Hús feldolgozó üzem szennyvíze

Data provider

Budapest University of Technology and Economics, Department of Applied Biotechnology and Food Science, Environmental Microbiology and Biotechnology Group

Organisation/Data provider's nameBudapest University of Technology and Economics, Department of Applied Biotechnology and Food Science, Environmental Microbiology and Biotechnology Group
Name of contact
Dr. Molnár Mónika, Dr. Feigl Viktória
Contact details
Telephone/fax
+36-1-4632347
E-mail
mmolnar@mail.bme.hu
vfeigl@mail.bme.hu
Website
http://envirotox.hu
General information about the waste or by-product
Denomination of the waste or by-productHús feldolgozó üzem szennyvíze
Denomination of the waste or by-product in English
Meet processing effluent
Type of the waste or by-product data-sheet
General characterization
Functional characterisation
Hazardous waste from food industry
EWC code of waste
  • 02 WASTES FROM AGRICULTURE, HORTICULTURE, AQUACULTURE, FORESTRY, HUNTING AND FISHING, FOOD PREPARATION AND PROCESSING
  • 02 02 wastes from the preparation and processing of meat, fish and other foods of animal origin
  • 02 02 99 waste not otherwise specified
Consistency of the waste or by-product
Fluid (liquid)
Description of the waste generating technology

A hús mosása, tisztítása, valamint az eszközök és berendezések tiszítása során keletkezik nagy mennyiségű magas fehérje és zsírtartalmú szennyvíz.

Any special characteristics of the waste or by-product

A feldolgozott hús fajtájától és minőségétől függően eltérő lehet.

Is it a hazardous waste?
yes
Characterisation of the waste as a chemical substance
Mixture of chemical substances
Characterisation and concentration of the chemical substances
Chemical substance, Main group|Chemical substance, Subgroup
  • Other inorganic chemical compounds
  • nitrogen (total)
Is the contained chemical substance main component, component or contaminant of the waste or by-products / biochar?
Component
Concentration of the chemical in the waste or by-product / biochar
115 mg/l
Chemical substance, Main group|Chemical substance, Subgroup
  • Other inorganic chemical compounds
  • phosphorous (total)
Is the contained chemical substance main component, component or contaminant of the waste or by-products / biochar?
Component
Concentration of the chemical in the waste or by-product / biochar
15 mg/l
Chemical substance, Main group|Chemical substance, Subgroup
  • Other inorganic chemical compounds
  • ammonia/ammonium
Is the contained chemical substance main component, component or contaminant of the waste or by-products / biochar?
Component
Concentration of the chemical in the waste or by-product / biochar
30 mg/l
Main characteristics of the waste/ by-product
Name of the waste/by-product
Vágóhídi és húsipari szennyvíz
Components of the waste/by-product

nagy mennyiségű vért, állati fehérjét és zsírt tartalmaznak. A zsír, mint felülúszó a víz felszínén megszilárdul, majd egyre vastagabb rétegre kiterjed, így a csatornanyílás elzáródásához vezethet. A húsipari szennyvizekben sok a darabos szennyezés, amelyek hús és béldarabkák, köröm, toll lehetnek. Mindemellett igen nagy mennyiségű szerves anyagot, gyomor- és béltartalmat, hígtrágyát, szőrt is tartalmaznak, ezért rövid időn belül erőteljes rothadásnak indulnak, intenzív szagképződés mellett. Egészségügyi szempontból magas baktérium fertőzöttség jellemzi, döntően patogén Salmonella törzsekkel http://www.pointernet.pds.hu/ujsagok/transpack/2006/11/2007020519231152…
http://www.bioamp.co.hu/industries-meat-processing

Physico-chemical properties of the waste or by-product
pH
7.5
Organic content (%)
40
C/N ratio
3.7
Total Organic Carbon (mg/l)
230 000
Chemical Oxygen Demand, COD (mg/l)
1900
Other

KOI: 530-4700 mg/l; Összes nitrogén: 40-230 mg/l, Ammónia formájú N: 3-70 mg/l, Összes foszfor: 6-34 mg/l.
Forrás: J.M. Russell, R.N. Cooper, S.B. Lindsey (1993) Soil denitrification rates at wastewater irrigation sites receiving primary-treated and anaerobically treated meat-processing effluent, Bioresource Technology 43(1), pp. 41-46.

Is this waste or by-product being utilised?
Yes
Utilisation

A húsfeldolgozó üzemi szennyvíz elválasztott szerves anyagai biogáz termelére használhatóak, valamint a talajra kijuttatható. A biogáz termelés során keletkező maradék biogázferment a talajra kijuttatható.

Hazards of the waste or by-product
Hazard characteristics
Not classified
No information
Measured harmful effects
No
Suspected harmful effects

Kezelés nélkül a környezetbe juttatva megnő a víz szerves anyag tartalma, mely a baktériumoknak tápanyagot jelent, a bontáshoz oxigén kell, csökken a víz oxigén tartalma, anaerob populáció jelenik meg, továbbá algásodást, iszaposodást, járványt idézhet elő.

Potential utilisation in soil
Would it be suitable for soil reclamation in general?
Yes
Justification, references

Magas szerves-anyag, nitrogén és foszfor tartalmának köszönhetően alkalmas.
Forrás:
J.M. Russell, R.N. Cooper, S.B. Lindsey (1993) Soil denitrification rates at wastewater irrigation sites receiving primary-treated and anaerobically treated meat-processing effluent, Bioresource Technology 43(1), pp. 41-46.

G. Erden, N. Buyukkamaci, A. Filibeli (2010) Effect of low frequency ultrasound on anaerobic biodegradability of meat processing effluent, Desalination 259(1–3), pp. 223-227.

M.R. Balks, C.D.A. McLay, C.G. Harfoot (1997) Determination of the progression in soil microbial response, and changes in soil permeability, following application of meat processing effluent to soil, Applied Soil Ecology 6(2), pp. 109-116.

A.J. van Oostrom (1995) Nitrogen removal in constructed wetlands treating nitrified meat processing effluent, Water Science and Technology 32(3), pp. 137-147.

E. Görgün, E. Ubay Çokgör, D. Orhon, F. Germirli, N. Artan (1995) Modelling biological treatability for meat processing effluent, Water Science and Technology 32(12), pp. 43-52.

J.M. Russell, R.N. Cooper, S.B. Lindsey (1993) Soil denitrification rates at wastewater irrigation sites receiving primary-treated and anaerobically treated meat-processing effluent,Bioresource Technology 43(1), pp. 41-46.

A.J. van Oostrom, R.N. Cooper (1990) MEAT PROCESSING EFFLUENT TREATMENT IN SURFACE-FLOW AND GRAVEL-BED CONSTRUCTED WASTEWATER WETLANDS, Constructed Wetlands in Water Pollution Control, pp. 321,321a,322-332.

J Luo, S Lindsey, J Xue (2004) Irrigation of meat processing wastewater onto land Agriculture, Ecosystems & Environment 103(1), pp. 123-148.

Would it supply nitrogen, phosphorous and/or potassium to the soil?
Yes
Justification, references

Magas nitrogén és foszfor tartalmának köszönhetően alkalmas.

Forrás:
J.M. Russell, R.N. Cooper, S.B. Lindsey (1993) Soil denitrification rates at wastewater irrigation sites receiving primary-treated and anaerobically treated meat-processing effluent, Bioresource Technology 43(1), pp. 41-46.

G. Erden, N. Buyukkamaci, A. Filibeli (2010) Effect of low frequency ultrasound on anaerobic biodegradability of meat processing effluent, Desalination 259(1–3), pp. 223-227.

M.R. Balks, C.D.A. McLay, C.G. Harfoot (1997) Determination of the progression in soil microbial response, and changes in soil permeability, following application of meat processing effluent to soil, Applied Soil Ecology 6(2), pp. 109-116.

A.J. van Oostrom (1995) Nitrogen removal in constructed wetlands treating nitrified meat processing effluent, Water Science and Technology 32(3), pp. 137-147.

E. Görgün, E. Ubay Çokgör, D. Orhon, F. Germirli, N. Artan (1995) Modelling biological treatability for meat pr

Would it supply mesoelements (Ca, Cl, Fe, Mg, Na, S, Si) to the soil?
No information
Would it supply microelements (B, Co, Cu, Mn, Mo, Zn, V) to the soil?
No information
Would it provide sufficient amounts of special nutrients to the soil?
No
Would it increase the humus/organic matter content of the soil?
Yes
Justification, references

Magas szerves-anyag, nitrogén és foszfor tartalmának köszönhetően alkalmas.
Forrás:
J.M. Russell, R.N. Cooper, S.B. Lindsey (1993) Soil denitrification rates at wastewater irrigation sites receiving primary-treated and anaerobically treated meat-processing effluent, Bioresource Technology 43(1), pp. 41-46.

G. Erden, N. Buyukkamaci, A. Filibeli (2010) Effect of low frequency ultrasound on anaerobic biodegradability of meat processing effluent, Desalination 259(1–3), pp. 223-227.

M.R. Balks, C.D.A. McLay, C.G. Harfoot (1997) Determination of the progression in soil microbial response, and changes in soil permeability, following application of meat processing effluent to soil, Applied Soil Ecology 6(2), pp. 109-116.

A.J. van Oostrom (1995) Nitrogen removal in constructed wetlands treating nitrified meat processing effluent, Water Science and Technology 32(3), pp. 137-147.

E. Görgün, E. Ubay Çokgör, D. Orhon, F. Germirli, N. Artan (1995) Modelling biological treatabilit

Would it suffice as a main component of growing media?
No
Justification, references

Állagából kifolyólag nem.

Would it suffice as an additive to growing media?
Yes
Justification, references

Magas szerves-anyag, nitrogén és foszfor tartalmának köszönhetően alkalmas.
Forrás:
J.M. Russell, R.N. Cooper, S.B. Lindsey (1993) Soil denitrification rates at wastewater irrigation sites receiving primary-treated and anaerobically treated meat-processing effluent, Bioresource Technology 43(1), pp. 41-46.

G. Erden, N. Buyukkamaci, A. Filibeli (2010) Effect of low frequency ultrasound on anaerobic biodegradability of meat processing effluent, Desalination 259(1–3), pp. 223-227.

M.R. Balks, C.D.A. McLay, C.G. Harfoot (1997) Determination of the progression in soil microbial response, and changes in soil permeability, following application of meat processing effluent to soil, Applied Soil Ecology 6(2), pp. 109-116.

A.J. van Oostrom (1995) Nitrogen removal in constructed wetlands treating nitrified meat processing effluent, Water Science and Technology 32(3), pp. 137-147.

E. Görgün, E. Ubay Çokgör, D. Orhon, F. Germirli, N. Artan (1995) Modelling biological treatabilit

Would it improve the structure of compacted soil and/or contribute to soil crumb formation of poorly structured soils?
No information
Would it be suitable for physical stabilisation and/or texture improvement of loose, quagmire soils?
No
Justification, references

Állagából kifolyólag nem.

Would it be suitable for amending sandy soils?
Yes
Justification, references

A szerkezeti humusztartalom növelésén keresztül alkalmas lehet.
Forrás:
M.R. Balks, C.D.A. McLay, C.G. Harfoot (1997) Determination of the progression in soil microbial response, and changes in soil permeability, following application of meat processing effluent to soil, Applied Soil Ecology 6(2), pp. 109-116.

Would it be suitable for erosion prevention?
No
Justification, references

Állagából kifolyólag nem.

Would it be suitable for amending acidic soils?
No
Justification, references

Nincs lúgosító hatása.

Would it be suitable for amending saline and sodic soils?
No
Justification, references

Nincs savanyító hatása.

Would it reduce the mobility and availability of the contaminants?
No information
Would it intensify the mobility, availability of the contaminants?
No information
Would it intensify physical, chemical, and/or biological degradation and decomposition of contaminants?
No information
Would it be suitable for production of geotechnical elements?
No
Justification, references

Állagából kifolyólag nem.

Risks associated with potential utilisation in soil

Kezelés nélkül a környezetbe juttatva megnő a víz szerves anyag tartalma, mely a baktériumoknak tápanyagot jelent, a bontáshoz oxigén kell, csökken a víz oxigén tartalma, anaerob populáció jelenik meg, továbbá algásodást, iszaposodást, járványt idézhet elő.

Properties of the datasheet
Datasheet id (original)
1212
Creator
Fekete-Kertész Ildikó
Status
Verified
Adatlap típusaWaste / by-product survey
Létrehozás
Módosítás