A sustainable water development
concept for the Texas Hill Country – and beyond
Imagine a water management strategy
that would accommodate growth and development without unsustainably pumping
down aquifers or incurring the huge expense and societal disruption to build
reservoirs or transport water from remote supplies to developing areas. Welcome
to the concept of Zero Net Water.
As the name implies, Zero Net Water
is a water management strategy that results in zero demand on our conventional
water supplies – rivers, reservoirs and aquifers. Under the Zero Net Water
development concept, water supply is centered on building-scale rainwater
harvesting, “waste” water management centers on project-scale reclamation and
reuse, and stormwater management employs distributed green infrastructure to
maintain the hydrologic integrity of the site. Together these result in minimal
disruption of flows through a watershed even as water is harvested at the site
scale and used – and reused – to support development.
The key is taking advantage of the
difference in capture and distribution efficiency between a building-scale
rainwater harvesting system and the watershed-scale rainwater harvesting
systems that compose all of our conventional water supplies. The basis for this
is illustrated in the schematics below.
The prevailing conventional water
supply strategy – again, this is watershed-scale rainwater harvesting – is
illustrated in this schematic. Typically only a very minor fraction of the
total rain falling onto the watershed makes it into the “cisterns” of that
rainwater harvesting system – the aquifers and reservoirs. The rest is lost to
evapotranspiration, a “loss” which maintains the ecology of the watershed.
Water that does make it into reservoirs is subject to high losses to
evaporation, up to half of total inflow. So the inherent capture efficiency of
this system is quite low.
Water supply produced from these
watershed-scale “cisterns” is distributed to points of use – where some of the
rain fell to begin with – a process which also suffers significant losses.
Water industry standards recognize a 15% water loss in the distribution system
as “good” performance, and many water systems have much greater losses. So here
too we suffer an inherent inefficiency in turning rainfall into water supply
that is available for human use.
The building-scale rainwater
harvesting concept is illustrated in this schematic. Close to 100% of the rain
falling onto a rooftop can be captured and converted into usable water supply.
There will be some losses to cistern overflows in large storms or when there is
an extended period of wet weather, so the actual efficiency will vary with
weather patterns, but in a system properly sized relative to the water usage
pattern, it will be consistently very high. The building-scale distribution
system is typically – and can practically be – maintained “tight” so there
would be negligible distribution losses.
This high capture and distribution
efficiency allows the water supply to be “grown” in fairly direct proportion to
water demand, one building at a time, thus rendering this a more sustainable
water supply strategy. And because the water supply would be provided, and paid
for, only to serve imminent development, this strategy is also economically
efficient, and thus more fiscally sustainable.
An immediate, practically knee-jerk,
objection to this water supply strategy is that harvesting rainwater off
rooftops would “rob” the watershed of streamflow and/or recharge, and would
thus produce no net gain in the available, usable water supply. As can be
inferred from the illustrations above, this is not the case. When not directly
harvested, a large majority of roof runoff would be abstracted in the
watershed. In any case, when land is developed, the amount of rainfall that
becomes quickflow – water that runs directly off the land – increases, and the
amount that infiltrates is reduced. Because of the other impervious surfaces
besides the rooftops that development adds, the volume of runoff would
typically increase even if building-scale rainwater harvesting were to be
implemented on all the buildings in the development, as noted in the
illustration below.
Indeed, because development
increases runoff, development regulations generally require that steps be taken
to treat and detain this excess runoff. Broadscale practice of building-scale
rainwater harvesting can actually reduce the magnitude of this problem. The net
result in any case is that the post-development runoff volume is typically
greater than the predevelopment runoff volume, thus there would be no “robbing”
of flows into the watershed-scale water supply system, relative to the
pre-development flow regime.
In any case, the water sequestered
in the building-scale cisterns is not removed from the watershed. Its release
back into the hydrologic cycle is simply delayed. Most of this water, once used
in the building, appears as wastewater flow. As reviewed below, and illustrated
in the schematic above, under the Zero Net Water concept this flow would
preferably be used to defray irrigation demands, so doing a better, more
targeted job of maintaining some of the plant life in the watershed. If instead
the wastewater were discharged into streams (after treatment of course), the
result would be to create a more steady flow of this water over time, as
opposed to the “flash” hydrology imparted by direct runoff from the rooftop.
A simple way to encapsulate all this
that we capture and utilize on site much of the additional runoff imparted by
placing impervious surfaces over the land. We do this instead of allowing this
additional runoff to become an increased quickflow that, if not mitigated in
some other way, creates water quality, channel erosion, and flooding problems.
So bottom line, broadscale practice of rainwater harvesting off all the
buildings in a watershed would actually improve the overall yield
from the watershed of water that would be directly usable by humans.
“Right-Sizing”
There is a caveat on the “zero” in
Zero Net Water. The cistern in a building-scale rainwater harvesting system
operates in the same manner as a reservoir in a conventional surface water
supply system – it stores the water for future use. Just like a reservoir, a
building-scale cistern has a “firm yield” that will cover a given water demand
profile. The building-scale cistern is typically sized to cover most
conditions, with imported backup supply added to get through the worst drought
periods.
Considerations of cost efficiency and the sustainability of the backup supply system lead to the concept of “right-sizing” of the building-scale rainwater harvesting system. This is the combination of roofprint and cistern volume relative to the expected water usage profile that would result in only limited backup supply requirements, needed only during the worst drought periods.
Considerations of cost efficiency and the sustainability of the backup supply system lead to the concept of “right-sizing” of the building-scale rainwater harvesting system. This is the combination of roofprint and cistern volume relative to the expected water usage profile that would result in only limited backup supply requirements, needed only during the worst drought periods.
The backup supply would of course be
drawn from the conventional water supply systems, from aquifers and/or
reservoirs. So there would be some small draw of water from the watershed-scale
system to get the building-scale rainwater harvesting systems through the
droughts. The magnitude would depend on how well the building-scale systems
were “right-sized” and on whether the users of those systems practiced
“sufficient” conservation, and also of course on the happenstance of the
rainfall patterns over the area. Still, modeling indicates that the vast
majority of the water supply for these buildings would be provided by direct
capture of the rainfall onto the building’s roofprint.
The “right-sized” facilities vary
around the state, depending on the area’s climate. In the Texas Hill Country, a
4-person household which is “reasonably” conservative with their water use
typically requires a roofprint of 4,500 sq. ft. and a cistern volume of 35,000
gallons. These sizes could be decreased if the users practice very good water
conservation. Most cost efficiently incorporating “extra” roofprint, and
perhaps integrating the cistern into the building envelope, are the province of
building design concepts. It is suggested that efforts be made to formulate a
“Hill Country rainwater harvesting vernacular” house design concept to address
those matters. This needs to be taken up by architecture schools, working
architects and homebuilders.
Wastewater Reuse
That “right-sized” system noted
above will only cover interior water use. To supply landscape irrigation
directly from the cistern would require either a significantly larger system or
would incur significantly greater backup supplies. However, there is a flow of
water right there, water that has already been provided for use in the house –
the wastewater flow out of the house. This flow can be treated and dispersed in
a subsurface drip irrigation field to defray landscape irrigation demands.
Modeling shows that doing this, a sizable area of irrigated landscaping can be
maintained without having to either upsize the cistern and
roofprint or incur much greater backup supplies.
This strategy was reviewed in “Slashing
pollution, saving water – the classic win-win (but ignored by society)”.
As set forth there, this sort of reuse system has been implemented on the site
scale for over two decades, and doing so will provide superior environmental
protection, particularly in sensitive watersheds. It is a small step to do this
same process on a project scale, if the nature of the development requires that
it employ a collective wastewater system, rather than an individual on-site
system for each house. That project-scale reclamation and reuse concept must be
part and parcel of the Zero Net Water concept if irrigated landscaping is to be
supported.
Stormwater Management
As noted previously, development
causes an increase in quickflow runoff at the expense of infiltration due to
some of the ground area having been covered with impervious surfaces. These
impervious surfaces also increase levels of pollution entrained in the runoff.
So development regulations typically require that methods be implemented to
blunt both the pollution and the impacts of the additional runoff on downstream
flooding and on channel erosion. The building-scale rainwater harvesting
systems can help to blunt all these impacts by sequestering roof runoff in the
cisterns.
Runoff from the rest of the
development and any cistern overflows can, and should, be addressed using
distributed low-impact development (LID) practices, focusing on intercepting
and infiltrating an initial depth of runoff deemed to have entrained most of
the pollution. The aim of the LID strategy is to restore the rainfall-runoff
response of the developed site as close as practical to that of the
pre-development site. This matching of runoff to pre-development conditions
would maintain the hydrologic integrity of the site, and by a multiplicity of
sites so treated, would maintain the hydrologic integrity of the watershed.
This whole area of “green” stormwater management is the subject of a future
entry on this blog. Suffice it here to note that it is an important element of
Zero Net Water, as it holds more water on the land and thus blunts the
“desertification” of the site that development typically imparts.
Confirmation – and Challenges
Modeling indicates that for all
locations in and around the Hill Country, “right-sized” rainwater harvesting
systems would not have required any backup supplies after the severe drought of
2010-2011 broke in late 2011, even though the general impression is that
drought has persisted in this region. One indicator of this is that water
levels in Lake Travis and Lake Buchanan remain very low. Indeed, it is reported
that inflow to the lakes in 2012 was the 6th lowest year on record
and in 2013 it was the 2nd lowest, above only the extreme drought
year of 2011. It is noted that this occurred despite total annual rainfalls
over the drainage basins flowing into the lakes having been generally around
the long-term average rainfalls there over those two years.
This is simply a confirmation that
the capture efficiency of the building-scale rainwater harvesting system is
inherently much higher than that of the watershed-scale system. The low inflows
to the lakes are a happenstance of rainfall patterns, failing to create the
large runoff events needed to significantly raise lake levels. But those same
rainfall patterns would result in high capture efficiency off of
a rooftop, and so the building-scale systems would not be under the same stress
that persists in the watershed-scale system.
Despite the overall efficiency of the
building-scale rainwater harvesting system, the Zero Net Water development
concept faces challenges to becoming commonly practiced. The building design
issues were noted above. The large roofprint required to “right-size” systems
in Central Texas would require “right-sized” lots to accommodate it. And
two-story houses would clearly be problematic under this concept. Multi-family
housing, as presently configured, would also be hard pressed to provide
roofprint commensurate with water demand. Then too storage cisterns would take up space, unless they were integrated into the building envelope. All that would have implications for development style, and so would require some tinkering with prevailing development models.
roofprint commensurate with water demand. Then too storage cisterns would take up space, unless they were integrated into the building envelope. All that would have implications for development style, and so would require some tinkering with prevailing development models.
On the other hand, with a typical
occupancy of only 2 persons, water demand in seniors-oriented developments –
which may be a considerable portion of new development in Central Texas – would
be supported by the roofprint typically provided by a one-story house plus
garage. Many commercial and institutional buildings would also have a favorable
relationship of roofprint to water use in the building. Indeed, as asserted in “First
‘Logue in the Water”, these would be prime candidates for a Zero Net
Water strategy. Employing some combination of building-scale rainwater
harvesting, condensate capture, and project-scale wastewater reclamation and
reuse, those types of buildings would draw no water from the watershed-scale
systems. That would relieve a significant portion of demand due to growth, and
as a bonus would also blunt stormwater impacts in those sorts of projects,
which typically entail high impervious cover, the roofprint being a significant
portion of it.
Cost is, of course, a primary
consideration, for society at large as well as development principals. Where
there is already a conventional water system nearby which has capacity to
provide service to the development, the cost of the building-scale systems
could not be justified relative to installing conventional distribution
infrastructure. Wherever capacity is a problem, however, then the real cost of
increasing capacity has to be figured in. Where those costs are very large –
e.g., building a new reservoir or tapping a remote aquifer and building
pipelines to deliver water from those to growth areas – then building-scale
facility costs may be globally competitive. And as noted previously,
building-scale facilities require money to be spent only to support buildings
as they are built, while those area-wide strategies require huge investments up
front of being able to sell the first lot, so the Zero Net Water concept is
inherently economically efficient.
We must indeed consider costs
globally, not just the immediately apparent costs of continuing with “business
as usual”. This comes starkly into play in the Hill Country, where aquifers are
under stress even at current usage rates, and serving considerable new
development out of them will only “mine” them further. The drawdown created is
drying up springs that historically flowed all throughout the Hill Country.
That creates a cost to the local ecology, and will fundamentally alter the
character of the region. The impact of this degradation was encapsulated in the
title of an article appearing in the Texas Observer a couple years ago,
“The End of the Hill Country”. This is not to mention reducing water
availability from the rivers flowing out of the Hill Country, water which is
depended upon for both water supply and ecological services all the way to the
Gulf of Mexico. Thus the Zero Net Water development concept may be particularly
valuable in the Hill Country.
While the Zero Net Water development
concept faces fiscal and institutional challenges, the prospects for
sustainably accommodating growth in a globally more cost efficient manner urge
its consideration as a water management strategy for new development over much
of Texas. Particularly in areas like the Hill Country, where aquifers are under
stress and the only other option is a long distance “California style” water
transfer from remote aquifers or reservoirs, which may entail both fiscal and
ecological sustainability issues. The Zero Net Water concept offers a pathway
toward sustainable water even where high growth rates are forecast. It remains
only to address the challenges and to put it into practice.
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