Squash in the HMI library has 68 reported results for lead, cadmium, total arsenic, inorganic arsenic, dimethylarsinic acid, total mercury, nickel, chromium, aluminium, Co, Cu, Fe, Mn, Zn, V, Sr and Ti from 6 sources.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Heavy metals in vegetables and potential risk for human healthScientia Agricola 69(1):54-60Read source →3Cadmium and lead in vegetable and fruit produce selected from specific regional areas of the UKThe Science of the Total Environment 533, 520-527 (2015); accepted author manuscriptRead source →4Analytical Results for Arsenic, Lead, Cadmium, and Mercury in Food Intended for Babies and Young Children - TEP (FY2009-FY2024)FDA analytical results tableRead source →5Evaluation of Health Risks Associated with Potential Toxic Elements in Selected Vegetables Consumed in the Western Black Sea Region of TurkeyACS Omega 2025, 10, 8843-8858Read source →6Monitoring of toxic metals (cadmium, lead, arsenic and mercury) in vegetables of Sindh, PakistanKathmandu University Journal of Science, Engineering and Technology 6 (II): 60-65Read source →
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Metals measured:
Lead, cadmium, total arsenic, inorganic arsenic, dimethylarsinic acid and total mercury and others, in 68 results from 6 sources.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Heavy metals in vegetables and potential risk for human healthScientia Agricola 69(1):54-60Read source →3Cadmium and lead in vegetable and fruit produce selected from specific regional areas of the UKThe Science of the Total Environment 533, 520-527 (2015); accepted author manuscriptRead source →4Analytical Results for Arsenic, Lead, Cadmium, and Mercury in Food Intended for Babies and Young Children - TEP (FY2009-FY2024)FDA analytical results tableRead source →
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Main drivers:
Form, basis and where the squash was sampled; reporting limits decide how many results are non-detects.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Heavy metals in vegetables and potential risk for human healthScientia Agricola 69(1):54-60Read source →3Cadmium and lead in vegetable and fruit produce selected from specific regional areas of the UKThe Science of the Total Environment 533, 520-527 (2015); accepted author manuscriptRead source →4Analytical Results for Arsenic, Lead, Cadmium, and Mercury in Food Intended for Babies and Young Children - TEP (FY2009-FY2024)FDA analytical results tableRead source →
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Practical framing:
Ask for lot results with a quantification limit well below the limit that applies in the destination market.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Heavy metals in vegetables and potential risk for human healthScientia Agricola 69(1):54-60Read source →3Cadmium and lead in vegetable and fruit produce selected from specific regional areas of the UKThe Science of the Total Environment 533, 520-527 (2015); accepted author manuscriptRead source →4Analytical Results for Arsenic, Lead, Cadmium, and Mercury in Food Intended for Babies and Young Children - TEP (FY2009-FY2024)FDA analytical results tableRead source →
Squash overview
Squash in the HMI library has 68 reported results for lead, cadmium, total arsenic, inorganic arsenic, dimethylarsinic acid, total mercury, nickel, chromium, aluminium, Co, Cu, Fe, Mn, Zn, V, Sr and Ti from 6 sources.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Heavy metals in vegetables and potential risk for human healthScientia Agricola 69(1):54-60Read source →3Cadmium and lead in vegetable and fruit produce selected from specific regional areas of the UKThe Science of the Total Environment 533, 520-527 (2015); accepted author manuscriptRead source →4Analytical Results for Arsenic, Lead, Cadmium, and Mercury in Food Intended for Babies and Young Children - TEP (FY2009-FY2024)FDA analytical results tableRead source →5Evaluation of Health Risks Associated with Potential Toxic Elements in Selected Vegetables Consumed in the Western Black Sea Region of TurkeyACS Omega 2025, 10, 8843-8858Read source →6Monitoring of toxic metals (cadmium, lead, arsenic and mercury) in vegetables of Sindh, PakistanKathmandu University Journal of Science, Engineering and Technology 6 (II): 60-65Read source → WHO GEMS/Food submissions reported lead in squash, as sold from 214 results in 3 reporting regions, with a subgroup median of 3.13 µg/kg.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → For cadmium, GEMS/Food gave subgroup medians from 2 to 2 µg/kg from 98 results.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
Guerra et al. 2012 reported lead at 500 µg/kg (mean) in squash, as sold from CEAGESP wholesale market.2Heavy metals in vegetables and potential risk for human healthScientia Agricola 69(1):54-60Read source → Across 2 other studies of ordinary farms and markets, reported cadmium means and medians on an as-sold or fresh-weight basis ranged from 3.1 µg/kg (Norton et al. 2015) to 50 µg/kg (Guerra et al. 2012).2Heavy metals in vegetables and potential risk for human healthScientia Agricola 69(1):54-60Read source →3Cadmium and lead in vegetable and fruit produce selected from specific regional areas of the UKThe Science of the Total Environment 533, 520-527 (2015); accepted author manuscriptRead source →
For a buyer the practical points are the form bought, the basis a result is reported on, where the squash came from and the laboratory’s reporting limit. Testing finds contamination but does not remove it.
What counts as squash
This page covers squash in 2 forms kept separate in every comparison: squash, as sold (67 results) and squash, juice (1 result).1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Heavy metals in vegetables and potential risk for human healthScientia Agricola 69(1):54-60Read source →3Cadmium and lead in vegetable and fruit produce selected from specific regional areas of the UKThe Science of the Total Environment 533, 520-527 (2015); accepted author manuscriptRead source →4Analytical Results for Arsenic, Lead, Cadmium, and Mercury in Food Intended for Babies and Young Children - TEP (FY2009-FY2024)FDA analytical results tableRead source →5Evaluation of Health Risks Associated with Potential Toxic Elements in Selected Vegetables Consumed in the Western Black Sea Region of TurkeyACS Omega 2025, 10, 8843-8858Read source →6Monitoring of toxic metals (cadmium, lead, arsenic and mercury) in vegetables of Sindh, PakistanKathmandu University Journal of Science, Engineering and Technology 6 (II): 60-65Read source → Foods made from squash that have their own pages, such as butternut squash and winter squash, are covered there.
Results stay on the basis each source reports: as sold or fresh weight, dry weight, or unstated. Dry-weight, as-sold and unstated results are never pooled, and no moisture conversion is applied.
Heavy metal contamination profile of squash
The table holds every extracted squash result: one row for each statistic a source reports for a form, group and metal, 68 rows in all, grouped by metal and form; percentiles, ranges and maxima for the same samples as a mean or median are shown on that row.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Heavy metals in vegetables and potential risk for human healthScientia Agricola 69(1):54-60Read source →3Cadmium and lead in vegetable and fruit produce selected from specific regional areas of the UKThe Science of the Total Environment 533, 520-527 (2015); accepted author manuscriptRead source →4Analytical Results for Arsenic, Lead, Cadmium, and Mercury in Food Intended for Babies and Young Children - TEP (FY2009-FY2024)FDA analytical results tableRead source →5Evaluation of Health Risks Associated with Potential Toxic Elements in Selected Vegetables Consumed in the Western Black Sea Region of TurkeyACS Omega 2025, 10, 8843-8858Read source →6Monitoring of toxic metals (cadmium, lead, arsenic and mercury) in vegetables of Sindh, PakistanKathmandu University Journal of Science, Engineering and Technology 6 (II): 60-65Read source → Monitoring medians are HMI calculations from individual submissions; non-detects remain intervals between zero and the reporting limit and are never read as zero.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
12 rows can be rated against an HMI reference for the same form and basis, 0 rows have a direct same-study comparison, and the rest stay unrated with the reason recorded.
Comparison methods and scope
Each row is one statistic a source reports for one form of squash, group and metal; percentiles, ranges and maxima reported for the same samples as a mean or median are shown on that row. Different forms and preparation states are kept apart, and dry-weight results never share a reference with as-sold or fresh-weight results. Ratings place a result against an HMI reference built from monitoring results and ordinary-setting medians for the same form and basis. Same-study contrasts compare a contaminated or treated site with its control, targeted with random sampling, a prepared form with the unprocessed one, or one group of a study with the median of its other groups. Held rows failed a check against their own source and are shown but not compared.
First displayed analyte: Lead: 19 findings from 6 sources. Each row retains its statistic and measurement basis.
Filter findings
67 of 67 findings · 17 analytes
About this table
| Food form | Collection scope | Finding (µg/kg) | Comparison | Evidence |
|---|---|---|---|---|
18 findings · 6 studies | ||||
| Squash, as soldWHO GEMS/Food | EURO2000 | median. | ||
| Squash, as soldWHO GEMS/Food | PAHO2006–2010 | median. | ||
| Squash, as soldWHO GEMS/Food | PAHO2000–2005 | median. | ||
| Squash, as soldWHO GEMS/Food | PAHO2015–2017 | median. | ||
| Squash, as soldWHO GEMS/Food | PAHO2000–2017 | median. | ||
| Squash, as soldWHO GEMS/Food | PAHO2014–2016 | median. | ||
| Squash, as soldWHO GEMS/Food | WPRO2004 | median. | ||
| Squash, as soldGuerra et al. 2012 | CEAGESP wholesale market2009 | mean. | ||
| Squash, as soldGuerra et al. 2012 | CEAGESP wholesale market2009 | mean. | ||
| Squash, as soldNorton et al. 2015 | SW Britain (Devon and Cornwall) basket surveyCollection date unreported | median. | ||
| Squash, as soldNorton et al. 2015 | SW Britain (Devon and Cornwall) basket surveyCollection date unreported | mean. | ||
| Squash, as soldNorton et al. 2015 | SW Britain (Devon and Cornwall) basket surveyCollection date unreported | min. | ||
| Squash, as soldNorton et al. 2015 | SW Britain (Devon and Cornwall) basket surveyCollection date unreported | max. | ||
| Squash, as soldU.S. Food and Drug Administration 2024 | Vegetables, FY20182009–2024 | sample value. | ||
| Squash, as soldU.S. Food and Drug Administration 2024 | Vegetables, FY20192009–2024 | sample value. | ||
| Squash, as soldU.S. Food and Drug Administration 2024 | Vegetables, FY20192009–2024 | not detected. | ||
| Squash, as soldAltıkulaç et al. 2025 | Group II2021–2022Dry weight | mean. | ||
| Squash, as soldAbbas et al. 2010 | cucurbit vegetables2007–2008Basis not stated | mean. | ||
1 finding · 1 study | ||||
| Squash, juiceWHO GEMS/Food | SEARO2013 | median. | ||
13 findings · 6 studies · 1 spread figure folded in | ||||
| Squash, as soldWHO GEMS/Food | EURO2000 | median. | ||
| Squash, as soldWHO GEMS/Food | PAHO2003–2010 | median. | ||
| Squash, as soldWHO GEMS/Food | PAHO2003–2017 | median. | ||
| Squash, as soldGuerra et al. 2012 | CEAGESP wholesale market2009 | mean. | ||
| Squash, as soldGuerra et al. 2012 | CEAGESP wholesale market2009 | mean. | ||
| Squash, as soldNorton et al. 2015 | SW Britain (Devon and Cornwall) basket surveyCollection date unreported | median. | ||
| Squash, as soldNorton et al. 2015 | SW Britain (Devon and Cornwall) basket surveyCollection date unreported | mean.Same samples: 5.5 µg/kg (maximum) | ||
| Squash, as soldNorton et al. 2015 | SW Britain (Devon and Cornwall) basket surveyCollection date unreported | min. | ||
| Squash, as soldNorton et al. 2015 | SW Britain (Devon and Cornwall) basket surveyCollection date unreported | max. | ||
| Squash, as soldU.S. Food and Drug Administration 2024 | Vegetables, FY20182009–2024 | sample value. | ||
| Squash, as soldU.S. Food and Drug Administration 2024 | Vegetables, FY20192009–2024 | sample value. | ||
| Squash, as soldU.S. Food and Drug Administration 2024 | Vegetables, FY20192009–2024 | not detected. | ||
| Squash, as soldAltıkulaç et al. 2025 | Group II2021–2022Dry weight | mean. | ||
| Squash, as soldAbbas et al. 2010 | cucurbit vegetables2007–2008Basis not stated | mean. | ||
9 findings · 4 studies | ||||
| Squash, as soldWHO GEMS/Food | EURO2003–2023 | median. | ||
| Squash, as soldWHO GEMS/Food | EURO2000 | median. | ||
| Squash, as soldWHO GEMS/Food | EURO2003–2017 | median. | ||
| Squash, as soldWHO GEMS/Food | WPRO2004 | median. | ||
| Squash, as soldU.S. Food and Drug Administration 2024 | Vegetables, FY20182009–2024 | not detected. | ||
| Squash, as soldU.S. Food and Drug Administration 2024 | Vegetables, FY20192009–2024 | not detected. | ||
| Squash, as soldU.S. Food and Drug Administration 2024 | Vegetables, FY20192009–2024 | not detected. | ||
| Squash, as soldAltıkulaç et al. 2025 | Group II2021–2022Dry weight | mean. | ||
| Squash, as soldAbbas et al. 2010 | cucurbit vegetables2007–2008Basis not stated | mean. | ||
2 findings · 1 study | ||||
| Squash, as soldWHO GEMS/Food | EURO2007–2011 | median. | ||
| Squash, as soldWHO GEMS/Food | EURO2017 | median. | ||
1 finding · 1 study | ||||
| Squash, as soldWHO GEMS/Food | EURO2017 | median. | ||
4 findings · 3 studies | ||||
| Squash, as soldWHO GEMS/Food | EURO2000 | median. | ||
| Squash, as soldWHO GEMS/Food | WPRO2004 | median. | ||
| Squash, as soldU.S. Food and Drug Administration 2024 | Vegetables, FY20192009–2024 | not detected. | ||
| Squash, as soldAbbas et al. 2010 | cucurbit vegetables2007–2008Basis not stated | mean. | ||
3 findings · 2 studies | ||||
| Squash, as soldGuerra et al. 2012 | CEAGESP wholesale market2009 | mean. | ||
| Squash, as soldGuerra et al. 2012 | CEAGESP wholesale market2009 | mean. | ||
| Squash, as soldAltıkulaç et al. 2025 | Group II2021–2022Dry weight | mean. | ||
4 findings · 3 studies | ||||
| Squash, as soldWHO GEMS/Food | EURO2000 | median. | ||
| Squash, as soldGuerra et al. 2012 | CEAGESP wholesale market2009 | mean. | ||
| Squash, as soldGuerra et al. 2012 | CEAGESP wholesale market2009 | mean. | ||
| Squash, as soldAltıkulaç et al. 2025 | Group II2021–2022Dry weight | mean. | ||
2 findings · 2 studies | ||||
| Squash, as soldWHO GEMS/Food | EURO2000 | median. | ||
| Squash, as soldAltıkulaç et al. 2025 | Group II2021–2022Dry weight | mean. | ||
3 findings · 2 studies | ||||
| Squash, as soldGuerra et al. 2012 | CEAGESP wholesale market2009 | mean. | ||
| Squash, as soldGuerra et al. 2012 | CEAGESP wholesale market2009 | mean. | ||
| Squash, as soldAltıkulaç et al. 2025 | Group II2021–2022Dry weight | mean. | ||
1 finding · 1 study | ||||
| Squash, as soldAltıkulaç et al. 2025 | Group II2021–2022Dry weight | mean. | ||
1 finding · 1 study | ||||
| Squash, as soldAltıkulaç et al. 2025 | Group II2021–2022Dry weight | mean. | ||
1 finding · 1 study | ||||
| Squash, as soldAltıkulaç et al. 2025 | Group II2021–2022Dry weight | mean. | ||
1 finding · 1 study | ||||
| Squash, as soldAltıkulaç et al. 2025 | Group II2021–2022Dry weight | mean. | ||
1 finding · 1 study | ||||
| Squash, as soldAltıkulaç et al. 2025 | Group II2021–2022Dry weight | mean. | ||
1 finding · 1 study | ||||
| Squash, as soldAltıkulaç et al. 2025 | Group II2021–2022Dry weight | mean. | ||
1 finding · 1 study | ||||
| Squash, as soldAltıkulaç et al. 2025 | Group II2021–2022Dry weight | mean. | ||
Shared dataset methods and interpretation
Source summaries retain their original statistic, material, basis and censoring. Each source drawer identifies methods and overlapping samples. No matched reference or pooled distribution is inferred.
HMI squash Pb reference · Squash, as sold
Reference and scope
HMI squash Pb reference · Squash, as sold. Squash, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤1.38 | 1–2 (bounded) | 2–7 (bounded) |
| Alternative weighting | ≤1.38 | 1–2 (bounded) | 2–7 (bounded) |
34 reference units; 2 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 32 | 50% |
| U.S. Food and Drug Administration 2024 | 2 | 50% |
Methods
HMI pools subgroup medians for squash, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
2 sampling families with different designs; none is a probability sample of world supply. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:squash-6f9122a6c830:54970d9545ba
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI squash Pb reference · Squash, juice
Reference and scope
HMI squash Pb reference · Squash, juice. Squash, juice; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤50 | ≤50 | ≤50 |
| Alternative weighting | ≤50 | ≤50 | ≤50 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for squash, juice on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
WHO GEMS/Food is the only compatible sampling family for squash, juice on this basis in the completed squash ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:squash-f19beff110df:8d53ac238c79
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI squash Cd reference · Squash, as sold
Reference and scope
HMI squash Cd reference · Squash, as sold. Squash, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 1–2 (bounded) | 2 | 3.1 |
| Alternative weighting | 1–2 (bounded) | 2 | 3.1 |
26 reference units; 3 sampling families. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 23 | 33% |
| Norton et al. 2015 | 1 | 33% |
| U.S. Food and Drug Administration 2024 | 2 | 33% |
Methods
HMI pools subgroup medians for squash, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
3 sampling families with different designs; none is a probability sample of world supply. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:squash-e4bf1c2f7d04:ba905ef38397
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI squash tAs reference · Squash, as sold
Reference and scope
HMI squash tAs reference · Squash, as sold. Squash, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤5 | ≤9 | ≤11.6 |
| Alternative weighting | ≤4.04 | ≤8.75 | ≤11.8 |
21 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 21 | 100% |
Methods
HMI pools subgroup medians for squash, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
WHO GEMS/Food is the only compatible sampling family for squash, as sold on this basis in the completed squash ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:squash-c9ae15799fa1:c891c6f02845
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI squash iAs reference · Squash, as sold
Reference and scope
HMI squash iAs reference · Squash, as sold. Squash, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 0.225–5.22 (bounded) | 24.2–29 (bounded) | 71 |
| Alternative weighting | 0.225–5.22 (bounded) | 24.2–29 (bounded) | 71 |
4 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 4 | 100% |
Methods
HMI pools subgroup medians for squash, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
WHO GEMS/Food is the only compatible sampling family for squash, as sold on this basis in the completed squash ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:squash-429527199f48:9895786eb601
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI squash DMA reference · Squash, as sold
Reference and scope
HMI squash DMA reference · Squash, as sold. Squash, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | ≤20 | ≤20 | ≤20 |
| Alternative weighting | ≤20 | ≤20 | ≤20 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for squash, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
WHO GEMS/Food is the only compatible sampling family for squash, as sold on this basis in the completed squash ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:squash-680a77ef6d3c:02d971fffa9f
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
HMI squash tHg reference · Squash, as sold
Reference and scope
HMI squash tHg reference · Squash, as sold. Squash, as sold; As sold, as eaten or fresh weight, µg/kg; no moisture conversion. Distribution of subgroup median concentration values.
| Reference (µg/kg) | Q1 | Median | Q3 |
|---|---|---|---|
| Primary HMI reference | 2 | 2 | 2 |
| Alternative weighting | 2 | 2 | 2 |
1 reference units; 1 sampling family. Counts describe evidence units, not independent studies or certainty.
| Contributing family | Reference units | Weight |
|---|---|---|
| WHO GEMS/Food | 1 | 100% |
Methods
HMI pools subgroup medians for squash, as sold on a as sold, as eaten or fresh weight basis: monitoring results summarized as one median per reporting region, sampling type and collection year, total diet composites and printed sample values as single observations, and printed subgroup medians from ordinary farms or markets. Each sampling family has equal total weight. Non-detects stay as zero-to-limit intervals, so quartiles carry lower and upper bounds. Means, ranges and maxima never enter as observations. Other forms, other bases, targeted sampling and results from mining, industrial, wastewater-affected, experimental, fertiliser or manufacturer settings are kept out of this reference.
Inverse weighted empirical CDF; midpoint at exact cumulative-weight boundaries. At least four reference units and a definitely positive Q1 to Q3 spread are required. This is a display eligibility rule, not statistical validation.
Limitations
WHO GEMS/Food is the only compatible sampling family for squash, as sold on this basis in the completed squash ledger, so this single-family reference cannot represent other markets. Reporting regions and purchase markets are not growing areas. Non-detects with differing limits widen the bounds. A position is descriptive concentration, not a safety or compliance judgment.
Admitted source families
Reference version and interpretation
Frozen evidence selection: 2026-10-22. Method: hmi-pooled-reference-v2.
hmi-pooled-reference-v2:squash-c1c54fd6feb6:9b014aa88a29
The reference is computed by HMI from admitted evidence, not copied from a study baseline. It describes the evidence currently in this scope; it is not a worldwide or current-lot benchmark. Source, year and region filters do not change it. Different HMI scopes are not one common ranking.
The source reports only a percentile, range or maximum for these samples, with no mean or median to place against the reference. Spread figures that do have a mean or median are shown on that row instead.
The result is below a reporting limit, and the range from zero to that limit crosses more than one band.
No medians or sample values exist for this form and metal, so no HMI reference could be built.
The HMI reference for this form has fewer than four units or no measurable spread, below the display minimum.
The result is on a basis (dry weight, or not stated) that no HMI reference for this form uses, so it cannot be placed.
Reporting limits overlap the study comparison, so no direction can be shown.
No findings match these filters. Change the selection or reset to show all source findings.
How metals reach squash
No study in the library compared squash from contaminated and ordinary settings, so the routes by which metals reach it are not measured here.
Which forms and regions measured lower
The HMI reference for lead in squash, as sold pools 34 subgroup units from 2 sampling families, with a median of between 1 and 2 µg/kg and a middle half spanning below 1.38 (lower quartile) and between 2 and 7 µg/kg (upper quartile).1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →4Analytical Results for Arsenic, Lead, Cadmium, and Mercury in Food Intended for Babies and Young Children - TEP (FY2009-FY2024)FDA analytical results tableRead source → For cadmium in squash, as sold, the reference median was 2 µg/kg, with a middle half from between 1 and 2 to 3.1 µg/kg across 26 units.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →3Cadmium and lead in vegetable and fruit produce selected from specific regional areas of the UKThe Science of the Total Environment 533, 520-527 (2015); accepted author manuscriptRead source →4Analytical Results for Arsenic, Lead, Cadmium, and Mercury in Food Intended for Babies and Young Children - TEP (FY2009-FY2024)FDA analytical results tableRead source → For total arsenic in squash, as sold, the reference median was below 9 µg/kg, with a middle half from below 5 to below 11.6 µg/kg across 21 units.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
Processing, cooking and preparation
No processing study for metals in this food is in the library yet.
Mitigation for squash
Lot testing against the applicable limit is the check that can be verified.
No measured way to lower metals in this food is in the library yet.
Trade-offs and limits of controls
Metals do not move together, so a lot that passes a lead limit says little about cadmium, arsenic or nickel unless those are tested as well.
Testing squash for metals
Results depend on the method and its reporting limit. Reporting limits for lead ranged from 0.667 µg/kg (WHO GEMS/Food) to 3,000 µg/kg (WHO GEMS/Food), so a non-detect from a less sensitive method says much less.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → Reporting limits for cadmium ranged from 0.64 µg/kg (Altıkulaç et al. 2025) to 1,000 µg/kg (WHO GEMS/Food), so a non-detect from a less sensitive method says much less.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →5Evaluation of Health Risks Associated with Potential Toxic Elements in Selected Vegetables Consumed in the Western Black Sea Region of TurkeyACS Omega 2025, 10, 8843-8858Read source → Reporting limits for total arsenic ranged from 0.667 µg/kg (WHO GEMS/Food) to 3,300 µg/kg (WHO GEMS/Food), so a non-detect from a less sensitive method says much less.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
A useful lot result names the form, the basis and a quantification limit well below the limit that applies.
Buying and verifying squash
No maximum level for metals in squash was verified from primary text for this page; buyers should confirm the limit that applies in the destination market.
Exposure from squash
No source in the library converted squash concentrations into a verified estimate of intake for a defined population. Concentrations describe the food, not individual risk.
Evidence review and remaining gaps
Every source record that names squash was decided on its content: 6 occurrence extracted, 6 records in all. The occurrence table renders every extracted result; held values remain visible with their reason.
References identify the sources used in these answers. The Sources index preserves additional discovery links; inclusion there does not mean a source has been reviewed for this assessment. Corrections, completed searches, new direct evidence and changes in requirements should reopen the relevant answer.
Squash FAQs
What heavy metals are found in squash?
The library reports lead, cadmium, total arsenic, inorganic arsenic, dimethylarsinic acid, total mercury, nickel, chromium, aluminium, Co, Cu, Fe, Mn, Zn, V, Sr and Ti in squash, most often lead, cadmium and total arsenic.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →2Heavy metals in vegetables and potential risk for human healthScientia Agricola 69(1):54-60Read source →3Cadmium and lead in vegetable and fruit produce selected from specific regional areas of the UKThe Science of the Total Environment 533, 520-527 (2015); accepted author manuscriptRead source →4Analytical Results for Arsenic, Lead, Cadmium, and Mercury in Food Intended for Babies and Young Children - TEP (FY2009-FY2024)FDA analytical results tableRead source → WHO GEMS/Food submissions reported lead in squash, as sold from 214 results in 3 reporting regions, with a subgroup median of 3.13 µg/kg.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
How much of the arsenic in squash is inorganic?
Inorganic arsenic, the more toxic form, was measured in 2 results from 1 source, far fewer than total arsenic.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source → WHO GEMS/Food submissions reported inorganic arsenic in squash, as sold from 19 results in 1 reporting region, with a subgroup median of 75.4 µg/kg.1GEMS/Food Contaminants database heavy-metal exportsGEMS/Food Contamination Monitoring and Assessment ProgrammeRead source →
References
Works cited on this page, in citation-number order. See Sources for this page’s source inventory. Each title links to a source record with bibliographic details, reported findings, and document provenance.
- GEMS/Food Contaminants database heavy-metal exportsDataset
- Heavy metals in vegetables and potential risk for human healthPeer-reviewed
- Cadmium and lead in vegetable and fruit produce selected from specific regional areas of the UKPeer-reviewed
- Analytical Results for Arsenic, Lead, Cadmium, and Mercury in Food Intended for Babies and Young Children - TEP (FY2009-FY2024)Dataset
- Evaluation of Health Risks Associated with Potential Toxic Elements in Selected Vegetables Consumed in the Western Black Sea Region of TurkeyPeer-reviewed
- Monitoring of toxic metals (cadmium, lead, arsenic and mercury) in vegetables of Sindh, PakistanPeer-reviewed
Sources
Browse Squash Sources for sources cited on this page and additional discovery candidates. The searchable index distinguishes verified citation use from discovery relationships whose relevance has not been established.
Update history
22 October 2026: Rebuilt from every squash record in the library: 6 occurrence sources, references by form and basis, same-study contrasts.
