis
3.2.4. Nitrate Analysis
3.2.5. Organic Nitrogen Analysis
3.3. Total Phosphorus Analysis
3.4. Plant Health Results
3.5. Aeration
4. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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Parameter | Winery | Brewery | Cidery | |||
---|---|---|---|---|---|---|
Average | Range | Average | Range | Average | Range | |
Chemical Oxygen Demand (mg/L) | 3236 | 320–296,000 | 11,214 | 800–20,000 | 8000 | >170,000 |
Biochemical Oxygen Demand (mg/L) | 2046 | 125–130,000 | 2746 | 1200–3600 | 4800 | N/A |
pH | 6.2 | 3–12.9 | 6.74 | 5–11 | N/A | N/A |
Sodium (mg/L) | 279 | 7–470 | N/A | N/A | N/A | N/A |
Total Solids (mg/L) | 11,311 | 1602–79,635 | 5600 (TSS *) | 5100–8750 | 6000 | N/A |
Total Phosphorus (mg/L) | 5.26 | 3.3–188.3 | 16–68 | 9–50 | N/A | N/A |
Total Nitrogen (mg/L) | 7.6 | 10–415 | 8.1 | 12–31 | N/A | N/A |
COD Concentration or Loading Value | Hydraulic Residence Time (Days) | Wastewater Type | Technology | Reference |
---|---|---|---|---|
440 +/− 217 mg/L * | 5 | Black water | Bio-contact oxidation; constructed wetland | [6] |
392 +/− 174 mg/L * on startup 723+/− 409 mg/L * once stable | 6, 5, 4 | Black water | Living Machine™ | [7] |
0.004 kg/m2/d | 7, 10, 9 (compared 3 technologies) | Sewage | Biofilters, surface flow wetland, stabilization pond | [15] |
0.03 kg/m2/d | 5 | Brewery wastewater | Hydroponics with grass | [16] |
425.7 mg/L * | 3.27 | Black water | Living Machine™ | [17] |
0.092 kg COD/m2/d | 3–5 | Winery wastewater | Constructed wetland | [18] |
Formulation | 95% Ethanol (mL/L) | Diluted Juice (mL/L) | Nitrogen Fertilizer (mg/L) | Sodium Phosphate (mg/L) | Salt (mg/L) |
---|---|---|---|---|---|
SWW | 2.0 | 3.3 | 45.5 | 7.5 | 0 |
COD Spike | 3.3 | 25 | 45.5 | 7.5 | 0 |
Nutrient Spike | 2.0 | 3.3 | 137 | 46 | 0 |
COD and Nutrient Spike | 47 | 25 | 228 | 37 | 0 |
Salt Spike | 2.0 | 3.3 | 137 | 46 | 688 |
Sample Location | COD (mg/L) | Mass, (g/d) | n | Std. Dev. | % Removal | % Removal Std. Dev |
---|---|---|---|---|---|---|
Train 1 SWW Influent | 1100 | 22.9 | 19 | 800 | 88 | 20.9 |
Train 1 SWW Effluent | BDL (125) | 2.56 | 20 | 90 | ||
Train 2 SWW Influent | 1200 | 24.6 | 4 | 600 | 67 | 12.5 |
Train 2 SWW Effluent | 400 | 8.05 | 4 | 100 | ||
Train 3 SWW Influent | 1100 | 22.2 | 4 | 700 | 74 | 15.9 |
Train 3 SWW Effluent | 300 | 5.82 | 4 | 80 | ||
Train 2 SWW Spiked with COD Influent | 4500 a | 92.2 | 6 | 6000 | 88 | 80.0 |
Train 2 SWW Spiked with COD Effluent | 560 b | 11.5 | 6 | 400 | ||
Train 3 SWW Spiked with Nutrients Influent | 1400 a | 28.3 | 6 | 1000 | 89 | 25.6 |
Train 3 SWW Spiked with Nutrients Effluent | BDL (125) b | 2.56 | 6 | 70 | ||
Train 2 SWW Spiked with COD and Nutrients Influent | 4500 a | 91.5 | 3 | 500 | 96 | 7.8 |
Train 2 SWW Spiked with COD and Nutrients Effluent | BDL (125) b | 2.56 | 3 | 10 | ||
Train 3 SWW Spiked with Salt and Nutrients Influent | 1400 a | 28.8 | 3 | 1000 | 90 | 25.2 |
Train 3 SWW Spiked with Salt and Nutrients Effluent | BDL (125) b | 2.56 | 3 | 20 | ||
Train 2 Winery Wastewater Influent | 7000 a | 144 | 7 | 9100 | 98 | 106.1 |
Train 2 Winery Wastewater Effluent | BDL (125) b | 2.56 | 7 | 20 | ||
Train 2 Brewery Wastewater Influent | 13,000 a | 266 | 3 | 1100 | 97 | 11.2 |
Train 2 Brewery Wastewater Effluent | 300 b | 6.84 | 3 | 100 | ||
Train 3 Cidery Wastewater Influent | 15,000 a | 312 | 7 | 18,500 | 98 | 147.7 |
Train 3 Cidery Wastewater Effluent | 300 b | 6.20 | 7 | 270 | ||
Train 3 SWW Recovery Influent after Cidery Exp. | 1100 | 23.3 | 2 | 630 | 89 | 16.5 |
Train 3 SWW Recovery Effluent after Cidery Exp. | BDL (125) | 2.56 | 2 | 12 |
Sample Location | mg/L N | Mass, mg/d | n | Std. Dev. | % Removal | % Removal Std. Dev |
---|---|---|---|---|---|---|
Train 1 SWW Influent | 5.7 | 117 | 19 | 3.6 | 64 | 1.17 |
Train 1 SWW Effluent | 2.0 | 41.9 | 20 | 1.5 | ||
Train 2 SWW Influent | 3.7 | 74.8 | 4 | 3.5 | 59 | 1.09 |
Train 2 SWW Effluent | 1.5 | 30.7 | 4 | 0.4 | ||
Train 3 SWW Influent | 3.0 | 61.0 | 4 | 2.6 | 32 | 0.49 |
Train 3 SWW Effluent | 2.0 | 41.4 | 3 | 0.4 | ||
Train 2 SWW Spiked with COD Influent | 16.7 | 343 | 5 | 18.7 | 31 | 1.65 |
Train 2 SWW Spiked with COD Effluent | 11.5 | 235 | 5 | 8.8 | ||
Train 3 SWW Spiked with Nutrients Influent | 10.8 | 221 | 5 | 7.5 | 76 | 1.74 |
Train 3 SWW Spiked with Nutrients Effluent | 2.60 | 53.2 | 5 | 0.5 | ||
Train 2 SWW Spiked with COD and Nutrients Influent | 16.6 | 341 | 4 | 6.5 | 11 | 0.18 |
Train 2 SWW Spiked with COD and Nutrients Effluent | 14.8 | 303 | 4 | 0.6 | ||
Train 3 SWW Spiked with Salt and Nutrients Influent | 14.6 | 299 | 4 | 7.5 | 64 | 1.39 |
Train 3 SWW Spiked with Salt and Nutrients Effluent | 5.3 | 108 | 4 | 2.3 | ||
Train 2 Winery Wastewater Influent | 22.2 * | 455 | 5 | 2.1 | 20 | 0.95 |
Train 2 Winery Wastewater Effluent | 17.9 | 366 | 7 | 20.5 | ||
Train 2 Brewery Wastewater Influent | 22.2 | 455 | 0 | 3.7 | 53 | 1.62 |
Train 2 Brewery Wastewater Effluent | 10.5 | 215 | 3 | 9.6 | ||
Train 3 Cidery Wastewater Influent | 45.3 | 928 | 6 | 59.3 | 88 | 7.95 |
Train 3 Cidery Wastewater Effluent | 5.3 | 108 | 7 | 4.2 | ||
Train 3 SWW Recovery Influent after Cidery Exp. | 7.0 | 144 | 2 | 3.0 | −52 | 0.00 |
Train 3 SWW Recovery Effluent after Cidery Exp. | 10.7 | 219 | 2 | 2.0 |
Sample Location | mg/L N | Mass, mg/d | n | Std. Dev. | % Removal | % Removal Std. Dev |
---|---|---|---|---|---|---|
Train 1 SWW Influent | BDL (0.5) | 10.2 | 20 | 0.77 | 0 | 0.00 |
Train 1 SWW Effluent | BDL (0.5) | 10.2 | 21 | 0.03 | ||
Train 2 SWW Influent | BDL (0.5) | 10.2 | 4 | 0.14 | 0 | 0.00 |
Train 2 SWW Effluent | BDL (0.5) | 10.2 | 4 | 0.02 | ||
Train 3 SWW Influent | BDL (0.5) | 10.2 | 4 | 0.10 | 0 | 0.00 |
Train 3 SWW Effluent | BDL (0.5) | 10.2 | 4 | 0.17 | ||
Train 2 SWW Spiked with COD Influent | BDL (0.5) | 10.2 | 6 | 0.26 | 0 | 0.00 |
Train 2 SWW Spiked with COD Effluent | BDL (0.5) | 10.2 | 6 | 1.21 | ||
Train 3 SWW Spiked with Nutrients Influent | BDL (0.5) | 10.2 | 6 | 0.32 | 0 | 0.00 |
Train 3 SWW Spiked with Nutrients Effluent | BDL (0.5) | 10.2 | 6 | 0.19 | ||
Train 2 SWW Spiked with COD and Nutrients Influent | 3.12 | 63.9 | 4 | 3.25 | 5 | 0.21 |
Train 2 SWW Spiked with COD and Nutrients Effluent | 2.95 | 60.4 | 4 | 5.83 | ||
Train 3 SWW Spiked with Salt and Nutrients Influent | 3.76 | 77.0 | 4 | 0.32 | 87 | 0.14 |
Train 3 SWW Spiked with Salt and Nutrients Effluent | BDL (0.5) | 10.2 | 4 | 0.02 | ||
Train 2 Winery Wastewater Influent | 6.48 a | 13.3 | 7 | 5.48 | 92 | 1.99 |
Train 2 Winery Wastewater Effluent | BDL (0.5) b | 10.2 | 7 | 0.01 | ||
Train 2 Brewery Wastewater Influent | * | 470 | 2 | 7.28 | 94 | 2.09 |
Train 2 Brewery Wastewater Effluent | 1.39 | 28.5 | 2 | 1.92 | ||
Train 3 Cidery Wastewater Influent | 1.75 a | 35.9 | 7 | 3.35 | 71 | 1.92 |
Train 3 SWW Cidery Wastewater Effluent | BDL (0.5) b | 10.2 | 7 | 0.64 | ||
Train 3 SWW Recovery Influent after Cidery Exp. | BDL (0.5) | 10.2 | 2 | 0.00 | 0 | 0.00 |
Train 3 SWW Recovery Effluent after Cidery Exp. | BDL (0.5) | 10.2 | 2 | 0.00 |
Sample Location | mg/L-N | Mass, mg/d | n | Std. Dev. | % Removal | % Removal Std. Dev |
---|---|---|---|---|---|---|
Train 1 SWW Influent | 0.89 | 18.2 | 18 | 0.54 | 35 | 0.30 |
Train 1 SWW Effluent | 0.58 | 11.8 | 19 | 0.47 | ||
Train 2 SWW Influent | 1.04 | 21.3 | 4 | 0.24 | 83 | 0.20 |
Train 2 SWW Effluent | BDL (0.115) | 2.35 | 4 | 0.02 | ||
Train 3 SWW Influent | 0.99 | 20.2 | 4 | 0.31 | 81 | 0.26 |
Train 3 SWW Effluent | BDL (0.115) | 2.35 | 4 | 0.02 | ||
Train 2 SWW Spiked with COD Influent | 5.39 a | 11.0 | 4 | 2.89 | 96 | 1.21 |
Train 2 SWW Spiked with COD Effluent | 0.23 b | 4.76 | 4 | 0.11 | ||
Train 3 SWW Spiked with Nutrients Influent | 1.19 | 24.3 | 4 | 0.60 | 25 | 0.26 |
Train 3 SWW Spiked with Nutrients Effluent | 0.89 | 18.3 | 4 | 0.86 | ||
Train 2 SWW Spiked with COD and Nutrients Influent | 4.73 | 96.8 | 4 | 3.78 | −2.5 | 0.00 |
Train 2 SWW Spiked with COD and Nutrients Effluent | 4.85 | 99.2 | 4 | 5.03 | ||
Train 3 SWW Spiked with Salt and Nutrients Influent | 0.79 | 16.1 | 4 | 0.60 | −350 | 0.00 |
Train 3 SWW Spiked with Salt and Nutrients Effluent | 3.56 | 72.9 | 4 | 0.94 | ||
Train 2 Winery Wastewater Influent | 3.51 | 71.9 | 7 | 4.58 | −125 | 0.00 |
Train 2 Winery Wastewater Effluent | 8.01 | 164 | 7 | 1.21 | ||
Train 2 Brewery Wastewater Influent | 11.5 a | 235 | 2 | 1.13 | 97 | 0.36 |
Train 2 Brewery Wastewater Effluent | 0.38 b | 7.70 | 2 | 0.10 | ||
Train 3 Cidery Wastewater Influent | 5.34 | 109 | 7 | 3.78 | 79 | 1.44 |
Train 3 Cidery Wastewater Effluent | 1.11 | 22.7 | 7 | 0.84 | ||
Train 3 SWW Recovery Influent after Cidery Exp. | 1.76 | 36.0 | 2 | 0.00 | 340 | 0.00 |
Train 3 SWW Recovery Effluent after Cidery Exp. | 7.69 | 157 | 2 | 1.00 |
Sample Location | mg/L-N | % Removal |
---|---|---|
Train 1 SWW Influent | 4.8 | 70 |
Train 1 SWW Effluent | 1.4 | |
Train 2 SWW Influent | 11.3 | 89 |
Train 2 SWW Effluent | 1.3 | |
Train 3 SWW Influent | 2.0 | 7.5 |
Train 3 SWW Effluent | 1.8 | |
Train 2 SWW Spiked with COD Influent | 11.9 | 5.5 |
Train 2 SWW Spiked with COD Effluent | 11.2 | |
Train 3 SWW Spiked with Nutrients Influent | 9.6 | 84 |
Train 3 SWW Spiked with Nutrients Effluent | 1.5 | |
Train 2 SWW Spiked with COD and Nutrients Influent | 18.6 | 50 |
Train 2 SWW Spiked with COD and Nutrients Effluent | 9.4 | |
Train 3 SWW Spiked with Salt and Nutrients Influent | 13.8 | 88 |
Train 3 SWW Spiked with Salt and Nutrients Effluent | 1.7 | |
Train 2 Winery Wastewater Influent | 18.6 | 47 |
Train 2 Winery Wastewater Effluent | 9.9 | |
Train 2 Brewery Wastewater Influent | N/A | N/A |
Train 2 Brewery Wastewater Effluent | 10.1 | |
Train 3 Cidery Wastewater Influent | 39.9 | 90 |
Train 3 Cidery Wastewater Effluent | 4.1 | |
Train 3 SWW Recovery Influent after Cidery Experiment | 5.3 | 43 |
Train 3 SWW Recovery Effluent after Cidery Experiment | 3.0 |
Sample Location | mg/L P | Mass, mg/d | n | Std. Dev. | % Removal | % Removal Std. Dev |
---|---|---|---|---|---|---|
Train 1 SWW Influent | 2.25 | 46.0 | 20 | 0.45 | 79 | 0.43 |
Train 1 SWW Effluent | BDL (0.25) | 5.12 | 21 | 0.22 | ||
Train 2 SWW Influent | 2.30 | 47.1 | 4 | 0.03 | 95 | 0.32 |
Train 2 SWW Effluent | BDL (0.25) | 5.12 | 4 | 0.16 | ||
Train 3 SWW Influent | 2.32 | 47.4 | 4 | 0.24 | 88 | 0.43 |
Train 3 SWW Effluent | BDL (0.25) | 5.12 | 4 | 0.23 | ||
Train 2 SWW Spiked with COD Influent | 3.25 a | 66.6 | 6 | 3.80 | 79 | 1.73 |
Train 2 SWW Spiked with COD Effluent | 0.69 b | 14.2 | 6 | 0.51 | ||
Train 3 SWW Spiked with Nutrients Influent | 4.94 a | 101 | 6 | 2.05 | 77 | 0.97 |
Train 3 SWW Spiked with Nutrients Effluent | 1.12 b | 22.9 | 6 | 0.89 | ||
Train 2 SWW Spiked with COD and Nutrients Influent | 6.41 a | 131 | 4 | 1.68 | 75 | 0.52 |
Train 2 SWW Spiked with COD and Nutrients Effluent | 1.63 b | 33.3 | 4 | 0.26 | ||
Train 3 SWW Spiked with Salt and Nutrients Influent | 6.31 a | 129 | 4 | 2.05 | 66 | 0.57 |
Train 3 SWW Spiked with Salt and Nutrients Effluent | 2.13 b | 43.5 | 4 | 0.40 | ||
Train 2 Winery Wastewater Influent | 9.40 a | 192 | 7 | 7.51 | 88 | 2.19 |
Train 2 Winery Wastewater Effluent | 1.09 b | 22.4 | 7 | 0.39 | ||
Train 2 Brewery Wastewater Influent | 89.7 a | 1840 | 3 | 61.2 | 91 | 6.05 |
Train 2 Brewery Wastewater Effluent | 7.83 b | 160 | 3 | 4.18 | ||
Train 3 Cidery Wastewater Influent | 23.9 a | 489 | 7 | 23.9 | 88 | 4.42 |
Train 3 Cidery Wastewater Effluent | 2.99 b | 61.1 | 6 | 2.16 | ||
Train 3 SWW Recovery Influent after Cidery Exp. | 2.44 | 49.9 | 2 | 0.00 | 0 | 0.00 |
Train 3 SWW Recovery Effluent after Cidery Exp. | 2.87 | 58.7 | 2 | 0.00 |
Sample Location | Average, mg/L | Std. dev. | n | # of Occurrences < 0.2 mg/L | % of Total Values < 0.2 mg/L |
---|---|---|---|---|---|
WW1 | 2.0 | 1.7 | 88 | 14 | 15.9 |
T1R1 | 3.1 | 2.5 | 98 | 16 | 16.3 |
T1R2 | 5.4 | 3.1 | 98 | 14 | 14.3 |
T1R3 | 3.2 | 2.5 | 98 | 14 | 14.3 |
WW2 | 2.0 | 1.8 | 88 | 20 | 22.7 |
T2R1 | 5.4 | 3.1 | 98 | 14 | 14.3 |
T2R2 | 3.2 | 2.9 | 98 | 18 | 18.4 |
T2R3 | 2.4 | 2.8 | 98 | 15 | 15.3 |
WW3 | 2.0 | 1.7 | 88 | 17 | 19.3 |
T3R1 | 2.2 | 2.1 | 98 | 18 | 18.4 |
T3R2 | 4.3 | 3.1 | 98 | 17 | 17.3 |
T3R3 | 2.7 | 2.5 | 98 | 16 | 16.3 |
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Allison, C.E.; Safferman, S.I. Evaluation of a Greenhouse Ecosystem to Treat Craft Beverage Wastewater. Sustainability 2024, 16, 7395. https://doi.org/10.3390/su16177395
Allison CE, Safferman SI. Evaluation of a Greenhouse Ecosystem to Treat Craft Beverage Wastewater. Sustainability. 2024; 16(17):7395. https://doi.org/10.3390/su16177395
Chicago/Turabian StyleAllison, Carley E., and Steven I. Safferman. 2024. "Evaluation of a Greenhouse Ecosystem to Treat Craft Beverage Wastewater" Sustainability 16, no. 17: 7395. https://doi.org/10.3390/su16177395
APA StyleAllison, C. E., & Safferman, S. I. (2024). Evaluation of a Greenhouse Ecosystem to Treat Craft Beverage Wastewater. Sustainability, 16(17), 7395. https://doi.org/10.3390/su16177395