Integrierte Vermeidung und Verminderung der Umweltverschmutzung
Integrierte Vermeidung und Verminderung der Umweltverschmutzung Integrierte Vermeidung und Verminderung der Umweltverschmutzung
Chapter 3 Unit operation Tomato juice, puree and paste (28 – 30 o Brix puree (1) ) Water consumption Waste water load Byproducts/ solid wastes Electrical energy Thermal energy No. Description (m 3 /t) (kg COD/t) (kg/t) (kWh/t) (kg steam/t) A.1 Materials handling and storage Sorting/screening, grading, 5 6 12 0.4 A.2 dehulling, destemming/ destalking and trimming 10 2 1.5 A.3 Peeling (refining) 150 – 200 8 – 12 A.4 Washing 15 5 B.1 Cutting, slicing, chopping, mincing, pulping and pressing 2.5 B.2 Mixing/blending, homogenisation and conching E.2 Blanching 15 – 25 700 – 900 E.8 Pasteurisation, sterilisation and UHT 0.5 60 – 80 F.1 Evaporation (liquid to liquid) 100 – 150 (2) 60 – 80 1500 – 1800 F.2 Drying (liquid to solid) H.1 Packing and filling 1.5 3.5 10 U.1 Cleaning and disinfection 1 U.4 Vacuum generation Overall totals of typical installations (all unit operations are not 1 4 - 5 undertaken at each installation, so the totals are not the sum of the levels for each unit operation) 130 – 180 (2) 10 – 12 160 – 210 90 – 125 2300 – 2800 60 – 80 (2) (1) All figures are referred to 1 t of 28 – 30 o Brix tomato puree. Conversion coefficients for other final products: 7 – 12 o Brix puree – multiply by 0.3; 20 – 22 o Brix puree – multiply by 0.7, 36 – 40 o Brix puree – multiply by 1.3 (2) Without cooling towers Table 3.22: Consumption and emission levels for manufacturing of tomato juice, puree and paste [89, Italian contribution, 2001, 184, Italy, 2003] 3.3.3.2 Waste water Waste water characteristics are affected by various factors. These include the raw material being processed, seasonal and source variations, unit operations, production patterns and operator practice. Table 3.23 shows data reported for canning fruits and vegetables in the US. Parameter Fruit Vegetables Waste water volume (m 3 /t raw material) 10.86 22.91 BOD5 (kg/t raw material) 11.8 13.0 TSS (kg/t raw material) 2.2 6.6 Table 3.23: Average waste water and water pollution generated in the US canning industry in 1975 [74, Greek Ministry for the Environment, 2001] Typically, waste water is high in SS, sugars and starches. Residual pesticides that are difficult to degrade during waste water treatment may be a concern, especially with produce from countries with less stringent controls on pesticide use. Reported levels of BOD and TSS in the waste water arising from the processing of various fruits and vegetables, are shown in Table 3.24 and Table 3.25. 164 January 2006 RHC/EIPPCB/FDM_BREF_FINAL
Chapter 3 BOD 5000 mg/l Product TSS mg/l Product TSS mg/l Product TSS mg/l Carrots 262 – 1540 Dried fruit 8 – 568 Beetroots 367 – 4330 Grape juice 216 – 228 Jams, jellies, preserves 404 – 711 Whole potatoes 1660 – 24300 Peas 79 – 673 Pears 84 – 702 Sweetcorn 131 – 2440 Potato crisps 1450 – 3910 Table 3.24: BOD and TSS concentrations in waste water from fruit and vegetable processing [140, World Bank (IBRD), et al., 1998] Type of operation Vegetables, frozen vegetables, preserves, fruit and vegetable juices SS (mg/l) 700 COD (mg/l) BOD5 (mg/l) Ntot (mg/l) Ptot (mg/l) RHC/EIPPCB/FDM_BREF_FINAL January 2006 165 5000 3000 Potato processing 700 10000 3000 150 200 Potato peeling Fruit and vegetable juices 1100 6000 2500 200 30 1 Apples 33 Apples (without pressing) 2 16.5 2 5500 2500 26.5 21 5100 2500 27 23 Sour cherries 9 2 4000 2300 15 Blackcurrants 24 2 4900 2600 13.5 12.5 Blackcurrants without pressing 21 2 4600 2100 – 9 Carrots 24 2 1) Rounded average figures 2) Settleable solids after two hours, ml/l 8600 2700 Table 3.25: Waste water characteristics from some fruit and vegetable processing [5, Derden A Vercaemst P and Dijkmans R, 1999, 65, Germany, 2002] Specific waste water generation and pollution loads are presented in the next two tables. Table 3.26 shows reported loads per unit production that can be achieved by implementing pollution reduction measures, such as procuring clean raw fruit and vegetables, and the use of countercurrent systems for washing and recycling process water, although the specific techniques used for each example and the unit of product are not identified. Table 3.27 shows the waste water volume and water pollution per unit of product generated in the processing of some fruit. 150 30
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Chapter 3<br />
Unit operation<br />
Tomato juice, puree and paste (28 – 30 o Brix puree (1) )<br />
Water<br />
consumption<br />
Waste water<br />
load<br />
Byproducts/<br />
solid<br />
wastes<br />
Electrical<br />
energy<br />
Thermal<br />
energy<br />
No. Description (m 3 /t) (kg COD/t) (kg/t) (kWh/t) (kg steam/t)<br />
A.1 Materials handling and storage<br />
Sorting/screening, grading,<br />
5 6 12 0.4<br />
A.2 dehulling, destemming/<br />
destalking and trimming<br />
10 2 1.5<br />
A.3 Peeling (refining) 150 – 200 8 – 12<br />
A.4 Washing 15 5<br />
B.1<br />
Cutting, slicing, chopping,<br />
mincing, pulping and pressing<br />
2.5<br />
B.2<br />
Mixing/blending,<br />
homogenisation and conching<br />
E.2 Blanching 15 – 25 700 – 900<br />
E.8<br />
Pasteurisation, sterilisation and<br />
UHT<br />
0.5 60 – 80<br />
F.1 Evaporation (liquid to liquid) 100 – 150 (2)<br />
60 – 80 1500 – 1800<br />
F.2 Drying (liquid to solid)<br />
H.1 Packing and filling 1.5 3.5 10<br />
U.1 Cleaning and disinfection 1<br />
U.4 Vacuum generation<br />
Overall totals of typical<br />
installations<br />
(all unit operations are not<br />
1 4 - 5<br />
<strong>und</strong>ertaken at each installation,<br />
so the totals are not the sum of<br />
the levels for each unit<br />
operation)<br />
130 – 180 (2)<br />
10 – 12 160 – 210 90 – 125 2300 – 2800<br />
60 – 80 (2)<br />
(1) All figures are referred to 1 t of 28 – 30 o Brix tomato puree. Conversion coefficients for other final products:<br />
7 – 12 o Brix puree – multiply by 0.3; 20 – 22 o Brix puree – multiply by 0.7, 36 – 40 o Brix puree – multiply by 1.3<br />
(2) Without cooling towers<br />
Table 3.22: Consumption and emission levels for manufacturing of tomato juice, puree and paste<br />
[89, Italian contribution, 2001, 184, Italy, 2003]<br />
3.3.3.2 Waste water<br />
Waste water characteristics are affected by various factors. These include the raw material being<br />
processed, seasonal and source variations, unit operations, production patterns and operator<br />
practice. Table 3.23 shows data reported for canning fruits and vegetables in the US.<br />
Parameter Fruit Vegetables<br />
Waste water volume (m 3 /t raw material) 10.86 22.91<br />
BOD5 (kg/t raw material) 11.8 13.0<br />
TSS (kg/t raw material) 2.2 6.6<br />
Table 3.23: Average waste water and water pollution generated in the US canning industry in 1975<br />
[74, Greek Ministry for the Environment, 2001]<br />
Typically, waste water is high in SS, sugars and starches. Residual pesticides that are difficult to<br />
degrade during waste water treatment may be a concern, especially with produce from countries<br />
with less stringent controls on pesticide use.<br />
Reported levels of BOD and TSS in the waste water arising from the processing of various<br />
fruits and vegetables, are shown in Table 3.24 and Table 3.25.<br />
164 January 2006 RHC/EIPPCB/FDM_BREF_FINAL