gate fees 2018/19 report comparing the costs of alternative waste treatment options … gate fees...
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Gate Fees 2018/19 Report
Comparing the costs of
alternative waste treatment
options
WRAP’s twelfth gate fees report analyses the gate fees charged for a range of waste treatment, recovery and disposal options as reported by local authorities. In addition, gate fees are supplied by organic facility operators.
Research date: October 2018 – January 2019 Date: July 2019
WRAP - Comparing the costs of alternative waste treatment options
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WRAP’s vision is a world in which resources are used sustainably. Our mission is to accelerate the move to a sustainable resource-efficient economy through re-inventing how we design, produce and sell products; re-thinking how we use and consume products; and re-defining what is possible through re-use and recycling.
Find out more at www.wrap.org.uk
Document reference: [e.g. WRAP, 2006, Report Name (WRAP Project TYR009-19. Report prepared by…..Banbury, WRAP]
Written by: Hannah Dick & Peter Scholes
WRAP - Comparing the costs of alternative waste treatment options
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Executive summary This report summarises the findings of WRAP’s twelfth annual gate fees survey. The survey
covers gate fees charged to local authorities in the UK for a range of municipal waste
recycling, recovery, treatment and disposal options, for the calendar year 2018. Given the
expected future growth in non-household recycling under the Circular Economy Package and
new Resources and Waste Strategy, commercial waste gate fees have been collected but are
reported in an accompanying report which can be found here.
The aim of this report is to increase price transparency and, by improving the flow of
information, improve efficiency in the waste management market. A lack of market
information may reduce a local authority’s ability to make informed decisions on waste
management options. The publication of indicative gate fee information should assist
authorities in making better informed decisions regarding waste management options and
benchmark what they might reasonably be expected to pay in gate fee.
Summary gate fee data reported by local authorities from 2018 for a range of technology
types are presented in Table 1.
Table 1: Summary of the UK gate fees reported by local authorities, 2018 (£/tonnes)1
Treatment Materials / Type of
Facility / Grade Median Mode2 Range3
No of
gate
fees
reported
2017
median
gate
fees
MRF
All contracts (all wastes) £25 £5 to
£10
-£41 to
£97 91 £22
Contracts beginning in
2018 £35
£35 to
£40
-£3 to
£60 18 £354
In-Vessel
Composting
(IVC)
Mixed food & green £50 £50 to
£55
£28 to
£67 28 £49
All feedstock types £46 £55 to
£60
£10 to
£73 52 £46
Anaerobic
Digestion
(AD)
All gate fees £27 £15 to
£20
-£5 to
£68 62 £26
UK (contracts started
between 2016 - 2018) £19 £0 to £5
-£5 to
£50 18 -
Energy from
Waste (EfW)5 All £89
£85 to
£90
£44 to
£125 68 £86
1 All gate fees reported excluding haulage costs. 2 Mode is the gate fee range (in £5 increments) which received the most responses in the survey data. 3 Range lists simply the ranges between the maximum and minimum data points in the survey data collected.
4 Contracts beginning 2017 5 Incineration with energy recovery.
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Treatment Materials / Type of
Facility / Grade Median Mode2 Range3
No of
gate
fees
reported
2017
median
gate
fees
Pre-2000 facilities £65 £65 to
£70
£44 to
£89 20 £57
Post-2000 facilities £93 £85 to
£90
£50 to
£121 45 £89
Landfill
Non-hazardous waste
including landfill tax6 £113
£114 to
£119
£91 to
£176 76 £1067
Non-hazardous waste
excluding landfill tax £24
£25 to
£30
£2 to
£87 76 £20
Introduction Data gathering for this gate fee survey was conducted in November to December 2018,
collecting data for the 2018 calendar year. The survey targeted three main stakeholder
groups: local authorities (including unitary, waste collection and waste disposal authorities);
private sector operators of waste management facilities; and senior managers of large waste
management companies operating within the UK market.
The pricing of municipal waste management services can be complex. Users of the gate fee
information in this report should be aware of the following:
◼ Not all waste management services are costed or charged on a simple gate fee basis
(£/tonne). In some cases, a tonnage-related payment is just one element of a wider
unitary charge8 paid by an authority. For many authorities it is not appropriate, or
practicable, to isolate a pro-rata cost per tonne for a facility that may form just part of a
broader integrated service provision. As a consequence, only services for which it
has been possible to identify a gate fee (£/tonne) are included within this
report.
◼ The gate fee information for individual treatment options may not be directly applicable in
instances where multiple services are being procured. For example, a service that includes
collection together with EfW. Therefore, quoted gate fees are literally “at the gate” of the
facility in question and do not include the cost of additional services, such as collection
from households or transport to the waste management facility;.
◼ Contract terms, risk allocations and performance guarantees may vary significantly
between different authorities’ contracts, even in instances where the same technology is
being utilised. Such differences could have a significant impact on the associated gate fees
6 The standard rate of landfill tax for 2017/18 is £88.95 /tonne. 7 The standard rate of landfill tax for 2016/17 was £86.10 /tonne. 8 For an integrated or PFI infrastructure waste services contract, the private sector contractor can bundle the payments for a variety of waste management services (including potentially the initial capital spend and the ongoing maintenance and operation cost for associated waste management facilities) into a single ('unitary') charge to the local authority customer, rather than charging individual gate fees for each individual service.
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WRAP – Comparing the costs of alternative waste treatment options
(for instance, the contractor taking the risk for recyclates commodity price fluctuations
would result in a higher gate fee to compensate, than if risk sharing between the
contractor and local authority was utilised).
◼ A significant proportion of municipal waste management services are delivered under
medium to long-term contracts. Gate fees for such historic long-term contracts are
included in the survey sample but may not be reflective of the current market. However,
where reasonable samples were available the gate fees associated with more recent
contracts have been separately reported.
◼ Year on year changes in gate fees may reflect sampling variation. For instance, of the 221
local authorities responding in 2018, 155 also responded to the 2017 survey (70%), but 66
did not, meaning they are unique respondents to the 2018 survey. This difference in
samples needs to be considered when comparing the 2017 survey to those reported last
year.
◼ Gate fees in this report are presented in nominal terms with no adjustment for inflation.
Key Findings The key findings in this year’s survey are as follows for the UK:
Material Recovery Facilities (MRFs)
◼ The upward trend in MRF gate fee reported last year appears to be continuing. The
median MRF gate fee for contracts sorting 4 or more materials is £25/tonne, compared to
£22/tonne last year and £15/tonne in 2016. This year, 12% (15) of local authority
respondents report not paying a gate fee for MRF services, i.e. a zero or negative gate
fees, down from 16% (14) last year, 21% (20) in 2016 and 28% (30) in 2015. For
contracts signed in 2018, the median gate fee is £35/tonne and median contract length
down to 2 years.
◼ Of the 129 authorities supplying responses, 89 (69%) reported a change in gate fee in
2018 (64% in 2017), with 12 (19 in 2017) reporting a decrease (mostly due to new
contract negotiation or commodity price tracking) and 49 (39 in 2017) an increase in gate
fees (mostly due to indexation and commodity price tracking), again suggesting some
hardening in gate fees between 2017 and 2018. Of those reporting a change in gate fee
and providing a reason, 9 (11%) report the signing of a new contract, 13 (15%) report fee
change as result of a regular contractual review, 31 (36%) changes in commodity prices
(with an additional 13 (15%) as part of a contractual monthly or quarterly review giving a
total of 51%), 5 (6%) a change in the level of contamination (both increases and
decreases reported), and 25 (29%) contractual RPI increases.
◼ Interviews with contractors this year confirmed that the market is moving much more to a
fixed gate fee plus commodity price adjustments to minimise the risk to the operator, and
that contracting is getting more sophisticated with a trend to separate MRF processing and
commodity sales requirements managed in separate contracts. Although recyclate
commodity price fluctuation has the biggest impact on increasing MRF gate fees,
contamination is a particular issue and contracted contamination limits are reducing as
operators try to secure new markets and better prices for the recyclates they generate.
Contractors reported that by the end of 2018 typical gate fees for new local authority
contracts are £45-55/tonne.
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In-Vessel Composting (IVC)
◼ The median IVC gate fee for all types of municipal feedstock (i.e. mixed organics, or green
or food waste presented separately) being sent to IVC facilities is £46/tonne, which is the
same gate fee as reported last year. The median gate fee for mixed food and green
waste, the most common feedstock type sent to IVC facilities, has increased by £1/tonne
since last year, to £50/tonne compared to £49/tonne. Operators cited a similar contract
gate fee for municipal mixed food and green waste of £48/tonne.
◼ Separate food waste is the most expensive at £61/tonne (the same as last year), and
green waste the least expensive at £33/tonne (an increase from £31/tonne). Nearly half
of the responses (small sample for this feedstock) were from Scotland and so not
necessarily representative of the whole of the UK.
◼ Contract gate fees given by operators are lower than those by local authorities, with
£45/tonne for food and £26/tonne for green waste. There is different regional
representation in the two samples which could be one reason for the difference, as policy
differences between Scotland and Wales, compared to England, mean there are
differences in gate fees particularly for separately collected food waste.
◼ The majority (72%) of local authorities sending waste to IVC facilities do so under contract
and are therefore likely to be reporting historic contract gate fees, which may explain why
there are some differences between gate fees cited by local authorities and the operators,
the latter reporting recently agreed municipal contract gate fees.
◼ Waste contractors also said they expect IVC gate fees to have remained somewhat stable
(in real terms i.e. in line with inflation), primarily due to the impact of long term contracts.
◼ Approximately 37% of authorities said their gate fees had changed in the last 12 months,
with 86% being increases, and the vast majority citing inflation/indexation as the reason.
Anaerobic Digestion (AD)
◼ The median AD gate fee reported by local authorities for 2018 for the UK as a whole is
£27/tonne, which is slightly higher than the £26/tonne gate fee from last year’s survey.
Before this year’s reported gate fee, the figure had shown steady decline, since 2015.
However, the median of contracts which have started in the last three years is £19/tonne,
which reflect waste contractor expectations of declining gate fees more accurately.
◼ For England, the pattern over the last four years has been of steady decline (£35/tonne in
2015, £30/tonne in 2016, £26/tonne in 2017, to £23/tonne last year) until this year, where
data reported by local authorities results in a median of £26/tonne.
◼ The median gate fee of all waste streams reported by the operators is £10/tonne, which is
a £3/tonne increase on last year’s figure. It is much lower than the £27/tonne reported by
the local authorities, although this figure includes gate fees from contracts signed some
years ago. The lower figure reported by operators is likely to reflect gate fees charged at
the time of the survey ie. December 2018, and therefore better reflect the current market.
However, the operator survey was also dominated by respondents in England, where lower
gate fees are seen compared to Wales and Scotland.
◼ The median gate fee in Wales has reduced from last year’s £49/tonne to £41/tonne. Due
to a small sample size for Wales, it is more likely than an individual authority’s reported
gate fee has an impact on the overall result, and so the result is more sensitive to changes
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WRAP – Comparing the costs of alternative waste treatment options
year on year. Despite this decrease, Wales still has the highest gate fees, which is thought
to reflect the fact that a high proportion of the contracts in Wales are long-term PFI
contracts.
◼ The market continues to be fragmented, affected by local competition and national
legislation and policy. For example for in Scotland, food waste collections are mandated in
the Waste (Scotland) Regulations 2012 and in Wales, food waste tonnages are boosted
through the Collections Blueprint, creating greater demand for food waste treatment
capacity, compared to England where separate food waste collections are currently not
mandatory. Market perception is very much impacted by what is happening in the markets
in London and the south east, where gate fees are under extreme pressure. Scotland,
Wales and Northern Ireland, as well as northern England, represent stronger markets with
higher typical gate fees, which are reflected in the overall medians generated by this
survey.
Energy from Waste facilities (EfW)
◼ This year the reported median gate fee for incineration with energy recovery (EfW) is
£89/tonne compared to £86/tonne last year. For pre-2000 EfW facilities, the median gate
fee is £65/tonne, compared to £57/tonne last year. For post-2000 facilities, median gate
fee is £93/tonne compared, compared to £89/tonne last year.
◼ Of the authorities responding to the question, 65% said their gate fee had changed in
2018. Most (93%) said this was due to an inflation increase or some other contractual
annual uplift, with others reporting a change due to negotiating a new contract or contract
extension.
Non-hazardous landfill
◼ The UK median landfill gate fee is £24/tonne, which is an increase compared to last year’s
of £20/tonne. Similar to last year, variability is getting larger, with a range of £2 to
£87/tonne). Landfill gate fees vary regionally, depending upon the availability of capacity
locally and of alternative options such as EfW or ports for RDF export.
◼ Local authorities and waste contractors expect to see increases in landfill gate fees in
future years as available landfill capacity reduces.
Detailed Summary
Materials Recovery Facilities (MRF)
◼ The median MRF gate fee (for MRF contracts which sort 4 materials or more) is £25/tonne
(based on 91 responses from local authorities), up from a median of £22/tonne last year.
◼ Only 12% of local authority respondents (i.e. 15) report not paying a gate fee for MRF
services i.e. a zero or negative gate fee, in comparison to 16% (14) last year, 20% (20) in
2016 and 28% (30) in 2015.
◼ The local authority gate fees reported include historic data (long term contracts) therefore
the median reflects a combination of the current market fees and fees inherited from
past years. For contracts signed in 2018, the median MRF gate fee has increased to
£35/tonne (18 reported contracts started in 2018). Contractor interviews report that new
contract gate fees could be as high as £45-55/tonne.
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WRAP – Comparing the costs of alternative waste treatment options
◼ Contracting data has shown that contract lengths have decreased over time, reducing the
contractor’s commodity pricing risk. The median contract length for 2018 signed contracts
is 2 years, compared to 6 years for contracts signed in 2014, and 19 years for contracted
started before 2014. Of all contracts reported, 49% were of 5 years duration or less.
◼ Of the 129 authorities supplying responses, 89 (69%) reported a change in gate fee in
2018 (64% in 2017), with 12 (19 in 2017) reporting a decrease (mostly due to new
contract negotiation or commodity price tracking) and 49 (39 in 2017) an increase in gate
fees (mostly due to indexation and commodity price tracking9), again suggesting some
hardening in gate fees between 2017 and 2018. Of those reporting a change in gate fee
and providing a reason, 9 (11%) report the signing of a new contract, 13 (15%) report fee
change as result of a regular contractual review, 31 (36%) changes in commodity prices
(with an additional 13 (15%) as part of a contractual monthly or quarterly review giving a
total of 51%), 5 (6%) a change in the level of contamination, and 25 (29%) contractual
RPI increases.
◼ The single price range with the most gate fees is £5 to £10/tonne (i.e. the mode,
compared to £0 to £5/tonne last year); the full range of responses was from -£41 to £97,
similar to last year. Reported gate fees are influenced by a wide range of factors including
material mix, contract length and age, contractual pricing mechanism, annual tonnage,
MRF technology employed, and the degree of risk share between the authority and
contractor.
◼ Analysing median gate fee and gate fee range per UK nation (plus London) shows Wales
and Northern Ireland experiencing higher median gate fees and minimum gate fees than
England, potentially due to relative market size. This corroborates trends seen in previous
years.
◼ The key driver in MRF gate fees, as evidenced in the last 3 to 4 years of gate fee surveys,
has been variability in the value of recyclates, and the need for contractors to reduce their
exposure to this risk. For instance, in 2017 some materials showed annual price
increases10, such as +63% for mixed cans and +25% for plastic bottles from 2016 lows,
with plastics and card showing decreases over the same period. In 2018, the impact of
the China Sword initiative pushed reductions in price particularly for fibres (e.g. card -
24%) and plastics (e.g. mixed plastics -36%). This unpredictable variability has increased
the number of contracts which exercise some form of price review mechanism (in some
cases as often as weekly or monthly) based upon a basket of commodity materials pricing.
For instance, in 2018, 51% of reported contracts included such a mechanism, compared to
37% in 2017 and 29% in 2016.
◼ Of the 117 respondents expressing an opinion, 97 (83% v 84% last year) expect gate fees
to increase in the future. Of factors which local authorities report as influencing MRF gate
fees, commodity prices, input material quality and operating costs, in rank order, are
9 Note that, depending upon when contracts were signed at the value of the applied commodity material basket at that time, gate fee adjustments to compensate for basket value fluctuation can result in both gate fee increases or reductions.
10 Based upon WRAP Materials Pricing Report; 2017 variations are based on the difference between prices first week Dec 2016 and first week Dec 2017; 2018 based upon the difference between the first week Dec 2017 and first week Dec 2018.
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deemed those having most impact on gate fees now and in the future, the same as in last
year’s survey.
◼ Interviews with contractors this year confirmed a number of factors evident from the
survey results:
o That gate fees to local authorities in general are continuing to increase;
o The market is moving much more to a fixed gate fee plus commodity price
adjustments to minimise the risk to the operator;
o That contracting is getting more sophisticated with a trend to separate MRF
processing and commodity sales requirements managed in separate contracts;
o That the market is moving much more to price review on a monthly, 3 monthly
or 6 monthly basis to take into account fluctuations in commodity prices;
o That contamination is a particular issue and contracted contamination limits are
reducing as operators try to secure new markets and prices for the recyclates
they generate.
Table 2: Summary of MRF gate fees reported by local authorities by nation (and London)
(2018) (£/tonne)
In-Vessel Composting (IVC)
◼ The median across all types of municipal feedstock being sent to IVC facilities is
£46/tonne, which is the same as was reported last year. Operators cited a similar contract
gate fee for municipal mixed food and green waste of £48/tonne.
◼ The median gate fee for mixed food and green waste for the UK, the most common
feedstock type sent to IVC facilities, has increased by £1/tonne since last year, to
£50/tonne compared to £49/tonne. Separately collected food waste is the most expensive
at £61/tonne (same as last year), and green waste the least expensive at and £33/tonne
(also increased from £31/tonne), with differences likely reflecting the additional ABPI
requirements of composting food waste, such as contamination removal before shredding,
prevention of cross-contamination between ABPI clean and dirty areas, and high
temperature composting requirements. However, the sample size for the separately
collected food waste in particular is small, and three of the seven authorities responding
were from Scotland. For food waste the operators survey median was £45/tonne, which is
significantly lower than that cited by local authorities which was £61/tonne. Regional
differences in policy and legislation impact the market for food waste. For example in
Country/Region Median Mode Range Number of gate fees
UK £25 £5 to £10 -£41 to £97 91
England (incl.
London) £17 £0 to £5 -£41 to £82 63
London £18 £5 to £10 -£2 to £38 11
Wales £49 £80 to
£85 -£2 to £81 7
Northern Ireland £39 £35 to
£40 £32 to £70 12
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Scotland, food waste collections are mandated in the Waste (Scotland) Regulations 2012
and in Wales, food waste tonnages are boosted through the Collections Blueprint, creating
greater demand for food waste treatment capacity, compared to England where separate
food waste collections are currently not mandatory. Therefore the gate fees seen for
separately collected food waste are different between the nations.
◼ It should be noted that of operators who completed the survey, nine out of the ten were
from England, and therefore are likely to report lower gate fees than the local authorities
where there is more of a mix of regional representation.
◼ Operators gave a slightly lower figure for green waste at £26/tonne, compared to the
£33/tonne cited by local authorities.
◼ The discrepancy between separately collected food and green waste gate fees specified by
local authorities and operators may be due to local authorities reporting contract gate fees
which have been agreed a number of years ago. The analysis shows that 72% of the
authorities report sending material to an IVC facility under a contract. Median gate fees
for contracts started in 2018 were reported at £46/tonne, compared to £45/tonne last year
and £38/tonne for those started in 2016.
◼ Approximately 37% of authorities said their gate fees had changed in the last 12 months,
with 86% being increases, and the vast majority citing inflation/indexation as the reason.
◼ The waste contractor interviews suggested that IVC gate fees have remained somewhat
stable (i.e. in line with inflation) as mainly their operation is based on long term municipal
contracts. This does align with responses from local authorities and the only slight
increases in median gate fees for mixed food and green waste and separate green waste.
However, it should be noted that in this year’s data, 23 new contracts have been signed in
the last 3 years and 57% of reported contracts have a term of five years or less, which
suggests there is more turnover in the market than these operator interviews indicate.
Table 3: IVC gate fees provided by local authorities by waste material type (£/tonne)
Waste Type Median Mode Range Responses
All materials
(UK) £46 £55 to £60 £10 to £73 52
Mixed food &
green waste £50 £50 to £55 £28 to £67 28
Food waste
only £61 £60 to £65 £30 to £73 7
Green waste
only £33 £40 to £45 £20 to £64 15
Anaerobic Digestion (AD)
◼ The median AD gate fee for 2017 is £27/tonne, which is slightly higher than the £26/gate
fee in last year’s survey. The range is exactly the same as last year, with six local
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authorities citing an income or £0/tonne gate fee for their food waste (twice more than the
three reporting last year).
◼ For England, the pattern over the last four years has been of steady decline (£35/tonne in
2014/15, £30/tonne in 2015/16, £26/tonne in 2016/17, to £23/tonne last year) until this
year, where data reported by local authorities results in a median of £26/tonne. The range
has remained the same since last year (-£5 to £68/tonne). The modal range is £15 to
£10/tonne and so the median does not fall within range, indicating variability.
◼ The median gate fee in London has increased by £1/tonne since last year, at £27/tonne.
This figure is based on eight gate fees from six local authorities. Information from waste
contractors suggests that this does not reflect the current market in London, or at least not
the more recent contracts. Only one of the contracts reported started in 2018, with a few
of the others reported as having started in the last decade, and therefore this could be a
reason the median does not reflect the market as seen by the industry. It should be noted
that there is significant variability, i.e. gate fees as low as £0/tonne and some as high as
£68/tonne.
◼ The median gate fee in Wales has reduced from last year’s £49/tonne to £41/tonne. The
range has shifted upwards slightly from £14 to £62/tonne last year, to £19 to £64/tonne
this year. One authority has made a significant saving since last year by changing
contract, and as Wales is a relatively small sample size, it is likely that this saving has
influenced the overall median figure. Despite this decrease, Wales still has the highest
gate fees, which is thought to reflect the fact that a high proportion of the contracts in
Wales are long-term PFI contracts.
◼ Although there was insufficient data to be able to report figures, for the first time this year,
an authority in Northern Ireland reported as sending separately collected food waste to
AD.
◼ The median figures of contracts which have started in each of the last three years have
been £20/tonne or below. Combining the last three years (sample size of 18 authorities),
the overall median is £19/tonne, with a range of -£5 to £50/tonne, and a modal range of
£0 to £5/tonne, which reflect waste contractor expectations of gate fees more accurately.
◼ The median gate fee of all waste streams reported by the operators is £10/tonne, which is
a £3/tonne increase on last year’s figure. It is much lower than the £27/tonne reported by
the local authorities, although this figure includes gate fees from contracts signed some
years ago. The operator survey was also dominated by respondents in England, where
lower gate fees are seen compared to Wales and Scotland.
◼ As first identified two years ago, market over-capacity (or lack of capture of available
unavoidable food waste as feedstock) in various parts of the UK is driving gate fees down
to an unsustainable level. for AD operators. The slight increase in gate fees reported by
local authorities is not reflected from the interviews with waste contractors, however they
also did not report further decreases.
◼ The waste company interviews reported that market continues to be fragmented, affected
by local competition and legislation (which affects supply). With most large waste
companies and AD sector membership organisations run from London, it seems that the
overall perception of the AD market is dominated by what is happening in the markets in
London and the south east, where gate fees are under extreme pressure. Scotland, Wales
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and Northern Ireland, as well as northern England, represent stronger markets with higher
typical gate fees, which are reflected in the overall medians generated by this survey.
Table 4: Summary of Anaerobic Digestion facility gate fees reported by local authorities
(£/tonne) by nation (and London)
Median Mode Range Responses
UK (all gate fees) £27 £15 to £20 -£5 to £68 62
UK (contracts
started between
2016 - 2018)
£19 £0 to £5 -£5 to £50 18
England (incl.
London) £26 £15 to £20 -£5 to £68 43
Wales £41 £15 to £20 £19 to £64 10
Northern Ireland Insufficient
data
Insufficient
data
Insufficient
data 1
London £27 £25 to £30 £0 to £68 8
Energy from Waste facilities (EfW)
◼ As in previous years, results are reported for the UK as a whole, segregating results for
facilities built before and after 2000.
◼ This year, the overall median gate fee reported by local authorities for EfW (incineration
with energy recovery) is £89/tonne compared to £86/tonne last year.
◼ For pre-2000 EfW facilities, the median gate fee is £65/tonne, compared to £57/tonne last
year. For post-2000 facilities, median gate fee is £93/tonne, compared to £89/tonne last
year. The difference between pre- and post-2000 facility gate fees is thought due to the
difference in the original construction cost of facilities, particularly taking environmental
controls into account, as well as the prevailing market conditions at the time contracts
were signed.
◼ Of the authorities responding to the question, 65% said their gate fee had changed in
2018. Of those that reported a reason for this change, most (93%) said this was due to an
inflation increase or some other contractual annual uplift, with others reporting a change
due to negotiating a new contract or contract extension.
◼ Based upon the responses to this survey, in the period 2013 to 2018, a total of 41 new
contracts are reported to have started. For these contracts signed over the 5 year period,
median gate fees show that for pre 2000 facilities, new contracts were being signed at
gate fees significantly above the overall median gate fee for 2018 (£85/tonne compared to
the overall median of £65/tonne) and more in line with market (and post-2000) gate fees.
For post-2000 facilities, new contracts between 2013 and 2018 were being signed with
gate fees slightly lower than the overall median gate fee for 2018 (£87/tonne compared to
the overall median of £92/tonne). It is not clear from the data supplied, why this should be
the case. . Note in terms of contract lengths, most of the post-2000 facility new contracts
filled all or most of the capacity for newly built facilities (i.e. anchor contracts), and
therefore average at 25 years. For new contracts for pre-2000 facilities, these are renewed
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WRAP – Comparing the costs of alternative waste treatment options
or replacement contracts for existing long-established facilities, reflected in a much shorter
median contract term of 7 years.
◼ The range in reported gate fees is broad at £44 to £125 (£85-90 mode range). This is
because there is a significant range of contractual and funding factors which can have an
influence on gate fee charged including mode of financing (PFI/PPP or prudential
borrowing), whether the asset reverts to the local authority or not, contract length, and
whether the authority made a capital contribution. Operators reported that contracts are
getting more sophisticated and applying a unique set of contractual and funding factors,
therefore making it difficult to compare individual gate fee figures.
◼ Discussions with the waste management companies confirmed the figures generated by
the survey, and that the main impact on local authority gate fees now all of the local
authority dedicated PFI capacity has been delivered, will be contracted inflation increases.
For new contracts in the future, the likely factors influencing gate fees will be the
propensity of merchant EfW capacity (there are some active projects coming through), the
availability of landfill (which will drive local disposal gate fees) and the impact on RDF
exports post Brexit. It is thought the low value of Sterling and possible reduction in the
availability of cheap back-haul transport to Europe post Brexit will impact the availability of
European free capacity as an option, could push up RDF pricing and potentially UK EfW
spot and new contract gate fees. Although it has been suggested that Dutch operators are
looking east for future material, and are taking smaller packages of waste to de-risk, UK
contractors explain that most want to keep communication open for if they need additional
waste for capacity drops in the future.
Table 5: Summary of Energy from Waste (Incineration with energy recovery) gate fees
reported by local authorities 2018 (£/tonne)
Type of
facility
Median Mode Range Responses
All £89 £85 to £90 £44 to £125 68
Pre-year
2000
All responses £65 £65 to £70 £44 to £89 20
With contracts £66 £65 to £70 £44 to £89 16
Without
contracts £54 £45 to £50 £47 to £81 4
Post-
year
2000
All responses £93 £85 to £90 £50 to £121 45
With contracts £92 £85 to £90 £50 to £121 42
Without
contracts £93 £90 to £95 £92 to £110 3
Non-hazardous landfill
◼ Across the UK the median landfill gate fee reported by local authorities is £24/tonne,
ranging from £2 to £87/tonne, and mode of £25 to £30/tonne. This is an increase on last
year’s median of £20/tonne. However, variability of the gate fees around this median is
getting larger, which is mirrored by the fact the median does not fall within the modal
range.
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WRAP – Comparing the costs of alternative waste treatment options
◼ From the data collected, it would suggest that both Wales and Northern Ireland’s gate fees
have dropped since last year. In the case of Wales, a significant decrease from £32 last
year to £19/tonne this year has been reported. For Northern Ireland the median has
decreased from £13 to £9/tonne. However, in both cases, the range is identical to last
year’s results, and given that both sample sizes are relatively small (in comparison with
England for example), it is likely that the reported changes are more a reflection of the
authorities that have responded and which happens to fall as the ‘median’, which is the
key average figure reported in the annual gate fee report, rather than being a reflection of
changes in the market.
◼ Gate fees in England have increased slightly from £22 to £24/tonne, and the range of gate
fees has decreased since last year, from £2-£50 to £5-£44/tonne. There are regional
differences in England. Similar to last year, the lowest gate fees are seen in the East of
England at £10/tonne (which is a slight decrease since last year at £13/tonne) and the
highest in the North West, which has increased by £1/tonne since last year to £30/tonne.
◼ Local authorities and waste contractors expect to see increases in landfill gate fees, due to
an increasing lack of available capacity.
Table 6: Summary of landfill gate fees reported by local authorities by nation (£/tonne)
Median Mode Range Responses Median 2017
UK (including
£88.95 landfill tax,
2018/19 tax year)
£113 £114 to
£119
£91 to
£176 76 £107
UK (excluding
landfill tax) £24 £25 to £30 £2 to £87 76 £20
England (incl.
London) £24 £25 to £30 £5 to £44 48 £22
Wales £19 £15 to £20 £2 to £48 7 £32
Northern Ireland £9 £5 to £10 £8 to £52 5 £13
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WRAP – Comparing the costs of alternative waste treatment options
Contents Executive summary .................................................................................................. 3
Contents ................................................................................................................. 15
Tables ..................................................................................................................... 16
Figures ................................................................................................................... 17
Glossary .................................................................................................................. 19
Acknowledgements ................................................................................................ 19
1.0 Introduction ................................................................................................. 20
2.0 Approach & Scope of this study ........................................................................ 21
3.0 Survey response rates ...................................................................................... 22
3.1 Local Authorities ............................................................................................... 22
3.2 Reasons for not supplying gate fee data ............................................................. 23
3.3 Organic operators survey .................................................................................. 25
3.4 Interviews with waste management companies ................................................... 26
4.0 Results and analysis ......................................................................................... 26
4.1 Materials Recovery Facilities (MRFs) ................................................................... 26
4.1.1 Current gate fees and trends ........................................................................ 27
4.1.2 Gate fee by contract year ............................................................................. 29
4.1.3 Contract review ........................................................................................... 30
4.1.4 Materials collected and sorted ...................................................................... 31
4.1.5 Key influencing factors ................................................................................. 33
4.1.6 Waste contractor interviews ......................................................................... 35
4.2 In-Vessel Composting ....................................................................................... 35
4.2.1 Current gate fees and trends ........................................................................ 35
4.2.2 Contract review ........................................................................................... 39
4.2.3 Key influencing factors ................................................................................. 40
4.2.4 Survey of IVC operators ............................................................................... 42
4.2.5 Key influencing factors – operators ............................................................... 43
4.2.6 Waste contractor interviews ......................................................................... 44
4.3 Anaerobic Digestion (AD) .................................................................................. 45
4.3.1 Current gate fees and trends ........................................................................ 45
4.3.2 Contract review ........................................................................................... 47
4.3.3 Key influencing factors ................................................................................. 48
4.3.4 Survey of AD operators ................................................................................ 50
4.3.5 Key influencing factors – operators ............................................................... 51
4.3.6 Waste contractor interviews ......................................................................... 52
4.4 Energy from Waste ........................................................................................... 52
4.4.1 Current gate fees and trends ........................................................................ 53
4.4.2 Contract review ........................................................................................... 55
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WRAP – Comparing the costs of alternative waste treatment options
4.4.3 Key influencing factors ................................................................................. 56
4.4.4 Waste contractor interviews ......................................................................... 57
4.5 Non-hazardous landfill ...................................................................................... 58
4.5.1 Current gate fees and trends ........................................................................ 58
4.5.2 Contract review ........................................................................................... 62
4.5.3 Key influencing factors ................................................................................. 63
4.5.4 Waste contractor interviews ......................................................................... 65
5.0 Recommendations for future surveys .............................................................. 65
Appendix 1 – Data Collection Methodology ............................................................ 67
Tables Table 1: Summary of the UK gate fees reported by local authorities, 2018 (£/tonnes) ............ 3
Table 2: Summary of MRF gate fees reported by local authorities by nation (and London)
(2018) (£/tonne) .............................................................................................................. 9
Table 3: IVC gate fees provided by local authorities by waste material type (£/tonne) .......... 10
Table 4: Summary of Anaerobic Digestion facility gate fees reported by local authorities
(£/tonne) by nation (and London) .................................................................................... 12
Table 5: Summary of Energy from Waste (Incineration with energy recovery) gate fees
reported by local authorities 2018 (£/tonne) ..................................................................... 13
Table 6: Summary of landfill gate fees reported by local authorities by nation (£/tonne) ...... 14
Table 7: Local authority response rates 2018 .................................................................... 22
Table 8: Local authority response rates 2017 .................................................................... 23
Table 9: Reasons given by local authorities not supplying gate fee data (count of responses,
2018 survey) .................................................................................................................. 24
Table 10: IVC and AD facility operator response rates 2018 ............................................... 25
Table 11: Composting and AD facility operator response rates and (responses with usable gate
fees) by survey year ....................................................................................................... 25
Table 12: MRF gate fees reported by local authority by nation and London (2018) (£/tonne) 27
Table 13: MRF gate fee reported by local authorities by contract start year (2014 to 2018,
from 2018 data £/tonne) ................................................................................................. 29
Table 14: Changes in MRF gate fees reported by local authorities in 2018 with reasons ........ 30
Table 16: Range and frequency of materials being sorted at MRFs reported by local authorities
in 2018, with material prices changes in December 2018 per key recyclate material (as %) .. 32
Table 17: Key influencing factors – current MRF pricing (indicated by 2018 local authority
survey – 112 respondents) .............................................................................................. 34
Table 18: Key influencing factors – future MRF pricing (indicated by 2018 local authority
survey – 118 respondents) .............................................................................................. 34
Table 19: IVC gate fees provided by local authorities by waste material type (£/tonne) ........ 35
Table 20: IVC contract lengths (for which contract length was submitted) ........................... 39
Table 21: IVC gate fees based on contract start year (£/tonne) .......................................... 40
Table 22: Factors influencing current IVC gate fees (indicated by local authority survey – 44
respondents) .................................................................................................................. 40
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WRAP – Comparing the costs of alternative waste treatment options
Table 23: Factors most likely to influence future IVC gate fees (indicated by local authority
survey – 43 responses) ................................................................................................... 41
Table 24: Contract and spot IVC gate fees, for municipal waste, provided by facility operators
(£/tonne) ....................................................................................................................... 42
Table 25: Factors influencing current IVC gate fees (indicated by IVC operators surveyed – 9
responses) ..................................................................................................................... 43
Table 26: Factors most likely to influence future IVC gate fees (indicated by IVC operators
surveyed – 9 responses) ................................................................................................. 44
Table 27: AD gate fees reported by local authorities by nation (and London) (£/tonne) ........ 45
Table 28: AD contract lengths ......................................................................................... 47
Table 29: Factors influencing current AD gate fees (indicated by local authorities surveyed –
28 Reponses) ................................................................................................................. 48
Table 30: Factors most likely to influence future AD gate fees (identified by local authorities –
27 responses) ................................................................................................................ 49
Table 31: Contract and spot AD gate fees, for municipal waste, provided by facility operators
(£/tonne) ....................................................................................................................... 50
Table 32: Factors influencing current AD gate fees (identified by AD operators surveyed – 10
responses) ..................................................................................................................... 51
Table 33:Factors most likely to influence future AD gate fees (identified by AD operators
surveyed – 8 responses) ................................................................................................. 51
Table 34: Summary of energy recovery (EfW) gate fees reported by local authorities 2018,
with and without contracts (£/tonne) ............................................................................... 53
Table 35: EfW contracts started and median gate fees reported by local authorities 2013-2018
(£/tonne) ....................................................................................................................... 55
Table 36: Energy recovery contract lengths reported 2018 ................................................. 56
Table 37: Key influencing factors – current energy recovery gate fees 2018 (indicated by local
authority survey – 63 responses) ..................................................................................... 56
Table 38: Key influencing factors – future energy recovery gate fees 2018 (indicated by local
authority survey – 65 responses) ..................................................................................... 57
Table 39: Landfill gate fees reported by local authorities, broken down by nations and regions
within England (£/tonne) ................................................................................................ 59
Table 40: Landfill contract lengths (for which contract length data was submitted) .............. 62
Table 41: Factors influencing current landfill gate fees (indicated by local authorities – 68
responses) ..................................................................................................................... 64
Table 42: Factors most likely to influence future landfill gate fees (indicated by local
authorities – 70 responses) ............................................................................................. 64
Figures Figure 1: Reasons given for local authorities not supplying gate fee data ............................ 24
Figure 2: UK MRF gate fees reported by local authorities over time, 2008 to 2018 (£/tonne) . 27
Figure 3: MRF gate fees reported by local authorities by nation and London (2018 in £/tonne)
..................................................................................................................................... 28
Figure 4: MRF gate fees reported by local authorities by English region (2018 in £/tonne) .... 29
Figure 5: Selling prices of key recyclates January 2016 to December 2018 (where January
2015 price = 100) Source: WRAP Materials Pricing Report ................................................. 32
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WRAP – Comparing the costs of alternative waste treatment options
Figure 6: IVC gate fees reported by local authorities by material stream (£/tonne) ............... 36
Figure 7: IVC gate fees reported by local authorities over time by material stream ............... 38
Figure 8: AD gate fees reported by local authorities over time for the whole of the UK
(£/tonne) ....................................................................................................................... 46
Figure 9: Impact of contract start date on AD gate fees reported by local authorities (£/tonne)
..................................................................................................................................... 48
Figure 10: Pre-2000 EfW gate fees reported by local authorities over time 2009-2018 (UK,
£/tonne) ........................................................................................................................ 54
Figure 11: Post-2000 EfW gate fees reported by local authorities over time 2010-2018 (UK,
£/tonne) ........................................................................................................................ 54
Figure 12: Landfill gate fees reported by local authorities over the time for the whole UK
(£/tonne) ....................................................................................................................... 58
Figure 13: Landfill gate fees over time reported by local authorities by nation (£/tonne) ....... 61
Figure 14: Impact of landfill contract lengths on gate fees (£/tonne) .................................. 63
Figure 15: Impact of contract start date on gate fees (£/tonne) ......................................... 63
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WRAP – Comparing the costs of alternative waste treatment options
Glossary
AD Anaerobic Digestion
C&I Commercial and Industrial
C&D Construction and Demolition
Dirty MRF Residual Waste MRF
EfW Energy from Waste
HWRC Household Waste Recycling Centre
IVC In-Vessel Composting
MBT Mechanical Biological Treatment
MHT Mechanical Heat Treatment
MRF Materials Recovery Facility
OAW Open-Air Windrow
PFI Private Finance Initiative
SRF Solid Recovered Fuel
RDF Refuse Derived Fuel
WCA Waste Collection Authority
WDA Waste Disposal Authority
WRA Wood Recyclers Association
Acknowledgements
Our thanks to all of the local authorities who took time to contribute to this survey, and all of
the waste management companies and individuals who generously provided information or
agreed to be interviewed. In addition, our thanks to the Renewable Energies Association
(REA), Anaerobic Digestion & Bioresources Association (ADBA) and the Chartered Institution
of Wastes Management (CIWM) for their help in promoting this survey.
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WRAP – Comparing the costs of alternative waste treatment options
1.0 Introduction
This report contains the findings of WRAP’s twelfth annual gate fees survey. It summarises the
gate fees charged to local authorities for a range of waste treatment, recovery and disposal
options. The report also looks at the factors likely to influence future gate fees and includes
comparisons to the previous year’s results.
The aim of the gate fees survey is to increase price transparency and, by improving the flow
of information, improve efficiency in the waste management market. A lack of market
information can reduce a local authority’s ability to make informed decisions on waste
management options. Therefore, the publication of indicative gate fee information, such as
that contained within this report, should assist local authorities in making better informed
decisions regarding waste management options. The year-on-year changes in gate fees are
also valuable in informing the changes in the state of the market for different ways of
managing waste.
The objectives of this year’s survey were as follows:
◼ To capture the variation in gate fees by treatment/disposal option, by surveying local
authorities that procure waste disposal services and service providers including Waste
Management Companies (WMCs) and operators of organic treatment facilities;
◼ To encompass a broad regional distribution of gate fees for facilities across England
(including London as a separate region, and where possible, to carry out analysis on a
regional basis within England), Wales and Northern Ireland; and
◼ To assess market trends via a comparison of gate fees over time.
This report presents a review of gate fees for a range of options for the treatment and
disposal of waste, together with a forward looking analysis of the factors likely to influence
future gate fees.
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WRAP – Comparing the costs of alternative waste treatment options
2.0 Approach & Scope of this study
This survey compiles information regarding gate fees charged in 2018 for a variety of waste
management services. The geographic scope covers the whole of the UK with the sub regional
data by English region where sample size allows.
Requests for gate fee information were issued to local authorities, including all Unitary
Authorities, Waste Disposal Authorities (WDAs), and Waste Collection Authorities (WCAs)
within the UK. The waste management services included in the local authority survey
questionnaire were:
◼ Materials Recovery Facilities (MRF);
◼ In-Vessel Composting (IVC);
◼ Anaerobic Digestion (AD);
◼ Energy from Waste (EfW);
◼ Non-hazardous landfill.
Separate requests for information were also distributed to waste management operators in the
following sectors:
◼ In-Vessel Composting;
◼ Anaerobic Digestion.
This involved another online survey, which included questions relating to both gate fees
relating to waste supplied from municipal sources (i.e. local authority services) and
commercial and industrial sources. The results of the latter have been reported in the
separate Commercial waste gate fees report .
In addition to the above, telephone or face-to-face interviews were held with representatives
of major waste management companies. These interviews were flexible in their scope, in that
they addressed all major waste service types offered by the company in question.
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WRAP – Comparing the costs of alternative waste treatment options
3.0 Survey response rates
3.1 Local Authorities
A summary of response rates by authority type and the gate fee data by facility type that have
been secured by this year’s survey are shown in Table 7 below. For comparison purposes the
same data reported in last year’s survey are shown in Table 8.
Table 7: Local authority response rates 2018
England Scotland Wales NI UK
WDA WCA Unitary London Unitary Total
No. of Local
Authorities 32 230 91 37 32 22 11 418
No. of emails sent
out 118 448 239
113 80 64 35 912
No. of Local
Authorities
responding
27
(84%)
86
(37%)
61
(67%)
21
(57%)
20
(63%)
16
(73%)
11
(100%)
221
(53%)
No. responding
with usable gate
fee(s)
12
(38%)
21
(9%)
42
(45%)
10
(27%)
15
(47%)
13
(59%)
9
(82%)
112
(27%)
No. of LAs that provided gate fee data for the following facilities:
MRFs 86 (21%)
IVC 36 (9%)
AD 44 (11%)
EfW (Incineration with Energy
Recovery)
62 (15%)
Landfill 61 (15%)
Response rates were higher than last year, from 213 to 221 local authorities overall, due to
regular emails and phone calls. The number of unitary authority respondents in England
increased from 55 to 61, as well as for WDAs from 23 to 27, with a slight decrease in WCAs
from 87 to 86. In London the number of respondents also showed an increase from 14 to 21.
Responses from authorities in Wales, Scotland and Northern Ireland (100% of authorities
represented) remained very similar, with a decrease by one for Wales.
Of WCA respondents, 55% completed the survey themselves, whereas the remaining 45%
deferred to the relevant WDA. The total response rate in England increased from to 165
(47%) to 174 (49%).
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WRAP – Comparing the costs of alternative waste treatment options
This year 27% of local authorities responded with usable gate fees in comparison to last year’s
31%. Around 50% of the authorities who responded to the survey responded with gate fees,
which is down from 60% last year.
Table 8: Local authority response rates 2017
England Scotland Wales NI UK
WDA WCA Unitary London Unitary Total
No. of
Local
Authorities
32 230 91 37 32 22 11 418
No. of
emails sent
out
132 535 287
99
82 64 56 1,139
No. of
Local
Authorities
responding
23
(72%)
87
(38%)
55
(60%)
14
(38%) 20 (63%)
17
(77%)
11
(100%)
213
(51%)
No.
responding
with usable
gate fee(s)
23
(72%)
26
(11%)
39
(43%) 8 (22%) 18 (56%)
13
(59%)
10
(91%)
129
(31%)
No. of LAs that provided gate fee data for the following facilities:
MRFs 94 (22%)
IVC 42 (10%)
AD 38 (9%)
EfW (Incineration with
Energy Recovery)
55 (13%)
Landfill 58 (14%)
The sample size of local authorities has increased this year from 213 to 221, the response rate
still remains high with over 53% of local authorities completing the survey. The mix of
responding local authorities was also different from last year. This difference in sample is
common for this survey. For instance, of the 221 local authorities responding in 2018, 155
also responded to the 2017 survey (70%), but 66 did not, meaning they are unique
respondents to the 2018 survey. This difference in samples needs to be considered when
comparing the 2017 survey to those reported last year.
3.2 Reasons for not supplying gate fee data
Every year there are a number of local authorities contacted that say they cannot supply gate
fee data for a number of reasons. This year these reasons were captured as part of the survey
and are presented within Table 9.
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WRAP – Comparing the costs of alternative waste treatment options
Table 9: Reasons given by local authorities not supplying gate fee data (count of responses,
2018 survey)
Survey
Section
Unknown
- part of
an
integrated
contract
Contractually
obliged not
to divulge
Contractor
says data is
confidential
WDA
holds
the
data
No gate
fee -
use In-
house
facilities
No of
Responses
with no
gate fee
data
MRF 25 15 9 1 5 30
AD 8 3 2 2 1 30
IVC 5 5 2 2 0 28
EfW 18 12 5 1
46
Landfill 18 10 3 0 2 42
Total 74 45 21 6 8 154
Note that not all local authorities that did not supply gate fee data provided a reason for not
doing so. Overall results are presented in Figure 1.
Figure 1: Reasons given for local authorities not supplying gate fee data
Although data confidentiality was an issue with around a third of those respondents providing
a reason, 52% of those not providing gate fees did so because they did not have access to
gate fee data per waste management service type, either because they paid a single price for
an integrated contract, or because this information was held by their waste disposal authority
(WDA). Only 1 out of all respondents said that they were unwilling to provide data as it was
being collected by a third-party contractor to WRAP.
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WRAP – Comparing the costs of alternative waste treatment options
Additionally, this year the question was posed as to whether the WRAP gate fees survey was
useful or not to local authorities. The majority of respondents did find the survey useful with
61% opting for ‘Yes’ with only 10% ‘No’. The remaining 29% of respondents left this question
blank.
3.3 Organic operators survey
Although the overall number of respondents for both IVC and AD was higher than last year,
the number who has provided useable gate fees has decreased by 2 for IVC. However, it has
remained the same for AD. The total number of usable gate fees for both has also decreased
since last year. This was despite the support of the REA, ADBA and CIWM in promoting the
survey with their members, along with emailed and telephoned chase up. The response rates
of the organic operators’ survey are shown in Table 10.
Table 10: IVC and AD facility operator response rates 2018
IVC AD
No. of operators contacted in relation to
each type of facility 105 142
Total No. of responses (and % operators
that responded) 11 (11%) 19 (13%)
Total No. with usable gate fees (and %
operators that responded) 9 (9%) 12 (11%)
The response rates achieved by this year’s survey compared with previous years are shown in
Table 11 below.
Table 11: Composting and AD facility operator response rates and (responses with usable
gate fees) by survey year
Survey Year IVC AD
2018 11 (9) 19 (12)
2017 12 (11) 16 (9)
2016 13 (11) 15 (12)
2015 17 (11) 23 (9)
2014/15 14 (14) 12 (12)
2013/14 20 (17) 32 (10)
2012/13 10 (10) 14 (11)
2011/12 10 (7) 11 (9)
2010/11 9 3
2009/10 7 n/a
2008/09 13 n/a
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WRAP – Comparing the costs of alternative waste treatment options
3.4 Interviews with waste management companies
Interviews were conducted at a senior level with 3 large waste management companies to
test the draft conclusions from the local authority and operators’ surveys. The interviews with
these companies were timetabled such that the initial gate fee findings of this year’s surveys
could be discussed. Discussions were open in scope, potentially including all aspects of the
market that were relevant to gate fees in the UK.
Additionally, AD and MRF operators were being interviewed specifically on commercial gate
fees and relevant information from these interviews were also fed into the conclusions of this
report. The scope of these conversations was in relation to their specific markets.
4.0 Results and analysis
As with previous years, analysis of the cleaned survey data focussed upon generation of:
◼ Median gate fee i.e. the value in the midpoint of the distribution of gate fee data collected,
with an equal probability of falling above or below it;
◼ Gate fee range i.e. the range between the minimum and maximum values obtained in the
survey.
The mode has also been calculated for a fourth year, due to the problems of interpreting the
sometimes large range between minimum and maximum figures collected. In this case, mode
is the gate fee range (in £5 increments) which received the most responses in the survey
data. Note that the median gate fee does not always reside within the mode range.
4.1 Materials Recovery Facilities (MRFs)
To make the reported data compatible and comparable to that published in previous years,
only gate fees for mixed recyclate streams of 4 materials or more have been included in the
following analysis.
Of a total of 174 responses from 147 local authorities, 13 were rejected as streams containing
less than 4 materials, 14 where no material information was provided and 2 for other reasons.
Of those 144 acceptable responses (from 125 local authorities: 93 in England, 15 in Scotland,
8 in Wales and 9 in Northern Ireland), 91 included usable gate fee data upon which the
following analysis was based. Of those not reporting gate fees and providing an explanation,
16 local authorities reported that MRF gate fee could not be extracted from fees for integrated
contracts, 11 explained that they were contractually obliged not to provide gate fees to third
parties and 6 reported that their contractor has asked for gate fees not to be provided. Of the
remaining 14 local authorities that supplied other explanations, most operated their own MRFs
so did not pay a relevant gate fee for access.
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WRAP – Comparing the costs of alternative waste treatment options
4.1.1 Current gate fees and trends The high-level results from the survey are given in Table 12. The median MRF gate fee (for
MRF contracts which sort 4 materials or more) in the current survey is £25/tonne from 91
responses reported by local authorities, with a range of responses between -£41/tonne (i.e. an
income) and £97/tonne.
Table 12: MRF gate fees reported by local authority by nation and London (2018) (£/tonne)
The median gate fee is more than the £22 reported last year for the UK as a whole,
suggesting another year on year hardening in gate fees. Figure 2 charts the median MRF gate
fee over time from the 2008 survey, plus min-max ranges.
Figure 2: UK MRF gate fees reported by local authorities over time, 2008 to 2018 (£/tonne)
In last year’s survey, 14 local authorities (16% of those responding with gate fees) reported
not paying a gate fee for or earning an income from MRF services, i.e. a zero or negative gate
fee. In 2016 this was 20 authorities, 21% of those responding; in 2015 30 authorities 28% of
those responding; and 2014 this was 38 authorities, 46% of those responding. This year this
number is 15 local authorities (12% of those responding) showing a further decline, with 1
authority paying a zero gate fee and 14 authorities a negative gate fee (i.e. receiving an
Country/Region Median Mode Range Number of gate fees
UK £25 £5 to
£10 -£41 to £97 91
England (incl.
London) £17 £0 to £5 -£41 to £82 63
London £18 £5 to
£10 -£2 to £38 11
Wales £49 £80 to
£85 -£2 to £81 7
Northern Ireland £39 £35 to
£40 £32 to £70 12
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WRAP – Comparing the costs of alternative waste treatment options
income). Of these, the majority are short term contracts (=<7 years, median 6 years) that
started between 2013 and 2016.
The single price range with the most gate fees is £5 to £10/tonne (i.e. the mode, compared
to £0 to £5/tonne last year); the full range of responses was from -£41 to £97, similar to last
year. Reported gate fees are influenced by a wide range of factors including material mix,
contract length and age, contractual pricing mechanism, annual tonnage, MRF technology
employed, and the degree of risk share between the authority and contractor.
Of those local authorities reporting gate fees, 69% (last year 64%) report a change in gate
fee during 2018. In addition, 33% of respondents report receiving revenue directly associated
with the sale of materials sorted by the MRF. This income has been taken into account in the
calculation of the reported median (and mode)gate fees.
Regarding input specification, 70% of respondents reported contamination limits of between
5% and 30% by weight, with most between 5% and 10% (median 10%).
Analysing median gate fee and gate fee range per UK nation (plus London) shows Wales and
Northern Ireland experiencing higher median gate fees and minimum gate fees than England,
potentially due to relative market size. This corroborates trends seen in previous years.
Median gate fee and range per nation are shown in Figure 3.
Figure 3: MRF gate fees reported by local authorities by nation and London (2018 in
£/tonne)
To this end, gate fees in England only were increased compared to last year at £17/tonne
(£13/tonne last year), whereas reductions were noted in Wales at £49/tonne (£52/tonne last
year) and Northern Ireland £39/tonne (£43/tonne last year).
Low response rates in some regions mean that direct comparisons between English regions
are difficult. The data collected does show peaks in gate fee in the South East in particular,
with median gate fee in London decreasing significantly from last year (£18 from 11 responses
29
WRAP – Comparing the costs of alternative waste treatment options
v. £43 from 8 responses last year). Median gate fees and ranges per English region are shown
in Figure 4.
Figure 4: MRF gate fees reported by local authorities by English region (2018 in £/tonne)
4.1.2 Gate fee by contract year
Of the 137 responses received, 119 (87%) report being under contract for MRF services,
similar to last year. The data received from local authorities includes a considerable amount of
historic (long term contract) data which does not necessarily reflect current market conditions.
Median gate fees were therefore determined for each contract start year, from which trends
could be identified. This shows an increasing trend in median gate fees for each contract start
year from 2014. New contracts reported this year had a median gate fee of £35 (from 18
contracts). Contract length also shows a considerable decrease depending upon the year the
contract started, from 19 years for contracts signed before 2014, to 2 years for contracts
started in 2018. Results are summarised in Table 13.
Table 13: MRF gate fee reported by local authorities by contract start year (2014 to 2018,
from 2018 data £/tonne)
Contract start year Median Mode Range
No of
contracts
started
Median
contract
length
2018 £35 35-40 -3 - 60 18 2
2017 £23 No mode11 -18 - 60 7 2
2016 £36 45-50 -10 - 70 24 3
11 i.e. no gate fee range attracted more responses than any other
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2015 £9 5-10 -10 - 82 8 5
2014 £8 5-10 -6 - 40 11 6
Before 2014 £24 5-10 -5 - 51 37 19
Of the 129 authorities supplying responses to this question, 89 (69%) reported a change in
gate fee in 2018 (64% in 2017), with 12 (19 in 2017) reporting a decrease (mostly due to new
contract negotiation or commodity price tracking) and 49 (39 in 2017) an increase in gate fees
(mostly due to indexation and commodity price tracking), again suggesting an increase in
gate fees between 2017 and 2018. Of those reporting a change in gate fee and providing a
reason, 9 (11%) report the signing of a new contract12, 13 (15%) report fee change as result
of a regular contractual review, 31 (36%) changes in commodity prices (with an additional 13
(15%) as part of a contractual monthly or quarterly review giving a total of 51%), 5 (6%) a
change in the level of contamination, and 25 (29%) contractual RPI increases. These results
are summarised in Table 14.
Table 14: Changes in MRF gate fees reported by local authorities in 2018 with reasons
4.1.3 Contract review
Reported contract length covers a wide range, although almost half (49% of responses) are
short term, i.e. 5 years or less, with 25% between 6 and 10 years. These are very similar
results to those obtained in 2017. Nevertheless, there are some long-term contracts reported
with 18% of responses giving contract lengths over 20 years.
12 Not all of the local authorities reporting a new contract responded to this question, hence the difference in new contract figures between table 13 and table 14
Change in Gate Fee
in 2018 Responses Reason Responses
Yes 89 (69%)
New contract 9 (11%)
Contract review 13 (15%)
Commodity Price Change 31 (36%)
Change in level of
contamination 5 (6%)
Regular contractual price
review (monthly or
quarterly)
13 (15%)
RPI 25 (29%)
No 40 (31%)
Total 129 85
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Table 15: MRF contract length
(2018)Contract length (years) Count Proportion of count
1 7 6%
2 14 12%
3 22 19%
4 6 5%
5 7 6%
6 6 5%
7 8 7%
8 4 4%
9 1 1%
10 9 8%
12 1 1%
14 2 2%
15 3 3%
18 1 1%
19 1 1%
20 2 2%
23 1 1%
24 2 2%
25 12 11%
>25 5 4%
Note: percentages do not add to 100% due to rounding.
4.1.4 Materials collected and sorted
Respondents reported the materials collected and sent to MRFs for sorting. Almost all report
the collection of key recyclates such as cans, plastic bottles, card and paper. This mirrors the
results obtained in last year’s survey. Of those responding, 70% report collecting glass in their
comingled collections. These results are summarised in Table 16.
The key driver in MRF gate fees, as evidenced in the last 3 to 4 years of gate fee surveys, has
been variability in the value of recyclates, and the need for contractors to reduce their
exposure to this risk. For instance, in 2017 some materials showed annual price increases,
such as +63% for mixed cans and +25% for plastic bottles from 2016 lows, with plastics and
card showing decreases over the same period. In 2018, the impact of the China Sword
initiative pushed reductions in price particularly for fibres (e.g. card -24%) and plastics (e.g.
mixed plastics -36%). This unpredictable variability has increased the number of contracts
which exercise some form of price review mechanism (in some cases as often as weekly or
monthly) based upon a basket of commodity materials pricing. For instance, in 2018, 51% of
reported contracts included such a mechanism, compared to 37% in 2017 and 29% in 2016.
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Table 16: Range and frequency of materials being sorted at MRFs reported by local
authorities in 2018, with material prices changes in December 2018 per key recyclate
material (as %)
Material Number of times
material is cited as
part of MRF gate
fee
% of
responses
Materials
price change
20181
Cans 91 99% -14%2
Plastic bottles 88 96% +7%3
Card (exc. drinks cartons) 83 90% -23%4
Paper 82 89% -3%5
Aerosols 77 84%
Drinks cartons e.g. Tetrapak 74 80%
Plastic: non-bottle rigids 66 72% 0%7
Foil 65 71%
Glass 64 70% 0%6
Plastic other 29 32% -36%8
Plastic film 27 29% -23%9
Other 9 10% Key:
1 source of data: WRAP Materials Pricing Report, comparing
first week Dec 2017 to first week Dec 2018
2 As mixed cans
3 As clear PET
4 As mixed paper & board
5 As News & PAMS
6 As clear glass
7 As mixed rigids
8 As mixed polymers
9 As LDPE film
Plotting WRAP sourced key recyclate prices from January 2016 to December 2018 (as in Figure 5) illustrates a variety of changes, with significant changes, for instance, in the price of card over this period.
Figure 5: Selling prices of key recyclates January 2016 to December 2018 (where January
2015 price = 100) Source: WRAP Materials Pricing Report
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4.1.5 Key influencing factors
As part of the survey, local authority officers were asked to select, from pre-defined lists, up
to three factors that they felt were important in influencing current and future gate fees
(respondents could select ‘other’ if they wished to add additional comments not covered in the
lists). All percentages quoted here are based on the total number of local authorities that
responded to these questions.
Of factors influencing gate fees, commodity prices, input material quality and operating costs
are deemed those having most impact on gate fees now and in the future, the same as in last
year’s survey. Note that more respondents (31 v 11) expected legislative requirements to have
an impact in future prices than they do now. Of the 117 respondents expressing an opinion,
97 (83% v 84% last year) expect gate fees to increase in the future. Results are summarised
in Table 17 and Table 18 following.
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Table 17: Key influencing factors – current MRF pricing (indicated by 2018 local authority
survey – 112 respondents)
Factor influencing current gate fees No. of responses %
Product/commodity end market prices 91 81%
Quality of input materials 69 62%
Operating costs 52 46%
Cost of managing residues 21 19%
Inflation (RPI, RPIX) 18 16%
Competition between similar facilities 16 14%
Complying with the MRF Code of Practice 15 13%
Contractual changes, other than inflation increase 12 11%
Legislative requirements 11 10%
Availability of capacity 10 9%
Other 9 8%
Investment/capital costs 3 3%
Competition from alternative treatment options 2 2%
Government incentive schemes e.g. renewables 1 1%
Table 18: Key influencing factors – future MRF pricing (indicated by 2018 local authority
survey – 118 respondents)
Factor influencing future gate fees No. of
responses %
Product/commodity end market prices 98 83%
Quality of input materials 78 66%
Operating costs 42 36%
Legislative requirements 31 26%
Competition between similar facilities 22 19%
Cost of managing residues 22 19%
Availability of capacity 13 11%
Complying with the MRF Code of Practice 10 8%
Other 10 8%
Investment/capital costs 9 8%
Government incentive schemes e.g. renewables 7 6%
Inflation (RPI, RPIX) 5 4%
Competition from alternative treatment options 3 3%
Contractual changes, other than inflation increase 0 0%
“Other” responses included Brexit, and lack of local markets for key materials such as plastics.
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4.1.6 Waste contractor interviews
In interviews with waste contractors last year, the Chinese import restrictions were starting to
bite, and gate fees of up to £45-£50/tonne were reported. Interviews with contractors this
year confirmed a number of factors evident from the survey results:
◼ That gate fees to local authorities in general are continuing to increase;
◼ The market is moving much more to a fixed gate fee plus commodity price adjustments to
minimise the risk to the operator;
◼ That contracting is getting more sophisticated with a trend to separate MRF processing
and commodity sales requirements managed in separate contracts;
◼ That the market is moving much more to price review on a monthly, 3 monthly or 6
monthly basis to take into account fluctuations in commodity prices; and
◼ That contamination is a particular issue and contracted contamination limits are reducing
as operators try to secure new markets and prices for the recyclates they generate.
Waste contractors expected that commodity price volatility will continue through 2019 before
finally stabilising in 2020.
Overall the view was that reported gate fees for new contracts were up to £45-55/tonne by
the end of 2018 and beginning of 2019, significantly higher than the averaged figures
reported by the survey.
4.2 In-Vessel Composting
A total of 68 responses from 61 local authorities, 4 were rejected due to inclusion of transport
costs. Of the 64 acceptable responses, 39 included 52 usable gate fees which are included in
the analysis.
Of the responses which did not include gate fees, 6 said the gate fee was part of an
integrated contract, 5 were contractually obliged to not share gate fees, 2 stated that the
contractor said the gate fees should be regarded as confidential, and 4 provided various other
reasons such as that the contract was managed by the disposal authority.
4.2.1 Current gate fees and trends
The median for all types of feedstock being sent to IVC facilities is £46/tonne, which is the
same gate fee as reported last year. However, it is perhaps more meaningful to consider the
gate fees by feedstock type, which can be seen in Table 19 and Figure 6. The median gate
fee for mixed food and green waste, the most common feedstock type sent to IVC facilities,
has increased by £1/tonne since last year, to £50/tonne compared to £49/tonne.
Table 19: IVC gate fees provided by local authorities by waste material type (£/tonne)
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Waste Type Median Mode Range Responses
All materials
(UK) £46 £55 to £60 £10 to £73 52
Mixed food &
green waste £50 £50 to £55 £28 to £67 28
Food waste
only £61 £60 to £65 £30 to £73 7
Green waste
only £33 £40 to £45 £20 to £64 15
No median figures were generated for other waste streams such as mixed green waste and
card, and for each of ‘mixed food, green and card waste’, only one response for the first was
received. The lack of responses for these material types has been sustained over three years
now, and so may justify a rationalisation of the survey to minimise the number of material
types included.
Of the feedstocks able to be reported, food waste is the most expensive at £61/tonne,
followed by mixed food and green waste at £50/tonne, and £33/tonne for green waste. For
most material types, the median falls within the mode range, with the exception of green
waste. The median for all materials does also not fall within the modal range, which is
expected as the markets for each material type can vary; as food waste gate fee will be
influenced by the local availability of anaerobic digestion capacity, and green waste on
availability of local open air windrow (OAW) capacity.
Figure 6: IVC gate fees reported by local authorities by material stream (£/tonne)
Figure 7 shows how the gate fees for the three types of reported feedstock have changed
since 2009/10. The following changes can be seen:
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WRAP – Comparing the costs of alternative waste treatment options
◼ The median gate fee for IVC using mixed food and green waste is £50/tonne, which is an
increase on the last few years, which have stayed at around £46-47/tonne prior to 2017.
The range has however remained relatively stable at the lower end for the last year, but
has seen increases at the top end over the last few years, from £28 to £63/tonne last year,
to £28 to £67/tonne this year.
◼ The median for food waste is the same as last year, at £61/tonne. Gate fees for this
material type had seen significant increases prior to this year, increasing from £45/tonne in
2015. Three of the seven responses for food waste feedstocks were from Scotland, where
the market is significantly different to the rest of the UK, partially due to the Waste
(Scotland) Regulations 2012 boosting food waste collections. The range in gate fees has
reduced this year, with the minimum increasing from £18 to £30/tonne, with the upper
range remaining the same at £73/tonne.
◼ The median for green waste only has increased from £31/tonne to £33/tonne. Although
an increase, the gate fees are not as high as in 2014/15 and 2015/16. OAW has not been
surveyed and so it is difficult to compare, but this is higher than the last median gate fee
for green waste reported in 2015/16 of £24/tonne. However, the range is fairly wide and
indicates reasonable variation.
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Figure 7: IVC gate fees reported by local authorities over time by material stream
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For mixed green and food waste, in England the gate fees have remained relatively stable,
having increased by only £1/tonne from £49 to £50/tonne (range £28 to £67/tonne). Last year,
there was insufficient data to be able to report IVC gate fees in Wales, and this year, slightly
smaller sample sizes were seen for both London and Northern Ireland as well.
The median for Northern Ireland seems to have increased from £49 last year to £58/tonne this
year. However, it is likely this is a reflection of the authorities who provided gate fees compared
to last year rather than significant market changes. The number of contracts in Northern Ireland
is also relatively small, as treatment contracts are managed on authorities’ behalf by waste
management groups such as arc21.
The median for London is £51/tonne compared to £55/tonne last year. As per last year, it
remains higher, but only slightly, than the English median.
4.2.2 Contract review
Of those providing data, 72% of the authorities report sending material to an IVC facility under a
contract, while 14% said they are not using a contract at present; 14% of the authorities did not
provide a response. This is over a 10% decrease in authorities using contracts, from 83% last
year.
Of those under contract, 80% provided start and end dates, which has allowed for calculation of
the contract length. Table 20 demonstrates that 54% of the contract gate fees are associated
with contracts of a duration of 5 years or less, 62% were for a duration of 10 years or less, and
5% of contracts are over 25 years.
Table 20: IVC contract lengths (for which contract length was submitted)
Contract Length (years) Number of contracts
No. %
1 1 3%
2 5 14%
3 5 14%
4 4 11%
5 5 14%
7 1 3%
9 1 3%
10 1 3%
11 1 3%
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Contract Length (years) Number of contracts
No. %
12 1 3%
15 8 22%
17 1 3%
24 1 3%
>25 2 5%
Total 37 100%
Table 21 shows that gate fees for new contracts seem to have been increasing since 2015, after
a drop from years prior to that. However, it should be noted that these contracts take into
account various types of feedstock and across the whole UK, and sample sizes are small and so
significant trends cannot be claimed.
Table 21: IVC gate fees based on contract start year (£/tonne)
Contract start
year Median No of contracts started
2018 £46 4
2017 £45 9
2016 £38 4
2015 £30 2
2014 £48 4
Before 2013 £53 15
Approximately 37% of the authorities said that their gate fees had changed in the last 12
months, with 86% (of those who gave us data) being increases, and the vast majority citing
inflation/indexation as the reason.
4.2.3 Key influencing factors
Table 22 shows that over 55% of the local authority respondents think that operating costs is by
far the most influential factor on their current gate fees. Inflation is next at 41%, with both
quality of input materials and availability of capacity in joint third with approximately a third of
respondents believing that these are the most influential.
Table 22: Factors influencing current IVC gate fees (indicated by local authority survey – 44
respondents)
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Factor influencing current gate
fees
Response Rates
No. %
Operating costs 24 55%
Inflation (RPI, RPIX) 18 41%
Availability of capacity 14 32%
Quality of input materials 14 32%
Competition between similar facilities 11 25%
Legislative requirements 10 23%
Competition from alternative treatment
options 7 16%
Product/commodity end market prices 6 14%
Contractual changes, other than
inflation increase 4 9%
Investment/capital costs 4 9%
Cost of managing residues 3 7%
Government incentive schemes e.g.
renewables 2 5%
Other 2 5%
Operating costs is also identified by local authorities as being most likely to influence gate fees in
the future (see Table 23), followed by competition between similar facilities and availability of
capacity. This is the same ranking as last year.
Table 23: Factors most likely to influence future IVC gate fees (indicated by local authority
survey – 43 responses)
Factor influencing future gate
fees
Response Rates
No. %
Operating costs 18 42%
Competition between similar facilities 17 40%
Availability of capacity 14 33%
Inflation (RPI, RPIX) 14 33%
Legislative requirements 13 30%
Quality of input materials 11 26%
Competition from alternative
treatment options 8 19%
Product/commodity end market prices 8 19%
Contractual changes, other than
inflation increase 5 12%
Cost of managing residues 5 12%
Investment/capital costs 3 7%
Other 1 2%
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Factor influencing future gate
fees
Response Rates
No. %
Government incentive schemes e.g.
renewables 0 0%
Of the 43 local authorities expressing an opinion, 65% think that gate fees will increase in the
future, compared to 28% that think they will stay the same and just 7% that they will decrease.
4.2.4 Survey of IVC operators
A total of 11 responses were received from IVC operators, providing 65 usable gate fees (including
both contract and spot market gate fees, for both municipal and commercial waste sources). Of
these, 49 were municipal gate fees. Details of the commercial waste gate fees can be found in the
Commercial waste gate fee report.
Table 24 shows the municipal gate fees provided by the operator’s survey. The median of
£35/tonne for all feedstock types under contract is £8/tonne lower than the £43/tonne reported
last year, and £11/tonne lower than that reported by local authorities. Less substantial changes
since last year’s operator figures are seen in specific feedstock types and so it is thought that this
result is likely to be due to the specific sample rather than reflective of particular market changes.
For example:
◼ Mixed food and green (contract): operators cited a median of £48/tonne which is a little lower than
the £50/tonne reported last year, and the £50/tonne median cited by local authorities this year,
but broadly aligns with the conclusion of a stable market.
◼ Food waste (contract): the operator’s median is £45/tonne compared to £44 last year. However,
this is significantly lower than that reported by local authorities which was £61/tonne.
◼ Green waste (contract): the operators reported a median of £26/tonne this year, a £1/tonne
decrease on last year. Local authorities reported a higher median of £33/tonne.
Table 24: Contract and spot IVC gate fees, for municipal waste, provided by facility operators
(£/tonne)
Feedstock No. of gate
fees
Gate fee (£/tonne)
Median Range
CONTRACT GATE FEES
All waste streams 40 £35 £9 to £65
Mixed food & green waste 16 £48 £27 to £65
Food waste only 9 £45 £31 to £55
Green waste only 15 £26 £9 to £35
SPOT MARKET GATE FEES
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Feedstock No. of gate
fees
Gate fee (£/tonne)
Median Range
All waste streams 9 £45 £45 to £48
Mixed food & green waste 6 £47 Not reported
Food waste only 0 No data No data
Green waste only 3 £45 No data
The major differences between local authority and operator figures are for the separately collected
materials. We know these markets to be more influenced by region, due to different policies on
organic collections, and greater demand and capacity availability. The majority of data from the
operator survey came from IVC facilities in England (i.e. 9 out of 11). This may explain why for
example food waste gate fees are lower than reported by local authorities, as policies in Wales and
Scotland for example are in place to encourage separate collection of food from green waste,
therefore creating greater demand for food waste treatment capacity.
4.2.5 Key influencing factors – operators
The key factor influencing current gate fees cited by operators was operating costs (see Table 25).
Competition from similar facilities, competition from alternative options and ‘other’ were all cited as
joint second most influential factors, with a third of respondents giving these as influential factors.
Inflation was rated the second most influential factor last year but has not been considered as
influential as last year, with only one respondent citing this. This does not correspond with local
authority responses which suggested this was one of the most influential factors on gate fees this
year.
Table 25: Factors influencing current IVC gate fees (indicated by IVC operators surveyed – 9
responses)
Factor influencing current gate fees Response rates
No. %
Operating costs 5 56%
Competition from similar facilities 3 33%
Competition from alternative treatment options 3 33%
Other 3 33%
Availability of capacity 2 22%
Legislative requirements 2 22%
Cost of managing residues 2 22%
Quantity of input materials 1 11%
Inflation (RPI, RPIX) 1 11%
Product/commodity end market prices 0 0%
Investment/capital costs 0 0%
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Factor influencing current gate fees Response rates
No. %
Government incentive schemes e.g. renewables 0 0%
Table 26 shows that IVC operators expect that operating costs are most likely to influence future
gate fees. Competition from both alternative treatment options and similar facilities were ranked
next important.
Table 26: Factors most likely to influence future IVC gate fees (indicated by IVC operators
surveyed – 9 responses)
Factor influencing future gate fees Response rates
No. %
Operating costs 6 67%
Competition from alternative treatment options 5 56%
Competition from similar facilities 4 44%
Legislative requirements 2 22%
Quantity of input materials 1 11%
Inflation (RPI, RPIX) 1 11%
Cost of managing residues 1 11%
Government incentive schemes e.g. renewables 1 11%
Availability of capacity 0 0%
Product/commodity end market prices 0 0%
Investment/capital costs 0 0%
Other 0 0%
4.2.6 Waste contractor interviews
The waste contractor interviews suggested that IVC gate fees have remained somewhat stable and
that most changes since last year will have been due to inflation, which does align with responses
from local authorities as there are only slight increases in median gate fees for mixed food and
green waste and separate green waste. However, it should be noted that 23 new contracts have
been signed in the last 3 years and 57% of reported contracts have a term of five years or less,
which suggests there is more turnover in the market than these operator interviews indicate.
Operators also commented that it seems like a declining market, with local authorities moving
from mixed food and green collections to enable diversion of separately collected material to
cheaper treatment options i.e. green waste to OAW and either food waste to AD, or stopping food
waste collections entirely. This is certainly the case in Wales, where authorities have been
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encouraged to align their collections with the Welsh Government Collection Blueprint which
specifies separate food and green waste collections.
4.3 Anaerobic Digestion (AD)
Of a total of 75 responses from 69 local authorities sending waste to anaerobic digestion facilities,
3 were rejected due to inclusion of transport costs. Of the 72 acceptable responses, 47 included
62 usable gate fees which are included in the analysis.
Of the responses which did not include gate fees, 8 said the gate fee was part of an integrated
contract, 3 were contractually obliged to not share gate fees, and 7 provided various other reasons
such as that the contract was managed by the disposal authority or that they operate their own
AD facility and therefore do not pay gate fees.
4.3.1 Current gate fees and trends
Table 27 and Figure 8 show the median AD gate fee is £27/tonne this year, which is slightly higher
than the £26/tonne gate fee in last year’s survey. The range is exactly the same as last year, with
six local authorities citing an income or £0/tonne gate fee for their food waste (twice more than
the three reporting last year).
Table 27: AD gate fees reported by local authorities by nation (and London) (£/tonne)
Median Mode Range Responses
UK £27 £15 to £20 -£5 to £68 62
England (incl.
London) £26 £15 to £20 -£5 to £68 43
Wales £41 £15 to £20 £19 to £64 10
Northern
Ireland Insufficient data Insufficient data Insufficient data 1
London £27 £25 to £30 £0 to £68 8
The median AD gate fee reported over time is summarised in Figure 8. This shows a steep decline
in gate fee in 2015 from a steady £40/tonne to less than £30/tonne. This reflected what waste
contractors and the operators were reporting at the time. This year the gate fee has remained
relatively static at this level with only a £1/tonne rise. The range has also widened over time, and
the fact the median does not fit within the modal range (£15 to £20/tonne) reiterates that there is
wide variability across the UK in AD gate fees.
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This median reported by local authorities is substantially higher than that reported for municipal
waste by the facility operators (£10/tonne); however, the local authority reported median does
contain a significant proportion of historical data, so the operator’s figure is thought more likely to
be an accurate reflection of current market prices, particularly in England.
Figure 8: AD gate fees reported by local authorities over time for the whole of the UK (£/tonne)
For England, the pattern over the last four years has been of steady decline (£35/tonne in
2014/15, £30/tonne in 2015/16, £26/tonne in 2016/17, to £23/tonne last year) until this year,
where data reported by local authorities results in a median of £26/tonne. The range has
remained the same since last year (-£5 to £68/tonne). The modal range is £15 to £10/tonne and
so the median doesn’t fall within range, indicating variability.
The median gate fee in London has increased by £1/tonne since last year, at £27/tonne. This
figure is based on eight gate fees from six local authorities. Information from waste contractors
suggests that this does not reflect the current market in London. Only one of the contracts
reported started in 2018, with a few of the others reported as having started in the last decade,
and therefore this could be a reason the median does not reflect the market as seen by the
industry. It should be noted that there is significant variability, i.e. gate fees as low as £0/tonne
and some as high as £68/tonne.
The median gate fee in Wales has reduced from last year’s £49/tonne to £41/tonne. The range
has shifted upwards slightly from £14 to £62/tonne last year, to £19 to £64/tonne this year. One
authority has made a significant saving since last year by changing contract, and as Wales is a
relatively small sample size, it is likely that this saving has influenced the overall median figure.
Despite this decrease, Wales still has the highest gate fees, which is thought to reflect the fact that
a high proportion of the contracts in Wales are long-term PFI contracts.
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Although there was insufficient data to be able to report figures, for the first time this year, an
authority in Northern Ireland reported as sending separately collected food waste to AD.
Of all the authorities that responded to the question, 52% said that gate fees had not changed in
the last twelve months and 48% said they had. Of those providing data (having said gate fees
had changed), nine responses reported decreases, compared to twelve increases. The decreases
tended to be more substantial (£19/tonne reduction was the largest) and linked to new contracts
and contract extensions, than most of the increases which were smaller and linked to inflation.
4.3.2 Contract review
Of those responding, 79% of the authorities report sending material to an AD facility under a
contract, while 13% said they are not using a contract at present; 8% of the authorities did not
provide a response. This is an increase in those not using contracts since last year (up from 6%).
Of those under contract, 81% of the authorities provided start and end dates, which has allowed
for calculation of the contract length. Table 28 demonstrates that 35% (53% last year) of contract
gate fees are associated with contracts of a duration of 5 years or less, 50% (67% last year) were
for a duration of 10 years or less, and 11% being 25 years long. Compared to last year, contract
lengths represented in this year’s sample seem to proportionally represent longer term contracts,
and so this may also explain an unanticipated rise in the gate fee median.
Table 28: AD contract lengths
Contract Length (years) Number of contracts
No. %
2 5 11%
3 6 13%
4 5 11%
6 2 4%
7 2 4%
8 1 2%
10 2 4%
11 2 4%
12 1 2%
14 2 4%
15 10 22%
18 1 2%
20 2 4%
25 5 11%
Total 46 100%
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Figure 9 shows the impact of contract start dates on AD gate fees. The median figures of
contracts which have started in the last three years have been £20/tonne or below. Combining
the last three years (sample size of 18 authorities), the overall median is £19/tonne, with a range
of -£5 to £50/tonne, and a modal range of £0 to £5/tonne.
2015 shows a much higher median but it should be noted that three of the five contracts started
were in Scotland and Wales, which is probably a reflection of the very different markets in these
countries in comparison in England.
Figure 9: Impact of contract start date on AD gate fees reported by local authorities (£/tonne)
4.3.3 Key influencing factors
Table 29 shows that an overwhelming 82% of local authorities believe that availability of capacity
is the greatest influencing factor on current AD gate fees. This is up from third last year.
Operating costs was ranked second with 75% and then competition between similar facilities with
71%. These three factors were also ranked as the top three last year but competition between
similar facilities ranked first last year.
Table 29: Factors influencing current AD gate fees (indicated by local authorities surveyed – 28
Reponses)
Factor influencing current gate fees Response Rates
No. %
Availability of capacity 23 82%
Operating costs 21 75%
Competition between similar facilities 20 71%
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Factor influencing current gate fees Response Rates
No. %
Product/commodity end market prices 15 54%
Government incentive schemes e.g. renewables 11 39%
Inflation (RPI, RPIX) 11 39%
Legislative requirements 11 39%
Contractual changes, other than inflation increase 8 29%
Quality of input materials 7 25%
Competition from alternative treatment options 5 18%
Investment/capital costs 5 18%
Cost of managing residues 3 11%
Other 2 7%
The same three factors rank in the same order, as being the most influential factors on future gate
fees. All of the authorities responding to this question said they thought availability of capacity
would influence them. Government incentive schemes was the fourth most influential at 70%.
Opinions about what will happen to AD gate fees over the next twelve months are relatively split,
with 45% believing they will stay the same and 41% increase, but only 14% think they will
decrease.
Table 30: Factors most likely to influence future AD gate fees (identified by local authorities –
27 responses)
Factor influencing future gate fees Response Rates
No. %
Availability of capacity 27 100%
Operating costs 22 81%
Competition between similar facilities 20 74%
Government incentive schemes e.g. renewables 19 70%
Legislative requirements 14 52%
Inflation (RPI, RPIX) 10 37%
Product/commodity end market prices 9 33%
Quality of input materials 7 26%
Competition from alternative treatment options 6 22%
Cost of managing residues 6 22%
Contractual changes, other than inflation increase 2 7%
Investment/capital costs 2 7%
Other 1 4%
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4.3.4 Survey of AD operators
Responses were received from 18 AD facility operators at 15 different sites. This is a small sample
of the existing AD facilities in the UK, of which there are around 10013, and therefore the results
cannot claim to be truly representative of the overall UK market. For example, only two of the
sites were based outside of England (in Scotland). From these operators, 214 usable gate fees
were provided, which were spread across different material categories (including food waste
supplied from municipal and commercial sources) and the type of commercial arrangement
entered into, e.g. contract or spot gate fees. Of these, 85 were municipal gate fees. Details of
the commercial waste gate fees can be found in the Commercial waste gate fee report.
Table 31 shows that the median gate fee of all waste streams reported by the operators is
£10/tonne, which is a £3/tonne increase on last year’s figure. It is much lower than the £27/tonne
reported by the local authorities, although this figure of course includes gate fees from contracts
signed some years ago. The operator survey was also dominated by respondents in England,
where lower gate fees are seen compared to Wales and Scotland. There is some differentiation of
waste stream type with the lowest fees for food waste in biobags and the highest for food
preparation waste.
Very few responses (from two operators) were received for spot market gate fees for municipal
waste, and therefore this is not reported separately.
Table 31: Contract and spot AD gate fees, for municipal waste, provided by facility operators
(£/tonne)
Feedstock
No. of
gate
fees
Gate fee (£/tonne)
Median Range
CONTRACT GATE FEES
All waste streams 46 £10 -£5 to £34
Food waste NOT packaged or in PE bags or biobags 4 £9 £7 to £34
Food waste in biobags 12 £7 £2 to £34
Food waste in PE bags 9 £22 £4 to £34
Packaged food waste 12 £10 -£5 to £34
Food preparation waste 9 £25 £0 to £34
13 http://www.biogas-info.co.uk/about/faqs/
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4.3.5 Key influencing factors – operators
Although a small number of responses (from 10 facilities) were received, competition from similar
facilities was identified as the most influential factor on currently gate fees, which was the same
as the two previous years (see
Table 32). Availability of capacity followed as the second most influential. This year, quantity of
input materials has ranked much higher than last year.
Table 32: Factors influencing current AD gate fees (identified by AD operators surveyed – 10
responses)
Factor influencing current gate fees Response rates
No. %
Competition from similar facilities 9 90%
Availability of capacity 8 80%
Quantity of input materials 6 60%
Operating costs 2 20%
Government incentive schemes e.g. renewables 2 20%
Other (please state below) 2 20%
Legislative requirements 0 0%
Competition from alternative treatment options 0 0%
Product/commodity end market prices 0 0%
Inflation (RPI, RPIX) 0 0%
Cost of managing residues 0 0%
Investment/capital costs 0 0%
Table 33 shows that very similar results came from the question about the greatest influence on
future AD gate fees, i.e. that competition and availability of capacity and quantity of input
materials are likely to continue influencing gate fees.
Table 33:Factors most likely to influence future AD gate fees (identified by AD operators
surveyed – 8 responses)
Factor influencing future gate fees Response Rates
No. %
Competition from similar facilities 8 80%
Availability of capacity 7 70%
Quantity of input materials 6 60%
Operating costs 5 50%
Government incentive schemes e.g. renewables 2 20%
Legislative requirements 1 10%
Other (please state below) 1 10%
Competition from alternative treatment options 0 0%
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Factor influencing future gate fees Response Rates
No. %
Product/commodity end market prices 0 0%
Inflation (RPI, RPIX) 0 0%
Cost of managing residues 0 0%
Investment/capital costs 0 0%
Of those responding, 74% of the operators thought that gate fees were going to decrease in the
next twelve months, compared to only 4% that thought they would increase; 22% thought that
gate fees would increase and remain the same.
4.3.6 Waste contractor interviews
As first identified two years ago, market over-capacity (or lack of capture of available
unavoidable food waste as feedstock) in various parts of the UK is driving gate fees down to an
unsustainable level. The slight increase in gate fees reported by local authorities is not reflected
from the interviews with waste contractors, however they also did not report further decreases.
Operators said that typically when pricing for AD, £0/tonne would be the start point. Additional
fees for packaging/contamination levels and consideration of the likely biogas yield would be
taken into account in the final pricing. However, the market is fragmented, affected by local
competition and legislation (which affects supply). Market perception is very much impacted by
what is happening in the markets in London and the south east, where gate fees are under
pressure. Scotland, Wales and Northern Ireland, as well as northern England, represent stronger
markets with higher typical gate fees, which are reflected in the overall medians generated by
this survey.
Some operators thought that aspirations contained in the England Resource and Waste Strategy,
which was published in late 2018, may have an impact on stabilising or even increasing gate
fees, as there is a requirement for local authorities to collect food waste. However, this depends
upon the results of the subsequent consultation, and it may take a while for local authorities to
all start adopting food waste collections, and so this may be a longer term impact rather than
having immediate effect.
4.4 Energy from Waste
In total there were 116 responses to the survey (excluding repeats and invalid responses) from
96 different local authorities, who reported use of energy from waste as a residual waste
recovery method. Of these responses, one outlier was excluded, and six responses received were
identified as RDF production for export to mainland Europe so were also excluded.
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This left 109 responses from which 68 had usable gate fees. These responses were from 58
different local authorities, 46 of which were English authorities, 4 from Scotland, 7 from Wales
and none from Northern Ireland.
4.4.1 Current gate fees and trends
As in previous years, results are reported for the UK as a whole, with results split for facilities
built before and after 2000. Results are summarised in Table 34.
This year, the reported median gate fee for EfW (all responses) is £89/tonne compared to
£86/tonne last year. Of this year’s respondents, just 2 reported new contracts in 2018, although
one of these authorities reported 2 new contracts.
For pre-2000 EfW facilities, the median gate fee is £65/tonne, compared to £57/tonne last year.
For post-2000 facilities, median gate fee is £92/tonne, compared to £89/tonne last year. Three
entries did not specify the destination of their waste.
Table 34: Summary of energy recovery (EfW) gate fees reported by local authorities 2018,
with and without contracts (£/tonne)
Type of
facility
Median Mode Range
Respons
es
All £89 £85 to £90 £44 to £125 68
Pre-year 2000
All responses £65 £65 to £70 £44 to £89 20
With contracts £66 £65 to £70 £44 to £89 16
Without contracts £54 £45 to £50 £47 to £81 4
Post-year 2000
All responses £93 £85 to £90 £50 to £121 45
With contracts £92 £85 to £90 £50 to £121 42
Without contracts £93 £90 to £95 Insufficient data 3
The majority of responses received were for contracted gate fees (80% pre-2000, 91% post-
2000). For pre-2000 facilities, non-contracted gate fees showed a lower median than for
contracted (£54/tonne v £66/tonne). For post-2000 facilities, contracted and non-contracted
median gate fees were similar at £92/tonne and £93/tonne respectively.
Of the 76 authorities responding to the question, 49 (65%) said their gate fee had changed in
2018. The majority of these (89%) were contracted. Of those that reported a reason for the
change in their annual gate fees (45 responses), most said this was due to an inflation increase
(42) or some other contractual annual uplift, with others reporting a new contract or contract
extension.
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The range in reported gate fees is broad at £44 to £125 (£85-90 mode range). This is because
there is a significant range of contractual and funding factors which can have an influence on
gate fee charged including mode of financing (PFI/PPP or prudential borrowing), whether the
asset reverts to the local authority or not, contract length, and whether the authority made a
capital contribution. Operators reported that contracts are getting more sophisticated and more
unique, therefore making it difficult to compare individual gate fee figures.
Looking at trends in gate fees over time, the pre-2000 gate fee has consistently hovered around
£60/tonne. Only one authority reported a new contract with pre-2000 facilities in 2018. Pre-2000
gate fee trends are shown in Figure 10.
Figure 10: Pre-2000 EfW gate fees reported by local authorities over time 2009-2018 (UK,
£/tonne)
For post-2000 facilities, median gate fees appear to have peaked at £100/tonne in 2014 and
have plateaued at £90-95 since then. This year 2 authorities reported new contracts with post-
2000 facilities. The data is summarised in Figure 11.
Figure 11: Post-2000 EfW gate fees reported by local authorities over time 2010-2018 (UK,
£/tonne)
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Based upon the responses to this survey, in the period 2013 to 2018, a total of 41 new contracts
are reported to have started. For these contracts, median gate fees and ranges are reported in
Table 35. These show that for pre 2000 facilities, new contracts are being signed at gate fees
significantly above the overall median gate fee (£85/tonne compared to the overall median of
£65/tonne) and more in line with market (and post-2000) gate fees. For post-2000 facilities, new
contracts are being signed with gate fees slightly lower than the median gate fee (£87/tonne
compared to the overall median of £93/tonne) and range of all contracts reported for this type of
facility. Note in terms of contract lengths, most of the post-2000 facility new contracts are anchor
contracts for newly built facilities, and therefore average at 25 years. For new contracts for pre-
2000 facilities, these are renewed or replacement contracts for existing long established facilities,
reflected in a much shorter average contract term of 7 years.
Table 35: EfW contracts started and median gate fees reported by local authorities 2013-2018
(£/tonne)
Facility type Contracts started Median gate
fee (£/tonne)
Range
(£/tonne)
Median
Contract
Length
Pre-2000 8 £85 £68-£89 7 years
Post-2000 33 £87 £50-116 25 years
4.4.2 Contract review
A range of contract lengths were reported. The split was mainly between authorities sending
material to established energy recovery facilities, with short to medium term contracts (21% of
reported contracts of length less than 10 years) with a significant proportion of PFI/PPP related
contracts for which dedicated energy recovery plants were constructed, with long term contracts
(71% of reported contracts with length 20 years or more). Contract length data is summarised in
Table 36.
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Table 36: Energy recovery contract lengths reported 2018
Contract length (years) Count Proportion of count
1 1 1%
3 1 1%
4 2 3%
5 3 4%
7 8 10%
8 1 1%
9 1 1%
10 3 4%
11 1 1%
14 1 1%
18 1 1%
23 2 3%
24 2 3%
25 28 35%
>25 24 30%
4.4.3 Key influencing factors
Of factors influencing gate fees, respondents reported indexation (RPI), increased operating
costs and availability of capacity as having the most impact on current and future gate fees;
similar to last year’s responses. Responses are summarised in Table 37 and Table 38.
Of the 80 respondents providing an opinion, 68 (85%, 73% last year) expected gate fees to
increase in the future, only 6% expected a reduction.
Table 37: Key influencing factors – current energy recovery gate fees 2018 (indicated by local
authority survey – 63 responses)
Influencing factor No of responses %
Inflation (RPI, RPIX) 40 63%
Availability of capacity 32 51%
Operating costs 28 44%
Competition between similar facilities 16 25%
Legislative requirements 16 25%
Contractual changes, other than inflation increase 15 24%
Investment/capital costs 15 24%
Other 12 19%
Cost of landfilling residues 10 16%
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Product/commodity end market prices 10 16%
Competition from alternative treatment options 8 13%
Competition from foreign incinerators 5 8%
Government incentive schemes e.g. renewables 4 6%
Quality of input materials 3 5%
Cost of recycling residues 2 3%
Table 38: Key influencing factors – future energy recovery gate fees 2018 (indicated by local
authority survey – 65 responses)
Influencing factor No of responses %
Availability of capacity 35 54%
Inflation (RPI, RPIX) 30 46%
Legislative requirements 28 43%
Competition between similar facilities 25 38%
Operating costs 25 38%
Competition from alternative treatment options 16 25%
Investment/capital costs 11 17%
Product/commodity end market prices 10 15%
Government incentive schemes e.g. renewables 8 12%
Quality of input materials 8 12%
Other 8 12%
Contractual changes, other than inflation increase 7 11%
Cost of landfilling residues 7 11%
Cost of recycling residues 5 8%
Competition from foreign incinerators 4 6%
4.4.4 Waste contractor interviews
Discussions with the waste management companies confirmed the figures generated by the
survey, and that the main impact on local authority gate fees now all of the local authority
dedicated PFI capacity has been delivered, will be contracted inflation increases.
For new contracts in the future, the likely factors influencing gate fees will be the propensity of
merchant EfW capacity (there are some active projects coming through), the availability of
landfill (which will drive local disposal gate fees) and the impact on RDF exports post Brexit. It is
thought the low value of Sterling and possible reduction in the availability of cheap back-haul
transport to Europe post Brexit will impact the availability of European free capacity as an option,
could push up RDF pricing and potentially UK EfW spot and new contract gate fees. Although it
has been suggested that Dutch operators are looking east for future material, and are taking
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smaller packages of waste to de-risk, UK contractors explain that most want to keep
communication open for if they need additional waste for capacity drops in the future.
4.5 Non-hazardous landfill
A total of 125 responses from 90 local authorities, 9 were rejected due to inclusion of transport
costs or being outliers. Of the 116 acceptable responses, 76 included usable gate fees which are
included in the analysis.
Of the responses which did not include gate fees, 18 said the gate fee was part of an integrated
contract, 10 were contractually obliged to not share gate fees, 2 said the contractor said the gate
fees should be regarded as confidential, and 6 provided various other reasons such as that the
contract was managed by the disposal authority.
4.5.1 Current gate fees and trends
The UK median landfill gate fee is £24/tonne, ranging from £2 to £87/tonne, and mode £25 to
£30/tonne, excluding landfill tax (£88.95/tonne in 2018) and haulage costs. This is an increase
compared to last year’s median (£20/tonne). Error! Not a valid bookmark self-reference.
shows that gate fees have remained relatively stable over the survey period. However, variability
of the gate fees around this mean is getting larger, which is mirrored by the fact that the median
does not fall within the modal range, and the general trend appears to be up.
Figure 12: Landfill gate fees reported by local authorities over the time for the whole UK
(£/tonne)
Table 39 shows the breakdown of gate fees by nation as well as per region within England.
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Table 39: Landfill gate fees reported by local authorities, broken down by nations and regions
within England (£/tonne)
Median Mode Range Responses Median 2017
UK (including
£88.95 landfill tax,
2018/19 tax year)
£113 £114 to £119 £91 to £176 76 £107*
UK (excluding
landfill tax) £24 £25 to £30 £2 to £87 76 £20
England £24 £25 to £30 £5 to £44 48 £22
London Insufficient
data Insufficient data
Insufficient
data 2
Insufficient
data
South East £23 £20 to £25 £12 to £29 9 £20
South West £28 £25 to £30 £10 to £39 14 £24
East of England £10 £5 to £10 £5 to £33 5 £13
East Midlands £22 £20 to £25 £11 to £28 4 £21
West Midlands £17 £15 to £20 £13 to £32 5 £24
North West £30 £40 to £45 £20 to £44 5 £29
North East £26 £25 to £30 Insufficient
data 3 £25
Yorkshire &
Humber
Insufficient
data
Insufficient data Insufficient
data 1 £13
Wales £19 £15 to £20 £2 to £48 7 £32
Northern Ireland £9 £5 to £10 £8 to £52 5 £13
Note: includes 2017/18 landfill tax value of £88.95/tonne
Figure 13 shows that gate fees are highest in England and lowest in Northern Ireland. Gate fees
in England have increased slightly from £22 to £24/tonne, and the range of gate fees has
decreased since last year, from £2 to £50 to £5 to £44/tonne.
Similar to last year, the lowest gate fees in England are seen in the East of England at £10/tonne
(which is a slight decrease since last year at £13/tonne) and the highest in the North West, which
has increased by £1/tonne since last year to £30/tonne (see Table 39).
From the data collected, it would suggest that both Wales and Northern Ireland’s gate fees have
dropped since last year. In the case of Wales, a significant decrease from £32 last year to
£19/tonne this year has been reported. For Northern Ireland the median has decreased from
£13 to £9/tonne. However, in both cases, the range is identical to last year’s results, and given
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that both sample sizes are relatively small (in comparison with England for example), it is likely
that the reported changes are more a reflection of the authorities that have responded and which
happens to fall as the ‘median’, which is the key average figure reported in the annual gate fee
report, rather than being a reflection of changes in the market.
Just under half the authorities reported that gate fees (not including landfill tax increases) had
changed since last year, with all but one authority out of those that provided figures, citing
increases. The majority were related to inflation.
Figure 13: Landfill gate fees over time reported by local authorities by nation (£/tonne)
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4.5.2 Contract review
Of those authorities sending material to landfill, 77% (72% last year) did so under a contract,
while 17% (19% last year) said they were not using a contract at present. The balance of
authorities did not provide a response.
Of those under contract, 76 provided start and end dates which has allowed for calculation of
the contract length. Table 40 demonstrates that a third of the contracts are for six years or
less, just over half (51%) are 14 years or less, and 36% of the contracts are for 25 years or
over.
Table 40: Landfill contract lengths (for which contract length data was submitted)
Contract Length (years) Number of contracts
No. %
1 2 3%
2 5 7%
3 6 8%
4 7 9%
5 3 4%
6 2 3%
7 8 11%
8 1 1%
10 2 3%
11 1 1%
14 2 3%
15 4 5%
16 3 4%
20 1 1%
23 2 3%
25 12 16%
>25 15 20%
Total 76 100%
Figure 14 shows that there seems to be a relationship between contract length and landfill
gate fees, with longer contracts having higher gate fees than shorter contracts. This may be
related to longer term contracts having an infrastructure investment element. Figure 15
shows that there is no clear relationship demonstrated by considering the year the contract
was started.
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Figure 14: Impact of landfill contract lengths on gate fees (£/tonne)
Figure 15: Impact of contract start date on gate fees (£/tonne)
4.5.3 Key influencing factors
Table 41 shows that that over half (54%) of the authorities thought that landfill tax was the
most influential factor on their existing gate fees. Legislative requirements ranked second,
compared to fourth last year, with 50% of the authorities feeling this was a key influence.
Availability of capacity dropped from second to third year at 44%, and operating costs and
inflation were both still within the top five as last year, each with over 30% of local authorities
naming these are key influences.
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The factors identified by local authorities as being the most likely to influence gate fees in the
future (
Table 42) are ranked differently to those thought to have influenced for the last twelve
months. Availability of capacity and legislative requirements are considered the most
important (53%), followed by landfill tax (50%).
Table 41: Factors influencing current landfill gate fees (indicated by local authorities – 68
responses)
Factor influencing current gate
fees
Response Rates
No. %
Landfill tax 37 54%
Legislative requirements 34 50%
Availability of capacity 30 44%
Inflation (RPI, RPIX) 23 34%
Operating costs 21 31%
Competition from alternative
treatment options 18 26%
Competition between similar
facilities 6 9%
Contractual changes, other than
inflation increase 5 7%
Other 5 7%
Investment/capital costs 2 3%
Product/commodity end market
prices 2 3%
Quality of input materials 2 3%
Government incentive schemes
e.g. renewables 0 0%
Table 42: Factors most likely to influence future landfill gate fees (indicated by local
authorities – 70 responses)
Factor influencing future gate
fees
Response Rates
No. %
Availability of capacity 37 53%
Legislative requirements 37 53%
Landfill tax 35 50%
Competition from alternative
treatment options 25 36%
Operating costs 18 26%
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Factor influencing future gate
fees
Response Rates
No. %
Inflation (RPI, RPIX) 17 24%
Competition between similar
facilities 10 14%
Investment/capital costs 5 7%
Other 4 6%
Contractual changes, other than
inflation increase 2 3%
Government incentive schemes
e.g. renewables 2 3%
Quality of input materials 2 3%
Product/commodity end market
prices 0 0%
There is an increasing trend of authorities believing that landfill gate fees will increase, with
86% of authorities saying so (up from 81%, 80% and 76% the last three years). Only 3%
thought they would decrease (same as last year), with 12% saying they would remain the
same.
4.5.4 Waste contractor interviews
Discussions with waste contractors that operate landfills confirm the regional nature of the
market. There are multiple drivers which have an impact on landfill gate fees. For example,
whether there is sufficient capacity within a region, or competition from energy from waste
facilities, and what the strategy of the operator may be, i.e. whether they want to conserve
their capacity (maintain or increase gate fees) or fill their landfills as quickly as possible (lower
gate fees). Also, as landfills close, this presents the opportunity for remaining operators to
increase prices as remaining capacity becomes scarce.
The view generally was that landfill gate fees would start to increase (which agrees with the
local authority perspective), due to no new landfill infrastructure development and that
materials which are going to landfill are increasingly difficult to deal with, e.g. mattresses.
5.0 Recommendations for future surveys
It is recommended each year, that the results from the previous survey are reflected upon
prior to deciding the scope of next year’s survey in light of any recent legislation or policy, and
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any other contextual changes. Currently, the survey captures the areas of most interest, and
in recent years has discounted open air windrow composting, mechanical biological treatment
(and other residual waste treatments) and wood waste outlets. However, with the Resource
and Waste Strategy having been launched at the end of last year, there could be outcomes
from the upcoming consultations, such as common approaches to recyclates and food waste
collections, which may need to be incorporated into the survey next year.
It should be noted in this review that changes in one sub-sector can impact other sub-sectors
e.g. potential overcapacity in AD capacity impacting on IVC gate fees, impact of RDF export
prices on landfill and EfW gate fees, so this should be taken into account when this selection
of target sub-sectors is made.
The questionnaires should be reviewed each year to ensure the questions are still relevant and
allow authorities and operators to provide pertinent information. They should also be
assessed as to whether they can be streamlined, to minimise the time required to for
respondees to maximise responses. For example, the material types being accepted into IVC
could be streamlined due to lack of responses for certain categories.
Response rates are slightly higher than last year, but not significantly. It shows that constant
chase up calls for the survey period, and engagement by organisations including CIWM, REA
and ADBA to actively promote the survey, are necessary to maintain levels but not necessarily
improve. The survey period was slightly longer this year, and completed before Christmas, as
per two years ago. Last year, the survey period spanned the Christmas period, and some
authorities said it clashed with other deadlines they had, such as their inputs for
WasteDataFlow, and does appear to coincide with a dip in responses.
Response rates from the organic operator surveys remains low, despite engagement with
ADBA and REA, who both promoted it. Engagement with waste operators proved less
successful this year. This may have been because of the publication of the Resource and
Waste Strategy at the end of last year, and the uncertainty about arrangements at the end of
March when the UK leaves the European Union. It is likely the people we sought were busy
with these other activities and unable to spare the time to comment on the results of the gate
fees survey this year.
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Appendix 1 – Data Collection Methodology
Local authority survey
This year’s survey followed the format of the last five years’ surveys, in that it was conducted
using a web-based questionnaire. The questionnaire was constructed and designed by
Anthesis and hosted by the website Survey Monkey.
The online questionnaire was publicised to local authorities by an email containing a survey
link for each local authority contact. At least one email was sent to a specific contact at every
local authority in the UK. Where multiple contact details were available within an authority, the
survey was sent to each one. The survey was also publicised on WRAP’s website.
The covering email contained summary information about the gate fees survey in general, and
provided links to WRAP’s webpage for the previous year’s survey. As the summary report from
last year’s survey is available on WRAP’s website, a link to the relevant webpage was provided
for both of these reports rather than providing attachments in the email. The covering email
also confirmed the support of relevant organisations14; this support was extremely important
in demonstrating the credibility and importance of the survey.
The covering email was sent to all local authorities on 2nd November 2018. A second email
was then sent out to all contacts on the 19th November 2018 to remind them about the survey
and of the deadline. The deadline was extended by a few extra days (from 30th November
until 7th December 2019) and a third email was sent to inform those who had not already
responded.
Authority responses were monitored throughout the survey. Extensive phone calling was made
throughout the survey period to local authorities, to ensure they had received the invitation to
participate, to ask if the correct people had received it, and to establish whether they intended
or were able to complete the survey, by the required deadline. Local authorities were also
offered the chance to complete the survey over the phone with the Anthesis team member
making the calls. During the survey period a helpline and email address were made available
by Anthesis to answer questions and support local authority officers with filling in the
questionnaire.
Sampling strategy
14 Supporting organisations include: Department for Environment, Food & Rural Affairs (England), The Welsh Government, The Welsh Local Government Association, the Department for the Environment (Northern Ireland), LARAC, Resource London, the Organics Recycling Group (ORG) and the Anaerobic Digestion & Bioresources Association (ADBA).
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The contact database for local authority officers was used to send emails to at least one
contact from each local authority. If a bounce-back email message was received, which
included details of a new officer, the contact list was updated and the email was re-sent. If no
new contact details were provided, attempts were made to try to identify updated contact
details (during the reminder phone calls) to which the questionnaire could be sent.
All local authorities in the UK were targeted. The intention was to maximise responses across
the board. However, there were some priority areas, to which chase up phones call were
given precedence. For example, London, partly due to the comparatively low number of
authorities, required a high response rate in order to produce accurate results. Wales was
also an area of particular interest. Phone calls were also concentrated on WDAs and Unitary
authorities, as these were considered the most likely to be able to complete the survey and
have most relevant data.
Questionnaire
A single questionnaire was used for capturing all data from local authorities. This
questionnaire included detailed questions covering all waste management services listed
within the survey scope (Section 0). Question logic was built into the survey so that if the
authority answered ‘no’ to using a specific service (e.g. a MRF or IVC) they then bypassed all
subsequent questions regarding that service type. In this manner the questionnaire was kept
relevant to the individual authority.
The online questionnaire that was developed by Anthesis for the 2015 survey was used as the
template, to which numerous alterations have been made over the years, for example removal
of MBT and wood waste reprocessing as requested by WRAP.
All questions relating to gate fees and changes in gate fees were open questions that required
the input of £/tonne values. Closed questions were restricted to the section that asked about
current and future factors influencing gate fees. This section provided a number of possible
options that respondents could select from a predefined list; however, respondents could also
select ‘other’, and add additional comments in a free text box if relevant factors were not
contained in the list.
Survey of organic waste treatment operators
The organic waste treatment operators’ survey followed the same approach as the local
authority survey, in that it was conducted using web-based questionnaires. A different
questionnaire was compiled for each of IVC and AD operators (wood waste reprocessors have
not been surveyed for the last few years). The questionnaires were constructed and designed
by Anthesis and hosted by market research website Survey Monkey.
The online questionnaires were publicised to organic waste treatment operators by a covering
email containing the relevant survey links depending on the contact and which treatment
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technologies were relevant to them. Where multiple contact details were available within a
company the survey was sent to each one. The survey was also publicised on WRAP’s website.
The covering email contained summary information about the gate fees survey in general and
provided links to WRAP’s webpage for the previous years’ survey. As the summary report from
last year’s survey is now available on request via WRAP’s website, a link to the relevant
webpage was provided for both of these reports rather than providing attachments in the
email. The covering email also contained the logos of the supporting organisations.
The introductory email was sent to organic waste treatment operators on 12th November
2018. A second email was then sent out to all contacts on 26th November to remind them
about the survey. A third email was sent out on 30th November 2018 to operators that had
partially completed a survey or had not yet responded, and the survey deadline was extended
to the 7th December 2018 (from the initial date of the 30th November), to encourage further
responses.
Operator responses were monitored throughout the entire duration of the survey. Phone calls
were made throughout the survey period, to ensure they had received the invitation to
participate, to ask if the correct people had received it, and to establish whether they intended
or were able to complete the survey, by the required deadline. Operators were also offered
the chance to complete the survey over the phone with the Anthesis team member making
the calls. During the survey period a helpline and email address were made available by
Anthesis to answer questions and support local authority officers with filling in the
questionnaire.
For this year’s study a contact database for IVC and AD operators was updated from last year
using Anthesis’ contact details for relevant operators. A total of 236 emails were sent to
approximately 150 operators at the start of the survey period (some with multiple contacts).
Questionnaires
Individual questionnaires were devised for IVC and AD operators, based upon those devised
by Anthesis for last year’s survey. If an operator was known to have more than one type of
organic facility, multiple links were included within the emails sent to these contacts.
Waste management companies
A number of waste management companies, that have a range of technology types and
regional distribution, were identified. Key contacts within these companies were contacted to
see whether they would be willing to take part in either a telephone or face-to-face interview,
with a senior member of the Anthesis delivery team.
As was the case with previous years, it was anticipated that information gained from these
interviews would not necessarily be actual gate fee figures associated with particular facilities,
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but, more likely, a range of gate fees and a market trend commentary. This information was
used to ‘sense check’ the information received from local authorities. The rationale was that
by not asking for gate fees for specific facilities, companies would be more willing to
participate, and would also engage in a discussion about relevant drivers in the market place.
The approach taken was to present a summary of the gate fees collected in the local authority
survey (median and regional differences) and ask the company representatives to confirm or
otherwise comment on them. General questions (rather than specific questions about gate
fees) were also asked about the local authority and commercial markets.
Data analysis and quality assurance
Whilst there is some data analysis functionality available through the website used to host the
online questionnaires it was insufficient for all the survey requirements. Consequently, the
data was exported into Microsoft Excel file format to facilitate detailed analysis and the
production of charts.
Data checking and cleansing
Once the data was exported it was checked for obvious errors, as well as less likely errors,
which required potential clarification with the respondents. This primarily involved senior
members of the team examining the data and highlighting potential errors using their
knowledge of the market.
Typical issues which were identified during this data checking and cleaning stage included for
example:
◼ Where £0/tonne gate fees were stated, checking with the authority these were valid and
that they hadn’t intended to leave blank;
◼ The same gate fee entered in both the including and excluding haulage fields; and
◼ Data which appeared to be outlying (either high or low) or illogical.
Such issues were identified within the data, checked with the supplying local authority by
phone or email and corrected prior to analysis of the data. In some cases, where responses
were not received and gate fees looked significantly out of step with others, they were
eliminated from the analysis.
Haulage costs
The key data for this survey are the gate fees charged at each type of facility (£/tonne). For
comparability reasons these must exclude all other costs which may be associated with the
management of a waste, e.g. collection, bulking, or haulage costs. For this reason, this survey
has differentiated between prices for ‘gate fees excluding transport’ and ‘gate fees including
transport’.
For comparison calculations, only gate fees excluding haulage have been used in the analysis
of data. Where responses had been received which included transport only, an estimate was
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made as to what the transport element of that gate fee was, so a gate fee excluding haulage
could be calculated. Authorities were asked, where possible, to provide gate fees both
including and excluding haulage. These were used to calculate an average ‘transport /tonne’
cost for each facility type and then removed from the gate fees which included haulage costs.
This enabled additional data points to be considered in the overall analysis. Due care was
taken to identify any calculated gate fees where transport costs were thought not be
accurately accounted for through this method and these were removed from the analysis.
PFI / integrated contracts
A number of local authorities, with existing PFI or integrated contracts, quoted gate fees
which were obviously not ‘gate fees’ for a specific treatment facility, but represented the
whole, or part of a payment for an integrated service. Comments provided within the survey
and further questioning of some of these authorities revealed that complex payment
mechanisms were in place for waste treatment and disposal, whereby the true cost of the
technology or technologies used was masked by the structure of the payment mechanism.
This issue is particularly marked under integrated contracts, where service fees may be paid to
operators covering a range of services.
Given the issues outlined above, all gate fees that were identified as being linked to complex
payment mechanisms, and that led to unusual gate fees being quoted, were excluded from
the dataset. Clear examples of this issue are when authorities quote the same gate fee for a
range of services.
Materials Recovery Facilities
MRF gate fees depend on the range of materials collected for sorting, and therefore to allow
for comparability, only gate fees provided which represented sorting of a typical mix of at
least four key materials were included in the overall analysis.
Data analysis limitations
In the analysis of the data collected, relevant sample sizes are reported. When examining data
in detail or comparing results per waste management service from this year to those obtained
from previous years, the size of the sample on which results are based needs to be
considered. This is particularly relevant when, for instance, comparing results for a particular
waste management type at national level, or comparing results between English regions,
where a small sample size per individual nation or region may make robust comparison
difficult. Where such issues arise, these are highlighted in the text.
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www.wrap.org.uk/gatefees2019