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Having developed a detailed list of environmental waste Recyling Facilities at Every Location. As a result of the new
streams, we began to build up a more realistic picture of the milk-run collection process, segregation of waste became
true nature of the problem. There were 12 sites in the essential and more awareness was required. People started to
Aberdeen area alone, and everyone had separate arrangements identify waste streams that had never previously been
for the removal and disposal of waste. Sometimes there were 5 identified. In the past, such waste was all considered “general
or 6 different vendors at one location, all responsible for one waste,” compounded by the fact that we only ever had one
small aspect of the process. There was no “management” of skip on site.
waste disposal at all.
The decision was made to move toward one single-source Sampling and Analysis, We established a program to sample
vendor for all waste management streams across all locations. and inspect both foul water and surface water interceptors on a
quarterly basis. As a result of this analysis, we became much
Establishing a Single-Source Vendor more sensitized to what we were disposing into our drains. We
Following an extensive vendor selection process involving focused our attention on cleaning up our washbays and yards
national and local waste management contractors, a single to minimize oily waste from entering the drains.
waste and interceptor management contract was awarded to an Figures 1 through 5 show the sampling information that
Aberdeen-based company, accredited to ISO 9000-2000 and was collected and analysed for a typical location.
ISO 14001 quality and environmental management systems,
with a 15-year proven track record with Schlumberger. The
vendor’s recent acquisition of new landfill sites and the pH VALUES
vendor’s flexible approach made them an ideal partner in our Foul
goal to measure, reuse, recycle, and reduce all waste streams. 12
The scope of the effort included the provision of total Surface
10
waste and interceptor management to the 12 main oilfield 8 S W Consent Low
services operational sites within a 30-mile radius of Aberdeen. 6
Based on an estimate of the waste streams received from each S W Consent
4
facility, we introduced the concept of a "milk-run” approach High
2
for selected waste streams. The milk-run approach consists of SL min Low
0
a dedicated vehicle that visits all SLB sites on a nominated
Q1 2004
Q2 2004
Q3 2004
Q4 2004
Q1 2005
Q2 2005
Q3 2005
Q4 2005
day to collect an identified waste stream. The rear-end loading SL min High
vehicle (REL) would collect general waste from the individual
sites, weighing the waste as it was collected, and then make
one journey at the end of the day to the sorting depot before Fig. 1—pH values taken from the interceptor. Key: Foul relates to
being disposed to the landfill. This included general waste foul water sewer; Surface is surface-water run-off; SL min Low is
the Schlumberger corporate limit for low pH levels, and
(plastic wrappers, used foodstuffs, and used packaging); wood correspondingly, SL min High is the same limit related to high-pH
waste; oil-contaminated waste; and the waste from the levels; S W Consent Low is the Scottish Water consent lower pH
emptying and cleaning of all site oil interceptors. limit; S W Consent High is the corresponding high pH limit.
Other initiatives included the accurate measurement of Scottish Water is the local regulatory authority for water-related
waste through the use of REL's with load-cell facilities. The legislation.
REL will know the weight it has onboard before it enters a
site; once it has collected the waste it deducts the new total Data in the figures show that the limits imposed by
weight from the previous weight, which then gives an accurate Schlumberger are more stringent that those applied by local
weight of waste collected. For the first time ever we would legislation. Schlumberger’s policy on these issues is that the
have accurate feedback on all waste streams from all sites. site is required to comply with the most stringent requirement
The first important foundation was achieved ”if you can”t defined, regardless of whether it is internal or external.
measure you can”t manage.” This strategy complemented the
waste stream segregation initiatives that were taking place in
tandem at each site.
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Q2 2004
Q3 2004
Q4 2004
Q1 2005
Q2 2005
Q3 2005
Q4 2005
Q1 2004
Q2 2004
Q3 2004
Q4 2004
Q1 2005
Q2 2005
Q3 2005
Q4 2005
Fig. 2—Readings for total hydrocarbons (THC), 2004–2005 to date. Fig. 5—Readings for biochemical oxygen demand (BOD), 2004–
The spike in Q4 2004 was a sampling error. This was a good 2005 to date. Key explained in Fig.1. Y-Axis units are mg/Litre.
learning opportunity to help improve the process. Key explained
in Fig.1. Y-Axis units are mg/litre.
Waste Reporting. All waste was segregated and recorded on
a monthly basis. Data in Figs. 1–5 show what was being
Suspended Solids recorded. These reports are detailed to ensure accuracy. The
2004 figures for waste costs for the contract were within 0.1%
600 of the figures that we routinely recorded in our internal QHSE
500 database, QUEST. This was very encouraging and highlighted
Foul the fact that the numbers we record are accurate.
400
Surface
300
S W Consent Consultancy and Advice. The contract that we developed
200 included a clause in which we requested that the provider give
SL limit
100 us feedback and advice that could improve our system or
0 could assist us in rectifying problems. We wanted the
Q1 2004
Q2 2004
Q3 2004
Q4 2004
Q1 2005
Q2 2005
Q3 2005
Q4 2005
Q2 2004
Q3 2004
Q4 2004
Q1 2005
Q2 2005
Q3 2005
Q4 2005
local area. Again in conjunction with our vendor, we designed became more aware of our obligation to protect all land from
and implemented a training program to prepare our staff to harmful substances.
manage accidental discharge and chemical spills. The training
is conducted in-house. The vendor provides regular updates Awareness of Treatment Costs. We had substantial
and input to keep the training current and relevant. Our vendor treatment costs associated with the disposal of contaminated
relationship works two ways—our vendor recently asked to water. We emptied our interceptors on a quarterly basis and
use some of our training material to assist other clients. were faced with escalating costs owing to the significant
hydrocarbon content in the water. The water had to be treated
Confidential Waste Disposal. The waste vendor provided a before it could be disposed of to meet landfill regulations. In
“curtain-side” 7.5-ton truck with a shredding machine fitted on an effort to reduce these costs, we established various methods
the back. The vendor shredded sensitive paper and binders to to recycle the water, rather than dispose of it. This had been
ensure Schlumberger and client confidentiality. recognised as “best practice” through our independent auditing
process on some of our sites. In one location in which we
Regular Review Meetings. Regular meetings were planned to conducted daily water pressure tests, we discovered that we
ensure two-way communication between both parties. were using 2000 to 3000 L of water for one test. On
Meetings would be held monthly with site representatives completion of the test, this water was disposed. By introducing
from each Schlumberger location to discuss relevant issues a holding tank and recycling capability, we were able to reuse
and proposals. This open dialogue with the vendor helped to the water for many months, thus saving several hundred
eradicate problems and improve quality. thousand liters of water.
We introduced a program of washbay management. This
Resiting Underground Tanks. We had several locations with enabled us to increase the interval between emptying the
underground storage tanks and pipes. We were concerned that interceptors. We moved to a six–month schedule, rather than
it was very difficult to determine the condition of this the original quarterly schedule. This made a huge impact by
equipment; it could be deteriorating and possibly leaking reducing the cost of emptying the interceptors, the further cost
contents into the ground. There was potential danger of of treatment of the contaminated water, and the cost of fresh
environmental damage to the local water courses. We decided water to refill the interceptor; it also reduced the number of
to remove all of the underground storage facilities and journeys made by the road tankers to empty the interceptors,
associated trunking. All equipment was relocated above which in turn helped to reduce the quantity of exhaust
ground to enable regular, robust integrity checks. The emissions to the atmosphere.
company would have demanded an exemption from our
worldwide enviormental standard if we had opted to leave the Incineration Costs. We identified a recycling center that
tanks underground. We would have had to justify this decision would take all the waste oil we produced. Though it had to be
based on risk assessment. This would have been very difficult transported some considerable distance, it was a more
to justify. environmentally friendly option than sending it to incineration
or landfill. It also resulted in considerable cost savings; only a
Immediate Success very small quantity was unsuitable for recycling and thus had
The results over the first few years were startling. The to be sent to incineration.
program affected results in four key areas.
Recycling Opportunities. One of the main aims of the
Segregation of Waste. With the contract in place; clearly contract was to reduce the amount of waste that went to
marked disposal routes were identified. Waste collection skips landfill. Figure 6 illustrates our monthly disposal of waste
were located in each site. The milk-run collection and ad hoc during 2005 year to date. The y-axis shows the number of tons
collection were quickly established. of waste disposed to landfill.
The monthly reports made an immediate impact; for the
first time we could quantify the amount of the waste being
produced.
It was quite startling to see how quickly our general
housekeeping improved now that there were clearly marked
outlets for the different waste streams.
There was better accountability in the disposal of
hazardous waste; we could now document what was on site
and ensure that the correct paper work was completed to
dispose of it in the correct manner. This ensured that no
hazardous waste materials were disposed of in the general
waste skip. Although this was legally acceptable at the time,
we could see how this might damage the landfill sites. We
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