Md Rasheduzzaman

Dr. Md Rasheduzzaman

orcid

Research Focus & Metrics

Academic Career Length

10Years (2017-Present)

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

Representative Publications

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17 October 2017 in Environmental Monitoring and Assessment
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Journal Article
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MRM. Tauhid Ur Rahman
M. Tauhid Ur Rahman
FTFaheemah Tabassum
Faheemah Tabassum
MRMd Rasheduzzaman
Md Rasheduzzaman
HSHumayra Saba
Humayra Saba
LSLina Sarkar
Lina Sarkar
AIA. Z. M. Zahedul Islam
A. Z. M. Zahedul Islam

1 March 2017 in Ocean & Coastal Management
Verified
Journal Article
Closed access
MRM. Tauhid Ur Rahman
M. Tauhid Ur Rahman
MRMd Rasheduzzaman
Md Rasheduzzaman
AHArman Habib
Arman Habib
AAAfzal Ahmed
Afzal Ahmed
STSyed Mohammed Tareq
Syed Mohammed Tareq
SMShah Md Muniruzzaman
Shah Md Muniruzzaman

26 January 2020 in Water
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Journal Article
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RSRajveer Singh
Rajveer Singh
Kerry HamiltonKerry Hamilton
Kerry Hamilton
MRMd Rasheduzzaman
Md Rasheduzzaman
ZYZhao Yang
Zhao Yang
SKSaurajyoti Kar
Saurajyoti Kar
Patrick Lee GurianPatrick Lee Gurian
Patrick Lee Gurian
Although many guidance documents have been developed to inform the design and operation of building water systems to ensure safe water quality, there is a lack of consensus on some topics. This study interviewed 22 subject matter experts (SMEs) to identify topics of concern for managing water quality in buildings and compared SME views with information available on these topics in 15 systematically screened important guidance documents. The study found 18 design and 11 operational topics as critical for managing water quality in buildings. No one guidance document addressed all these topics, suggesting that a compendium of available guidance is needed. SMEs most frequently recommended temperature and residual disinfectant measurements as good parameters for monitoring overall building water quality. Both SME and guidance document recommendations for temperature for controlling opportunistic pathogen growth were reasonably consistent with water heater setpoint >60 °C. However, hot water temperature recommendations varied between 50 and 55 °C for other locations (i.e., the water temperature at the tap or end of the return loop). On the contrary, recommendations for disinfectant residual levels (0.2–2.0 mg/L), flushing frequency (1–14 days), and allowable time for hot water to reach the tap (10–60 s) were not consistent. While this study was able to reconcile diverging views on some of the water quality topics, such as identifying common guidance for water heater set point to at least 60 °C, it also highlights lack of definitive guidance on other critical topics, such as residual level, flushing frequency, hot water time to tap, and the use of thermostatic mixing valves, indicating that these are significant knowledge gaps that need further investigation. The study concludes that there is a need for developing evidence-based guidance, particularly on the topics where expert opinions diverged.

1 September 2020 in Water Research
Verified
Journal Article
Closed access
MRMd Rasheduzzaman
Md Rasheduzzaman
RSRajveer Singh
Rajveer Singh
CHCharles N. Haas
Charles N. Haas
PGPatrick L. Gurian
Patrick L. Gurian

5 September 2019 in Water
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Journal Article
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MRMd Rasheduzzaman
Md Rasheduzzaman
RSRajveer Singh
Rajveer Singh
CHCharles N. Haas
Charles N. Haas
DTDienye Tolofari
Dienye Tolofari
HYHamed Yassaghi
Hamed Yassaghi
Patrick Lee GurianPatrick Lee Gurian
Patrick Lee Gurian
Opportunistic premise plumbing pathogens such as Pseudomonas aeruginosa and Naegleria fowleri are a growing concern in building water systems because of their potential risks to human health. The aim of this study was to determine the critical concentrations of P. aeruginosa and N. fowleri in water that are associated with meaningful public health risks. To determine these concentrations, a reverse quantitative microbial risk assessment (QMRA) was conducted. Environmental concentrations of P. aeruginosa and N. fowleri corresponding to the risk target of one micro-disability-adjusted life year (DALY) per person per year and 10−4 annual risks of illness were calculated for several applicable exposure scenarios. To calculate the concentration of P. aeruginosa, cleaning contact lenses with potentially contaminated tap water in the absence of an appropriate cleaning solution was considered. For N. fowleri, two exposure scenarios, recreational exposure (swimming) and nasal cleansing (via the use of a neti pot™ or similar device) were considered. The highest critical concentration for P. aeruginosa was found to be 33 CFU/L with a 95% confidence interval of (2.0, 118) for the drop exposure scenario using the 10−4 annual risk target. For N. fowleri, based on the DALY approach, critical concentrations were 0.000030 N. fowleri/L for swimming and 0.00000060 N. fowleri/L for neti pot™ use scenario. Considering heat inactivation, the critical concentration limits for P. aeruginosa using the DALY approach and the 10−4 annual risk target approach were found to be 0.55 CFU/L and 55 CFU/L, respectively. For N. fowleri, the 10−4 annual risk target approach resulted in 0.022 N. fowleri/L and the DALY approach resulted in 0.00000064 N. fowleri/L for the neti pot™ scenario. For P. aeruginosa, N50 (the median infective dose) and alpha (α) contributed the most and contact rates the least to the variability and uncertainty of the estimates for all the scenarios. For N. fowleri, N50 and contact rates contributed the most and α the least to the variability and uncertainty to calculate the concentrations for all the scenarios. The QMRA framework implemented in this research can be used to incorporate more information regarding opportunistic pathogens to inform management decisions, and to prioritize the best interventions regarding estimated reduction in infections caused by opportunistic pathogens.

ACAlasdair Cohen
Alasdair Cohen
MRMd Rasheduzzaman
Md Rasheduzzaman
ADAmanda Darling
Amanda Darling
Leigh-Anne KrometisLeigh-Anne Krometis
Leigh-Anne Krometis
MEMarc Edwards
Marc Edwards
EMElizabeth T. Rogawski McQuade
Elizabeth T. Rogawski McQuade
Consumption of unsafe drinking water is associated with a substantial burden of disease globally. In the US, ~1.8 million people in rural areas lack reliable access to safe drinking water. Our objective was to characterize and assess household-level water sources, water quality, and associated health outcomes in Central Appalachia. We collected survey data and water samples (tap, source, and bottled water) from consenting households in a small rural community without utility-supplied water in southwest Virginia. Water samples were analyzed for physicochemical parameters, total coliforms, E. coli, nitrate, sulfate, metals (e.g., arsenic, cadmium, lead), and 30+ enteric pathogens. Among the 69% (n = 9) of households that participated, all had piped well water, though 67% (n = 6) used bottled water as their primary drinking water source. Total coliforms were detected in water samples from 44.4% (n = 4) of homes, E. coli in one home, and enteric pathogens (Aeromonas, Campylobacter, Enterobacter) in 33% (n = 3) of homes. Tap water samples from 11% (n = 1) of homes exceeded the EPA MCL for nitrate, and 33% (n = 3) exceeded the EPA SMCL for iron. Among the 19 individuals residing in study households, reported diarrhea was 25% more likely in homes with measured E. coli and/or specific pathogens (risk ratio = 1.25, cluster-robust standard error = 1.64, p = 0.865). Although our sample size was small, our findings suggest that a considerable number of lower-income residents without utility-supplied water in rural areas of southwest Virginia may be exposed to microbiological and/or chemical contaminants in their water, and many, if not most, rely on bottled water as their primary source of drinking water.