Abstract
Federal Regulation 40 CFR §63.670 requires flare operators to specify smokeless design capacity for flares with no visible emissions. Alternatively, 96.5% combustion efficiency (CE) or 98% destruction efficiency must be achieved with threshold limits of minimum combustion zone net heating value (NHVcz) ≥ 270 British thermal unit/standard cubic feet (BTU/scf) for steam-assisted and net heating value dilution parameter (NHVdil) ≥ 22 BTU/ft2 for air-assisted flares. There is still no guarantee for smokeless flaring (SLF) or CE >96.5%. Robust response surface models developed in this study expressed %CE and %Opacity as a function of operating variables for air- and steam-assisted flares. Opacity and CE test data from 1983 to 2016 were analyzed. General quadratic models with transforms of CE and Opacity showed R2 > 0.90, and bivariate sigmoid models for CE showed R2 > 0.87. Two-dimensional (2D) contours illustrate the trends of major operating parameters. Operational setpoints at the incipient smoke point (ISP) and SLF were determined by solving the models subject to NHVcz and NHVdil threshold limits specifying Opacity at 3% (ISP) and 2% (SLF). The predicted steam/air assists/makeup fuel, NHVcz (or NHVdil), and CE at ISP and SLF conditions are compared with the experimental 1984 Environmental Protection Agency (EPA) and 2010 Texas Commission on Environmental Quality flare study ISP test data. These setpoints would help flare operators to establish ISP or SLF conditions either by adding makeup fuel to vent gas with low heating value or by minimizing the assist without adding makeup fuel for steam- and air-assisted flares.
Introduction
Flares are an important safety device for pressure relief from process units and storage vessels, especially during start-up, shutdown, and malfunction situations. Flares dispose of purged and waste products from refineries, gaseous wastes from chemical processing, vent gases from furnaces and coke ovens, and unrecoverable gases from oil/gas industries (U.S. EPA, 2018b). Russia leads the top 30 flaring countries (19.9 billion cubic meters [bcm] in 2017), while the United States ranks fourth, flaring 9.5 bcm in 2017 according to World Bank satellite data (Korppoo, 2018; World Bank, 2018). Flare emissions consist of unburned fuel (methane and unburned volatile organic compounds) and combustion byproducts such as soot, CO, CO2, oxides of nitrogen, and sulfur (Singh et al., 2014a). These emissions have direct health impacts associated with exposure and indirect health impacts like the resulting ozone formation. For instance, flares account for 61% of the highly reactive volatile organic compounds (HRVOCs) emissions based on the 2007 HRVOC special emissions inventory data collected from the projects undertaken by the facilities in Harris County, Texas (ENVIRON, 2008, 2009).
Flaring can also emit black carbon (BC) as a by-product, which is an anthropogenic forcer of climate with public health implications (Anenberg et al., 2012; Bond et al., 2013; Stohl et al., 2013; Schwartz et al., 2015). Gas flaring dominates the estimated BC emissions in the Arctic, while it contributes to 3% of global BC emissions (Stohl et al., 2013). During its short life time for a few days, 1 g of BC warms the atmosphere several hundred times >1 g of CO2 does in 100 years (Jacobson et al., 2013). Control of BC and VOC emissions from flaring is an important issue from the environmental standpoint.
Destruction efficiency (DE) and combustion efficiency (CE) are common indicators of flare performance in addition to smoke generated by incomplete combustion of hydrocarbons (Schwartz et al., 2001; U.S. EPA, 2012).
Federal regulations (40CFR60.18 and 63.670) require smokeless flaring (SLF), which motivates flare operators to oversteam or overair to suppress smoke at the expense of CE. Recently, Environmental Protection Agency (EPA), in addition to combustion zone net heating value (NHVcz) requirements, required steam-assisted flares with the perimeter assist air intentionally entrained in lower and upper steam at the flare tip of diameter <9 in. needs to meet net heating value dilution parameter (NHVdil) ≥ 22 BTU/ft2. Flare operators should establish the smokeless capacity in a 15-min block average to ensure 98% DE or 96.5% CE or higher at all times, and assess the exceedance of the smokeless capacity based on cumulative volumetric flow rate and/or flare tip velocity (U.S. EPA, 2018a). Still, there is no guarantee that CE will be ≥96.5% (Fry and Coburn, 2012; Zeng et al., 2016).
Furthermore, many operation parameters such as steam assist (S) and air assist (A) used to combust vent gas, flare tip exit velocity (V), vent gas composition (carbon to hydrogen molar ratio [CHR]), net heating value (NHV), flare tip diameter (D), and wind speed (u) affect flare performance by influencing soot formation and unburned VOC emissions (Castiñeira and Edgar, 2006; Allen and Torres, 2011a, 2011b; Levitsky, 2011). All these issues lead to questions of operating flares in a most environmentally responsible and cost-effective manner in compliance with regulations, achieving SLF, and still maximizing CE under a given set of design and operating conditions.
Few studies were performed to predict flare emissions and performance using computational fluid dynamics (CFD) and WRF-SMOKE-CMAQ modeling system (Singh et al., 2012, 2014a, 2014b; Pan et al., 2015; Damodara et al., 2017). Field measurements (such as FTIR, MEMS, EI, LIF, and REMPI) for estimating flare efficiency are expensive and difficult to deploy on-site, even though the remote, optical CE measurement technology developed by Providence Photonics (Zeng et al., 2016) has gained much attention. Detailed CFD flare modeling based on rigorous kinetic mechanisms is also comparatively expensive and time-consuming. As a result, this study seeks to develop easy-to-use response surface models in quadratic form and sigmoid functions to predict the flare performance in terms of operational parameters based on the experimental study with soot and CE data. Quadratic form is the highest order linear regression in response surface methodology apt to model a curved relationship between input variables and the responses.
Similarly, sigmoid function is a nonlinear regression used to model curve relationships, and mathematically explain relation between a response and one or more predictor variables. Both functions can yield graphs to show curvatures (Minitab, 2018). Logit functions of response variables showed better data distribution and more accurate fitting. Bivariate sigmoid functions are developed with major parameters NHVcz (or NHVdil) and V per 40 CFR 63.670 requirements for flares. Two-dimensional contours illustrate the trends of major operating parameters.
Large and varying time delays in gas chromatograph (GC) analysis (15–20 min) in vent gas heating value measurements, nonlinear behavior of flaring process with wide variation in waste gas stream flow, and use of N2 as a purge gas to maintain positive pressure in the vent gas pipes were the major challenges in flaring control. Model-Free Adaptive control (Cybosoft, 2016) and steam to hydrocarbon ratio control with feed-forward action minimized the time delays caused by GC analysis and overcame those challenges with robust performance (Srinivasarao and Krishna, 2015, 2017).
Since various parameters affect the flare performance, simple guidelines for SLF were elusive (ENVIRON, 2009; U.S. EPA, 2009, 2015). Therefore, setpoints to adjust steam/air or makeup fuel in a feed-forward control based on a prediction model to ensure smokeless combustion are critical. The second objective of this study is to determine the operation setpoints for S (or A) and makeup fuel volumetric flow rate (
Methodology
Data source and analysis
The experimental data for response surface models collected from previous flare study reports include flare efficiency study (McDaniel, 1983), evaluation of the efficiency of industrial flares (Pohl et al., 1984), 2010 Texas Commission on Environmental Quality (TCEQ) flare study final report (Allen and Torres, 2011a, 2011b), Marathon Petroleum company flare study report (Cade and Evans, 2010; Roesler et al., 2010), Carleton University soot emission rate measurements (Corbin and Johnson, 2014a, 2014b), and Providence Photonics data (Zeng et al., 2016). Data collected from the literature include the geometry of steam-, air-, and nonassisted flares, meteorological data (crosswind speed/direction), operating data (aeration, steaming, exit velocity, waste gas/pilot fuel species), flare efficiencies, and soot emission.
Table 1 shows the data sources and the range of the variables used in response surface models. Since the flare tests conducted include different fuel mixtures such as propylene, propane, natural gas, methane, ethylene, and typical refinery fuel, the presence of π-bond (Pivg) in vent gas, π-bond in the combustibles (Picz), carbon number (CN) and CHR of vent gas were introduced to account for the effect of vent gas composition. The presence of π-bonds is highly correlated with the SP2 hybridization of carbon atoms, which increases the absorption efficiency of carbon when it cools down due to large number of free charge careers resulting in higher electron density caused by π-bonds (Jager et al., 1999). Alkenes with higher CHR have π-bonds, which are highly correlated with SP2 hybridization of carbon atoms, which may lead to higher Opacity as absorption efficiency increases due to high electron density. π-Bonds and σ-Bonds section in Supplementary Data (as shown in Supplementary Fig. S1) discuss π-bond and its presence in different molecules and compounds.
Data Sources used in Response Surface Models
TCEQ, Texas Commission on Environmental Quality; TNG, Tulsa natural gas.
Flare data include a wide range of diameters 1.5–3 in. for laboratory-scale flares and 3–36 in. for industrial flares. Only two of R, u, and V are selected interchangeably as the independent variables to analyze their effect on the response variables. In other words, R and u represent two degrees of freedom as u and V. Models developed including R in conjunction with u help us analyze the effect of V at a constant u. Modeling trials showed CE models developed with R and u and Opacity models developed with u and V predicted better with high R2 values. Variable transform methods such as logit and log functions showed better distributions for CE and Opacity (Supplementary Fig. S2). Therefore, air-assisted flare models were developed with Logit (100–CE) and Logit Opacity as the response variables. Since Absorbance (Abs) is equivalent to 2–log (100–Opacity) (Gallik, 2017), steam-assisted flare models were developed with Logit (100–CE) and Log Abs as the response variables.
CE reported in 2010 TCEQ flare study report (Allen and Torres, 2011a, 2011b) were corrected for soot emissions to a maximum of 0.2% based on revised data provided by Aerodyne Research, Inc. (Aerodyne Research Inc, 2010; Fortner et al., 2012). To develop the precise model equations, CE was recalculated considering the soot emissions as expressed in the following equation:
where soot is the volume concentration of BC particles (molecular weight [MW] = 12.01) in the plume (parts per million by volume, ppmv) after combustion has ceased.
According to Allen and Torres (2011a, 2011b), NHVcz is defined as
where
NHVdil is defined by U.S. EPA (2015) as
where NHVdil is the net heating value dilution parameter (BTU/ft2) and
General quadratic response surface modeling
Generalized response surface models were established using Minitab 18 statistics toolbox (Minitab, 2018). Initially, a linear model is developed, and then the model is validated based on R2, adjusted R2, predicted R2, and analysis of variance table to check the adequacy of each parameter for the response (Ma et al., 2015). The significance of the coefficients in the model was determined based on p-value (Homayoonfal et al., 2015). If a linear model is not appropriate, then a quadratic model is developed to show the curvature in response surface (Minitab, 2018). The interaction terms with significant effects were added to the model for better fitting by the stepwise regression option in Minitab while performing response surface analysis. Outliers were removed in each step based on standardized residual plot analysis, and then recursive regression was performed to develop the final model (Model Validation section, Best Subsets Regression: Logit (%Opacity) Versus A, CHR, D, V, u, NHVdil, section as shown in Supplementary Table S1, Removal of Outliers section, and Validation of the Model Logit (100–%CE) Versus A, CHR, D, R, NHVdil section in Supplementary Data as shown in Supplementary Fig. S3).
The quadratic form of the response surface model is expressed as
where Z is the response variable, X is the operational variable, i = 1 to n (n—the number of variables), e is the residual error, a0 is the constant term, ai are the linear coefficients, aii are the quadratic coefficients, and bij are the interaction coefficients. The coefficients were determined by solving the regression equation using the experimental values of operational variables, so that the residual error is minimized. 80% of the data were randomly selected using Excel for model development, and the remaining 20% data were used for model validation, such that the data used in model validation lie within the range of the variables used in models. VE (variance explained, %) and MAE (mean absolute error, %) (Li, 2017) are reported as accuracy and error measures for the Opacity and CE back-calculated from the response variables (Accuracy and Error Measures section in Supplementary Data).
Statistically significant and highly correlated variables determined by Best Subsets Regression method are V, u, A, NHVdil, D, and CHR for Logit Opacity and A, CHR, NHVdil, and R for Logit (100–CE) models for air-assisted flares. CHR, CN, NHVcz, S, V, and u were found to have a significant effect on Log (Abs), while CHR, CN, NHVcz, R, S, and u had a significant effect on Logit (100–CE) for steam-assisted flares.
Sigmoid models
Sigmoid function is a nonlinear function that fits the data, which do not exhibit general linear behavior (Bates and Watts, 1988; Bates and Chambers, 1992; Fox, 2008; Smith, 2012). This function forms an “S” shape (sigmoid curve) and is expressed as
Equation (5) is modified by introducing a coefficient “a” to the exponent “e” and substituting NHVcz (combustion zone parameter) for t, and then CE is expressed as
CE exhibited an “S” shape characteristic of the sigmoid function when plotted against NHVcz in a previous study (Smith, 2012). Parameters a and b were estimated using the curve fitting toolbox of MATLAB (Mathworks, 2015). As the numerical methods used in these algorithms are sensitive to initial guess, a proper initial guess is critical for better prediction (Galant, 1975; Ratkowsky, 1990). Initial guess was estimated by minimizing the errors using Excel Solver.
Bivariate model for CE was developed with NHVcz and flare tip exit velocity as the independent variables for the data range shown in Table 2. The coefficient of NHVcz in Equation (6) has been parameterized to become a linear function of V (promotes fuel-air mixing) to adjust for the slope change of the sigmoid function at the inflection point due to V. The location of the inflection point is also parameterized as d+e * V, and the bivariate sigmoid function is expressed as follows:
Steam-Assisted Flare Test Data Ranges Used in Response Surface Models
Source: Data are from references (McDaniel, 1983; Pohl et al., 1984; Aerodyne Research Inc., 2010; Cade and Evans, 2010; Roesler et al., 2010; Allen and Torres, 2011a, 2011b; Fortner et al., 2012; Corbin and Johnson, 2014a, 2014b; Zeng et al., 2016).
BTU, British thermal unit; CE, combustion efficiency; CHR, carbon to hydrogen molar ratio; CN, carbon number; NHVcz, combustion zone net heating value; scf, standard cubic feet.
Finally, Equation (8) is derived by multiplying the two components of the exponent “e” in Equation (7), and the simplified quadratic function is expressed as
In a similar method, univariate and bivariate sigmoid models for CE were developed involving NHVdil and V for air-assisted flares.
Setpoint determination of operation variables
Response surface models for Opacity are solved by equating the models to 3% (ISP) and 2% (SLF) based on the ISP characterization (Chen and Alphones, 2019) using the Newton-Raphson method in Polymath to determine the setpoints for steam (or air assist) and makeup fuel specifying NHVcz ≥ 270 BTU/scf for steam-assisted or NHVdil ≥ 22 BTU/ft2 for air-assisted flares. The initial values are chosen to solve the Opacity models for the minimum steam (or air assist) with minimum makeup fuel flow rate (
Setpoint determination for steam-assisted flares
Equations (10) and (11) were solved for S and NHVcz by specifying makeup fuel flow rate,

Setpoint determination for air-assisted flares
Equations (13) and (14) were solved for A and NHVdil by specifying

Results and Discussions
General quadratic response surface models
Response surface models for steam-assisted flares
Response surface models were developed for the transformed response variables Log Abs and Logit (100–CE) to fit the steam-assisted flare data range shown in Table 2. As the parameters representing vent gas species, CHR, and Pivg are highly correlated (Pearson's correlation coefficient >0.7), two sets of models were developed for Opacity and CE, one with CHR and other with Pivg. Table 3 shows the final models with N (number of data points), R2, and R2 (Adj), including VE% and MAE% values for the back-calculated Opacity and CE. Based on the accuracy measure expressed as VE%, error measure expressed as MAE%, R2, and number of terms, the best model was chosen for further analysis and setpoint determination.
General Quadratic Model Equations for Steam-Assisted Flares
Units and the data range for the models are provided in Table 1; R2 and R2(Adj) represent the correlation between experimental and predicted Logit functions, while MAE% and VE% are between the experimental and the predicted CE or Opacity.
MAE, mean absolute error; MW, molecular weight; VE, variance explained.
Figure 3 indicates good correlation between the experimental and predicted values for the Logit (100–CE) model. Table 4 shows the parameter estimates and their coefficients with 95% confidence interval and p-values for Logit (100–CE) model. The significance of the parameters was determined from their p-values <0.001 and standard error values smaller than the estimated coefficient values (Ghoreishian et al., 2016). Likewise, the parameters and their coefficients in Log Abs model were validated based on 95% confidence interval and p-values.

Comparison of experimental and predicted values of the Logit (100–CE) model for steam-assisted flares.
Coded Coefficients of the General Quadratic Model Logit (100–CE) for Steam-Assisted Flare Test Data
CI, confidence interval; SE, standard error.
Effect of operating parameters on Opacity and CE for steam-assisted flares
The effect of major parameters on the predicted Opacity from the Log Abs model was illustrated by 2D contour plots, while other parameters were fixed at certain values. Figure 4A and B show the 2D contour plot for predicted Opacity versus NHVcz, V at two different levels of CHR (0.38 for 100% propane and 0.43 for propylene and Tulsa natural gas [TNG] mixture), while S, u, and CN are fixed. The contour lines in the 2D plots are intended to show the effect of the operating parameters based on proposed models, while the black dots represent the experimental data.

Figure 4A and B shows Opacity decreases at a high V (∼400 ft/s). At a low value of V (V < 5 ft/s), the Opacity increases even when there is an increase in NHVcz. Higher flare tip exit velocity leads to better fuel-air mixing compared with lower flare tip exit velocity, which results in poor fuel-air mixing and soot formation. Furthermore, Opacity is higher for propylene and TNG mixture than propane due to the relatively high soot formation potential of alkenes compared with alkanes.
Figure 5A and B shows the 2D contour plot for predicted CE from the Logit (100–CE) model versus NHVcz, R at two different levels of CHR (0.5 for 100% propene and 0.38 for 100% propane), while S, u, and CN are fixed. Figure 5A and B shows that CE decreases with increase in R for the range of NHVcz, which substantiates the conclusion that CE increases with increase in exit velocity at a constant crosswind speed for the available data range, and the factors promoting mixing of fuel with steam have a significant effect on combustion. The proposed response surface models are simple quadratic equations applied to predict wide range of experimental data flaring different vent gas mixtures.

Response surface models for air-assisted flares
Similarly, response surface models were developed for Logit Opacity and Logit (100–CE) to fit the air-assisted flare test data shown in Table 5. As in the steam-assisted flares, only one of CHR and Pivg or Picz is selected for modeling Opacity and CE for air-assisted flares. Table 6 shows the models, N (number of data points), R2, and R2 (Adj) values, including VE% and MAE% values for the back-calculated Opacity and CE. From the models shown in Table 6, it is clear that A, V, and u (factors influencing mixing), D (laboratory-scale to industrial size flare tips), CHR (for vent gas species), and NHVdil (dilution parameter) have a significant effect on Logit Opacity, while R (replacing u and V), D, A, CHR, and NHVdil have a significant effect on Logit (100–CE). The coefficients of assist air in the models imply that increase in assist air decreases the soot emission but increases the emission of unburned VOCs, thereby reducing the CE (Allen and Torres, 2011a, 2011b).
Data Ranges Used in Response Surface Models: Air-Assisted Flares
Source: Data are from references (McDaniel, 1983; Aerodyne Research Inc., 2010; Allen and Torres, 2011a, 2011b; Fortner et al., 2012; Corbin and Johnson, 2014a, 2014b; Zeng et al., 2016).
NHVdil, net heating value dilution parameter.
General Quadratic Model Equations for Air-Assisted Flares
Units and the data range for the models are provided in Table 4; R2 and R2(Adj) represent the correlation between experimental and predicted Logit functions, while MAE% and VE% are between the experimental and the predicted %CE or %Opacity.
Effect of operating parameters on Opacity and CE for air-assisted flares
Opacity predicted by the Logit Opacity model is plotted against NHVdil and CHR at two levels of A (1,000 and 4,000 lb/millions of BTU [MMBTU]), while other variables were fixed, to analyze the response for change in predictors. Figure 6A and B shows that Opacity increases in the direction toward high CHR and low NHVdil. Opacity can be higher at a lower NHVdil due to a lower flame temperature caused by a lower NHVvg since air assist is fixed at a certain value. Opacity is higher for alkenes (CHR = 0.5) at lower NHVdil than for alkanes. The contour lines in the 2D plots are intended to show the effect of the operating parameters based on proposed models, while the black dots represent the experimental data.

Figure 7A and B shows the 2D contour plot for predicted CE from the Logit (100–CE) model versus NHVdil, R at two different levels of A, while other variables are fixed. From the Fig. 7A and B, it is observed that CE decreases with an increase in A. Also, increasing R, that is, increasing u or decreasing V, or decreasing NHVdil lowers CE. Hence, the factors influencing the mixing of fuel with air (R and A) have a significant effect on combustion.

Sigmoid models
Sigmoid models for steam-assisted flares
Table 7 shows the univariate and bivariate sigmoid models for CE and corresponding model statistics. The data range for CE, NHVcz, and V used in these models is shown in Table 2. Twenty-three outliers were removed out of 280 total data points, and the remaining 257 data points were used in univariate models. The univariate sigmoid function is presented to show the derivation of bivariate quadratic equation from a simple sigmoid function. Figure 8 shows a curvature for the univariate model. Since the response variable CE showed a curvature when plotted against NHVcz, a quadratic form of bivariate sigmoid function was developed further to analyze the effect of important predictors (NHVcz and V) on the response using response surfaces. Figure 9 shows the 2D contour plot for the response CE versus NHVcz, V. The proposed quadratic bivariate form of sigmoid function produced reasonable contours for CE versus NHVcz and V.

CE versus NHVcz sigmoid fit for steam-assisted flares.

Two-dimensional contour plot of CE versus NHVcz, V, Vmax, and VISP for steam-assisted flares.
Univariate and Bivariate Sigmoid Model Equations for Steam-Assisted Flares
Two hundred fifty-seven data points are used in these models.
Two hundred thirty-three data points are used in these models.
RMSE, root mean square error.
A correlation for maximum exit velocity and NHVcz is derived from the EPA relation (ECFR, 2015; U.S. EPA, 2015).
According to Chen and Alphones (2019), the exit velocity at the ISP is expressed as
Vmax and VISP have been calculated for various values of NHVcz using these correlations and plotted on the contours of CE in Fig. 9.
Vmax and VISP for various values of NHVcz obtained from the above correlations are substituted in the CE model, and the results are shown in Supplementary Table S2 and S3. Figure 9 shows that CE drops at a low velocity (V < 3 ft/s) for NHVcz < 260 BTU/scf. Furthermore, there is approximately one order of magnitude difference between Vmax and VISP at the same NHVcz (Chen and Alphones, 2019). The graph also indicates that CE remains high for NHVcz > 350 BTU/scf even if the exit velocity exceeds Vmax specified by EPA.
Sigmoid models for air-assisted flares
Table 5 shows the data range of V, NHVdil, and CE used to develop the univariate and bivariate sigmoid models for CE shown in Table 8. Figure 10 shows the sigmoid plot for the univariate model. Since the response variable CE showed a curvature when plotted against NHVdil, a quadratic form of bivariate sigmoid function was developed further to analyze the effect of important predictors (NHVdil and V) on the response. Table 8 indicates significant improvement from univariate to bivariate sigmoid function with two parameters (R2(Adj) changes from 0.83 to 0.91 for bivariate sigmoid with the same number of data points). Figure 11 shows the 2D contour plot of response variable CE on NHVdil and V plane. The proposed quadratic bivariate form of sigmoid function produced reasonable contours for CE versus NHVdil and V. To maintain CE ≥96.5%, NHVdil must be greater than the threshold value ranging from 22 to 500 BTU/ft2 over a range of exit velocities as shown in Fig. 11.

CE versus NHVdil sigmoid fit for air-assisted flares.

Two-dimensional contour plot of CE versus NHVdil, V for air-assisted flares.
Univariate and Bivariate Sigmoid Model Equations for Air-Assisted Flares
One hundred two data points are used in these models.
Setpoint determination for steam/air-assisted flares
Based on the ISP characterization for steam- and air-assisted flares, the calculated Opacity range was 1.5–6.6% with an average of 3% Opacity. Ringelmann number 1 corresponds to 20% Opacity, 0.5 corresponds to 10%, and 0.25 corresponds to 5% (Stockham and Betz, 1971; Terry and Ashley, 2013). As the recent EPA regulations require SLF, Opacity <5% is preferred at the discretion of the flare operators.
Setpoint determination for steam-assisted flares
Table 9 shows the comparison of experimental and predicted S, NHVcz, the required
Summary of Setpoints for Steam-Assisted Flares at Incipient Smoke Point
Exp, experimental; MMBTU, millions of BTU; Pred, predicted.
Summary of Setpoints for Steam-Assisted Flares at Smokeless Flaring
Comparison of setpoints at ISP and SLF for steam-assisted flares
Figure 12A–C shows the comparison of predicted S, NHVcz, and CE (at ISP and SLF) with experimental values for steam-assisted flares. The average of predicted setpoints for steam assist (31 lb/MMBTU at the ISP and 45 lb/MMBTU at SLF) lies below the experimental steam assist, 57 lb/MMBTU (geometric mean, x50) for ISP test cases. Since no makeup fuel is required at ISP and SLF, the NHVvg,req remains the same. The discrepancy between the predicted ISP steam/makeup fuel and experimental data can be attributed to (1) the simplicity of the quadratic form even with the transforms; (2) the observed ISP's uncertainties caused by human observation errors (as seen by the wide variations in characterized Opacity, CE, heating value, etc. at the ISP); and (3) the ISP or SLF can be achieved in multiple states experimentally by simultaneously increasing NHVvg,req (NHVvg and makeup fuel) and the diluent (steam) for better mixing. Due to minimization of steam assist at ISP and SLF, the predicted CE is maximized (98.6% at ISP and 98% SLF) compared with 97.6% for the experimental ISP cases.

Setpoint determination for air-assisted flares
Table 11 shows the comparison of experimental and predicted values of A, NHVdil, CE, and the required
Summary of Setpoints for Air-Assisted Flares at the Incipient Smoke Point
Table 12 shows the comparison of experimental and predicted values at SLF. Since NHVdil is a function of A and NHVvg,req with
Summary of Setpoints for Air-Assisted Flares at Smokeless Flaring
Comparison of setpoints at ISP and SLF for air-assisted flares
Figure 13A–D shows the comparison of predicted and experimental values of A, NHVdil,

Conclusions
General quadratic response surface models for transformed Opacity (Log Abs for steam and Logit Opacity for air) and CE were developed for both steam- and air-assisted flares based on the experimental flare study data collected from 1983 through 2016 for which soot and CE values were available. Reported CE in the literature was corrected for soot emissions. The major conclusions of this study are as follows:
The goodness-of-fit (R2) values for CE and Opacity models with the operation parameters were 0.93 and 0.91 for steam-assisted flares and 0.98 and 0.95 for air-assisted flares, respectively. Best subsets regression method was used to determine the best set of variables for the Opacity and CE models. The parameters that influence mixing with ambient air for the flares with tips ranging from laboratory scale to industrial scale burning vent gas species with natural gas mixtures (C1) to olefin mixtures (C2 and C3) and the NHVdil were found to have a significant effect on Opacity and CE models developed for air-assisted flares. The parameters that influence mixing with ambient air for the flares burning vent gas species with natural gas mixtures (C1) to olefin mixtures (C2 and C3) and the NHVcz were found to have a significant effect on Opacity and CE models developed for steam-assisted flares. Bivariate sigmoid models for steam- and air-assisted flares showed a good agreement with the experimental data with the goodness of fit >0.9. Two-dimensional contours developed to analyze the effect of major parameters on the response variable CE showed that the NHVcz >270 BTU/scf (for steam-assisted flares) and NHVdil > 22 BTU/ft2 (for air-assisted flares) are required to achieve CE >96.5%. The discrepancy between the predicted steam assist/air assist/makeup fuel and experimental data may arise from (1) the simplicity of the quadratic form of the response surface models; and (2) the uncertainties caused by human observation errors of Opacity as seen from the wide variations in characterized Opacity values at the ISP; and (3) the existence of multiple states experimentally with simultaneous increase of vent gas heating values and steam/air assists. Setpoints would help flare operators to establish ISP or SLF conditions either by adding makeup fuel to the vent gas with low heating value along with the assist or by minimizing the air or steam assist alone. From an economic standpoint,
Footnotes
Acknowledgments
We specially thank Ed Fortner and Scott Herndon of Aerodyne Research Inc., Scott Evans from Clean Air Engineering, Dr. Darcy Corbin and Dr. Matthew Johnson from Carleton University, and Dr. Yousheng Zeng from Providence Photonics for providing the flare test data.
Author Disclosure Statement
No competing financial interests exist.
Disclaimer Language
The content, findings, opinions, and conclusions are the work of the author(s) and do not necessarily represent findings, opinions, or conclusions of the TCEQ.
Funding Information
The authors gratefully acknowledge the financial support from TCEQ Grant for Activities Program (Project # 582-10-94307-FY14-06), TCEQ Supplemental Environmental Program (SEP Agreement No. 2009-009), and the Texas Air Research Center (TARC Grant #079LUB0096A).
Nomenclature
Subscripts:
References
Supplementary Material
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