SASA conducts a wide range of activities monitoring wildlife and the environment in support of a raft of legislation.
Its work on aphid monitoring and phenology are vital in the management of aphid-borne viral disease in Scottish seed potatoes.
It provides GM services and serves as the GM Inspectorate for Scotland.
It provides analytical and forensic support for the investigation of wildlife crime incidents and it provides advice on wildlife management to the Scottish Government and a wide range of stakeholder bodies.
In order to ensure that you have access to the most up to date information please sign up to receive regular aphid bulletin E-mails (if you have not already done so) by contacting Fiona Highet (via ‘Contact Us).
The role of aphids as vectors of potato viruses is of concern to the Scottish seed potato industry. SASA operates a national network of suction traps collecting information about aphid abundance and movement, and providing advice on the risk of virus transmission and the need for aphid control.
The suction trap data contribute to a UK network of traps operated by Rothamsted Research. Weekly aphid bulletins are published by the Rothamsted Insect Survey.
The Entomology laboratory provides technical support to the Aphid Monitoring Programme, introduced into the Seed Potato Classification Scheme in 1992. This programme ensures that seed stocks on which aphids have been poorly controlled can be identified, and that subsequent classification of these stocks is dependent upon a post-harvest tuber test for the presence of viruses.
A development programme to improve our understanding of potato virus epidemiology is underway and has improved the accuracy with which virus levels in seed crops can be forecast. See the Scottish Aphid Bulletins page for more information.
SASA also recommends that growers consult with the guidelines on “Virus management in seed potatoes 2020” issued by the Scottish Aphid-Borne Virus Working Group. The guidelines are available via AHDB’s aphid and virus webpage
AHDB Potatoes fund 100 in-crop water traps in the major seed growing areas of Great Britain. The trap contents are analysed weekly at FERA in York, with results posted on the APHMON website. Users of the service can also sign up to receive e-mail and SMS alerts when Peach-potato aphids (Myzus persicae) are found in their region or when aphid catches in any trap in their region exceed a weekly threshold. Comparative information with previous seasons is also available.
The SASA aphid Monitoring pages are updated regularly over the growing season (usually every Friday). Interested parties can contact Fiona Highet (via 'contact us') to receive a weekly bulletin E-mail covering the main Scottish aphid headlines for the week and links to pages for more information. SASA's twitter account also reports aphid news over the growing season, again with links to relevant pages.
View:
The 'Scottish Aphid Bulletin' consists of a table of 21 species, mostly species of major economic significance, and a second table listing all the other 'non-bulletin' aphids caught during the week.
SASA currently operates four suction traps located at Inverness, Ayr, Dundee and at SASA's headquarters at Gogarbank on the west side of Edinburgh. Data from each of these traps are presented as totals for the duration of each report. Only the traps at Edinburgh and Dundee are identified in 'real time' so are presented as cumulative totals and compared to previous years.
Three additional columns of data are also presented under the title of 'Cumulative Totals'. The first presents the total catch from the two traps (Edinburgh and Dundee) for the current year, up to and including the period covered by the report. The second column provides the yearly catch of aphids for the equivalent period during the previous year, i.e. 2020. The final column provides the mean cumulative catch of aphids over the same period during the previous 10 years, i.e. 2011-2020. Presenting the data in this way enables the current year's catch of any species to be viewed in the context of data from both the previous year and an average year. As the last column presents an arithmetic mean, this figure is strongly influenced by those years when the total for that particular species of aphid has been high.
In November 2000, the historic Elgin trap ceased operation due to the sale of the site. A new Elgin trap was erected approximately 4 kilometres from the old Elgin site. This trap started collecting aphids on 16 May 2002, and discontinued in October 2016. A permanent home for the northern trap has now been identified at Knocknagael Stud Farm, Inverness. This trap started running on 18 April 2019,has been added to the bulletin and will be added to cumulative totals in due course.
At the end of 2005, the Edinburgh trap ceased operation at the East Craigs site. It was replaced by the Gogarbank trap located 3 kilometres to the south-west of East Craigs. The 10-year averages for Edinburgh now consist entirely of data from the new trap.
Due to time restraints, data from the Ayr trap will not be included in the Scottish aphid bulletin cumulative totals during 2021. The trap experienced some technical difficulties during 2020 which could not be rectified due to travel restrictions in place; we aim to have this trap running again in June 2021 and hope to be able to identify catches from it in real time during summer 2021 as time allows.
SASA is extremely grateful to the organisations where the traps are sited and to the staff who collect the samples. If you require any further information, or wish to use the contents of the Scottish Aphid Bulletins in any way, please email the Zoology team.
Prolonged exposure to low winter temperatures is known to have lethal and sub-lethal effects on populations of Myzus persicae which, in Scotland, overwinters as larvae or apterous adults. Poor over-winter survival delays the build-up of populations of this species in the forthcoming growing season. Prior to 2011, SASA had used the mean temperature for January and February to predict when M. persicae will become active in the summer. In 2011, following an extremely cold December in 2010, SASA predicted aphid activity based on the mean temperatures during the three-month period of December – February. We intend to continue to use the model based on this three-month period, which explains the slight difference to the dates published by Rothamsted who use Jan/Feb mean temperatures.
During winter 2020-21, the mean temperatures were below the mean over the last 50 years: 3.46°C at SASA (Edinburgh; mean = 4.0°C) and 3.12°C at JHI (Dundee; mean = 3.7°C). These winter temperatures rank the 37th warmest from the last 53 years at Edinburgh and the 39th warmest from the last 55 years at Dundee. Based on these figures, the prediction for the first flight of M. persicae is 23 June at Edinburgh (average date of first catch is 14 June) with 75% confidence limits of 2 June and 13 July. The prediction for the first flight of M. persicae is 26 June at Dundee (average date of first catch is 13 June). Therefore, based on the Edinburgh met data, M. persicae activity in 2021 is expected to commence around 2 weeks later than in an average summer, and around 4 weeks later than in 2020.
NB. Following the closure of Higgins, the Elgin suction trap did not operate in either 2017 or 2018. A new suction trap site at the Scottish Government Farm at Knocknagael, south of Inverness was operational through 2019. It is still a little early to assess how to best utilise these data.
In 2020, the first M. persicae at Edinburgh was recorded on 28 May, 17 days earlier than the average date of first catch and 4 days later than predicted. The first M. persicae at Dundee was recorded on 16 June, 2 days later than the average date and 13 days later than predicted. The first arrival date for Edinburgh and Dundee were within the 75% confidence limits of predictions.
The predictions for the potato aphid Macrosiphum euphorbiae, the rose-grain aphid Metopolophium dirhodum and the grain aphid Sitobion avenae are provided by Rothamsted Research and AHDB (found at https://ahdb.org.uk/aphid-forecasts) and are based on mean temperatures over January and February 2021 (Table 1).
Table 1
|
|
2021 Prediction |
75% Confidence Limits |
2020 Obs'n |
2021 Obs'n |
|
Edinburgh |
||||
|
Myzus persicae |
23 June |
2 June – 13 July |
28 May |
27 June |
|
Macrosiphum euphorbiae |
- |
10 May – 23 June |
20 May |
30 May |
|
Metopolophium dirhodum |
- |
8 May - 26 June |
4 May |
12 June |
|
Sitobion avenae |
- |
19 May - 28 June |
28 May |
19 May |
|
Dundee |
||||
|
Myzus persicae |
26 June |
31 May - 22 July |
16 June |
24-26 May |
|
Macrosiphum euphorbiae |
- |
* |
25 May |
21 June |
|
Metopolophium dirhodum |
- |
* |
4 May |
27 May |
|
Sitobion avenae |
- |
* |
26 May |
4 June |
* - awaiting met data for this site
The colder than average temperatures over 2020-21 winter, indicate that the first flights of M. persicae should be 2-3 weeks later than on average. Based on the AHDB/Rothamsted predictions, other important vector species are also expected to fly later than usual. Consequently, population levels have less potential to develop to levels that could threaten the virus health of seed crops. The prediction for the total of M. persicae caught by 31 July is 12 at Dundee and 11 at Edinburgh. The 75% confidence intervals for these predictions are between 2 and 41.
Therefore, populations of M. persicae are unlikely to be high during the growing season for potatoes in 2021. As a result, despite the increase in the PLRV inoculum observed during 2020, there is no major risk of extensive leaf roll transmission in potato crops in 2021, presenting a risk for the 2022 crop.
From midsummer onwards, the catches of cereal aphids in the suction traps usually dominate the Scottish aphid bulletin and significantly affect the index that is used to estimate the vector pressure for aphid-transmitted potato viruses. Three species, the Rose-Grain aphid (Metopolophium dirhodum), the Grain aphid (Sitobion avenae) and the Bird Cherry-Oat aphid (Rhopalosiphum padi), are known to be vectors of non-persistently transmitted potato viruses (e.g. PVY) and because they can occur in high numbers in the suction traps, each individual species can make a relatively high contribution to the overall aphid vector pressure index. SASA have conducted field trials that support the role of cereal aphids, particularly the Rose-Grain aphid and the Grain aphid, in virus transmission.
As would be expected, cereal aphids are also important pests of cereal crops, causing direct damage by feeding on crops and through the transmission of viruses such as barley yellow dwarf virus (BYDV).
During 2020, all four dominant species of cereal aphids were caught in below average numbers in the Scottish suction traps. For the period when most virus transmission is believed to occur (before July 31), the catches of the Rose-Grain aphid ranked 27th out of the last 32 years, the Bird-Cherry Oat aphid ranked 28th and the Grain Aphid ranked 23rd. These are the three species most strongly associated with the transmission of the most prevalent potato virus (PVY) in Scotland.
It is anticipated that the incidence of plants showing mosaic symptoms in 2021 will be at a lower level compared to what was observed in 2020. A balanced approach to the management of non-persistent viruses and their vectors should be adequate based on the information currently available for the 2021 summer.
Potato varieties that have been revealed by virus testing of leaf samples collected during classification inspections as particularly prone to the acquisition of PVY include King Edward, Harmony, Shepody, Maris Peer and Nicola.
The first cereal aphids of 2021 were caught in the Scottish traps on the week ending 23rd May, with the omission of the Rose-Grain aphid which started a week later.
As the Inverness trap only started trapping in April 2019, we currently report on Edinburgh and Dundee catches only.
Please note that the graphs below represent actual numbers of aphids caught in these two east coast suction traps using a log scale. Viewing population data on a log scale makes it easier to spot subtle changes in numbers when comparing data to the large number of aphids caught in previous seasons.
Rose-Grain aphid in 2021
The first two Rose-Grain aphids (Metopolophium dirhodum) were caught in the Dundee suction trap on 27 May. After a slow start the summer migration appears to have commenced, with cumulative total until 11 July rising to 246, now ranking 22nd over the last 34 years of trapping. This is the one to watch for the next two weeks.

A total of 43 Grain aphid (Sitobion avenae) has been caught in Dundee and Edinburgh to 11 July, ranking 29th from the last 34 years of monitoring. This first individual was recorded at Edinburgh on the 19th May.

Bird Cherry-Oat aphid in 2021
A total of 63 Bird Oat-Cherry aphids (Rhopalosiphum padi) were caught in the Dundee and Edinburgh suction traps to 11 July. The total catch for this species now ranks 27th over the last 34 years.

Apple-Grass aphid in 2021
A total of 389 Apple-Grass aphids (Rhopalosiphum oxyacanthae) were caught in Dundee and Edinburgh to 11 July, ranking 5th over the last 34 years. 14% of individuals were caught at Dundee, 86% at Edinburgh.

The Peach-Potato aphid Myzus persicae has traditionally been considered as the most important aphid vector of potato viruses. However, in Scotland, Peach-Potato aphids generally fly later and in far lower numbers than in warmer countries and their relative scarcity generally makes this species less of a concern to potato growers. In some years, usually following a particularly mild winter, Peach-Potato aphids can present a very high risk of virus transmission, particularly Leaf Roll, within the Scottish seed potato crop.
Prolonged exposure to low winter temperatures are known to have lethal and sub-lethal effects on populations of M. persicae which, in Scotland, overwinter as larvae or apterous adults. Poor over-winter survival delays the build-up of populations of this species in the forthcoming growing season. Prior to 2011, SASA had used the mean temperatures for January and February to predict when M. persicae will become active in the summer. In 2011, following an extremely cold December 2010, SASA predicted aphid activity based on the mean temperatures during the three-month period of December-February. We intend to continue to use the model based on the 3-month period, which explains the slightly different approach taken by Rothamsted who still use Jan/Feb mean temperatures.
During winter 2020-21, the mean temperatures were below the mean over the last 50 years: 3.46°C at SASA (Edinburgh; mean = 4.0°C) and 3.12°C at JHI (Dundee; mean = 3.7°C). These winter temperatures rank the 37th warmest from the last 53 years at Edinburgh and the 39th warmest from the last 55 years at Dundee. Based on these figures, the prediction for the first flight of M. persicae is 23 June at Edinburgh (average date of first catch is 14 June) with 75% confidence limits of 2 June and 13 July. The prediction for the first flight of M. persicae is 26 June at Dundee (average date of first catch is 13 June). Therefore, based on the Edinburgh met data, M. persicae activity in 2021 is expected to commence around 2 weeks later than in an average summer, and around 4 weeks later than in 2020.
The colder than average temperatures over 2020-21 winter indicate that the first flights of M. persicae should be 2-3 weeks later than on average. Based on the AHDB/Rothamsted predictions, other important vector species are also expected to fly later than usual. Consequently, population levels have less potential to develop to levels that could threaten the virus health of seed crops. The prediction for the total of M. persicae caught by 31 July is 12 at Dundee and 11 at Edinburgh. The 75% confidence intervals for these predictions are between 2 and 41. Therefore, populations of M. persicae are unlikely to be high during the growing season for potatoes in 2021. Therefore, despite the increase in the PLRV inoculum observed during 2020, there is no major risk of extensive leaf roll transmission in potato crops in 2021, presenting a risk for the 2022 crop.
Table
| M. persicae | Dundee | Edinburgh |
| First catch in 2021 | 24-26 May | 27 June |
| 1st catch prediction 2021 | 26 June | 23 June |
| Mean date of first Catch | 13 June | 14 June |
| Total catch to 11 July 2021 | 7 | 2 |
| Predicted catch to 31 July 2021 | 12 | 11 |
| Mean catch to 31 July | 44 | 35 |
A recent collaboration between scientists in the Met Office’s Vegetation-Climate Interactions group, the Rothamsted Insect Survey (RIS), University of Warwick, Defra and SASA allow further resolution of Myzus persicae activity predictions in Scotland and the rest of the U.K.
The maps below display the estimated date on which the first 5% of the annual flight of M. persicae will have occurred, using at 1km2 resolution across Scotland. As few M. persicae are caught in Scotland compared to the rest of the U.K., this correlates well with the ‘first catch’ in Scotland but it is worth noting that this is a different measurement, so ‘first flights’ and 5% will be different in areas where a larger number of individuals are caught.
As with first flight predictions there are observable differences between 2020 and 2021 due to the ‘higher than average’ winter temperatures during 2019-20 and the ‘lower than average’ winter temperatures in 2020-21. By using the HadUK-Grid dataset climate scientists can refine predictions to a more local scale which may be of particular use to growers. Note that factors such as land use and availability of host plants are not used in this predictive model.

Nine Peach-Potato aphids have been caught to 11 July, ranking 22nd when compared to the last 34 years.
This first individual was caught in Dundee on 24-26th May (this was a combined catch due to mechanical issues). This is more than four weeks earlier than predicted, and outwith 75% confidence limits. There is limited evidence of in-field aphid activity around Dundee associated with this finding and it is hoped that this individual is an unusual 'outlier'. The second individual in Dundee was caught on 3 July (7 days after the predicted first flight at this site) and the first individuals caught in Edinburgh were caught on 27 June, four days later than predicted and well within the 75% confidence limits.
Note the use of a logarithmic scale to allow better visualisation of lower values following years of high peaks (such as 2019).

The Potato aphid Macrosiphum euphorbiae is often the most numerous of the five or six species of aphids that regularly colonize potato crops in Scotland. It is also a potential aphid vector of non-persistent potato viruses (e.g. PVY, PVA).
As with Peach-Potato aphids Myzus persicae, early season predictions made following the 2020-21 winter indicated that Potato aphid flights should be earlier than in an average year. Therefore, total catches of Potato aphids may be relatively high and consequently the risk of virus transmission within potato crops colonised by Potato aphids have the potential to be higher than average. However, environmental conditions over the early summer do influence population development, and growers should monitor how the populations of this species develop over the season.
Table
| M. euphorbiae | Dundee | Edinburgh |
| First catch 2021 | 21 June | 30 May |
| First catch prediction 2021 (75% confidence limits) | - | 10 May - 23 June |
| Mean date of first catch | 1 June | 24 May |
| Total catch to 11 July 2021 | 9 | 20 |
| Predicted catch to 31 July 2021 | N/A | N/A |
| Mean catch to 31 July | 73 | 57 |
29 Potato aphids have been caught up to 11th July, ranking 25th from the previous 34 years. The first individual of this species was caught at Edinburgh on 30 May. This is 10 days later than in 2020, and within 75% confidence limits.

Inspection of the 2020 Scottish seed potato crop revealed an incidence of crops containing virus affected plants of 22.7% of the total area entered for classification (slightly down from 23.7% in 2019).
The incidence of crops containing mosaic symptoms (i.e. excluding leaf roll) decreased to 18.3% from 21.0% in 2019. Within this 18.3%, the incidence of crops containing plants affected by PVYN was 16.7% (19.0% in 2019) and PVYO was 0.9% (1.3% in 2019). In March 2020, we had predicted that the overall incidence of crops containing PVY would decrease from 19.9% to 16.2% in 2020, based on catches of cereal aphids from just the Dundee and Edinburgh suction traps, using the three most abundant cereal aphids which have been most closely linked with PVY transmission in Scotland. The overall PVY incidence observed in 2020 was slightly higher at 17.5%. A revised model based on 6 species of aphids, predicts that the levels of PVY observed in the last two seasons will decline to around presence of infected plants in 12% of the 2021 Scottish seed crop.
The incidence of crops found to contain leaf roll infected plants increased from 1.7% in 2019 to 4.4% in 2020. Fortunately, the predicted populations of peach-potato aphids did not materialise, and leaf roll is not predicted to increase in 2021. The relationship described by a model based on aphid data before the introduction of aphid monitoring in 1992 can no longer be used. Instead a model based on more recent data and showing a much weaker relationship, suggests that leaf roll will decline to 3.5% of crops in 2021.
The colder than average temperatures over 2020-21 winter, indicate that the first flights of M. persicae should be 2-3 weeks later than on average. Consequently, population levels have less potential to develop to levels that could threaten the virus health of seed crops. Going into the 2021 season, virus inoculum levels for both PVY and PLRV are higher than usual, so effective management of the source of inoculum should be a priority. A balanced approach to the management of both leaf roll and non-persistent viruses and their vectors should be adequate based on the information currently available for the 2021 summer.
Notifiable Pests and Diseases
SASA provides laboratory based diagnostic support to the Scottish bee inspectorate in the identification and control of the statutory bee pests and diseases American Foulbrood, European Foulbrood, Tropilaelaps mites and Small Hive Beetle. Samples submitted by Scottish bee inspectors are examined for the presence of these statutory bee pests and diseases, and if confirmed SASA provides support in the implementation of legislation and control of these diseases.
View more information about bee health in Scotland and the role of the Scottish bee inspectors.
If you think you need to contact a bee inspector, please email Bees Mailbox with your details.
View our Importing bees into Scotland page for more information on the regulations.
Other Diagnostic Services
In addition to testing for statutory pests and diseases SASA also offers the following diagnostic services to Scottish beekeepers on behalf of the Scottish Government:
If you require either of these services, please visit our pages below for further information.
Suspected Poisoning Incidents
Incidents of suspected poisoning of animals (including bees) by pesticides in Scotland are investigated by SASA’s Wildlife Incident Investigation Scheme (WIIS)
The Scottish Government published a Honey Bee Health Strategy in July 2010. The aim of this Strategy is to achieve a sustainable and healthy population of honey bees for pollination and honey production in Scotland by working with stakeholders with an interest in honey bees. SASA has been closely involved in the development and implementation of this ten year action plan. The 2010 strategy is currently under review, results of which will help to form the basis of a new strategy.
Register
Scottish beekeepers can now sign up to Beebase. This allows beekeepers to register their details free of charge on a secure database and allows them access to an extensive range of information on bee health, including up to date information on the distribution of bee diseases. Knowing the location of Scottish bee colonies allows us to manage bee diseases more successfully and improve the health and long term future of Scottish honey bee colonies.
Learn More
Education is a key aspect of the Honey Bee Health Strategy. Take time to familiarise yourself with aspects of good husbandry, biosecurity and the pests and disease that can affect your bees. Advisory leaflets, best practice guides and fact sheets are available on BeeBase . The Bee Health Partnership provide annual bee health workshops and evening lectures to local associations. The SRUC Bee Advisor also provides lectures and practical training on many aspects of bee health and management. Lectures and workshops are advertised locally through associations and through the SBA website.
Monitor for Signs Of Disease
Whilst beekeepers should maintain good biosecurity and keep an eye out for problems at all times, we would also recommend that you carry out at least two specific annual ‘health checks’ on your stocks to look for signs of disease. If you suspect the presence of a notifiable disease or pest in your colonies (foulbroods, small hive beetle or tropilaelaps) then please contact beesmailbox@gov.scot as soon as possible.
Other Useful Information
See also the Scottish Government's Review into Options for Restocking Honey Bee Colonies in Scotland.
Introduction and Biosecurity
Adult honey bees can suffer from a number of pests and diseases, and in some instances these can cause the affected colony to weaken and die.
In cases of colony loss, we would always recommend that a beekeeper carries out a basic hive ‘post mortem’. This should involve checking for common issues such as queen problems, starvation and Varroa control.
Should the reason for the colony loss remain unclear after this examination, SASA offers a limited service where a sample of adult bees is examined for the presence of Acarine mites, Nosema and evidence of Varroa damage. Whilst the results of these tests often provide no further reason for colony loss to the beekeeper the information gathered from these samples allows us to monitor for trends in native pests and diseases, and to check for new threats to Scottish beekeeping. In any instance where colony loss remains undetermined or a transmissible pathogen such as Nosema, chalkbrood or virus is identified/suspected, it is recommended that equipment is sterilised and potentially contaminated material (such as comb) removed. Further information on hive cleaning and sterilising can be found on the national bee unit website.
Submitting a sample for analysis
The adult bees sampled should be as fresh as possible, contain a minimum of 30 bees, and be packaged in a crush resistant container, preferably cardboard. If a plastic container is used, then the bees should be wrapped in kitchen paper to prevent them degrading in transit.
Samples should be clearly labelled with the hive identifier and sent to "Bee Diseases" at the address in the ‘contact us’ box on the right of the screen. Please remember to include your own contact details for reporting of results and any information pertinent to the analysis. This may include the strength of the colony, management and treatment, and any unusual symptoms noted prior to the loss.
Advice without submitting a sample
Alternatively, you can get in touch with Scotland’s Apiculture Advisor Graeme Sharpe, SRUC, who may be able determine the reason for the colony loss based on the colony symptoms and hive management history. Graeme can be contacted at Graeme.Sharpe@sruc.ac.uk - try to include as many details as possible:
Further information on pests and diseases of honey bees
Additional information on pests and diseases affecting adult honey bees can be found in the advisory leaflet ‘Common Pests, Diseases and Disorders of the Adult Honey Bee’ on the [BeeBase] website.
Background
The key requirements for imports from EU member states and the rest of the world are:
1. You must notify all imports in advance via the IPAFFS system. Information about the system and details regarding how to register are available by clicking on the link.
2. You must ensure that consignments from EU member states and the rest of the world are accompanied by a health certificate which has been obtained from the relevant competent authority;
3. Points of entry:
4. You cannot import packages or colonies of bees from any country other than New Zealand.
5. Only queen honey bees accompanied by up to 20 attendants can be imported into GB from the EU and any other third country, except New Zealand.
For full information on importing bees into Scotland, please see the following guidance.
If you have any queries about the import requirements for honey bees, please contact the Bees Mailbox.
Post Import Controls
These controls are aimed at reducing the risk of the introduction and spread of exotic bee pests, in particular Small hive beetle and Tropilealaps mite (which are notifiable in the UK). When you receive a consignment of imported honey bees you must:
1. Transfer the queens to new queen cages before they are introduced to any local colonies
2. Send the original cages, attendant worker bees and other material that accompanied the queen bees from their country of origin to SASA within 5 days of receipt for examination for the presence of the Small Hive Beetle and Tropilaelaps mite.
How to send a sample
Following removal of the queen, all queen cages and attendant bees should be contained within a sealable plastic bag and (where possible) stored in a freezer overnight, or until ready to post. Please retain the material in this sealed bag, package it securely in a rigid box, and send to the below address, along with your contact details and the CHED reference number (found on part I of the CHED form.
Bee Health – Imports
SASA
Roddinglaw Road
Edinburgh
EH12 9FJ
Since its first discovery in England in 1992 the parasitic mite, Varroa destructor, has spread to infest colonies of honey bees throughout the UK. It has caused massive economic losses and expense for beekeepers, and its destructive power is evident from the huge number of colonies lost since it first arrived in Europe. Varroa management has now become a routine and essential part of bee husbandry.
In Scotland, some remote areas remain free from this damaging bee pest. To support these areas of varroa freedom, SASA offers a varroa screening service based on samples of floor debris or hive inserts (the natural drop method of monitoring).
Submitting a sample for analysis
Samples should be clearly labelled with the hive identifier and sent to "Bee Diseases" at the address in the ‘contact us’ box on the right of the screen. Please remember to include your own contact details for reporting of results.
Further Information
Further information on the varroa mite, its management, and how to interpret your results is available in the excellent ‘Varroa Management’ leaflet available on the [BeeBase] website
GM Team
The Scottish Government opposes the cultivation of Genetically Modified (GM) crops which could damage Scotland's rich environment and threaten our reputation for producing high quality and natural foods. The Scottish Government believes GM cultivation would diminish Scotland's image as a land of food and drink.
Taking account of this policy, SASA provides advice on the release of GM crop plants and other organisms (GMOs) into the environment and on the contained use of GMOs. In addition the GM team provides GM diagnostic testing services.
GM Inspectorate
The GM Inspectorate is also based at SASA. Key services provided are:
SASA also provides a diagnostic testing service for the GM Inspectorate.
Advances in molecular biology made in the mid 1970s enable the genetic material of an organism (either DNA or RNA) to be altered using methods that do not occur in nature. These alterations are known as genetic modification (GM) and plants, animals or microbes resulting from such modifications are known as genetically modified organisms (GMOs). GM covers a variety of techniques which have been applied worldwide in human and veterinary medicine, horticulture, agriculture, biotechnology and for research purposes.
GM raises important safety issues for human health and protection of the environment. European, Scottish and UK GM legislation requires that these are addressed at every stage of a GMO’s (or GMO product’s) development, starting in the laboratory through to commercial production (see the GM Regulatory Framework page).
GMOs are primarily regulated through EU legislation with supporting UK and Scottish legislation.
For detailed information, see the Genetic Modification (GM) Legislation page on the gov.scot website.
All work involving GMOs is regulated. Work carried out in laboratories, glass houses or which is otherwise contained, where there is no release into the environment, is considered ‘contained use’ work. The HSE is responsible for assessing risk to human health of all work involving the contained use of GMOs in the UK. The GM team at SASA and scientific experts from other Scottish-based organisations provide advice about the environmental risk of contained use GMO work to be carried out in Scotland. For more information on working with GMOs in a contained way and how to notify your work, or apply for consent see the HSE webpage.
Consents for releasing GMOs into the environment for research purposes are granted on a case by case basis by Scottish Ministers. A detailed risk assessment must be submitted to the GM team at SASA, and is considered by ACRE (Advisory Committee on Releases to the Environment). ACRE comprises independent scientific experts who advise on the risks to human health and the environment from the release of GMOs. Scottish Ministers also take advice from SASA, the Health and Safety Executive, the Food Standards Agency and Scottish Natural Heritage as appropriate. Consents set out the conditions and limitations governing releases.
Consents for releasing GMOs for commercial reasons are granted at the EU level and are effective throughout the EU. The EU legislation has recently been amended to allow member states to opt-out or ban GM cultivation on their territory. This legislation allows member states and regions to ban biotech crops for reasons other than the risks to health and the environment assessed by the European Food Safety Authority (EFSA).
Compliance with the above regulations is established by official inspection. Non-compliance with consent conditions can lead to enforcement action including forwarding cases to the Procurator Fiscal Service where necessary. SASA has taken responsibility for the inspection and enforcement of the deliberate release and marketing of GMOs (principally crops plants) in Scotland since May 2000. For England and Wales, GM inspection and enforcement services for the deliberate release of GMOs are provided for Defra by the Animal and Plant Health Agency (APHA).
Allied to the GMO regulations are traceability and labeling rules, 1830/2003/EC, which include a threshold of 0.9%, above which the adventitious (accidental) presence of material from an EU authorised GMO in a non-GM product triggers traceability and labelling of the product. Enforcement of these regulations (1829/2003 and 1830/2003) in Scotland is the responsibility of Local Authority Environmental Health (food) or Trading Standards (feed) Departments.
EU legislation on seeds (notably Directive 2002/53/EC on the Common Catalogue of varieties of agricultural plant species and 2002/55/EC on the marketing of vegetable seed) requires national authorities that have agreed to the marketing of seed of a certain variety on their territory to notify the acceptance of the variety to the European Commission. Seed legislation also requires that genetically modified varieties must be authorised in accordance with EU Directive 2001/18/EC amendment 2018/350 before they are included in the Common Catalogue and marketed in the EU.
GM Team
The GM Team provide advice and technical support to Scottish Government colleagues and participates in UK committees on experimental deliberate release and contained use of GMOs (SACGM and ACRE). They also administer and provide assessors for applications for the Contained Use of GMOs in Scotland. They are full members of ENGL (the European Network of GMO Laboratories) providing input into EU level GM technical documentation, and also through ENGL, other international technical documentation such as ISO standards. They provide analytical testing to support enforcement activities, and also strategic development and improvement of molecular methods for use in GMO testing.
GM Inspectorate
Scottish Government GM inspectors are appointed under Part VI of the Environmental Protection Act 1990. The work is in support of the CAP Reform and Crop Policy Branch of the Rural and Environment Directorate who are Scotland’s Competent Authority for the regulation of the deliberate release of GMO’s under EC Directive 2001/18.
For details of the GM legislation that inspectors work to see the GM Regulatory Framework page.
The Animal and Plant Health Agency (APHA) is authorised by Defra to carry out equivalent inspection and enforcement services in England. SASA liaises closely with the GM Inspectorate in APHA, particularly in sharing information about seed material that crosses borders for production or marketing, and incidents that are common to both England and Scotland. Northern Ireland and Wales have separate arrangements.
Genetically modified crops are steadily being grown more widely throughout the world since they were first commercialised in 1996. Where GMO crops are grown in seed producing areas, there is a risk of cross-pollination or GM seed inadvertently becoming mixed amongst conventional (non-GM) seedlots. This is known as adventitious GM presence (AGMP).
To assist Scottish merchants, processors and packers (MPP) minimise the risk of marketing seed that may contain AGMP, the GM Inspectorate runs a voluntary scheme to determine whether seed of high risk species has been imported directly into Scotland. Questionnaires are sent out to all MPPs biannually.
To assist seed producers or importers who wish to market agricultural seed for the purposes of tests and trials see Guidance to market seed for tests and trials.
It is important to note that participation in the monitoring programme should not be seen as an assurance that the GM Inspectorate will not exercise its powers in appropriate cases under Part VI of the Environmental Protection Act 1990.
Questionnaires can be returned by email or post. The address for email returns is: GMInspectorate@sasa.gov.scot. Postal returns should be sent to Scottish Government GM Inspectorate, SASA, Roddinglaw Road, Edinburgh, EH12 9FJ.
For a summary of the biannual surveys and any resulting follow-up action please see GM Inspectorate Publications.
In seed producing areas where GM crops co-exist with seed crops of conventionally bred varieties, there is a risk that seed from conventionally bred seed may inadvertently contain GM seed (AGMP) through cross-pollination or physical mixing of seed during processing. The legislative EU framework requires the labelling of conventional seed lots that contain any detectable traces of authorised GM seeds. If unauthorised GM seed is found in conventional crop seed, there is zero tolerance and the affected seedlot cannot be marketed.
Risk analyses undertaken on conventionally breed crops suggest that some species are at a higher risk, relative to other crops, from incorporation of adventitious GM material during seed production. Crops that are important to Scottish Agriculture that fall into this high risk category are:
The risk status of all crop species listed above is regularly reviewed.
Importers, producers, processors and merchants of non-GM (conventionally bred) agricultural and vegetable seed are recommended to take all reasonable steps to ensure, before obtaining or marketing high risk category seed it is free of AGMP (see relevant Guidance pages).
Anyone considering marketing seed of certified, conventionally-bred crop varieties in Scotland that are of a high risk category of containing adventitious GM presence are advised to:
In Scotland, high risk category species are winter and spring oilseed rape, turnip fodder rape & related species, fodder maize & sweet corn.
This information will assist your company to meet your legal duties to ensure that you have taken steps to minimise the risk of adventitious GM presence in conventional seed. It will also help you in answering customers questions relating to adventitious GM presence.
Should you have any queries over these measures contact the Scottish Government GM Inspectorate.
Seed importers that have made a seed declaration on the Scottish Government GM Inspectorate’s Seed Monitoring form are advised to:
These measures should follow the GM Inspectorate Guidance for importers and producers on the prevention of adventitious GM presence in conventional varieties of the relevant crops.
It is the role of the Scottish Government GM Inspectorate to audit seed importers to ensure appropriate steps (due diligence) have been taken and that appropriate documentation is available. We will contact import companies and will request access to the following information:
Should you have any queries over these measures contact the GM Inspectorate.
It is a requirement under the Seed (Scotland) (Amendments for Tests and Trials etc.) Regulations 2007 (2007 No. 224) and Regulation 9 of the Beet Seed No.2. (Scotland) 2010 (2010 No. 148) that authorisation is given by either the Scottish Government or another European Authority for seed to be marketed for the purposes of conducting tests or trials, including tests for scientific purposes and selection work.
Breeders or Merchants, Processors or Packers based in Scotland should apply for the authorisation to use seed for these purposes by contacting SASA either in writing to Seed Certification Branch, using GM Inspectorate email address or by telephoning Mike Parker (0131 244 8853).
For those species that have a high risk category of containing adventitious GM presence, the Scottish Government GM Inspectorate also recommends that you obtain a letter of assurance from the breeder of the variety giving assurances that the seed is free from adventitious GM presence or obtain details of analytical tests on individual seed batches or seedlots, that follow the GM Inspectorate Guidance for importers and producers on the prevention of adventitious GM presence in conventional varieties of the relevant crops.
Should you have any queries over these measures contact the GM Inspectorate.
The GM Inspectorate investigates incidents that arise by through their routine duties or through enquiries that have been brought to the attention the Scottish Government’s CAP Reform and Crop Policy Branch.
Previous incidents have involved the trialling of conventional varieties which contained adventitious GM seed that were not authorised for cultivation.
For information on any case by case investigations please see GM Inspectorate Publications.
The Scottish Government GM Inspectorate directly monitored, or oversaw monitoring of, three sites where inadvertent sowings of GM crop seed took place in September 2008. Monitoring was continued until the autumn of 2011 with no further presence detected.
Although all Scottish consents for GM crop research trials have expired, landowners of former GM research trial sites, particularly those for oilseed rape, still have an obligation to ensure the produce of following conventional crops complies with the traceability and labelling requirements for food and feed products of GMOs (EU Regulation 1830/2003). This is because GM oilseed rape volunteers can persist at levels that may require a following non-GM oilseed rape crop to be labelled as ‘GM’
Deliberate release of GMOs for research purposes are authorised under Part B of the Deliberate Release into the Environment of GMOs Directive, 2001/18/EC amendment 2018/350. These are small scale releases carried out under tight control. Many research releases involve trials of GM crops in field plots but, increasingly, research releases can include medical trials of GM pharmaceuticals such as vaccines administered under controlled conditions in hospitals and clinics. Consents for releasing GMOs into the environment for research purposes are granted on a case by case basis by Scottish Ministers. A detailed risk assessment must be submitted to the GM Team at SASA, and is considered by ACRE (Advisory Committee on Releases to the Environment).
Brief outline of application process for research releases:
This is a brief outline of the process, for more detailed information please contact the GM Team at SASA.
Competent Authority for Deliberate Release to the Scottish Environment
CAP, GM and Agriculture Climate Change Branch
Scottish Government, Agriculture and Food Division
D Spur
Saughton House
Broomhouse Drive
Edinburgh EH11 3XD
Telephone: 0131 244 9503
UK Lead Territorial Competant Authority for Deliberate Release
Department for Environment, Food and Rural Affairs,
GM Policy, Science and Regulation Unit
Area 3B, Nobel House
17 Smith Square
London SW1P 3JR
Government GM web sites
Scottish Government – Genetic Modification
Defra GM (Genetic Modification) (Department for Environment, Food and Rural Affairs)
Government Advisory committees
Advisory Committee on Releases to the Environment (ACRE)
Scientific Advisory Committee on Genetic Modification (Contained Use (SACGM)
SACGM Compendium of Guidance
Advisory Committee on Novel Foods and Processes (ACNFP)
Other public bodies/Agencies
Food Standards Scotland
Health and Safety Executive (HSE)
APHA GM Inspectorate (the English GM Inspectorate)
Legislation
Directive 2001/18/EC the European directive covering GM releases to the environment and amendment 2018/350
Directive (EU) 2015/412 amending Directive 2001/18/EC as regards the possibility for the Member States to restrict or prohibit the cultivation of GMOs in their territory
The Environmental Protection Act (1990)
The Genetically Modified (Deliberate Release) (Scotland) Regulations 2002
The Genetically Modified Organisms (Contained Use) Regulations 2014
International bodies
ENGL European Network of GM Laboratories
ISTA GMO Proficiency Tests (International Seed Testing Association)
GMOs authorised for Deliberate release in the EU for marketing and import
GMO Register
Application and consent process for research purposes in the UK
Genetically Modified Organisms: Applications and Consents
Many aphid species are specialist herbivores and major pests of agriculture, forestry and horticulture. They have short generation times and rapid growth rates making them one of the invertebrate groups that are most sensitive to climate change.
SASA monitors aphids caught in four 12.2m suction traps operated continuously at Dundee (since 1967), Edinburgh (1969), Elgin (1970) and Ayr (1974). Daily records of abundance of aphid species are available from the main aphid flight season and weekly records from other times.
Within the EU-funded EXAMINE project a consortium of scientists involved in collecting national data on aphid distribution has developed one of the most comprehensive databases for any terrestrial invertebrate group anywhere in the world. EXAMINE covers a network of standard suction traps established in 22 countries, providing a unique resource for studies on the impacts of global change on phenology and abundance(http://www.rothamsted.ac.uk/examine/).
Negative trends were found when the dates of first capture in the Scottish suction traps were examined for 43 out of 46 aphid species over the period 1971–2004. Twenty of these 43 trends were statistically significant and the mean trend indicates that over this 34-year period the date of first capture in 2004 was earlier by 0.47 days/annum or 16 days in total. The average response to temperature was 12.5 days/°C. The green spruce aphid (Elatobium abietinum) has advanced by 4.3 days/decade and 8.1 days/°C and has been proposed as an indicator species for looking at terrestrial phenology (Sparks et al., 2006).

Live aphid data are available on the Aphid Monitoring Programme pages in the form of weekly bulletins. More specific requests should be made to Zoology@sasa.gov.scot.
Suction trap catches can be used to study changes in the biodiversity of a wide range of insect groups. Only aphids are currently identified, but historic catches are retained at SASA.
Sparks, T.H., Collinson, N., Crick, H., Croxton, P., Edwards, M., Huber, K., Jenkins, D., Johns, D., Last, F., Maberly, S., Marquiss, M., Pickup, J., Roy, D., Sims, D., Shaw, D., Turner, A., Watson, A., Woiwod, I. and Woodbridge, K. (2006). Natural Heritage Trends of Scotland: phenological indicators of climate change. Scottish Natural Heritage Commissioned Report No. 167 (ROAME No. F01NB01)
Wildlife crime manifests itself in many ways from the illegal international trade in wildlife to the deliberate persecution of animals. Investigating wildlife crime often requires an unusual set of forensic tools, and here at SASA we have expertise relating to chemical analysis of suspected animal poisoning, and also wildlife DNA forensics.
The illegal poisoning of animals is a particular crime that has persisted in Scotland for decades. It is no surprise that pesticides have emerged as the poisons of choice. Many pest control products (pesticides or biocides) are designed to kill or control invertebrate (insect) or vertebrate (rodent) pests. However, if these chemicals are used incorrectly they can be extremely toxic to animals and humans.
SASA specialises in the detection, identification and quantitation of a wide range of chemicals involved in illegal poisoning. A variety of specimens such as suspected victims and baits, suspicious substances and poisoning paraphernalia are submitted for chemical residue analysis. Analytical results obtained are used as evidence in criminal proceedings or for enforcement of Scottish Government policies. SASA chemists can also be cited to appear as expert witnesses.
Wildlife Management staff undertake Wildlife Incident Investigation Scheme (WIIS) field investigations involving the suspected illegal use of fumigation products, and provide advice to statutory authorities, such as the Police, on the legalities of traps and snares.
At SASA, we carry out wildlife DNA forensic analysis for the police and other organisations involved in wildlife crime investigation. Investigators can find a wide range of evidence that can be subjected to forensic DNA analysis: from trace samples such as blood, fur or feathers, to powdered medicines or ornamental carvings.
At its broadest level, this evidence can be used to identify the species present. From trace evidence or processed products it is often not possible to identify the species present without using DNA based species identification.
Following species identification, it can be necessary to carry out more detailed DNA profiling to tie a suspect to a specific crime. For example paternity testing of captive birds of prey can determine whether the breeding records are correct, or whether birds may have been illegally collected from the wild. It is also possible to use DNA profiling to match a trace sample, such as blood on a suspect’s clothing, to a specific animal carcass – tying the suspect to a specific crime.
In addition to analysing evidence in ongoing wildlife crime investigations, we also carry out research to improve the variety of DNA tests available for the forensic analysis of non-human samples.
SASA is setting up a DNA database to provide a unique identifier for individual rhinoceros horn in UK museums and also zoo animals. This is in response to an increase in rhino horn theft from museums in recent years and an initiative by UK enforcement to crack down on this illegal activity perpetrated by criminal gangs. Unique DNA profiles will be generated from small samples of horn, which will help trace the origin of any stolen rhino horn intercepted by the police or customs.
Museums interested in getting involved with this project should email wildlifeforensics@sasa.gov.scot for more information.
We work in conjunction with Police Scotland and fully support their wildlife crime awareness campaign. For more information on this campaign please see the Police Scotland website.
Incidents of suspected poisoning of animals by pesticides in Scotland are investigated. The aim of the scheme is to identify any adverse effects on non-target animals that might arise from the approved use of pesticides. If the data gathered by the scheme, and sister schemes throughout the UK, indicate a particular problem, then the registration status of the pesticide concerned is subject to review by the UK regulatory body. The data are also used in the validation and improvement of risk assessments for existing and new compounds.
In cases where there is evidence to indicate either the misuse or the deliberate abuse of pesticides, the results of investigations may also be used in the enforcement of legislation affording protection to animals.
Wildlife Management staff undertake WIIS field investigations involving the suspected illegal use of fumigation products, and provide advice to statutory authorities, such as the Police, on the legalities of traps and snares.
Annual reports on animal poisoning in Scotland from 1999 to 2012 can be downloaded from the Animal Poisoning Reports page.
There is an on-going requirement to develop and refine high quality analytical methodologies to meet demands associated with the introduction of new pesticides, to deal effectively with any concerns relating to existing pesticides, and to make analytical efficiency gains.
Find out more about the analytical techniques currently available.
See also the list of Pesticide & Chemical Analysis papers and poster presentations.
Information on how to go about reporting pesticide incidents
Incidents of suspected poisoning of animals in Scotland involving;
should be notified as soon as possible to WIIS-Scotland.
Samples may be submitted to the scheme via

Useful Links
The Health and Safety Executive's Chemicals Regulations Division provides information on pesticides, biocides and WIIS UK.
Environmental contamination incidents in Scotland should be reported to the Scottish Environment Protection Agency (SEPA) Pollution Hotline 0800 80 70 60.
General information on reporting other types of pesticide incidents is available from HSE.
Covering post mortem examinations and pesticide analysis
Post mortem examinations are undertaken by SAC Consulting Veterinary Services, a division of Scotland's Rural College (SRUC), and are an essential element of the investigation. Other causes of death that may be unrelated to possible exposure to a pesticide can be identified, eliminating the requirement for analysis. Alternatively evidence consistent with poisoning being the cause of death may be gained, and appropriate tissue samples taken for analysis
Field information is used together with the findings of the post mortem examination to determine the extent of any analytical investigation. Analytical techniques and equipment capable of identifying low levels of pesticides considered to present possible hazards to vertebrates or beneficial insects are employed. Multi-residue methods are employed where possible. Three methods are routinely used: covering a range of insecticides, fungicides and herbicides; anticoagulant rodenticides; chloralose, metaldehyde and strychnine. These are supplemented by compound-specific analytical methods as necessary. Residues identified are subject to rigorous confirmation criteria for acceptance. The laboratory operates to an internal quality system accredited to the ISO 17025 standard for testing laboratories by UKAS, with some of the above methods included in the scope of accreditation.
Our accreditation is limited to those activities described on our UKAS schedule of accreditation, see our [QA page].
Field information and residue data are assessed, and where possible incidents of poisoning attributed to one of the following categories of use:
Approved use
Misuse
Abuse
Background
Veterinary use
Unspecified use
View more information about these categories on the WIIS Quarterly Reports page.
At the conclusion of each investigation, an individual incident report is issued to the person who initiated the incident and to partner organisations which participated in the investigation.
A database of incident information (1972 onwards) is maintained, and can be interrogated to provide information required by the Scottish Government and to service requests from other parties.
Requests for information should be directed to wiis-scotland@sasa.gov.scot.
Details of incidents where pesticides poisoning has been shown to be the cause are forwarded to the UK regulatory body, Chemicals Regulation Division (CRD). The data are included in annual reports on the poisoning of animals by pesticides, published by the Environmental Panel of the Advisory Committee on Pesticides. In addition CRD selectively request information from the WIIS database (1972 onwards) to support the ongoing approvals review process.
Incidents involving the suspected deliberate abuse of pesticides are actively pursued by Police Scotland supported by Scottish Government Rural Payments & Inspections Division (RPID) Staff and other partner organisations, with a view to eventual prosecution.
Information on pesticide legislation can be found on the Health & Safety Executive (HSE) website through the link in the Related Links box on the right of the screen.
The results of incidents involving pesticides have, until now, been published quarterly in January, April, July and October. It is now our intention that the results of all incidents reported to SASA will be available in a searchable spreadsheet which will still be published quarterly. However, due to the nature of some incidents and the investigations relating to these it may be necessary to limit the information published. We will publish updates to such cases as further information becomes available. This new reporting format will replace SASA publication of the annual Pesticide Poisoning of Animals Report – A Report of Investigations in Scotland.
To make the information clearer all reported incidents will now identify whether the pesticides found in an incident were the principle cause of the incident or present at background or trace levels only. The information will be presented as follows:
Pesticide involved: An investigation into the circumstances of the case concluded that these pesticide(s) were the principle cause.
Other Pesticides found: An investigation into the circumstances of the case concluded that these pesticide(s) were present, but were at background or trace levels only.
From 2013 information regarding the categories will also be clearer and where appropriate provide additional information as it relates to the results. For example, where the death of an animal is from a cause other than pesticide poisoning and the other cause is known this will be reported under additional information. The categories used to classify pesticide poisoning incidents are:
Approved use: An investigation into the circumstances of the case concluded that the pesticide(s) involved were used in accordance with their conditions of authorisation. Where an animal is involved the cause of death has been established as pesticide poisoning.
Misuse: An investigation into the circumstances of the case concluded that the pesticide(s) involved were not used in accordance with their conditions of authorisation. The pesticides involved may have been used carelessly or accidently but there was no indication of any intention to deliberately harm wildlife or other animals. Where an animal is involved the cause of death has been established as pesticide poisoning.
Abuse: An investigation into the circumstances of the case concluded that the pesticide(s) involved had been used in breach of their authorisation conditions and that this has been done with the deliberate intent of harming or attempting to harm wildlife or other animals. Where an animal is involved the cause of death has been established as pesticide poisoning.
Unspecified: An investigation into the circumstances of the case could not establish where the pesticide may have come from and therefore if the pesticide(s) involved were used in accordance with their conditions of authorisation; if the pesticide had been misused or whether or not there was a deliberate intention to harm wildlife or other animals. Where an animal is involved the cause of death has been established as pesticide poisoning.
Unknown: The cause of death has not been established as pesticide poisoning; an investigation into the circumstances of the case could not establish a cause of harm or death and found no evidence of the involvement of pesticides.
It is not always possible to establish that pesticides are involved in a case reported under the scheme; this may be because samples are not available for chemical analysis or because the results of analysis are inconclusive. Where a case is classified as unknown and this was due to a problem with the availability or quality of samples this will be reported under additional information.
Other cause: The cause of death has not been established as pesticide poisoning; an investigation into the circumstances of the case found no evidence of the involvement of pesticides and was able to attribute another probable cause.
Where a case is accepted into the scheme and another cause of death is identified it is less likely that samples will be tested for the full range of chemical analyses, although analysis may still be undertaken in cases where pesticides are strongly suspected. Where a case is classified as “Other cause” the cause of death will be identified as far as possible and will be reported under additional information. Other causes include trauma (road traffic accidents, shooting, etc.), disease or starvation.
Not applicable: An investigation into the circumstances of the case was not able to establish a link to pesticide use. No wildlife or other animals were involved and any suspected baits or other samples contained no detectable pesticide residues.
Veterinary use: Where it is established that veterinary products are involved in a case. These cases are not formally included in the WIIS scheme but are recorded as some actives substances in veterinary products are also found in pesticides. Cases involving veterinary products are categorised separately under the scheme and their use is not classified into abuse, misuse, approved use or unspecified use.
Species or Samples involved: The species or samples that are collected or identified as involved in the case. Samples collected and analysed under the scheme include the bodies of wildlife and animals, which may be sent for post mortem and associated tests, tissue and other samples sent for chemical analysis, and samples of baits and suspicious substances. Samples also include beneficial insects (bees) which may be assessed for disease and analysed for pesticide residues. All available information, including the result of the analysis of samples, is taken into account in assigning cases to a category.
For results prior to 2013 information will continue to be present in the old format as follows:
Approved use: a pesticide is used in accordance with its conditions of authorisation
Misuse: the product has not been used according to the conditions of its authorisation, but often just carelessly or accidently, without the intention of harming animals
Abuse: a pesticide has been deliberately used in an illegal manner to poison, or to try to poison animals
Background residues: residues of pesticides found but levels are probably not indicative of lethal poisoning
Unspecified use: the cause of death was uncertain or the incident could not be classed as being in one of the other categories
Veterinary products: Incidents arising from veterinary use are not included in the scheme
Scientific advice and technical expertise are provided to Scottish Government (Agriculture and Rural Economy Directorate, and Environment and Forestry Directorate) where conflict arises between mammalian and avian wildlife, agriculture, fisheries and game. Advice relates to policy matters, changes in UK or EU legislation, licensing advice to SNH regarding the killing and taking of protected species and general advice regarding any aspect of vertebrate management procedures.
Wildlife Management staff
Spring Traps
See our trap guidance page for information on Spring traps, including instructions for DOC traps and Tully Trap baffles.
Representational duties of Wildlife Management staff
These include:-
Wild boar sightings in Scotland
See our Wild boar sightings in Scotland page.
Contact
Email our wildlifeunit@sasa.gov.scot
DOC Trap Guidance
Predator Traps Instructions UK (published 10/2/21)
Tully Trap Guidance
Tully Trap Grey Squirrel Baffle Instructions (published 10/2/21)
Trap Guides
SASA Guide to Approved Spring Traps
Spring Trap Approvals
Spring Traps Approval (Scotland) Amendment Order 2020
Spring Traps Approval (Scotland) Amendment Order 2018
Spring Traps Approval (Scotland) Order 2011
Wildlife Management Research on Goodnature traps
Hedgehog interactions with the Goodnature trap
Please submit the following details to info@sears.scotland.gov.uk:
If you are happy to be contacted back, please provide your name and contact details. If not, please write "DO NOT CONTACT".
This reporting service is not operated by SASA but will forward the information you provide to the relevant bodies such as NatureScot (SNH).
Other useful links:
The following links are hosted on the Global Biodiversity Information Facility using data from a number of sources: