QUAL-UFMG Model

Input data

Temperature

River flow rate

Saturation dissolved oxygen

River dissolved oxygen

River BOD5

River organic nitrogen

River ammoniacal nitrogen

River nitrite

River nitrate

River organic phosphorous

River inorganic phosphorous

River coliform concentration

River length

Deoxigenation coefficient (K1)

BOD decomposition coefficient (Kd)

BOD settling coefficient (Ks)

Reaeration coefficient (K2)

Organic nitrogen settling coefficient (Kso)

Organic-ammoniacal nitrogen conversion coefficient (Koa)

Ammonia-nitrite conversion coefficient (Kan)

Nitrite-nitrate conversion coefficient (Knn)

Ammoniacal nitrogen release by settled sediment (Snamon)

Ammonia-nitrite conversion oxygen (O2Namon)

Nitrite-nitrate conversion oxygen (O2Nnitri)

Low DO nitrification inhibition coefficient in L/mg (knitr)

pH

Organic phosphorous settling coefficient (Kspo)

Organic-inorganic phosphorous conversion coefficient (Koi)

Coliforms decay rate (Kb)

Length of the smaller river base

Stream slope

Manning coefficient

Section factor (z)

Output data

Flow

River cross section area

Depth

Downstream BOD5

Downstream organic phosphorous

Downstream inorganic phosphorous

Downstream nitrate

Downstream nitrite

Downstream ammoniacal nitrogen

Downstream organic nitrogen

Downstream dissolved oxygen

Downstream coliforms (NMP/100ml)

Curves

Description

The QUAL-UFMG model is a comprehensive tool for simulating water quality in rivers, developed to assess the spatial distribution of pollutants and water quality parameters along watercourses. The model considers multiple biogeochemical processes and allows detailed analysis of the evolution of various water quality constituents.

 

The model offers 3 cross-sectional geometric configurations:

 

  • Trapezoidal section: For natural channels with side slopes
  • Rectangular section: For artificial channels with vertical walls
  • Triangular section: For V-shaped channels

 

Modeled processes

The QUAL-UFMG model simulates the following processes:

  • Oxygen cycle: Consumption by organic matter decomposition, nitrification, and atmospheric reaeration
  • Nitrogen cycle: Conversion of organic nitrogen → ammonia → nitrite → nitrate
  • Phosphorus cycle: Transformation between organic and inorganic phosphorus
  • Coliform decay: Natural death of indicator organisms
  • Sedimentation: Removal of particulate material by deposition

Fundamental equations

The model uses the following differential equations to describe temporal concentration variations:

Dissolved oxygen:

dDOdt=K2(DOsatDO)KdBODKTO2NamonNNH3KanfnitrO2NnitriNNO2Knnfnitr\frac{dDO}{dt} = K_2(DO_{sat} - DO) - K_d \cdot BOD \cdot K_T - O2Namon \cdot N_{NH_3} \cdot K_{an} \cdot f_{nitr} - O2Nnitri \cdot N_{NO_2} \cdot K_{nn} \cdot f_{nitr}

BOD:

dBODdt=KrBOD\frac{dBOD}{dt} = -K_r \cdot BOD

where Kr=Kd+KsK_r = K_d + K_s

Organic nitrogen:

dNorgdt=(Kso+Koa)Norg\frac{dN_{org}}{dt} = -(K_{so} + K_{oa}) \cdot N_{org}

Ammoniacal nitrogen:

dNNH3dt=KoaNorgKanNNH3fnitr+SNH3h\frac{dN_{NH_3}}{dt} = K_{oa} \cdot N_{org} - K_{an} \cdot N_{NH_3} \cdot f_{nitr} + \frac{S_{NH_3}}{h}

Organic phosphorus:

dPorgdt=(Kspo+Koi)Porg\frac{dP_{org}}{dt} = -(K_{spo} + K_{oi}) \cdot P_{org}

Temperature correction

All kinetic coefficients are corrected for temperature using:

KT=K20θ(T20)K_T = K_{20} \cdot \theta^{(T-20)}

where θ\theta varies between 1.024 and 1.080 depending on the process.

Channel hydraulics

For trapezoidal sections:

  • Wetted area: A=h(b+zh)A = h(b + zh)
  • Wetted perimeter: P=b+2h1+z2P = b + 2h\sqrt{1 + z^2}

For rectangular sections:

  • Wetted area: A=bhA = bh
  • Wetted perimeter: P=b+2hP = b + 2h

For triangular sections:

  • Wetted area: A=zh2A = zh^2
  • Wetted perimeter: P=2h1+z2P = 2h\sqrt{1 + z^2}

Depth is calculated using Manning's equation:

Q=AnRh2/3S1/2Q = \frac{A}{n} \cdot R_h^{2/3} \cdot S^{1/2}

Input data

ParameterStandard unitsDescription
Temperature°CWater temperature for kinetic coefficient correction
River flow ratem³/sVolumetric flow rate of the watercourse
Saturation dissolved oxygenmg/LDO saturation concentration at specified temperature
River dissolved oxygenmg/LInitial DO concentration in the river
River BOD5mg/LInitial 5-day biochemical oxygen demand
River organic nitrogenmg/LInitial organic nitrogen concentration
River ammoniacal nitrogenmg/LInitial ammoniacal nitrogen concentration
River nitritemg/LInitial nitrite concentration
River nitratemg/LInitial nitrate concentration
River organic phosphorusmg/LInitial organic phosphorus concentration
River inorganic phosphorusmg/LInitial inorganic phosphorus concentration
River coliform concentrationMPN/100mlMost probable number of coliforms per 100 ml
River lengthkmLength of river reach to be simulated
Deoxygenation coefficient (K1)d⁻¹Rate of DO removal by BOD decomposition
BOD decomposition coefficient (Kd)d⁻¹Rate of organic matter degradation
BOD settling coefficient (Ks)d⁻¹Rate of BOD removal by sedimentation
Reaeration coefficient (K2)d⁻¹Rate of atmospheric reoxygenation
Organic nitrogen settling coefficient (Kso)d⁻¹Rate of organic nitrogen sedimentation
Organic-ammoniacal nitrogen conversion coefficient (Koa)d⁻¹Rate of Norg → NH₃ conversion
Ammonia-nitrite conversion coefficient (Kan)d⁻¹Rate of NH₃ → NO₂ nitrification
Nitrite-nitrate conversion coefficient (Knn)d⁻¹Rate of NO₂ → NO₃ oxidation
Ammoniacal nitrogen release by settled sediment (Snamon)g/m²/dNH₃ flux from sediment to water column
Ammonia-nitrite conversion oxygen (O2Namon)-Stoichiometric O₂:NH₃ ratio in nitrification
Nitrite-nitrate conversion oxygen (O2Nnitri)-Stoichiometric O₂:NO₂ ratio in nitratation
Low DO nitrification inhibition coefficient (knitr)d⁻¹Nitrification inhibition parameter at low DO concentrations
pH-Water hydrogen potential
Organic phosphorus settling coefficient (Kspo)d⁻¹Rate of organic phosphorus sedimentation
Organic-inorganic phosphorus conversion coefficient (Koi)d⁻¹Rate of Porg → Pinorg mineralization
Coliforms decay rate (Kb)d⁻¹Natural death rate of coliforms
Length of the smaller river basemBottom width of channel (trapezoidal/rectangular sections)
Stream slope-Longitudinal slope of channel
Manning coefficient-Roughness coefficient for hydraulic calculation
Section factor (z)-Bank slope in trapezoidal/triangular sections

Output data

ParameterStandard unitsDescription
Flowm³/sConfirmed volumetric flow rate
River cross section areaWetted area of cross section
DepthmCalculated hydraulic depth
Downstream BOD5kg/m³Final BOD5 concentration at end of reach
Downstream organic phosphorusmg/LFinal organic phosphorus concentration
Downstream inorganic phosphorusmg/LFinal inorganic phosphorus concentration
Downstream nitratemg/LFinal nitrate concentration
Downstream nitritemg/LFinal nitrite concentration
Downstream ammoniacal nitrogenmg/LFinal ammoniacal nitrogen concentration
Downstream organic nitrogenmg/LFinal organic nitrogen concentration
Downstream dissolved oxygenmg/LFinal dissolved oxygen concentration
Downstream coliformsMPN/100mlFinal coliform concentration
Curves-Graphs of spatial evolution of all parameters

References

  • Von Sperling, M. (2007 e 2014). Estudos e modelagem da qualidade da água de rios. DESA-UFMG e Editora UFMG.