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Laboratory water systems: Cost-effective generation and distribution
Part
2: System design and operations
By
Norman H. Toussaint, PE, and Lauren M. Goodfellow
This two-part article outlines the challenges and some solutions
for designing a robust yet cost-effective lab water system. The
first installment, published last month, discussed quality requirements
and demand calculation; the second installment, below, reviews specific
design choices, equipment, and operational issues.
Central vs. local systems After determining required system
capacity, the next step is determining the approach to generation
and distribution. Two different approaches are available for generating
high-purity water:
Installation of a central system supplying to all areas.
Installation of a local system at each point of use. Each
approach offers technical and financial advantages and disadvantages.
Centralized systems, where installed, are often sized to meet the
demands of multiple uses, including non-laboratory uses such as
boiler feedwater or closed-loop mechanical system makeup, in addition
to laboratory uses. Product capacities can vary from tens to hundreds
of gal/min (gpm). A central system is typically most cost-effective
if the total facility laboratory water demand is constant, or if
there is a continuous need for treated water for other applications.
A central system also simplifies operation and maintenance with
only one system to manage.
Local systems (in-lab point of use systems) are available from a
variety of water treatment system vendors in a range of capacities.
Although typically sized for one laboratory or one application,
they can provide up to 1 gpm product water capacity. Depending on
the treatment methods employed, these systems are capable of producing
very high-purity water.
One advantage of a localized system is a customized quality specification
for low-volume demand. For example, if a laboratory facility has
only 10% wet labs, a local system costing $5,000 to $8,000/gpm can
be a very cost-effective way to meet pure water demand when compared
to $25,000 to $40,000/gpm for a centralized system. On the down
side, dispersal of equipment can increase maintenance complexity,
resulting in additional labor costs.
A combination of central and local systems can be a cost-effective
solution in cases where the demand for ultra-high-purity water is
limited and variable, but when there is a sufficient constant demand
for a lower-grade water. The local system can work as a “step-up”
unit focusing on certain contaminants and providing quality delivery.
Treatment equipment The selection of equipment, whether
central or point-of-use, depends on the water quality objectives
(e.g., removal of trace minerals or metals, or removal of organic
and microbial materials), and to a lesser extent, on the quality
of the incoming water supply.
Treatment systems are conventionally broken down in two groups:
pre-treatment (or makeup) and polishing systems. Pre-treatment systems
are designed to remove the bulk of suspended, dissolved, and organic
contaminants, providing feedwater suitable for makeup to a variety
of facility systems, scientific equipment cooling, or feed to additional
pre-treatments or polishing systems. Without pre-treatment, the
equipment used to produce high-purity water could see significant
contaminant loads, resulting in lower efficiency and higher operating
costs.
Pre-treatment systems typically include one or more of the following
steps:
Filtration.
Activated carbon.
Reverse osmosis.
Continuous ion exchange (electrodeionization).
Depending on inlet water quality and the performance of RO or EDI
equipment selected, product water from pre-treatment systems can
meet ASTM Type II “Reagent Grade” water standards without further
processing.
Fig. 1. Typical makeup/polishing system components. All figures: HDR Architecture.Click
to enlarge. |
Polishing
systems are designed to further process the pre-treated water to
meet the final water quality objectives. Depending on these objectives,
the technology can include:
Distillation.
Mixed bed ion exchange.
Ultra- or nano-filtration.
UV oxidation.
Sub-micron filtration.
An example of a makeup and polishing system is illustrated in Fig.
1 (above, left).
It is important to recognize that achieving one water treatment
objective may have negative impacts on another. For instance, ion
exchange resins selected to remove dissolved minerals and achieve
high resistivity values can contribute to elevated levels of organics
and bacteria. Treatment system components must be sequenced to progressively
reduce undesirable contaminants without introducing new ones into
the product stream.
Typical sizing criteria for treatment equipment (such as RO systems
and deionized water units) are well-established, and are beyond
the scope of this discussion. It is worth repeating that pre-treatment
or makeup systems may supply building uses other than laboratory
water, e.g., makeup to closed-loop systems or humidification systems,
and these demands need to be included in any preliminary estimates.
System sizes (and the supporting infrastructure) also need to consider
adequate capacity for backwash and rinsing operations, chemical
dilution, and so on.
Local or in-lab systems typically combine pre-treatment and polishing
steps in one or more treatment modules. They are available as on-demand
units or with storage capability. These systems can be fed from
the building potable water supply or from a pre-treated source (central
water softener or pre-treatment system); pre-treating the local
treatment system supply usually results in a longer service life
and can also improve treatment system performance. While most, if
not all, water quality objectives can be accomplished using local
treatment units, the fact that the system can be idle when there
is no demand may lead to problems with bacteriological contamination;
this needs to be carefully reviewed with the users.
Storage and distribution of laboratory water The primary considerations
in design of laboratory water distribution systems are straightforward:
The system must meet the average and peak demands from all users
while delivering water that meets the required quality criteria.
From an engineering perspective, this means selecting and sizing
piping systems to maintain velocity criteria and avoid stagnant
flows and dead legs, while providing sufficient flexibility to allow
for laboratory renovations or expansions. In a complex laboratory
facility, however, this is not always a simple exercise.
Most laboratory water systems, even point-of-use systems, include
provision for storage of product water. Providing storage allows
makeup systems to be right-sized to take advantage of water production
during off-peak hours. For central plant storage, the capacity should
be carefully determined so that all demands can be satisfied without
providing unnecessary volume, which increases vessel cost and required
space. It should also be noted that storage of high-purity water
requires particular attention to storage vessel construction materials
and venting or nitrogen blanketing provisions, to minimize the re-contamination
of the water due to infiltration or contamination imparted from
the interior vessel surface.
Fig. 2. Distribution loop configurations.Click
to enlarge. |
There
are a number of ways to route laboratory water system piping from
the point of generation to the point of use. To maintain water quality,
the distribution loop should be as short as possible and sized to
maintain proper flow conditions at normal and peak demands (typically,
5- to 9-ft/sec in supply piping with minimum 3 ft. per second in
the return flow). This is also the most cost-effective approach.
The ultimate configuration depends on the layout of laboratories
in the building, including the stack configuration in the case of
multi-floor facilities. If water quality is critical to laboratory
operation, the water distribution piping concepts should be provided
during initial building planning (along with other critical services
decisions like air management) to ensure that sufficient space and
access is provided. Several of the most common loop configurations
are shown in Fig. 2 (left).
The number and location of service connections should be carefully
planned with the user, and should correlate to the demand and diversity
estimates. Aside from adding to the overall system cost, each outlet
introduces a flow disturbance where contamination such as microbial
growth can occur. This can be a particular concern when connecting
to fixtures provided with laboratory furniture such as fume hoods,
unless the fixtures are designed for high-purity water applications
(e.g., recirculating tap fittings).
Selection of piping system materials can also have a significant
impact on total cost, although the primary consideration should
be maintenance of water quality. Plastics such as polyvinyl chloride
(PVC) and acrylonitrile butadiene styrene (ABS) are appropriate
for makeup systems but can contribute significant contaminants to
high-purity water. Unpigmented polymer materials such as polypropylene
and polyvinylidine difluoride (PVDF), particularly when joined by
heat fusion welding with minimal internal beads or crevices at the
joints, are appropriate for ultra-high-purity water distribution.
Fig.3. Relative material costs.Click
to enlarge. |
For
high-purity applications, the selection of valves and fittings (for
example, diaphragm valves with zero dead leg) is as important as
piping material specification and piping system design. These high-
purity valves and fittings can be significantly more expensive than
comparable components of PVC or ABS. An example of relative piping
system costs in various materials of construction is provided in
Fig. 3 (above).
Cost considerations Equipment for production of high-purity water
can greatly vary in cost (in the range of $5,000 to $40,000/gpm
of product flow). This is one reason why careful analysis by the
design team is needed to properly match the technology and capacity
to the need.
With a centralized distribution system, a significant portion of
system cost can be spent on the treatment equipment; therefore we
recommend considering alternate delivery strategies early in the
project. Alternatives include:
Point-of-use treatment units.
“Modular” design of central plant systems.
Build/own/operate arrangements.
It should be noted that these alternative approaches do not minimize
the importance in proper system planning, selection and specification
as described in this article.
Designing a central treatment plant with modular treatment units
can be a useful strategy to minimize initial cost and deal with
uncertainties in capacity growth and/or increasingly stringent water
quality criteria. If the capacity is sized for short-term requirements,
the distribution system must still consider the full build-out capacity
and the maximum and minimum flow rates at initial and future conditions.
A common trend in scientific facilities is “shelled” laboratory
space. When construction dollars are at a premium or when detailed
laboratory requirements cannot be determined in time to support
the construction schedule, the project team may decide to “shell
out” portions of a new facility for future fit-out, and offset the
initial costs.
The laboratory water system designer must be careful to specify
distribution piping headers for the maximum anticipated build-out
density, leaving branches or laterals until later; otherwise the
optimum flow and velocity criteria may be unachievable. One does
not always save full ft2 costs when deferring lab water systems
to a future build-out phase.
Operational issues Consideration of performance, efficiency, and
cost does not end at completion of laboratory water system installation.
Throughout the life of laboratory water systems, numerous decisions
and actions that must be taken, and the two major cost drivers are
materials and labor. Troubleshooting, maintenance, and repair efforts
can be reduced if proper attention is paid during planning and design.
Installation of flow metering and continuous quality monitoring
instrumentation (for example, at the point of supply from the polishing
system) adds to initial system capital cost but can ultimately reduce
operating cost by providing information to allow efficient system
balancing and early indication of preventative or corrective maintenance.
Placement of monitoring instruments after regenerable or replaceable
treatment components like ion exchangers can provide the operator
with a more accurate indication of capacity breakthrough than predictive
methods (time or cumulative flow), resulting in dynamic treatment
and reductions in chemical cost.
Planning for easy access to all system components can reduce maintenance
time and expense; the impact on budget is a one-time additional
area allocated to the laboratory water system, in facilities where
providing usable research space is the primary objective. This is
another feature that can be provided at reasonable cost if carefully
planned. It is often possible to share maintenance space with other
uses. Similarly, providing isolation valves (or even piping headers)
for future use can be seen as extravagant until the costs of a future
retrofit are taken into account.
In summary, the design of laboratory water systems involves accurately
establishing the quality and sizing criteria to meet specific laboratory
needs, developing schemes to build in flexibility (for example,
to accommodate future changes in laboratory use), selecting materials
and fixtures, and specifying system components. System design is
made more challenging by the various laboratory water standards
and treatment options available. Only when the user’s real quality
criteria and mode of operation are understood can a cost-effective
solution be realized.
Norman H. Toussaint, PE, LEED AP, is a senior chemical engineer
in the London, U.K., office of HDR Architecture Inc. Lauren M. Goodfellow
is a laboratory planner in the firm’s Mountain View, Calif., office.
HDR offers a broad array of architectural, engineering, consulting,
and management services for various sectors, with science and technology
as a core market group.
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