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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

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2018 Impact Factor: 3.883

Front. Environ. Sci. Eng.    2021, Vol. 15 Issue (1) : 12    https://doi.org/10.1007/s11783-020-1304-3
RESEARCH ARTICLE
Acceleration of the particulate organic matter hydrolysis by start-up stage recovery and its original microbial mechanism
Yanqing Duan1, Aijuan Zhou1,2(), Xiuping Yue1,2(), Zhichun Zhang1, Yanjuan Gao1, Yanhong Luo1,3, Xiao Zhang1
1. College of Environmental Science and Engineering, Taiyuan University of Technology, Taiyuan 030024, China
2. Shanxi Engineer Research Institute of Sludge Disposition and Resources, Taiyuan University of Technology, Taiyuan 030024, China
3. School of Environment and Safety Engineering, North University of China, Taiyuan 030051, China
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Abstract

• Carbon availability was partially solved by POM recovery and fermentation.

• 12% carbon sources were regenerated by fermentation of the entrapped 35% TCOD.

• The unique microbial communities facilitated the efficient hydrolysis of the POM.

• Considerable economic benefits in aeration power and ECS dosage were anticipated.

To address the availability of carbon sources for denitrification, the accelerated hydrolysis of the most abundant but low-availability fraction of particulate organic matter (POM) was investigated. Mesh sieves with different pore sizes were used as primary pretreatment at the start-up-stage of the biological process to separate some POM from the liquid system. The changes in soluble carbohydrates and proteins were monitored to investigate the hydrolysis performance of the sieved POM, with waste activated sludge (WAS) as the control test. The results showed that an average of 35% POM could be entrapped before filtrate mat development. In addition, benefiting from the high polysaccharides concentration, as well as the high availability due to the relatively loose physical structure, a 23% hydrolysis efficiency of POM was obtained, in contrast to that of WAS (3.4%), with a hydrolysis constant of 0.39 h1. The prominent performance was also attributed to the unique microbial communities having been domesticated at a lower temperature, especially the cellulose-degrading bacteria Paraclostridium and psychrophile Psychrobacter, making up 6.94% and 2.56%, respectively. Furthermore, the potential benefits and application of improved POM hydrolysis by start-up stage recovery via mesh sieves combined with anaerobic fermentation were evaluated, including selective POM entrapment, alleviation of blockage and wear, and a reduction in aeration energy. By the proposed strategy, carbon availability for biological nutrient removal (BNR) processes is anticipated to be improved more economically than that can be achieved by primary clarifier elimination.

Keywords Particulate organic matter (POM)      Hydrolysis      Microbial community      Mass balance     
Corresponding Author(s): Aijuan Zhou,Xiuping Yue   
Issue Date: 11 August 2020
 Cite this article:   
Yanqing Duan,Aijuan Zhou,Xiuping Yue, et al. Acceleration of the particulate organic matter hydrolysis by start-up stage recovery and its original microbial mechanism[J]. Front. Environ. Sci. Eng., 2021, 15(1): 12.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-020-1304-3
https://academic.hep.com.cn/fese/EN/Y2021/V15/I1/12
Fig.1  Selective performance of particular organic matter (POM) by micro-sieving: (a) for POM concentration change with different pore size; (b) for particle size distribution before and after micro-sieving with a pore size of 0.131 mm (Note: error bars represent standard deviation).
Parameters Value a)
R-POM WAS
TS (%) 5.4 2.3
TSS (mg/L) 39397±1632 39052±1123
VSS (mg/L) 23240±1518 20693±732
VS/TS 0.59 0.53
TCOD (mg/L) 35642±632 28510±632
TCa/TCOD b) 17.4 9.0
TPr/TCOD b) 31.5 47.0
Lip/TCOD b) 4.06 0.5
SCOD/TCOD 8.3 1.6
C/N 13.1±0.86 5.4±0.6
Cellulose (%) 18.4±1.68 3.79±0.25
N (mg/L) 173±12 244±13
P (mg/L) 23.5±0.8 56±7.2
Tab.1  Characteristics of R-POM and WAS
Fig.2  SEM images being magnified by 5000 times, (a) for WAS collected in the same plant; (b) and (c) for R-POM by sieves with pore sizes of 273 micron and 154 micron, respectively.
Fig.3  Time-course profiles of hydrolysis performance of R-POM and WAS fermentation: (a) for soluble polysaccharides; (b) for soluble proteins; (c) for fitting curve of SCOD release; (d) for hydrolytic enzyme activities (Note: error bars represent standard deviation).
Parameters POM WAS
CPCOD,0
(mg COD/L)
31427±237 26590±306
CSCOD,0
(mg COD/L)
4021±67 1797±14
kH (h1) 0.3928 0.0303
α 5177 12362
R2 0.9919 0.9788
P 0.02 0.05
Tab.2  Modeling statistics of Eq. (1) for the fitting SCOD-time profiles for R-POM and WAS
Fig.4  Taxonomic classifcation of pyrosequences from bacterial communities in R-POM and WAS at phylum (a), class (b) and genus (c) level.
Fig.5  Mass balance of the proposed R-POM entrapment and regeneration based on carbon fractions transformation and conversion (Unit: kg COD/d).
Parameters Units Reference Proposed Empirical formulas adopted
W kg VSS/d 1483 1025 W = W1-W2 + W3
W1 kg VSS/d 1534 1105 W1 = Y×(C0-CeQ/1000
W2 kg VSS/d 681 490 W2 = Kd×Xv×V; Xv = f×X
W3 kg VSS/d 630 410 W3 = f×(SS0-SSe)×Q×30%
Nslu kg N/d 190 137 Nslu = 0.124×Wslu
Nni kg N/d 260 313 Nni = Nin-Nen-Nslu; Nde = Nin
OT kg O2/d 1113 934 OT = Oc + Oni- Ode
Ode kg O2/d -743 -895 Ode = -2.86×Nde
Oni kg O2/d 1187 1430 Oni = 4.57×Nni
Oc kg O2/d 669 399 Oc = 0.51×Cmine
Tab.3  Sludge production and aeration consumption for the two processes
Abbreviation Name Unit
POM Particulate organic matter
BNR Biological nutrient removal
WWTPs Wastewater treatment plants
WAS Waste activated sludge
ECS External carbon sources
ISS Inorganic suspended solids
VSS Volatile suspended solids
TSS Total suspended solids
VFAs Volatile fatty acids
COD Chemical oxygen demand
TCOD Total COD mg COD/L
PCOD Particulate COD mg COD/L
Ss Soluble readily biodegradable COD mg COD/L
SA VFAs components in Ss mg COD/L
SF Non-VFAs components in Ss mg COD/L
Si Soluble inert COD mg COD/L
Xs Particulate slowly biodegradable COD mg COD/L
Xss Settable slowly biodegradable COD mg COD/L
Xi Particulate inert COD mg COD/L
  
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