Item talk:Q231393
From geokb
{
"USGS Publications Warehouse": { "@context": "https://schema.org", "@type": "Article", "additionalType": "Journal Article", "name": "A comparison of zero-order, first-order, and monod biotransformation models", "identifier": [ { "@type": "PropertyValue", "propertyID": "USGS Publications Warehouse IndexID", "value": "70020693", "url": "https://pubs.usgs.gov/publication/70020693" }, { "@type": "PropertyValue", "propertyID": "USGS Publications Warehouse Internal ID", "value": 70020693 }, { "@type": "PropertyValue", "propertyID": "DOI", "value": "10.1111/j.1745-6584.1998.tb01091.x", "url": "https://doi.org/10.1111/j.1745-6584.1998.tb01091.x" }, { "@type": "PropertyValue", "propertyID": "ISSN", "value": "0017467X" } ], "journal": { "@type": "Periodical", "name": "Ground Water", "volumeNumber": "36", "issueNumber": "2" }, "inLanguage": "en", "isPartOf": [ { "@type": "CreativeWorkSeries", "name": "Ground Water" } ], "datePublished": "1998", "dateModified": "2018-12-21", "abstract": "Under some conditions, a first-order kinetic model is a poor representation of biodegradation in contaminated aquifers. Although it is well known that the assumption of first-order kinetics is valid only when substrate concentration, S, is much less than the half-saturation constant, K(s), this assumption is often made without verification of this condition. We present a formal error analysis showing that the relative error in the first-order approximation is S/K(S) and in the zero-order approximation the error is K(s)/S. We then examine the problems that arise when the first-order approximation is used outside the range for which it is valid. A series of numerical simulations comparing results of first- and zero-order rate approximations to Monod kinetics for a real data set illustrates that if concentrations observed in the field are higher than K(s), it may better to model degradation using a zero-order rate expression. Compared with Monod kinetics, extrapolation of a first-order rate to lower concentrations under-predicts the biotransformation potential, while extrapolation to higher concentrations may grossly over-predict the transformation rate. A summary of solubilities and Monod parameters for aerobic benzene, toluene, and xylene (BTX) degradation shows that the a priori assumption of first-order degradation kinetics at sites contaminated with these compounds is not valid. In particular, out of six published values of KS for toluene, only one is greater than 2 mg/L, indicating that when toluene is present in concentrations greater than about a part per million, the assumption of first-order kinetics may be invalid. Finally, we apply an existing analytical solution for steady-state one-dimensional advective transport with Monod degradation kinetics to a field data set.A formal error analysis is presented showing that the relative error in the first-order approximation is S/KS and in the zero-order approximation the error is KS/S where S is the substrate concentration and KS is the half-saturation constant. The problems that arise when the first-order approximation is used outside the range for which it is valid are examined. A series of numerical simulations comparing results of first- and zero-order rate approximations to Monod kinetics for a real data set illustrates that if concentrations observed in the field are higher than KS, it may be better to model degradation using a zero-order rate expression.", "description": "8 p.", "publisher": { "@type": "Organization", "name": "Wiley" }, "author": [ { "@type": "Person", "name": "Warren, E.", "givenName": "E.", "familyName": "Warren" }, { "@type": "Person", "name": "Godsy, E.M.", "givenName": "E.M.", "familyName": "Godsy" }, { "@type": "Person", "name": "Bekins, B.A.", "givenName": "B.A.", "familyName": "Bekins" } ], "funder": [ { "@type": "Organization", "name": "Toxic Substances Hydrology Program", "url": null } ] }, "OpenAlex": { "abstract_inverted_index": { "Abstract": [ 0 ], "Under": [ 1 ], "some": [ 2 ], "conditions,": [ 3 ], "a": [ 4, 9, 57, 122, 148, 158, 197, 243, 272 ], "first\u2010order": [ 5, 26, 68, 93, 159, 201, 250 ], "kinetic": [ 6 ], "model": [ 7, 145 ], "is": [ 8, 19, 28, 35, 47, 70, 80, 95, 103, 210, 227, 236 ], "poor": [ 10 ], "representation": [ 11 ], "of": [ 12, 25, 52, 107, 112, 157, 181, 200, 216, 220, 249 ], "biodegradation": [ 13 ], "in": [ 14, 66, 74, 131, 238 ], "contaminated": [ 15, 206 ], "aquifers.": [ 16 ], "Although": [ 17 ], "it": [ 18, 102, 140 ], "well": [ 20 ], "known": [ 21 ], "that": [ 22, 62, 89, 127, 195, 233 ], "the": [ 23, 39, 63, 67, 75, 78, 87, 92, 98, 132, 165, 176, 196, 247 ], "assumption": [ 24, 46, 199, 248 ], "kinetics": [ 27, 120, 203, 251, 270 ], "valid": [ 29 ], "only": [ 30, 225 ], "when": [ 31, 91, 234 ], "substrate": [ 32 ], "concentration,": [ 33 ], "S,": [ 34 ], "much": [ 36 ], "less": [ 37 ], "than": [ 38, 136, 229, 241 ], "half\u2010saturation": [ 40 ], "constant,": [ 41 ], "K": [ 42, 81, 137, 221 ], "s": [ 43, 72, 82, 138, 222 ], ",": [ 44, 139 ], "this": [ 45, 53 ], "often": [ 48 ], "made": [ 49 ], "without": [ 50 ], "verification": [ 51 ], "condition.": [ 54 ], "We": [ 55, 84 ], "present": [ 56, 237 ], "formal": [ 58 ], "error": [ 59, 65, 79 ], "analysis": [ 60 ], "showing": [ 61 ], "relative": [ 64 ], "approximation": [ 69, 77, 94 ], "S/K": [ 71 ], "and": [ 73, 114, 183, 190 ], "zero\u2010order": [ 76, 115, 149 ], "/S.": [ 83 ], "then": [ 85 ], "examine": [ 86 ], "problems": [ 88 ], "arise": [ 90 ], "used": [ 96 ], "outside": [ 97 ], "range": [ 99 ], "for": [ 100, 121, 186, 223, 262 ], "which": [ 101 ], "valid.": [ 104, 212 ], "A": [ 105, 179 ], "series": [ 106 ], "numerical": [ 108 ], "simulations": [ 109 ], "comparing": [ 110 ], "results": [ 111 ], "first\u2010": [ 113 ], "rate": [ 116, 150, 160 ], "approximations": [ 117 ], "to": [ 118, 144, 161, 170, 271 ], "Monod": [ 119, 154, 184, 268 ], "real": [ 123 ], "data": [ 124, 274 ], "set": [ 125 ], "illustrates": [ 126 ], "if": [ 128 ], "concentrations": [ 129, 163, 172, 239 ], "observed": [ 130 ], "field": [ 133, 273 ], "are": [ 134 ], "higher": [ 135, 171 ], "may": [ 141, 173, 252 ], "be": [ 142, 253 ], "better": [ 143 ], "degradation": [ 146, 193, 202, 269 ], "using": [ 147 ], "expression.": [ 151 ], "Compared": [ 152 ], "with": [ 153, 207, 267 ], "kinetics,": [ 155 ], "extrapolation": [ 156, 169 ], "lower": [ 162 ], "under\u2010predicts": [ 164 ], "biotransformation": [ 166 ], "potential,": [ 167 ], "while": [ 168 ], "grossly": [ 174 ], "over\u2010predict": [ 175 ], "transformation": [ 177 ], "rate.": [ 178 ], "summary": [ 180 ], "solubilities": [ 182 ], "parameters": [ 185 ], "aerobic": [ 187 ], "benzene,": [ 188 ], "toluene,": [ 189, 224 ], "xylene": [ 191 ], "(BTX)": [ 192 ], "shows": [ 194 ], "priori": [ 198 ], "at": [ 204 ], "sites": [ 205 ], "these": [ 208 ], "compounds": [ 209 ], "not": [ 211 ], "In": [ 213 ], "particular,": [ 214 ], "out": [ 215 ], "six": [ 217 ], "published": [ 218 ], "values": [ 219 ], "one": [ 226 ], "greater": [ 228, 240 ], "2": [ 230 ], "mg/L,": [ 231 ], "indicating": [ 232 ], "toluene": [ 235 ], "about": [ 242 ], "part": [ 244 ], "per": [ 245 ], "million,": [ 246 ], "invalid.": [ 254 ], "Finally,": [ 255 ], "we": [ 256 ], "apply": [ 257 ], "an": [ 258 ], "existing": [ 259 ], "analytical": [ 260 ], "solution": [ 261 ], "steady\u2010state": [ 263 ], "one\u2010dimensional": [ 264 ], "advective": [ 265 ], "transport": [ 266 ], "set.": [ 275 ] }, "apc_list": null, "apc_paid": null, "authorships": [ { "author_position": "first", "author": { "id": "https://openalex.org/A5053558713", "display_name": "B. 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