- Page 1: Persulfate Persistence and Treatabi
- Page 5 and 6: Abstract Petroleum hydrocarbons (PH
- Page 7 and 8: observed at 1 g/L as compared to 20
- Page 9 and 10: Acknowledgements God, as some cynic
- Page 11: simply conceded to, acknowledging t
- Page 14 and 15: 3.3.1 Methods…………………
- Page 17 and 18: List of Figures Figure 2.1. Persulf
- Page 19: and (b) naphthalene……………
- Page 23 and 24: Chapter 1 Introduction 1.1. GENERAL
- Page 25 and 26: subsurface zones to minimize the or
- Page 27 and 28: 2004; Dahmani et. al, 2006). Brown
- Page 29 and 30: to activated persulfate utilization
- Page 31: is presented here without change. C
- Page 34 and 35: 2.1. INTRODUCTION The treatment of
- Page 36 and 37: persulfate demand of the aquifer so
- Page 38 and 39: at early time to >15 days at later
- Page 42 and 43: This acid-catalyzed reaction was as
- Page 44 and 45: mass of aquifer solids. In general,
- Page 46 and 47: correlation as compared with nNOM o
- Page 48 and 49: Eq. 2.12 can be combined with Eq. 2
- Page 50 and 51: investigation was undertaken to eva
- Page 52 and 53: changes in kobs are consistent with
- Page 54 and 55: porosity)ρparticle/porosity) of 5.
- Page 56 and 57: C/C o pH 1.2 1.0 0.8 0.6 0.4 0.2 10
- Page 58 and 59: C/C o 0 0 10 20 30 40 Time (days) F
- Page 60 and 61: C/C o 1.2 1 0.8 0.6 0.4 0.2 0 0 5 1
- Page 63 and 64: Chapter 3 Stability of Activated Pe
- Page 65 and 66: 3.1. INTRODUCTION Sodium persulfate
- Page 67 and 68: presence of aquifer materials. Whil
- Page 69 and 70: eactions and oxidation mechanisms w
- Page 71 and 72: aquifer materials identified as Bor
- Page 73 and 74: Therefore, the molar concentrations
- Page 75 and 76: After the initial loss, the remaini
- Page 77 and 78: constituents (e.g., FeAm, TOC), but
- Page 79 and 80: where, TOS kobs is the estimated fi
- Page 81 and 82: and rapid oxidation of Fe(II) occur
- Page 83 and 84: C/C o C/C o C/C o 1.2 1 0.8 0.6 0.4
- Page 85 and 86: C/C o C/C o C/C o 1.2 1 0.8 0.6 0.4
- Page 87 and 88: Table 3.1. Summary of experimental
- Page 89: Table 3.3. Summary of the impact of
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4.1. INTRODUCTION Gasoline is one o
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−• − 2− SO 4 + e → SO4 (E
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4.2.2. Experimental Setup Batch exp
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exhibits a higher persulfate degrad
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4.3.1. Unactivated Persulfate Treat
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Huang et al. (2005) observed signif
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further study is required for a bet
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that the alkaline activation of per
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naturally activate persulfate. Enha
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28 days indicates excellent persist
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C/C o C/C o C/C o 1.2 1 0.8 0.6 0.4
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C/C o 2.4 2 1.6 1.2 0.8 0.4 0 0 10
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94 Table 4.2. First-order oxidation
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5.1. INTRODUCTION Gasoline is among
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2− compounds, residual persulfate
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5.2. METHODS 5.2.1. Oxidant Injecti
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persulfate degradation and in conju
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were equilibrated to room temperatu
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The pre-treatment concentration pro
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materials and MGCs. SO and Na + con
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MGC concentrations was observed bet
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occurred quickly (
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Analyses of the organic and inorgan
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116 (a) Figure 5.1(a): Plan view of
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Depth (m) Depth (m) 0 1 2 3 4 5 (c)
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Ethylbenzene (μg/L) Naphthalene (
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M (g/day) ● 10 2 10 1 10 0 Toluen
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Table 5.1 Summary of contaminated s
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• Based on these observations, a
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• Persistence of persulfate was l
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and cumulative mass flow of target
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sampling frequency for different ty
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Houston, A.C., 1913. Studies in Wat
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USEPA, 2006. MTBE in Drinking Water
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Gates-Anderson, D.D., Siegrist, R.L
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CHAPTER 3 Anipsitakis, G.P., Dionys
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Singh, U.C., Venkatarao, K., 1976.
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Huang, K., Couttenye, R.A., Hoag, G
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Zhou, Q., Suna, F., Liu, R., 2005.
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Liang, C., Huang, C., Chen, Y., 200