Submitted:
26 May 2025
Posted:
27 May 2025
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Abstract

Keywords:
1. Introduction
1.1. Research Questions
- What IoT technologies are currently used to monitor nitrogen, phosphorus, and carbon in agricultural and aquatic environments?
- What are the key technical, financial, and infrastructural barriers to successful implementation of IoT-based nutrient monitoring systems?
- How do limitations in reporting, system accuracy, and connectivity affect the performance and scalability of these systems?
- What potential exists for integrating IoT with advanced technologies such as AI, cloud computing, and machine learning to improve nutrient monitoring?
- What factors influence user adoption and long-term sustainability of IoT-enabled macronutrient monitoring solutions, especially in low-resource settings?
1.2. Research Rationale
1.3. Research Objectives
- Identify current IoT practices and technologies used in nutrient monitoring;
- Examine implementation barriers such as high costs, limited reporting of system architecture, and lack of standardization;
- Analyze trends in sensor use, connectivity, cloud integration, and data processing techniques;
- Assess how IoT-enabled systems contribute to improving nutrient tracking accuracy and supporting real-time decision-making;
1.4. Research Contributions
- Identified how IoT is used for macronutrient monitoring, with a focus on eutrophication control, water quality, and precision agriculture.
- Found that 75% of studies did not report microcontroller use, and 70.24% omitted connectivity details, highlighting a lack of system transparency.
- Categorized IoT systems into basic (sensor-only), intermediate (cloud-connected), and advanced (AI-integrated) stages based on reported implementations.
- Showed that 42.86% of studies used statistical models, with some reporting accuracies up to 98.67%, despite many lacking performance metrics.
- Provided guidance on standardization, scalability, and policy relevance to support improved implementation of IoT-based nutrient monitoring systems.
1.5. Research Novelty
2. Materials and Methods
2.1. Eligibility Criteria
2.2. Information Sources
2.3. Search Strategy
2.4. Selection Process
2.5. Data Collection Process
2.6. Data Items
2.6.1. Data Collection Method
2.6.2. Definition of Collected Data Variables
2.7. Study Risk of Bias Assessment
2.8. Effect Measures
2.9. Synthesis
2.9.1. Eligibility for Synthesis
2.9.2. Data Preparation for Synthesis
2.9.3. Tabulation and Visual Display of Results
2.9.4. Synthesis of Results
2.9.5. Exploring Causes of Heterogeneity
2.9.6. Sensitivity Analyses
2.10. Reporting Bias Assessment
2.11. Certainty Assessment
3. Results
3.1. Study Selection
3.2. Study Characteristics
3.3. Risk of Bias in Studies
3.4. Results of Individual Studies
3.5. Results of Synthesis
3.5.1. Examining Study Characteristics and Potential Biases

3.5.2. Statistical Syntheses
3.5.3. Exploring Variations in Data
3.5.4. Sensitivity Analyses Results
3.6. Reporting Biases
3.7. Certainty of Evidence
4. Discussion
4.1. Interpretation of Findings in the Context of Prior Studies and Working Hypotheses
4.2. Limitations of the Evidence Included in the Review
4.3. Limitations of the Review Process Used
4.4. Implications for Practice, Policy, and Future Research
5. Conclusions
Author Contributions
Funding
Acknowledgments
Conflicts of Interest
Appendix A
| Ref. | Year | Research Focus | Methodology | Key Outcomes | Challenges Identified | Recommendations | ||
| Li et al. (2025) |
2025 | Seasonal variations and drivers of TN and TP in surface waters |
Regression & Advanced Modeling Techniques |
Analyzed spatial and temporal distribution of TN and TP in China’s surface waters; highlighted human and natural influence |
Not specified | Not provided | ||
| Paerl et al. (2016) | 2016 | Dual nutrient (N & P) reductions to prevent eutrophication |
Statistical Analysis & Modeling |
Phosphorus reduction alone insufficient; dual N & P reductions needed to mitigate eutrophication and HABs |
Not specified | Target both N & P simultaneously in lake management plans | ||
| Pishbin et al. (2021) | 2021 | Efficiency of microalgae in removing N and P from wastewater |
Engineering Design; Regression & Advanced Modeling |
Synechococcus elongatus removed 87.4% nitrogen and 85.1% phosphorus under mixotrophic conditions |
Not specified | Use mixotrophic microalgae for eco-friendly dairy wastewater treatment | ||
| Mitsch (2017) | 2017 | Restoration of Great Black Swamp to reduce P in Lake Erie |
Statistical & Computational Modeling |
Wetland restoration could reduce phosphorus by up to 40% in Maumee River Basin |
Not specified | Adopt phased wetland restoration with demonstration projects before full-scale implementation | ||
| Martin et al. (2020) | 2020 | Reducing nutrient loads in agricultural watersheds |
Statistical Analysis & Modeling; Sensor Integration |
Controlled fertilizer application and wetland restoration reduce eutrophication with 89% prediction accuracy |
Seasonal variability affects strategy efficiency |
Implement precision agriculture and seasonally adaptive measures |
||
| Elser et al. (2019) | 2019 | Global nutrient limitation patterns in lakes |
Regression & Advanced Modeling Techniques |
62% lakes P-limited, 25% N-limited, 13% co-limited; management should consider local limitation types |
Not specified | Tailor eutrophication control based on site-specific nutrient limitation | ||
| Gu et al. (2020) | 2020 | Impact of cyanobacteria on P cycling and aquatic ecosystems |
Experimental & Computational Modes |
Cyanobacteria absorb more P than macrophytes; excess P (>1.0 mg/L) suppresses growth; toxins harm biota |
Not specified | Monitor cyanobacteria and manage P to control eutrophication |
||
| Mielcarek et al. (2024) | 2024 | Nutrient management in soilless cultivation systems |
Not specified | Closed-loop systems improve nutrient recovery and reduce pollution |
Uncontrolled discharge of drainage water |
Research on optimizing nutrient recirculation techniques | ||
| Wang et al. (2021) | 2021 | Harmful algal blooms (HABs) in Chinese coastal waters |
Regression modeling using MATLAB and R; analysis of nutrient ratios |
85% accuracy in predicting HAB occurrences; high N:P ratios (>25) correlate with increased HAB frequency; projections indicate worsening conditions even under sustainability scenarios |
Excess nitrogen loading since the 1980s; imbalance in nutrient ratios |
Implement nutrient reduction strategies focusing on nitrogen control; enhance monitoring of nutrient inputs |
||
| Kaushal et al. (2017) | 2017 | Nitrogen and phosphorus budgets in urban watersheds |
Statistical analysis and modeling using programming languages and statistical software |
92% accuracy; urban watersheds contribute significantly to nutrient pollution, with nitrogen inputs much higher than phosphorus |
High nitrogen surplus from urban runoff; household activities like lawn fertilization and pet waste contribute to nutrient loads |
Develop targeted nutrient management strategies focusing on reducing nitrogen surplus; promote public awareness on household contributions to nutrient pollution | ||
| Tang et al. (2016) | 2016 | Effects of external nutrient reductions on algal blooms in Lake Taihu, China |
GIS and hydrological modeling; regression and advanced modeling techniques |
Up to 38% reduction in chlorophyll- a with 50-84% nutrient reduction; phosphorus identified as the primary limiting factor |
Need for additional ecological restoration measures beyond nutrient reduction |
Combine nutrient reduction with ecological restoration efforts; prioritize phosphorus control during summer months | ||
| Bergbusch et al. (2021) | 2021 | Effects of nitrogen removal from waste- water on phytoplankton in eutrophic prairie streams |
Regression and advanced modeling techniques using programming languages and statistical software |
69%-79% accuracy; nitrogen removal by biological nutrient removal (BNR) technology reduced phytoplankton abundance by 52% and shifted community composition |
Limited impact on phosphorus levels; need for comprehensive nutrient removal |
Implement comprehensive nutrient removal strategies addressing both nitrogen and phosphorus; monitor shifts in phytoplankton communities | ||
| Wurochekke et al. (2021) | 2021 | Nutrient removal from artificial bathroom greywater by phycoremediation using Botryococcus. |
Experimental and computational modes |
Nitrate removal reached 97%; phosphate removal up to 87% over 30 days |
Scalability and long-term efficiency of phycoremediation |
Explore large-scale applications of phycoremediation; assess long-term sustainability and efficiency | ||
| Payen et al. (2021) | 2021 | Spatially explicit fate factors for nitrogen and phosphorus emissions at the global scale |
GIS and hydrological modeling; statistical analysis and modeling |
94% accuracy; developed spatially explicit fate factors for both nitrogen and phosphorus; emphasized importance of high- resolution river basin data |
Traditional models often consider phosphorus as the sole limiting factor |
Incorporate both nitrogen and phosphorus in eutrophication impact assessments; utilize high-resolution data for accurate modeling | ||
| Xiao et al. (2017) | 2017 | Nutrient removal f rom Chinese coastal waters by large-scale seaweed aquaculture |
Not specified | Seaweed aquaculture removes significant nutrients, mitigating coastal eutrophication |
Quantifying the exact impact of seaweed aquaculture on nutrient removal |
Promote large-scale seaweed aquaculture as a nutrient mitigation strategy; conduct further research to quantify its effectiveness | ||
| Lapointe et al. (2015) | 2015 | Sewage-driven eutrophication and algal blooms in Florida's Indian River Lagoon |
Regression and advanced modeling techniques using MATLAB and R |
89% accuracy in predicting nutrient- induced algal blooms; high nitrogen and phosphorus levels from septic system leakage and storm water runoff contribute to harmful algal blooms |
Excess nutrients from human activities degrade lagoon water quality |
Improve sewage treatment infrastructure; implement storm water management practices to reduce nutrient runoff | ||
| Hossain et al. (2019) | 2019 | Nutrient management and structural shifts in fish assemblages in Lake Ontario |
Regression and advanced modeling techniques |
94% and 88% accuracy; long-term phosphorus reductions led to fish community shifts, reducing total fish biomass per unit of total phosphorus |
Further phosphorus reduction may cause a 24% decline in fish biomass, affecting key species |
Balance nutrient reduction efforts with ecological considerations; monitor fish community responses to nutrient management | ||
| Mennaa et al. (2015) | 2015 | Urban wastewater treatment by seven species of microalgae and an algal bloom |
Not specified | Microalgae species efficiently remove nitrogen and phosphorus, with high biomass productivity |
Optimization of microalgae species for maximum nutrient removal |
Identify and cultivate microalgae species with high nutrient removal efficiency; integrate microalgae-based treatment in urban wastewater management | ||
| Chen et al. (2017) | 2017 | Tracking nitrogen sources, transformation, and transport at a basin scale with complex plain river networks |
Statistical analysis and modeling using programming languages and statistical software |
88% accuracy; identified point and nonpoint sources of nitrogen pollution; seasonal variations affect nitrogen transport |
Long-term agricultural pollution control is essential to combat eutrophication |
Implement long-term agricultural best management practices; monitor seasonal variations in nitrogen transport | ||
| Park et al. (2020) | 2020 | Advances in ICT and sensor technology for monitoring water quality |
Statistical analysis and modeling using programming languages and statistical software |
96.4% accuracy; reviewed advancements in ICT and sensor technology for real-time water quality monitoring |
Integration of ICT and sensor technology in existing water quality monitoring frameworks |
Develop and implement ICT-based real-time water quality monitoring systems; ensure compatibility with existing infrastructure | ||
| Kumar et al. (2024) | 2024 | AI-driven nutrient removal in algae-based systems |
AI/ML models (ANN, RF) and lab experiments | AI models achieved 99.87% accuracy in predicting optimal algal growth for maximum nutrient removal |
Requires extensive training data; high computational power needed | Integrate AI with real-time sensor networks. | ||
| Martínez et al. (2020) | 2020 | Portable nitrate/nitrite monitoring | Electrochemical sensors Arduino and MATLAB/R validation |
Sensor showed 93% accuracy compared to standard lab methods |
Sensors required frequent calibration in field conditions |
Use automated calibration protocols. | ||
| Watson et al. (2016) | 2019 | Coastal algal blooms | Electrochemical sensors and ESP8266, Wi-Fi and cloud analytics |
Established correlation between N:P ratios and bloom intensity (87.5% accuracy) |
Marine organisms fouled sensors, reducing accuracy over time | Apply anti-fouling coatings to sensors for long term deployment. | ||
| Manahan (2018) | 2018 | Nutrient cycling in aquatic systems |
Optical/chemical sensors and Arduino and statistical modeling |
Found agricultural runoff accounts for more than 60% of nutrient imbalances |
Sensor interference from organic matter |
Combine multiple sensor types to improve measurement accuracy. | ||
| Álvarez et al. (2017) | 2017 | Watershed nutrient pollution |
GIS and hydrological modeling |
Agriculture and sewage caused more than 90% of nutrient loads in studied watershed | Difficult to track non-point source pollution | Implement buffer zones and precision farming techniques | ||
| Wurtsbaugh et al. (2019) | 2019 | Dual-nutrient (N/P) reduction |
Meta-analysis and DPSIR framework | 95% Nitrogen and 90% Phosphorus reduction needed to control blooms. |
Current policies focus on single nutrients |
Establish cross-sectoral nutrient quotas addressing both N and P | ||
| Xiao et al. (2017) | 2017 | Seaweed aquaculture for N/P removal | Not specified | Calculated 75,000 tons nitrogen removed annually by current farms |
Space competition with commercial fishing operations |
Create incentives for offshore seaweed farming zones | ||
| Tiwari and Pal (2022) | 2022 | Mapped nutrient contamination hotspots in river ecosystems |
IoT-enabled spectrophotometry with ESP8266 microcontrollers |
Identified industrial/agricultural hotspots (91% N, 85% P accuracy) | Nutrients released from sediments during floods |
Combine dredging with phytoremediation strategies | ||
| Martínez et al. (2020) | 2020 | IoT system for wastewater nitrate monitoring |
Teensy 3.6 microcontroller with GSM/GPRS transmission to cloud |
Showed strong correlation with lab results in real-time monitoring | Limited power supply in remote monitoring locations |
Develop solar-powered sensor nodes for off-grid use | ||
| Daigavane and Gaikwad (2017) | 2017 | IoT water quality sensors for parameter estimation |
ESP32 chips with LoRa wireless transmission to cloud services |
Achieved 90% accuracy in estimating key water quality parameters |
Experienced data transmission delays in some conditions |
Implement edge computing to reduce latency in analysis | ||
| Lapointe et al. (2015) | 2015 | Phosphorus-driven eutrophication | Optical sensors and Arduino and long-term monitoring | Phosphorus from detergents/sewage increased blooms 2.4–2.7times. | Legacy Phosphorus in sediments. |
Ban Phosphorous in detergents and sediment caps. | ||
| Shen et al. (2015) | 2015 | Microalgae for wastewater treatment |
Experimental & Computational Modes |
Scenedesmus removed 83.5% Ammonium ion, 57.9%Phosphate ion. |
Low Nitrate ion removal (39%). | Genetic engineering of algal strains. | ||
| Nankya et al. (2019) | 2019 | Agricultural nutrient management |
Surveys and statistical analysis (SPSS) |
Poor practices led to 52% Nitrogen/Phosphorus loss in Uganda. |
Farmer adoption barriers. | Use subsidies for sustainable fertilizers. | ||
| Eom et al. (2016) | 2016 | Wastewater Nitrogen removal limitations |
Experimental & Computational Modes: Lab-scale BNR reactor tests |
BNR reduced N but not dissolved organic N (DON). |
DON persistence in effluents. |
Combine BNR with advanced oxidation. | ||
| Znachor et al. (2020) | 2020 | Phytoplankton response to nutrients |
Experimental & Computational Modes |
89% accuracy of diatoms dominated under Phosphorus limitation | Climate change interactions. |
Implement adaptive Phosphorus reduction strategies. | ||
| Nandakumar et al. (2019) | 2019 | Wetland N/P removal | Not specified | Brachiaria mutica achieved 82% Phosphorus removal. |
Winter efficiency drops. | Introduce hybrid wetland designs for cold climates. | ||
| Shang et al. (2023) | 2023 | Remote water quality monitoring |
Statistical Analysis & Modeling: Sentinel-2 and XGBoost ML model |
Predicted Chlorophyl-a concentration and ammonium concentration with 90–73% accuracy |
Cloud cover disrupting satellite data. |
Combine satellites with ground sensors. | ||
| Hendriks and Langeveld (2017) | 2017 | Flexible WWTP nutrient standard | Regression & Advanced Modeling Techniques MATLAB/R and scenario modeling |
Achieved 89% accuracy and Dynamic Nitrogen to Phosphorus (N:P) ratio control reduced blooms. |
Regulatory resistance. | Pilot adaptive permit systems. | ||
| Tiwari and Pal (2022) | 2022 | River eutrophication mitigation |
Statistical Analysis & Modeling: Field sampling and spectrophotometry |
95.3% nutrient impact from point sources. | Enforcement gaps. | Introduce stricter industrial discharge permits. | ||
| Strokal et al. (2015) | 2015 | Pearl River nutrient modeling |
Statistical Analysis & Modeling: SPARROW model and sub-basin analysis |
Agriculture contributed 71% of Nitrogen and 92% of Phosphorus loads. |
Data scarcity in rural basins. |
Expand monitoring networks. | ||
| Amit Kumar Tiwari and Dan Bahadur Pal. (2022) | 2022 | Nutrient contamination & eutrophication in river ecosystems |
Eutrophication in river ecosystems Literature review, empirical refeLal case referreferences |
Eutrophication in river ecosystems | Literature review, empirical refeLal case referreferences | Eutrophication causes oxygen depletion, algal blooms, loss of biodiversity, water quality decline |
Anthropogenic nutrient runoff, industrial waste, lack of awareness, inadequate regulation |
Reduce fertilizer use, control runoff, improve wastewater treatment, increase awareness & monitoring |
| Strokal et al. (2015) | 2015 | Nutrient export (N & P) and eutrophication in Pearl River basin | Sub-basin scale modeling using Global NEWS-2 (1970–2050), scenario analysis, and model validation |
Nitrogen and phosphorus exports doubled since 1970; agriculture and sewage drive increases. | Rapid urbanization, intense agriculture, poor management, limited treatment, and uncertain socioeconomic future. |
Prioritize downstream nutrient management, improve sewage treatment, reduce agricultural inputs, enhance monitoring and policies. | ||
| Lin, Tsai and Lyu. (2021) | 2021 | Wireless IoT multi- sensor system monitors aquaculture water quality and mining impacts in Saudi SMEs. |
Designed and implemented ESP32 multi-sensor system with pH, DO, EC, temperature sensors; tested 20 days in situ |
Achieved reliable real-time monitoring of water temperature, pH, dissolved oxygen, conductivity, and salinity for aquaculture. |
Sensor drift, contamination risk, maintenance required, dependence on stable Wi-Fi connection. |
Regular calibration, maintenance, self-cleaning design, expandability for diverse aquaculture and long-term use. | ||
| Suresh et al. (2023) | 2023 | Advancements in water quality indicators for eutrophication in global freshwater lakes |
Reviewed literature; used DPSIR framework; developed causal network linking 58 indicators in seven themes. |
Emphasized holistic indicators climate, land use, socioeconomics and developed causal network showing system feedbacks. |
Lack of integrated monitoring, poor ecosystem modeling, limited data, fragmented assessments, especially in developing regions. |
Expand monitoring, link land use, combine satellite data, model nutrients, and promote interdisciplinary management. | ||
| Hua et al. (2023) | 2023 | Impact of upgrading protected areas (PAs) on conservation effectiveness in the Tibetan Plateau |
Used propensity score matching, NDVI trend analysis, and empirical case studies. |
Upgrading protected areas reverses decline; nine of eleven showed improved vegetation growth. |
Infrastructure growth, overgrazing, funding shortages, livelihood conflicts, and climate change impacts |
Reduce fertilizer use, control runoff, improve wastewater treatment, increase awareness & monitoring | ||
| Han et al. (2021) | 2021 | Nutrient source analysis in phosphorus-rich watershed |
SWAT modeling, scenario analysis |
Crop production caused 66% N, 87% P; N is limiting nutrient | Legacy phosphorus, overfertilization, poor rural treatment |
Cut N 60%, stop P, manage sources, consider legacy impacts | ||
| Chemical Lake Restoration. (2021) | 2021 | Eutrophication causes, internal phosphorus cycling, and impacts on lake ecosystems |
Comprehensive literature review, case studies | Eutrophication from phosphorus causes algal blooms, oxygen loss, and delayed lake recovery. |
Internal phosphorus loading and algal blooms slow recovery, causing ecological and economic losses. |
Combine prevention and treatment, manage sediments, apply circular economy, and improve policy coordination. | ||
| Wu et al. (2017) | 2017 | Pyropia yezoensis and Ulva species effectively remove nutrients in offshore aquaculture systems. |
Field biomass measurement, nutrient analysis, remote sensing, and statistical analysis were used in the study. |
Pyropia removed 3688 tons nitrogen and 106 tons phosphorus; Ulva removed 77 tons nitrogen and 3 tons phosphorus. | High nutrients from agriculture and aquaculture; limited Ulva use and market; Pyropia seasonal limits. |
Promote Ulva use, add heat-tolerant seaweeds, integrate harvesting in nutrient management. | ||
| Liang et al. (2015) | 2015 | Nutrient removal efficiency using rice-straw in denitrifying bioreactor |
Pilot experiment comparing woodchip media, nutrient loading rates, and hydraulic retention times. |
At medium nutrient load (24-hour retention), rice-straw removed more nutrients than woodchips. |
Rice-straw outperforms woodchips at medium load; high load reduces efficiency and raises TOC risk. |
Use rice-straw at medium nutrient loads with 24-hour retention; monitor organic carbon; woodchips for low loads.. | ||
| Zhu et al. (2024) | 2024 | Advances in on-site spectrophotometric nutrient measurement in aquatic ecosystems | Comprehensive review (2019–2023) covers flow analysis, lab-on-chip, smartphone, and microfluidic nutrient detection systems. | Reviewed 40+ sensors with nanomolar to micromolar detection; lab-on-chip and smartphones enable low- cost monitoring |
Challenges: variability, degradation, sensitivity, interference, lack of standards, no ammonium references. | Improve standards; enhance sensing; integrate AI and IoT; develop ammonium references; support collaborations. | ||
| Fernandes et al. (2017) | 2017 | Ecological optimization of N:P recovery from blackwater using microalgae | Lab experiment using Chlorella sorokiniana in photobioreactors across N:P ratios (15–26) |
Phosphorus recovered in 4 days, nitrogen 75% in two weeks, biomass 12 g/L |
Delayed nitrogen removal enlarges system; N losses as ammonia and nitrous oxide. |
Use high N:P species or mixtures; apply eco-stoichiometry; select resilient species for treatment. | ||
| Andersen et al. (2019) | 2019 | Seasonal nutrient limitation of algal groups in a hyper-eutrophic reservoir | Weekly experiments, nutrient additions, N-form tests, sampling | Seasonal shifts: spring P-limit, summer N-limit; taxa show N-form preferences | Variable nutrient sources, fish excretion, storm-driven nutrient changes | Manage both N and P; include N form; improve internal nutrient control | ||
| Smith, King and Williams. (2015) | 2015 | Causes of algal blooms in Lake Erie |
Review of literature and agricultural trends | Increased soluble Phosphorus drives harmful algal blooms | Climate shifts, poor fertilizer timing, soil layering, drainage, large farm sizes |
Revise fertilizer guidelines, control runoff, target phosphorus at landscape level | ||
| Morales-Marín, et al. (2017) | 2017 | Nutrient loading in prairie reservoir |
Catchment modeling using SPARROW | High nutrient retention; fertilizer is major nutrient source | Agricultural runoff, population growth, reservoir limitations |
Optimize land use, reduce inputs, improve monitoring | ||
| Diaz-Elsayed et al. (2017) | 2017 | Sustainability of onsite wastewater treatment | Life cycle and cost assessments |
Advanced systems remove more nitrogen, lower eutrophication | High costs, material and energy use, variable performance |
Use efficient designs, sustainable materials, reduce maintenance | ||
| Alazaiza et al. (2023) | 2023 | Microalgae-based sewage water treatment | Experimental, various mixing ratios, biomass tracking | 97% phosphorus, 95% nitrogen, 84% organic removal, biomass yield | Light limitation, cost, scalability, pH, temperature control. | Optimize conditions, integrate systems, improve harvesting methods | ||
| Liu et al. (2025) | 2025 | Eutrophication in separated urban ponds | Field sampling, phosphorus analysis, water testing | High phosphorus, Class V water, Fe/Al-P main eutrophication source | Sediment pollution, sewage input, poor circulation, ineffective treatment | Remove silt, plant submerged vegetation, divert and treat sewage | ||
| Chen et al. (2017) | 2017 | Phytoremediation of nutrient-polluted drainage |
Pot experiment with five plant species | LS removed 57.7% nitrogen, 57.3% phosphorus; high plant uptake | Poor growth of some species, limited scalability, root decay | Use LS, OS, IA; harvest on time; test in real field conditions | ||
| Ma, Huang and Kao. (2018) | 2018 | Gate management impact on river water quality |
WASP modeling with hydrology and pollution data | Gate opening raises BOD, ammonia; 5 days to self-recover |
High pollution load, tidal effects, system sensitivity |
Limit gate open time, simulate effects, optimize closure strategy | ||
| Vymazal & Kröpfelová (2015) | 2015 | How hydraulic loading and seasonality affect nutrient removal in free-water-surface constructed wetlands |
Monitored N and P removal in a temperate free-water-surface wetland across seasonal hydraulic load rates | Removal rates ranged 4–12 g P m⁻² yr⁻¹ and 50–75 g N m⁻² yr⁻¹, peaking in summer |
Seasonal cold and high flows reduced performance | Adapt hydraulic loading seasonally to optimize removal vs. | ||
| Shuet et al. (2018) |
2018 | Nutrient removal by Chlorella vulgaris and Scenedesmus quadricauda in batch reactors | Operated batch algal reactors with municipal wastewater; tracked NH₄–N, NO₃–N, PO₄ removal kinetics | S. quadricauda removed 84 % NH₃–N, C. vulgaris 77 % TN; PO₄ removal < 50 % |
Both strains limited in NO₃–N and PO₄ |
Employ mixed-strain consortia and kinetic modeling to boost uptake rates | ||
| Pedersen & Borum (2016) |
2016 | Nutrient removal via biomass accumulation on artificial substrata in the northern Baltic Sea |
Deployed artificial substrates in situ for 14.5 months; quantified accumulated N, P in biomass |
Substrata biomass sequestered ~50 g N m⁻² and 5 g P m⁻² primarily in invertebrate and algal biomass | Heavy-metal uptake by biomass limits its use as soil amendment |
Locate substrata near point sources and valorize biomass for bioenergy | ||
| Mao et al. (2020) |
2020 | Quantification of N and P removal by China’s seaweed aquaculture | Combined national seaweed production statistics with tissue N/P content to estimate total nutrient sink |
China’s seaweed farms removed ~75,000 t N and 9,500 t P in 2010 | Expansion constrained by market incentives and profitability | Support seaweed farmers through policy incentives and integrate aquaculture into eutrophication management | ||
| Meng et al. (2020) |
2020 | IoT/cloud-based potassium sensor for real- time water quality |
Developed an ion-selective electrode for K⁺ linked via MQTT to a cloud platform; validated against lab assays |
Sensor achieved R² = 0.992 vs. lab standards; detection limit 0.1 mg L⁻¹ | Electrode fouling requires frequent calibration | Integrate self-cleaning membranes and remote calibration routines | ||
| Dodds et al. (2018) |
2018 | Review of N and P roles in stream eutrophication and management implications | Meta-analysis of global stream nutrient–chlorophyll datasets; developed trophic state classification thresholds | Defined thresholds where TN > 2 mg L⁻¹ or TP > 0.05 mg L⁻¹ drove periphyton blooms; dual N+P |
Overlooking N control leads to persistent cyanobacteria |
Manage both N and P in stream catchments simultaneously | ||
| Liet al.(2017) | 2017 | Advanced tertiary treatment of wastewater with Desmodesmus sp. SNN1 |
Batch culture optimization of pH and inoculum density for municipal secondary effluent polishing | Achieved ~90 % TN, 95 % TP and ~100 % NH₄⁺ removal within 12 days | Maintaining elevated pH operationally challenging | Deploy Desmodesmus in tertiary ponds and valorize algal biomass | ||
| Wang & Lü (2015) |
2015 | Impact of pyrolysis temperature on nutrient retention in poultry litter biochar | Produced biochar at 300 °C and 500 °C; characterized nutrient availability and sorption properties in lab assays |
Higher-temperature biochar (500 °C) had greater C stability but reduced P availability; 300 °C char released more labile |
Trade-off between nutrient stabilization and availability |
Apply 500 °C biochar with co-amendments to balance P retention and release | ||
| Fu et al. (2022) |
2022 | Warming and acidification effects on Heterosigma akashiwo cellular composition |
Cultured under current vs. elevated T (+4 °C) and pCO₂ (1000 µatm); measured cellular C, N, P, DNA/RNA content |
Future climate reduced cellular C, N, P and nucleic acids by 30–36 %, indicating potential bloom declines | Species-specific responses complicate projections | Incorporate multispecies experiments into climate–eutrophication models | ||
| Paerl & Huisman (2021) | 2021 | Global trends in harmful cyanobacterial blooms driven by climate change |
Synthesized > 200 satellite and in situ bloom records (2003–2007); correlated bloom frequency with SST and nutrient loads | Bloom frequency increased ~2 % yr⁻¹; warming strongest |
Distinguishing climate vs. nutrient driverse | Strengthen long-term monitoring and coupled climate–nutrient models | ||
| Wu et al. (2021) |
2021 | IoT-based dissolved oxygen monitoring for river basins |
Deployed wireless microcontroller DO sensors linked via NB-IoT to cloud; validated against YSI sondes | Enabled continuous DO profiles with error < 0.15 mg L⁻¹; supported remote data visualization |
Field connectivity and power supply consistency | Integrate solar power and mesh networking for robust basin-scale DO monitoring | ||
| Zhou et al (2017) | 2017 | Effects of CAS vs. BNR wastewater effluent on algal bloom potential | Bioassays exposing freshwater algal communities to CAS (conventional activated sludge) vs. BNR (biological nutrient removal) plant effluents |
BNR effluent triggered higher N-based algal yield despite lower TN, due to more bioavailable forms | Variability in nutrient speciation alters downstream effects | Evaluate effluent bioavailability before implementing full-scale BNR conversion | ||
| Mehta et al. (2015) | 2015 | River–lake connectivity effects on sediment C:N:P ratios in large lakes | Sampled sediments from 82 lakes; compared C:N:P stoichiometry in connected vs. isolated systems using elemental analysis | Connected lakes had higher sediment P; isolated lakes showed greater C and N accumulation; eutrophication reduced carbon sequestration | Heterogeneity in connectivity and hydrodynamics | Tailor sediment management to connectivity context (e.g., dredging vs. biomanipulation) | ||
| Kim et al. (2018) | 2018 | Smart IoT water-monitoring system for pH, CO₂, water level | Built ARM-based sensor nodes measuring pH, temperature, CO₂ and level; cloud integration with alert functions | Real-time monitoring with < 5 min latency; automated malfunction alerts | Scaling across multiple sites challenged by network bandwidth | Employ LPWAN protocols and edge computing for scalable, low-power deployments | ||
| Zhang et al. (2020) | 2020 | Microbial community response to nutrient removal in coastal sediment using ecological concrete | Embedded eco-concrete aggregates in nutrient-rich sediments; tracked microbial 16S rRNA gene abundances and TN/TP removal over 28 days | Eco-concrete promoted denitrifying bacteria (e.g., Sulfurovum); achieved ~8 % TN, 8 % TP removal | Low overall removal efficiency; substrate performance varied | Optimize eco-concrete formulations and support targeted microbial colonization | ||
| Wu et al. (2016) | 2016 | Phytoremediation of eutrophic waters by paired emergent vs. submerged macrophytes |
Paired plantings of Thalia dealbata, Canna indica (emergent) and Vallisneria natans (submerged) in waters high in N, P or both; measured uptake and biomass over 30 days | Dual emergent–submerged combinations removed nutrients more effectively; T. dealbata + C. indica best for TN, NH₃–N, NO₃–N and TP removal |
Site-specific species performance; optimal pairings vary with nutrient profile | Design phytoremediation schemes tailored to dominant nutrient stress (N, P or mixed) |
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|---|---|---|---|---|---|
| Chang et al. (2015) | 146 | 2015 | Reviewed remote sensing technologies for water quality monitoring; categorized methods and platforms; provided inversion models and case | Integrative and historical approach; detailed methodological classification; supports ecosystem-based and multiscale water quality management. | Limited citation of applications in developing countries; less focus on recent AI-based models; lacks real-time operational framework. |
| Watson et al. (2016) | 646 | 2016 | Provided a comprehensive synthesis of nutrient loading, HABs, and hypoxia in Lake Erie, outlining causes, impacts, and adaptive management strategies. | Offered a multidisciplinary analysis across ecology, climatology, and nutrient modeling; highly relevant for policymakers addressing eutrophication. | Region-specific (Lake Erie); challenges in generalizing findings to other aquatic systems. |
| Glibert et al. (2018) | 99 | 2018 | Synthesized almost two decades of global research on harmful algal blooms (HABs), emphasizing ecological drivers, international case studies, and emerging trends through the GEOHAB program. | Comprehensive global perspective; multidisciplinary approach; foundation for future HAB research via Global HAB initiative. | Limited focus on freshwater HABs; some regional disparities in data coverage. |
| Wurtsbaugh et al. (2019) | 986 | 2019 | Provides a broad review of eutrophication impacts, nutrient sources, and algal blooms from freshwater to marine systems, stresses dual nutrient control. | Comprehensive and interdisciplinary; covers freshwater to marine systems; supports policy and management decisions. | General in scope; lacks primary data or modeling; geographic focus mainly on North America and Europe. |
| Richa et al. (2021) | 27 | 2021 | Reviewed the integration of ion-selective electrodes and IoT technologies for nutrient monitoring in hydroponic systems. Focused on sensor performance, ion sensitivity, system calibration, and automation. | Demonstrated the potential of ISEs for real-time monitoring, emphasizing PVC-membrane sensor advantages, IoT-enabled automation, and support for sustainable agriculture | Limited micronutrient sensor development. |
| Akinnawo. (2023) | 264 | 2023 | Reviewed causes, effects, and mitigation of eutrophication; assessed pollutant removal efficiencies, material performance, and advanced technologies like Nano filtration and electrocoagulation. | Provided a comprehensive and comparative review incorporating real-world performance data and integrating multidisciplinary mitigation strategies | Highlighted high technical complexity, limited scalability in developing regions, and the lack of a unified framework for selecting mitigation techniques |
| Sharma et al. (2024) | 5 | 2024 | Conducted a review on AI and IoT applications in plant growth monitoring, covering climatic factors, sensor technologies, data processing, and emerging tools like block chain and robotics. | Integrated a wide range of technologies and case studies, identifying key AI and IoT tools and their agricultural relevance, aiding in the design of intelligent monitoring systems | Lacks original empirical data or field validation. |
| Sguanci et al. (2024) | 8 | 2024 | Reviewed how IoT technologies support nutritional management for patients with chronic neurological cognitive impairments, identifying key applications in monitoring, intervention, and education. | Highlights promising IoT innovations for remote nutritional care, provides a roadmap for future research, and offers insights for healthcare providers. | IoT solutions are in early development, with a lack of standardization and most studies based on small samples and Western contexts |
| Lan et al. (2024) | 31 | 2024 | Provided a comprehensive review of HABs, linking causes to eutrophication from agricultural and urban sources, and evaluating monitoring and treatment methods for effectiveness and sustainability | Offers an integrated view of HABs’ causes and responses, with a detailed analysis of global patterns and highlights technological advancements in monitoring and mitigation | Lacks new empirical data or modeling, with generalizations that may overlook regional variability and a descriptive approach without deep comparative analysis of interventions. |
| Bai et al. (2025) | 2 | 2024 | Conducted a meta-analysis on 115 studies to evaluate nitrogen and phosphorus removal efficiency in ecological ditches, analyzing factors like plant type, materials, temperature, and hydraulic retention time. | Offers a comprehensive synthesis across multiple variables and vegetation setups, useful for designing agricultural pollution mitigation strategies | Limited geographic diversity (mostly from China), lacks real-time or operational field-testing data, and does not fully address potential variability due to local climate or soil. |
| Proposed systematic review | Reviews current applications of Internet of Things (IoT) technologies in monitoring macronutrients (nitrogen, phosphorus, potassium) in agricultural and environmental systems. | Identifies technological advancements, integration potential with real-time data analytics, and enhanced precision in nutrient monitoring and management. | Limited scalability in rural or underdeveloped regions, concerns over data privacy, and high initial costs for deployment and maintenance of IoT infrastructure. | ||
| Criteria | Inclusion | Exclusion |
|---|---|---|
| Topic | Research papers focusing on real-time monitoring of macronutrients (Carbon, Nitrogen, Phosphorus) using IoT-based sensors. | Research papers not focusing on real-time monitoring of macronutrients or those studying unrelated water quality parameters. |
| Research Framework | Research articles with a clear methodology linking IoT technology to macronutrient monitoring | Articles without empirical research frameworks or relevant methodologies |
| Language | Research papers must be written in English. | Research papers published in languages other than English. |
| Period | Articles between 2015 to 2025 | Articles outside 2015 and 2025 |
| Source | Search string | Results |
|---|---|---|
| Web of science | ("nutrient management" OR "nutrient removal" OR "aquatic systems") AND ("eutrophication" OR "algal bloom") AND ("phosphorus" OR "nitrogen" OR "carbon" OR "dissolved carbon") OR ("IoT" OR "Internet of Things") AND ("water quality" OR "water monitoring") | 2743 |
| Scopus | (nutrient management OR nutrient removal) AND (eutrophication OR algal bloom) AND (phosphorus OR nitrogen) AND IoT. For Google Scholar, the search included ("nutrient management" OR "nutrient removal") AND ("eutrophication" OR "algal bloom") AND ("phosphorus" OR "nitrogen") | 708 |
| Google Scholar | ("nutrient management" OR "nutrient removal") AND ("eutrophication" OR "algal bloom") AND ("phosphorus" OR "nitrogen") | 16800 |
| Stage | Action | Researchers |
|---|---|---|
| Initial Screening | First 80 records independently reviewed. | K, NC, OA and KP |
| Discussion of Calibration | Discussed and resolved early disagreements | K, NC, OA and KP |
| Independent Title/Abstract Screening | Remaining records screened individually | K, NC, OA and KP |
| Full Text Review | Independently checked full text articles for eligibility | K, NC, OA and KP |
| Final Consensus Meeting | Resolve conflicts through discussions | K, NC, OA and KP |
| Field | Definition |
|---|---|
| Paper ID Paper Title Citations Year |
An internal identifier assigned to each paper for organization. Full title of the study. Number of citations the study had received (at time of collection) to assess impact Publication year to identify trends over time. |
| Research Type Online repository Country of Authors Water source Investigated water aspect Macronutrients Sensor Microcontroller Connection type Cloud used Software used Software used Model evaluation metrics Accuracy Key findings IEEE Reference Format Link |
Categorization as a Journal Paper, Conference Paper, Book Chapter, Dissertation, or Thesis. Source database used to retrieve the study (Google Scholar, SCOPUS, or Web of Science). Country or countries affiliated with the authors, for geographical trend analysis. Specific water body or source investigated (e.g., rivers, lakes, wastewater). The aspect of water quality that was the focus (e.g., nutrient concentration, eutrophication monitoring). The aspect of water quality that was the focus (e.g., nutrient concentration, eutrophication monitoring). Types of sensors or sensing technology applied Type of microcontroller used Communication protocols employed (e.g., Wi-Fi) Whether and which cloud platforms were utilized for data storage or processing (e.g., AWS, Azure, Google Cloud). Any software tools mentioned for data analysis, visualization, or system development. Any software tools mentioned for data analysis, visualization, or system development. Metrics used to evaluate predictive or monitoring models (e.g., RMSE, R², MAE). Reported accuracy values associated with the models Major conclusions or innovations reported by the study Complete reference citation for standardized referencing Direct access link to the paper or its repository record |
| Outcome | Measure used | Purpose |
|---|---|---|
| Sensor accuracy | Percentage (%) | To show detection performance |
| Technology comparison | Visual arts, counts | To compare commonly used tools |
| System responsiveness | Time recorded | To show how fast sensors respond to water change |
| Challenges reported | Frequency count | To identify technically recurring issues |
| Study ID | IoT Application | Environment (Agriculture/Aquatic | Nutrient focus | Outcome Reported | Included for synthesis |
|---|---|---|---|---|---|
| 1 |
Smart nutrient Monitoring |
Agriculture |
Nitrogen, Phosphorus |
Improved detection accuracy | Yes |
| 2 |
Wireless sensor network for water quality |
Aquatic |
Nitrogen |
Real-time monitoring data |
Yes |
| 3 | Laboratory prototype only |
Laboratory only (Excluded) |
Phosphorus | No field deployment reported | No |
| Subgroup Criteria | Findings | Observed differences |
|---|---|---|
| Environment Type | Aquatic systems favored sensor accuracy in nutrient detection | Agricultural setups showed more variation due to soil interference |
| Sensor Type | Optical sensors performed better in clear water environments | Electrochemical sensors had more variability in muddy or low-flow conditions |
| Nutrient Type | Nitrogen monitoring was most frequently studied | Carbon monitoring was less consistent in method and outcomes |
| Ref. | QA1 | QA2 | QA3 | QA4 | QA5 | Total | % grading |
|---|---|---|---|---|---|---|---|
| Paerl et al., 2016, Bai et al., 2025, Strokal et al., 2015, Wurtsbaugh et al., 2019 | 1 | 1 | 1 | 1 | 1 | 5 | 100 |
| Martínez et al., 2020 | 1 | 1 | 0.5 | 1 | 0.5 | 4 | 80 |
| Park et al., 2020 | 1 | 0.5 | 0.5 | 1 | 0.5 | 3.5 | 70 |
| Mielcarek et al., 2023 | 0.5 | 0 | 0.5 | 0.5 | 0 | 1.5 | 30 |
| Year of Publications | Journal Article | Book Chapter |
|---|---|---|
| 2015 | 7 | 0 |
| 2016 | 6 | 0 |
| 2017 | 15 | 0 |
| 2018 | 2 | 0 |
| 2019 | 7 | 0 |
| 2020 | 9 | 0 |
| 2021 | 8 | 2 |
| 2022 | 4 | 2 |
| 2023 | 11 | 0 |
| 2024 | 5 | 0 |
| 2025 | 4 | 0 |
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