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Table of Contents
Introduction
Acknowledgements
Executive
Summary
Local
Context
Ecological
Wastewater Overview
Ecological
Treatment in Cantarrana
Concept
Plan
Appendices
Bibliography
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Overview of Ecological Wastewater Treatment
Ecological wastewater systems
can be a feasible and effective option for Havana, particularly in the
neighborhood of Cantarrana. Like conventional, centralized treatment
facilities, ecological systems can help reduce the level of Biological
Oxygen Demand (BOD) and disease-causing
organisms in water bodies.
| However,
unlike conventional systems, ecological alternatives can provide
much needed recreational space for the neighborhood, become a source
of fertilizer, income, and even food for the neighborhood, it can
create a focus for general river cleanup, and it can train people
to be more aware of water quality issues and more capable of solving
them. The system may also provide educational opportunities for
local schools and institutions. Furthermore, the overall capital
and maintenance costs for ecological systems are substantially lower
than conventional systems in that they require less resources for
construction and often no chemicals and energy for operation. |

Conventional Wastewater Treatment System
Click for larger image
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| The lack
of existing infrastructure in Cantarrana actually makes developing
an alternative treatment system more cost-efficient than if such
a system were to be developed in neighborhoods with existing treatment
systems. |
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Benefits of Alternative Wastewater Treatment
Systems
If properly treated,
household wastewater is a valuable resource for nutrients used
in common fertilizers for horticulture, agriculture and forestry.
A conventional centralized treatment plant, in which non-renewable
nutrients are wasted, will not sustain the nutrition requirements
of a growing global population. (Niemczynowicz)
Conventional
wastewater treatment relies on large scale plants It is the preferred
form of wastewater treatment in developed countries to a large
extent because it is a well-known technology in which civil engineers
throughout the world are trained. It also minimizes the area required
for treatment per capita, which is an important consideration
in urban areas where space is at a premium. Conventional treatment
also shortens the period that the wastewater effluent remains
in retention ponds and so can treat more effluent over a period
of time. However, some of the disadvantages are shown at right
Ecological alternatives
to wastewater treatment are newer technologies, often unknown
and resisted by the engineering and public works communities.
Their land requirements are greater than conventional plants and
therefore are widely perceived as not applicable in urban areas
where land is scarce. However, where feasible, ecological alternatives
provide the advantages shown in the box to the right.

Generalized diagram of alternative wastewater treatment. Click
to enlarge.
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Disadvantages
of Conventional Treatment
- Retrofit or replacement
of piping is labor and resource intensive.
- No alternatives
in the event of a disaster.
- Is not easily adaptable
to new technologies or to varying scales.
- Does not promote
water conservation.
- Intensive use of
chemicals in the treatment process.
- Recycling of nutrients
and reuse of water is not optimized.
- Water quality benefits
are inconclusive.
- High capital and
maintenance cost for plants and supporting infrastructure.
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Advantages
of Ecological Alternatives
- Reclamation of
nutrients
- May be built on
any scale
- Flexible and adaptable
to a variety of sites
- Are more "transparent"
- Provide useable
open space for recreation or wildlife habitat
- Low capital and
maintenance costs
- Little or no chemical
use
- Decentralized locations
- Educational value
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Ecological
Wastewater Treatment Options Examined
The study team examined
two major system types most closely for applications in Cantarrana:
constructed wetlands (both surface and subsurface flow systems)
and aquaculture systems. An overview
of basic characteristics of each system follows. It is important
to bear in mind that alternative wastewater treatment systems
are quite flexible, and any system that the community eventually
develops may use a combination of components from any of the major
system types. In addition, other wastewater treatment strategies,
such as source separation of greyawaters, blackwaters, and urban
runoff can further increase the efficiency and effectiveness of
such a system.
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| Many sites
in the United States utilize ecological wastewater alternatives
in lieu of a centralized treatment system, and overall costs compare
favorably to the conventional systems. One study compared the capital
costs of four ecological systems (Cannon Beach, Oregon, Gustine,
California; Incline Village, Nevada; and Orlando, Florida) to the
typical construction costs of conventional systems, leading to the
findings in Table 1. |
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Type
of System
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Cost
range (1997)
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Ecological
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$170 to $410
per m3/day
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Traditional
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$800 to $1,000
per m3/day
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| m3/day
= cubic meters treated per day |
| Table
1: Cost comparison |
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Constructed
Wetlands
"Wetlands are
land where the water surface is at or above the ground surface
for a long enough time each year to maintain saturated soil conditions
and the growth of related vegetation."*
There are three major types of constructed wetlands that mimic
these natural systems, freewater surface (FWS), horizontal subsurface
flow (HSF), and vertical flow (VF) systems. These systems consist
of a series of connected ponds or reed beds through which the
wastewater flows. All constructed wetlands contain an impermeable
basin that prevents wastewater from infiltrating and potentially
contaminating groundwater. Aquatic plants are introduced within
constructed wetland systems that are capable of thriving in saturated,
nutrient-rich conditions. Because constructed wetlands mimic natural
native systems, there is often a level of increasing native species
diversity as the system progresses and nutrient and organic compound
levels decrease.
Constructed wetlands
can be especially appropriate in developing countries. Their enormous
versatility suits them to a wide range of size and function requirements:
flow systems can be open (FWS) horizontal (HSF), vertical (VF)
or any combination of the three.
Enhancing this flexibility
is the variety of emergent rooted and floating aquatic plants
that system designers can include. A tropical climate is an especially
good environment for constructed wetlands due to the warmer temperatures
that increase biological activity and removal efficiency. Other
major benefits of constructed wetlands are that they can provide
both wildlife habitat and, in the later stages of the process,
open or recreational space.
Constructed wetlands
also require more land than conventional systems, but the use
of land is less intensive. Proper design and maintenance will
ensure a successful system. Therefore potential limitations must
also be considered. Without contained separation of solids and
up-front filtering, odor will at times be significant. Relative
to conventional treatment, constructed wetlands have low maintenance
requirements. However, managers must remove sediments and harvest
plants every 15-20 years.*
Harvest and replanting depends on the ability of the system to
absorb phosphorous, which depends on the loading rate of the influent.
Nutrient recycling with constructed wetlands is among the lowest
among ecological treatment systems. Constructed wetlands also
require more land than conventional systems, but the use of land
is less intensive. Proper design and maintenance will ensure a
successful system. Therefore potential limitations must also be
considered. Without contained separation of solids and up-front
filtering, odor will at times be significant. Relative to conventional
treatment, constructed wetlands have low maintenance requirements.
However, managers must remove sediments.
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Freewater
Surface Systems
A Freewater Surface
System (FWS) contains open water ponds, using settling as the
major treatment mechanism. In addition to settling, flow between
wetland plants and percolation into the upper part of the root
zone provide a more passive type of filtration than a HSF or VF
system. FWS are often densely vegetated with floating or rooted
emergent plants that grow at a water depth of 40 centimeters.*
Horizontal
Subsurface (HSF) and Vertical Flow (VF) Systems
In a HSF or VF system,
wastewater flows below the surface within a porous, planted substrate,
using filtering as the primary treatment technique. Filtration
systems can be designed in a variety of shapes using a variety
of mediums. Substrates suitable for filtration include sand, gravel,
LECA, or a mixture. Plants grow in this saturated substrate and
the wastewater filters through the root zone. The planted root-zone
acts as a biofilter, trapping suspended solids, organic matter,
nutrients, and pollutants.
The benefit of a HSF
or VF system over a FWS is a shorter retention time and higher
removal efficiency. However, often the filtering substrate within
a HSF or VF system needs more rapid replacement. For these reasons,
phases 1-3 of the recommended system for Cantarrana combines FWS
with HSF, in order to exploit the benefits of each system type.
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Free Surface Flow Wetland
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Conveyance Channel with gravel filtration dam
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Artistic
constructed wetland near residences
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Aquaculture
Aquaculture is one
of the oldest techniques used for wastewater treatment. The natural
process of an aquatic food chain breaks down organic material.
Systems range from indoor and outdoor, containerized mesocosms
to large wastewater-fed aquaculture ponds used for fish production
in developing countries. Depending on the climatic conditions,
systems can contain smaller plant and animal organisms such as
microscopic bacteria, zooplankton, and phytoplankton and larger
species such as snails, water hyacinths, pistia, carp, tilapia
and a variety of other plants and animals.
Usually solids, fats
and feces are separated mechanically or through settling. Liquid
with suspended solids may go directly into the system, or undergo
pre-treatment before entering the constructed food chain. Systems
sometimes use anaerobic treatment to further degrade organic compounds
and precipitate metal sulfides into ores. Although not necessary,
these initial stages and techniques can insure the protection
of organisms within the food chain. The use of these up-front
techniques depends on the quality of the influent, desired effluent
quality and the economic situation of the community.
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Aquaculture systems
can provide many benefits. Compared to conventional and constructed
wetland systems, aquaculture has many opportunities for more efficient
nutrient recycling. In addition to the use of effluent for fertilizer,
communities may use harvested plants to feed livestock, compost
them for fertilizer, or use them in combination with sludge to
produce biogas. Today, systems throughout China and India raise
fish as a source of protein. *
Such systems are also valuable sources for all levels of teaching
and research within biological sciences or engineering. In tropical
climates, costs are less, as systems are more productive in year-round
warm outdoor environments.
Despite the many benefits,
aquaculture systems do have some limitations. Generally, aquaculture
systems are more expensive than wetlands or filtration systems,
and have longer retention times. They are also more delicate,
due to the presence of aquatic micro and macro organisms. There
is the risk of wastewater contamination by other substances or
user negligence, which can make maintenance and operation more
of a challenge.
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Alternative Systems in Havana
Infrastructure planners
and community leaders must consider the appropriateness of applying
ecological wastewater treatment techniques to the neighborhoods
of Havana within the context of the larger regional development
plans. Currently there are plans to increase the operational capacity
of the existing María del Carmen treatment plant and to
construct one new plant at Puentes Grandes and one in the Luyanó
River Basin. The plant on the Bay will only serve parts of the
city which already have existing sewerage. The Puentes Grandes
facility is still in the design phase and may not be completed
for many years, if at all.
In certain areas of
the city, where there is sufficient infrastructure and available
financing, a central treatment plant may be the best option. However,
for the parts of Havana such as Cantarrana that
have no sewer lines, it is more feasible to develop decentralized
systems constructed with minimal outside funding, using local
materials, and providing additional benefits to the local population.
An ecological treatment
system may be constructed in phases, at lower capital and operating
costs than conventional systems. An ecological system can also
take advantage of underutilized open space in Cantarrana and convert
it to trails, parks, agriculture or wildlife habitat in conjunction
with the treatment system. Residents indicated in interviews and
in the community meeting that open space was lacking in their
neighborhood, and meeting participants prioritized a system that
would generate useable open space connected to the community.
In addition to treating
wastewater, the proposed plant will allow for production of potentially
valuable byproducts such as fertilizer, biogas and water for irrigation.
With the potential decommissioning of the two factories in the
neighborhood, there may be job shortages within the community
which could be mitigated in part with the construction and maintenance
of an ecological system, but also through the creation of new
employment opportunities that utilize the products generated from
effluent.
The river itself lends
another argument for decentralization of wastewater treatment.
Since the Almendares and its tributaries carry such high quantities
of wastewater, there is some speculation that piping all of the
waste to a central plant will dewater the riverbed completely.
The Ejercito Rebelde reservoir must maintain certain volumes to
recharge the aquifer that supplies Havanas drinking water.
If centralized treatment projects were to divert substantial quantities
of wastewater from its current course in the Almendares basin,
it is unlikely that the dam would be able to increase its discharge
rate to replace the volume lost.
Currently, ecological
wastewater treatment is relatively unknown in Havana, though several
Cuban engineers are investigating the use of constructed wetlands.
Dr. Celia Rodríguez of the Center for Hydrologic Studies
at the Instituto Superior Politécnico José A. Echevarría
(ISPJAE) has identified tropical parameters for the application
of the various ecological wastewater treatment systems in Cuba.
Dr. Rodríguez and Yociel Marrero have constructed demonstration
wetlands at IPSJAE in Havana, and the PMH is in the process of
building a constructed wetland system in the neighborhood of Pogolotti,
south of Cantarrana. This wetland, when completed, will provide
treatment for 500 people at a total cost of around $18,000 U.S.
The Canadian International Development Agency (CIDA) contributed
$10,000 for construction and local microbrigadas provided the
labor. Construction on the wetland has been halted until the remainder
of the funding becomes available.
Although these projects
have demonstrated the viability of these ecological wastewater
options in Cuba, more working examples of these technologies are
necessary. Systems in Cantarrana and Pogolotti can educate and
convince Cuban decision-makers and technical experts about the
their feasibility. Developing these low-cost systems will visibly
improve the quality of life in poor neighborhoods such as Cantarrana,
and serve as models that can be replicated in other parts of Cuba,
as well as in other developing countries.
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