Replanting Obligation

Farmers Journal, Part 1

Dated, April 2016 but still the best explanation on the replanting obligation

Forest owners in Ireland are legally obliged to reforest land after a crop has been removed or destroyed due to disease, fire, windblow or other causes. The replanting obligation is enshrined in the 2014 Forestry Act. It is regarded by the State as vital in protecting and expanding our forest resource, while a number of organisations claim it is an unnecessary interference and acts as a disincentive to achieving a viable afforestation programme.

The replanting requirement is not unique to Ireland, although it is much more detailed than other European countries in relation to the kind of forests the minister will permit following final harvest. It is also specific with regard to the severity of fines should forest owners fail to comply with the act (see panel).

Europe

The UN Food and Agriculture Organisation published “Forest Legislation in Europe” in 2004 outlining how 23 countries approach the obligation to reforest.

Authored by Josephine Bauer, Matleena Kniivilä and Franz Schmithüsen, the report states: “Reforestation is obligatory and some kind of time limit for regeneration is defined in the forest laws of Austria, Bosnia and Herzegovina, Bulgaria, Croatia, Czech Republic, Finland, Hungary, Lithuania, Poland, Romania and Sweden.” The Forest Act in Finland “does not prevent forestry land from being adopted for other purposes”.

The authors say that the laws of France, Germany, Slovak Republic and Switzerland “provide for reforestation in a general manner as part of the principle of sustainable forest management and planning.”

They quote the German Forest Act “which constitutes a framework for legislation at state level” and obliges “all forest owners … to reforest or supplement when natural stock regeneration is incomplete in clearfelled forest areas or thinned out forest stands within a reasonable period of time”.

In relation to changing land use in Germany, they say: “If a forest is converted to other use for a specified period, the authorities have to make sure that the area is duly reforested within a reasonable period of time.”

The authors do not mention fines or other penalties, should owners not comply with the various replanting requirements of the 23 European countries surveyed. Incidentally, Ireland was not featured in the report.

Ireland

The Irish Forestry Act 2014 is specific about the need to replant and what kind of forest is required by the Forest Service. The IFA regards the replanting order as “a major deterrent to farmers considering forestry” as outlined by Michael Fleming, IFA farm forestry chair. While the IFA accepts the act, it advises farmers to be extremely cautious and to make themselves aware of the implications of the replanting obligation.

It is not alone in its opposition to the replanting obligation. A number of private forest owners and organisations representing their interests maintain that it is unnecessary. They claim that forest owners have fulfilled their obligations during a normal forest rotation. They maintain that few, if any, would revert to another land use but the statutory presence of the replanting obligation acts as a barrier to future afforestation. This is reflected in the reduction in land values after planting as existing and future forest owners are locked into forestry. This is perceived as a major barrier to afforestation because it restricts land owners to the same crop in perpetuity, which is unique in land-use policy.

The State, on the other hand, claims that the taxpayer has invested heavily in creating the forest resource and this would be jeopardised by the removal of the replanting obligation as would other benefits such as future carbon accounting and timber supply. 

Those who favour the retention of the replanting requirement maintain that it is a fundamental aspect of sustainable forest management, which is vital to Ireland considering our low forest cover.

Over the past 100 years, six forestry acts have been enacted to cover primary forest legislation in Ireland outlining issues such as the function of the minister responsible for forestry, felling licences, forest damage and replanting.

The 1928 Forestry Act was the first act that had the power to control the felling of trees and to attach replanting conditions. The 1946 Forestry Act retained the replanting obligation, while the 2014 act made “further and better provision in relation to forestry, to provide for the development and promotion of forestry in a manner that maximises the economic, environmental and social value of forests within the principles of sustainable forest management” and to confer certain powers on the minister to ensure the act is implemented.

Part four of the act refers to the application for a felling licence and addressed the replanting obligation which follows. It states: “Subject to section 7, where a person wishes to fell or otherwise remove any tree or trees, he or she shall apply to the minister for a licence to do so.”

An application will include particulars of the tree or trees concerned, and such other particulars as may be prescribed by the minister. The licence shall be valid for such period as the minister decides, but shall not exceed 10 years but the minister may extend the duration of the licence for one or more further periods, not exceeding a total of five years.

The minister may at any time attach or vary conditions to any licence granted, including the requirement to:Replant trees, at such places, of such species, in such numbers, of such surface area and density, within such period of time, as may be specified.Protect and maintain the reforested area including the erection of fencing or barriers to prevent trespass by animals, during such period of time as may be specified.Submit a report to the minister with such information as the minister considers appropriate.Submit a forest management plan to the minister and, where such a plan has been approved, in whole or in part, by the minister, to implement the plan as approved.

Offence

Under the act, “a person who fells or otherwise removes one or more trees, or causes or permits one or more trees to be felled or otherwise removed, without a licence, or in contravention of a condition of a licence, shall be guilty of an offence and be liable” to the following penalties:A fine not exceeding €200 for every tree in respect of which the offence was committed (but which total penalty shall not exceed €5,000) or imprisonment for a term not exceeding six months or both; orA fine not exceeding €1,000,000 or imprisonment for a term not exceeding five years or both.

Part 2

The replanting – or reforestation – obligation is not unique to Ireland as discussed in last week’s article. Replanting is a requirement in most EU member states as well as many developed countries, while third world countries that export timber to member states and the US need to show that they practise sustainable forest management, which includes reforestation as covered by the European Timber Regulation (EUTR) and the US Lacey Act .

The replanting obligation is not a major consideration in Europe where forest cover is over 30% of the land area in 25 countries, so forestry is well established and there are relatively few new entrants to forestry.

The objective in Ireland is to increase forest cover to 18% by 2050, which will be achieved by the private sector, mainly farmers. Forestry is a long-term land use and the concept of land staying under one land use in perpetuity is new to Irish farmers and, for some, it is a barrier to planting. As a result, many in the forestry sector favour the removal or modification of the requirement.

IFA farm forestry chair Michael Fleming says the obligation is self-defeating. The permanence of forestry, “particularly the replanting obligation is a barrier to the increased uptake of forestry by farmers,” he maintained.

Donal Whelan, director of the Irish Timber Growers Association (ITGA), sought a change to the obligation during negotiations on the Forestry Act. “The reforestation requirement after felling, acts as a barrier to afforestation and… it should not be mandatory for growers to have to replant when a final crop has been removed,” he says.

John O’Reilly, chief executive of Green Belt, says the replanting obligation acted as a barrier for some farmers who might otherwise plant. He favours flexibility that “would allow a portion of the land to return to another land use after a mature crop was harvested, if requested by the owner”.

The Forest Service argues for the retention of the replanting obligation as outlined in the Forestry Act 2014. “The State has invested heavily in the afforestation programme through payment of grants and premiums and generous tax arrangements,” according to a Department spokesperson. “Not to insist on replanting would result in deforestation and a poor return for the State investment already made. The objective of increasing forest cover and providing a continuous wood supply for industry would not be facilitated by the removal of this condition.”

Paddy Bruton, managing director of Forestry Services, agreed that the removal of the obligation wouldn’t lead to deforestation. “From our experience, I have no doubt that few, if any, farmers with forests would revert to another land use, after final harvest,” he says. “Apart from the high conversion costs, farmers with forests see it as an excellent investment.” 

However, many farmers thinking about planting see the obligation as a barrier and, occasionally, it is even an excuse not to plant. While Bruton acknowledges that removal is unlikely, he agrees that a flexible approach to reforestation would help.

In this regard, the Department spokesperson has not ruled out a degree of flexibility on how the act is interpreted. “ The 2014 Forestry Act allows the minister to set conditions which include the replanting of trees, so there is an element of discretion allowed in relation to this issue,” he maintains. “ It is a matter of policy how this is implemented.”

Because forestry is a long-term investment, a number of forestry companies contacted believed that growers should receive reconstitution grants if their forests are damaged due to natural causes before a commercial crop is harvested, such as applies in plantations damaged by ash dieback.

“Some farmers who had forests destroyed in the 2014 storms, received less for their timber sales than the cost of reforestation,” Bruton says. “These are at a loss not only in replanting but must wait a further two decades before receiving any income.” While a reconstitution grant has not been definitively ruled out, the Department spokesperson says “there is currently no scheme that caters for situations where a forest has suffered windblow damage”.

When asked about changing from forestry to another land use, the spokesperson stated: “All felling licences are assessed on a case-by-case basis, but in general planting of alternative land equivalent in area and quality can be considered taking into consideration the sensitivities of the existing wood and the areas proposed for replanting. 

‘‘Technical approval for afforestation is required for alternative planting sites,” according to the spokesperson. Coillte has availed of this condition when selling land for windfarms and other land uses.

Investment

The average payout by the Department in afforestation grants and premium payments is €10,000/ha in “one of the most supportive range of forestry packages in the world”, which “has a Government commitment to growing the sector,” the spokesperson says.

However, organisations such as the IFA and ITGA argue that the commitment by the private forest owner is far greater as it continues long after the state’s obligation ends at year 15 when final premium payments are made. In addition, the forest owner’s land investment, time and management costs – valued at between €10,000 and €18,000/ha – exceed state funding. They also point out that afforested land devalues because future owners are legally restricted to forestry. 

While flexibility in interpreting the Forestry Act is possible, it is unlikely that the replanting obligation will be removed because of the perceived fear by the Department that if could cause deforestation resulting in disruption to continuity of future timber supply and forecast uncertainty in forest carbon accounting.

While the replanting obligation is enshrined in the Forestry Act 2014, it allows for flexibility. To increase confidence in the current Forestry Programme, the Department could take two modest steps relating to the reforestation requirement:Provide reconstitution grants for replanting land damaged by natural causes before a viable crop has been harvested. Natural causes include windblow, flooding, frost, mammal, insect and fungal damage.Allow a small portion of land to return to other land uses similar to New Zealand where it is acknowledged that minor clearances – less than one hectare – are not considered as deforestation and do not result in Emissions Trading Scheme (ETS) obligations.

Converting land to forest cover is a major partnership by farmers and the State. In the first 15 years of the life of a forest, the total investment by both partners is as high as €30,000/ha. The long-term returns to both and to society are enormous in relation to import substitution, rural job and wealth creation, renewable energy and climate change mitigation.

The investment by the farmer in the forestry programme needs to matched by the State in terms of risk sharing where damage is caused through no fault of either party. If the state insists on the replanting obligation, then it has to share some of the risks especially when losses occur in the pre-commercial phase. The Department cannot have it both ways.

Read part one, The legal requirement to replant after final harvest, here.

DECC Governance, Risk & Compliance Tracking Software

Currently there is a requirement for a Governance, Risk and Compliance tracking software solution to replace an existing manual process. The current manual process involves up to 80 different external organisations, operating in different sectors of the economy, submitting a Self-Assessment spreadsheet on a yearly basis

These spreadsheets are used to track organisations’ performance against key outcomes and progress of Corrective Action Plans. These spreadsheets span multiple excel tabs, within each tab there are multiple sections and multiple columns. Organisations assess themselves against these out-comes which are then used by DECC to track performance.

This current manual process has a number of drawbacks such as difficulty to:

  • compare performance across years
  • identifying common gaps or issues
  • identifying areas of good or poor performance
  • produce reliable and detailed reports
  • inability to query information easily

The move to replace this manual process is part of a move to increase electronic management of the documents and automation of steps within the compliance process. An opportunity now exists to implement a software solution which will deliver a single, unified platform capable of delivering a secure and user-friendly application for the end users. The change is also aiming to create reliable and timely statistics, detailed reports, audit tracking capabilities and the ability to easily identify gaps to facilitate management of the compliance process as well as reporting to senior management and external constituents on compliance progression.

State bodies under the aegis of DECC

https://www.gov.ie/en/organisation-information/3bd1c-state-bodies-under-our-aegis/

West Cork Flood Relief Schemes

Non-Return Valves


• River Ilen (Skibbereen) Flood Relief Scheme (also known as the Skibbereen FRS)
• River Bandon Flood Relief Scheme (also known as the Bandon FRS)
• Clonakilty Flood Relief Scheme (also known as the Clonakilty FRS)


These schemes were built under the OPW powers of the Arterial Drainage Acts 1945 & as amended in 1995.
The above schemes are now in the Operation & Maintenance (O&M) phase.

AIE Request: Submissions received on the Consultation on the Draft Arterial Drainage Maintenance Activities 2022-2027 and associated SEA Environmental Report and AA Natura Impact Statement Report

Under the AIE Regs to request copy of the submissions received on the Consultation on the Draft Arterial Drainage Maintenance Activities 2022-2027 and associated SEA Environmental Report and AA Natura Impact Statement Report

The original closing date for submissions was extended by the OPW. There is a statutory obligation for the OPW to consult with the National Parks and Wildlife Service, and the OPW welcome submissions from individuals/bodies during a consultation process.

“I have seen many actions on the river Moy by the OPW destroying the trees along the banks”

East Mayo Anglers Association

Killmastulla Drainage Committee in Tipperary

Response from the Wild Trout Trust

Note: worth a read as a very considered submission that is a good summary of the issues

The Arterial Drainage Act in Ireland has delivered severe dredging, realignment and incision of many watercourses, altering their natural hydromorphological processes and in many cases leading to degradation of channel form and function

East Mayo Anglers, Swinford, Co. Mayo

DAERA NI

LAWPRO Submission

015 Record in public domain

https://cieem.net/resource/response-to-the-opw-consultation-on-the-draft-arterial-drainage-maintenance-activities/

Irish Ramsar Wetland Committee Submission

019 Record in public domain – EPA submission

https://www.epa.ie/publications/corporate/submissions–position-papers/epa-submission-arterial-drainage-maintenance-activities-2022-2027-.php

Coillte and Coillte Nature: Average Number of Employees in 2021 and 2022

AIE Requests 20230040 and 20230041

1) The average number of employees employed by Coillte in 2021 and 2022.
2) The number and principal role of those employees working exclusively within Coillte Nature during 2021 and 2022
3) The number and principal role of those employees working principally, but not exclusively, within Coillte Nature during 2021 and 2022


For the purposes of this AIE request, ‘principally’ is defined as not less than 60% of the work (on the basis of time) being undertaken by the employee relating to Coillte Nature.

2021 – Coillte total 840 employees – 5 working for Coillte Nature (0.6% of the total number of Coillte employees)

2022 – Unknown number of total employees – 6 working for Coillte Nature

Note new position – Dermot Tiernan, Peatlands Manager

Coillte Nature Employees 2021
✓ Ciaran Fallon, Director of Coillte Nature
✓ Declan Little, Environmental & Technical Specialist
✓ Hedda Dick, Coillte Nature Outreach Manager
✓ Karen Woods, Operations Manager
✓ Lynn Sheeran, Financial Accountant


Coillte Nature Employees 2022
✓ Ciaran Fallon, Director of Coillte Nature
✓ Declan Little, Environmental & Technical Specialist
✓ Dermot Tiernan, Peatlands Manager
✓ Hedda Dick, Coillte Nature Outreach Manager
✓ Karen Woods, Operations Manager
✓ Lorraine Rockett, Director of Corporate Finance

WWTP Kylemore Abbey, Galway: discharge licence W294/94R1

AIE 16

Standards for several parameters are set under Condition 2.3 of your discharge licence W 294/94R1. The results show non-compliances with the conditions of your licence.


Glan Agua have taken the time to review this for Kylemore quite thoroughly with the attached being their output which suggests Ferric can be used and should result in a vast improvement in the levels of Phosphorous being measured from the outlet of the system. The proposal to also redirect existing septic tanks to the system also being beneficial.

The NIS is actually viewable on the planning file 11/1003. I don’t believe we actually carried out an AA as would be done now but the NIS was assessed and the council was satisfied with it’s contents.

Review of Kylemore Abbey Wastewater Treatment Plant Report

Glan Agua

The current Emission Limit Values (ELVs) are as follows;
• Biological Oxygen Demand (BOD): 5mg/l
• Chemical Oxygen Demand (COD): 25mg/l
• Total Suspended Solids (TSS): 10mg/l
• Fats, Oils and Greases (FOG): 5mg/l
• Total Phosphorous (TP): 2mg/l
• Orthophosphate (OrthoP): 1mg/l
• Ammonia: 0.2mg/l
• Nitrate: 10mg/l
• pH: 6-9 pH units

The current treatment process consists in the following:
• Multiple septic tanks on the network
• Inlet pump station (directly to primary settlement)
• 2no. precast primary settlement tanks (36,000 L ea.) directly upstream of the RBCs operating in series at the main plant.
• RBC
• Final Settlement Tank (FST)
• Sludge Return
• Phosphorous Reduction
• Polishing Lagoons (Reed Beds)

Whilst the current treatment process capacity cannot be accurately evaluated without additional information, it is fairly unlikely to be able to comply with the extremely stringent ELVs currently in place for the following reasons:


• There are numerous septic tanks on the network, which could lead to excessive retention time, septicity issues and ultimately detrimental impact on the process performances. Rationalisation of the network should be considered so that the remaining septic tanks operate within typical design parameters. This can be seen from the particularly low concentrations of solids and low BOD/TSS ratio in the influent, as well as anecdotal evidence (smell in the 2no. precast septic tanks).


• The storm water network looks to be amalgamated with the sewer network allowing introduction of high volumes of rain/storm water into the treatment system.


• BOD/COD/TSS ELVs
o The BOD/COD/TSS ELVs are extremely stringent. Typical ELVs for an RBC treatment process based on the current influent sample results would be 25mg/l BOD, 125mg/L COD and 35mg/l TSS.


• OrthoP, TP and residual aluminium ELVs
o For the OrthoP and TP ELVs, a chemical removal stage would be required to guarantee the ELVs. Based on the jar tests carried out which have shown the ELVs are readily achievable using chemical phosphorus removal, the system was designed assuming a Fe mole ratio of 3.5mol Fe/mol P. Assuming 29.9d storage, this would mean a coagulant storage tank of around 1000l would be required. 2no. chemical dosing pumps of 10l/h each (based on the estimated peak wastewater flow of 52.7m3/d plus 50% safety factor, i.e., daily peak flow of 79.1m3/d and assumed peak flow of 9.9m3/h) would be required.
o Optimisation of the chemical mole ratio through regular sampling and adjustment of the pumps will allow the process to minimise the risk of residual metal carryover. This would be further strengthened if a tertiary filtration stage was also provided as suggested above based on the BOD/COD/TSS ELVs. An iron probe could be provided; however, it should be noted that the licence does not include for an iron limit either.
o Due to the scale of the plant, and to the high costs associated with an OrthoP online monitor, the provision of this equipment to control the chemical dosing pumps would not be considered as viable.


• Ammonia and TN
o The existing RBCs is unlikely to be able to comply with the extremely stringent current ammonia ELV. With RBCs, the oxygen used for the nitrification reaction is only provided through diffusion from the ambient air to the wastewater when the disc is above the water, and it is therefore difficult to guarantee full nitrification. Available effluent results provided to Glan Agua for 2021 showed that the effluent from the RBCs was nonetheless generally compliant with the ammonia limit.
o For the nitrate ELV, a denitrification zone with nitrate recirculation (so that nitrates generated in the aerobic zone can be returned where BOD availability is greater) would be required – the existing process does not have such a zone and the existing ELV therefore cannot be guaranteed. An anoxic zone would need to be provided to guarantee compliance with the ELV.
o It should be noted that, due to alkalinity consumption by nitrification and coagulant dosing, alkalinity boosting using NaOH may be required depending on the outcome of the stormwater separation process and operational results when resuming ferric sulphate dosing.
▪ Assuming no denitrification, the max. storage volume required for 27.2d storage would be around 2000l, and 2no. 9.2l/h chemical dosing pumps would be required.
▪ If there was an anoxic zone provided upstream of the aeration stage with internal recirculation of nitrates, the denitrification reaction would allow for some alkalinity recovery and drop the requirement to 1500l (29.3d storage) storage and 6.4l/h chemical dosing.
o Finally, it should be noted that the existing polishing lagoons can actually have a detrimental impact on the effluent quality, due to the risk of algae or other organic matter growing in the lagoons, decomposition of vegetation, animal contamination etc. This was not seen for “Kylemore Remote WQ Baseline Data- 01.11.2021” apart from the 19/10/21 sample where the COD concentration at the outlet of the RBC (SW7) was 29mg/l, against 47mg/l at the outlet of the lagoon.

However, it is a risk that should be considered if a larger upgrade of the WwTP besides the provision of chemical dosing was considered

No application form would have been submitted for the review. An application form is only submitted if it’s an application for a new licence. The council issued a notice of review and the licencee submits info based on this. The info submitted by the licencee is what makes up most of volume 2. The NIS is actually viewable on the planning file
11/1003. I don’t believe we actually carried out an AA as would be done now but the NIS was assessed and the council was satisfied with it’s contents.

Department of Housing, Local Government and Heritage – Open Data Strategy

AIE -010-2023

Please see below responses to each of your questions in your request:


1. Any data audits conducted by or for NPWS to identify environmental datasets under the Open Data Directive
No data audits were conducted by of for NPWS in the specified request period of July 22nd 2021 to 18th January 2023 to identify environmental datasets under the Open Data Directive.


2. Directive 2019/1024/EU introduces the concept of high value datasets (HVDs). Please list any HVDs identified by NPWS
The European Commission’s ‘Implementing Regulation laying down a list of specific high-value datasets and the arrangements for their publication and re-use’ was recently published on 21st January 2023. NPWS have not yet identified data sets which meet the criteria specified in this regulation.


3. Under Regulation 4 of SI 376/2021 all Departments/Offices and relevant bodies under their aegis are obliged to supply to the Minister for Public Expenditure and Reform with information as requested from time to time, such as open data progress reports. Provide copies of the NPWS progress reports as supplied to PER.
No NPWS progress reports were supplied to PER in the specified request period of July 22nd 2021 to 18th January 2023.


4. All Departments/Offices and relevant bodies under their aegis must assign responsibility to an officer for matters arising under these Regulations in line with the national Open Data Strategy. Please provide contacts for any Open Data officers appointed at NPWS from 2021 to date.
NPWS is part of the Department of Housing, Local Government and Heritage. The Departments Open Data section can be contacted at : opendata@housing.gov.ie.
No NPWS Open Data officers have been appointed in the request period July 22nd 2021 to 18th January 2023.


5. In line with Regulation 13 of SI 376/2021, the details of any new exclusive arrangements being entered into must be published online at least two months before they come into force. Please provide list of any exclusive arrangements agreed to date by NPWS.
Exclusive arrangements have not been identified to date.


6. Any exemptions sought by NPWS to the release of open data, and which datasets these exemptions related to


NPWS Open Data policy for its biodiversity data is available at
https://www.npws.ie/maps-and-data/open-data-policy#:~:text=NPWS%20Data%20Available%20by%20Request&text=the%20Intellectual%20Property%20Rights%20or,is%20still%20in%20draft%20form

This sets out the key reasons where NPWS biodiversity datasets are not available as Open Data, a follows;
the protection of the environment to which such information relates, such as the location of rare species – see our guidelines on access and usage of NPWS sensitive data;
the Intellectual Property Rights or copyright of the data, or part thereof, belong to a third party that has not given permission for its re-use;
there is personal data in the dataset and data protection restrictions apply; the dataset is unpublished as it is still in draft form.


7. Public Bodies must draft an Open Data Publication Plan. Provide a copy of any NPWS draft or completed open data plans to date
As set out in the data strategy for the Department of Housing, Local Government and Heritage, the Department aims to build and manage an integrated data platform to inter alia deliver open data streams to the public by 2024

(https://www.gov.ie/en/publication/5fb13-data-strategy-foundations-sprint-2021-2024/)

8. All public bodies need to publish details of what data is available for re-use and the licencing conditions that apply (CC BY 4.0 Attribution advised). Please provide a list of (where this differs from data audit list, see above)


Where possible, NPWS publishes biodiversity data as Open Data, licensed under Creative Commons Attribution 4.0 International Licence.

Details of NPWS biodiversity data licencing conditions are available at
https://www.npws.ie/maps-and-data/open-data-policy

NPWS biodiversity data is published to;
NPWS website http://www.npws.ie,
https://www.npws.ie/maps-and-data
ISDE (Irish Spatial Data Exchange)
http://www.isde.ie/geonetwork/srv/eng/catalog.search#/home,
and harvested to;
https://www.data.gov.ie
https://osi.ie/services/geohive/.

NPWS data is also shared directly to the National Biodiversity Data Centre for onward publication via https://biodiversityireland.ie/


Licence details are provided in the metadata associated with each biodiversity data publication.


9. Copy of NPWS’s RPSI Policy (RPSI is Reuse of Public Sector Information)
Departmental level policy is publicly available at https://www.gov.ie/en/organisation-information/cac56-re-use-of-public-sector-information/


Schedule of records
There are no records, no records are provided.