Landscape and visual impact assessment

Understand where the development will be seen and in what setting

We review landscape character and the project features influencing perception, including location, dimensions, layout and relationships with existing buildings or vegetation. Viewpoints and viewing directions are selected for the assessment purpose. Available spatial information and agreed field material are used with their currency and level of detail explained, including limitations affecting the analysis.

The assessment combines visibility analysis with interpretation of the significance of the anticipated change. Visibility alone does not determine the scale of landscape impact. Background, screening and the use of observation locations are considered, while alternatives are compared using consistent assumptions. Maps and analytical visualisations explain these relationships rather than simply displaying the proposed structure.

Conclusions identify options worth considering, such as location, layout or setting adjustments where relevant to the project. Visualisation detail is agreed before work starts; photorealistic promotional imagery is not assumed. We also explain how season, input data and viewing position influence the representation, enabling readers to interpret the scenarios appropriately.

Technical data

Subject The development's relationship with the landscape and visibility from selected locations.
Service type Landscape assessment and visual impact analysis.
Assessment basis and requirements Project parameters, spatial data, agreed viewpoints and the selected level of visualisation detail.
Method
  1. Review landscape character and project features relevant to visibility.
  2. Select viewpoints and prepare spatial information for the assessment.
  3. Analyse visibility and compare alternatives using maps and visualisations.
  4. Interpret effects and identify mitigation options alongside assessment limitations.
Delivery model KFB Enviro with a partner/subcontractor

What you receive

You receive a report, maps and analytical visualisations at the agreed level of detail. The package identifies viewpoints, assumptions, comparison results and limitations. Conclusions address the development's relationship with its surroundings and possible mitigation measures. Visualisation scope is defined for the assignment and does not automatically include photorealistic or marketing materials.

Scope and limitations

Level of visualisation to be agreed

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Preliminary land contamination risk assessment

Locate potential risks before commissioning intrusive investigation

We reconstruct site uses from available historical material, process documentation and information supplied by the owner or operator. The review looks for locations associated with substance storage, production, waste handling and incidents that may have affected the ground. Confirmed facts are distinguished from assumptions and areas where reliable information is limited or absent.

Potential sources are connected to possible contaminant migration pathways and current or proposed land uses. Existing investigation results are reviewed in terms of location, age and actual coverage. This identifies questions already partly answered and areas needing targeted investigation, rather than selecting sampling locations without a clear link to the site's history.

The preliminary review helps define the next stage but does not demonstrate that an entire property is free from contamination. An absence of recorded incidents is not proof that none occurred. Findings help investors, operators or transaction advisers consider additional documents, intrusive investigation or clarification of a specific risk before making further commitments.

Technical data

Subject Historical and current potential sources of land contamination.
Service type Preliminary risk assessment using site history and available evidence.
Assessment basis and requirements Historical records, process descriptions, earlier investigations and the intended use of the property.
Method
  1. Review site use history, process documentation and existing investigation results.
  2. Identify potential sources and gaps in the historical evidence.
  3. Connect sources with migration pathways and relevant land uses.
  4. Propose a further investigation programme targeting the identified risks.
Delivery model KFB Enviro with a partner/subcontractor

What you receive

You receive a preliminary report and programme of next steps identifying potential contamination sources, the quality of available evidence and significant uncertainties. Recommendations organise the need for further documentation or investigation. The material helps commission purposeful follow-up work and explains which conclusions cannot yet be supported by a review of the property's history alone.

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Soil and groundwater investigation planning and coordination

Design an investigation around the site's actual questions

Site history, earlier findings and the assignment's purpose determine which areas and substances need investigation. The programme proposes locations, depths and sample types appropriate to the available understanding. Access restrictions, infrastructure and practical arrangements are considered so issues requiring clarification can be addressed before specialist teams enter an operating facility or development site.

We coordinate agreed fieldwork and laboratory analysis undertaken by partners or subcontractors. Samples are linked to their locations, field records and commissioned analytical scope. When results are available, we check completeness and interpret the evidence against the investigation purpose, site conditions and relevant criteria, explaining the limitations associated with the representativeness of the samples collected.

Findings inform whether the investigation is sufficient or needs to be extended in coverage or analytical scope. A single campaign does not automatically describe changes in groundwater quality over time and is not a complete monitoring programme. Measured findings are clearly distinguished from interpretation between investigation points, avoiding unjustified certainty in subsequent decisions.

Technical data

Subject Soil and groundwater at locations selected for the investigation purpose.
Service type Planning and coordination of field investigation and laboratory analysis.
Assessment basis and requirements Site investigation model, sampling programme and interpretation criteria selected for the media, substances and investigation objectives.
Method
  1. Define investigation questions and scope from the existing site understanding.
  2. Select locations, depths, sample media and analytical parameters.
  3. Coordinate specialist sampling and laboratory analysis undertaken by providers.
  4. Check result completeness and interpret the need for further investigation.
Delivery model Partner/subcontractor coordinated by KFB Enviro

What you receive

You receive the investigation programme, collected results and an interpretation linked to the agreed objective. The material connects findings to sampling locations, explains investigation limits and identifies any need to extend the work. Specialist activities and laboratory analysis may be subcontracted; the documentation provided reflects the agreed programme and the activities actually completed.

Scope and limitations

Specialist work and laboratory analysis may be subcontracted

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Remediation strategy or plan

Translate investigation findings into a justified remediation approach

We examine contaminant types and distribution, ground and groundwater conditions, and current and intended land uses. The review considers whether the investigation supports definition of remediation objectives or needs extending. Concentrations matter alongside the extent of the problem, potential migration pathways and constraints imposed by ongoing operations or the development programme.

Suitable approaches are compared in terms of their technical, organisational and environmental implications. We identify assumptions requiring confirmation before selection and explain how outcomes could be evaluated. The strategy connects remedial activities, verification and future site use rather than reducing the decision to the choice of a technology without its wider site context.

Within the agreed scope, we prepare a strategy or draft remediation plan to support further consultations and implementation planning. Remediation works remain outside the core consulting scope. We do not predetermine an option's effectiveness without adequate investigation or the outcome of an administrative process; we identify conditions relevant to implementation and verification of the intended results.

Technical data

Subject Remediation objectives and options for contaminated land.
Service type Remediation strategy development or preparation of a draft remediation plan.
Assessment basis and requirements Investigation findings, intended land use, site conditions and requirements relevant to the agreed procedural route.
Method
  1. Assess investigation completeness and define the objectives of remedial action.
  2. Compare options against ground, groundwater and practical operating conditions.
  3. Identify implementation assumptions, verification needs and further consultation points.
  4. Prepare a strategy or draft plan for the selected direction.
Delivery model KFB Enviro with a partner/subcontractor

What you receive

You receive a remediation strategy or draft plan explaining the objectives, options and proposed approach. It records assumptions, constraints and the agreed method for evaluating outcomes. It identifies questions requiring further investigation or consultation and supports preparation of a specialist works commission; carrying out remediation works is not included in this consulting deliverable.

Scope and limitations

Remediation works are outside the core consulting scope

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Remediation supervision and monitoring

Track remediation progress through verifiable evidence

Before supervision starts, we define control points derived from the remediation plan, contractor documentation needs and information-sharing arrangements. We distinguish activities requiring observation from those assessable through records and test results. Attendance and frequency are selected for the agreed assignment rather than implying continuous site presence irrespective of the work being undertaken.

During implementation, documented activities are compared with the plan and deviations requiring explanation are identified. Monitoring results are considered alongside sampling locations, dates and conditions so dissimilar datasets are not treated as directly comparable. We highlight signals relevant to subsequent decisions, including a need for additional checks or reassessment of the planned approach.

Outcome assessment relies on the evidence collected and criteria relevant to the particular plan. A specialist contractor carries out the works; supervision does not replace that contractor's delivery responsibilities. Where evidence cannot substantiate a result, we identify what is missing rather than treating completion of works as proof that every remediation objective has been achieved across the site.

Technical data

Subject Remediation activities and monitoring evidence of their outcomes.
Service type Environmental supervision, monitoring and assessment of remediation results.
Assessment basis and requirements Agreed remediation plan, contractor records, control programme and relevant outcome assessment criteria.
Method
  1. Agree control points, records and responsibilities during implementation.
  2. Check activities against the plan and record identified deviations.
  3. Analyse monitoring results in light of how they were obtained.
  4. Assess evidenced outcomes and identify any further verification needed.
Delivery model KFB Enviro with a partner/subcontractor

What you receive

You receive supervision reports and an outcome assessment based on available records and monitoring results. The material describes observations, identified deviations and matters requiring action. It distinguishes demonstrated achievements from conclusions needing further confirmation, supporting decisions on additional works, supplementary investigation or documentation summarising implementation of the remediation plan.

Scope and limitations

Remediation works are carried out by a specialist contractor

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Water and wastewater monitoring and action plan

From a monitoring location to a decision on the result

We start with the monitoring purpose: process control, observation of facility impacts or implementation of documented conditions. The water and wastewater system, existing control points and available results are reviewed. Parameters and frequencies are proposed in relation to operating variability, stream characteristics and requirements confirmed for the specific facility, rather than a universal schedule.

The programme sets out arrangements for sampling, sharing results and evaluating findings. We identify operating information that should accompany each test so an unusual result can be investigated. The approach addresses comparison between monitoring rounds, missing data and signals requiring repeat checks, installation review or escalation to the person responsible for the next decision.

The action procedure helps prevent results being archived without interpretation. Responsibilities of the operator, coordinator and testing provider are distinguished, taking account of practical access to monitoring locations. Preparing a programme does not include completing an entire monitoring cycle; sampling and analysis require a separately agreed scope. Process changes may also require the programme to be revised.

Technical data

Subject Water and wastewater monitoring locations, parameters and responses to findings.
Service type Monitoring programme design and follow-up action procedure.
Assessment basis and requirements Facility arrangements, historical results and documented requirements confirmed for the relevant water uses.
Method
  1. Define monitoring objectives and review existing control arrangements.
  2. Select locations, parameters, frequency and supporting operating information.
  3. Describe result assessment and the response route for deviations.
  4. Allocate responsibilities and establish when the programme needs updating.
Delivery model KFB Enviro with a partner/subcontractor

What you receive

You receive a monitoring programme and a procedure connecting test results to follow-up actions. The documents specify control locations, parameters, proposed frequency, information flow and responsibilities. They support commissioning tests, comparing successive rounds and recording responses to identified problems, while distinguishing the agreed plan from field and laboratory activities required to implement it.

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Air emission source inventory and emissions balance

Turning facility data into a traceable emissions balance

We identify sources associated with production, fuel combustion and other activities within the agreed boundary. Installation documentation is combined with operating records, available measurement results and input from process owners. Actual operating parameters, design values and assumptions are kept distinct so that calculations do not inadvertently mix incompatible bases.

For each source, we establish the relevant pollutants, units and reporting period. Emission quantities are compiled so their origin can be traced and related to installation activity. Checks address missing streams, inconsistent operating hours and potential double counting. Where information is incomplete, we describe the gap and explain how it affects the resulting balance.

The assessment identifies the contribution of different sources and the information worth improving before modelling, documentation or reporting. It does not replace measurements where these are needed to determine emissions. When fuel, capacity or operating arrangements change, the structured inventory helps identify the records requiring revision without rebuilding the entire source catalogue.

Technical data

Subject Emission sources, fuels, materials and processes within the agreed facility boundary.
Service type Source inventory and quantitative air emissions balance.
Assessment basis and requirements Technical documentation, operating data, available measurements and calculation methods selected for the sources and intended use.
Method
  1. Define the inventory boundary and a common reference period.
  2. Link sources to processes, fuels and operating activity records.
  3. Calculate emissions with documented parameters, units and assumptions.
  4. Check the balance and identify information gaps and update needs.
Delivery model KFB Enviro with a partner/subcontractor

What you receive

You receive an emissions balance and source database containing the parameters used in the calculations. The package records data origins, assumptions and gaps affecting reliability. Its consistent structure supports transfer into modelling, environmental documentation or reporting and subsequent updates following installation changes, within the scope agreed for the assignment.

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Air pollutant dispersion modelling

Understand concentration patterns before selecting a design

We develop the model from source characteristics, emission quantities and the operating conditions of the facility. The study area, assessment points and environmental inputs are selected for the question being addressed. We check whether the available information represents the intended scenario and identify parameters requiring further evidence or a clearly stated assumption.

Calculations describe the spatial distribution of concentrations for the agreed pollutants and scenarios. Alternatives involving operating arrangements, source locations or emission parameters can be compared on a consistent basis. Results are interpreted against criteria relevant to the assessment purpose, highlighting sensitive locations, influential sources and the significance of input data for the conclusions.

A model is a forecasting tool, not a measurement of actual air quality at every location and moment. We explain scenario limitations and circumstances requiring additional evidence. This enables the designer or operator to decide whether to adjust the technical solution, investigate another alternative or incorporate the findings into broader environmental documentation.

Technical data

Subject Dispersion of agreed pollutants around identified emission sources.
Service type Computational modelling and comparison of emission scenarios.
Assessment basis and requirements Emission, source and environmental data; methods and assessment criteria selected for the location and documentation purpose.
Method
  1. Check the source inventory and representativeness of emission inputs.
  2. Prepare the model, assessment locations and agreed operating scenarios.
  3. Calculate concentration patterns and compare alternatives on a common basis.
  4. Interpret results, model limitations and requirements for further assessment.
Delivery model KFB Enviro

What you receive

You receive the model in an agreed form, results maps and an assessment report. The report explains inputs, scenarios, interpretation criteria and calculation limitations. Conclusions highlight differences between alternatives and issues requiring attention from the designer or operator, so the output supports a practical decision rather than simply presenting a collection of maps.

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Surface water monitoring

Monitor surface water with the sampling context in view

We establish what the monitoring needs to address: conditions before works begin, potential effects of an activity or changes observed during operation. Locations and parameters are chosen in relation to the development, the water body and available information on other influences. We check that repeat investigations and documentation of relevant conditions are practicable at the selected locations.

The agreed schedule is coordinated with fieldwork providers and the laboratory. Results are considered alongside information on construction or facility operation and conditions recorded during sampling. Differences between locations and successive rounds are reviewed, paying attention to method consistency and completeness of records. Unusual results are interpreted within the wider evidence rather than in isolation.

A change in one parameter does not by itself establish its cause or describe the entire watercourse. We identify when repeat testing or wider observation would be useful. Measurements are delivered by the appropriate partner and laboratory analyses by a suitable laboratory. KFB Enviro provides the agreed coordination and interpretation in relation to programme objectives.

Technical data

Subject Surface water quality at selected locations around a development or facility.
Service type Environmental monitoring programme design, coordination and interpretation.
Assessment basis and requirements Monitoring objectives, water body and site characteristics, documented facility conditions and methods suited to the selected parameters and sampling arrangements.
Method
  1. Define locations, parameters and the purpose of comparing results.
  2. Coordinate sampling and analysis with suitable specialist providers.
  3. Relate findings to field conditions and site activities.
  4. Interpret changes and prepare a report with follow-up recommendations.
Delivery model Partner/subcontractor coordinated by KFB Enviro

What you receive

You receive a monitoring report identifying locations, results and interpretation within the agreed context. It explains investigation conditions, differences between rounds and limitations of comparison. The material helps identify the need for further observation or investigation and provides the project team or operator with an organised record of conditions at the sampled locations.

Scope and limitations

Laboratory testing is performed by an appropriate laboratory or partner

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Soil and ground monitoring

Connect laboratory results with the locations they actually represent

We establish the investigation objective, history of the area and processes that may have affected its condition. Previous investigations and proposed land-use changes are reviewed. Sampling points, depths and analytical parameters are then defined for the agreed task, with a clear explanation of which questions the proposed sampling arrangement can address and which remain outside its coverage.

We coordinate the field partner's work and transfer of samples to an appropriate laboratory. Results are linked to sample locations and descriptions, then interpreted against the identified conditions and criteria selected for the site. Where historical results are available, we assess whether comparisons are meaningful given differences in depth, methods and sampling point selection.

Interpretation distinguishes an analytical result from a conclusion about the wider area. Findings at one point are not extended across a property without justification. Laboratory analyses are provided by the appropriate partner, while KFB Enviro coordinates the scope and interpretation. Further investigations, remediation planning or physical works require a separate scope informed by the evidence obtained.

Technical data

Subject Soil and ground conditions at defined site locations and sampling depths.
Service type Investigation planning and coordination with environmental interpretation.
Assessment basis and requirements Investigation purpose and boundaries, site history, sample characteristics and criteria and methods appropriate to the assessed area.
Method
  1. Review site history and the existing investigation record.
  2. Define sampling points, depths and laboratory analytical scope.
  3. Coordinate sampling and connect results with sample documentation.
  4. Interpret site conditions and identify the need for further investigation.
Delivery model Partner/subcontractor coordinated by KFB Enviro

What you receive

You receive an investigation report and interpretation identifying sampling points, depths and analytical scope. It explains how the results address the investigation purpose and where coverage remains limited. The material supports planning of subsequent site activities, including additional investigations where needed, without treating unsampled areas as if their condition had been established.

Scope and limitations

Laboratory testing is performed by an appropriate laboratory or partner

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