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Review

Remote Sensing Approaches for Water Hyacinth and Water Quality Monitoring: Global Trends, Techniques, and Applications

1
Faculty of Civil and Water Resources Engineering, Bahir Dar Institute of Technology, Bahir Dar University, Bahir Dar P.O. Box 79, Ethiopia
2
Department of Land and Water Management, IHE Delft Institute for Water Education, Westvest 7, 2611 AX Delft, The Netherlands
3
Department of Water Science and Engineering, Vrije Universiteit Brussel, Boulevard de la Plaine 2, 1050 Ixelles, Belgium
4
College of Agriculture and Environmental Sciences, Bahir Dar University, Bahir Dar P.O. Box 79, Ethiopia
5
Blue Nile Water Institute, Bahir Dar University, Bahir Dar P.O. Box 79, Ethiopia
6
Department of Natural and Environmental Sciences, Global Water Center, University of Nevada, 1664 N. Virginia Str., Reno, NV 89557, USA
7
Department of Hydroinformatics and Socio-Technical Innovation, IHE Delft Institute for Water Education, Westvest 7, 2611 AX Delft, The Netherlands
*
Author to whom correspondence should be addressed.
Water 2025, 17(17), 2573; https://doi.org/10.3390/w17172573
Submission received: 23 July 2025 / Revised: 24 August 2025 / Accepted: 28 August 2025 / Published: 31 August 2025
(This article belongs to the Section Ecohydrology)

Abstract

Water hyacinth (Eichhornia crassipes), native to South America, is a highly invasive aquatic plant threatening freshwater ecosystems worldwide. Its rapid proliferation negatively impacts water quality, biodiversity, and navigation. Remote sensing offers an effective means to monitor such aquatic environments by providing extensive spatial and temporal coverage with improved resolution. This systematic review examines remote sensing applications for monitoring water hyacinth and water quality in studies published from 2014 to 2024. Seventy-eight peer-reviewed articles were selected from the Web of Science, Scopus, and Google Scholar following strict criteria. The research spans 25 countries across five continents, focusing mainly on lakes (61.5%), rivers (21%), and wetlands (10.3%). Approximately 49% of studies addressed water quality, 42% focused on water hyacinth, and 9% covered both. The Sentinel-2 Multispectral Instrument (MSI) was the most used sensor (35%), followed by the Landsat 8 Operational Land Imager (OLI) (26%). Multi-sensor fusion, especially Sentinel-2 MSI with Unmanned Aerial Vehicles (UAVs), was frequently applied to enhance monitoring capabilities. Detection accuracies ranged from 74% to 98% using statistical, machine learning, and deep learning techniques. Key challenges include limited ground-truth data and inadequate atmospheric correction. The integration of high-resolution sensors with advanced analytics shows strong promise for effective inland water monitoring.

1. Introduction

Water hyacinth (Eichhornia crassipes [Mart.] Solms), native to South America, is now one of the most pervasive invasive species affecting tropical and subtropical aquatic ecosystems across the globe, excluding Antarctica [1]. It thrives in warm, nutrient-rich waters and can double its biomass within weeks under sympathetic conditions [2,3]. Its proliferation is driven by eutrophication, high nutrient concentrations (especially total nitrogen and phosphorus), elevated pH, increased temperature, low lake water level, and minimal disturbance of the water body [4,5,6,7,8].
Satellite-based remote sensing has become a vital tool for capturing spatial and temporal environmental changes, often caused by natural processes or anthropogenic activities [9]. Especially in data-scarce or inaccessible regions, remote sensing offers a practical means of monitoring aquatic systems. Since the launch of the Landsat program in the 1970s, remote sensing technologies have evolved significantly, enhancing monitoring frequency, spatial resolution, and thematic scope [10]. The introduction of multispectral and hyperspectral sensors in the 1980s–1990s expanded their utility in environmental applications, while later advances such as Synthetic Aperture Radar (SAR) enabled effective monitoring under cloud cover and at night. The 2010s saw further enhancements with the use of Unmanned Aerial Vehicles (UAVs) and the integration of machine learning algorithms, improving spatial detail and classification accuracy [11].
Sensor resolution remains critical: MODIS, with coarse resolution (250 m–1 km), has been applied to large-scale assessments [12,13], whereas high-resolution sensors such as Landsat 8 OLI and Sentinel-2 MSI enable localized, long-term studies [14,15]. Landsat sensors, including ETM+, OLI, and TIRS, have been widely used to monitor water hyacinth distribution and water quality indicators, such as chlorophyll-a, turbidity, and suspended solids [16,17]. Sentinel-2A/B, offering 10–20 m resolution with a 5-day revisit cycle, is increasingly applied in the mapping of aquatic vegetation and optically active water quality parameters like algal blooms [18,19,20].
Hyperspectral sensors, especially in the 700–900 nm range, have demonstrated superior performance in differentiating water hyacinth from native vegetation, with methods like the Spectral Angle Mapper (SAM) improving classification accuracy by over 20% [21]. Similarly, combining Sentinel-2 MSI with UAV imagery and machine learning classifiers such as Random Forest has achieved over 92% accuracy in detecting small-scale infestations [22].
Spectral indices such as the Normalized Difference Vegetation Index (NDVI), the Normalized Difference Water Index (NDWI), and the Enhanced Vegetation Index (EVI) have also been employed to estimate water hyacinth biomass and seasonal changes [13,23]. NDVI values > 0.6 typically indicate dense mats [24,25]. NDWI enhances water-body delineation and, when combined with NDVI, improves vegetation classification [26,27].
Traditionally, monitoring inland waters has been challenging due to spatial and temporal limitations. The highly dynamic nature of water hyacinth across time and space makes it difficult to accurately measure its areal coverage and expansion rate. Obtaining reliable spatial and temporal data through conventional methods also requires significant labor and financial resources. Furthermore, assessing water quality using traditional approaches relies on laboratory-based analyses, which are limited in spatial coverage and typically focus on a few selected sampling points [28].
Remote sensing technologies now enable efficient, large-scale, and near real-time monitoring of aquatic systems [29]. Despite advancements in remote sensing, a comprehensive synthesis of global applications for monitoring water hyacinth and water quality remains lacking. This gap is increasingly critical given the rapid spread of water hyacinth and worsening pollution in freshwater ecosystems worldwide.
This systematic review is essential for understanding the global impact of water hyacinth and current monitoring practices that incorporate satellite remote sensing. While some regions have established effective monitoring systems, many affected areas, particularly in resource-constrained settings, still lack consistent and reliable approaches. Existing studies are often fragmented and region-specific, utilizing a wide range of sensors, methodologies, and indices, which limits comparability and knowledge transfer.
Although some regions have implemented effective monitoring systems, many, particularly in resource-constrained settings, still lack consistent, scalable, and cost-effective strategies for water hyacinth monitoring [6,30]. Knowledge of the most effective monitoring approaches for managing this invasive species remains limited and consolidated. Existing studies are fragmented and highly context-specific, utilizing a range of sensors, methodologies, and indices. This diversity hinders standardization, comparability, and the broader application of monitoring strategies [27].
Moreover, there is a notable absence of global syntheses that integrate recent advances in satellite remote sensing with machine learning and deep learning techniques, especially across diverse freshwater environments. Few studies have rigorously assessed the adaptability and performance of these algorithms in combination with Earth observation data for detecting water hyacinth and assessing associated water quality parameters [31,32]
Therefore, an organized, up-to-date review of current monitoring practices, emphasizing the use of advanced satellite platforms and analytical tools, is important. Such a synthesis could offer valuable insights for researchers, practitioners, and policymakers, supporting the development of more effective, scalable, and technology-driven solutions for managing aquatic invasive species and protecting water quality. This systematic review aims to (1) categorize trends in remote sensing applications for monitoring water hyacinth and optically active water quality parameters (substances in water that absorb or scatter light, altering water’s color and clarity), (2) assess the integration of machine learning algorithms with remote sensing datasets, and, finally, (3) identify current gaps, challenges, and future directions in the remote sensing-based monitoring of inland water bodies.

2. Materials and Methods

This study employed a systematic literature review to investigate global applications of remote sensing technologies in monitoring water hyacinth and key water quality parameters. The methodological process was structured into three main phases: literature identification, screening and selection, and comprehensive data extraction following the Preferred Reporting Items for Systematic Reviews and Meta-Analyses (PRISMA) guidelines [33]. These phases supported subsequent bibliometric, thematic, and spatial analyses to synthesize trends and insights from the selected literature.
The selection of articles was guided by research objectives and structured using the PICO framework (Population, Intervention/Exposure, Comparison, and Outcome). Inclusion criteria considered publication type (peer-reviewed or otherwise), language, and the relevance of reported outcomes to the review objectives. Conversely, studies were excluded if they did not directly address the research question, were non-peer-reviewed or non-scholarly, or duplicated existing work. The PRISMA checklist was applied to ensure transparency and rigor in the review process.
The literature identification phase involved a structured and comprehensive search of peer-reviewed journal articles published between 2014 and 2024. The focus was on studies that employed remote sensing technologies, particularly satellite imagery and unmanned aerial vehicles (UAVs), to detect and quantify water hyacinth or assess optically active water quality parameters such as chlorophyll-a, turbidity, and total suspended solids (TSS). The search strategy was carefully designed using Boolean operators (“AND” and “OR”) to ensure both precision and breadth, allowing for the retrieval of studies that integrated relevant remote sensing methods with ecological and water quality applications.
Searches were conducted across three major academic databases: Scopus, Web of Science, and Google Scholar. We systematically included Google Scholar as an additional database to ensure comprehensive coverage of the peer-reviewed literature. This strategy was employed to capture relevant articles potentially missed by the Web of Science and Scopus, thereby reducing publication bias and enhancing the overall completeness and rigor of our review. The keyword development process is centered on five major thematic categories, Table 1. The first involved remote sensing tools and terminology, including terms like “remote sensing,” “satellite imagery,” “UAV,” and “drone.” The second focused on the target invasive species, using keywords such as “water hyacinth” and “Eichhornia crassipes.” The third category addressed water quality parameters, incorporating terms like “chlorophyll-a,” “turbidity,” and “total suspended solids.” The fourth category included broader context and functional descriptors such as “monitoring,” “detection,” “mapping,” while the final category described the geographic or ecosystem type including “lakes,” “rivers,” “wetlands,” and “global water bodies.”
A representative search string applied during this phase is as follows: TITLE-ABS-KEY ((“remote sensing” OR “satellite imagery” OR “UAV” OR “drone”) AND (“water hyacinth” OR “Eichhornia crassipes”) OR (“water quality” OR “chlorophyll-a” OR “turbidity” OR “total suspended solids”) AND (“monitoring” OR “detection” OR “mapping”) AND (“global water bodies” OR “lakes” OR “rivers” OR “wetlands”)). Through this process, a total of 1215 unique articles were retrieved from the three databases.
Following the literature identification, the next step involved a rigorous screening and selection process.
Initially, duplicate entries typically arising from overlapping indexing across databases were identified and removed. This step resulted in the elimination of 422 redundant records. The remaining studies (793) were then subjected to a two-stage relevance screening process.
In the first stage, titles and abstracts were reviewed to assess whether the studies met basic inclusion criteria. Eligible articles were required to be published in English, fall within the 2014–2024 timeframe, and demonstrate the application of remote sensing technologies within aquatic ecosystems. At the conclusion of this stage, 451 articles were retained for full-text evaluation (Figure 1).
The second stage consisted of a detailed full-text review to determine methodological rigor and thematic relevance. Articles were included if they employed remote sensing to monitor water hyacinth, water quality parameters, or both. Additional inclusion criteria were an explicit description of the study’s spatial context and scale, as well as the type of sensor or platform used, and a clearly articulated methodological framework. Studies that lacked transparency in their methodology did not focus on aquatic ecosystems or failed to incorporate remote sensing as a core analytical component were excluded. After this thorough evaluation, about 373 articles were screened out and 78 studies were deemed suitable for in-depth analysis (Figure 1).
Data extraction focused on capturing key bibliometric and methodological attributes from the selected studies. A structured template was developed in Microsoft Excel to standardize metadata, including publication year, author affiliations, journal title, geographic study location, sensor type, and analytical approach. The dataset was carefully cleaned to address formatting inconsistencies and ensure uniform categorization across entries.
Subsequently, a bibliometric analysis was conducted to explore publication trends, sensor usage patterns, disciplinary distribution, and geographic representation. Special attention was paid to the types and details of the remote sensing platforms employed, as well as the types of journals that published these studies. Quantitative trends were visualized using line and bar charts to highlight dominant research trajectories and identify temporal or regional gaps in literature.
In addition to bibliometric characterization, a thematic analysis was conducted to classify the studies based on their research focus and methodological orientation. A deductive color-coding approach was adopted on Microsoft excel, whereby each article was reviewed and categorized into thematic areas based on its objectives and analytical methods.
The thematic classification distinguished between studies focused solely on the detection and mapping of water hyacinth or retrieval of water quality parameters, and integrated studies addressing both topics. Further thematic dimensions included the use of different sensor platforms (e.g., multispectral satellite data, UAV-based imagery), analytical techniques (e.g., empirical method, semi-empirical method, and analytical method), and the specific water body type studied.
The coding process was performed manually through an iterative reading of the studies to ensure consistency and validity. Cross-validation of themes was conducted by comparing objectives and conclusions to confirm the accuracy of classifications. This thematic synthesis enabled the identification of methodological innovations, technology integration patterns, and existing research gaps.
To assess the geographic distribution of the reviewed studies, spatial data were extracted from each article and processed using QGIS version 3.34.12 accessed via https://qgis.org/resources/hub/. Geocoded study locations were mapped to visualize the global distribution of research activities, involving the application of remote sensing technologies for inland water monitoring. This spatial analysis revealed distinct regional clusters of research, particularly in countries with a well-established remote sensing infrastructure and technical capacity. These disparities in spatial research coverage underscore uneven access to remote sensing resources and technical expertise. The geographic visualization thus provided critical insights into global imbalances in technological application, informing recommendations for future research investment and capacity-building efforts in data-scarce regions.
Reference management was carried out using freely available too called Mendeley Desktop, version 1.19.8 accessed through https://www.elsevier.com/products/mendeley ensuring systematic organization and accurate citation throughout the review process.

3. Results

3.1. Description of Articles and Publication Trends

An analysis of publication trends indicates that, between 2014 and 2017, the annual number of published articles remained relatively low and stable, ranging from three to five publications per year. This period coincided with the early phase of the Sentinel-2 mission, which had not yet begun capturing imagery, leaving Landsat 8 OLI as the primary freely accessible multispectral high-resolution sensor in use [34]. However, beginning in 2019, a marked increase in annual publication output was observed. As shown in Figure 2a, the number of studies focusing on water hyacinth and water quality monitoring exhibited a steady upward trend from 2018 to 2024.
In terms of the types of water bodies investigated between 2014 and 2024, lakes were the most frequently studied, accounting for 48 studies (61.5%) (Figure 2b). Rivers followed, with 16 studies (21%), while wetlands were the focus of 8 studies (10.3%), primarily published in 2019, 2023, and 2024. A smaller portion of research (six studies, 7.7%) analyzed both lakes and rivers, reported in 2015 and 2018 publications.
The reviewed studies were further categorized based on their primary focus: water hyacinth mapping, water quality assessment, or both (Figure 3). Approximately 33 studies (42%) focused on water hyacinth, including biomass estimation and a spatiotemporal variability analysis. Meanwhile, 38 studies (49%) addressed water quality parameters. The remaining seven studies (9%) investigated both water hyacinth and water quality within integrated case studies (Figure 3).
Figure 4a illustrates the application trends of satellite sensors used for monitoring water hyacinth and water quality. Among the sensors analyzed, Sentinel-2 MSI emerged as the most frequently utilized, appearing in 24 studies focused on lakes, rivers, and wetlands. Its usage has notably increased since 2017, both as a standalone dataset and in combination with other sensors.
Irrevocably, the use of unmanned aerial vehicles (UAVs) equipped with RGB sensor cameras for inland water monitoring has increased in recent years, as evidenced by their application in seven reviewed studies. UAVs were predominantly employed for lake water quality monitoring, owing to their high spatial resolution, operational flexibility, and ability to capture detailed local-scale data.
In parallel, MODIS Terra and Landsat 7 ETM+ were each utilized in four studies within the review period, reflecting their continued relevance in inland water monitoring applications. Additionally, hyperspectral Hyperion EO-1, Terra ASTER, Sentinel-1 SAR, and Landsat 5 TM were each reported in two studies, highlighting their more limited but targeted application in monitoring water hyacinth and water quality in various global water bodies Figure 4a.
Figure 4b presents the distribution of integrated sensor applications across the reviewed studies. Within the reviewed literature, a total of 16 combined sensor applications were identified. Among these, the integration of Sentinel-2MSI and UAVs equipped with RGB cameras emerged as the most frequently employed multi-sensor approach, reported in four studies (25%).
Additionally, three studies (18.75%) utilized integrated datasets from Landsat 8 OLI and Sentinel-2 MSI to monitor water hyacinth and assess water quality parameters. Both sensors were also widely used individually and in combination for the estimation of chlorophyll-a (Chl-a) concentrations in global lakes. Furthermore, combined applications within the Sentinel satellite series and triple-sensor integrations involving Landsat 8 OLI, Sentinel-2 MSI, and MODIS Terra were each reported in two studies (12.5%), primarily aimed at enhancing temporal resolution and detection accuracy (Figure 4b).
In contrast, a limited number of studies employed other sensor combinations, such as the integration of Landsat 8 OLI with MODIS, PlanetScope with MODIS, various combinations of the Landsat series, and the fusion of MODIS with MERIS. These approaches showed relatively low adoption in the reviewed literature, indicating more specialized or context-specific applications in inland water monitoring.

3.2. Trends in Journal Publications

Figure 5 presents the top ten journals that published the articles included in this review. The diversity of journal categories reflects the interdisciplinary nature and broad thematic coverage of the studies, spanning remote sensing, water quality, hydrology, and ecological monitoring. This variety highlights a wide array of suitable publication outlets for research in these domains.
Journals such as Environmental Science & Technology, Ecological Indicators, and the Journal of Hydrology served as prominent platforms for high-impact publications. Meanwhile, specialized journals like Remote Sensing and Water were frequently utilized for publishing technical and application-specific research.
Among the identified journals, Remote Sensing emerged as the most prominent outlet, accounting for 26 articles (33.3%) among the reviewed studies. This was followed by Ecological Indicators, with seven articles (9%). Water, Sensors, and Environmental Monitoring and Assessment each published five articles (6.4%), while Ecological Informatics contributed four articles (5%).
In contrast, Journal of Earth and Environmental Science, Drones, and the African Journal of Aquatic Science each accounted for two publications (2.6%). Environmental Science and Technology appeared least frequently among the top ten, contributing only one article (1.3%) Figure 5.
Table 2 summarizes the journals included in the review, presenting their publishers, Impact Factor (IF), 5-Year IF, quartile rankings, SCImago Journal Rank (SJR), and CiteScore.

3.3. Global Distribution of Studies

The spatial distribution of research articles on the application of remote sensing technologies for monitoring water hyacinth and water quality, as illustrated in the choropleth map (Figure 6), reveals notable global patterns. Studies were conducted across five continents Asia, North America, South America, Africa, and Europe, spanning a total of 25 countries.

3.4. Temporal Analysis of the Studies

Figure 7 illustrates the temporal distribution of studies on water hyacinth monitoring and water quality assessment. Our review shows that 40% of water hyacinth studies span more than ten years, while 60% cover shorter durations. In comparison, 30% of water quality assessment studies extend beyond a decade, whereas 70% were limited to less than ten years. On average, water hyacinth studies exhibit a temporal coverage of 22 years, compared to 15 years for water quality assessments.

3.5. Remote Sensing for Water Hyacinth Monitoring

Multispectral sensors have been widely employed in inland water monitoring, offering critical insights into aquatic vegetation and water quality. Operating across visible, near-infrared (NIR), and shortwave infrared (SWIR) bands, these sensors enable the effective detection of water hyacinth and related environmental parameters [35,36].
Several case studies highlight the application of multispectral data in water hyacinth monitoring. For example, [25] used Sentinel-2 MSI (bands B3, B4, B8) to map water hyacinth in Lake Tana, Ethiopia, achieving NDVI values between 0.6 and 0.95, indicating dense infestations. Similarly, ref. [37] identified Sentinel-2 bands 5 to 11 (0.740–1.610 µm) as optimal for detecting water hyacinth in Brazilian reservoirs. Ref. [38] applied Landsat 8 OLI bands 1–3 and 5 to assess inland water quality and vegetation dynamics, successfully delineating water hyacinth presence in Portuguese freshwater systems.
The choice of spectral bands and indices varies by objective, but vegetation indices such as NDVI have proven effective in isolating water hyacinth and turbidity signatures [2,13]. More recently, hyperspectral sensors such as Hyperion have enabled finer-scale analysis due to their high spectral resolution (0.4–2.5 µm). Ref. [39] demonstrated Hyperion’s utility in detecting chlorophyll-a concentrations in eutrophic waters, using continuous blue-green band ratios, which also support invasive plant monitoring through pigment analysis.

Modeling Approaches for Water Hyacinth Monitoring

Accuracy assessments for water hyacinth classification indicated that traditional statistical models, including Linear Regression (LR), Multiple Linear Regression (MLR), and Linear Discriminant Analysis (LDA), achieved an accuracy ranging from 74% to 95%. Machine learning algorithms, such as Random Forest (RF), Support Vector Machine (SVM), Classification and Regression Tree (CART), K-Nearest Neighbors (KNN), and Naïve Bayes (NB), exhibited accuracies between 65% and 98%. In comparison, deep learning architectures, including U-Net, Residual U-Net (Res-U-Net), and DeepLabV3 Plus, consistently outperformed conventional methods with accuracies ranging from 90% to 97%. Additionally, hybrid or index-based models incorporating Data Augmentation with Principal Data Augmentation (DA + PDA) and Spectral Band Combinations demonstrated an accuracy between 82% and 95%, as summarized in Table 3.

3.6. Remote Sensing for Water Quality Assessment

The advancement of remote sensing techniques has significantly increased the number of studies focusing on physical, chemical, and biological water quality parameters across spatial and temporal scales [34]. In earlier years, multispectral satellite sensors such as MODIS and MERIS were predominantly used for water quality assessment [34]. However, recent findings demonstrate a broader integration of technologies, including multispectral and hyperspectral sensors, unmanned aerial vehicles (UAVs) equipped with high-resolution cameras, and the application of machine learning algorithms to monitor key water quality parameters.
Among these, Sentinel-2 MSI has been frequently utilized for monitoring three primary water quality indicators. Table 4 presents the specific water quality parameters investigated during the study period, along with the corresponding satellite sensors employed.

Methods Used for Establishing Inversion Algorithms

Figure 8 illustrates the number of studies, and the corresponding methods employed to assess water quality parameters. Empirical methods were the most widely used, accounting for 76% of the total studies, followed by semi-empirical methods, at 17%. Semi-analytical methods were the least utilized, representing only 3% of the reviewed studies. Analytical and semi-analytical approaches remain relatively rare in water quality research. Instead, a combination of statistical techniques, measured spectral responses, and bio-optical theory is commonly applied for parameter estimation [59]. In addition, the review identified that machine learning algorithms have increasingly been used to support empirical approaches, with Random Forest (RF), Support Vector Machine (SVM), Extreme Gradient Boosting (XGBoost), and Categorical Boosting (CatBoost) emerging as the most frequently applied models for predicting water quality parameters.
Our review further identified that the empirical method is predominantly applied in the assessment of chlorophyll-a (Chl-a), turbidity, and total suspended solids (TSS). Semi-empirical methods also played a significant role, particularly in studies involving these three parameters. Analytical and semi-analytical methods were occasionally employed, especially in the analysis of turbidity and TSS.

4. Discussion

4.1. Publication Trends

The number of published articles using satellite sensors for inland water monitoring has increased over time. Studies attribute this growth to advancements in remote sensing technology, improved data availability, and enhanced accessibility through cloud-based platforms such as Google Earth Engine (GEE). Additionally, global policy and monitoring initiatives targeting inland water ecosystems have increased interest and led to a significant rise in scholarly publications in water resources monitoring [31,60,61]. Similarly, [62] reported that the advancement of machine learning techniques has significantly enhanced the classification and modeling capabilities of satellite data, thereby improving the efficiency and effectiveness of inland water monitoring using satellite sensors. As a result, the number of remote sensing-based studies for inland water monitoring has increased in recent years.
An analysis of thematic trends reveals that water quality was the first focus (49%) across the study period. The number of studies addressing water quality increased linearly over time, reflecting growing global research priorities over environmental degradation and the need for improved surface water monitoring [59]. Ref. [63] also highlighted that the deterioration of surface water quality poses a major challenge for water resource managers, emphasizing the urgent need for continuous and detailed water quality assessments. Furthermore, the emergence of new contaminants, including microplastics, has intensified global attention on water quality. This shift is consistent with international environmental commitments, first articulated under the Millennium Development Goals (MDGs) and advanced through the Sustainable Development Goals (SDGs), which have intensified efforts in the systematic monitoring of lake water quality [64]. This has emerged as a critical focus as lake water quality deterioration accelerates the proliferation of water hyacinth and other invasive aquatic weeds, thereby disrupting ecosystem integrity. Addressing the root cause of degraded water quality should therefore take precedence over managing the symptom, including the spread of water hyacinth. In response, remote sensing-based studies on water quality have increased, aiming to address global water quality issues and support sustainable inland water management.
In contrast, studies focusing on water hyacinth, which accounted for the second major research theme (42%) in this review, tend to receive comparatively less attention across many regions. This is largely because funding agencies often prioritize water quality research, given its global significance and direct implications for public health and resource management. Although water hyacinth is widely acknowledged as a highly invasive species, it is frequently regarded as a region-specific or localized challenge that can be mitigated through conventional control strategies such as mechanical removal, biological control, or resource utilization. Consequently, this perception limits its research priority and reduces scholarly engagement compared to the more universally relevant issue of water quality.
The emphasis on lakes in remote sensing applications is largely due to their relatively larger surface area and spatial continuity, which make them more suitable for satellite-based monitoring. Additionally, the global availability of long-term remote sensing data, along with the ecological importance and relevance of lakes in addressing global environmental challenges, has contributed to their prioritization in scientific research [65,66,67].
Similarly, water hyacinth-related studies have shown a steady increase and were conducted every year throughout the review period. Water hyacinth, which is now found on every continent except Antarctica, has drawn scientific interest due to its widespread ecological impact [68]. Ref. [29] demonstrated a linear growth in the number of satellite-based studies
Remote sensing applications for monitoring water hyacinth and water quality have been documented across five continents—Asia, North America, South America, Africa, and Europe, covering 25 countries. This global distribution reflects growing recognition of aquatic ecosystem degradation and the value of satellite-based monitoring. In Asia, China, India, Pakistan, and Taiwan are major contributors, with China leading the region. The rise in publications is driven by industrialization, increasing water demand, and policy shifts toward improved resource management [69]. In North America, the United States dominates research output, followed by Guatemala. The U.S. also demonstrates strong international collaborations, particularly with India, advancing shared methods and datasets for global monitoring [34]. In South America, Brazil and Chile are primary contributors. Brazil, covering much of the Amazon Basin and historically impacted by water hyacinth, has played a key role in developing remote sensing approaches tailored to tropical aquatic systems.
In Africa, South Africa leads, followed by Kenya, Ethiopia, and Zimbabwe. Research is supported by the growing use of Landsat and Sentinel data to address pollution, eutrophication, and invasive species in inland waters [70]. In Europe, studies from Portugal, Belgium, Estonia, Turkey, and Czechia are notable. Portugal utilizes multispectral data from the Copernicus Sentinel-2 program, reflecting the region’s strong engagement with open-access geospatial technologies.
Overall, the research landscape is globally distributed but spatially uneven. While countries like China, the U.S., and South Africa serve as hubs, many regions remain underrepresented. Addressing this imbalance requires targeted investment in research capacity and geospatial infrastructure in low- and middle-income countries. Expanding the geographic reach of remote sensing will support more equitable and comprehensive monitoring of freshwater ecosystems.
Moreover, the temporal analysis indicates that water hyacinth studies generally span longer durations, reflecting the relative ease of detecting its distinct spectral reflectance compared to the more complex retrieval of water quality parameters. Floating macrophytes such as water hyacinth often exhibit strong and distinguishable optical signals in near-infrared and red-edge wavelengths, which enhances their detectability under remote sensing [71]. In contrast, water quality constituents frequently require sophisticated retrieval algorithms, face challenges in atmospheric correction and mixed pixel effects, and are constrained by trade-offs in sensor resolution and revisit frequency [72].

4.2. Satellite Sensors Used for Monitoring

This growing adoption is primarily attributed to Sentinel-2 MSI’s design tailored for environmental monitoring, offering high spatial resolution (10 m), frequent revisit times, and advanced capabilities for water quality assessment, aquatic vegetation detection, and mapping the extent of water bodies [73,74,75]. Similarly, ref. [51] successfully demonstrated the suitability of Sentinel-2 MSI imagery for monitoring inland water quality, highlighting its potential for application in various freshwater systems globally.
On the other hand, Landsat 8 OLI was the second most used satellite sensor, appearing in 18 studies during the review period (Figure 4a). Its widespread application is largely attributed to its extensive historical archive, moderate spatial resolution (30 m), and freely accessible, open-source data, making it a valuable resource for researchers around the world. The sensor provides global coverage every 16 days, allowing for consistent monitoring of inland water bodies. Landsat 8 OLI is equipped with key spectral bands Blue, Green, Red, NIR, and SWIR, which are particularly effective for detecting water hyacinth and retrieving important water quality parameters such as chlorophyll-a (Chl-a), turbidity, and total suspended solids (TSS). According to [76], the long-term use of Landsat 8 has played a critical role in inland water monitoring, primarily due to its moderate spatial resolution and consistent, long-term data availability. As a result, Landsat 8 OLI has become a widely trusted data source for researchers, particularly in regions with limited or inconsistent ground-based observations. Its openly accessible archive allows for retrospective analysis, enabling the study of temporal trends and long-term ecological changes [22].
Achieving enhanced spatial and temporal resolution is essential for supporting environmental decision-making and advancing research in inland water monitoring [77]. To address the limitations of individual sensors, such as coarse spatial resolution, low revisit frequency, and cloud interference, researchers have increasingly adopted image fusion techniques. These approaches combine datasets from multiple sensors to produce composite imagery with improved spatial and temporal detail [74,78].
These methods were primarily implemented in Asian inland water bodies, particularly in China, for the retrieval of key water quality parameters and to support water resource management and policy development decisions [35,79,80]. The combined application of UAV imagery and Sentinel-2 MSI enables the generation of high-resolution, multi-scale datasets, facilitating more detailed and accurate assessments of inland aquatic environments.

4.3. The Changing Landscape of Peer-Reviewed Journals

Overall, the distribution of publications underscores the expanding application of remote sensing technologies in environmental research, particularly in geospatial data analysis. The predominance of Remote Sensing as a leading publisher of such research reflects the growing emphasis on spatial and temporal analysis in the study of inland and global water bodies
The diversity of journals highlights the interdisciplinary nature of the field, spanning environmental science, remote sensing, hydrology, and ecological monitoring.
Among the highest-ranking outlets, Nature stood out with an exceptional IF of 69.0 and SJR of 18.786, reflecting its status as a premier multidisciplinary journal. Environmental Science & Technology (IF = 11.3, SJR = 2.625, CiteScore = 14.8) and Marine Pollution Bulletin (IF = 8.0, SJR = 1.748, CiteScore = 9.1) were also identified as leading Q1 journals, frequently publishing high-impact research on water quality and environmental pollution.
Journals such as Ecological Indicators (IF = 7.4), Journal of Hydrology (IF = 5.9), and Drones (IF = 4.8) were consistently ranked in Q1, emphasizing their relevance in ecological assessment, hydrological analysis, and remote sensing applications. Their strong CiteScores (6.0–8.6) indicate sustained scholarly engagement.
Remote Sensing (MDPI) emerged as a major open-access platform (IF = 4.2, CiteScore = 5.1, Q1), widely used for publishing studies with a spatial and temporal focus. Other MDPI journals, such as Water (IF = 3.0), Sensors (IF = 3.5), Plants (IF = 4.1), and Sustainability (IF = 2.6) provided accessible outlets with moderate to high impact and relatively faster publication timelines, primarily in Q1–Q2 categories.
Additional journals included Ecological Informatics (IF = 5.0, Q1), focused on ecological modeling, and the Egyptian Journal of Remote Sensing and Space Sciences (IF = 4.1, Q2), which supports regionally focused studies. Lower-level journals like Environmental Monitoring and Assessment (IF = 2.5, Q3), Desalination and Water Treatment (IF = 1.0, Q4), and Invasive Plant Science & Management (IF = 1.5, Q2) were also present but contributed fewer citations (Table 2).
In comparison, Elsevier and Springer journals consistently ranked higher in terms of SJR and CiteScore, indicating stronger academic influence, while MDPI journals offered wider accessibility and faster dissemination.

4.4. Spatial and Temporal Variability of Water Hyacinth Expansion

The spatial and temporal coverage of water hyacinth (Eichhornia crassipes) varies considerably across regions and seasons, driven by both environmental and anthropogenic factors growth [44,68,81]. Despite decades of control efforts, remote sensing evidence indicates that water hyacinth infestations in freshwater ecosystems are not only persisting but are expanding globally [2,5].
Water hyacinth coverage has shown significant seasonal and interannual variability across freshwater systems. In Vietnam’s Saigon River, the weed occupied up to 24% of the river surface in upstream sections during the dry season [82]. In Ethiopia’s Lake Tana, infestation expanded sharply from less than 10,000 hectares in 2011 to nearly 50,000 hectares by 2017 [83,84], with localized growth from 112.1 ha in 2013 to 1512 ha by 2017 [85]. The northern part of the lake, previously unaffected in 2010, reached over 1360 ha by 2019, growing at an average rate of 136 ha per year [86]. Short-term assessments using MODIS data revealed rapid fluctuations, with increases of 14 ha/day between August and November 2017, followed by a decline of 6 ha/day during subsequent removal efforts [81].
Sentinel-2 observations captured similar dynamics in Lake Tana, showing an increase from 278 ha in February 2015 to over 2050 ha by December 2019 [87]. These fluctuations highlight the influence of seasonal variability, cloud cover, acquisition timing, and the plant’s mobility.
Environmental drivers such as eutrophication, water level changes, and temperature regimes play a central role in the weed’s proliferation [87,88]. Optimal growth has been reported at surface water temperatures of 28–30 °C and nighttime air temperatures of 13–19 °C [8,81], though persistence has been observed at lower temperatures, down to 12 °C [38], indicating a broader thermal tolerance.
Lake morphology and water quality further influence infestation dynamics. Shallow systems (<6 m depth) are particularly vulnerable, with seasonal variation linked to pH levels (6.5–8.5), nitrate concentrations (5.5–20 mg/L), phosphate (1.66–3 mg/L), and potassium levels up to 55 mg/L [4].
Advancements in remote sensing technologies, particularly when integrated with machine learning algorithms, have enhanced the capacity to detect, map, and monitor water hyacinth infestations with high spatial and temporal resolution. These tools offer critical support for developing data-driven management strategies [50,89,90,91].

Comparative Approaches to Water Hyacinth Monitoring and Assessment

Traditional statistical methods have long been used in the classification of water hyacinth due to their simplicity and interpretability. Techniques such as Linear Regression (LR), Multiple Linear Regression (MLR), and Linear Discriminant Analysis (LDA) rely on assumptions of linearity and statistical independence. LR has been successfully applied in remote sensing contexts, with [81] reporting 91% overall accuracy and [40] achieving 95% using MODIS and Sentinel-2 data, respectively. MLR, using Landsat 8 imagery, yielded an 85% accuracy in [41]. LDA, used by [92] and [42], produced comparatively lower accuracies ranging from 74% to 81%, likely due to its assumption of equal class covariances. While computationally efficient and easily interpretable, these methods are often limited in complex environments where nonlinear relationships dominate, and they can be sensitive to multicollinearity and outliers [93,94].
Machine learning (ML) methods have gained significant traction due to their ability to model complex, nonlinear patterns without relying on strict statistical assumptions. Among the most widely used is the Random Forest (RF) classifier, with demonstrated accuracies between 90% and 98% in water hyacinth classification tasks [43]. RF is known for its robustness to overfitting and ability to handle high-dimensional, multivariate datasets [90,95]. Support Vector Machines (SVM) have also been employed effectively, with reported accuracy ranging from 65% to 94%, depending on kernel selection and data properties [7,38]. Other ML approaches, such as Classification and Regression Trees (CART), K-Nearest Neighbors (KNN), and Naive Bayes (NB), have shown moderate performance, with accuracy between 83% and 87% [38]. Although it is simple to implement, KNN and NB tend to underperform on large-scale or noisy datasets due to their basic conceptual frameworks.
Deep learning (DL) techniques have recently been adopted in water hyacinth mapping to improve classification precision. Convolutional neural network architectures, including U-Net, Res-U-Net, and DeepLabV3+, have achieved remarkable results. For instance, ref. [46] applied U-Net to multispectral images from a self-assembled sensor system, achieving 97% accuracy. Similarly, Res-U-Net applied to Sentinel-2 data reached 90% accuracy [96], while DeepLabV3+ using MODIS and MERIS datasets attained 95% accuracy [48]. These models are particularly effective in capturing spatial and spectral features but require large, annotated datasets and substantial computational resources [31].
Hybrid models offer a compromise between model complexity and practicality. For example, ref. [49] applied a combined Discriminant Analysis (DA) and Partial Discriminant Analysis (PDA) approach to Landsat 8 data, achieving 95% accuracy. Simpler two-band index combinations using Sentinel-2 imagery also demonstrated effectiveness, yielding up to 82% accuracy [50].
Overall, the literature reveals a clear trend toward more sophisticated classification models, from statistical techniques to machine and deep learning. While advanced models generally offer higher accuracy, they also demand greater computational power, larger datasets, and technical expertise [45,97]. Therefore, the choice of classification method should consider the specific project’s context, including target accuracy, data availability, and computational constraints [98]. Although machine learning and deep learning approaches are currently the most accurate, traditional and hybrid methods remain valuable, particularly in resource-limited settings or those where training data are scarce [99]. Continued research is needed to advance adaptive, ensemble, and hybrid frameworks that balance performance with accessibility and scalability across diverse ecological monitoring scenarios [46].

4.5. Satellite-Based Monitoring of Water Quality Dynamics

4.5.1. Chlorophyll-a

Chlorophyll-a (Chl-a) is a widely used indicator for assessing the trophic status of freshwater bodies, as its concentration reflects phytoplankton biomass and overall water quality [100,101]. Elevated Chl-a levels are often linked to harmful algal blooms that can deplete dissolved oxygen, release toxins, and pose significant risks to aquatic ecosystems and public health [34].
Remote sensing platforms such as Sentinel-2 MSI and Landsat 8 OLI are particularly effective for Chl-a detection due to their spectral bands in the blue (430–450 nm) and red (660–670 nm) wavelengths [100,102]. For instance, ref. [103] recorded a Chl-a concentration of 292.2 mg/L in the Poteran Islands (Indonesia), while ref. [104] reported 94 mg/L in a lake in Czechia, with corresponding model performances (R2) of 0.58 and 0.90. In Lake Peipsi (Estonia), ref. [51] reported 23.4 mg/L with an R2 of 0.83.
Conversely, significantly lower Chl-a concentrations have been reported in post-rainy season studies using Sentinel-2 MSI. These include values of 0.001 mg/L, 0.004 mg/L, and 0.06 mg/L with strong model performances (R2 = 0.86, 0.97, and 0.75, respectively) [61,105,106]. In China’s Karst wetlands, ref. [97] applied deep learning models integrating multi-sensor, multi-platform remote sensing data and found a mean Chl-a concentration of 0.26 mg/L (R2 = 0.93). The study noted that 32.66% of the water surface exceeded the pollution threshold of 0.06 mg/L, indicating significant water quality concerns.
Spatial heterogeneity can affect remote sensing accuracy. For example, ref. [105] reported an underestimation of Chl-a (26 µg/L) in Lake Taihu, China, due to its complex spatial structure. In Turkey’s Borabey Dam, hyperspectral imagery produced a Chl-a estimate of 0.9 mg/L with a high model fit (R2 = 0.96), highlighting the value of red-edge bands and high-resolution sensors [107]. Similarly, ref. [108] reported 1.54 mg/L in Utah Lake (USA) using a combined approach with Landsat 8 OLI, Sentinel-2 MSI, and MODIS Terra.
In Lake Sergoit, Kenya, ref. [22] used a combined Sentinel-2 and Landsat 8 approach and reported a Chl-a concentration of 2.56 mg/L, though with modest model performance (R2 = 0.51). In Ethiopia’s Lake Tana, ref. [25] applied Sentinel-2A/B imagery and reported a mean Chl-a value of 8.5 mg/L with a strong fit (R2 = 0.85), confirming the sensor’s suitability for inland water quality monitoring when appropriate atmospheric corrections are applied.
Therefore, the selection of satellite imagery for Chlorophyll-a estimation depends on factors such as spatial and temporal resolution requirements, the size and heterogeneity of the water body, specific research objectives, and resource availability [109]. Sentinel-2 MSI and Landsat 8 OLI offer a practical balance between spatial resolution and coverage, making them well-suited for both routine monitoring and large-scale water quality assessment [110].

4.5.2. Turbidity

Turbidity is one of the most frequently assessed parameters in inland water monitoring using satellite remote sensing [22]. It represents the extent to which light penetrates the water column and is closely associated with the presence of suspended particulates, including silt, clay, organic matter, algae, and microorganisms [58]. As a key water quality indicator, turbidity influences underwater light availability, which in turn affects photosynthesis, thermal structure, and the overall ecological integrity of aquatic systems [111,112].
Optically, turbid waters exhibit heightened reflectance in the visible spectrum, particularly in the green (~550 nm) and red (~660 nm) wavelengths, due to increased backscattering from suspended solids. With rising turbidity, reflectance in the near-infrared (NIR) region also increases, driven by stronger scattering effects [113].
In Ethiopia’s Lake Tana, ref. [81] reported a maximum turbidity value of 348 NTU in the northern basin, though model performance was modest (R2 = 0.27). In contrast, a study in India’s Chilika Lake using a spectral similarity approach and multispectral sensors recorded 178 NTU with stronger model accuracy (R2 = 0.80) [112]. Multiple studies in China reported varying turbidity values 150 NTU [113], 121 NTU [114], 60 NTU [115], 18.07 NTU [79], and 16.9 NTU [116] highlighting spatial heterogeneity. The highest values were derived from Sentinel-2 MSI and UAV-mounted RGB imagery, emphasizing the role of sensor type and spatial resolution in turbidity estimation.
Lower turbidity levels were also observed in other contexts. For example, ref. [97] reported a minimum value of 1.31 NTU in Turkey using RapidEye imagery, while ref. [58] recorded 3.66 NTU in Florida using high-resolution multispectral sensors and empirical modeling.
Overall, the use of multispectral and hyperspectral sensors enabled effective turbidity monitoring across diverse aquatic environments from small rivers and wetlands to large lakes. However, turbidity values vary significantly across regions and seasons, primarily influenced by environmental drivers such as rainfall, sediment influx, and nutrient loading.

4.5.3. Total Suspended Solids

The spectral response of Total Suspended Solids (TSS) varies across different regions of the electromagnetic spectrum, particularly in the blue (400–495 nm), green (495–570 nm), red (620–750 nm), and near-infrared (>750 nm) wavelengths [117]. These variations are influenced by particle size, concentration, and composition.
Among the reviewed studies, the highest TSS concentration 2511 mg/L was recorded in India using Sentinel-2 MSI and semi-empirical methods [32]. Similarly, ref. [113] reported 416 mg/L, in Taiwanese river using the same sensor and empirical methods, while ref. [118] recorded 71.2 mg/L using hyperspectral sensors and semi-empirical models. Notably, ref. [32] applied a novel approach integrating Google Earth Engine (GEE) and spectral indices to estimate TSS post-rainy season, highlighting the potential of user-oriented visualization tools for environmental monitoring. Extremely high TSS values, up to 2627 mg/L, have been reported in global studies across lakes, rivers, and estuaries [119,120], indicating the variable nature of TSS, influenced by hydrological and seasonal dynamics.
Overall, findings from this review indicate significant spatial and temporal variability in TSS concentrations, emphasizing the influence of local environmental conditions. The integration of emerging technologies, particularly machine learning, enhances the retrieval accuracy and predictive capacity of satellite-based TSS monitoring.

4.5.4. Spatiotemporal Variability of Water Quality Parameters

Understanding the spatial and temporal variability of water quality is critical for the sustainable management of freshwater systems that support drinking water supply, irrigation, hydropower, and recreational activities. Declining water quality poses serious ecological, health, and environmental risks, often limiting the suitability of water bodies for these uses [34]. Variability in water quality is primarily influenced by climatic conditions and anthropogenic activities such as land use changes, urbanization, and agricultural runoff.
In Ethiopia’s Lake Tana, remote sensing observations during the dry season revealed that elevated temperatures were associated with increased concentrations of chlorophyll-a (Chl-a) and suspended matter, indicating strong seasonal influences on water quality dynamics [121]. Similarly, a long-term analysis of the Yangtze River Basin in China (2006–2018) using Landsat ETM+ imagery found a significant relationship between land use patterns and water quality parameters, underscoring the impact of watershed development on aquatic conditions [122]. Sensor selection has also been shown to affect detection accuracy; for example, ref. [108] demonstrated that choosing appropriate sensors was critical to capturing spatiotemporal variability in Utah Lake and the Great Salt Lake, USA.
In Sri Lanka, ref. [123] developed a remote sensing-based water quality index for Beira Lake, successfully tracking changes between 2016 and 2023 using multispectral imagery. In Turkey, ref. [124] reported higher Chl-a concentrations in the northern region of Lake Burdur, attributing these spatial patterns to land use alterations in the surrounding watershed. Likewise, in Chile, ref. [125] integrated in situ data with Landsat 8 OLI imagery to monitor eutrophication processes in an urban lake, highlighting the value of combined data approaches.
A recent study on Lake Koka in Ethiopia using Sentinel-2 MSI imagery illustrated pronounced spatial and seasonal variation in key water quality indicators [126]. Monthly Chl-a concentrations ranged from 59.69 to 144.25 µg/L, turbidity from 79.67 to 115.39 NTU, and total suspended solids (TSS) from 38.46 to 368.97 mg/L. Spatially, the highest Chl-a levels were observed in the southern and southeastern zones of the lake, while turbidity and TSS peaked along the western shoreline, reflecting the heterogeneous nature of water quality in the system.
These findings collectively emphasize the importance of integrating spatial and temporal perspectives in remote sensing-based water quality monitoring. Such approaches improve the ability to detect trends, assess the impact of land and climate dynamics, and support more informed management and policy decisions across diverse aquatic environments.

4.6. Challenges and Gaps of Remote Sensing Applications

Remote sensing has emerged as a powerful tool for monitoring inland water bodies, offering broad spatial coverage and temporal consistency. However, several challenges and research gaps continue to constrain their full potential in water quality and aquatic vegetation assessments. One prominent issue is the limited understanding and inconsistent application of sensor-specific characteristics and image processing protocols, particularly atmospheric correction procedures [127,128]. Many reviewed studies applied differing correction methods, while others relied solely on top-of-atmosphere (TOA) reflectance without performing atmospheric correction. Such inconsistencies can introduce significant errors in the estimation of water quality indices, compromising the reliability of results.
Another critical limitation is the insufficient validation of remote sensing outputs. Approximately 10% of the reviewed studies lacked proper validation through in situ ground-truth data. This shortfall is often attributed to challenges such as limited field access, adverse seasonal weather conditions, and the unavailability of reliable ground-based measurements. The absence of validation reduces the credibility of remote sensing-derived estimates and hampers their integration into management frameworks.
Furthermore, research has disproportionately focused on large water bodies such as lakes, reservoirs, and major rivers, while ecologically significant small water bodies, including ponds, wetlands, and small rivers, remain underrepresented in remote sensing studies. These smaller systems, despite their importance for biodiversity and local water supply, are often overlooked due to limitations in sensor resolution and methodological design.
Remote sensing holds strong potential for mapping water hyacinth and monitoring inland water quality, but its application is limited by data gaps, methodological inconsistencies, and insufficient validation. Integrating citizen science provides essential ground truth, enhancing coverage and predictive capacity. Together, they offer a comprehensive framework for informed inland water management and sustainable decision-making.

5. Conclusions

In conclusion, the global application of remote sensing technologies for monitoring water hyacinth and water quality in inland aquatic ecosystems has expanded considerably. Of the studies reviewed, 61.5% focused on lakes, 21% on rivers, and 10.3% on wetlands, and 7.7% addressed both lakes and rivers. Nearly half (49%) of the studies targeted water quality assessment, while 42% focused on mapping water hyacinth and estimating its biomass, while the remaining 9% examined both.
Spatial distribution analysis revealed that China, India, South Africa, and the United States lead in the application of remote sensing technologies for aquatic monitoring. Sentinel-2 MSI emerged as the most widely used satellite sensor, followed by Landsat 8 OLI and UAV-mounted RGB cameras for the whole review period. Notably, the combination of UAV-mounted RGB sensors with Sentinel-2 MSI was the most frequently employed setup used for chlorophyll-a (Chl-a) retrieval. Sentinel-2 MSI and Landsat 8 OLI have also been extensively used to detect Chl-a, turbidity, and water hyacinth infestations.
In terms of modeling approaches, linear regression (LR), multiple linear regression (MLR), and linear discriminant analysis (LDA) achieved mapping accuracies ranging from 74% to 95%. Machine learning algorithms such as random forest (RF), support vector machine (SVM), classification and regression trees (CART), k-nearest neighbors (KNN), and naive Bayes (NB) demonstrated a broader accuracy range of 65% to 98%. More recently, deep learning architectures, including U-Net, ResU-Net, and DeepLabV3, have enhanced mapping accuracy up to 97% in water hyacinth studies.
However, around 10% of the reviewed studies did not apply appropriate validation techniques or atmospheric correction procedures, which compromise the accuracy and reliability of their results. To address this gap, future research should focus more on underrepresented small and medium-sized inland water bodies and broaden the scope of remote sensing applications to include optically inactive water quality parameters, such as nutrients and dissolved oxygen.
The integration of multi-source datasets, particularly UAV-based observations, with advanced machine learning and deep learning models holds substantial promise for enhancing the accuracy of remote sensing analyses. This approach could also serve as a reliable ground-truthing mechanism to validate and support satellite-based water quality and vegetation monitoring. Expanding the search to include additional databases such as Dimensions, Microsoft Academic, ProQuest, and the gray literature from institutional repositories would improve coverage. Moreover, while this review focused on selected key optically active water quality parameters, future studies should consider both optically active and non-optically active parameters to better capture global water quality dynamics. Finally, incorporating non-English language publications would help include valuable regional studies often overlooked in global syntheses.
Finally, these findings offer valuable insights into developing water resource management strategies across diverse water bodies, particularly for addressing challenges such as water quality deterioration and water hyacinth proliferation. Promoting effective legislation and community-based initiatives is essential to mitigate global water degradation driven by anthropogenic pressures and climate change.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/w17172573/s1, Table S1: Summary of multispectral sensors and their characteristics; Table S2: Summary of Studies on Chl-a with Methods and Sensors Applied; Table S3: Summary of Studies on Turbidity with Methods and Sensors Applied; Table S4: Summary of Studies on TSS with Methods and Sensors Applied. References [129,130,131,132,133,134,135,136,137] are cited in the Supplementary Materials.

Author Contributions

L.Y.A.: Conceptualization, methodology, formal analysis, writing—original draft, visualization; D.A.: supervision, data interpretation, writing—review and editing, validation, final approval; A.v.G.: supervision, writing—review and editing, validation, final approval; G.G.: supervision, project administration, writing—review and editing; S.Y.: methodology, supervision, project administration, writing—review and editing; W.B.A.: writing—review and editing, critical revision of the manuscript for intellectual content; M.G.D.: data curation, supervision, writing—review and editing; D.A.M.: methodology, software, spatial analysis, drafting of figures. C.I.M.: funding acquisition, writing—review and editing, critical revision for intellectual content; S.A. (Selamawit Amare): data analysis, writing—review and editing and S.A. (Sisay Asress): formal analysis, writing—review and editing. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by The IHE Delft Water and Development Partnership Program (WDPP), financed by the Dutch Ministry of Foreign Affairs, through the project Remote Sensing for Community-driven Applications: from WA+ to Co-learning (RS-4C, grant number 111362). The article processing charge (APC) was supported by IHE Delft Institute for Water Education, Westvest 7, 2611 AX Delft, The Netherlands.

Data Availability Statement

The original contributions presented in this study are included in the article/Supplementary Materials. Further inquiries can be directed to the corresponding author.

Acknowledgments

The authors acknowledge the Bahir Dar Institute of Technology, Bahir Dar University, and the Blue Nile Water Institute for providing institutional guidance and support. Special thanks are extended to the IHE Delft Institute for Water Education for its valuable support in training and capacity building related to this work. Finally, sincere gratitude is expressed to Bantsew Muluye for his unwavering support and continuous encouragement throughout the study.

Conflicts of Interest

The authors declare no conflicts of interest.

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Figure 1. PRISMA flow diagram adapted for this study.
Figure 1. PRISMA flow diagram adapted for this study.
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Figure 2. (a) Annual number of remote sensing studies on water hyacinth and water quality; (b) annual number of remote sensing studies on specific water body types.
Figure 2. (a) Annual number of remote sensing studies on water hyacinth and water quality; (b) annual number of remote sensing studies on specific water body types.
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Figure 3. Research articles distribution based on study focus.
Figure 3. Research articles distribution based on study focus.
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Figure 4. (a) Frequency of satellites applied for the study from year 2014 to 2024; (b) combined application of different remote sensing datasets.
Figure 4. (a) Frequency of satellites applied for the study from year 2014 to 2024; (b) combined application of different remote sensing datasets.
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Figure 5. Leading ten journals regarding the publication of studies.
Figure 5. Leading ten journals regarding the publication of studies.
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Figure 6. Global distribution of studies on remote sensing applications focused on water hyacinth and water quality.
Figure 6. Global distribution of studies on remote sensing applications focused on water hyacinth and water quality.
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Figure 7. Temporal distribution of studies.
Figure 7. Temporal distribution of studies.
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Figure 8. Number of studies of water quality inversion methods.
Figure 8. Number of studies of water quality inversion methods.
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Table 1. Summary of keywords used applied in the literature search.
Table 1. Summary of keywords used applied in the literature search.
CategoryKeywords Used
Remote Sensing Technologies“Remote sensing”, “satellite imagery”, “UAV”, “Drone”
Target Species“Water hyacinth”, “Eichhornia crassipes”
Water Quality Parameters“Chlorophyll-a”, “Turbidity”, “Total suspended solids”
Functional/application-oriented terms“Monitoring”, “Detection”, “Mapping”
Geographical/Ecosystem type“Global water bodies”, “Lakes”, “Rivers”, “Wetlands”
Table 2. Summary of journals in the review and their impact details.
Table 2. Summary of journals in the review and their impact details.
JournalPublisherImpact Factor (2023/2024)5-Year IFQuartileSJRCiteScore
Remote SensingMDPI4.24.8Q11.0915.1
Ecological IndicatorsElsevier7.47.2Q11.6338.6
WaterMDPI3.03.3Q20.7245.0
Environmental Science & TechnologyACS11.311.6Q12.62514.8
Environmental Monitoring and AssessmentSpringer2.5-Q30.5023.4
SensorsMDPI3.53.7Q20.8566.1
Ecological InformaticsElsevier5.0-Q11.3486.7
DronesMDPI4.85.0Q11.1145.5
ISPRS ArchivesISPRS0.5-Unranked0.1980.7
Physics and Chemistry of the EarthElsevier3.33.2Q20.7193.9
NatureSpringer Nature69.0-Q118.78695.0
HeliyonElsevier3.63.9Q20.7114.9
Desalination and Water TreatmentElsevier1.0-Q40.2982.2
Journal of Applied Water ScienceSpringer5.76.2Q10.8926.0
Egyptian Journal of Remote Sensing and Space SciencesElsevier4.14.8Q20.7454.5
International Journal of Geo-InformationMDPI3.4-Q20.8925.3
Earth Observation and Remote SensingHarwood Academic0.1-Unranked0.1030.2
PlantsMDPI4.1-Q11.0125.7
Invasive Plant Science & ManagementCUP1.5-Q20.5232.6
SustainabilityMDPI2.6-Q20.6614.0
Journal of HydrologyElsevier5.9-Q11.9937.9
GIS and Remote SensingTaylor & Francis2.0-Q20.6923.8
Marine Pollution BulletinElsevier8.0-Q11.7489.1
Table 3. Summary of methods, techniques, and overall accuracy achieved.
Table 3. Summary of methods, techniques, and overall accuracy achieved.
Method TypeTechniquesAccuracy RangeReferences
Statistical ModelsLR, MLR, LDA74–95%[38,40,41,42,43]
Machine LearningRF, SVM, CART, KNN, NB65–98%[43,44,45]
Deep LearningU-Net, Res-U-Net, DeepLabV3+90–97%[46,47,48,49,50]
Hybrid/Index-BasedDA+PDA, Band Combinations82–95%[49,50]
Table 4. Summary of water quality parameters and satellite sensors used for studies.
Table 4. Summary of water quality parameters and satellite sensors used for studies.
Water Quality Parameters Satellite Sensors UsedKey Studies (Citations)
Chlorophyll-aLandsat-8 OLI, Sentinel-2 MSI[32,51,52,53,54,55]
TurbidityMODIS Terra, Sentinel-2 MSI, Landsat-8 OLI[18,25,56,57]
Total suspended solidsMODIS Terra, Sentinel-2 MSI, Landsat-8 OLI[18,22,56,58]
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MDPI and ACS Style

Alemneh, L.Y.; Aklog, D.; Griensven, A.v.; Goshu, G.; Yalew, S.; Abebe, W.B.; Dersseh, M.G.; Mhiret, D.A.; Michailovsky, C.I.; Amare, S.; et al. Remote Sensing Approaches for Water Hyacinth and Water Quality Monitoring: Global Trends, Techniques, and Applications. Water 2025, 17, 2573. https://doi.org/10.3390/w17172573

AMA Style

Alemneh LY, Aklog D, Griensven Av, Goshu G, Yalew S, Abebe WB, Dersseh MG, Mhiret DA, Michailovsky CI, Amare S, et al. Remote Sensing Approaches for Water Hyacinth and Water Quality Monitoring: Global Trends, Techniques, and Applications. Water. 2025; 17(17):2573. https://doi.org/10.3390/w17172573

Chicago/Turabian Style

Alemneh, Lakachew Y., Daganchew Aklog, Ann van Griensven, Goraw Goshu, Seleshi Yalew, Wubneh B. Abebe, Minychl G. Dersseh, Demesew A. Mhiret, Claire I. Michailovsky, Selamawit Amare, and et al. 2025. "Remote Sensing Approaches for Water Hyacinth and Water Quality Monitoring: Global Trends, Techniques, and Applications" Water 17, no. 17: 2573. https://doi.org/10.3390/w17172573

APA Style

Alemneh, L. Y., Aklog, D., Griensven, A. v., Goshu, G., Yalew, S., Abebe, W. B., Dersseh, M. G., Mhiret, D. A., Michailovsky, C. I., Amare, S., & Asress, S. (2025). Remote Sensing Approaches for Water Hyacinth and Water Quality Monitoring: Global Trends, Techniques, and Applications. Water, 17(17), 2573. https://doi.org/10.3390/w17172573

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