Availability and quality |
Impacts |
-
-
Water scarcity: almost 65% of the population has access to less than 1,000 m3/inhabitant/year of water (Fig. 2) [83].
-
-
Discharge volumes in the Maipo Basin (the principal supplier of potable water for the Santiago metropolitan area) are estimated to decrease by up to 40% in the future [84].
-
-
Droughts impact water quality [85,86].
-
-
High turbidity events impact the operation of the drinking water supply systems [86,87].
-
-
High concentrations of metals and metalloids in rivers of northern-central zones [88] and groundwaters [21].
|
Causes |
-
-
Climate change: lack of precipitation and drought [89].
-
-
Intensive use of water by mining and agriculture activities [90].
-
-
Climate change: warm storms in the Maipo River [91] causing high turbidity events.
-
-
Geogenic metal enrichments in addition to anthropogenic activities in the northern and central zones of Chile [92].
|
Current plans for action |
-
-
National Strategic Plan for Disaster Risk Reduction in the Water Sector 2020–2030 [93].
-
-
Framework law of climate change: establish water balance and projections, information on quantity, quality, infrastructure, and institutions that intervene in the decision-making process regarding water resources and propose a set of actions to safeguard water security [37].
-
-
Construction of reservoirs to increase the autonomy of water production systems and reduce the impact of turbidity events [94].
-
-
Expansion of the monitoring network, promotion of scientific research, and early warning systems [94].
-
-
More comprehensive surveillance programs for ambient water quality standards [21].
-
-
Establishment of regulations and standards for the collection, reuse, and disposal of greywater [95].
|
Distribution and consumption of drinking water |
Impacts |
-
-
Total urban water production increased by 40% between 1999 and 2020, up to 1,787 million m3 per year (Fig. 3) [86,96].
-
-
There is a national average of 33.4% of non-revenue water in 2020 [86].
-
-
Water leakages in the distribution system are estimated to account for 74% of non-revenue water [97].
-
-
Access to drinking water, sewage, and wastewater treatment in urban areas in 2020 reached 99.9%, 97.3%, and 97.3% [86].
-
-
Water consumption per capita in Chile: 17.4 m3/client/month in 2020 (i.e. approximately 161 L/day/person) (Fig. 3) [86].
|
Causes |
-
-
Urban population growth [98].
-
-
Inefficient water markets due to lack of complete information, poorly flexible distribution systems, high transaction costs [99], and fragmented governance of water resources [100].
|
Current plans for action |
-
-
Water leakage control strategies: pressure management [101], night flow analysis in individual District Metering Areas (DMAs) [102].
-
-
Incorporate network monitoring systems and increase the replacement of obsolete infrastructure [103].
|
Wastewater treatment |
Impacts |
-
-
Alteration of marine ecosystem functioning: effects on the biochemical composition of sediments, production of organic enrichments, which later degradation lead to lower oxygen concentrations and hypoxia [104].
-
-
Pharmaceuticals and personal care products found in effluents from wastewater treatment plants involve endocrine disruption effects on freshwater fish [105].
-
-
Highly energy-intensive activated sludge technology with important volumes of sewage sludge [106,107].
|
Causes |
-
-
Excessive discharge of nutrients (nitrogen and phosphorus) to water bodies [21].
-
-
Marine outfalls collect 11% of wastewaters: 33 of the 301 treatment systems include neither biological nor chemical processes [86].
-
-
Tertiary treatment is not performed for nutrient removal in wastewater treatment plants [21].
-
-
The lack of secondary environmental standards (i.e. regulating ambient pollutant concentration) in Chilean water bodies, similar to Total Maximum Daily Loads (TMDL) [108].
-
-
Plants are not designed to remove pollutants such as pharmaceuticals and personal care products [105].
-
-
Use of energy-intensive technology in various stages of the treatment process [109,110], in an urban water cycle not optimized in terms of energy efficiency [111].
|
Current plans for action |
-
-
Development of secondary environmental standards: Five of the 101 watersheds have secondary environmental standards [112].
-
-
Modification of the Supreme Decree Nº90 standards for liquid waste discharges into marine and continental surface waters [113].
-
-
Define watershed-specific ambient water quality standards and more stringent discharge standards for treated wastewaters [21].
|
Stormwater management |
Impacts |
-
-
Large stormwater volumes and discharges cause urban flooding and fluvial ecosystem deterioration [114,115].
-
-
Degradation of the quality of water bodies receiving stormwaters [116].
|
Causes |
-
-
The replacement of the vegetation cover with impervious surfaces [117].
-
-
The occupation and poor management of floodplains [118].
-
-
Urban areas as nonpoint sources of metals, oxygen-demanding substances, and suspended solids transported in stormwaters [116].
|
Current plans for action |
-
-
The urban drainage manual provides planning strategies, designing tools, and standards for stormwater control (i.e. conveyance, infiltration, and storage) [119].
-
-
The sustainable urban drainage guide for southern Chile provides information about natural drainage systems, including green infrastructures, the national regulatory framework, and planning strategies for their implementation [120].
|