Wednesday, 18 April 2012

The steel frame is up at the Frome Medical Centre.

The site of the new primary care centre is on Frome showground adjacent to Frome Community Hospital.  The new building will provide 4,500m2 serving the primary health care needs of up to 32,000 patients, and accommodating a local GP surgery, minor surgery suite and training/teaching facility.  In addition the building will contain a pharmacy, dentist and optician.

The medical practice, one of the largest in the country, will be designed to provide a series of spaces on a scale to provide a more intimate approach whilst still providing a wide range of services.  The new building will recreate the ‘joined up’ working relationship and complete the concept of Frome Health Park.

Clarkebond is commissioned as civil, highway and structural engineers in the development of the site advising and providing design to the site to manage the impact of the ‘public open space’ status of the site and develop a building that contributes to its environment positively in the design of a green, low carbon facility that integrates with its locality and inspires its users.

Monday, 16 April 2012

Refurbishment of Purifier House

Clarkebond selected for the refurbishment of Purifier House, near Bristol city centre
Clarkebond have been appointed to provide civil, geo-environmental and structural engineering advice on a Grade II historic Purifier House which will provide 26 apartments, retail use and restaurant/cafe.

It will also include the erection of three/four storey building to provide 10 residential units, retail use and restaurant/cafe, associated car parking, cycle parking, landscaping and boundary treatment.

Resilience and Recovery - Ealing Broadway Bombing

Following the 2001 bombing in Ealing, west London Clarkebond was commissioned by Prudential to assess damage incurred to the structure and instruct the redevelopment of 11 high street multi-tenanted properties, some dating back to the early 1800s.

Extensive forensic investigation included the assessment of blast pressures and dynamic response, and assessment of the potential danger of collapse determining the need for temporary restraint.

After obtaining loss adjustor approval and securing agreement from the clients' insurers, a scope of works for the part refurbishment and part redevelopment of the site was delivered, phased for tenant re-occupation.



Management & Implementation

Whitehart Triangle
As design partner Clarkebond was responsible for all aspects of the investigation, remediation, and planning and design of the primary infrastructure of this 27ha heavily contaminated site owned by the London Borough of Greenwich and Tilfen Land.

Works included a 150m triple space highway bridge, 1.5km spine road, the installation of primary utilities and surface and foul water drainage networks. The £80m development will ultimately provide industrial, office, warehousing and distribution space.



Environment & Sustainability - Dart Marina

Dart Marina
The £21m redevelopment of Dart Marina in Dartmouth comprised the design 145 residential units, a 110 berth marina, the refurbishment of an existing hotel and facilities for boat owners including a luxury spa, swimming pool, gym and bistro.

Located on a former dry dock and boat storage yard works included extensive marine civil engineering work prior to construction the extent of which Clarkebond determined and managed through to completion.

The design required the extension of the river wall, strengthening works, reclamation increasing the plot area, extensive piling and foundation works and general infrastructure such as drainage and utilities. In addition retention of existing highway and adjoining residential designed to the local vernacular. The development was awarded 'Best Development and Best Marina Development' in the Daily Mail UK Property Awards 2007.


Thursday, 5 April 2012

Geoenvironmental Engineering - Silvertown Way

Geoenvironmental Engineering

Silvertown Way
Clarkebond undertook a number of surveys of this semi derelict site as part of the Canning Town redevelopment a project led by the London Development Agency. Investigations included geoenvironmental investigations to quantify contamination risk through quantitative risk assessments; flood risk assessment; ecology assessments including on site surveys for protected species and investigation into unexploded ordinance and asbestos. A remediation strategy was developed based on the groundwater and human health risk models the ground testing and addresses the high levels of hydrocarbon contamination derived from on and offsite sources.


Structural Engineering

Structural Engineering

DEFRA

This headquarters building was one of the first developments in Temple Quarter, a major regeneration area of Bristol.

Built on a previously contaminated brownfield site (a former railway yard) the concrete framed building is an exemplar of sustainable design achieving a BREEAM 'excellent' rating.

The six storey triangular block, provides over 16,000m2 for 840 staff, and is linked by a central atrium which maximises natural light and creates a 'stack effect' ventilation system, with the high level louvers working in tandem with the manual and automated windows.

Exposed concrete slabs, forming the internal office soffit, allow for night time cooling. Structurally, the building is braced by five lift shafts contained in two cores of the atrium while a glazed roof, supported by slender steel trusses distinguishes the atrium from the pitched roofs of the office wings.



Monday, 2 April 2012

Civil Engineering - Royal Albert Basin

Royal Albert Basin
Clarkebond was commissioned by the London Development Agency as lead consultants for the remediation of this inner city site, and the construction of a new primary infrastructure, signalised junctions and major utility works.

The masterplan for the regeneration comprises an extensive riverside development with parcels of land to the north for commercial units, allocated for business relocation due to the development of the Olympic site.

The works programme was carefully; designed for sufficient utility capacity for future developments, responding to the specific development platforms in line with the 2012 programme and monitoring site traffic to ensure little impact on transport flow.




Party Wall - Swansea Metropolitan University

Swansea Metropolitan University
Clarkebond were instructed to provide a detailed structural survey and a dilapidations/condition survey on the former Swansea Central Library building (Grade II listed), currently used as the School of Glass.  The building has a floor area of approximately 4000 sq m and involved the production of comprehensive written and photographic information on both internal and external defects and associated remedial work, accompanied by and elemental budget costing for repairs of approximately £1.8m.  Party Wall etc. Act and CDM 2007 duties will also be performed.


Monday, 19 March 2012

Resilience and Recovery

Buncefield
Buncefield Oil Depot hit the headlines in December 2005 when a series of powerful explosions destroyed the majority of the petrochemical facility and caused significant damage to surrounding properties. It took the fire service two days to bring the resulting fire under control.
Clarke Bond was appointed in the immediate aftermath of the incident by Keystone Foods (USA), Prudential Property Investment Managers and Legal & General to provide specialist blast damage assessments and major incident management services, including full structural engineering, building surveying, fabric and site contamination and overall project management.
Based on site the team prepared detailed analysis and recommendations for repair strategies, looking at buildings at 250m to 2km from the incident. The reports showed that the low intensity and long duration of the explosion resulted in widespread, random damage to buildings and, although it incurred no fatalities, it affected both commercial and residential properties in an area that employs approximately 16,500 people.
Clarke Bond’s analysis recommended demolishing a number of existing buildings in and around the Buncefield site, but in addition highlighted the future risks and how to mitigate against them for areas where industrial, commercial and residential buildings are juxtapositioned.
The analysis carried out on the Buncefield incident informs Clarke Bond’s resilience and recovery expertise; where we advise and educate developers, architects, planners and end users on property and asset resilience investigation and repair and recovery.




Management & Implementation

Legoland
Legoland Developments’ vision for its £150m theme park at Gunzburg, Germany was to create an attractive and pleasant family leisure destination. The challenging technical programme of the project, for which Clarke Bond provided management of all site operations, was put under pressure when ten months was taken out of the delivery programme.
Clarke Bond was appointed following the initial design scoping during which budgetary and scheduling risks were identified and evaluated. Our brief was to revisit and value all elements of the 27ha scheme to identify savings that could be achieved without compromising the quality of the delivered product.
As a result of our successful project review and revaluation, we were appointed for overall engineering design and the management of all site operations. This embraced over 150 individual contracts from an autobahn junction to external works and park theming. The project was completed in record time and opened 10 months ahead of schedule and within budget, this despite the extreme weather conditions encountered during construction.


Friday, 16 March 2012

Assessment & Treatment Options for Regent Street Disease

Assessment & Treatment Options for Regent Street Disease

Most people would agree that prevention is better than cure, but in some instances prevention is impossible, leaving the cure as the only option. This is the situation with so-called Regent Street disease (RSD).

The problem however is not confined to London’s Regent Street; in Manchester it is known as Deansgate disorder and it is also to be found riddling the skyscrapers of Chicago in the US. It occurs in buildings constructed using a steel frame covered in facing stone – in the case of Regent Street, Portland stone - but also in other materials such as brick or terracotta.



The use of such an emotive term, akin to ‘concrete cancer’ for reinforced concrete structures, indicates the concern that is generated by these problems. As with human medical conditions, the sooner the symptoms are recognised, the faster and more effectively an appropriate treatment can be initiated. Designers today, aware of the disease, build in mechanisms such as cathodic prevention to steel frame structures (i.e. the Broadgate development in the City of London) to inhibit any occurrence in the future.


THE DISEASE
Corrosion problems associated with early 20th century masonry clad steel frame buildings have become increasingly evident over the past few decades.

Buildings affected by corrosion were generally constructed during the first half of the 20th century and many are now Listed or designated within conservation areas. These buildings often have ornate stone or masonry facades which provides the impression of traditional solid load bearing construction.

The problems of corrosion in early 20th century steel framed buildings are related to the original designs. Unlike modern buildings utilising cavity wall construction techniques, these buildings have thick masonry or stone units tightly built about the structural steel frame.

As the facing masonry and masonry in-fill materials are often porous this method of construction allows moisture entering the structure to come into contact with the steelwork. Sufficient levels of moisture for corrosion can enter the structure through a variety of routes the more common of which include: open joints, cracks, directly through porous masonry facings, or through inadequate or poorly maintained rainwater protection details. 



Detailing may inadvertently trap inborne rain against the steelwork, so that once any original paint or other applied protection has broken down, corrosion can take place with no outside evidence – or at least initially. A similar problem can occur with hard bricks, and with terra cotta and faience, compounded by the inability of moisture to ‘breathe’ out through these non-porous materials once it has entered the fabric.

Within a given local environment, corrosion rates can vary markedly, due to the effects of sheltering and prevailing winds etc. It is therefore the ‘micro-climate’ immediately surrounding the structure which determines corrosion rates for particular processes.

Typically the volume change is a 5 to 10 times enlargement and since most elements have a flattish surface it follows that rusting tends to ‘grow’ outwards’ forming a surface layer.

Evidence of such corrosion can include vertical cracking at column positions and outward displacement of stonework in front of a member. Such stones may eventually become dangerous if they are dislodged and fall.   

Cast iron has a generally good resistance to corrosion as-cast, as silica in the moulding sand or loam fuses and coats the surface of the casting and forms a barrier to oxygen. Cut or fractured surfaces however will corrode quite rapidly. Wrought iron has a reasonable corrosion resistance, generally agreed to be somewhat better than that of carbon steel.

In unprotected and unrestrained conditions, iron and steel typically corrode at about 0.1mm/year in a damp clean atmosphere. In a marine, abrasive, or other aggressive environments the corrosion rate will be
much greater.

When investigating structures for appraisal it will often be necessary to assess the residual section where corrosion has occurred. Iron and steel that is embedded in masonry or encased in concrete may present particular difficulties for appraisal.

Firstly, it is generally inaccessible, both for routine inspection and maintenance during its previous life, and for examination now. Secondly, it may be exposed to damp conditions, with an adequacy of oxygen but no significant air movement to remove the moisture. Altering this environment to prevent further corrosion, or applying corrosion protection, may be difficult. 


ORIGINAL CONSTRUCTION PROTECTION MEASURES
Embedded steel frames in masonry were rarely adequately protected against corrosion. The 1930 London Building Act requirement in this respect was:

“All structural metalwork comprised in the skeleton framework of a building shall be clean of all scale, dust and loose rust, and be thoroughly coated with one coat of boiled oil, tar or paint before erection, and after erection shall receive at least one additional coat. Where such metalwork is to be embedded or encased in brickwork, terracotta, concrete, stone, tiles or other incombustible materials one coat of Portland cement wash of adequate consistency applied after erection may be used in lieu of coats of oil, tar or paint.”

In practice, it is found that steel in such construction has received only one coat of ‘paint’ (typically red lead), or even none, before being embedded in masonry. This paint is, after over half a century or more, unlikely to provide protection now or in the future.

Corrosion damage in such cases is very variable and often depends on location and on detailing. Thus a roof level beam immediately below a defective and poorly maintained gutter, or one under a limestone window sill, may be severely corroded, whereas an immediately adjacent structure appears quite sound. Because of this, it is difficult to be sure that corrosion is absent without 100% investigation – a daunting and potentially disruptive and expensive task.  


Today there are two repair options available to address this problem.
1. Removal of external stone/masonry to repair steelwork
2. Cathodic protection

1. REMOVAL OF EXTERNAL STONE/MASONRY CLADDING to undertake repair to the corroding steelwork,

This process involves cleaning the exposed steelwork to remove the surface rust by either sand blasting or needle gunning and treating the exposed surface with an appropriate site applied protective paint coating.

Normally the treatment is limited to the external face of the embedded steelwork as this is most at risk from moisture migrating inwards. However, damaged and or faulty buried rainwater goods can cause more general corrosion to steel members buried within the elevation. Parapets and cornices can also be more vulnerable to more extensive corrosion.


CORNICE  STEELWORK CORROSION

Unless all of the steelwork is treated there is a residual risk of ongoing future corrosion. However, it may not be practically possible to expose the steelwork without seriously impacting the external envelope and causing significant disruption to the occupant.

Locally deconstructing cornice stones can prove technically challenging bearing in mind that they may rely on the dead weight of the façade over to stabilise them. Furthermore, the resulting widespread destruction of the decorative stone details may prove sensitive with the planners, particularly if the building is listed or within a conservation area, and if the repair detail involves a man-made moulding to replicate the original detail. 



 Whilst taking the stone off and treating the steelwork is more expensive and time consuming the owner (and/or tenant on a FRI lease) has the peace of mind of physically seeing the work being done. It also offers the structural engineer the opportunity to assess the structural adequacy of the corroded members and strengthen as necessary.

2. CATHODIC PROTECTION (CP)
When the disease first emerged in the 1970s, the only option for treatment was to remove the masonry to access the steel frame, treat and/or remove and replace the steel and finally replace the masonry. Clearly this was not only costly, but also highly disruptive to the daily business of a building.

CP relies on the passage of a DC current from the environment into the protected metal surface to reverse the direction of electric currents associated with the corrosion process. It does not make good previous corrosion but suppresses the continuation of the process. Iron usually dissolves (rusts) to form positive ions and the damage caused by corrosion occurs at locations (termed the anode of the corrosion cell) where a positive current leaves the surface.

In reversing the direction of this current flow the cathodic protection system shifts the metal potential in the negative direction. As unlike charges attract more negative steel potentials provide a barrier to iron dissolution. Thus, the performance of a CP system may be monitored by determining the metal potential shift using an independent reference electrode.

The above description applies to all CP systems. The main difference between systems comes from the components used to distribute the current to the protected steelwork. It should be noted that CP requires the instillation of an electrical system with all its associated components.

The most important of these is termed the anode. There are primarily four anode systems available :

Conductive paint
Titanium mesh with a cementitious overly
Conductive cementitious overlay
Discrete anodes


For steel framed buildings it is appropriate to use discrete anodes and for reinforced concrete buildings, either conductive paint or discrete anodes.

The positive terminal of the DC power (the anode) is connected to the conductive material (the masonry). The negative terminal is connected to the steel (the cathode). The anodic reaction occurs in the embedded anode which is design to resist deterioration over the design life of the system.

CORNICE STEELWORK STRENGTHENING & REPAIR

Early systems relied on the protective current being created by the dissolution (corrosion) of a sacrificial piece anodic metal (galvanic system) such as zinc attached to the structure in a low electrical resistivity medium such as soil or sea water. In the case of reinforced concrete and masonry the current is produced from an external power supply and the current is impressed towards the corroding materials embedded within the structure.

The two forms of CP systems are now generally termed either ‘Sacrificial’ or ‘Impressed Current’ Cathodic Protection. The important major difference between these two forms of CP is that the anode is not consumed and the current output is fully controllable under an Impressed Current CP system. Both these qualities are generally essential for the successful operation of a masonry or concrete CP system.

CATHODIC PROTECTION : PRACTICAL CONSIDERATIONS

Making CP work in practice is a specialist skill. As a first step a feasibility study is normally carried out to assess the suitability of CP for the structure. 

The feasibility study should include a site visit, an examination of as-built drawings and all available reports. Various technical parameters are also considered such as electrical continuity, substrate conditions, presence of other embedded metals and fixings and any possible adverse side effects. If such information is not available then a site survey and testing may be required.

The site visit will also involve undertaking targeted key hole opening up of the structure to assess the general extent of corrosion and highlight any concerns regarding the structural integrity of the corroding steelwork. It is not unusual to find in the more vulnerable areas of the external envelope that local strengthening and/or replacement of steel members is also required as the CP scheme ca not address such matters, it will only prevent future deterioration.

Before deciding on which system to use i.e. galvanic (sacrificial) system or impressed-current system fundamental design decisions must be made to select the type of system and the most suitable type of anode appropriate to that system. Also required, is the determination of the size and number of the power sources, or sacrificial anodes, and their distribution on the structure.

Before concluding that CP is a viable option for a steel framed building it is essential that the following factors are assessed.

1. Continuity of the steel frame, fixings and other metallic elements
Failure to ensure the electrical continuity of all metallic elements in a steel framed building can result in stray current interactions between the various elements of the structure, resulting in the accelerated corrosion of the discontinuous elements. CP designers and engineers involved with steel framed buildings should always be fully acquainted with all common design details, historical methods of construction and testing and inspection methods for identification of discontinuous metallic elements.



DISCREET ANODES & WIRING BEING INSTALLED


2. Level of contact between the steel and masonry facing
The CP of steel framed buildings is possible since the protective current can be passed through the stonework or masonry to the steel via the mortar/masonry contact. Knowledge of the connection between the two elements is not always easy to ascertain. In some cases in-fill is completely absent. Expert knowledge of steel frame construction is required to make an accurate risk assessment on voidage.

For the system to be effective, large voids may need to be grouted Identification and filling any voids around the steelwork with a suitable material is an important part of the CP design and instillation. Once the voids around the steel are eliminated if the CP system fails the risk of masonry cracking is increased as a small amount of corrosion can cause it.

3. Current distribution
(controlled by mortar and stone resistivity)
The electrical resistivity’s of most masonry materials are in a suitable range for the application of CP when containing more than 2% moisture by weight. However as with any porous material it is important to understand the behavior of moisture content on resistivity.

The external cladding material should be carefully considered. Particular care is required when materials such as terra-cotta, faience and glazed bricks where the glazing or fire skin layer acts as insulator making it difficult to distribute protective currents to the steel surface. However, protection is possible in the majority of cases if, for example, the anode materials are in contact with the underlying porous material beyond the surface layer.

4. The impact of anode location and type
With regard to steel framed buildings, there are two main choices of anode:
·         mixed metal oxide coated expanded titanium mesh ribbon anode
·         discreet rod anodes

Expanded mixed metal oxide coated anodes have several distinct advantages:

i. The anodes are not visible in mortar joints
ii. The anodes can be installed using standard masonry pointing techniques
iii. The anodes can often be installed parallel to beams
& columns
iv. They cause minimal internal disturbance

Discreet rod anodes can be installed externally, however, careful consideration is required in relation to their positioning and resultant disturbance on the facade. However, they have the following advantages:

i. They can be installed internally and require no
external access.
ii. Anodes can be placed deep within the structure making them less susceptible to wetting and drying cycles on the building surface.

5. Aesthetic considerations
Cables can be installed in mortar bed joints with no noticeable visual effects on the front façade.


ECONOMIC DECISIONS
At the design stage of a CP scheme, a decision must be made as to whether the scheme will be a galvanic or impressed-current system. In specific circumstances, the use of both types of systems may be appropriate, but care is required to avoid interaction between them.

Galvanic systems have the advantage of being
·         simple to install
·         independent of a source of external electric power
·         suitable for localised protection
·         less liable to cause interaction on neighbouring structures

However, the current output available from the practical size and weight of galvanic anodes is relatively small and depends principally on the electrical resistivity of
the electrolyte.

The current from the anodes is not normally controllable; thus changes in the structure that causes 
an increase in protection current demand, may necessitate the instillation of further sacrificial anodes
 to maintain protection.

Impressed-current instillations have the advantage of being
·         able to supply a relatively large current
·         able to provide high DC driving voltages enabling it to be used in most types of electrolytes (environments)
·         able to provide a flexible output that may accommodate changes in, and additions to, the structure being protected

Generally, however, care must be taken in the design to minimise interaction on other structures and, if no
AC supply is available, an alternative power source (solar, diesel, etc), is required. Impress current systems
require regular maintenance and monitoring and may be connected up to the BMS or remotely monitored
via the phone line.

For badly corroded steelwork direct intervention in the form of physical repart and strengthening to thsteelwork may be the only protractible solution.

Prior to installation of a CP system a pilot study should first be undertaken to assess its suitability


MONITORING
The effectiveness of a CP system is assessed in accordance with a number of nationally and internationally verified and accepted criteria. These criteria are based on electrochemical parameters that can be measured and on-going monitoring and adjustment is required on a regular basis.

Time to first maintenance is determined by the life of the anodes which should provide at least 25 years service.

A well designed, installed, operated and inspected CP system should not require any major maintenance throughout its design life. An impressed anode CP system could last between 10 and 120 years depending on the type of anode CP system. Any electrical components and cabling would be expected to be renewed after
about 30 years.

The major risk with CP systems in commercial buildings is that its electrical distribution infrastructure is accidentally damaged by tenants when undertaking fit-out works. Hopefully this is picked up in the monitoring of the system and within the facility management procedures.

It is good practice to inform all building owners of CP systems and infrastructures in the area of influence of any new CP systems, or of significant changes to existing systems, so that their effect on these facilities may be assessed.


Saturday, 3 March 2012

Environment & Sustainability - Rackheath

Environment & Sustainability

Rackheath
Eco-Communities such as Rackheath will be low carbon developments, designed to the highest environmental standards and acting as best practice examples for future design and construction.
Clarke Bond’s role includes transportation, highways, water and sustainable drainage, civil and structural design, infrastructure design and co-ordination, energy strategy and energy services.
The Eco-Community will be committed to efficient public transport links, providing frequent and user-friendly bus and rail services, which includes plans for a new railway station, offering residents a regular service to and from Norwich city centre - and beyond. There will also be significant provision for cycle paths and walkways.
Government guidelines indicate that at least 30 per cent of the new Eco-Communities should be affordable homes. The proposed Rackheath development will feature around 5000 new and existing properties.
Residents will benefit from excellent local services and amenities with high quality healthcare, shopping and education at the heart of the community, along with excellent recreation facilities and plentiful green open spaces.
The Eco-Community will favour the use of locally-sourced goods and services; they will be desirable places to live, promoting a tangible sense of civic pride, responsibility and, as the name suggests, community.

The proposed community is likely to contain;
·         5000 new Eco-Homes
·         2 Primary Schools
·         New Secondary School
·         Community Centre
·         Adult Education Centre
·         Medical Centre
·         Local shops selling locally produced food
·         Heat and power generation provided by CHP plant
·         40% open space
·         Sustainable travel with buses and new station on existing railway line to Norwich


Geoenvironmental Engineering - Gibraltar Airport Tunnel

Geoenvironmental Engineering

Gibraltar Airport Tunnel

Clarke Bond were commissioned and continue to provide environmental management and waste
management expertise to the Government of Gibraltar for a major infrastructure project in
Gibraltar.  The project involves the design and construction of a new section of dual carriageway
that passes under the runway by means of a 350 m long cut-and-cover tunnel with 250m and
220m approach ramps. A subway is also included for pedestrian and cycle traffic.
A new roundabout is included in the scheme, along with two footbridges.  Ancillary items include
all associated mechanical and electrical installations, drainage and adjustments of existing
infrastructure.

Due to a history of military use including ammunition, aviation fuel storage and rifle ranges, the soil and groundwater at the site was found to be contaminated with heavy metals and hydrocarbons. Due to Gibraltar’s size and location, sustainable use of the waste soil arisings (70,000 m3) was key to the success of the project.
Clarke Bond initially worked with the local project management team to ensure that the contractor’s proposals were suitably designed to mitigate the risk posed by the contaminated land and groundwater.  This included oversight of the construction of a large groundwater treatment facility capable of treating significantly contaminated water to below Saline Environmental Quality Standards.  In addition, we undertook a detailed site investigation of the tunnel profile and managed the specification and commissioning of a soil wash facility. 
We have subsequently provided detailed assistance on groundwater treatment facilities, and have recently been commissioned to provide a Waste Management Plan and a detailed specification to facilitate the tracking and management of all excavated contaminated soil.