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Creative Commons License BY 4.0.
This report is for the watershed with an outlet near 4°25'37"S, 73°26'41"W, or (-4.427, -73.445), with a drainage area of around 714,000 km².
The watershed is located in three countries, as shown below in Table 1 below.
Table 1. Countries in the watershed.
| Country | Area (km²) | Percent of watershed |
|---|---|---|
| Peru | 649,000 | 91% |
| Ecuador | 65,300 | 9% |
| Brazil | 633 | 0% |
Data on political boundaries comes from Natural Earth, https://www.naturalearthdata.com.
The watershed has an estimated population of 12,400,000 in the year 2020. Figure 1 shows how population has changed from 1990 to 2020. The population grew at an average rate of 1.1% per year over this time period.
Population data comes from GlobPop, Global Gridded Population Estimates, created by researchers at Beijing Normal University (Liu 2024).
Human population growth can affect water quality via increased pollution from households, industry, and agriculture. Further, land use and land cover change associated with population growth can have a major impact on watersheds (see the next section of this report).
The most common land cover type in the watershed is tree cover, covering 447,000 km² in 2020. More detailed information about land cover and how it has changed is shown in Table 3 and Figure 2 below. Pairs of bars represent the area for each land cover type in the years 2000 and 2020.
Table 3. Land cover in the watershed.
| Land Cover Type | Area in 2000, km² | Area in 2020, km² | Change |
|---|---|---|---|
| Tree cover | 451,000 | 447,000 | 0% |
| Dense short vegetation | 142,000 | 139,000 | -2% |
| Wetland + tree cover | 83,600 | 82,700 | -1% |
| Semi-arid | 24,300 | 24,500 | 0% |
| Open surface water | 7,580 | 8,350 | 10% |
| Built-up | 2,470 | 8,340 | 237% |
| Wetland + dense short vegetation | 4,380 | 4,390 | 0% |
| Cropland | 1,100 | 2,020 | 84% |
Land cover data comes from the GLAD: Global Land Cover and Land Use Change, 2000-2020 (Popatov et al. 2022). This dataset, created by researchers at the University of Maryland, is available online here. Classification is based on satellite imagery from Landsat and machine learning tools.
Land cover change can profoundly influence watershed hydrology and water quality. Urbanization and development can increase the impervious cover, causing more water to run off rather than infiltrate into the ground. This can decrease groundwater recharge and river baseflows, or the flows that occur during dry times. Deforestation and agricultural development are often accompanied by an increase in soil erosion and sediment loads. Other land use types are associated with water pollution. For example, agriculture can increase loads of pesticides and nutrients (nitrogen and phosphorus) from fertilizers. Urbanization and industrialization can cause contamination from a wide range of chemicals used in households and industry.
The average annual precipitation over the watershed is 1,744 mm/year. (Precipitation includes all forms of water, including snow and rain.) Some of this water leaves the watershed surface via evaporation and transpiration, or the loss of water from plants. Annual evapotranspiration is estimated at 1,185 mm/year. The basin climatology, or the monthly average precipitation and evapotranspiration, is shown in Figure 4.
Precipitation data comes from WorldClim, a global gridded dataset by researchers at the University of East Anglia (Harris et al. 2020). This dataset is based on downscaling and bias-correcting the CRU-TS dataset (Fick and Hijmans 2017), which is based on a large collection of station observations that span 1901–2018.
Evapotranspiration is even more difficult to estimate than precipitation. Here, we use a dataset, GLEAM v3.6B, which combines modeling and remote sensing data (Martens et al. 2017; Miralles et al. 2011).
It is difficult to estimate water cycle variables over large areas. So you should keep in mind that these estimates are uncertain (not perfect).
The GRACE satellites provide information about changes in the amount of water over different locations on the Earth. Figure 3 shows the average terrestrial water storage anomaly over the watershed.
The GRACE satellites make highly accurate measurements of the Earth's gravitational field, and provide measurements of changes in the mass of water on a monthly time scale. These measurements do not tell us how much water there is in a region, but rather, how it the amount of water has changed compared to a baseline. The measurement includes all forms of water, including water in rivers, lakes, and reservoirs, soil moisture, groundwater, glaciers, snow, and ice. For an introduction to GRACE, see the section of my PhD thesis on Remote Sensing of the Water Cycle.
The total amount of water in the watershed appears to be trending downwards at a rate of -0.2 cm per decade (P = 0.83). This P-value indicates that the observed trend is not statistically significant. In other words, there is insufficient evidence to conclude that there is a meaningful trend in the data.
GRACE Terrestrial Water Storage Anomaly data is from the Center for Space Research at the University of Texas, Austin (Save et al. 2016, 2022).
The watershed had about 5767.1 km² of land equipped for irrigation in 2005. This is about 0.8% of the watershed. Figure 5 shows the development of irrigated area from 1900 to 2005. These estimates are based on a global dataset published by an international team of researchers (Siebert et al. 2015).
Irrigation brings many benefits for growing crops. In arid regions, it enables production where it would be otherwise impossible. In humid regions, irrigation can increase crop quality and yield, and provide more certainty against unpredictable climate. Yet, the expansion of irrigation can have impacts on watersheds that need to be carefully managed.
Increased irrigation usually requires more water to be withdrawn from rivers, lakes, or groundwater sources, which can reduce streamflow and alter natural flow patterns. This reduced flow can harm aquatic ecosystems and diminish the water available downstream for other uses. Irrigation often introduces fertilizers and pesticides into the watershed, and may increase soil erosion and sediment transport. When nutrients run off into rivers and streams, they can lead to nutrient pollution, algal blooms, and eutrophication. This plus chemical pesticides and herbicides negatively impacts aquatic life and water quality for human uses.
This watershed contains 24 dams identified in the Global Dam Watch database, with a total storage capacity of 2,210 million m³.
Information on these dams is listed in Table 4. The number and size of dams in a watershed is one measure of hydromodification, or how much the natural hydrologic cycle is influenced by human activities.
Table 4. Dams in the watershed. Unknown or missing data shown with a dash.
| Dam Name | Reservoir Name | River | Main Use | Year | Dam Height (m) | Capacity (10⁶ m³) | Latitude | Longitude | URL |
|---|---|---|---|---|---|---|---|---|---|
| – | – | – | – | – | -9.577 | -76.745 | – | ||
| – | – | – | – | – | -12.465 | -74.787 | – | ||
| – | – | – | – | – | -12.484 | -74.745 | – | ||
| – | – | – | – | – | -2.749 | -78.414 | – | ||
| Upamayo | Junin | Lago Junin | – | Built 1936 | 10.0 | 556.0 | -10.979 | -76.196 | link |
| Mazar | – | Paute | Hydroelectricity | Built 2011 | 166.0 | 410.0 | -2.599 | -78.624 | link |
| Chaglla | – | Huallaga | Hydroelectricity | Built 2016 | 202.0 | 375.0 | -9.695 | -75.836 | link |
| Choclococha | – | Pampas | – | Built 1960 | 12.0 | 170.0 | -13.243 | -75.073 | – |
| – | – | – | – | Built before 1985 | 121.0 | -13.352 | -75.086 | – | |
| Daniel Palacios | – | Paute | Hydroelectricity | Built 1982 | 120.0 | -2.592 | -78.566 | link | |
| Sibinacocha | Lake Sibinacocha | Sibinacocha | Hydroelectricity | Built 1996 | 12.0 | 110.0 | -13.901 | -71.006 | link |
| – | – | – | – | – | 75.9 | -11.405 | -76.332 | – | |
| Antacoto | Antacoto | Santa Eulalia | – | Built 1966 | 61.2 | -11.408 | -76.362 | – | |
| – | – | – | – | Built before 1985 | 54.1 | -11.959 | -75.912 | – | |
| – | – | – | – | – | 44.5 | -11.719 | -76.122 | – | |
| Pias I | – | – | Hydroelectricity | – | 39.2 | -7.890 | -77.567 | – | |
| – | – | – | – | – | 26.7 | -11.777 | -76.093 | – | |
| – | – | – | – | Built 2016 | 26.5 | -12.290 | -74.685 | – | |
| – | – | – | – | Built before 1985 | 7.1 | -11.478 | -76.272 | – | |
| – | – | – | – | – | 4.6 | -2.077 | -78.204 | – | |
| – | – | – | – | Built 2006 | 4.1 | -1.193 | -78.827 | – | |
| – | – | – | – | Built 2012 | 1.9 | -1.209 | -78.809 | – | |
| – | – | – | – | – | 1.8 | -7.173 | -78.277 | – | |
| – | – | – | – | – | 1.6 | -1.398 | -78.383 | – |
Dams serve many useful purposes including electric generation, water supply, irrigation, flood control, and recreation. However, if not carefully planned and managed, dams can have a heavy environmental impact. Today, many governments are removing dams to bring rivers back to life.
For a detailed look at the impact of dams on people and the environment, I encourage you to read the book Silenced Rivers by Patrick McCully. To help conserve free-flowing rivers, consider supporting the nonprofit International Rivers.
Data on dams comes from the Global Dam Watch database, published in July 2024. For more details, see the journal article by lead researchers at McGill University (Lehner et al. 2024).
The longest river is the watershed is 2,840 km long. It is shown highlighted in the map in Figure 5 below.
This is the longest continuous flowline in the source dataset, MERIT-Basins. It is not necessarily the mainstem of the river, or the one with the same name. When it comes to naming rivers, historical, legal, and cultural influences are also important.
Figure 6 shows the elevation profile of the longest river reach. Elevations on the plot are in meters above mean sea level. The river begins at 4,180 m, and the outlet is at 86 m.
Elevation data for the profile plot is from MERIT-DEM (Yamazaki et al. 2017). Actual distances on the plot may be underestimated somewhat. This is because river paths are based on a grid or raster data, which simplifies the meandering path of real-world rivers.
Terrain elevations in the watershed range from 93 m to 5,400 m above sea level. The average, or mean, elevation is 1,500 m. Figure 7 shows a distribution of terrain elevations in the watershed.
Elevation data is provided by EarthEnv (Amatulli et al. 2021), and is based on the Global Multi-resolution Terrain Elevation Data 2010 dataset (GMTED2010). Statistics are based on gridded elevation data with pixels that are about 5 km on a side. Because of the size of the pixels, some smoothing takes place, and so the statistics reported above may not capture the true minimum and maximum elevation.
The watershed is home to 222 threatened freshwater species. Table 5 shows the species that are endangered, vulnerable, or near-threatened, based on assessments by the International Union for the Conservation of Nature, or IUCN. Data comes from the IUCN Red List.
For a photo of the species, hover the mouse over Scientific Name in the table, or tap on mobile. Click the link under Status to view the IUCN assessment. Here you can find out more about the reasons the species decline, view maps of the species distribution, and read about any conservation measures being taken.
Table 5. Threatened species in the watershed.
| Type | Scientific Name | Common Name | Status | Presence |
|---|---|---|---|---|
| amphibians | Nymphargus sucre | Sucre’s Glassfrog | Critically Endangered ⧉ | Extant |
| amphibians | Telmatobius vellardi | Vellard’s Water Frog | Critically Endangered ⧉ | Possibly Extinct |
| amphibians | Hyloxalus shuar | Santiago Rocket Frog | Critically Endangered ⧉ | Extant |
| amphibians | Telmatobius cirrhacelis | Loja Water Frog | Critically Endangered ⧉ | Possibly Extinct |
| amphibians | Hyloxalus peculiaris | Funny Rocket Frog | Critically Endangered ⧉ | Possibly Extinct |
| amphibians | Atelopus bomolochos | Azuay Stubfoot Toad | Critically Endangered ⧉ | Extant |
| amphibians | Telmatobius timens | Tojologue Water Frog | Critically Endangered ⧉ | Extant |
| fish | Astroblepus ubidiai | Andean Catfish | Critically Endangered ⧉ | Probably Extant |
| birds | Cinclodes palliatus | White-bellied Cinclodes | Critically Endangered ⧉ | Extant |
| amphibians | Atelopus podocarpus | Unknown | Critically Endangered ⧉ | Possibly Extinct |
| amphibians | Ameerega planipaleae | Oxapampa Poison Frog | Critically Endangered ⧉ | Extant |
| amphibians | Atelopus boulengeri | Boulenger’s Stubfoot Toad | Critically Endangered ⧉ | Possibly Extinct |
| amphibians | Telmatobius mendelsoni | Unknown | Critically Endangered ⧉ | Possibly Extinct |
| plants | Isoetes hewitsonii | Unknown | Critically Endangered ⧉ | Extant |
| amphibians | Rhinella amabilis | Unknown | Critically Endangered ⧉ | Possibly Extinct |
| plants | Isoetes dispora | Unknown | Critically Endangered ⧉ | Extant |
| amphibians | Atelopus nanay | Unknown | Critically Endangered ⧉ | Extant |
| fish | Paratrygon aiereba | Discus Stingray | Critically Endangered ⧉ | Extant |
| fish | Rhamdella montana | bagre | Critically Endangered ⧉ | Extant |
| amphibians | Atelopus patazensis | Unknown | Critically Endangered ⧉ | Possibly Extinct |
| fish | Aposturisoma myriodon | shitari | Critically Endangered ⧉ | Extant |
| amphibians | Atelopus petersi | Unknown | Critically Endangered ⧉ | Possibly Extinct |
| fish | Nannostomus mortenthaleri | red pencil | Critically Endangered ⧉ | Extant |
| amphibians | Atelopus palmatus | Unknown | Critically Endangered ⧉ | Extant |
| amphibians | Hyloscirtus hillisi | Unknown | Critically Endangered ⧉ | Extant |
| fish | Astroblepus formosus | bagre de torrente | Critically Endangered ⧉ | Extant |
| amphibians | Centrolene buckleyi | Buckley’s Glassfrog | Critically Endangered ⧉ | Extant |
| amphibians | Atelopus ignescens | Quito Stubfoot Toad | Critically Endangered ⧉ | Extant |
| amphibians | Atelopus tricolor | Bolivian Stubfoot Toad | Critically Endangered ⧉ | Possibly Extinct |
| amphibians | Atelopus nepiozomus | Gualecenita Stubfoot Toad | Critically Endangered ⧉ | Extant |
| amphibians | Atelopus pachydermus | Schmidt’s Stubfoot Toad | Critically Endangered ⧉ | Possibly Extinct |
| amphibians | Atelopus halihelos | Morona-Santiago Stubfoot Toad | Critically Endangered ⧉ | Possibly Extinct |
| amphibians | Atelopus peruensis | Peru Stubfoot Toad | Critically Endangered ⧉ | Possibly Extinct |
| amphibians | Atelopus pyrodactylus | Unknown | Critically Endangered ⧉ | Extant |
| amphibians | Nannophryne cophotis | Paramo Toad | Critically Endangered ⧉ | Possibly Extinct |
| amphibians | Hyloxalus exasperatus | Yapitya Rocket Frog | Critically Endangered ⧉ | Possibly Extinct |
| amphibians | Hyloxalus anthracinus | South American Rocket Frog | Critically Endangered ⧉ | Extant |
| amphibians | Hyloxalus marmoreoventris | Rio Negro Rocket Frog | Critically Endangered ⧉ | Possibly Extinct |
| amphibians | Colostethus jacobuspetersi | Unknown | Critically Endangered ⧉ | Possibly Extinct |
| amphibians | Atelopus epikeisthos | Unknown | Critically Endangered ⧉ | Extant |
| amphibians | Atelopus erythropus | Carabaya Stubfoot Toad | Critically Endangered ⧉ | Possibly Extinct |
| amphibians | Telmatobius niger | Black Water Frog | Critically Endangered ⧉ | Possibly Extinct |
| amphibians | Pristimantis metabates | Cutin of Chiriaco | Endangered ⧉ | Extant |
| amphibians | Hyloxalus sylvaticus | Forest Rocket Frog | Endangered ⧉ | Extant |
| amphibians | Atelopus seminiferus | Upper Amazon Stubfoot Toad | Endangered ⧉ | Extant |
| amphibians | Ctenophryne aequatorialis | Cuenca Nelson Frog | Endangered ⧉ | Extant |
| amphibians | Nannophryne corynetes | Abra Malaga Toad | Endangered ⧉ | Extant |
| amphibians | Rhinella vellardi | Alto Marañon Toad | Endangered ⧉ | Extant |
| amphibians | Telmatobius brachydactylus | Junín Riparian Frog | Endangered ⧉ | Presence Uncertain |
| amphibians | Gastrotheca cuencana | Unknown | Endangered ⧉ | Extant |
| amphibians | Telmatobius punctatus | Huánaco Water Frog | Endangered ⧉ | Extant |
| amphibians | Hyloxalus maculosus | Spotted Rocket Frog | Endangered ⧉ | Extant |
| amphibians | Nymphargus phenax | Tutumbaro Cochran Frog | Endangered ⧉ | Extant |
| amphibians | Nymphargus lindae | Linda’s Glassfrog | Endangered ⧉ | Extant |
| amphibians | Hyloscirtus tapichalaca | Tapichalaca Treefrog | Endangered ⧉ | Extant |
| amphibians | Gastrotheca turnerorum | Unknown | Endangered ⧉ | Extant |
| amphibians | Hyloscirtus condor | Unknown | Endangered ⧉ | Extant |
| amphibians | Telmatobius ignavus | Piura Water Frog | Endangered ⧉ | Extant |
| amphibians | Centrolene sanchezi | Sanchez’s Giant Glass Frog | Endangered ⧉ | Extant |
| amphibians | Nymphargus chancas | Peru Cochran Frog | Endangered ⧉ | Extant |
| amphibians | Ameerega silverstonei | Silverstone’s Poison Frog | Endangered ⧉ | Extant |
| fish | Chaetostoma loborhynchos | carachama | Endangered ⧉ | Extant |
| amphibians | Ameerega yoshina | Unknown | Endangered ⧉ | Extant |
| amphibians | Telmatobius macrostomus | Lake Junin Frog | Endangered ⧉ | Possibly Extant |
| mammals | Anotomys leander | Ecuadoran Ichthyomyine | Endangered ⧉ | Extant |
| mammals | Inia geoffrensis | Amazon River Dolphin | Endangered ⧉ | Extant |
| fish | Otocinclus cocama | carachamita | Endangered ⧉ | Extant |
| amphibians | Atelopus andinus | Unknown | Endangered ⧉ | Extant |
| amphibians | Atelopus exiguus | Unknown | Endangered ⧉ | Extant |
| mammals | Pteronura brasiliensis | Giant Otter | Endangered ⧉ | Extant |
| mammals | Tapirus pinchaque | Mountain Tapir | Endangered ⧉ | Extant |
| birds | Laterallus tuerosi | Junin Rail | Endangered ⧉ | Extant |
| amphibians | Ranitomeya summersi | Summers’ Poison Frog | Endangered ⧉ | Extant |
| amphibians | Nymphargus pluvialis | Pistipata Cochran Frog | Endangered ⧉ | Extant |
| amphibians | Gastrotheca stictopleura | Unknown | Endangered ⧉ | Extant |
| amphibians | Hyloscirtus pacha | Morona-Santiago Treefrog | Endangered ⧉ | Extant |
| amphibians | Telmatobius latirostris | Cajamarca Water Frog | Endangered ⧉ | Extant |
| amphibians | Hyalinobatrachium anachoretus | Unknown | Endangered ⧉ | Extant |
| amphibians | Centrolene condor | El Cóndor Glass Frog | Endangered ⧉ | Extant |
| birds | Podiceps taczanowskii | Junin Grebe | Endangered ⧉ | Possibly Extinct |
| amphibians | Pristimantis citriogaster | Throated Robber Frog | Endangered ⧉ | Extant |
| amphibians | Hyloxalus mystax | Cloud Forest Rocket Frog | Endangered ⧉ | Extant |
| amphibians | Hyloxalus cevallosi | Palanda Rocket Frog | Endangered ⧉ | Extant |
| amphibians | Callimedusa baltea | Purple-sided Leaf Frog | Endangered ⧉ | Extant |
| amphibians | Nymphargus anomalus | Anomalous Glassfrog | Endangered ⧉ | Extant |
| fish | Panaqolus albivermis | Unknown | Endangered ⧉ | Extant |
| amphibians | Centrolene charapita | Charapita Glass Frog | Endangered ⧉ | Extant |
| fish | Orestias polonorum | andean killfish | Endangered ⧉ | Extant |
| amphibians | Hyloxalus azureiventris | Sky Blue Poison Dart Frog | Endangered ⧉ | Extant |
| amphibians | Gastrotheca yacuri | Unknown | Endangered ⧉ | Extant |
| amphibians | Boana palaestes | Unknown | Endangered ⧉ | Extant |
| fish | Trichomycterus weyrauchi | bagre | Endangered ⧉ | Extant |
| amphibians | Telmatobius marmoratus | Marbled Water Frog | Endangered ⧉ | Extant |
| mammals | Sotalia fluviatilis | Tucuxi | Endangered ⧉ | Extant |
| fish | Chaetostoma daidalmatos | carachama | Endangered ⧉ | Extant |
| amphibians | Atelopus oxapampae | Unknown | Endangered ⧉ | Extant |
| amphibians | Centrolene hesperia | Basecamp Giant Glass Frog | Endangered ⧉ | Extant |
| amphibians | Hyalinobatrachium yaku | Yaku Glassfrog | Endangered ⧉ | Extant |
| fish | Orestias gymnota | Andean Killfish | Endangered ⧉ | Extant |
| amphibians | Ameerega cainarachi | Cainarachi Poison Frog | Endangered ⧉ | Extant |
| fish | Ancistrus marcapatae | carachama | Endangered ⧉ | Extant |
| amphibians | Strabomantis cornutus | Rio Suno Robber Frog | Endangered ⧉ | Extant |
| amphibians | Nymphargus colomai | Coloma’s Glassfrog | Endangered ⧉ | Extant |
| amphibians | Atelopus colomai | Coloma’s Harlequin Toad | Endangered ⧉ | Possibly Extinct |
| fish | Chaetostoma stroumpoulos | carachama | Endangered ⧉ | Extant |
| fish | Chaetostoma changae | Unknown | Endangered ⧉ | Extant |
| amphibians | Ameerega rubriventris | Rana Venenosa | Endangered ⧉ | Extant |
| fish | Trichomycterus taeniops | bagre | Endangered ⧉ | Extant |
| fish | Orestias elegans | Unknown | Endangered ⧉ | Extant |
| amphibians | Rulyrana saxiscandens | Tarapoto Cochran Frog | Endangered ⧉ | Extant |
| amphibians | Telmatobius brevirostris | Shortsnout Water Frog | Endangered ⧉ | Extant |
| amphibians | Nymphargus cariticommatus | Unadorned Glassfrog | Endangered ⧉ | Extant |
| fish | Potamotrygon tigrina | Tiger Freshwater Stingray | Endangered ⧉ | Possibly Extant |
| fish | Chaetostoma branickii | carachama | Vulnerable ⧉ | Probably Extant |
| crabs | Hypolobocera gracilignatha | Unknown | Vulnerable ⧉ | Probably Extant |
| crabs | Moritschus ecuadorensis | Unknown | Vulnerable ⧉ | Probably Extant |
| amphibians | Atelopus pulcher | Peruvian Camouflaged Harlequin | Vulnerable ⧉ | Extant |
| amphibians | Ranitomeya fantastica | Fantastic Poison Frog | Vulnerable ⧉ | Extant |
| mammals | Trichechus inunguis | Amazonian Manatee | Vulnerable ⧉ | Extant |
| crabs | Hypolobocera rathbuni | Unknown | Vulnerable ⧉ | Probably Extant |
| amphibians | Hyloxalus insulatus | Unknown | Vulnerable ⧉ | Extant |
| birds | Phoenicoparrus andinus | Andean Flamingo | Vulnerable ⧉ | Extant |
| fish | Attonitus bounites | Unknown | Vulnerable ⧉ | Extant |
| amphibians | Hyloscirtus torrenticola | El Pepino Treefrog | Vulnerable ⧉ | Extant |
| amphibians | Telmatobius truebae | Trueb’s Water Frog | Vulnerable ⧉ | Extant |
| birds | Calidris fuscicollis | White-rumped Sandpiper | Vulnerable ⧉ | Extant |
| amphibians | Excidobates captivus | Rio Santiago Poison Frog | Vulnerable ⧉ | Extant |
| birds | Limosa haemastica | Hudsonian Godwit | Vulnerable ⧉ | Extant |
| fish | Brachyplatystoma rousseauxii | Gilded Catfish | Vulnerable ⧉ | Extant |
| fish | Sturisoma graffini | Unknown | Vulnerable ⧉ | Extant |
| amphibians | Ameerega pepperi | Unknown | Vulnerable ⧉ | Extant |
| fish | Chaetostoma marmorescens | carachama | Vulnerable ⧉ | Extant |
| fish | Heliotrygon rosai | Rosa’s Round Ray | Vulnerable ⧉ | Extant |
| amphibians | Pristimantis pinchaque | Tapir Robber Frog | Vulnerable ⧉ | Extant |
| plants | Hypericum callacallanum | Unknown | Vulnerable ⧉ | Extant |
| amphibians | Callimedusa ecuatoriana | Agua Rica Leaf Frog | Vulnerable ⧉ | Extant |
| plants | Isoetes saracochensis | Unknown | Vulnerable ⧉ | Extant |
| amphibians | Hyloscirtus diabolus | Unknown | Vulnerable ⧉ | Extant |
| amphibians | Pleurodema marmoratum | Marbled Four-eyed Frog | Vulnerable ⧉ | Extant |
| amphibians | Pristimantis nigrogriseus | Charcoal Robber Frog | Vulnerable ⧉ | Extant |
| amphibians | Telmatobius atahualpai | Amazonas Water Frog | Vulnerable ⧉ | Extant |
| amphibians | Ameerega pongoensis | Unknown | Vulnerable ⧉ | Extant |
| plants | Isoetes parvula | Unknown | Vulnerable ⧉ | Extant |
| amphibians | Ranitomeya benedicta | Blessed Poison Frog | Vulnerable ⧉ | Extant |
| mammals | Sigmodon inopinatus | Unexpected Cotton Rat | Vulnerable ⧉ | Extant |
| plants | Isoetes ecuadoriensis | Unknown | Vulnerable ⧉ | Extant |
| amphibians | Leucostethus fugax | Pastaza Rocket Frog | Vulnerable ⧉ | Extant |
| fish | Astroblepus supramollis | bagre de torrente | Vulnerable ⧉ | Extant |
| mammals | Tapirus terrestris | Lowland Tapir | Vulnerable ⧉ | Extant |
| amphibians | Hyloscirtus psarolaimus | Papallacta Treefrog | Vulnerable ⧉ | Extant |
| fish | Orestias multiporis | Andean Killifish | Vulnerable ⧉ | Extant |
| amphibians | Telmatobius brevipes | Huahachuco Water Frog | Vulnerable ⧉ | Extant |
| amphibians | Allobates fratisenescus | Mera Rocket Frog | Vulnerable ⧉ | Extant |
| amphibians | Hyloxalus vertebralis | Boulenger’s Rocket Frog | Vulnerable ⧉ | Extant |
| amphibians | Gastrotheca riobambae | Riobamba Marsupial Frog | Vulnerable ⧉ | Extant |
| amphibians | Gastrotheca lojana | Rana Marsupial Lojana | Vulnerable ⧉ | Extant |
| amphibians | Gastrotheca lateonota | El Tambo Marsupial Frog | Vulnerable ⧉ | Extant |
| fish | Plesiotrygon iwamae | Antenna Ray | Vulnerable ⧉ | Extant |
| amphibians | Telmatobius peruvianus | Peru Water Frog | Vulnerable ⧉ | Presence Uncertain |
| fish | Tahuantinsuyoa chipi | bujurqui | Vulnerable ⧉ | Extant |
| fish | Orestias munda | Andean Killfish | Vulnerable ⧉ | Extant |
| birds | Pluvialis squatarola | Grey Plover | Vulnerable ⧉ | Extant |
| amphibians | Boana nigra | Black-flanked Treefrog | Vulnerable ⧉ | Extant |
| birds | Limnodromus griseus | Short-billed Dowitcher | Vulnerable ⧉ | Extant |
| birds | Tringa flavipes | Lesser Yellowlegs | Vulnerable ⧉ | Extant |
| amphibians | Ameerega bassleri | Pleasing Poison Frog | Vulnerable ⧉ | Extant |
| fish | Paracetopsis atahualpa | Bagre Ballena | Vulnerable ⧉ | Possibly Extant |
| amphibians | Telmatobius carrillae | Ancash Water Frog | Vulnerable ⧉ | Extant |
| fish | Apistogramma cinilabra | bujurqui | Vulnerable ⧉ | Extant |
| fish | Anablepsoides derhami | pez anual | Near Threatened ⧉ | Extant |
| amphibians | Hyalinobatrachium pellucidum | Rio Azuela Glass Frog | Near Threatened ⧉ | Extant |
| birds | Charadrius vociferus | Killdeer | Near Threatened ⧉ | Extant |
| fish | Corydoras panda | panda | Near Threatened ⧉ | Extant |
| birds | Calidris minutilla | Least Sandpiper | Near Threatened ⧉ | Extant |
| mammals | Lontra longicaudis | Neotropical Otter | Near Threatened ⧉ | Extant |
| fish | Plesiotrygon nana | Dwarf Antenna Ray | Near Threatened ⧉ | Extant |
| fish | Hyphessobrycon ecuadorensis | Sardina de rio | Near Threatened ⧉ | Extant |
| fish | Trichomycterus piurae | Unknown | Near Threatened ⧉ | Possibly Extant |
| fish | Paracetopsis bleekeri | Ciego | Near Threatened ⧉ | Possibly Extant |
| fish | Phenacobrycon henni | Sardinitas | Near Threatened ⧉ | Possibly Extant |
| birds | Arenaria interpres | Ruddy Turnstone | Near Threatened ⧉ | Extant |
| birds | Calidris pusilla | Semipalmated Sandpiper | Near Threatened ⧉ | Extant |
| amphibians | Gastrotheca pseustes | San Lucas Marsupial Frog | Near Threatened ⧉ | Extant |
| reptiles | Micrurus peruvianus | Peru Coral Snake | Near Threatened ⧉ | Extant |
| amphibians | Atelopus loettersi | Unknown | Near Threatened ⧉ | Extant |
| amphibians | Rulyrana mcdiarmidi | McDiarmid’s Glassfrog | Near Threatened ⧉ | Extant |
| fish | Ichthyoelephas humeralis | Chaguingo | Near Threatened ⧉ | Possibly Extant |
| reptiles | Helicops petersi | Spiral Keelback | Near Threatened ⧉ | Extant |
| amphibians | Gastrotheca aguaruna | Unknown | Near Threatened ⧉ | Extant |
| fish | Astroblepus prenadillus | Unknown | Near Threatened ⧉ | Extant |
| birds | Podiceps juninensis | Northern Silvery Grebe | Near Threatened ⧉ | Extant |
| amphibians | Hyloscirtus armatus | Unknown | Near Threatened ⧉ | Extant |
| amphibians | Telmatobius jelskii | Acancocha Water Frog | Near Threatened ⧉ | Extant |
| fish | Pseudocurimata boulengeri | Dica | Near Threatened ⧉ | Possibly Extant |
| birds | Phoenicopterus chilensis | Chilean Flamingo | Near Threatened ⧉ | Extant |
| birds | Calidris canutus | Red Knot | Near Threatened ⧉ | Extant |
| fish | Hemibrycon inambari | mojarita | Near Threatened ⧉ | Extant |
| birds | Tringa melanoleuca | Greater Yellowlegs | Near Threatened ⧉ | Extant |
| fish | Moenkhausia margitae | mojara | Near Threatened ⧉ | Extant |
| amphibians | Pristimantis philipi | Unknown | Near Threatened ⧉ | Extant |
| amphibians | Pristimantis muscosus | Moss Cutin | Near Threatened ⧉ | Possibly Extant |
| birds | Phegornis mitchellii | Diademed Plover | Near Threatened ⧉ | Extant |
| amphibians | Epipedobates anthonyi | Anthony’s Poison-Arrow Frog | Near Threatened ⧉ | Extant |
| fish | Iotabrycon praecox | Cachuelas | Near Threatened ⧉ | Possibly Extant |
| birds | Agamia agami | Agami Heron | Near Threatened ⧉ | Extant |
| birds | Gallinago nobilis | Noble Snipe | Near Threatened ⧉ | Extant |
| fish | Landonia latidens | Sardinitas | Near Threatened ⧉ | Possibly Extant |
| birds | Calidris himantopus | Stilt Sandpiper | Near Threatened ⧉ | Extant |
| amphibians | Boana almendarizae | Almendariz’s Treefrog | Near Threatened ⧉ | Extant |
| fish | Chaetostoma mollinasum | carachama | Near Threatened ⧉ | Extant |
| fish | Colossoma macropomum | Tambaqui | Near Threatened ⧉ | Extant |
| amphibians | Rulyrana spiculata | Cuzco Cochran Frog | Near Threatened ⧉ | Extant |
| fish | Anablepsoides elongatus | pez anual | Near Threatened ⧉ | Extant |
| fish | Orestias empyraeus | andean killifish | Near Threatened ⧉ | Extant |
| birds | Myrmoborus melanurus | Black-tailed Antbird | Near Threatened ⧉ | Extant |
| fish | Brycon posadae | Unknown | Near Threatened ⧉ | Probably Extant |
| fish | Hyphessobrycon ecuadoriensis | Sardinita | Near Threatened ⧉ | Possibly Extant |
| amphibians | Rhinella leptoscelis | Unknown | Near Threatened ⧉ | Extant |
| amphibians | Hyloxalus pulchellus | Espada’s Rocket Frog | Near Threatened ⧉ | Extant |
| birds | Vermivora chrysoptera | Golden-winged Warbler | Near Threatened ⧉ | Extant |
| fish | Pseudocurimata peruana | Dica | Near Threatened ⧉ | Possibly Extant |
| amphibians | Telmatobius arequipensis | Chili Water Frog | Near Threatened ⧉ | Extant |
The presence of endangered species in a watershed provides important information about ecosystem health and biodiversity. Many factors can threaten endangered species within watersheds:
Water management plays an important role in protecting endangered species. This includes maintaining adequate streamflows, protecting riparian zones and wetlands, controlling pollution sources, and preserving habitat connectivity throughout the watershed.
If you're concerned about endangered species in your watershed, there are many ways you can help. Support organizations working on species conservation and habitat protection, or local watershed councils and land trusts in your area. Many watersheds have dedicated conservation groups focused on protecting local rivers, wetlands, and wildlife. Search for [your watershed name] + "conservation," "river keeper," or "watershed association."
You can also take direct action in your community. Participate in river cleanups, plant native vegetation along stream banks, reduce pesticide and fertilizer use, and support land use policies that protect riparian corridors and wetlands.
If you own property near streams or wetlands, consider conservation easements through organizations like the Land Trust Alliance.
Report wildlife sightings to citizen science platforms like iNaturalist or eBird. Your observations can contribute to scientific understanding and conservation planning. Finally, use your voice: contact local officials to support clean water regulations, habitat protection, and sustainable development practices that consider watershed health and wildlife needs.
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