Characteristics of typical dissolved black carbons and their influence on the formation of disinfection by-products in chlor(am)ination

Highlights

● The physicochemical and structural properties of DBC were characterized.

● The effects of DBC on DBPs and DBPFP generation during disinfection were evaluated.

● The DBPs and DBPFP generation during chlor(am)ination were compared.

Abstract

Dissolved black carbon (DBC) released from biochar can be one of the potential disinfection by-products (DBPs) precursors in the dissolved organic matter pool. However, the physiochemical and structural properties of DBC and the effects on the development of DBPs and DBP formation potential (DBPFP) during the disinfection process remain unclear. In this study, the characteristics of two kinds of DBC, namely, animal-derived DBC (poultry litter DBC, PL-DBC) and plant-derived DBC (wheat straw DBC, WS-DBC), were investigated. The effects of different kinds of DBC on the evolution of DBPs and DBPFP in chlorine and chloramine disinfection processes were compared with natural organic matter (NOM). The results showed that the total DBPs concentrations derived from PL-DBC, WS-DBC and NOM were similar during chlorination (i.e., 61.23 μg/L, 64.59 μg/L and 64.66 μg/L, respectively) and chloramination (i.e., 44.63 μg/L, 44.42 μg/L and 45.58 μg/L, respectively). The lower total DBPs and DBPFP concentrations in chloramination could be attributed to the fact that the introduction of ammonia in chloramine inhibited the breaking of the bond between the disinfectant and the active group of the precursor. Additionally, DBC presented much lower total DBPFP concentrations than NOM in both chlorination and chloramination. However, both kinds of DBC tended to form more monochloroacetic acids and haloacetamides than NOM, which could result from the higher organic strength, higher protein matter, and nitrogen-rich soluble microbial products of DBC.

Graphical abstract

Keywords

Dissolved black carbon (DBC) / Chlorine / Chloramine / Disinfection by-products (DBPs) / Disinfection by-products formation potential (DBPFP)

References

[1] Alfredo K . (2021). The “Burn”: Water quality and microbiological impacts related to limited free chlorine disinfection periods in a chloramine system. Water Research, 197 : 117044

[2] Cabaniss S E , Zhou Q , Maurice P A , Chin Y P , Aiken G R . (2000). A Log-normal distribution model for the molecular weight of aquatic fulvic acids. Environmental Science & Technology, 34( 6): 1103– 1109

[3] Chen W , Westerhoff P , Leenheer J A , Booksh K . (2003). Fluorescence excitation-emission matrix regional integration to quantify spectra for dissolved organic matter. Environmental Science & Technology, 37( 24): 5701– 5710

[4] Chow A T , Dahlgren R A , Zhang Q , Wong P K . (2008). Relationships between specific ultraviolet absorbance and trihalomethane precursors of different carbon sources. Journal of Water Supply: Research & Technology - Aqua, 57( 7): 471– 480

[5] Chu W , Li X , Bond T , Gao N , Yin D . (2015). The formation of haloacetamides and other disinfection by-products from non-nitrogenous low-molecular weight organic acids during chloramination. Chemical Engineering Journal, 285( 1): 164– 171

[6] Chu W H , Gao N Y , Deng Y , Krasner S W . (2010). Precursors of dichloroacetamide, an emerging nitrogenous DBP formed during chlorination or chloramination. Environmental Science & Technology, 44( 10): 3908– 3912

[7] Chuang Y H , Lin A Y , Wang X H , Tung H H . (2013). The contribution of dissolved organic nitrogen and chloramines to nitrogenous disinfection byproduct formation from natural organic matter. Water Research, 47( 3): 1308– 1316

[8] Ding Y , Cawley K M , Da Cunha C N , Jaffe R . (2014). Environmental dynamics of dissolved black carbon in wetlands. Biogeochemistry, 119( 1−3): 259– 273

[9] Dong H Zhang H Wang Y Qiang Z Yang M ( 2021). Disinfection by-product (DBP) research in China: Are we on the track? Journal of Environmental Sciences-China, 110( 7): 99– 110

[10] Du Z , He Y , Fan J , Fu H , Zheng S , Xu Z , Qu X , Kong A , Zhu D . (2018). Predicting apparent singlet oxygen quantum yields of dissolved black carbon and humic substances using spectroscopic indices. Chemosphere, 194 : 405– 413

[11] Fan Z , Yang H , Li S , Yu X . (2020). Tracking and analysis of DBP precursors’ properties by fluorescence spectrometry of dissolved organic matter. Chemosphere, 239 : 124790

[12] Hockaday W C , Grannas A M , Kim S , Hatcher P G . (2006). Direct molecular evidence for the degradation and mobility of black carbon in soils from ultrahigh-resolution mass spectral analysis of dissolved organic matter from a fire-impacted forest soil. Organic Geochemistry, 37( 4): 501– 510

[13] Hockaday W C , Grannas A M , Kim S , Hatcher P G . (2007). The transformation and mobility of charcoal in a fire-impacted watershed. Geochimica et Cosmochimica Acta, 71( 14): 3432– 3445

[14] Hong H , Xiong Y , Ruan M , Liao F , Lin H , Liang Y . (2013). Factors affecting THMs, HAAs and HNMs formation of Jin Lan Reservoir water exposed to chlorine and monochloramine. Science of the Total Environment, 444( 1): 196– 204

[15] Hu J , Song H , Addison J W , Karanfil T . (2010). Halonitromethane formation potentials in drinking waters. Water Research, 44( 1): 105– 114

[16] Hu Y , Qian Y , Chen Y , Guo J , Song J , An D . (2021). Characteristics of trihalomethane and haloacetic acid precursors in filter backwash and sedimentation sludge waters during drinking water treatment. Science of the Total Environment, 775( 25): 145952

[17] Hua G , Kim J , Reckhow D A . (2014). Disinfection byproduct formation from lignin precursors. Water Research, 63( 63C): 285– 295

[18] Hua G , Reckhow D A , Abusallout I . (2015). Correlation between SUVA and DBP formation during chlorination and chloramination of NOM fractions from different sources. Chemosphere, 130 : 82– 89

[19] Hua L C , Lin J L , Chen P C , Huang C . (2017). Chemical structures of extra- and intra-cellular algogenic organic matters as precursors to the formation of carbonaceous disinfection byproducts. Chemical Engineering Journal, 328( 15): 1022– 1030

[20] Jaffé R , Ding Y , Niggemann J , Vähätalo A V , Stubbins A , Spencer R G , Campbell J , Dittmar T . (2013). Global charcoal mobilization from soils via dissolution and riverine transport to the oceans. Science, 340( 6130): 345– 347

[21] Jutaporn P , Laolertworakul W , Tungsudjawong K , Khongnakorn W , Leungprasert S . (2021). Parallel factor analysis of fluorescence excitation emissions to identify seasonal and watershed differences in trihalomethane precursors. Chemosphere, 282 : 131061

[22] Kaal J , Wagner S , Jaffé R . (2016). Molecular properties of ultrafiltered dissolved organic matter and dissolved black carbon in headwater streams as determined by pyrolysis-GC–MS. Journal of Analytical and Applied Pyrolysis, 118 : 181– 191

[23] Kali S , Khan M , Ghaffar M S , Rasheed S , Waseem A , Iqbal M M , Bilal Khan Niazi M , Zafar M I . (2021). Occurrence, influencing factors, toxicity, regulations, and abatement approaches for disinfection by-products in chlorinated drinking water: A comprehensive review. Environmental Pollution, 281( 1): 116950

[24] Kanokkantapong V Marhaba T F Wattanachira S Panyapinyophol B Pavasant P ( 2006). Interaction between organic species in the formation of haloacetic acids following disinfection. Journal of Environmental Science and Health. Part A, Toxic/Hazardous Substances & Environmental Engineering, 41( 6): 1233– 1248

[25] Kim S , Kaplan L A , Benner R , Hatcher P G . (2004). Hydrogen-deficient molecules in natural riverine water samples—evidence for the existence of black carbon in DOM. Marine Chemistry, 92( 1−4): 225– 234

[26] Knicker H . (2007). How does fire affect the nature and stability of soil organic nitrogen and carbon? A review.. Biogeochemistry, 85( 1): 91– 118

[27] Knicker H . (2011). Pyrogenic organic matter in soil: Its origin and occurrence, its chemistry and survival in soil environments. Quaternary International, 243( 2): 251– 263

[28] Le Roux J , Nihemaiti M , Croué J P . (2016). The role of aromatic precursors in the formation of haloacetamides by chloramination of dissolved organic matter. Water Research, 88 : 371– 379

[29] Li A , Zhao X , Mao R , Liu H , Qu J . (2014). Characterization of dissolved organic matter from surface waters with low to high dissolved organic carbon and the related disinfection byproduct formation potential. Journal of Hazardous Materials, 271( 1): 228– 235

[30] Li C Wang D Xu X Wang Z ( 2017). Formation of known and unknown disinfection by-products from natural organic matter fractions during chlorination, chloramination, and ozonation. Science of the Total Environment, 587–588( 1): 177– 184

[31] Liu Z , Xu B , Lin Y L , Zhang T Y , Ye T , Hu C Y , Lu Y S , Cao T C , Tang Y L , Gao N Y . (2020). Mechanistic study on chlorine/nitrogen transformation and disinfection by-product generation in a UV-activated mixed chlorine/chloramines system. Water Research, 184 : 116116

[32] Lu J , Zhang T , Ma J , Chen Z . (2009). Evaluation of disinfection by-products formation during chlorination and chloramination of dissolved natural organic matter fractions isolated from a filtered river water. Journal of Hazardous Materials, 162( 1): 140– 145

[33] Luo Y C , Feng L , Liu Y Z , Zhang L Q . (2020). Disinfection by-products formation and acute toxicity variation of hospital wastewater under different disinfection processes. Separation and Purification Technology, 238( 1): 116405

[34] Maheshwari A , Abokifa A , Gudi R D , Biswas P . (2020). Optimization of disinfectant dosage for simultaneous control of lead and disinfection-byproducts in water distribution networks. Journal of Environmental Management, 276( 15): 111186

[35] Majidzadeh H , Chen H , Coates T A , Tsai K P , Olivares C I . (2019). Long-term watershed management is an effective strategy to reduce organic matter export and disinfection by-product precursors in source water. International Journal of Wildland Fire, 28( 10): 804– 813

[36] Majidzadeh H , Wang J J , Chow A T . (2015). Prescribed fire alters dissolved organic matter and disinfection by-product precursors in forested watersheds - Part I. A controlled laboratory study. ACS Symposium Series, 1190 : 271– 292

[37] Malghani S , Gleixner G , Trumbore S E . (2013). Chars produced by slow pyrolysis and hydrothermal carbonization vary in carbon sequestration potential and greenhouse gases emissions. Soil Biology & Biochemistry, 62 : 137– 146

[38] Marais S S , Ncube E J , Msagati T , Mamba B B , Nkambule T . (2019). Assessment of trihalomethane (THM) precursors using specific ultraviolet absorbance (SUVA) and molecular size distribution (MSD). Journal of Water Process Engineering, 27 : 143– 151

[39] Masiello C A . (2004). New directions in black carbon organic geochemistry. Marine Chemistry, 92( 1-4): 201– 213

[40] Mompremier R , Fuentes Mariles Ó A , Becerril Bravo J E , Ghebremichael K . (2019). Study of the variation of haloacetic acids in a simulated water distribution network. Water Science and Technology: Water Supply, 19( 1): 88– 96

[41] Ndegwa P M . (2004). Solids separation enhances reduction of organic strength of swine manure subjected to aeration treatments. Transactions of the ASAE. American Society of Agricultural Engineers, 47( 5): 1659– 1666

[42] Polubesova T , Chefetz B . (2014). DOM-affected transformation of contaminants on mineral surfaces: A review. Critical Reviews in Environmental Science and Technology, 44( 3): 223– 254

[43] Potvin C M , Zhou H . (2011). Interference by the activated sludge matrix on the analysis of soluble microbial products in wastewater. Chemosphere, 85( 7): 1139– 1145

[44] Qu X , Fu H , Mao J , Ran Y , Zhang D , Zhu D . (2016). Chemical and structural properties of dissolved black carbon released from biochars. Carbon, 96 : 759– 767

[45] Sfynia C , Bond T , Kanda R , Templeton M R . (2020). The formation of disinfection by-products from the chlorination and chloramination of amides. Chemosphere, 248 : 125940

[46] Shi Y , Li S , Wang L , Li J , Shen G , Wu G , Xu K , Ren H , Geng J . (2020). Characteristics of DOM in 14 AAO processes of municipal wastewater treatment plants. Science of the Total Environment, 742 : 140654

[47] Sohi S P , Krull E , Lopez-Capel E , Bol R . (2010). A review of biochar and its use and function in soil. Advances in Agronomy, 105( 1): 47– 82

[48] Thomas C , Kuhlbusch A J . (1998). Enhanced: black carbon and the carbon. Science, 280( 19): 1903– 1904

[49] Tian C , Liu R , Liu H , Qu J . (2013). Disinfection by-products formation and precursors transformation during chlorination and chloramination of highly-polluted source water: significance of ammonia. Water Research, 47( 15): 5901– 5910

[50] Tsai K P , Rogers M F , Chow A T , Diaz A . (2015). Prescribed fire alters dissolved organic matter and disinfection by-product precursor in forested watersheds – Part II. A controlled field study. ACS Symposium Series, 1190 : 293– 306

[51] Uzun H , Zhang W , Olivares C I , Erdem C U , Coates T A , Karanfil T , Chow A T . (2020). Effect of prescribed fires on the export of dissolved organic matter, precursors of disinfection by-products, and water treatability. Water Research, 187( 1): 116385

[52] Wagner S , Jaffé R , Stubbins A . (2018). Dissolved black carbon in aquatic ecosystems. Limnology and Oceanography Letters, 3( 3): 168– 185

[53] Wang J J , Dahlgren R A , Erşan M S , Karanfil T , Chow A T . (2015). Wildfire altering terrestrial precursors of disinfection byproducts in forest detritus. Environmental Science & Technology, 49( 10): 5921– 5929

[54] Wang J J , Ng T W , Zhang Q , Yang X B , Dahlgren R A , Chow A T , Wong P K . (2012). Technical Note: Reactivity of C1 and C2 organohalogens formation – from plant litter to bacteria. Biogeosciences, 9( 10): 3721– 3727

[55] Wei C Fu H Qu X Zhu D ( 2017). Environmental processes of dissolved black carbon. Progress in Chemistry, 29( 9): 1042− 1052 (in Chinese)

[56] Xu F , Wei C , Zeng Q , Li X , Alvarez P J J , Li Q , Qu X , Zhu D . (2017). Aggregation behavior of dissolved black carbon: Implications for vertical mass flux and fractionation in aquatic systems. Environmental Science & Technology, 51( 23): 13723– 13732

[57] Xu Y , Ou Q , He Q , Wu Z , Ma J , Huangfu X . (2021). Influence of dissolved black carbon on the aggregation and deposition of polystyrene nanoplastics: Comparison with dissolved humic acid. Water Research, 196( 15): 117054

[58] Yamashita Y , Kojima D , Yoshida N , Shibata H . (2021). Relationships between dissolved black carbon and dissolved organic matter in streams. Chemosphere, 271 : 129824

[59] Yang B , Fang H , Chen B , Yang S , Ye Z , Yu J . (2021). Effects of reductive inorganics and NOM on the formation of chlorite in the chlorine dioxide disinfection of drinking water. Journal of Environmental Sciences-China, 104 : 225– 232

[60] Yang X , Fan C , Shang C , Zhao Q . (2010). Nitrogenous disinfection byproducts formation and nitrogen origin exploration during chloramination of nitrogenous organic compounds. Water Research, 44( 9): 2691– 2702

[61] Yang X , Shang C , Lee W , Westerhoff P , Fan C . (2008). Correlations between organic matter properties and DBP formation during chloramination. Water Research, 42( 8−9): 2329– 2339

[62] Zhang H , Zhang Y , Shi Q , Hu J , Chu M , Yu J , Yang M . (2012). Study on transformation of natural organic matter in source water during chlorination and its chlorinated products using ultrahigh resolution mass spectrometry. Environmental Science & Technology, 46( 8): 4396– 4402

[63] Zhang Q , Kuang W F , Liu L Y , Li K , Wong K H , Chow A T , Wong P K . (2009). Trihalomethane, haloacetonitrile, and chloral hydrate formation potentials of organic carbon fractions from sub-tropical forest soils. Journal of Hazardous Materials, 172( 2−3): 880– 887

[64] Zhang S , Lin T , Chen H , Xu H , Chen W , Tao H . (2020). Precursors of typical nitrogenous disinfection byproducts: Characteristics, removal, and toxicity formation potential. Science of The Total Environment, 742( 10): 140566

[65] Zhu Z L Yuan-Xin G E Hong-Mei M A Zhao J F ( 2008). Study on characteristics of chlorination reaction of humic acid in different molecular weight ranges. China Water & Wastewater, 24( 19): 101− 105 (in Chinese)

Acknowledgements

We gratefully acknowledge the funding from the National Natural Science Foundation of China (Nos. 52170021, 42177051, and 41977317).

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