Use this form to record the results of drinking water quality testing and to compare those results with the quality limits, guideline values or benchmarks that apply in your own jurisdiction, operating context or internal specification. The form is generic and does not reference any single country's legal framework; the person completing it is responsible for identifying which limits apply and for interpreting the results appropriately.
Please complete every applicable field, enter values in the units stated, and attach laboratory reports where available. Fields marked as required must be completed before submission. Where a value is estimated, flagged as estimated or reported as not detected, note this in the remarks so that reviewers can interpret the record correctly.
I understand that this form is a record-keeping and analysis tool only and does not by itself constitute a regulatory determination, legal certification or medical opinion.
I confirm that the data entered reflects the sampling and analytical information available to me and that any estimated or derived values are clearly identified.
Report or record reference number
Date this record was prepared
Name of person completing this form
Role or job title of person completing this form
Organisation, utility or facility name
Contact email address
Contact telephone number
Was this testing requested or reviewed by an external party such as a consultant, auditor, client or authority?
What type of water source or system was sampled?
Protected groundwater bore or well
Unprotected well or spring
Surface water intake such as a river, stream or lake
Rainwater harvesting system
Treated water from a municipal or community supply
Water from a storage tank, cistern or reservoir
Water from a private or institutional distribution network
Desalinated or reconditioned water
Packaged or bottled water source
Other:
Source or supply name/identifier
Sampling point description and location
Approximate number of people served by this supply
What is the primary use of the water sampled?
Drinking and cooking
General domestic use
Institutional use such as a school, clinic or workplace
Food or beverage preparation
Process or industrial use with human contact
Irrigation of food crops
Recreational or aesthetic use
Mixed or other use
Is the water treated before the point of sampling?
Has this source been tested before?
Date and time of sampling
Name of sampler
Sampling category
Routine scheduled monitoring
Follow-up or resampling after an earlier result
Incident or complaint investigation
Commissioning of a new source or treatment step
Post-maintenance or post-repair verification
Baseline or exploratory survey
Verification after a treatment change
Other sampling category
Other:
Which sampling method was used to collect the sample?
Grab sample from a running tap after flushing
Grab sample without flushing
Composite sample collected over time
Sterile bottle collection for microbiological testing
Sample drawn from a treatment process stream
Sample drawn from a storage vessel
Other:
Flushing time before collection, in minutes
Water temperature at time of sampling, in degrees Celsius
Weather and environmental conditions at the time of sampling
Clear and dry
Overcast and dry
Light rain
Heavy rain or recent storm event
Flooding or high water levels observed
Drought or unusually low water levels
Conditions not observed or not recorded
Were any unusual conditions observed at the sampling point, such as discoloration, odour, sediment, pressure loss or visible damage?
Was a field blank, duplicate sample or equipment blank collected alongside this sample?
Sample identification code(s)
Number of containers submitted
Which preservation or holding measures were applied during transport?
Cooling to approximately 4 degrees Celsius
Chemical preservative added such as acid or base
Protected from light
Kept at ambient temperature
Sterile containers used and left unopened
No special preservation applied
Other:
Time elapsed between collection and delivery to the laboratory, in hours
Was the sample delivered within the holding time expected for the requested analyses?
Laboratory name and location
Does the laboratory hold a current accreditation, recognition or documented quality system for the analyses requested?
Please upload the signed chain of custody record or equivalent sample transfer documentation.
Please upload the laboratory report or certificate of analysis, if available.
Enter field readings as measured. Where a parameter was not measured in the field, leave the value blank and note this in the remarks at the end of the section. Instrument model and calibration details help reviewers judge the reliability of the readings.
Instrument(s) used for field measurements and identification number
Were the field instruments calibrated on the day of sampling or according to their documented schedule?
pH value
Turbidity value
Unit used for the turbidity reading
Nephelometric turbidity units (NTU)
Formazin turbidity units (FTU)
Formazin nephelometric units (FNU)
Other turbidity unit
Other:
Electrical conductivity value
Unit used for the conductivity reading
Microsiemens per centimetre (uS/cm)
Millisiemens per centimetre (mS/cm)
Other:
Was the conductivity reading temperature compensated?
Total dissolved solids (TDS) value
How was the total dissolved solids value obtained?
Measured directly with a dedicated TDS meter
Calculated from conductivity using a conversion factor
Gravimetric laboratory determination
Estimated from another measurement
Method not recorded
Free or residual disinfectant concentration, if applicable
Unit used for the residual disinfectant reading
Milligrams per litre (mg/L)
Parts per million (ppm)
Not applicable, no disinfectant used
Other unit
Dissolved oxygen, if measured
Oxidation-reduction potential, if measured, in millivolts
Apparent colour, if measured, in colour units
Odour description as observed in the field
Remarks on field measurements, instrument performance or unusual readings:
Record the analytical result for each parameter requested. Use the units shown in the laboratory report. If a parameter was not analysed, leave the result blank and note the reason in the remarks at the end of this section. Where a result is reported as below a detection limit, enter the detection limit value and select the corresponding qualifier.
Physical and chemical analytical results
Example values, if shown, are illustrative only and must not be treated as applicable limits without verification.
Analysed? | Parameter | Reported Result | Unit | Result Qualifier | Reporting or Detection Limit | |
|---|---|---|---|---|---|---|
Total hardness as calcium carbonate | 186.000 | mg/L | Detected | 5.000 | ||
Total alkalinity as calcium carbonate | 142.000 | mg/L | Detected | 5.000 | ||
Calcium | 58.000 | mg/L | Detected | 0.500 | ||
Magnesium | 12.400 | mg/L | Detected | 0.200 | ||
Chloride | 41.000 | mg/L | Detected | 1.000 | ||
Nitrate as nitrogen | 8.600 | mg/L | Detected | 0.500 | ||
Nitrite as nitrogen | 0.020 | mg/L | Detected | 0.010 | ||
Fluoride | 0.710 | mg/L | Detected | 0.050 | ||
Sulphate | 34.000 | mg/L | Detected | 1.000 | ||
Iron | 0.120 | mg/L | Detected | 0.020 | ||
Manganese | 0.015 | mg/L | Detected | 0.005 | ||
Arsenic | mg/L | Not analysed | 0.001 |
Which qualifier applies to results reported at or below a detection limit?
Results reported as not detected with the detection limit shown
Results reported as less than the detection limit
Results reported as estimated values below the quantitation limit
No detection-limit reporting convention applied
Other convention
Were any additional chemical parameters analysed beyond those listed above?
Was any parameter re-analysed or confirmed by a second technique?
Remarks on laboratory chemical analysis, sample condition on receipt or deviations from standard methods:
Microbial indicators are commonly used to assess the potential presence of faecal contamination and the effectiveness of hygiene barriers. Record the indicator organism, the method used and the result in the unit reported by the laboratory. Interpretation should always consider the sampling conditions and the intended use of the water.
Was microbiological testing performed on this sample?
Microbial indicator results
Example values, if shown, are illustrative only and must not be treated as applicable limits without verification.
Indicator Organism or Test | Result Value | Unit | Method Used | Incubation Time (hours) | Detected? | |
|---|---|---|---|---|---|---|
Total coliforms | 0.00 | CFU/100 mL | Membrane filtration | 24.0 | ||
E. coli | 0.00 | CFU/100 mL | Membrane filtration | 24.0 | ||
Enterococci | 0.00 | CFU/100 mL | Membrane filtration | 48.0 | ||
Heterotrophic plate count | 12.00 | CFU/mL | Pour plate | 48.0 | ||
How were microbial results expressed in the laboratory report?
Colony forming units per 100 mL
Colony forming units per mL
Most probable number per 100 mL
Presence or absence in a stated volume
Other expression
Was the sample dechlorinated or neutralised before microbiological testing?
Was any presumptive positive result confirmed by further testing?
Remarks on microbial testing, sample handling or interpretation:
Quality control information helps reviewers judge how much confidence can be placed in the reported results. Record the control measures that were applied and any performance issues identified during analysis.
Which quality control measures were applied during analysis?
Method blanks
Laboratory control samples or spikes
Matrix spikes or matrix spike duplicates
Duplicate analyses
Certified reference materials or control standards
Internal calibration verification standards
Control charts or proficiency testing results
Second analyst review or independent verification
No documented quality control measures applied
Other quality control measure
Did all quality control results fall within the laboratory's acceptance criteria?
Analytical methods or method references used
Were any results qualified, estimated or flagged by the laboratory?
Estimated overall measurement uncertainty, if reported, in percent
Please upload any quality control summary, control chart or proficiency testing record referenced above.
Identify the source of the quality limits used for comparison. Limits may come from national or local requirements, a supply contract, a recognised international guideline, an internal operating target or a customer specification. Record the reference clearly so that the basis of comparison is transparent.
What is the primary basis for the drinking water quality limits used in this analysis?
National or federal drinking water requirements
Regional, provincial or local authority requirements
Recognised international guideline values
Supply contract or customer specification
Internal operating targets or action levels
Industry or sector guidance
Limits agreed with a laboratory or consultant
No formal limits identified; comparison is indicative only
Reference document, standard or guideline title and version used
Date of the reference document or its last revision
Jurisdiction / country / region
Issuing authority or organisation
How are the limit values classified in the reference used?
Legally binding maximum values
Guideline values intended as health-based targets
Aesthetic or acceptability values such as taste, odour or appearance
Operational or process targets
Alert or action levels below a maximum value
Mixture of binding values and non-binding guidance
Classification not stated in the reference
Are there any additional internal targets that are stricter than the external limits?
Do any parameters in this analysis have limits that vary by season, temperature, exposure duration or population group?
Are any parameters covered by a temporary or provisional limit, waiver, exemption or alternative arrangement?
Please upload the reference document, extract or table of limits used for this comparison, if available.
Enter each measured value alongside the applicable limit identified in the previous section. The final column calculates the difference between the limit and the measured value so that reviewers can see how close a result is to its limit. A positive difference generally indicates the result is below the limit; a negative difference indicates the result is above the limit. Always confirm the direction of the comparison for parameters where a lower value is the target rather than an upper bound.
Parameter-by-parameter comparison with applicable limits
Example results and limit values shown in this table are illustrative only. Replace them with actual laboratory results and the applicable parameter-specific limits or ranges from the reference identified in Section 10. Verify the units, criteria and comparison direction before interpreting the results.
Parameter | Measured Value | Unit | Applicable Limit Value | Limit Type | Margin (Limit minus Result) | Result Above Limit? | |
|---|---|---|---|---|---|---|---|
pH | 7.420 | pH units | 8.500 | Acceptability range upper bound | 1.080 | ||
Turbidity | 0.680 | NTU | 1.000 | Operational target | 0.320 | ||
Conductivity | 412.000 | uS/cm | 1000.000 | Acceptability value | 588.000 | ||
Total dissolved solids | 264.000 | mg/L | 600.000 | Acceptability value | 336.000 | ||
Total hardness | 186.000 | mg/L | 300.000 | Acceptability value | 114.000 | ||
Total alkalinity | 142.000 | mg/L | 200.000 | Operational guidance | 58.000 | ||
Chloride | 41.000 | mg/L | 250.000 | Acceptability value | 209.000 | ||
Nitrate as nitrogen | 8.600 | mg/L | 11.300 | Health-based value | 2.700 | ||
Fluoride | 0.710 | mg/L | 1.500 | Health-based value | 0.790 | ||
E. coli | 0.000 | CFU/100 mL | 0.000 | Microbial indicator target | 0.000 |
Does any measured result exceed its applicable limit?
Overall outcome of the comparison for this sampling event
All parameters within the applicable limits
One or more parameters above an acceptability or aesthetic value only
One or more parameters above an operational target or action level
One or more parameters above a health-based or binding value
Comparison incomplete because limits or results are missing
Outcome not yet determined pending further review
Were any parameters excluded from the comparison because no applicable limit could be identified?
Is a combined or aggregate assessment needed, for example where several related parameters are each close to their individual values?
Comparing current results with earlier data helps identify gradual changes that a single sampling event may not reveal. Enter the previous values where records are available and note any clear direction of change.
Comparison with previous sampling results
Parameter | Previous Sampling Date | Previous Result | Current Result | Change (Current minus Previous) | Direction of Change | |
|---|---|---|---|---|---|---|
pH | 7.380 | 7.420 | 0.040 | Stable | ||
Turbidity | 0.410 | 0.680 | 0.270 | Increasing | ||
Nitrate as nitrogen | 7.200 | 8.600 | 1.400 | Increasing | ||
Fluoride | 0.690 | 0.710 | 0.020 | Stable | ||
Do any parameters show a consistent upward or downward trend across several sampling events?
Have any process, source or operational changes occurred since the previous sampling that could explain differences in the results?
Number of sampling events in the current monitoring period
Additional comments on trends, variability or seasonal patterns:
This section records the reviewer's interpretation of the results. Keep statements factual and measured. Avoid drawing medical, legal or scientific conclusions that are not supported by the data or by a qualified professional. Where uncertainty exists, state it plainly.
Which aspects of the results may be significant for the intended use of the water?
Microbial indicators suggesting a possible hygiene barrier weakness
Nutrient-related parameters such as nitrate or nitrite
Mineral content affecting taste, appearance or scaling tendency
Parameters affecting corrosion or pipe material compatibility
Parameters relevant to sensitive groups such as infants or people with specific health conditions
Parameters affecting treatment process performance
Parameters affecting food or beverage preparation quality
No particular significance identified at this stage
Other aspect considered significant
How would you describe the overall reliability of this dataset for decision making?
High, complete data with documented quality control
Moderate, generally complete with minor gaps
Limited, notable gaps or qualified results
Low, substantial gaps or handling concerns
Not yet assessed
Is any result considered an outlier or inconsistent with the rest of the dataset?
Are any limitations or uncertainties likely to affect how these results should be read?
Summary interpretation of the results in plain language:
This interpretation has been reviewed by a person with appropriate technical responsibility for the sampling programme.
Do any results require notification to a person or organisation outside the immediate team?
Date on which notification was issued or is planned
Summary of what was communicated, to whom and by what means:
Was any interim advice given to users of the supply while the results were reviewed?
Is follow-up communication planned once further analysis or resampling is complete?
Record any action arising from this testing. Actions may include resampling, process adjustment, maintenance, source protection measures, further investigation or changes to the monitoring schedule. Assign responsibility and target dates so that progress can be tracked.
Which actions are proposed or already underway?
Confirmatory or resampling at the same point
Sampling at additional points to locate a source of concern
Review or adjustment of treatment process settings
Cleaning, repair or replacement of equipment or storage
Review of source protection measures
Increased monitoring frequency for selected parameters
Further specialised analysis such as trace metals or organic compounds
Review of sampling and handling procedures
User awareness or hygiene measures
No action required at this stage
Other action
Action tracking register
Action Description | Responsible Person | Target Completion Date | Priority | Completed? | Notes or Evidence of Completion | |
|---|---|---|---|---|---|---|
Repeat nitrate analysis on a fresh sample | High | Sample bottles prepared and courier booked | ||||
Inspect and clean raw water storage tank | Medium | Work order raised, awaiting access window | ||||
Review turbidity control on the filtration unit | Medium | Performance data being compiled | ||||
Planned date for the next sampling event
Should the monitoring schedule be revised as a result of these findings?
Is any additional specialist input needed to interpret these results or plan the response?
Please upload photographs of the sampling point, equipment or any visible observations, if available.
Please upload instrument calibration certificates or calibration logs referenced in this form.
Please upload previous monitoring results used for trend comparison.
Please upload any other supporting record, correspondence or technical note.
List of attachments included with this record:
By signing below, the reviewer confirms that the information recorded in this form reflects the data available at the time of review. Signing does not represent a regulatory approval, a legal certification or a guarantee of fitness for any particular purpose.
Name of reviewer
Role or position of reviewer
Review outcome
Accepted as recorded
Accepted with comments or qualifications
Returned for correction or clarification
Held pending further results or resampling
Escalated for specialist review
Reviewer comments, conditions or qualifications:
Date of review
Reviewer signature
Has this record been approved for distribution to the recipients identified earlier in this form?
Retention location or records system reference for this completed form
Analysis for Drinking Water Quality Testing & Compliance Analysis Form
Important Note:
This analysis provides strategic insights to help you get the most from your form's submission data for powerful follow-up actions and better outcomes.
AI-Generated Content: This template and its accompanying guidance are AI-generated to provide a practical starting point for your form-building needs. Please review and customise the content to ensure it is accurate, appropriate and suitable for your intended use.
This guide is provided for general informational and planning purposes only. It does not constitute professional, legal, financial, medical, employment, privacy, regulatory, or advice of any other kind, nor does it certify that this template is suitable or compliant for any particular jurisdiction or purpose.
Laws, regulations, industry practices and business requirements vary. You are responsible for reviewing and customising the template to suit your intended use and obtaining advice from appropriately qualified professionals where necessary.
Please delete this section before publishing your form. See our Terms of Service for further information.
This comprehensive Drinking Water Quality Testing & Compliance Analysis Form is a well-structured record-keeping and analytical comparison tool designed to capture field measurements, laboratory results, microbial indicator data, quality control information, and compliance comparisons against user-identified drinking water quality limits. The form spans approximately 17 major sections and covers the full lifecycle of a water quality testing event — from source description and sampling logistics through analytical results, trend review, interpretation, notification, corrective actions, and final sign-off. Its generic framing is a notable strength: the introductory paragraphs clearly state that the form does not reference any single jurisdiction's legal framework and that the user is responsible for identifying applicable limits and interpreting results appropriately. This approach makes the form adaptable across different operating contexts while avoiding unsupported regulatory claims.
The opening section sets clear expectations for the respondent. The two acknowledgement checkboxes — one confirming the form is a record-keeping tool only, and one confirming data accuracy with estimated values clearly identified — establish a useful accountability baseline before any data is entered. This design choice helps reduce misinterpretation of the form's role and encourages transparent data entry practices.
Report or record reference number provides a unique identifier that enables efficient filing, retrieval, and cross-referencing with laboratory reports and other records. Date this record was prepared establishes a clear timeline anchor for the documentation. Name of person completing this form ensures accountability and a point of contact for follow-up queries. Role or job title of person completing this form adds useful context about the respondent's position and likely familiarity with the subject matter. Organisation, utility or facility name identifies the operating entity, which is important for multi-site or multi-organisation contexts. Contact email address provides a primary digital communication channel. Contact telephone number offers an alternative contact route. The question Was this testing requested or reviewed by an external party such as a consultant, auditor, client or authority? uses conditional follow-up logic effectively — capturing either the external party's details or the internal initiator depending on the response — which helps trace the origin and purpose of the testing.
What type of water source or system was sampled? offers a broad set of source categories with an 'Other' option and descriptive follow-up, ensuring the form can accommodate diverse supply types. Source or supply name/identifier and Sampling point description and location together provide the spatial and logistical context needed to interpret results and plan follow-up sampling. Approximate number of people served by this supply adds population context that may be relevant for prioritising actions. What is the primary use of the water sampled? helps frame the significance of results in relation to intended use. The treatment-related questions — Is the water treated before the point of sampling? with its detailed multiple-choice follow-up covering a wide range of treatment steps — are particularly effective, as they capture the process context that directly influences water quality outcomes. Has this source been tested before? with its follow-up on previous results supports continuity of monitoring records.
Date and time of sampling and Name of sampler are essential for traceability. Sampling category distinguishes routine monitoring from incident response or commissioning, which affects how results should be interpreted. Which sampling method was used to collect the sample? captures collection technique details that can influence representativeness. Fields for Flushing time before collection, Water temperature, and Weather and environmental conditions provide useful contextual metadata. The question about unusual conditions observed at the sampling point with its follow-up on immediate actions taken is a practical addition. The quality control question about field blanks, duplicate samples or equipment blanks demonstrates attention to analytical reliability.
Sample identification code(s) links the physical sample to this record. The preservation and holding time questions — including Time elapsed between collection and delivery and Was the sample delivered within the holding time expected? — address factors that can significantly affect result reliability. Laboratory name and location and the accreditation question provide transparency about analytical capability. The file upload fields for chain of custody records and laboratory reports support comprehensive documentation.
The field measurement section is well-organised, with clear instructions to enter values as measured and leave blanks where not measured. Instrument(s) used for field measurements and identification number and the calibration question support data quality assessment. The core parameters — pH value, Turbidity value, Electrical conductivity value, and Total dissolved solids (TDS) value — are each paired with unit selection fields, which is an excellent design choice that prevents ambiguity in reported values. The temperature compensation question for conductivity and the TDS derivation method question further enhance interpretability. Optional fields for residual disinfectant, dissolved oxygen, oxidation-reduction potential, colour, and odour round out the field observations.
The physical and chemical analytical results table is pre-populated with common parameters including hardness, alkalinity, calcium, magnesium, chloride, nitrate, nitrite, fluoride, sulphate, iron, manganese, and arsenic. Each row includes an 'Analysed?' checkbox, result value, unit, qualifier, and detection limit — a structured approach that supports consistent data entry. The detection-limit reporting convention question and the follow-ups for additional parameters and confirmatory analyses add depth to the analytical record.
The microbial section begins with a clear question about whether microbiological testing was performed, with appropriate follow-up in both cases. The indicator selection covers a comprehensive range from total coliforms to Legionella and Pseudomonas. The results table captures organism, value, unit, method, incubation time, and detection status. Questions about result expression, dechlorination, and presumptive positive confirmation demonstrate attention to methodological detail that affects interpretation.
The QA/QC section captures control measures, acceptance criteria, analytical methods, and flagged results. The question about Estimated overall measurement uncertainty is a sophisticated addition that supports confidence assessment. File upload for QC summaries further strengthens the record.
This section is thoughtfully designed to make the basis of comparison transparent. What is the primary basis for the drinking water quality limits used in this analysis? and Reference document, standard or guideline title and version used together establish the reference framework. The classification question (binding values vs. guideline values vs. aesthetic values) and the questions about internal targets, variable limits, and provisional arrangements add nuance that supports accurate interpretation.
The comparison table with its calculated margin column (limit minus result) is a practical analytical tool. The formula-driven margin calculation and the 'Result Above Limit?' checkbox enable quick identification of exceedances. The follow-up questions about exceedances, results close to limits, overall outcome, excluded parameters, and combined assessments provide a structured approach to compliance analysis.
The trend comparison table with its calculated change column and direction-of-change field supports longitudinal analysis. Questions about consistent trends, operational changes, and seasonal patterns encourage thoughtful interpretation of temporal data.
This section encourages measured, factual interpretation. The significance checklist, reliability assessment, outlier identification, and limitations questions promote balanced analysis. The plain-language summary field and the technical review checkbox add appropriate accountability.
The notification section with its conditional logic captures who needs to be informed, when, and how. The interim advice and follow-up communication questions ensure that stakeholder communication is tracked.
The action selection checklist and the action tracking register with responsible persons, target dates, and completion status provide a practical follow-up mechanism. The monitoring schedule revision and specialist input questions ensure that the response to findings is proportionate and well-planned.
The attachment upload fields and the structured review and sign-off section — including reviewer name, role, outcome, comments, date, and signature — provide a clear closure mechanism. The distribution approval question and retention location field complete the documentation lifecycle.
Strengths: The form demonstrates exceptional breadth and logical organisation, moving from identification through data collection to analysis and action. Its generic framing avoids jurisdiction-specific claims. Conditional logic is used effectively throughout to reduce unnecessary fields. Calculated columns in comparison and trend tables add analytical value. Pre-populated parameter rows provide helpful structure. The inclusion of quality control, chain of custody, and instrument calibration information supports data reliability assessment. File upload fields enable comprehensive documentation. Areas for consideration: The form's considerable length and detail may require significant time to complete, which could affect completion rates for routine monitoring. Consider whether a condensed version might be appropriate for simple routine checks, with the full form reserved for comprehensive assessments. Some sections (e.g., trend review, notification, corrective actions) may not be applicable to every sampling event; the form could benefit from clearer guidance on when sections can be skipped. The pre-populated example values in tables are helpful as guidance but should be clearly labelled as illustrative to avoid confusion during actual data entry.
Mandatory Question Analysis for Drinking Water Quality Testing & Compliance Analysis Form
Important Note:
This section explains why certain fields in this form are marked as required and provides general guidance on how these requirements may support the collection of complete, accurate and relevant information.
Required fields and information-collection obligations may vary depending on your industry, jurisdiction, business operations and intended use of the form. A field marked as required in this template does not necessarily mean that collecting the information is legally mandatory.
Please review each required field to determine whether it is necessary, appropriate and lawful for your particular purpose. Consider applicable privacy, data protection, consent and industry-specific requirements, and consult an appropriately qualified legal, privacy or compliance professional where necessary.
Please delete this section before publishing your form. See our Terms of Service for further information.
The following fields are currently set as mandatory (required) in the form. Each is analysed below in terms of how requiring it may support data completeness, operational processing, and record-keeping within the form's stated purpose.
Report or record reference number
Recommendation: Requiring a unique reference number supports efficient filing, retrieval, and cross-referencing with laboratory reports and other documentation. Without a stable identifier, completed records may be difficult to locate or associate with specific sampling events, particularly in organisations managing multiple water sources or monitoring programmes. This requirement is proportionate to the form's record-keeping purpose.
Date this record was prepared
Recommendation: Recording the preparation date establishes a clear timeline anchor for the documentation. This supports chronological filing and helps reviewers understand when the analysis was compiled relative to sampling and laboratory delivery dates. Requiring this field is consistent with standard record-keeping practice.
Name of person completing this form
Recommendation: Identifying the person who compiled the record ensures accountability and provides a point of contact for clarification queries. This is a basic and proportionate requirement for any structured data collection form where follow-up communication may be needed.
Contact email address
Recommendation: Requiring an email address provides a primary digital communication channel for follow-up questions, confirmation of receipt, or requests for additional information. Whether this field should remain mandatory may depend on the form creator's communication practices; some contexts may rely on telephone or in-person contact instead.
What type of water source or system was sampled?
Recommendation: Identifying the source type is fundamental to interpreting water quality results, as different source types (groundwater, surface water, treated supply, etc.) have different expected quality profiles and risk considerations. Requiring this field ensures that every record has the basic context needed for meaningful analysis.
Source or supply name/identifier
Recommendation: Naming the specific source or supply supports traceability and enables results to be associated with the correct physical location or system. This is particularly important where an organisation monitors multiple sources and needs to track results over time for each one.
Sampling point description and location
Recommendation: Recording where the sample was taken provides spatial context that affects result interpretation and enables consistent resampling at the same point. A clear sampling point description reduces ambiguity and supports reliable trend comparisons.
Date and time of sampling
Recommendation: The sampling date and time are essential for establishing the timeline of the testing event, assessing holding time compliance, and correlating results with environmental or operational conditions. Requiring this field supports basic data integrity for the record.
Name of sampler
Recommendation: Identifying who collected the sample supports accountability and provides a contact for questions about sampling conditions or technique. This is a proportionate requirement for traceability purposes.
Which sampling method was used to collect the sample?
Recommendation: The collection method can influence sample representativeness and result interpretation. Requiring this field ensures that reviewers have the methodological context needed to assess the data appropriately. The inclusion of an 'Other' option with a descriptive follow-up accommodates non-standard methods.
Sample identification code(s)
Recommendation: Sample codes link the physical sample containers to this record and to laboratory reports. Without these codes, it may be difficult to match results to the correct sampling event, particularly where multiple samples are submitted for different analyses. This requirement supports basic chain-of-custody documentation.
Laboratory name and location
Recommendation: Identifying the analysing laboratory supports traceability and enables reviewers to assess the analytical capability and any accreditation status. This information is important for evaluating result reliability and for any follow-up queries to the laboratory.
Instrument(s) used for field measurements and identification number
Recommendation: Recording field instrument details supports data quality assessment by enabling reviewers to verify calibration status and instrument performance. This requirement is proportionate to the form's emphasis on data reliability and quality assurance.
pH value
Recommendation: pH is one of the most fundamental water quality indicators, affecting treatment processes, distribution system conditions, and the behaviour of other chemical parameters. Requiring this field ensures that every record includes this core measurement, which is consistent with the form's stated purpose of capturing key water quality parameters.
Turbidity value
Recommendation: Turbidity is a key indicator of water clarity and can signal changes in source water quality, treatment performance, or distribution system integrity. Requiring this measurement supports the form's core analytical purpose and provides data that is commonly used in operational monitoring.
Electrical conductivity value
Recommendation: Conductivity provides a broad indicator of dissolved ion content and can signal changes in source water or treatment performance. Including it as a required field ensures that this widely used parameter is captured consistently across records.
Total dissolved solids (TDS) value
Recommendation: TDS is a commonly reported water quality parameter related to mineral content and taste acceptability. Requiring this field ensures it is captured alongside the other core physical and chemical measurements specified in the form's purpose.
Analytical methods or method references used
Recommendation: Recording the analytical methods supports result interpretation and enables reviewers to assess whether appropriate techniques were applied. This information is important for evaluating data quality and for any subsequent review or verification. Requiring this field is proportionate to the form's quality assurance focus.
What is the primary basis for the drinking water quality limits used in this analysis?
Recommendation: Identifying the source of the comparison limits is essential for transparency in the compliance analysis. Without knowing whether limits derive from national requirements, international guidelines, contractual specifications, or internal targets, reviewers cannot properly interpret the comparison results. This requirement directly supports the form's compliance analysis purpose.
Reference document, standard or guideline title and version used
Recommendation: Recording the specific reference document and version ensures that the basis of comparison is clearly documented and can be verified or updated in future analyses. This supports reproducibility and transparency in the compliance comparison.
Overall outcome of the comparison for this sampling event
Recommendation: Capturing the overall comparison outcome provides a concise summary that supports quick review and decision-making. This field synthesises the parameter-level comparisons into a single assessment, which is useful for reporting and for tracking compliance status over time.
Name of reviewer
Recommendation: Identifying the reviewer establishes accountability for the final assessment and provides a contact for questions about the review outcome. This is a standard and proportionate requirement for any reviewed record.
Role or position of reviewer
Recommendation: Recording the reviewer's role provides context about the level of technical responsibility and authority behind the review outcome. This supports appropriate interpretation of the sign-off and is consistent with good record-keeping practice.
Review outcome
Recommendation: Capturing the review outcome (accepted, returned for correction, held pending results, etc.) provides a clear decision record that supports workflow management and follow-up tracking. Requiring this field ensures that every completed record has a documented disposition.
Date of review
Recommendation: The review date establishes when the assessment was completed and supports chronological record-keeping. This is a basic and proportionate requirement for documenting the review process.
Reviewer signature
Recommendation: A reviewer signature provides a formal confirmation of the review and adds a layer of accountability to the record. The form appropriately notes that signing does not represent regulatory approval or legal certification, which sets clear expectations. Whether a digital or physical signature is appropriate may depend on the organisation's documentation practices.
The form contains approximately 26 mandatory fields distributed across identification, sampling, analytical, compliance, and review sections. This distribution is generally well-balanced, with mandatory fields concentrated at key points in the data lifecycle — identity and traceability at the beginning, core measurements in the middle, and review accountability at the end. The following observations and recommendations may be useful:
Overall, the mandatory field strategy is thoughtful and proportionate to the form's purpose. The required fields capture essential identification, measurement, and accountability information without imposing excessive burden on the respondent. The optional fields provide valuable additional context without creating barriers to submission.