George Kastl

Dr. George Kastl


Research Focus & Metrics

Academic Career Length

8Years (2019-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 October 2020 in Water Research
Verified
Journal Article
Closed access
ASArumugam Sathasivan
Arumugam Sathasivan
GKGeorge Kastl
George Kastl
SKShashika Korotta-Gamage
Shashika Korotta-Gamage
VGVaruni Gunasekera
Varuni Gunasekera

1 November 2019 in Science of The Total Environment
Verified
Journal Article
Closed access
DRDileepa Rathnayake
Dileepa Rathnayake
ASArumugam Sathasivan
Arumugam Sathasivan
GKGeorge Kastl
George Kastl
KKK.C. Bal Krishna
K.C. Bal Krishna

1 November 2020 in Science of The Total Environment
Verified
Journal Article
Closed access
RRReyad Roy
Reyad Roy
ASArumugam Sathasivan
Arumugam Sathasivan
GKGeorge Kastl
George Kastl

5 October 2022 in Science of The Total Environment
Verified
Journal Article
Closed access
SPSajith Madhawa Premarathna
Sajith Madhawa Premarathna
GKGeorge Kastl
George Kastl
IFIan Fisher
Ian Fisher
ASArumugam Sathasivan
Arumugam Sathasivan

21 February 2025 in Water
Verified
Journal Article
Open access
PDF file
MFMohamed Fawaz FAWZER
Mohamed Fawaz FAWZER
GKGeorge Kastl
George Kastl
KKK.C. Bal Krishna
K.C. Bal Krishna
IFIan Fisher
Ian Fisher
ASArumugam Sathasivan
Arumugam Sathasivan
Using a laboratory-scale system, consisting of a primary disinfection tank (PDT) and three intermittently mixed reactors (R1–R3) in series, bulk water and biofilm contributions to chlorine decay were quantified. The reactors (surface-to-volume ratio: 23.7 m−1; retention time in each reactor: 42.6 ± 1.18 h) were fed with plant-filtered water (PFW). Secondary disinfection was carried out in R1. Free chlorine concentration decreased with travel time (R1: 1.2 mg/L; R2: 0.6 mg/L; and R3: 0.12 mg/L). The bacterial number (ATP) decreased from 67 pg/mL in PFW and remained at ~2–3 pg/mL in R1 and R2 but increased back to 68 pg/mL in R3. First-order chlorine decay rate coefficients decreased from R1 to R2, as expected, but increased by five-fold from R2 to R3. The increased bacterial number (ATP) in R3 and batch chlorine decay tests confirmed that bulk water (soluble compounds, microbes, and sediments) contributed approximately 40% of the decay, and the biofilm contributed 60% in R3. When ATP levels in the reactors were combined with literature data, the bacterial number increased significantly when free chlorine decreased below 0.2 mg/L, but data between 0.2 and 0.5 mg/L are limited. More investigation is needed in the future for chlorine < 0.5 mg/L regarding bacterial regrowth and its effect on bulk water chlorine decay.