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. 2023 Jul 12;9(7):e18191. doi: 10.1016/j.heliyon.2023.e18191

Table 2.

Urban water cycle.

Availability and quality Impacts
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    Water scarcity: almost 65% of the population has access to less than 1,000 m3/inhabitant/year of water (Fig. 2) [83].

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    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].

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    Droughts impact water quality [85,86].

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    High turbidity events impact the operation of the drinking water supply systems [86,87].

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    High concentrations of metals and metalloids in rivers of northern-central zones [88] and groundwaters [21].

Causes
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    Climate change: lack of precipitation and drought [89].

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    Intensive use of water by mining and agriculture activities [90].

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    Climate change: warm storms in the Maipo River [91] causing high turbidity events.

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    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].

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    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].

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    Construction of reservoirs to increase the autonomy of water production systems and reduce the impact of turbidity events [94].

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    Expansion of the monitoring network, promotion of scientific research, and early warning systems [94].

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    More comprehensive surveillance programs for ambient water quality standards [21].

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    Establishment of regulations and standards for the collection, reuse, and disposal of greywater [95].

Distribution and consumption of drinking water Impacts
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    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].

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    Marine outfalls collect 11% of wastewaters: 33 of the 301 treatment systems include neither biological nor chemical processes [86].

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    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].

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    Plants are not designed to remove pollutants such as pharmaceuticals and personal care products [105].

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    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].

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    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].

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    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].